Line of Evidence (LOE) for Decision ID 74204, Aluminum
|
Region 1 |
Klamath River HU, Shasta River HA |
|
|
LOE ID: |
123161 |
|
Pollutant: |
Aluminum |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Total |
|
Beneficial Use: |
Municipal & Domestic Supply |
|
Number of Samples: |
5 |
Number of Exceedances: |
4 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
State Water Board staff re-assessed SWAMP data for Klamath River HU, Shasta River HA to determine beneficial use support and results are as follows: 4 of 5 samples exceed the criterion for Aluminum, Total. This LOE re-assesses data from LOE 21509 from the 2010 Integrated Report. Data were re-assessed in order to (1) update the numeric objective, and (2) evaluate these data in their own LOE, instead of being evaluated in the same LOE as other metals data. |
Data Reference: |
Surface Water Ambient Monitoring Program (SWAMP). Summary Report for the North Coast Region (RWQCB-1) for years 2000-2006. North Coast Regional Water Quality Control Board. March 2008 |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
Water Quality Control Plan, North Coast Region (NCRWQCB 2011): Waters designated for use as domestic or municipal supply (MUN) shall not contain concentrations of chemical constituents in excess of the limits specified in California Code of Regulations, Title 22, Chapter 15. The secondary maximum contaminant level listed in Table 64449-A for Aluminum is 0.2 mg/L. |
Objective/Criterion Reference: |
Water Quality Control Plan (Basin Plan) for the North Coast Region |
Objective/Criterion Reference: |
Secondary Maximum Contaminant Levels and Compliance. CCR Title 22 section 64449. |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
Data for this line of evidence for Klamath River HU, Shasta River HA was collected at 1 monitoring site [ Shasta River at Montague - 105SHAMON] |
Temporal Representation: |
Data was collected over the time period 10/7/2002-6/19/2003. |
Environmental Conditions: |
There are no known environmental conditions (e.g., seasonality, land use practices, fire events, storms, etc.) that are related to these data. |
QAPP Information: |
Quality control was conducted in accordance with the SWAMP Quality Assurance Management Plan (SWAMP 2002). |
QAPP Information Reference(s): |
Quality Assurance Management Plan for the State of California's Surface Water Ambient Monitoring Program. Sacramento, CA. State Water Resources Control Board. SWAMP. December 2002 (1st version)
|
|
Line of Evidence (LOE) for Decision ID 74204, Aluminum
|
Region 1 |
Klamath River HU, Shasta River HA |
|
|
LOE ID: |
103105 |
|
Pollutant: |
Aluminum |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Total |
|
Beneficial Use: |
Municipal & Domestic Supply |
|
Number of Samples: |
5 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP RWB1 Monitoring data for Klamath River HU, Shasta River HA to determine beneficial use support and results are as follows: 0 of 5 samples exceeded the water quality standard for Aluminum. |
Data Reference: |
Water Quality Assessment Data for the 2018 solicitation cycle submitted through CEDEN for SWAMP RWB1 Monitoring .
|
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
Water Quality Control Plan, North Coast Region (NCRWQCB 2018): Waters designated for use as domestic or municipal supply (MUN) shall not contain concentrations of chemical constituents in excess of the limits specified in California Code of Regulations, Title 22, Chapter 15. The secondary maximum contaminant level listed in Table 64449-A for Aluminum is 0.2 mg/L. |
Objective/Criterion Reference: |
Water Quality Control Plan (Basin Plan) for the North Coast Region |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
The samples were collected at 1 monitoring site(s) (105SH1452) |
Temporal Representation: |
The samples were collected between the dates of 2013-03-06 and 2013-11-20 |
Environmental Conditions: |
|
QAPP Information: |
Quality Assurance Program Plan and Standard Operating Procedures for SWAMP program |
QAPP Information Reference(s): |
Quality Assurance Program Plans, Quality Assurance Project Plans, and Standard Operating Procedures for the SWAMP program |
|
Line of Evidence (LOE) for Decision ID 74204, Aluminum
|
Region 1 |
Klamath River HU, Shasta River HA |
|
|
LOE ID: |
103106 |
|
Pollutant: |
Aluminum |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Total |
|
Beneficial Use: |
Municipal & Domestic Supply |
|
Number of Samples: |
5 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP RWB1 Monitoring data for Klamath River HU, Shasta River HA to determine beneficial use support and results are as follows: 0 of 5 samples exceeded the water quality standard for Aluminum. |
Data Reference: |
Water Quality Assessment Data for the 2018 solicitation cycle submitted through CEDEN for SWAMP RWB1 Monitoring .
|
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
Water Quality Control Plan, North Coast Region (NCRWQCB 2018): Waters designated for use as domestic or municipal supply (MUN) shall not contain concentrations of chemical constituents in excess of the limits specified in California Code of Regulations, Title 22, Chapter 15. The secondary maximum contaminant level listed in Table 64449-A for Aluminum is 0.2 mg/L. |
Objective/Criterion Reference: |
Water Quality Control Plan (Basin Plan) for the North Coast Region |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
The samples were collected at 1 monitoring site(s) (105SH9274) |
Temporal Representation: |
The samples were collected between the dates of 2013-03-07 and 2013-11-20 |
Environmental Conditions: |
|
QAPP Information: |
Quality Assurance Program Plan and Standard Operating Procedures for SWAMP program |
QAPP Information Reference(s): |
Quality Assurance Program Plans, Quality Assurance Project Plans, and Standard Operating Procedures for the SWAMP program |
|
Line of Evidence (LOE) for Decision ID 74204, Aluminum
|
Region 1 |
Klamath River HU, Shasta River HA |
|
|
LOE ID: |
41316 |
|
Pollutant: |
Aluminum |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Total |
|
Beneficial Use: |
Municipal & Domestic Supply |
|
Number of Samples: |
4 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP data for Klamath River HU, Shasta River HA to determine beneficial use support and results are as follows: 0 of 4 samples exceed the criterion for Aluminum. |
Data Reference: |
RWB1 Trend Maintenance Periods FYs 2007 2008 |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
Water Quality Control Plan, North Coast Region (NCRWQCB 2011): Waters designated for use as domestic or municipal supply (MUN) shall not contain concentrations of chemical constituents in excess of the limits specified in California Code of Regulations, Title 22, Chapter 15. The secondary maximum contaminant level listed in Table 64449-A for Aluminum is 0.2 mg/L. |
Objective/Criterion Reference: |
Secondary Maximum Contaminant Levels and Compliance. CCR Title 22 section 64449. |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
Data for this line of evidence for Klamath River HU, Shasta River HA was collected at 1 monitoring site [ Shasta River near Edgewood - 105SHAEDG] |
Temporal Representation: |
Data was collected over the time period 11/15/2007-7/16/2008. |
Environmental Conditions: |
Staff is not aware of any special conditions that might affect interpretation of the data. |
QAPP Information: |
The SWAMP QAPP (2008) was followed. |
QAPP Information Reference(s): |
Surface Water Ambient Monitoring Program Quality Assurance Program Plan |
|
Line of Evidence (LOE) for Decision ID 74204, Aluminum
|
Region 1 |
Klamath River HU, Shasta River HA |
|
|
LOE ID: |
123162 |
|
Pollutant: |
Aluminum |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Total |
|
Beneficial Use: |
Municipal & Domestic Supply |
|
Number of Samples: |
5 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
State Water Board staff re-assessed SWAMP data for Klamath River HU, Shasta River HA to determine beneficial use support and results are as follows: 0 of 5 samples exceed the criterion for Aluminum, Total. This LOE re-assesses data from LOE 21509 from the 2010 Integrated Report. Data were re-assessed in order to (1) update the numeric objective, and (2) evaluate these data in their own LOE, instead of being evaluated in the same LOE as other metals data. |
Data Reference: |
Surface Water Ambient Monitoring Program (SWAMP). Summary Report for the North Coast Region (RWQCB-1) for years 2000-2006. North Coast Regional Water Quality Control Board. March 2008 |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
Water Quality Control Plan, North Coast Region (NCRWQCB 2011): Waters designated for use as domestic or municipal supply (MUN) shall not contain concentrations of chemical constituents in excess of the limits specified in California Code of Regulations, Title 22, Chapter 15. The secondary maximum contaminant level listed in Table 64449-A for Aluminum is 0.2 mg/L. |
Objective/Criterion Reference: |
Water Quality Control Plan (Basin Plan) for the North Coast Region |
Objective/Criterion Reference: |
Secondary Maximum Contaminant Levels and Compliance. CCR Title 22 section 64449. |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
Data for this line of evidence for Klamath River HU, Shasta River HA was collected at 1 monitoring site [ Shasta River near Edgewood - 105SH9274] |
Temporal Representation: |
Data was collected over the time period 10/7/2002-6/19/2003. |
Environmental Conditions: |
There are no known environmental conditions (e.g., seasonality, land use practices, fire events, storms, etc.) that are related to these data. |
QAPP Information: |
Quality control was conducted in accordance with the SWAMP Quality Assurance Management Plan (SWAMP 2002). |
QAPP Information Reference(s): |
Quality Assurance Management Plan for the State of California's Surface Water Ambient Monitoring Program. Sacramento, CA. State Water Resources Control Board. SWAMP. December 2002 (1st version)
|
|
Line of Evidence (LOE) for Decision ID 74204, Aluminum
|
Region 1 |
Klamath River HU, Shasta River HA |
|
|
LOE ID: |
41339 |
|
Pollutant: |
Aluminum |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Total |
|
Beneficial Use: |
Municipal & Domestic Supply |
|
Number of Samples: |
4 |
Number of Exceedances: |
1 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP data for Klamath River HU, Shasta River HA to determine beneficial use support and results are as follows: 1 of 4 samples exceed the criterion for Aluminum. |
Data Reference: |
RWB1 Trend Maintenance Periods FYs 2007 2008 |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
Water Quality Control Plan, North Coast Region (NCRWQCB 2011): Waters designated for use as domestic or municipal supply (MUN) shall not contain concentrations of chemical constituents in excess of the limits specified in California Code of Regulations, Title 22, Chapter 15. The secondary maximum contaminant level listed in Table 64449-A for Aluminum is 0.2 mg/L. |
Objective/Criterion Reference: |
Secondary Maximum Contaminant Levels and Compliance. CCR Title 22 section 64449. |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
Data for this line of evidence for Klamath River HU, Shasta River HA was collected at 1 monitoring site [ Shasta River at Hwy 263 - 105SHA263] |
Temporal Representation: |
Data was collected over the time period 11/15/2007-7/16/2008. |
Environmental Conditions: |
Staff is not aware of any special conditions that might affect interpretation of the data. |
QAPP Information: |
The SWAMP QAPP (2008) was followed. |
QAPP Information Reference(s): |
Surface Water Ambient Monitoring Program Quality Assurance Program Plan |
|
Line of Evidence (LOE) for Decision ID 74204, Aluminum
|
Region 1 |
Klamath River HU, Shasta River HA |
|
|
LOE ID: |
103104 |
|
Pollutant: |
Aluminum |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Dissolved |
|
Beneficial Use: |
Municipal & Domestic Supply |
|
Number of Samples: |
5 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP RWB1 Monitoring data for Klamath River HU, Shasta River HA to determine beneficial use support and results are as follows: 0 of 5 samples exceeded the water quality standard for Aluminum. |
Data Reference: |
Water Quality Assessment Data for the 2018 solicitation cycle submitted through CEDEN for SWAMP RWB1 Monitoring .
|
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
Water Quality Control Plan, North Coast Region (NCRWQCB 2018): Waters designated for use as domestic or municipal supply (MUN) shall not contain concentrations of chemical constituents in excess of the limits specified in California Code of Regulations, Title 22, Chapter 15. The secondary maximum contaminant level listed in Table 64449-A for Aluminum is 0.2 mg/L. |
Objective/Criterion Reference: |
Water Quality Control Plan (Basin Plan) for the North Coast Region |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
The samples were collected at 1 monitoring site(s) (105SH9274) |
Temporal Representation: |
The samples were collected between the dates of 2013-03-07 and 2013-11-20 |
Environmental Conditions: |
|
QAPP Information: |
Quality Assurance Program Plan and Standard Operating Procedures for SWAMP program |
QAPP Information Reference(s): |
Quality Assurance Program Plans, Quality Assurance Project Plans, and Standard Operating Procedures for the SWAMP program |
|
Line of Evidence (LOE) for Decision ID 74204, Aluminum
|
Region 1 |
Klamath River HU, Shasta River HA |
|
|
LOE ID: |
123170 |
|
Pollutant: |
Aluminum |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Total |
|
Beneficial Use: |
Municipal & Domestic Supply |
|
Number of Samples: |
7 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
State Water Board staff re-assessed SWAMP data for Klamath River HU, Shasta River HA to determine beneficial use support and results are as follows: 0 of 7 samples exceed the criterion for Aluminum, Total. This LOE re-assesses data from LOE 21509 from the 2010 Integrated Report. Data were re-assessed in order to (1) update the numeric objective, and (2) evaluate these data in their own LOE, instead of being evaluated in the same LOE as other metals data. |
Data Reference: |
Surface Water Ambient Monitoring Program (SWAMP). Summary Report for the North Coast Region (RWQCB-1) for years 2000-2006. North Coast Regional Water Quality Control Board. March 2008 |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
Water Quality Control Plan, North Coast Region (NCRWQCB 2011): Waters designated for use as domestic or municipal supply (MUN) shall not contain concentrations of chemical constituents in excess of the limits specified in California Code of Regulations, Title 22, Chapter 15. The secondary maximum contaminant level listed in Table 64449-A for Aluminum is 0.2 mg/L. |
Objective/Criterion Reference: |
Water Quality Control Plan (Basin Plan) for the North Coast Region |
Objective/Criterion Reference: |
Secondary Maximum Contaminant Levels and Compliance. CCR Title 22 section 64449. |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
Data for this line of evidence for Klamath River HU, Shasta River HA was collected at 1 monitoring site [ Yreka Creek at Anderson Rd - 105YREAND] |
Temporal Representation: |
Data was collected over the time period 10/9/2002-6/20/2005. |
Environmental Conditions: |
There are no known environmental conditions (e.g., seasonality, land use practices, fire events, storms, etc.) that are related to these data. |
QAPP Information: |
Quality control was conducted in accordance with the SWAMP Quality Assurance Management Plan (SWAMP 2002). |
QAPP Information Reference(s): |
Quality Assurance Management Plan for the State of California's Surface Water Ambient Monitoring Program. Sacramento, CA. State Water Resources Control Board. SWAMP. December 2002 (1st version)
|
|
Line of Evidence (LOE) for Decision ID 74204, Aluminum
|
Region 1 |
Klamath River HU, Shasta River HA |
|
|
LOE ID: |
123171 |
|
Pollutant: |
Aluminum |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Total |
|
Beneficial Use: |
Municipal & Domestic Supply |
|
Number of Samples: |
3 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
State Water Board staff re-assessed SWAMP data for Klamath River HU, Shasta River HA to determine beneficial use support and results are as follows: 0 of 3 samples exceed the criterion for Aluminum, Total. This LOE re-assesses data from LOE 21509 from the 2010 Integrated Report. Data were re-assessed in order to (1) update the numeric objective, and (2) evaluate these data in their own LOE, instead of being evaluated in the same LOE as other metals data. |
Data Reference: |
Surface Water Ambient Monitoring Program (SWAMP). Summary Report for the North Coast Region (RWQCB-1) for years 2000-2006. North Coast Regional Water Quality Control Board. March 2008 |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
Water Quality Control Plan, North Coast Region (NCRWQCB 2011): Waters designated for use as domestic or municipal supply (MUN) shall not contain concentrations of chemical constituents in excess of the limits specified in California Code of Regulations, Title 22, Chapter 15. The secondary maximum contaminant level listed in Table 64449-A for Aluminum is 0.2 mg/L. |
Objective/Criterion Reference: |
Water Quality Control Plan (Basin Plan) for the North Coast Region |
Objective/Criterion Reference: |
Secondary Maximum Contaminant Levels and Compliance. CCR Title 22 section 64449. |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
Data for this line of evidence for Klamath River HU, Shasta River HA was collected at 1 monitoring site [ Yreka Creek at Highway 3 - 105YREHW3] |
Temporal Representation: |
Data was collected over the time period 10/21/2004-6/20/2005. |
Environmental Conditions: |
There are no known environmental conditions (e.g., seasonality, land use practices, fire events, storms, etc.) that are related to these data. |
QAPP Information: |
Quality control was conducted in accordance with the SWAMP Quality Assurance Management Plan (SWAMP 2002). |
QAPP Information Reference(s): |
Quality Assurance Management Plan for the State of California's Surface Water Ambient Monitoring Program. Sacramento, CA. State Water Resources Control Board. SWAMP. December 2002 (1st version)
|
|
Line of Evidence (LOE) for Decision ID 74204, Aluminum
|
Region 1 |
Klamath River HU, Shasta River HA |
|
|
LOE ID: |
47545 |
|
Pollutant: |
Aluminum |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Total |
|
Beneficial Use: |
Municipal & Domestic Supply |
|
Number of Samples: |
28 |
Number of Exceedances: |
7 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP data for Klamath River HU, Shasta River HA to determine beneficial use support and results are as follows: 7 of 28 samples exceed the criterion for Aluminum. This LOE replaces LOE 25362 from the 2010 Integrated Report cycle. The original LOE has been replaced in order to re-assess data against the secondary MCL (instead of the primary MCL). |
Data Reference: |
Surface Water Ambient Monitoring Program (SWAMP). Summary Report for the North Coast Region (RWQCB-1) for years 2000-2006. North Coast Regional Water Quality Control Board. March 2008 |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
Water Quality Control Plan, North Coast Region (NCRWQCB 2011): Waters designated for use as domestic or municipal supply (MUN) shall not contain concentrations of chemical constituents in excess of the limits specified in California Code of Regulations, Title 22, Chapter 15. The secondary maximum contaminant level listed in Table 64449-A for Aluminum is 0.2 mg/L. |
Objective/Criterion Reference: |
Secondary Maximum Contaminant Levels and Compliance. CCR Title 22 section 64449. |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
Samples were collected in the mainstem Shasta River from 3 locations as follows: (1) near Edgewood Road (SWAMP Station ID SHAEDG), (2) at Montague Grenada Road (SWAMP Station ID SHAMON), and (3) at Highway 263 (SWAMP Station ID SHA263). Samples were collected in well-mixed flows in glides or riffles. |
Temporal Representation: |
The samples from Edgewood Road and Montague Grenada Road were collected as grab samples during 5 site visits at each site during the 2002 - 2003 fiscal years. Samples from Highway 263 were collected as grab samples during 22 site visits during the 2000 - 2006 fiscal years. The site visits corresponded to fall, winter, spring and early summer seasonal conditions. |
Environmental Conditions: |
There are no known environmental conditions (e.g., seasonality, land use practices, fire events, storms, etc.) that are related to these data. |
QAPP Information: |
Quality control was conducted in accordance with the SWAMP Quality Assurance Management Plan (Puckett 2002). |
QAPP Information Reference(s): |
Quality Assurance Management Plan for the State of California's Surface Water Ambient Monitoring Program. Sacramento, CA. State Water Resources Control Board. SWAMP. December 2002 (1st version)
|
|
Line of Evidence (LOE) for Decision ID 74204, Aluminum
|
Region 1 |
Klamath River HU, Shasta River HA |
|
|
LOE ID: |
47546 |
|
Pollutant: |
Aluminum |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Total |
|
Beneficial Use: |
Municipal & Domestic Supply |
|
Number of Samples: |
10 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP data for Klamath River HU, Shasta River HA to determine beneficial use support and results are as follows: 0 of 10 samples from Yreka Creek exceed the criterion for Aluminum. This LOE replaces LOE 25363 from the 2010 Integrated Report cycle. The original LOE has been replaced in order to re-assess data against the secondary MCL (instead of the primary MCL). |
Data Reference: |
Surface Water Ambient Monitoring Program (SWAMP). Summary Report for the North Coast Region (RWQCB-1) for years 2000-2006. North Coast Regional Water Quality Control Board. March 2008 |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
Water Quality Control Plan, North Coast Region (NCRWQCB 2011): Waters designated for use as domestic or municipal supply (MUN) shall not contain concentrations of chemical constituents in excess of the limits specified in California Code of Regulations, Title 22, Chapter 15. The secondary maximum contaminant level listed in Table 64449-A for Aluminum is 0.2 mg/L. |
Objective/Criterion Reference: |
Secondary Maximum Contaminant Levels and Compliance. CCR Title 22 section 64449. |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
Samples were collected from Yreka Creek from two locations as follows: (1) at Highway 3 (SWAMP Station ID YREHW3), and (2) at Anderson Grade Road (SWAMP Station ID YREAND). Samples were collected from well-mixed flows in glides or riffles. |
Temporal Representation: |
Samples were collected from October 2004 to June 2005. The site visits corresponded to fall, winter, spring and early summer seasonal conditions. |
Environmental Conditions: |
There are no known environmental conditions (e.g., seasonality, land use practices, fire events, storms, etc.) that are related to these data. |
QAPP Information: |
Quality control was conducted in accordance with the SWAMP Quality Assurance Management Plan (Puckett 2002). |
QAPP Information Reference(s): |
Quality Assurance Management Plan for the State of California's Surface Water Ambient Monitoring Program. Sacramento, CA. State Water Resources Control Board. SWAMP. December 2002 (1st version)
|
|
Line of Evidence (LOE) for Decision ID 74204, Aluminum
|
Region 1 |
Klamath River HU, Shasta River HA |
|
|
LOE ID: |
103103 |
|
Pollutant: |
Aluminum |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Dissolved |
|
Beneficial Use: |
Municipal & Domestic Supply |
|
Number of Samples: |
5 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP RWB1 Monitoring data for Klamath River HU, Shasta River HA to determine beneficial use support and results are as follows: 0 of 5 samples exceeded the water quality standard for Aluminum. |
Data Reference: |
Water Quality Assessment Data for the 2018 solicitation cycle submitted through CEDEN for SWAMP RWB1 Monitoring .
|
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
Water Quality Control Plan, North Coast Region (NCRWQCB 2018): Waters designated for use as domestic or municipal supply (MUN) shall not contain concentrations of chemical constituents in excess of the limits specified in California Code of Regulations, Title 22, Chapter 15. The secondary maximum contaminant level listed in Table 64449-A for Aluminum is 0.2 mg/L. |
Objective/Criterion Reference: |
Water Quality Control Plan (Basin Plan) for the North Coast Region |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
The samples were collected at 1 monitoring site(s) (105SH1452) |
Temporal Representation: |
The samples were collected between the dates of 2013-03-06 and 2013-11-20 |
Environmental Conditions: |
|
QAPP Information: |
Quality Assurance Program Plan and Standard Operating Procedures for SWAMP program |
QAPP Information Reference(s): |
Quality Assurance Program Plans, Quality Assurance Project Plans, and Standard Operating Procedures for the SWAMP program |
|
Line of Evidence (LOE) for Decision ID 74204, Aluminum
|
Region 1 |
Klamath River HU, Shasta River HA |
|
|
LOE ID: |
123160 |
|
Pollutant: |
Aluminum |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Total |
|
Beneficial Use: |
Municipal & Domestic Supply |
|
Number of Samples: |
19 |
Number of Exceedances: |
3 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
State Water Board staff re-assessed SWAMP data for Klamath River HU, Shasta River HA to determine beneficial use support and results are as follows: 3 of 19 samples exceed the criterion for Aluminum, Total. This LOE re-assesses data from LOE 21509 from the 2010 Integrated Report. Data were re-assessed in order to (1) update the numeric objective, and (2) evaluate these data in their own LOE, instead of being evaluated in the same LOE as other metals data. |
Data Reference: |
Surface Water Ambient Monitoring Program (SWAMP). Summary Report for the North Coast Region (RWQCB-1) for years 2000-2006. North Coast Regional Water Quality Control Board. March 2008 |
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SWAMP Data: |
SWAMP |
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Water Quality Objective/Criterion: |
Water Quality Control Plan, North Coast Region (NCRWQCB 2011): Waters designated for use as domestic or municipal supply (MUN) shall not contain concentrations of chemical constituents in excess of the limits specified in California Code of Regulations, Title 22, Chapter 15. The secondary maximum contaminant level listed in Table 64449-A for Aluminum is 0.2 mg/L. |
Objective/Criterion Reference: |
Water Quality Control Plan (Basin Plan) for the North Coast Region |
Objective/Criterion Reference: |
Secondary Maximum Contaminant Levels and Compliance. CCR Title 22 section 64449. |
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Evaluation Guideline: |
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Guideline Reference: |
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Spatial Representation: |
Data for this line of evidence for Klamath River HU, Shasta River HA was collected at 1 monitoring site [ Shasta River at Hwy 263 - 105SH1452] |
Temporal Representation: |
Data was collected over the time period 2/27/2002-11/16/2006. |
Environmental Conditions: |
There are no known environmental conditions (e.g., seasonality, land use practices, fire events, storms, etc.) that are related to these data. |
QAPP Information: |
Quality control was conducted in accordance with the SWAMP Quality Assurance Management Plan (SWAMP 2002). |
QAPP Information Reference(s): |
Letter requesting acceptance of late submittal |
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Line of Evidence (LOE) for Decision ID 78845, Organic Enrichment/Low Dissolved Oxygen
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Region 1 |
Klamath River HU, Shasta River HA |
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LOE ID: |
1656 |
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Pollutant: |
Organic Enrichment/Low Dissolved Oxygen |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Not Specified |
Fraction: |
None |
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Beneficial Use: |
Cold Freshwater Habitat |
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Number of Samples: |
0 |
Number of Exceedances: |
0 |
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Data and Information Type: |
Not Specified |
Data Used to Assess Water Quality: |
Unspecified¿This LOE is a placeholder to support a 303(d) listing decision made prior to 2006. |
Data Reference: |
Placeholder reference 2006 303(d) |
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SWAMP Data: |
Non-SWAMP |
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Water Quality Objective/Criterion: |
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Objective/Criterion Reference: |
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Evaluation Guideline: |
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Guideline Reference: |
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Spatial Representation: |
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Temporal Representation: |
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Environmental Conditions: |
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QAPP Information: |
QA Info Missing |
QAPP Information Reference(s): |
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Line of Evidence (LOE) for Decision ID 78845, Organic Enrichment/Low Dissolved Oxygen
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Region 1 |
Klamath River HU, Shasta River HA |
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LOE ID: |
101356 |
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Pollutant: |
Oxygen, Dissolved |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
None |
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Beneficial Use: |
Cold Freshwater Habitat |
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Number of Samples: |
0 |
Number of Exceedances: |
0 |
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Data and Information Type: |
Not Specified |
Data Used to Assess Water Quality: |
If DO concentrations fall below the numeric objectives set forth by the Basin Plan (2018). If NO, then the waterbody is supporting that beneficial use, if YES, then that waterbody is considered impaired. |
Data Reference: |
Water Quality Control Plan (Basin Plan) for the North Coast Region |
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SWAMP Data: |
Non-SWAMP |
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Water Quality Objective/Criterion: |
Water Quality Control Plan, North Coast Region (NCRWQCB 2018): Dissolved oxygen (DO) concentrations shall conform to the numeric objectives expressed in section 3.3.5. |
Objective/Criterion Reference: |
Water Quality Control Plan (Basin Plan) for the North Coast Region |
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Evaluation Guideline: |
EVIDENCE OF SALMONID PRESENCE & LIFE CYCLE USE: Chinook, coho and steelhead are present in the watershed below Shastina and trout are present in Shastina and tributaries to Shastina (NCRWQCB 2006; Whelan 2005). Rearing occurs year-round and spawning, incubation, and emergence occurs from September 16th to June 30 (NCRWQCB 2006). Non-core rearing occurs in the mainstem Shasta River year-round, and core rearing occurs in the tributaries to the Shasta River. |
Guideline Reference: |
Email correspondence between Jim Whelan (DFG) and North Coast Regional Water Board staff regarding fisheries in Lake Shastina |
Guideline Reference: |
Staff Report for the Action Plan for the Shasta River Watershed Temperature and Dissolved Oxygen Total Maximum Daily Loads |
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Spatial Representation: |
Information pertains to Klamath River HU, Shasta River HA. |
Temporal Representation: |
Data are reflective of current conditions in this water body. |
Environmental Conditions: |
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QAPP Information: |
Information is considered to be of adequate quality for the Integrated Report process. |
QAPP Information Reference(s): |
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Line of Evidence (LOE) for Decision ID 78845, Organic Enrichment/Low Dissolved Oxygen
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Region 1 |
Klamath River HU, Shasta River HA |
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LOE ID: |
34082 |
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Pollutant: |
Oxygen, Dissolved |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Total Dissolved |
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Beneficial Use: |
Cold Freshwater Habitat |
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Number of Samples: |
4 |
Number of Exceedances: |
0 |
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Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
None of the 4 samples exceeded the objective. |
Data Reference: |
RWB1 Trend Maintenance Periods FYs 2007 2008 |
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SWAMP Data: |
SWAMP |
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Water Quality Objective/Criterion: |
Water Quality Control Plan, North Coast Region (NCRWQCB 2011): The minimum dissolved oxygen objective for the mainstem Shasta River is 7.0 mg/L. The 50% lower limit dissolved oxygen objective is 9.0 mg/L. The 50% lower limit represents the 50 percentile values of the monthly means for a calendar year. 50% or more of the monthly means must be greater than or equal to the lower limit. |
Objective/Criterion Reference: |
Water Quality Control Plan (Basin Plan) for the North Coast Region |
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Evaluation Guideline: |
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Guideline Reference: |
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Spatial Representation: |
Samples were collected from the Shasta River near Edgewood station (105SHAEDG). |
Temporal Representation: |
Samples were collected approximately once per quarter year from November 2007 to July 2008. |
Environmental Conditions: |
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QAPP Information: |
SWAMP QAPP |
QAPP Information Reference(s): |
Surface Water Ambient Monitoring Program Quality Assurance Program Plan |
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Line of Evidence (LOE) for Decision ID 78845, Organic Enrichment/Low Dissolved Oxygen
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Region 1 |
Klamath River HU, Shasta River HA |
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LOE ID: |
32897 |
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Pollutant: |
Oxygen, Dissolved |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Total Dissolved |
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Beneficial Use: |
Cold Freshwater Habitat |
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Number of Samples: |
1386 |
Number of Exceedances: |
1028 |
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Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
One thousand and twenty-eight of the thirteen hundred and eighty-six daily minimum DO values were below the 7.0 mg/L objective. Additionally, more than 50% of the daily minimum DO values at all sites in 2008 and 2009 were below 9.0 mg/L. |
Data Reference: |
Data for Various Pollutants in the Shasta Valley Resource Convservation District, 2008-2009. |
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SWAMP Data: |
Non-SWAMP |
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Water Quality Objective/Criterion: |
Water Quality Control Plan, North Coast Region (NCRWQCB 2011): The minimum dissolved oxygen objective is 7.0 mg/L. The 50% lower limit dissolved oxygen objective is 9.0 mg/L. The 50% lower limits represent the 50 percentile values for a calendar year. 50% or more of the values must be greater than or equal to the lower limit. |
Objective/Criterion Reference: |
Water Quality Control Plan (Basin Plan) for the North Coast Region |
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Evaluation Guideline: |
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Guideline Reference: |
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Spatial Representation: |
Samples were collected at the following locations: Site 105SRA1DO-SRA-Downstream Dam, site 105SRA2DO-SRA-Upstream Dam, site 105SRA3DO-SRA-Upstream Pump/Screen, and site 105SRA4DO-SRA-Highway 3 Bridge. |
Temporal Representation: |
Samples were collected between 03/22/08 and 9/1/2009. |
Environmental Conditions: |
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QAPP Information: |
Quality Assurance Project Plan for the 'Araujo Diversion Removal Project' Prepared by: Amy Hansen Shasta Valley Resource Conservation District July 30, 2007 Version Number 1.0 |
QAPP Information Reference(s): |
Quality Assurance Project Plan for the Shasta Water Association Dam Demobilization and Water Quality Improvements Project, Version Number 1.0 and for the Araujo Diversion Removal Project, Version Number 1.0. |
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Line of Evidence (LOE) for Decision ID 78845, Organic Enrichment/Low Dissolved Oxygen
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Region 1 |
Klamath River HU, Shasta River HA |
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LOE ID: |
33156 |
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Pollutant: |
Oxygen, Dissolved |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Total Dissolved |
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Beneficial Use: |
Cold Freshwater Habitat |
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Number of Samples: |
672 |
Number of Exceedances: |
448 |
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Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Four hundred and forty-eight of the six hundred and seventy-two daily minimum DO values were below the 7.0 mg/L objective. Additionally, more than 50% of the daily minimum DO values at all sites in 2008 and 2009 were below 9.0 mg/L. |
Data Reference: |
Data for Various Pollutants in the Shasta Valley Resource Convservation District, 2008-2009. |
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SWAMP Data: |
Non-SWAMP |
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Water Quality Objective/Criterion: |
Water Quality Control Plan, North Coast Region (NCRWQCB 2011): The minimum dissolved oxygen objective is 7.0 mg/L. The 50% lower limit dissolved oxygen objective is 9.0 mg/L. The 50% lower limits represent the 50 percentile values for a calendar year. 50% or more of the values must be greater than or equal to the lower limit. |
Objective/Criterion Reference: |
Water Quality Control Plan (Basin Plan) for the North Coast Region |
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Evaluation Guideline: |
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Guideline Reference: |
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Spatial Representation: |
Samples were collected at the following locations: Site 105SRS1DO-downstream of the old dam, site 105SRS2DO-upstream of the old dam, site 105SRSA3DO-Shasta River at bend, and site 105SRS4DO-Shasta River at the small bridge. |
Temporal Representation: |
Samples were collected between 03/22/08 and 9/2/2009. |
Environmental Conditions: |
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QAPP Information: |
Quality Assurance Project Plan for the 'Shasta Water Association Dam Demobilization and Water Quality Improvements Project' Prepared by: Amy Hansen Shasta Valley Resource Conservation District May 21, 2007 Version Number 1.0 |
QAPP Information Reference(s): |
Quality Assurance Project Plan for the Shasta Water Association Dam Demobilization and Water Quality Improvements Project, Version Number 1.0 and for the Araujo Diversion Removal Project, Version Number 1.0. |
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Line of Evidence (LOE) for Decision ID 78845, Organic Enrichment/Low Dissolved Oxygen
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Region 1 |
Klamath River HU, Shasta River HA |
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LOE ID: |
33870 |
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Pollutant: |
Oxygen, Dissolved |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Total Dissolved |
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Beneficial Use: |
Cold Freshwater Habitat |
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Number of Samples: |
1 |
Number of Exceedances: |
0 |
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Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
The sample collected did not exceed the objective. |
Data Reference: |
Statewide Perennial Streams Assessment 2008 |
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SWAMP Data: |
SWAMP |
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Water Quality Objective/Criterion: |
Water Quality Control Plan, North Coast Region (NCRWQCB 2011): The site specific objective for streams in the Shasta Valley HA is a minimum value of 7.0 mg/L. In addition, the 50% lower limit of 9.0 mg/L which represents the 50 percentile values of the monthly means for a calendar year applies to this water body. Therefore, 50% or more of the monthly means in a calendar year must be less than or equal to an upper limit. |
Objective/Criterion Reference: |
Water Quality Control Plan (Basin Plan) for the North Coast Region |
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Evaluation Guideline: |
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Guideline Reference: |
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Spatial Representation: |
One sample was collected from the Evans Ditch station (105PS0188). |
Temporal Representation: |
One sample was collected in August 2008. |
Environmental Conditions: |
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QAPP Information: |
SWAMP QAPP |
QAPP Information Reference(s): |
Surface Water Ambient Monitoring Program Quality Assurance Program Plan |
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Line of Evidence (LOE) for Decision ID 78845, Organic Enrichment/Low Dissolved Oxygen
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Region 1 |
Klamath River HU, Shasta River HA |
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LOE ID: |
103374 |
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Pollutant: |
Oxygen, Dissolved |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Total |
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Beneficial Use: |
Warm Freshwater Habitat |
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Number of Samples: |
5 |
Number of Exceedances: |
0 |
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Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP RWB1 Monitoring data for Klamath River HU, Shasta River HA to determine beneficial use support and results are as follows: 0 of 5 samples exceeded the water quality standard for Oxygen, Dissolved. |
Data Reference: |
Water Quality Assessment Data for the 2018 solicitation cycle submitted through CEDEN for SWAMP RWB1 Monitoring .
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|
SWAMP Data: |
SWAMP |
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Water Quality Objective/Criterion: |
Water Quality Control Plan, North Coast Basin, Chapter III, General Objectives for all Inland Surface Waters, Enclosed Bays and Estuaries states: Dissolved oxygen concentrations shall conform to those limits listed in Section 3.3.5. Section 3.3.5 lists dissolved oxygen concentration limits for WARM beneficial use waters to be a daily minimum of 5.0 mg/L and a 7-day moving average of 6.0 mg/L. |
Objective/Criterion Reference: |
Water Quality Control Plan (Basin Plan) for the North Coast Region |
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Evaluation Guideline: |
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Guideline Reference: |
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Spatial Representation: |
The samples were collected at 1 monitoring site(s) (105SH1452) |
Temporal Representation: |
The samples were collected between the dates of 2013-03-06 and 2013-11-20 |
Environmental Conditions: |
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QAPP Information: |
Quality Assurance Program Plan and Standard Operating Procedures for SWAMP program |
QAPP Information Reference(s): |
Quality Assurance Program Plans, Quality Assurance Project Plans, and Standard Operating Procedures for the SWAMP program |
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Line of Evidence (LOE) for Decision ID 78845, Organic Enrichment/Low Dissolved Oxygen
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Region 1 |
Klamath River HU, Shasta River HA |
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LOE ID: |
109508 |
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Pollutant: |
Oxygen, Dissolved |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Total |
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Beneficial Use: |
Warm Freshwater Habitat |
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Number of Samples: |
1 |
Number of Exceedances: |
0 |
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Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP Perennial Stream Surveys data for Klamath River HU, Shasta River HA to determine beneficial use support and results are as follows: 0 of 1 samples exceeded the water quality standard for Oxygen, Dissolved. |
Data Reference: |
Water Quality Assessment Data for the 2018 solicitation cycle submitted through CEDEN for SWAMP Perennial Stream Surveys .
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|
SWAMP Data: |
SWAMP |
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Water Quality Objective/Criterion: |
Water Quality Control Plan, North Coast Basin, Chapter III, General Objectives for all Inland Surface Waters, Enclosed Bays and Estuaries states: Dissolved oxygen concentrations shall conform to those limits listed in Section 3.3.5. Section 3.3.5 lists dissolved oxygen concentration limits for WARM beneficial use waters to be a daily minimum of 5.0 mg/L and a 7-day moving average of 6.0 mg/L. |
Objective/Criterion Reference: |
Water Quality Control Plan (Basin Plan) for the North Coast Region |
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Evaluation Guideline: |
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Guideline Reference: |
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Spatial Representation: |
The samples were collected at 1 monitoring site(s) (105PS0231) |
Temporal Representation: |
The samples were collected between the dates of 2013-08-29 and 2013-08-29 |
Environmental Conditions: |
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QAPP Information: |
Quality Assurance Program Plan and Standard Operating Procedures for SWAMP program |
QAPP Information Reference(s): |
Quality Assurance Program Plans, Quality Assurance Project Plans, and Standard Operating Procedures for the SWAMP program |
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Line of Evidence (LOE) for Decision ID 78845, Organic Enrichment/Low Dissolved Oxygen
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Region 1 |
Klamath River HU, Shasta River HA |
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LOE ID: |
103378 |
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Pollutant: |
Oxygen, Dissolved |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Total |
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Beneficial Use: |
Warm Freshwater Habitat |
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Number of Samples: |
5 |
Number of Exceedances: |
0 |
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Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP RWB1 Monitoring data for Klamath River HU, Shasta River HA to determine beneficial use support and results are as follows: 0 of 5 samples exceeded the water quality standard for Oxygen, Dissolved. |
Data Reference: |
Water Quality Assessment Data for the 2018 solicitation cycle submitted through CEDEN for SWAMP RWB1 Monitoring .
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|
SWAMP Data: |
SWAMP |
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Water Quality Objective/Criterion: |
Water Quality Control Plan, North Coast Basin, Chapter III, General Objectives for all Inland Surface Waters, Enclosed Bays and Estuaries states: Dissolved oxygen concentrations shall conform to those limits listed in Section 3.3.5. Section 3.3.5 lists dissolved oxygen concentration limits for WARM beneficial use waters to be a daily minimum of 5.0 mg/L and a 7-day moving average of 6.0 mg/L. |
Objective/Criterion Reference: |
Water Quality Control Plan (Basin Plan) for the North Coast Region |
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Evaluation Guideline: |
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Guideline Reference: |
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Spatial Representation: |
The samples were collected at 1 monitoring site(s) (105SH9274) |
Temporal Representation: |
The samples were collected between the dates of 2013-03-07 and 2013-11-20 |
Environmental Conditions: |
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QAPP Information: |
Quality Assurance Program Plan and Standard Operating Procedures for SWAMP program |
QAPP Information Reference(s): |
Quality Assurance Program Plans, Quality Assurance Project Plans, and Standard Operating Procedures for the SWAMP program |
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Line of Evidence (LOE) for Decision ID 78845, Organic Enrichment/Low Dissolved Oxygen
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Region 1 |
Klamath River HU, Shasta River HA |
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LOE ID: |
105074 |
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Pollutant: |
Oxygen, Dissolved |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Total |
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Beneficial Use: |
Cold Freshwater Habitat |
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Number of Samples: |
1 |
Number of Exceedances: |
0 |
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Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP Perennial Stream Surveys data for Klamath River HU, Shasta River HA to determine beneficial use support and results are as follows: 0 of 1 samples exceeded the water quality standard for Oxygen, Dissolved. |
Data Reference: |
Water Quality Assessment Data for the 2018 solicitation cycle submitted through CEDEN for SWAMP Perennial Stream Surveys .
|
|
SWAMP Data: |
SWAMP |
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Water Quality Objective/Criterion: |
Water Quality Control Plan, North Coast Basin, Chapter III, General Objectives for all Inland Surface Waters, Enclosed Bays and Estuaries states: Dissolved oxygen concentrations shall conform to those limits listed in Section 3.3.5. Section 3.3.5 lists dissolved oxygen concentration limits for COLD beneficial use waters to be a daily minimum of 6.0 mg/L and a 7-day moving average of 8.0 mg/L. |
Objective/Criterion Reference: |
Water Quality Control Plan (Basin Plan) for the North Coast Region |
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Evaluation Guideline: |
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Guideline Reference: |
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Spatial Representation: |
The samples were collected at 1 monitoring site(s) (105PS0231) |
Temporal Representation: |
The samples were collected between the dates of 2013-08-29 and 2013-08-29 |
Environmental Conditions: |
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QAPP Information: |
Quality Assurance Program Plan and Standard Operating Procedures for SWAMP program |
QAPP Information Reference(s): |
Quality Assurance Program Plans, Quality Assurance Project Plans, and Standard Operating Procedures for the SWAMP program |
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Line of Evidence (LOE) for Decision ID 78845, Organic Enrichment/Low Dissolved Oxygen
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Region 1 |
Klamath River HU, Shasta River HA |
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LOE ID: |
103376 |
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Pollutant: |
Oxygen, Dissolved |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Total |
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Beneficial Use: |
Cold Freshwater Habitat |
Aquatic Life Use: |
Fish Spawning |
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Number of Samples: |
4 |
Number of Exceedances: |
0 |
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Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP RWB1 Monitoring data for Klamath River HU, Shasta River HA to determine beneficial use support and results are as follows: 1 of 5 samples exceeded the water quality standard for Oxygen, Dissolved. |
Data Reference: |
Water Quality Assessment Data for the 2018 solicitation cycle submitted through CEDEN for SWAMP RWB1 Monitoring .
|
|
SWAMP Data: |
SWAMP |
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Water Quality Objective/Criterion: |
Water Quality Control Plan, North Coast Basin, Chapter III, General Objectives for all Inland Surface Waters, Enclosed Bays and Estuaries states: Dissolved oxygen concentrations shall conform to those limits listed in Section 3.3.5. Section 3.3.5 lists dissolved oxygen concentration limits for SPAWN beneficial use waters to be a daily minimum of 9.0 mg/L and a 7-day moving average of 11.0 mg/L. |
Objective/Criterion Reference: |
Water Quality Control Plan (Basin Plan) for the North Coast Region |
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Evaluation Guideline: |
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Guideline Reference: |
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Spatial Representation: |
The samples were collected at 1 monitoring site(s) (105SH9274) |
Temporal Representation: |
The samples were collected between the dates of 2013-03-07 and 2013-11-20 |
Environmental Conditions: |
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QAPP Information: |
Quality Assurance Program Plan and Standard Operating Procedures for SWAMP program |
QAPP Information Reference(s): |
Quality Assurance Program Plans, Quality Assurance Project Plans, and Standard Operating Procedures for the SWAMP program |
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Line of Evidence (LOE) for Decision ID 78845, Organic Enrichment/Low Dissolved Oxygen
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Region 1 |
Klamath River HU, Shasta River HA |
|
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LOE ID: |
103375 |
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Pollutant: |
Oxygen, Dissolved |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Total |
|
Beneficial Use: |
Cold Freshwater Habitat |
|
Number of Samples: |
1 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP RWB1 Monitoring data for Klamath River HU, Shasta River HA to determine beneficial use support and results are as follows: 0 of 1 samples exceeded the water quality standard for Oxygen, Dissolved. |
Data Reference: |
Water Quality Assessment Data for the 2018 solicitation cycle submitted through CEDEN for SWAMP RWB1 Monitoring .
|
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
Water Quality Control Plan, North Coast Basin, Chapter III, General Objectives for all Inland Surface Waters, Enclosed Bays and Estuaries states: Dissolved oxygen concentrations shall conform to those limits listed in Section 3.3.5. Section 3.3.5 lists dissolved oxygen concentration limits for COLD beneficial use waters to be a daily minimum of 6.0 mg/L and a 7-day moving average of 8.0 mg/L. |
Objective/Criterion Reference: |
Water Quality Control Plan (Basin Plan) for the North Coast Region |
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Evaluation Guideline: |
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Guideline Reference: |
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Spatial Representation: |
The samples were collected at 1 monitoring site(s) (105SH9274) |
Temporal Representation: |
The samples were collected between the dates of 2013-07-30 |
Environmental Conditions: |
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QAPP Information: |
Quality Assurance Program Plan and Standard Operating Procedures for SWAMP program |
QAPP Information Reference(s): |
Quality Assurance Program Plans, Quality Assurance Project Plans, and Standard Operating Procedures for the SWAMP program |
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Line of Evidence (LOE) for Decision ID 78845, Organic Enrichment/Low Dissolved Oxygen
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Region 1 |
Klamath River HU, Shasta River HA |
|
|
LOE ID: |
103372 |
|
Pollutant: |
Oxygen, Dissolved |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Total |
|
Beneficial Use: |
Cold Freshwater Habitat |
|
Number of Samples: |
1 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP RWB1 Monitoring data for Klamath River HU, Shasta River HA to determine beneficial use support and results are as follows: 0 of 5 samples exceeded the water quality standard for Oxygen, Dissolved. |
Data Reference: |
Water Quality Assessment Data for the 2018 solicitation cycle submitted through CEDEN for SWAMP RWB1 Monitoring .
|
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
Water Quality Control Plan, North Coast Basin, Chapter III, General Objectives for all Inland Surface Waters, Enclosed Bays and Estuaries states: Dissolved oxygen concentrations shall conform to those limits listed in Section 3.3.5. Section 3.3.5 lists dissolved oxygen concentration limits for COLD beneficial use waters to be a daily minimum of 6.0 mg/L and a 7-day moving average of 8.0 mg/L. |
Objective/Criterion Reference: |
Water Quality Control Plan (Basin Plan) for the North Coast Region |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
The samples were collected at 1 monitoring site(s) (105SH1452) |
Temporal Representation: |
The samples were collected between the dates of 2013-07-30 |
Environmental Conditions: |
|
QAPP Information: |
Quality Assurance Program Plan and Standard Operating Procedures for SWAMP program |
QAPP Information Reference(s): |
Quality Assurance Program Plans, Quality Assurance Project Plans, and Standard Operating Procedures for the SWAMP program |
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Line of Evidence (LOE) for Decision ID 78845, Organic Enrichment/Low Dissolved Oxygen
|
Region 1 |
Klamath River HU, Shasta River HA |
|
|
LOE ID: |
103373 |
|
Pollutant: |
Oxygen, Dissolved |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Total |
|
Beneficial Use: |
Cold Freshwater Habitat |
Aquatic Life Use: |
Fish Spawning |
|
Number of Samples: |
4 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP RWB1 Monitoring data for Klamath River HU, Shasta River HA to determine beneficial use support and results are as follows: 0 of 4 samples exceeded the water quality standard for Oxygen, Dissolved. |
Data Reference: |
Water Quality Assessment Data for the 2018 solicitation cycle submitted through CEDEN for SWAMP RWB1 Monitoring .
|
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
Water Quality Control Plan, North Coast Basin, Chapter III, General Objectives for all Inland Surface Waters, Enclosed Bays and Estuaries states: Dissolved oxygen concentrations shall conform to those limits listed in Section 3.3.5. Section 3.3.5 lists dissolved oxygen concentration limits for SPAWN beneficial use waters to be a daily minimum of 9.0 mg/L and a 7-day moving average of 11.0 mg/L. |
Objective/Criterion Reference: |
Water Quality Control Plan (Basin Plan) for the North Coast Region |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
The samples were collected at 1 monitoring site(s) (105SH1452) |
Temporal Representation: |
The samples were collected between the dates of 2013-03-06 and 2013-11-20 |
Environmental Conditions: |
|
QAPP Information: |
Quality Assurance Program Plan and Standard Operating Procedures for SWAMP program |
QAPP Information Reference(s): |
Quality Assurance Program Plans, Quality Assurance Project Plans, and Standard Operating Procedures for the SWAMP program |
|
Line of Evidence (LOE) for Decision ID 78845, Organic Enrichment/Low Dissolved Oxygen
|
Region 1 |
Klamath River HU, Shasta River HA |
|
|
LOE ID: |
34081 |
|
Pollutant: |
Oxygen, Dissolved |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Total Dissolved |
|
Beneficial Use: |
Cold Freshwater Habitat |
|
Number of Samples: |
4 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
None of the 4 samples exceeded the objective. |
Data Reference: |
RWB1 Trend Maintenance Periods FYs 2007 2008 |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
Water Quality Control Plan, North Coast Region (NCRWQCB 2011): The minimum dissolved oxygen objective for the mainstem Shasta River is 7.0 mg/L. The 50% lower limit dissolved oxygen objective is 9.0 mg/L. The 50% lower limit represents the 50 percentile values of the monthly means for a calendar year. 50% or more of the monthly means must be greater than or equal to the lower limit. |
Objective/Criterion Reference: |
Water Quality Control Plan (Basin Plan) for the North Coast Region |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
Samples were collected from the Shasta River at Hwy 263 station (105SHA263). |
Temporal Representation: |
Samples were collected approximately once per quarter year from November 2007 to July 2008. |
Environmental Conditions: |
|
QAPP Information: |
SWAMP QAPP |
QAPP Information Reference(s): |
Surface Water Ambient Monitoring Program Quality Assurance Program Plan |
|
Line of Evidence (LOE) for Decision ID 157124, Temperature, water
|
Region 1 |
Klamath River HU, Shasta River HA |
|
|
LOE ID: |
32817 |
|
Pollutant: |
Temperature, water |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
None |
|
Beneficial Use: |
Cold Freshwater Habitat |
|
Number of Samples: |
2 |
Number of Exceedances: |
2 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Two of two annual maximum temperatures in the Shasta River exceeded the evaluation guideline. The annual maximum temperature in 2008 was 25.0 degrees C, and in 2009 was 24.5 degrees C. |
Data Reference: |
Data for Various Pollutants in the Shasta Valley Resource Convservation District, 2008-2009. |
|
SWAMP Data: |
Non-SWAMP |
|
Water Quality Objective/Criterion: |
Water Quality Control Plan, North Coast Region (NCRWQCB 2011): Natural receiving water temperature of intrastate waters shall not be altered unless it can be demonstrated to the satisfaction of the Regional Water Board that such alteration in temperature does not adversely affect beneficial uses. At no time or place shall the temperature of any COLD water be increased more than 5 degrees Fahrenheit (F) above natural receiving water temperature. |
Objective/Criterion Reference: |
Water Quality Control Plan (Basin Plan) for the North Coast Region |
|
Evaluation Guideline: |
According to the Shasta River TMDL, at River Mile (RM) 21.2 an annual maximum water temperature of 17.9 degrees C in the mainstem Shasta River is consistent with the "Water Quality Compliance Scenario", which includes 1) site potential riparian shade conditions on a river-reach scale, 2) modified temperature regime of tailwater return flows such that the return flows do not cause heating of the receiving water, 3) Big Springs Creek temperatures reduced by 4 degrees C from baseline, 4) Parks Creek temperatures reduced by 2 degrees C from baseline, and 5) 50% increase in Shasta River flows downstream of the Big Springs Creek confluence (an increase of 45 cfs). The maximum temperature value for RM 21.2 of the Shasta River is an estimate extrapolated from the Shasta River temperature TMDL model's water quality compliance scenario (Figure 6.3 in the Staff Report for the Action Plan for the Shasta River Watershed Dissolved Oxygen and Temperature TMDLs) (NCRWQCB 2006)." |
Guideline Reference: |
Staff Report for the Action Plan for the Shasta River Watershed Temperature and Dissolved Oxygen Total Maximum Daily Loads |
|
Spatial Representation: |
Continuous data were collected at one location on the Shasta River at site 105SRS01T. |
Temporal Representation: |
Data were collected hourly from April - September 2008 and March - September 2009. |
Environmental Conditions: |
|
QAPP Information: |
Quality Assurance Project Plan for the 'Shasta Water Association Dam Demobilization and Water Quality Improvements Project' Prepared by: Amy Hansen Shasta Valley Resource Conservation District May 21, 2007 Version Number 1.0 |
QAPP Information Reference(s): |
Quality Assurance Project Plan for the Shasta Water Association Dam Demobilization and Water Quality Improvements Project, Version Number 1.0 and for the Araujo Diversion Removal Project, Version Number 1.0. |
|
Line of Evidence (LOE) for Decision ID 157124, Temperature, water
|
Region 1 |
Klamath River HU, Shasta River HA |
|
|
LOE ID: |
31721 |
|
Pollutant: |
Temperature, water |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
None |
|
Beneficial Use: |
Cold Freshwater Habitat |
|
Number of Samples: |
2 |
Number of Exceedances: |
2 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Two of two annual maximum temperatures in the Shasta River exceeded the evaluation guideline. The annual maximum temperature in 2009 at site 105SRS1DO (RM 17.9) was 26.1 degrees C, and at site 105SRS2DO (RM 18.2) was 26.0 degrees C. Annual maximum temperatures at these two sites in 2008 could not be determined, as the data did not include late July/early August when the highest annual temperatures generally occur. |
Data Reference: |
Data for Various Pollutants in the Shasta Valley Resource Convservation District, 2008-2009. |
|
SWAMP Data: |
Non-SWAMP |
|
Water Quality Objective/Criterion: |
Water Quality Control Plan, North Coast Region (NCRWQCB 2011): Natural receiving water temperature of intrastate waters shall not be altered unless it can be demonstrated to the satisfaction of the Regional Water Board that such alteration in temperature does not adversely affect beneficial uses. At no time or place shall the temperature of any COLD water be increased more than 5 degrees Fahrenheit (F) above natural receiving water temperature. |
Objective/Criterion Reference: |
Water Quality Control Plan (Basin Plan) for the North Coast Region |
|
Evaluation Guideline: |
According to the Shasta River TMDL, at River Mile (RM) 17.9 and 18.1 an annual maximum water temperature of 18.2 degrees C in the mainstem Shasta River is consistent with the "Water Quality Compliance Scenario", which includes 1) site potential riparian shade conditions on a river-reach scale, 2) modified temperature regime of tailwater return flows such that the return flows do not cause heating of the receiving water, 3) Big Springs Creek temperatures reduced by 4 degrees C from baseline, 4) Parks Creek temperatures reduced by 2 degrees C from baseline, and 5) 50% increase in Shasta River flows downstream of the Big Springs Creek confluence (an increase of 45 cfs). The maximum temperature value for RM 17.9 & 18.1 of the Shasta River is an estimate extrapolated from the Shasta River temperature TMDL model's water quality compliance scenario (Figure 6.3 in the Staff Report for the Action Plan for the Shasta River Watershed Dissolved Oxygen and Temperature TMDLs) (NCRWQCB 2006)." |
Guideline Reference: |
Staff Report for the Action Plan for the Shasta River Watershed Temperature and Dissolved Oxygen Total Maximum Daily Loads |
|
Spatial Representation: |
Continuous data were collected at two locations on the Shasta River: 1) downstream dam site (105SRS1DO) and 2) upstream dam site (105SRS2DO). |
Temporal Representation: |
Data were collected hourly from March 2009 - September 2009. |
Environmental Conditions: |
|
QAPP Information: |
Quality Assurance Project Plan for the 'Shasta Water Association Dam Demobilization and Water Quality Improvements Project' Prepared by: Amy Hansen Shasta Valley Resource Conservation District May 21, 2007 Version Number 1.0 |
QAPP Information Reference(s): |
Quality Assurance Project Plan for the Shasta Water Association Dam Demobilization and Water Quality Improvements Project, Version Number 1.0 and for the Araujo Diversion Removal Project, Version Number 1.0. |
|
Line of Evidence (LOE) for Decision ID 157124, Temperature, water
|
Region 1 |
Klamath River HU, Shasta River HA |
|
|
LOE ID: |
31698 |
|
Pollutant: |
Temperature, water |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
None |
|
Beneficial Use: |
Cold Freshwater Habitat |
|
Number of Samples: |
6 |
Number of Exceedances: |
6 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Six of six annual maximum temperatures in the Shasta River exceeded the evaluation guideline. The annual maximum temperature in 2008 & 2009 at sites 105SRA1DO (RM 13.6), site 105SRA2DO (RM 13.6), and site 105SRA3DO (RM 13.5) ranged from 27.1 to 28.7 degrees C. |
Data Reference: |
Data for Various Pollutants in the Shasta Valley Resource Convservation District, 2008-2009. |
|
SWAMP Data: |
Non-SWAMP |
|
Water Quality Objective/Criterion: |
Water Quality Control Plan, North Coast Region (NCRWQCB 2011): Natural receiving water temperature of intrastate waters shall not be altered unless it can be demonstrated to the satisfaction of the Regional Water Board that such alteration in temperature does not adversely affect beneficial uses. At no time or place shall the temperature of any COLD water be increased more than 5 degrees Fahrenheit (F) above natural receiving water temperature. |
Objective/Criterion Reference: |
Water Quality Control Plan (Basin Plan) for the North Coast Region |
|
Evaluation Guideline: |
According to the Shasta River TMDL, at River Mile (RM) 13.6 and 13.5 an annual maximum water temperature of 17.9 degrees C in the mainstem Shasta River is consistent with the "Water Quality Compliance Scenario", which includes 1) site potential riparian shade conditions on a river-reach scale, 2) modified temperature regime of tailwater return flows such that the return flows do not cause heating of the receiving water, 3) Big Springs Creek temperatures reduced by 4 degrees C from baseline, 4) Parks Creek temperatures reduced by 2 degrees C from baseline, and 5) 50% increase in Shasta River flows downstream of the Big Springs Creek confluence (an increase of 45 cfs). The maximum temperature value for RM 13.6 & 13.5 of the Shasta River is an estimate extrapolated from the Shasta River temperature TMDL model's water quality compliance scenario (Figure 6.3 in the Staff Report for the Action Plan for the Shasta River Watershed Dissolved Oxygen and Temperature TMDLs) (NCRWQCB 2006)." |
Guideline Reference: |
Staff Report for the Action Plan for the Shasta River Watershed Temperature and Dissolved Oxygen Total Maximum Daily Loads |
|
Spatial Representation: |
Continuous data were collected at three locations on the Shasta River: 1) downstream dam site (105SRA1DO) , 2) upstream dam site (105SRA2DO), and upstream pump/screen (105SRA3DO). |
Temporal Representation: |
Data were collected hourly from March - September in 2008 & 2009. |
Environmental Conditions: |
|
QAPP Information: |
Quality Assurance Project Plan for the 'Araujo Diversion Removal Project' Prepared by: Amy Hansen Shasta Valley Resource Conservation District July 30, 2007. |
QAPP Information Reference(s): |
Quality Assurance Project Plan for the Shasta Water Association Dam Demobilization and Water Quality Improvements Project, Version Number 1.0 and for the Araujo Diversion Removal Project, Version Number 1.0. |
|
Line of Evidence (LOE) for Decision ID 157124, Temperature, water
|
Region 1 |
Klamath River HU, Shasta River HA |
|
|
LOE ID: |
43251 |
|
Pollutant: |
Temperature, water |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
None |
|
Beneficial Use: |
Cold Freshwater Habitat |
|
Number of Samples: |
2 |
Number of Exceedances: |
1 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP data for Klamath River HU, Shasta River HA to determine beneficial use support and results are as follows: 1 of 2 annual maximum temperatures in the Shasta River at Highway 263 exceed the evaluation guideline for Water Temperature. A total of 4 grab samples were collected and annual maximum temperatures were calculated for each calendar year. |
Data Reference: |
RWB1 Trend Maintenance Periods FYs 2007 2008 |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
Water Quality Control Plan, North Coast Region (NCRWQCB 2011): Natural receiving water temperature of intrastate waters shall not be altered unless it can be demonstrated to the satisfaction of the Regional Water Board that such alteration in temperature does not adversely affect beneficial uses. At no time or place shall the temperature of any COLD water be increased more than 5 degrees Fahrenheit (F) above natural receiving water temperature. |
Objective/Criterion Reference: |
Water Quality Control Plan (Basin Plan) for the North Coast Region |
|
Evaluation Guideline: |
According to the Shasta River TMDL, at River Mile (RM) 7.3 (Shasta River at Highway 263) an annual maximum water temperature of 18.8 degrees C in the mainstem Shasta River is consistent with the "Water Quality Compliance Scenario", which includes 1) site potential riparian shade conditions on a river-reach scale, 2) modified temperature regime of tailwater return flows such that the return flows do not cause heating of the receiving water, 3) Big Springs Creek temperatures reduced by 4 degrees C from baseline, 4) Parks Creek temperatures reduced by 2 degrees C from baseline, and 5) 50% increase in Shasta River flows downstream of the Big Springs Creek confluence (an increase of 45 cfs). The maximum temperature value for RM 7.3 of the Shasta River is an estimate extrapolated from the Shasta River temperature TMDL model's water quality compliance scenario (Figure 6.3 in the Staff Report for the Action Plan for the Shasta River Watershed Dissolved Oxygen and Temperature TMDLs) (NCRWQCB 2006)." |
Guideline Reference: |
Staff Report for the Action Plan for the Shasta River Watershed Temperature and Dissolved Oxygen Total Maximum Daily Loads |
|
Spatial Representation: |
Data for this line of evidence for Klamath River HU, Shasta River HA was collected at 1 monitoring site [ Shasta River at Hwy 263 - 105SHA263] |
Temporal Representation: |
Data was collected over the time period 11/15/2007-7/16/2008. |
Environmental Conditions: |
Staff is not aware of any special conditions that might affect interpretation of the data. |
QAPP Information: |
The SWAMP QAPP (2008) was followed. |
QAPP Information Reference(s): |
Surface Water Ambient Monitoring Program Quality Assurance Program Plan |
|
Line of Evidence (LOE) for Decision ID 157124, Temperature, water
|
Region 1 |
Klamath River HU, Shasta River HA |
|
|
LOE ID: |
32858 |
|
Pollutant: |
Temperature, water |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
None |
|
Beneficial Use: |
Cold Freshwater Habitat |
|
Number of Samples: |
1 |
Number of Exceedances: |
1 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
One of one annual maximum temperature in the Shasta River exceeded the evaluation guideline. The annual maximum temperature in 2008 was 28.2 degrees C. The annual maximum temperature in 2009 at this site could not be determined, as the data did not include late July/early August when the highest annual temperatures generally occur. |
Data Reference: |
Data for Various Pollutants in the Shasta Valley Resource Convservation District, 2008-2009. |
|
SWAMP Data: |
Non-SWAMP |
|
Water Quality Objective/Criterion: |
Water Quality Control Plan, North Coast Region (NCRWQCB 2011): Natural receiving water temperature of intrastate waters shall not be altered unless it can be demonstrated to the satisfaction of the Regional Water Board that such alteration in temperature does not adversely affect beneficial uses. At no time or place shall the temperature of any COLD water be increased more than 5 degrees Fahrenheit (F) above natural receiving water temperature. |
Objective/Criterion Reference: |
Water Quality Control Plan (Basin Plan) for the North Coast Region |
|
Evaluation Guideline: |
According to the Shasta River TMDL, at River Mile (RM) 10.9 an annual maximum water temperature of 17.3 degrees C in the mainstem Shasta River is consistent with the "Water Quality Compliance Scenario", which includes 1) site potential riparian shade conditions on a river-reach scale, 2) modified temperature regime of tailwater return flows such that the return flows do not cause heating of the receiving water, 3) Big Springs Creek temperatures reduced by 4 degrees C from baseline, 4) Parks Creek temperatures reduced by 2 degrees C from baseline, and 5) 50% increase in Shasta River flows downstream of the Big Springs Creek confluence (an increase of 45 cfs). The maximum temperature value for RM 10.9 of the Shasta River is an estimate extrapolated from the Shasta River temperature TMDL model's water quality compliance scenario (Figure 6.3 in the Staff Report for the Action Plan for the Shasta River Watershed Dissolved Oxygen and Temperature TMDLs) (NCRWQCB 2006)." |
Guideline Reference: |
Staff Report for the Action Plan for the Shasta River Watershed Temperature and Dissolved Oxygen Total Maximum Daily Loads |
|
Spatial Representation: |
Continuous data were collected at one location on the Shasta River at site 105SRA01T. |
Temporal Representation: |
Data were collected hourly from April - September 2008. |
Environmental Conditions: |
|
QAPP Information: |
Quality Assurance Project Plan for the 'Araujo Diversion Removal Project' Prepared by: Amy Hansen Shasta Valley Resource Conservation District July 30, 2007. |
QAPP Information Reference(s): |
Quality Assurance Project Plan for the Shasta Water Association Dam Demobilization and Water Quality Improvements Project, Version Number 1.0 and for the Araujo Diversion Removal Project, Version Number 1.0. |
|
Line of Evidence (LOE) for Decision ID 157124, Temperature, water
|
Region 1 |
Klamath River HU, Shasta River HA |
|
|
LOE ID: |
32815 |
|
Pollutant: |
Temperature, water |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
None |
|
Beneficial Use: |
Cold Freshwater Habitat |
|
Number of Samples: |
2 |
Number of Exceedances: |
2 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Two of two annual maximum temperatures in the Shasta River exceeded the evaluation guideline. The annual maximum temperature in 2008 was 25.1 degrees C, and in 2009 was 26.0 degrees C. |
Data Reference: |
Data for Various Pollutants in the Shasta Valley Resource Convservation District, 2008-2009. |
|
SWAMP Data: |
Non-SWAMP |
|
Water Quality Objective/Criterion: |
Water Quality Control Plan, North Coast Region (NCRWQCB 2011): Natural receiving water temperature of intrastate waters shall not be altered unless it can be demonstrated to the satisfaction of the Regional Water Board that such alteration in temperature does not adversely affect beneficial uses. At no time or place shall the temperature of any COLD water be increased more than 5 degrees Fahrenheit (F) above natural receiving water temperature. |
Objective/Criterion Reference: |
Water Quality Control Plan (Basin Plan) for the North Coast Region |
|
Evaluation Guideline: |
According to the Shasta River TMDL, at River Mile (RM) 18.4 an annual maximum water temperature of 18.3 degrees C in the mainstem Shasta River is consistent with the "Water Quality Compliance Scenario", which includes 1) site potential riparian shade conditions on a river-reach scale, 2) modified temperature regime of tailwater return flows such that the return flows do not cause heating of the receiving water, 3) Big Springs Creek temperatures reduced by 4 degrees C from baseline, 4) Parks Creek temperatures reduced by 2 degrees C from baseline, and 5) 50% increase in Shasta River flows downstream of the Big Springs Creek confluence (an increase of 45 cfs). The maximum temperature value for RM 18.4 of the Shasta River is an estimate extrapolated from the Shasta River temperature TMDL model's water quality compliance scenario (Figure 6.3 in the Staff Report for the Action Plan for the Shasta River Watershed Dissolved Oxygen and Temperature TMDLs) (NCRWQCB 2006)." |
Guideline Reference: |
Staff Report for the Action Plan for the Shasta River Watershed Temperature and Dissolved Oxygen Total Maximum Daily Loads |
|
Spatial Representation: |
Continuous data were collected at one location on the Shasta River at site 105SRS3DO. |
Temporal Representation: |
Data were collected hourly from March - September in 2008 and 2009. |
Environmental Conditions: |
|
QAPP Information: |
Quality Assurance Project Plan for the 'Shasta Water Association Dam Demobilization and Water Quality Improvements Project' Prepared by: Amy Hansen Shasta Valley Resource Conservation District May 21, 2007 Version Number 1.0 |
QAPP Information Reference(s): |
Quality Assurance Project Plan for the Shasta Water Association Dam Demobilization and Water Quality Improvements Project, Version Number 1.0 and for the Araujo Diversion Removal Project, Version Number 1.0. |
|
Line of Evidence (LOE) for Decision ID 157124, Temperature, water
|
Region 1 |
Klamath River HU, Shasta River HA |
|
|
LOE ID: |
32838 |
|
Pollutant: |
Temperature, water |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
None |
|
Beneficial Use: |
Cold Freshwater Habitat |
|
Number of Samples: |
2 |
Number of Exceedances: |
2 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Two of two annual maximum temperature in the Shasta River exceeded the evaluation guideline. The annual maximum temperature in 2008 was 27.5 degrees C and in 2009 was 28.7 degrees C. |
Data Reference: |
Data for Various Pollutants in the Shasta Valley Resource Convservation District, 2008-2009. |
|
SWAMP Data: |
Non-SWAMP |
|
Water Quality Objective/Criterion: |
Water Quality Control Plan, North Coast Region (NCRWQCB 2011): Natural receiving water temperature of intrastate waters shall not be altered unless it can be demonstrated to the satisfaction of the Regional Water Board that such alteration in temperature does not adversely affect beneficial uses. At no time or place shall the temperature of any COLD water be increased more than 5 degrees Fahrenheit (F) above natural receiving water temperature. |
Objective/Criterion Reference: |
Water Quality Control Plan (Basin Plan) for the North Coast Region |
|
Evaluation Guideline: |
According to the Shasta River TMDL, at River Mile (RM) 13.2 an annual maximum water temperature of 17.6 degrees C in the mainstem Shasta River is consistent with the "Water Quality Compliance Scenario", which includes 1) site potential riparian shade conditions on a river-reach scale, 2) modified temperature regime of tailwater return flows such that the return flows do not cause heating of the receiving water, 3) Big Springs Creek temperatures reduced by 4 degrees C from baseline, 4) Parks Creek temperatures reduced by 2 degrees C from baseline, and 5) 50% increase in Shasta River flows downstream of the Big Springs Creek confluence (an increase of 45 cfs). The maximum temperature value for RM 13.2 of the Shasta River is an estimate extrapolated from the Shasta River temperature TMDL model's water quality compliance scenario (Figure 6.3 in the Staff Report for the Action Plan for the Shasta River Watershed Dissolved Oxygen and Temperature TMDLs) (NCRWQCB 2006)." |
Guideline Reference: |
Staff Report for the Action Plan for the Shasta River Watershed Temperature and Dissolved Oxygen Total Maximum Daily Loads |
|
Spatial Representation: |
Continuous data were collected at one location on the Shasta River at site 105SRA4DO. |
Temporal Representation: |
Data were collected hourly from March - September 2008 & 2009. |
Environmental Conditions: |
|
QAPP Information: |
Quality Assurance Project Plan for the 'Araujo Diversion Removal Project' Prepared by: Amy Hansen Shasta Valley Resource Conservation District July 30, 2007. |
QAPP Information Reference(s): |
Quality Assurance Project Plan for the Shasta Water Association Dam Demobilization and Water Quality Improvements Project, Version Number 1.0 and for the Araujo Diversion Removal Project, Version Number 1.0. |
|
Line of Evidence (LOE) for Decision ID 157124, Temperature, water
|
Region 1 |
Klamath River HU, Shasta River HA |
|
|
LOE ID: |
31510 |
|
Pollutant: |
Temperature, water |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Total |
|
Beneficial Use: |
Cold Freshwater Habitat |
|
Number of Samples: |
0 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
Not Specified |
Data Used to Assess Water Quality: |
The following process is utilized to interpret the narrative Temperature Objective in the Basin Plan for impairment assessments. Step 1: determine if temperatures reflect natural conditions. If Yes, then the water body is not considered impaired, if No, Then go to Step 2. Step 2: Determine if temperatures adversely affect beneficial uses. If Yes, then the water body is considered impaired, if No, then go to Step 3. Step 3: Determine if temperatures are increased by 5 degrees F. If Yes, then water body is impaired, if No, then water body is not impaired. |
Data Reference: |
Presentation: Interpreting Temperature Standards in the North Coast Region. North Coast Regional Water Quality Control Board. |
|
SWAMP Data: |
Non-SWAMP |
|
Water Quality Objective/Criterion: |
Water Quality Control Plan, North Coast Region (NCRWQCB 2011): Natural receiving water temperature of intrastate waters shall not be altered unless it can be demonstrated to the satisfaction of the Regional Water Board that such alteration in temperature does not adversely affect beneficial uses. At no time or place shall the temperature of any COLD water be increased more than 5 degrees Fahrenheit (F) above natural receiving water temperature. |
Objective/Criterion Reference: |
Water Quality Control Plan (Basin Plan) for the North Coast Region |
|
Evaluation Guideline: |
EVIDENCE OF ALTERATION OF NATURAL RECEIVING WATER TEMPERATURES (NON-NATURAL TEMPS): Water temperatures of the Shasta River HA do not reflect natural conditions as environmental factors that influence water temperature have been altered by human activities as discussed in the Staff Report For the Action Plan for the Shasta River Watershed Temperature and Dissolved Oxygen TMDLs (NCRWQCB 2006). EVIDENCE OF SALMONID PRESENCE & LIFE CYCLE USE: Chinook, coho and steelhead are present in the watershed below Shastina and trout are present in Shastina and tributaries to Shastina (NCRWQCB 2006; Whelan 2005). Rearing occurs year-round and spawning, incubation, and emergence occurs from September 16th to June 30 (NCRWQCB 2006). Non-core rearing occurs in the mainstem Shasta River year-round, and core rearing occurs in the tributaries to the Shasta River. |
Guideline Reference: |
Staff Report for the Action Plan for the Shasta River Watershed Temperature and Dissolved Oxygen Total Maximum Daily Loads |
Guideline Reference: |
Email correspondence between Jim Whelan (DFG) and North Coast Regional Water Board staff regarding fisheries in Lake Shastina |
|
Spatial Representation: |
Information pertains to Klamath River HU, Shasta River HA. |
Temporal Representation: |
Data are reflective of current conditions in this water body. |
Environmental Conditions: |
|
QAPP Information: |
Information is considered to be of adequate quality for the Integrated Report. |
QAPP Information Reference(s): |
|
Line of Evidence (LOE) for Decision ID 157124, Temperature, water
|
Region 1 |
Klamath River HU, Shasta River HA |
|
|
LOE ID: |
326958 |
|
Pollutant: |
Temperature, water |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
None |
|
Beneficial Use: |
Cold Freshwater Habitat |
|
Number of Samples: |
1 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP Reference Condition Management Plan data for Klamath River HU, Shasta River HA to determine beneficial use support and results are as follows: 0 of 1 samples exceeded the water quality threshold for Temperature. |
Data Reference: |
Benthic, Field, Habitat, WQ from the Surface Water Ambient Monitoring Program for the 2026 Integrated Report in Region 1 |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
Natural receiving water temperature of intrastate waters shall not be altered unless it can be demonstrated to the satisfaction of the Regional Water Board that such alteration in temperature does not adversely affect beneficial uses. At no time or place shall the temperature of any COLD water be increased more than 5 degrees Fahrenheit (F) above natural receiving water temperature (Basin Plan, North Coast Region). |
Objective/Criterion Reference: |
Water Quality Control Plan (Basin Plan) for the North Coast Region |
|
Evaluation Guideline: |
According to Carter (2008) the lethal temperature evaluation guideline for salmonid spawning, egg incubation & fry emergence is 20C. |
Guideline Reference: |
Effects of Temperature, Dissolved Oxygen/Total Dissolved Gas, Ammonia, and pH on Salmonids. Implications for California's North Coast TMDLs. California Regional Water Quality Control Board, North Coast Region |
|
Spatial Representation: |
The samples were collected at 1 monitoring site: 105WE0592 (Eddy Creek ~0.8 miles downstream from end of 4WD road.). |
Temporal Representation: |
The samples were collected between the dates of 2015-07-13 and 2015-07-13 |
Environmental Conditions: |
|
QAPP Information: |
QAPP for Surface Water Ambient Monitoring Program (SWAMP) |
QAPP Information Reference(s): |
Generic SWAMP QAPrP |
|
Line of Evidence (LOE) for Decision ID 157124, Temperature, water
|
Region 1 |
Klamath River HU, Shasta River HA |
|
|
LOE ID: |
326936 |
|
Pollutant: |
Temperature, water |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
None |
|
Beneficial Use: |
Cold Freshwater Habitat |
|
Number of Samples: |
25 |
Number of Exceedances: |
2 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP RWB1 Monitoring data for Klamath River HU, Shasta River HA to determine beneficial use support and results are as follows: 2 of 25 samples exceeded the water quality threshold for Temperature. |
Data Reference: |
Benthic, Field, Habitat, Tissue, Toxicity, WQ from the Surface Water Ambient Monitoring Program for the 2026 Integrated Report in Region 1 |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
Natural receiving water temperature of intrastate waters shall not be altered unless it can be demonstrated to the satisfaction of the Regional Water Board that such alteration in temperature does not adversely affect beneficial uses. At no time or place shall the temperature of any COLD water be increased more than 5 degrees Fahrenheit (F) above natural receiving water temperature (Basin Plan, North Coast Region). |
Objective/Criterion Reference: |
Water Quality Control Plan (Basin Plan) for the North Coast Region |
|
Evaluation Guideline: |
According to Carter (2008) the lethal temperature evaluation guideline for salmonid spawning, egg incubation & fry emergence is 20C. |
Guideline Reference: |
Effects of Temperature, Dissolved Oxygen/Total Dissolved Gas, Ammonia, and pH on Salmonids. Implications for California's North Coast TMDLs. California Regional Water Quality Control Board, North Coast Region |
|
Spatial Representation: |
The samples were collected at 1 monitoring site: 105PO0001 (Parks Creek Overflow at Big Springs Road Crossing). |
Temporal Representation: |
The samples were collected between the dates of 2021-04-08 and 2021-10-28 |
Environmental Conditions: |
|
QAPP Information: |
QAPP for Surface Water Ambient Monitoring Program (SWAMP) |
QAPP Information Reference(s): |
Generic SWAMP QAPrP |
|
Line of Evidence (LOE) for Decision ID 157124, Temperature, water
|
Region 1 |
Klamath River HU, Shasta River HA |
|
|
LOE ID: |
43240 |
|
Pollutant: |
Temperature, water |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
None |
|
Beneficial Use: |
Cold Freshwater Habitat |
|
Number of Samples: |
2 |
Number of Exceedances: |
1 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP data for Klamath River HU, Shasta River HA to determine beneficial use support and results are as follows: 1 of 2 annual maximum temperatures in the Shasta River near Edgewood exceed the evaluation guideline for Water Temperature. A total of 4 grab samples were collected and annual maximum temperatures were calculated for each calendar year. |
Data Reference: |
RWB1 Trend Maintenance Periods FYs 2007 2008 |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
Water Quality Control Plan, North Coast Region (NCRWQCB 2011): Natural receiving water temperature of intrastate waters shall not be altered unless it can be demonstrated to the satisfaction of the Regional Water Board that such alteration in temperature does not adversely affect beneficial uses. At no time or place shall the temperature of any COLD water be increased more than 5 degrees Fahrenheit (F) above natural receiving water temperature. |
Objective/Criterion Reference: |
Water Quality Control Plan (Basin Plan) for the North Coast Region |
|
Evaluation Guideline: |
Per "Effects of Temperature, Dissolved Oxygen/Total Dissolved Gas, Ammonia, and pH on Salmonids" (Carter 2008): The lethal temperature evaluation guideline for both steelhead adult migration & holding and juvenile growth & rearing of 24°C applies in the Shasta River above Lake Shastina July - September 15th. The lethal temperature evaluation guideline for salmonid spawning, egg incubation & fry emergence is 20C and applies September 16th - June. See LOE ID 31510 for more information on natural temperature alterations and salmonid presence and periodicity in this water body. |
Guideline Reference: |
Effects of Temperature, Dissolved Oxygen/Total Dissolved Gas, Ammonia, and pH on Salmonids. Implications for California's North Coast TMDLs. California Regional Water Quality Control Board, North Coast Region |
|
Spatial Representation: |
Data for this line of evidence for Klamath River HU, Shasta River HA was collected at 1 monitoring site [ Shasta River near Edgewood - 105SHAEDG] |
Temporal Representation: |
Data was collected over the time period 11/15/2007-7/16/2008. |
Environmental Conditions: |
Staff is not aware of any special conditions that might affect interpretation of the data. |
QAPP Information: |
The SWAMP QAPP (2008) was followed. |
QAPP Information Reference(s): |
Surface Water Ambient Monitoring Program Quality Assurance Program Plan |
|
Line of Evidence (LOE) for Decision ID 157124, Temperature, water
|
Region 1 |
Klamath River HU, Shasta River HA |
|
|
LOE ID: |
32839 |
|
Pollutant: |
Temperature, water |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
None |
|
Beneficial Use: |
Cold Freshwater Habitat |
|
Number of Samples: |
2 |
Number of Exceedances: |
2 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Two of two annual maximum temperature in the Shasta River exceeded the evaluation guideline. The annual maximum temperature in 2008 was 28.8 degrees C and in 2009 was 29.6 degrees C. |
Data Reference: |
Data for Various Pollutants in the Shasta Valley Resource Convservation District, 2008-2009. |
|
SWAMP Data: |
Non-SWAMP |
|
Water Quality Objective/Criterion: |
Water Quality Control Plan, North Coast Region (NCRWQCB 2011): Natural receiving water temperature of intrastate waters shall not be altered unless it can be demonstrated to the satisfaction of the Regional Water Board that such alteration in temperature does not adversely affect beneficial uses. At no time or place shall the temperature of any COLD water be increased more than 5 degrees Fahrenheit (F) above natural receiving water temperature. |
Objective/Criterion Reference: |
Water Quality Control Plan (Basin Plan) for the North Coast Region |
|
Evaluation Guideline: |
According to the Shasta River TMDL, at River Mile (RM) 11.9 an annual maximum water temperature of 17.4 degrees C in the mainstem Shasta River is consistent with the "Water Quality Compliance Scenario", which includes 1) site potential riparian shade conditions on a river-reach scale, 2) modified temperature regime of tailwater return flows such that the return flows do not cause heating of the receiving water, 3) Big Springs Creek temperatures reduced by 4 degrees C from baseline, 4) Parks Creek temperatures reduced by 2 degrees C from baseline, and 5) 50% increase in Shasta River flows downstream of the Big Springs Creek confluence (an increase of 45 cfs). The maximum temperature value for RM 11.9 of the Shasta River is an estimate extrapolated from the Shasta River temperature TMDL model's water quality compliance scenario (Figure 6.3 in the Staff Report for the Action Plan for the Shasta River Watershed Dissolved Oxygen and Temperature TMDLs) (NCRWQCB 2006)." |
Guideline Reference: |
Staff Report for the Action Plan for the Shasta River Watershed Temperature and Dissolved Oxygen Total Maximum Daily Loads |
|
Spatial Representation: |
Continuous data were collected at one location on the Shasta River at site 105SRA02T. |
Temporal Representation: |
Data were collected hourly from April - September in 2008 & March - September in 2009. |
Environmental Conditions: |
|
QAPP Information: |
Quality Assurance Project Plan for the 'Araujo Diversion Removal Project' Prepared by: Amy Hansen Shasta Valley Resource Conservation District July 30, 2007. |
QAPP Information Reference(s): |
Quality Assurance Project Plan for the Shasta Water Association Dam Demobilization and Water Quality Improvements Project, Version Number 1.0 and for the Araujo Diversion Removal Project, Version Number 1.0. |
|
Line of Evidence (LOE) for Decision ID 157124, Temperature, water
|
Region 1 |
Klamath River HU, Shasta River HA |
|
|
LOE ID: |
32837 |
|
Pollutant: |
Temperature, water |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
None |
|
Beneficial Use: |
Cold Freshwater Habitat |
|
Number of Samples: |
2 |
Number of Exceedances: |
2 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Two of two annual maximum temperatures in the Shasta River exceeded the evaluation guideline. The annual maximum temperature in 2008 was 25.2 degrees C, and in 2009 was 25.5 degrees C. |
Data Reference: |
Data for Various Pollutants in the Shasta Valley Resource Convservation District, 2008-2009. |
|
SWAMP Data: |
Non-SWAMP |
|
Water Quality Objective/Criterion: |
Water Quality Control Plan, North Coast Region (NCRWQCB 2011): Natural receiving water temperature of intrastate waters shall not be altered unless it can be demonstrated to the satisfaction of the Regional Water Board that such alteration in temperature does not adversely affect beneficial uses. At no time or place shall the temperature of any COLD water be increased more than 5 degrees Fahrenheit (F) above natural receiving water temperature. |
Objective/Criterion Reference: |
Water Quality Control Plan (Basin Plan) for the North Coast Region |
|
Evaluation Guideline: |
According to the Shasta River TMDL, at River Mile (RM) 23.6 an annual maximum water temperature of 17.7 degrees C in the mainstem Shasta River is consistent with the "Water Quality Compliance Scenario", which includes 1) site potential riparian shade conditions on a river-reach scale, 2) modified temperature regime of tailwater return flows such that the return flows do not cause heating of the receiving water, 3) Big Springs Creek temperatures reduced by 4 degrees C from baseline, 4) Parks Creek temperatures reduced by 2 degrees C from baseline, and 5) 50% increase in Shasta River flows downstream of the Big Springs Creek confluence (an increase of 45 cfs). The maximum temperature value for RM 23.2 of the Shasta River is an estimate extrapolated from the Shasta River temperature TMDL model's water quality compliance scenario (Figure 6.3 in the Staff Report for the Action Plan for the Shasta River Watershed Dissolved Oxygen and Temperature TMDLs) (NCRWQCB 2006)." |
Guideline Reference: |
Staff Report for the Action Plan for the Shasta River Watershed Temperature and Dissolved Oxygen Total Maximum Daily Loads |
|
Spatial Representation: |
Continuous data were collected at one location on the Shasta River at site 105SRS02T. |
Temporal Representation: |
Data were collected hourly from April - September 2008 and March - September 2009. |
Environmental Conditions: |
|
QAPP Information: |
Quality Assurance Project Plan for the 'Shasta Water Association Dam Demobilization and Water Quality Improvements Project' Prepared by: Amy Hansen Shasta Valley Resource Conservation District May 21, 2007 Version Number 1.0 |
QAPP Information Reference(s): |
Quality Assurance Project Plan for the Shasta Water Association Dam Demobilization and Water Quality Improvements Project, Version Number 1.0 and for the Araujo Diversion Removal Project, Version Number 1.0. |
|
Line of Evidence (LOE) for Decision ID 157124, Temperature, water
|
Region 1 |
Klamath River HU, Shasta River HA |
|
|
LOE ID: |
32816 |
|
Pollutant: |
Temperature, water |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
None |
|
Beneficial Use: |
Cold Freshwater Habitat |
|
Number of Samples: |
1 |
Number of Exceedances: |
1 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
One of one annual maximum temperature in the Shasta River exceeded the evaluation guideline. The annual maximum temperature in 2009 was 25.6 degrees C. The annual maximum temperature in 2008 at this site could not be determined, as the data did not include late July/early August when the highest annual temperatures generally occur. |
Data Reference: |
Data for Various Pollutants in the Shasta Valley Resource Convservation District, 2008-2009. |
|
SWAMP Data: |
Non-SWAMP |
|
Water Quality Objective/Criterion: |
Water Quality Control Plan, North Coast Region (NCRWQCB 2011): Natural receiving water temperature of intrastate waters shall not be altered unless it can be demonstrated to the satisfaction of the Regional Water Board that such alteration in temperature does not adversely affect beneficial uses. At no time or place shall the temperature of any COLD water be increased more than 5 degrees Fahrenheit (F) above natural receiving water temperature. |
Objective/Criterion Reference: |
Water Quality Control Plan (Basin Plan) for the North Coast Region |
|
Evaluation Guideline: |
According to the Shasta River TMDL, at River Mile (RM) 18.7 an annual maximum water temperature of 18.4 degrees C in the mainstem Shasta River is consistent with the "Water Quality Compliance Scenario", which includes 1) site potential riparian shade conditions on a river-reach scale, 2) modified temperature regime of tailwater return flows such that the return flows do not cause heating of the receiving water, 3) Big Springs Creek temperatures reduced by 4 degrees C from baseline, 4) Parks Creek temperatures reduced by 2 degrees C from baseline, and 5) 50% increase in Shasta River flows downstream of the Big Springs Creek confluence (an increase of 45 cfs). The maximum temperature value for RM 18.7 of the Shasta River is an estimate extrapolated from the Shasta River temperature TMDL model's water quality compliance scenario (Figure 6.3 in the Staff Report for the Action Plan for the Shasta River Watershed Dissolved Oxygen and Temperature TMDLs) (NCRWQCB 2006)." |
Guideline Reference: |
Staff Report for the Action Plan for the Shasta River Watershed Temperature and Dissolved Oxygen Total Maximum Daily Loads |
|
Spatial Representation: |
Continuous data were collected at one location on the Shasta River at site 105SRS4DO. |
Temporal Representation: |
Data were collected hourly from March - September 2009. |
Environmental Conditions: |
|
QAPP Information: |
Quality Assurance Project Plan for the 'Shasta Water Association Dam Demobilization and Water Quality Improvements Project' Prepared by: Amy Hansen Shasta Valley Resource Conservation District May 21, 2007 Version Number 1.0 |
QAPP Information Reference(s): |
Quality Assurance Project Plan for the Shasta Water Association Dam Demobilization and Water Quality Improvements Project, Version Number 1.0 and for the Araujo Diversion Removal Project, Version Number 1.0. |
|
Line of Evidence (LOE) for Decision ID 157124, Temperature, water
|
Region 1 |
Klamath River HU, Shasta River HA |
|
|
LOE ID: |
1657 |
|
Pollutant: |
Temperature, water |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
None |
|
Beneficial Use: |
Cold Freshwater Habitat |
|
Number of Samples: |
0 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
Not Specified |
Data Used to Assess Water Quality: |
Unspecified--This LOE is a placeholder to support a 303(d) listing decision made prior to 2006. |
Data Reference: |
Placeholder reference 2006 303(d) |
|
SWAMP Data: |
Non-SWAMP |
|
Water Quality Objective/Criterion: |
|
Objective/Criterion Reference: |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
|
Temporal Representation: |
|
Environmental Conditions: |
|
QAPP Information: |
QA Info Missing |
QAPP Information Reference(s): |
|
Line of Evidence (LOE) for Decision ID 157124, Temperature, water
|
Region 1 |
Klamath River HU, Shasta River HA |
|
|
LOE ID: |
43971 |
|
Pollutant: |
Temperature, water |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
None |
|
Beneficial Use: |
Cold Freshwater Habitat |
|
Number of Samples: |
1 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP data for Klamath River HU, Shasta River HA to determine beneficial use support and results are as follows: 0 of 1 samples exceed the criterion for Water Temperature. |
Data Reference: |
Statewide Perennial Streams Assessment 2008 |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
Water Quality Control Plan, North Coast Region (NCRWQCB 2011): Natural receiving water temperature of intrastate waters shall not be altered unless it can be demonstrated to the satisfaction of the Regional Water Board that such alteration in temperature does not adversely affect beneficial uses. At no time or place shall the temperature of any COLD water be increased more than 5 degrees Fahrenheit (F) above natural receiving water temperature. |
Objective/Criterion Reference: |
Water Quality Control Plan (Basin Plan) for the North Coast Region |
|
Evaluation Guideline: |
Per "Effects of Temperature, Dissolved Oxygen/Total Dissolved Gas, Ammonia, and pH on Salmonids" (Carter 2008): The lethal temperature evaluation guideline for both steelhead adult migration & holding and juvenile growth & rearing of 24°C applies in the Shasta River above Lake Shastina July - September 15th. The lethal temperature evaluation guideline for salmonid spawning, egg incubation & fry emergence is 20C and applies September 16th - June. See LOE ID 31510 for more information on natural temperature alterations and salmonid presence and periodicity in this water body. |
Guideline Reference: |
Effects of Temperature, Dissolved Oxygen/Total Dissolved Gas, Ammonia, and pH on Salmonids. Implications for California's North Coast TMDLs. California Regional Water Quality Control Board, North Coast Region |
|
Spatial Representation: |
Data for this line of evidence for Klamath River HU, Shasta River HA was collected at 1 monitoring site [ Evans Ditch - 105PS0188 ] |
Temporal Representation: |
Data was collected on a single day 8/26/2008. |
Environmental Conditions: |
Staff is not aware of any special conditions that might affect interpretation of the data. |
QAPP Information: |
The SWAMP QAPP (2008) was followed. |
QAPP Information Reference(s): |
Surface Water Ambient Monitoring Program Quality Assurance Program Plan |
|
Line of Evidence (LOE) for Decision ID 157124, Temperature, water
|
Region 1 |
Klamath River HU, Shasta River HA |
|
|
LOE ID: |
329256 |
|
Pollutant: |
Temperature, water |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
None |
|
Beneficial Use: |
Cold Freshwater Habitat |
|
Number of Samples: |
25 |
Number of Exceedances: |
11 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed Karuk Tribe (Tribal) data for Klamath River HU, Shasta River HA to determine beneficial use support and results are as follows: 11 of 25 samples exceeded the water quality threshold for Temperature. |
Data Reference: |
WQX from the NWQMP for the 2026 Integrated Report in Region 1 |
|
SWAMP Data: |
Non-SWAMP |
|
Water Quality Objective/Criterion: |
Natural receiving water temperature of intrastate waters shall not be altered unless it can be demonstrated to the satisfaction of the Regional Water Board that such alteration in temperature does not adversely affect beneficial uses. At no time or place shall the temperature of any COLD water be increased more than 5 degrees Fahrenheit (F) above natural receiving water temperature (Basin Plan, North Coast Region). |
Objective/Criterion Reference: |
Water Quality Control Plan (Basin Plan) for the North Coast Region |
|
Evaluation Guideline: |
According to Carter (2008) the lethal temperature evaluation guideline for salmonid spawning, egg incubation & fry emergence is 20C. |
Guideline Reference: |
Effects of Temperature, Dissolved Oxygen/Total Dissolved Gas, Ammonia, and pH on Salmonids. Implications for California's North Coast TMDLs. California Regional Water Quality Control Board, North Coast Region |
|
Spatial Representation: |
The samples were collected at 1 monitoring site: KARUKDNR_WQX-SH (Shasta River). |
Temporal Representation: |
The samples were collected between the dates of 2011-04-28 and 2022-09-28 |
Environmental Conditions: |
|
QAPP Information: |
Karuk Tribe QA |
QAPP Information Reference(s): |
Data collected by a California Tribe QAPP Approved by U.S. EPA
QAPP Reference
|
|
Line of Evidence (LOE) for Decision ID 157124, Temperature, water
|
Region 1 |
Klamath River HU, Shasta River HA |
|
|
LOE ID: |
329312 |
|
Pollutant: |
Temperature, water |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
None |
|
Beneficial Use: |
Cold Freshwater Habitat |
|
Number of Samples: |
1 |
Number of Exceedances: |
1 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed USGS California Water Science Center data for Klamath River HU, Shasta River HA to determine beneficial use support and results are as follows: 1 of 1 samples exceeded the water quality threshold for Temperature. |
Data Reference: |
WQX from the NWQMP for the 2026 Integrated Report in Region 1 |
|
SWAMP Data: |
Non-SWAMP |
|
Water Quality Objective/Criterion: |
Natural receiving water temperature of intrastate waters shall not be altered unless it can be demonstrated to the satisfaction of the Regional Water Board that such alteration in temperature does not adversely affect beneficial uses. At no time or place shall the temperature of any COLD water be increased more than 5 degrees Fahrenheit (F) above natural receiving water temperature (Basin Plan, North Coast Region). |
Objective/Criterion Reference: |
Water Quality Control Plan (Basin Plan) for the North Coast Region |
|
Evaluation Guideline: |
According to Carter (2008) the lethal temperature evaluation guideline for salmonid spawning, egg incubation & fry emergence is 20C. |
Guideline Reference: |
Effects of Temperature, Dissolved Oxygen/Total Dissolved Gas, Ammonia, and pH on Salmonids. Implications for California's North Coast TMDLs. California Regional Water Quality Control Board, North Coast Region |
|
Spatial Representation: |
The samples were collected at 1 monitoring site: USGS-11516750 (SHASTA R NR EDGEWOOD CA). |
Temporal Representation: |
The samples were collected between the dates of 2015-08-27 and 2015-08-27 |
Environmental Conditions: |
|
QAPP Information: |
QAPP not required for USGS projects |
QAPP Information Reference(s): |
QAPP for USGS Data Collected during the 2026 Integrated Report Cycle |
|
Line of Evidence (LOE) for Decision ID 157124, Temperature, water
|
Region 1 |
Klamath River HU, Shasta River HA |
|
|
LOE ID: |
326916 |
|
Pollutant: |
Temperature, water |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
None |
|
Beneficial Use: |
Cold Freshwater Habitat |
|
Number of Samples: |
15 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP RWB1 Monitoring data for Klamath River HU, Shasta River HA to determine beneficial use support and results are as follows: 0 of 15 samples exceeded the water quality threshold for Temperature. |
Data Reference: |
Benthic, Field, Habitat, Tissue, Toxicity, WQ from the Surface Water Ambient Monitoring Program for the 2026 Integrated Report in Region 1 |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
Natural receiving water temperature of intrastate waters shall not be altered unless it can be demonstrated to the satisfaction of the Regional Water Board that such alteration in temperature does not adversely affect beneficial uses. At no time or place shall the temperature of any COLD water be increased more than 5 degrees Fahrenheit (F) above natural receiving water temperature (Basin Plan, North Coast Region). |
Objective/Criterion Reference: |
Water Quality Control Plan (Basin Plan) for the North Coast Region |
|
Evaluation Guideline: |
According to Carter (2008) the lethal temperature evaluation guideline for salmonid spawning, egg incubation & fry emergence is 20C. |
Guideline Reference: |
Effects of Temperature, Dissolved Oxygen/Total Dissolved Gas, Ammonia, and pH on Salmonids. Implications for California's North Coast TMDLs. California Regional Water Quality Control Board, North Coast Region |
|
Spatial Representation: |
The samples were collected at 1 monitoring site: 105LS9900 (Little Springs Creek at Outlet Works). |
Temporal Representation: |
The samples were collected between the dates of 2021-06-03 and 2021-10-28 |
Environmental Conditions: |
|
QAPP Information: |
QAPP for Surface Water Ambient Monitoring Program (SWAMP) |
QAPP Information Reference(s): |
Generic SWAMP QAPrP |
|
Line of Evidence (LOE) for Decision ID 157124, Temperature, water
|
Region 1 |
Klamath River HU, Shasta River HA |
|
|
LOE ID: |
326977 |
|
Pollutant: |
Temperature, water |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
None |
|
Beneficial Use: |
Cold Freshwater Habitat |
|
Number of Samples: |
80 |
Number of Exceedances: |
23 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed Klamath Hydroelectric Settlement Monitoring data for Klamath River HU, Shasta River HA to determine beneficial use support and results are as follows: 23 of 80 samples exceeded the water quality threshold for Temperature. |
Data Reference: |
Field, WQ from the Klamath Basin Monitoring Program for the 2026 Integrated Report in Region 1 |
|
SWAMP Data: |
Non-SWAMP |
|
Water Quality Objective/Criterion: |
Natural receiving water temperature of intrastate waters shall not be altered unless it can be demonstrated to the satisfaction of the Regional Water Board that such alteration in temperature does not adversely affect beneficial uses. At no time or place shall the temperature of any COLD water be increased more than 5 degrees Fahrenheit (F) above natural receiving water temperature (Basin Plan, North Coast Region). |
Objective/Criterion Reference: |
Water Quality Control Plan (Basin Plan) for the North Coast Region |
|
Evaluation Guideline: |
According to Carter (2008) the lethal temperature evaluation guideline for salmonid spawning, egg incubation & fry emergence is 20C. |
Guideline Reference: |
Effects of Temperature, Dissolved Oxygen/Total Dissolved Gas, Ammonia, and pH on Salmonids. Implications for California's North Coast TMDLs. California Regional Water Quality Control Board, North Coast Region |
|
Spatial Representation: |
The samples were collected at 1 monitoring site: SH00000_KHSA (Shasta River near mouth (Baseline)). |
Temporal Representation: |
The samples were collected between the dates of 2010-09-08 and 2016-12-14 |
Environmental Conditions: |
|
QAPP Information: |
Klamath Hydroelectric Settlement Monitoring QAPP |
QAPP Information Reference(s): |
San Francisco Estuary Institute - QA doc_cyano SOP (2009) - Klamath Hydroelectric Settlement Monitoring - 402674 |
|
Line of Evidence (LOE) for Decision ID 157124, Temperature, water
|
Region 1 |
Klamath River HU, Shasta River HA |
|
|
LOE ID: |
326964 |
|
Pollutant: |
Temperature, water |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
None |
|
Beneficial Use: |
Cold Freshwater Habitat |
|
Number of Samples: |
24 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP RWB1 Monitoring data for Klamath River HU, Shasta River HA to determine beneficial use support and results are as follows: 0 of 24 samples exceeded the water quality threshold for Temperature. |
Data Reference: |
Benthic, Field, Habitat, Tissue, Toxicity, WQ from the Surface Water Ambient Monitoring Program for the 2026 Integrated Report in Region 1 |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
Natural receiving water temperature of intrastate waters shall not be altered unless it can be demonstrated to the satisfaction of the Regional Water Board that such alteration in temperature does not adversely affect beneficial uses. At no time or place shall the temperature of any COLD water be increased more than 5 degrees Fahrenheit (F) above natural receiving water temperature (Basin Plan, North Coast Region). |
Objective/Criterion Reference: |
Water Quality Control Plan (Basin Plan) for the North Coast Region |
|
Evaluation Guideline: |
According to Carter (2008) the lethal temperature evaluation guideline for salmonid spawning, egg incubation & fry emergence is 20C. |
Guideline Reference: |
Effects of Temperature, Dissolved Oxygen/Total Dissolved Gas, Ammonia, and pH on Salmonids. Implications for California's North Coast TMDLs. California Regional Water Quality Control Board, North Coast Region |
|
Spatial Representation: |
The samples were collected at 1 monitoring site: 105PC0001 (Parks Creek at Shasta River). |
Temporal Representation: |
The samples were collected between the dates of 2021-04-15 and 2021-10-28 |
Environmental Conditions: |
|
QAPP Information: |
QAPP for Surface Water Ambient Monitoring Program (SWAMP) |
QAPP Information Reference(s): |
Generic SWAMP QAPrP |
|
Line of Evidence (LOE) for Decision ID 157124, Temperature, water
|
Region 1 |
Klamath River HU, Shasta River HA |
|
|
LOE ID: |
326985 |
|
Pollutant: |
Temperature, water |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
None |
|
Beneficial Use: |
Cold Freshwater Habitat |
|
Number of Samples: |
22 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP RWB1 Monitoring data for Klamath River HU, Shasta River HA to determine beneficial use support and results are as follows: 0 of 22 samples exceeded the water quality threshold for Temperature. |
Data Reference: |
Benthic, Field, Habitat, Tissue, Toxicity, WQ from the Surface Water Ambient Monitoring Program for the 2026 Integrated Report in Region 1 |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
Natural receiving water temperature of intrastate waters shall not be altered unless it can be demonstrated to the satisfaction of the Regional Water Board that such alteration in temperature does not adversely affect beneficial uses. At no time or place shall the temperature of any COLD water be increased more than 5 degrees Fahrenheit (F) above natural receiving water temperature (Basin Plan, North Coast Region). |
Objective/Criterion Reference: |
Water Quality Control Plan (Basin Plan) for the North Coast Region |
|
Evaluation Guideline: |
According to Carter (2008) the lethal temperature evaluation guideline for salmonid spawning, egg incubation & fry emergence is 20C. |
Guideline Reference: |
Effects of Temperature, Dissolved Oxygen/Total Dissolved Gas, Ammonia, and pH on Salmonids. Implications for California's North Coast TMDLs. California Regional Water Quality Control Board, North Coast Region |
|
Spatial Representation: |
The samples were collected at 1 monitoring site: 105SH6389 (Shasta River downstream Parks Creek). |
Temporal Representation: |
The samples were collected between the dates of 2021-04-08 and 2021-10-21 |
Environmental Conditions: |
|
QAPP Information: |
QAPP for Surface Water Ambient Monitoring Program (SWAMP) |
QAPP Information Reference(s): |
Generic SWAMP QAPrP |
|
Line of Evidence (LOE) for Decision ID 157124, Temperature, water
|
Region 1 |
Klamath River HU, Shasta River HA |
|
|
LOE ID: |
326989 |
|
Pollutant: |
Temperature, water |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
None |
|
Beneficial Use: |
Cold Freshwater Habitat |
|
Number of Samples: |
21 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP RWB1 Monitoring data for Klamath River HU, Shasta River HA to determine beneficial use support and results are as follows: 0 of 21 samples exceeded the water quality threshold for Temperature. |
Data Reference: |
Benthic, Field, Habitat, Tissue, Toxicity, WQ from the Surface Water Ambient Monitoring Program for the 2026 Integrated Report in Region 1 |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
Natural receiving water temperature of intrastate waters shall not be altered unless it can be demonstrated to the satisfaction of the Regional Water Board that such alteration in temperature does not adversely affect beneficial uses. At no time or place shall the temperature of any COLD water be increased more than 5 degrees Fahrenheit (F) above natural receiving water temperature (Basin Plan, North Coast Region). |
Objective/Criterion Reference: |
Water Quality Control Plan (Basin Plan) for the North Coast Region |
|
Evaluation Guideline: |
According to Carter (2008) the lethal temperature evaluation guideline for salmonid spawning, egg incubation & fry emergence is 20C. |
Guideline Reference: |
Effects of Temperature, Dissolved Oxygen/Total Dissolved Gas, Ammonia, and pH on Salmonids. Implications for California's North Coast TMDLs. California Regional Water Quality Control Board, North Coast Region |
|
Spatial Representation: |
The samples were collected at 1 monitoring site: 105SH6418 (Shasta River upstream Parks Creek). |
Temporal Representation: |
The samples were collected between the dates of 2021-04-08 and 2021-10-14 |
Environmental Conditions: |
|
QAPP Information: |
QAPP for Surface Water Ambient Monitoring Program (SWAMP) |
QAPP Information Reference(s): |
Generic SWAMP QAPrP |
|
Line of Evidence (LOE) for Decision ID 157124, Temperature, water
|
Region 1 |
Klamath River HU, Shasta River HA |
|
|
LOE ID: |
326930 |
|
Pollutant: |
Temperature, water |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
None |
|
Beneficial Use: |
Cold Freshwater Habitat |
|
Number of Samples: |
8 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP RWB1 Monitoring data for Klamath River HU, Shasta River HA to determine beneficial use support and results are as follows: 0 of 8 samples exceeded the water quality threshold for Temperature. |
Data Reference: |
Benthic, Field, Habitat, Tissue, Toxicity, WQ from the Surface Water Ambient Monitoring Program for the 2026 Integrated Report in Region 1 |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
Natural receiving water temperature of intrastate waters shall not be altered unless it can be demonstrated to the satisfaction of the Regional Water Board that such alteration in temperature does not adversely affect beneficial uses. At no time or place shall the temperature of any COLD water be increased more than 5 degrees Fahrenheit (F) above natural receiving water temperature (Basin Plan, North Coast Region). |
Objective/Criterion Reference: |
Water Quality Control Plan (Basin Plan) for the North Coast Region |
|
Evaluation Guideline: |
According to Carter (2008) the lethal temperature evaluation guideline for salmonid spawning, egg incubation & fry emergence is 20C. |
Guideline Reference: |
Effects of Temperature, Dissolved Oxygen/Total Dissolved Gas, Ammonia, and pH on Salmonids. Implications for California's North Coast TMDLs. California Regional Water Quality Control Board, North Coast Region |
|
Spatial Representation: |
The samples were collected at 1 monitoring site: 105LS9999 (Little Springs Creek at Spring Head). |
Temporal Representation: |
The samples were collected between the dates of 2021-04-08 and 2021-05-27 |
Environmental Conditions: |
|
QAPP Information: |
QAPP for Surface Water Ambient Monitoring Program (SWAMP) |
QAPP Information Reference(s): |
Generic SWAMP QAPrP |
|
Line of Evidence (LOE) for Decision ID 157124, Temperature, water
|
Region 1 |
Klamath River HU, Shasta River HA |
|
|
LOE ID: |
326909 |
|
Pollutant: |
Temperature, water |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
None |
|
Beneficial Use: |
Cold Freshwater Habitat |
|
Number of Samples: |
24 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP RWB1 Monitoring data for Klamath River HU, Shasta River HA to determine beneficial use support and results are as follows: 0 of 24 samples exceeded the water quality threshold for Temperature. |
Data Reference: |
Benthic, Field, Habitat, Tissue, Toxicity, WQ from the Surface Water Ambient Monitoring Program for the 2026 Integrated Report in Region 1 |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
Natural receiving water temperature of intrastate waters shall not be altered unless it can be demonstrated to the satisfaction of the Regional Water Board that such alteration in temperature does not adversely affect beneficial uses. At no time or place shall the temperature of any COLD water be increased more than 5 degrees Fahrenheit (F) above natural receiving water temperature (Basin Plan, North Coast Region). |
Objective/Criterion Reference: |
Water Quality Control Plan (Basin Plan) for the North Coast Region |
|
Evaluation Guideline: |
According to Carter (2008) the lethal temperature evaluation guideline for salmonid spawning, egg incubation & fry emergence is 20C. |
Guideline Reference: |
Effects of Temperature, Dissolved Oxygen/Total Dissolved Gas, Ammonia, and pH on Salmonids. Implications for California's North Coast TMDLs. California Regional Water Quality Control Board, North Coast Region |
|
Spatial Representation: |
The samples were collected at 1 monitoring site: 105BS7150 (Big Springs Creek at Old Water Wheel). |
Temporal Representation: |
The samples were collected between the dates of 2021-04-08 and 2021-10-28 |
Environmental Conditions: |
|
QAPP Information: |
QAPP for Surface Water Ambient Monitoring Program (SWAMP) |
QAPP Information Reference(s): |
Generic SWAMP QAPrP |
|
Line of Evidence (LOE) for Decision ID 157124, Temperature, water
|
Region 1 |
Klamath River HU, Shasta River HA |
|
|
LOE ID: |
326995 |
|
Pollutant: |
Temperature, water |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
None |
|
Beneficial Use: |
Cold Freshwater Habitat |
|
Number of Samples: |
1 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP Perennial Stream Surveys data for Klamath River HU, Shasta River HA to determine beneficial use support and results are as follows: 0 of 1 samples exceeded the water quality threshold for Temperature. |
Data Reference: |
Benthic, Field, Habitat, WQ from the Surface Water Ambient Monitoring Program for the 2026 Integrated Report in Region 1 |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
Natural receiving water temperature of intrastate waters shall not be altered unless it can be demonstrated to the satisfaction of the Regional Water Board that such alteration in temperature does not adversely affect beneficial uses. At no time or place shall the temperature of any COLD water be increased more than 5 degrees Fahrenheit (F) above natural receiving water temperature (Basin Plan, North Coast Region). |
Objective/Criterion Reference: |
Water Quality Control Plan (Basin Plan) for the North Coast Region |
|
Evaluation Guideline: |
According to Carter (2008) the lethal temperature evaluation guideline for salmonid spawning, egg incubation & fry emergence is 20C. |
Guideline Reference: |
Effects of Temperature, Dissolved Oxygen/Total Dissolved Gas, Ammonia, and pH on Salmonids. Implications for California's North Coast TMDLs. California Regional Water Quality Control Board, North Coast Region |
|
Spatial Representation: |
The samples were collected at 1 monitoring site: 105PS0295 (Shasta River ~1mi above Cooley Gulch). |
Temporal Representation: |
The samples were collected between the dates of 2016-06-15 and 2016-06-15 |
Environmental Conditions: |
|
QAPP Information: |
QAPP for Surface Water Ambient Monitoring Program (SWAMP) |
QAPP Information Reference(s): |
Generic SWAMP QAPrP |
|
Line of Evidence (LOE) for Decision ID 101152, Aldrin
|
Region 1 |
Klamath River HU, Shasta River HA |
|
|
LOE ID: |
40906 |
|
Pollutant: |
Aldrin |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Total |
|
Beneficial Use: |
Municipal & Domestic Supply |
|
Number of Samples: |
0 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Three non-detect sample results were not used in the assessment because the laboratory data reporting limit was above the objective and therefore the results could not be quantified with the level of certainty required by the Listing Policy. |
Data Reference: |
RWB1 Trend Maintenance Periods FYs 2007 2008 |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
Water Quality Control Plan, North Coast Region (NCRWQCB 2011): All waters shall be maintained free of toxic substances in concentrations that are toxic to, or that produce detrimental physiological responses in human, plant, animal, or aquatic life. The established numeric criteria for aldrin to protect of human health from the consumption of water and organisms is 0.00013 ug/L (California Toxics Rule, 2000). |
Objective/Criterion Reference: |
Code of Federal Regulations 40 part 131.38 Establishment of numeric criteria for priority toxic pollutants for the State of California. 7/1/2011 Edition |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
Data for this line of evidence for Klamath River HU, Shasta River HA was collected at 1 monitoring site [ Shasta River at Hwy 263 - 105SHA263] |
Temporal Representation: |
Data was collected over the time period 11/15/2007-7/16/2008. |
Environmental Conditions: |
Staff is not aware of any special conditions that might affect interpretation of the data. |
QAPP Information: |
The SWAMP QAPP (2008) was followed. |
QAPP Information Reference(s): |
Surface Water Ambient Monitoring Program Quality Assurance Program Plan |
|
Line of Evidence (LOE) for Decision ID 101152, Aldrin
|
Region 1 |
Klamath River HU, Shasta River HA |
|
|
LOE ID: |
114235 |
|
Pollutant: |
Aldrin |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Total |
|
Beneficial Use: |
Municipal & Domestic Supply |
|
Number of Samples: |
0 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP RWB1 Monitoring data for Klamath River HU, Shasta River HA to determine beneficial use support, and the results are as follows: 0 of the 0 samples exceeded the evaluation guideline for Aldrin. Although a total of 1 samples were collected, 1 of these samples were not included in the assessment because the laboratory data reporting limit(s) was above the objective and therefore the results could not be quantified with the level of certainty required by the Listing Policy Section 6.1.5.5. |
Data Reference: |
Water Quality Assessment Data for the 2018 solicitation cycle submitted through CEDEN for SWAMP RWB1 Monitoring .
|
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
Water Quality Control Plan, North Coast Region (NCRWQCB 2018): All waters shall be maintained free of toxic substances in concentrations that are toxic to, or that produce detrimental physiological responses in human, plant, animal, or aquatic life. The established numeric criteria for aldrin to protect of human health from the consumption of water and organisms is 0.00013 ug/L (California Toxics Rule, 2000). |
Objective/Criterion Reference: |
Water Quality Standards 2000. Establishment of numeric criteria for priority toxic pollutants for the State of California: Rules and regulations. Federal Register Vol. 65, No. 97. Washington, D.C.: Environmental Protection Agency |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
Data was collected from 1 station(s) (Station Code(s) 105SH1452). |
Temporal Representation: |
Date for this waterbody was collected over the date range 2013-04-29 to 2013-04-29 |
Environmental Conditions: |
|
QAPP Information: |
Quality Assurance Program Plan and Standard Operating Procedures for SWAMP program |
QAPP Information Reference(s): |
Quality Assurance Program Plans, Quality Assurance Project Plans, and Standard Operating Procedures for the SWAMP program |
|
Line of Evidence (LOE) for Decision ID 101152, Aldrin
|
Region 1 |
Klamath River HU, Shasta River HA |
|
|
LOE ID: |
40950 |
|
Pollutant: |
Aldrin |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Total |
|
Beneficial Use: |
Warm Freshwater Habitat |
|
Number of Samples: |
3 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP data for Klamath River HU, Shasta River HA to determine beneficial use support and results are as follows: 0 of 3 samples exceed the criterion for Aldrin. |
Data Reference: |
RWB1 Trend Maintenance Periods FYs 2007 2008 |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
Water Quality Control Plan, North Coast Region (NCRWQCB 2011): All waters shall be maintained free of toxic substances in concentrations that are toxic to, or that produce detrimental physiological responses in human, plant, animal, or aquatic life. The established numeric aldrin criterion maximum concentration to protect aquatic life in freshwater is 3 ug/L (California Toxics Rule, 2000). |
Objective/Criterion Reference: |
Code of Federal Regulations 40 part 131.38 Establishment of numeric criteria for priority toxic pollutants for the State of California. 7/1/2011 Edition |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
Data for this line of evidence for Klamath River HU, Shasta River HA was collected at 1 monitoring site [ Shasta River near Edgewood - 105SHAEDG] |
Temporal Representation: |
Data was collected over the time period 11/15/2007-7/16/2008. |
Environmental Conditions: |
Staff is not aware of any special conditions that might affect interpretation of the data. |
QAPP Information: |
The SWAMP QAPP (2008) was followed. |
QAPP Information Reference(s): |
Surface Water Ambient Monitoring Program Quality Assurance Program Plan |
|
Line of Evidence (LOE) for Decision ID 101152, Aldrin
|
Region 1 |
Klamath River HU, Shasta River HA |
|
|
LOE ID: |
40951 |
|
Pollutant: |
Aldrin |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Total |
|
Beneficial Use: |
Warm Freshwater Habitat |
|
Number of Samples: |
3 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP data for Klamath River HU, Shasta River HA to determine beneficial use support and results are as follows: 0 of 3 samples exceed the criterion for Aldrin. |
Data Reference: |
RWB1 Trend Maintenance Periods FYs 2007 2008 |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
Water Quality Control Plan, North Coast Region (NCRWQCB 2011): All waters shall be maintained free of toxic substances in concentrations that are toxic to, or that produce detrimental physiological responses in human, plant, animal, or aquatic life. The established numeric aldrin criterion maximum concentration to protect aquatic life in freshwater is 3 ug/L (California Toxics Rule, 2000). |
Objective/Criterion Reference: |
Code of Federal Regulations 40 part 131.38 Establishment of numeric criteria for priority toxic pollutants for the State of California. 7/1/2011 Edition |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
Data for this line of evidence for Klamath River HU, Shasta River HA was collected at 1 monitoring site [ Shasta River at Hwy 263 - 105SHA263] |
Temporal Representation: |
Data was collected over the time period 11/15/2007-7/16/2008. |
Environmental Conditions: |
Staff is not aware of any special conditions that might affect interpretation of the data. |
QAPP Information: |
The SWAMP QAPP (2008) was followed. |
QAPP Information Reference(s): |
Surface Water Ambient Monitoring Program Quality Assurance Program Plan |
|
Line of Evidence (LOE) for Decision ID 101152, Aldrin
|
Region 1 |
Klamath River HU, Shasta River HA |
|
|
LOE ID: |
40905 |
|
Pollutant: |
Aldrin |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Total |
|
Beneficial Use: |
Municipal & Domestic Supply |
|
Number of Samples: |
0 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Three non-detect sample results were not used in the assessment because the laboratory data reporting limit was above the objective and therefore the results could not be quantified with the level of certainty required by the Listing Policy. |
Data Reference: |
RWB1 Trend Maintenance Periods FYs 2007 2008 |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
Water Quality Control Plan, North Coast Region (NCRWQCB 2011): All waters shall be maintained free of toxic substances in concentrations that are toxic to, or that produce detrimental physiological responses in human, plant, animal, or aquatic life. The established numeric criteria for aldrin to protect of human health from the consumption of water and organisms is 0.00013 ug/L (California Toxics Rule, 2000). |
Objective/Criterion Reference: |
Code of Federal Regulations 40 part 131.38 Establishment of numeric criteria for priority toxic pollutants for the State of California. 7/1/2011 Edition |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
Data for this line of evidence for Klamath River HU, Shasta River HA was collected at 1 monitoring site [ Shasta River near Edgewood - 105SHAEDG] |
Temporal Representation: |
Data was collected over the time period 11/15/2007-7/16/2008. |
Environmental Conditions: |
Staff is not aware of any special conditions that might affect interpretation of the data. |
QAPP Information: |
The SWAMP QAPP (2008) was followed. |
QAPP Information Reference(s): |
Surface Water Ambient Monitoring Program Quality Assurance Program Plan |
|
Line of Evidence (LOE) for Decision ID 101152, Aldrin
|
Region 1 |
Klamath River HU, Shasta River HA |
|
|
LOE ID: |
103098 |
|
Pollutant: |
Aldrin |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Total |
|
Beneficial Use: |
Cold Freshwater Habitat |
|
Number of Samples: |
1 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP RWB1 Monitoring data for Klamath River HU, Shasta River HA to determine beneficial use support and results are as follows: 0 of 1 samples exceeded the water quality standard for Aldrin. |
Data Reference: |
Water Quality Assessment Data for the 2018 solicitation cycle submitted through CEDEN for SWAMP RWB1 Monitoring .
|
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
Water Quality Control Plan, North Coast Region (NCRWQCB 2018): All waters shall be maintained free of toxic substances in concentrations that are toxic to, or that produce detrimental physiological responses in human, plant, animal, or aquatic life. The established numeric criteria for aldrin to protect aquatic life in freshwater as criterion maximum concentration is 3 ug/L . This established criteria was divided by 2 in order to better represent a CMC value as specified in footnote g of Table (b)(1) of the California Toxics Rule, 2000. |
Objective/Criterion Reference: |
Water Quality Standards 2000. Establishment of numeric criteria for priority toxic pollutants for the State of California: Rules and regulations. Federal Register Vol. 65, No. 97. Washington, D.C.: Environmental Protection Agency |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
The samples were collected at 1 monitoring site(s) (105SH1452) |
Temporal Representation: |
The samples were collected between the dates of 2013-04-29 and 2013-04-29 |
Environmental Conditions: |
|
QAPP Information: |
Quality Assurance Program Plan and Standard Operating Procedures for SWAMP program |
QAPP Information Reference(s): |
Quality Assurance Program Plans, Quality Assurance Project Plans, and Standard Operating Procedures for the SWAMP program |
|
Line of Evidence (LOE) for Decision ID 101152, Aldrin
|
Region 1 |
Klamath River HU, Shasta River HA |
|
|
LOE ID: |
40971 |
|
Pollutant: |
Aldrin |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Total |
|
Beneficial Use: |
Cold Freshwater Habitat |
|
Number of Samples: |
3 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP data for Klamath River HU, Shasta River HA to determine beneficial use support and results are as follows: 0 of 3 samples exceed the criterion for Aldrin. |
Data Reference: |
RWB1 Trend Maintenance Periods FYs 2007 2008 |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
Water Quality Control Plan, North Coast Region (NCRWQCB 2011): All waters shall be maintained free of toxic substances in concentrations that are toxic to, or that produce detrimental physiological responses in human, plant, animal, or aquatic life. The established numeric criteria for aldrin to protect aquatic life in freshwater as criterion maximum concentration is 3 ug/L (California Toxics Rule, 2000). |
Objective/Criterion Reference: |
Code of Federal Regulations 40 part 131.38 Establishment of numeric criteria for priority toxic pollutants for the State of California. 7/1/2011 Edition |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
Data for this line of evidence for Klamath River HU, Shasta River HA was collected at 1 monitoring site [ Shasta River near Edgewood - 105SHAEDG] |
Temporal Representation: |
Data was collected over the time period 11/15/2007-7/16/2008. |
Environmental Conditions: |
Staff is not aware of any special conditions that might affect interpretation of the data. |
QAPP Information: |
The SWAMP QAPP (2008) was followed. |
QAPP Information Reference(s): |
Surface Water Ambient Monitoring Program Quality Assurance Program Plan |
|
Line of Evidence (LOE) for Decision ID 101152, Aldrin
|
Region 1 |
Klamath River HU, Shasta River HA |
|
|
LOE ID: |
111190 |
|
Pollutant: |
Aldrin |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Total |
|
Beneficial Use: |
Commercial or recreational collection of fish, shellfish, or organisms |
|
Number of Samples: |
0 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP RWB1 Monitoring data for Klamath River HU, Shasta River HA to determine beneficial use support, and the results are as follows: 0 of the 0 samples exceeded the evaluation guideline for Aldrin. Although a total of 1 samples were collected, 1 of these samples were not included in the assessment because the laboratory data reporting limit(s) was above the objective and therefore the results could not be quantified with the level of certainty required by the Listing Policy Section 6.1.5.5. |
Data Reference: |
Water Quality Assessment Data for the 2018 solicitation cycle submitted through CEDEN for SWAMP RWB1 Monitoring .
|
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
Water Quality Control Plan, North Coast Region (NCRWQCB 2018): All waters shall be maintained free of toxic substances in concentrations that are toxic to, or that produce detrimental physiological responses in human, plant, animal, or aquatic life. The established numeric criteria for aldrin criteria for the protection of human health from consumption of organisms only is 0.00014 ug/L (California Toxics Rule, 2000). |
Objective/Criterion Reference: |
Water Quality Standards 2000. Establishment of numeric criteria for priority toxic pollutants for the State of California: Rules and regulations. Federal Register Vol. 65, No. 97. Washington, D.C.: Environmental Protection Agency |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
Data was collected from 1 station(s) (Station Code(s) 105SH1452). |
Temporal Representation: |
Date for this waterbody was collected over the date range 2013-04-29 to 2013-04-29 |
Environmental Conditions: |
|
QAPP Information: |
Quality Assurance Program Plan and Standard Operating Procedures for SWAMP program |
QAPP Information Reference(s): |
Quality Assurance Program Plans, Quality Assurance Project Plans, and Standard Operating Procedures for the SWAMP program |
|
Line of Evidence (LOE) for Decision ID 101152, Aldrin
|
Region 1 |
Klamath River HU, Shasta River HA |
|
|
LOE ID: |
123342 |
|
Pollutant: |
Aldrin |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
None |
|
Beneficial Use: |
Municipal & Domestic Supply |
|
Number of Samples: |
0 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
State Water Board staff re-assessed SWAMP data for Klamath River HU, Shasta River HA to determine beneficial use support and results are as follows: 0 of 0 samples exceed the criterion for Aldrin, Total. Four sample results were not used in the assessment because the laboratory data reporting limit(s) was above the objective and therefore the results could not be quantified with the level of certainty required by the Listing Policy. This LOE re-assesses data from LOE 29849 from the 2010 Integrated Report. Data were re-assessed in order to (1) update the numeric objective, and (2) evaluate these data in their own LOE, instead of being evaluated in the same LOE as other pesticide data. |
Data Reference: |
Surface Water Ambient Monitoring Program (SWAMP). Summary Report for the North Coast Region (RWQCB-1) for years 2000-2006. North Coast Regional Water Quality Control Board. March 2008 |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
Water Quality Control Plan, North Coast Region (NCRWQCB 2011): All waters shall be maintained free of toxic substances in concentrations that are toxic to, or that produce detrimental physiological responses in human, plant, animal, or aquatic life. The established numeric criteria for aldrin to protect of human health from the consumption of water and organisms is 0.00013 ug/L (California Toxics Rule, 2000). |
Objective/Criterion Reference: |
Water Quality Control Plan (Basin Plan) for the North Coast Region |
Objective/Criterion Reference: |
Code of Federal Regulations 40 part 131.38 Establishment of numeric criteria for priority toxic pollutants for the State of California. 7/1/2011 Edition |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
Data for this line of evidence for Klamath River HU, Shasta River HA was collected at 1 monitoring site [ Shasta River near Edgewood - 105SH9274] |
Temporal Representation: |
Data was collected over the time period 10/7/2002-6/19/2003. |
Environmental Conditions: |
There are no known environmental conditions (e.g., seasonality, land use practices, fire events, storms, etc.) that are related to these data. |
QAPP Information: |
Quality control was conducted in accordance with the SWAMP Quality Assurance Management Plan (SWAMP 2002). |
QAPP Information Reference(s): |
Quality Assurance Management Plan for the State of California's Surface Water Ambient Monitoring Program. Sacramento, CA. State Water Resources Control Board. SWAMP. December 2002 (1st version)
|
|
Line of Evidence (LOE) for Decision ID 101152, Aldrin
|
Region 1 |
Klamath River HU, Shasta River HA |
|
|
LOE ID: |
123328 |
|
Pollutant: |
Aldrin |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
None |
|
Beneficial Use: |
Municipal & Domestic Supply |
|
Number of Samples: |
0 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
State Water Board staff re-assessed SWAMP data for Klamath River HU, Shasta River HA to determine beneficial use support and results are as follows: 0 of 0 samples exceed the criterion for Aldrin, Total. Four sample results were not used in the assessment because the laboratory data reporting limit(s) was above the objective and therefore the results could not be quantified with the level of certainty required by the Listing Policy. This LOE re-assesses data from LOE 29849 from the 2010 Integrated Report. Data were re-assessed in order to (1) update the numeric objective, and (2) evaluate these data in their own LOE, instead of being evaluated in the same LOE as other pesticide data. |
Data Reference: |
Surface Water Ambient Monitoring Program (SWAMP). Summary Report for the North Coast Region (RWQCB-1) for years 2000-2006. North Coast Regional Water Quality Control Board. March 2008 |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
Water Quality Control Plan, North Coast Region (NCRWQCB 2011): All waters shall be maintained free of toxic substances in concentrations that are toxic to, or that produce detrimental physiological responses in human, plant, animal, or aquatic life. The established numeric criteria for aldrin to protect of human health from the consumption of water and organisms is 0.00013 ug/L (California Toxics Rule, 2000). |
Objective/Criterion Reference: |
Water Quality Control Plan (Basin Plan) for the North Coast Region |
Objective/Criterion Reference: |
Code of Federal Regulations 40 part 131.38 Establishment of numeric criteria for priority toxic pollutants for the State of California. 7/1/2011 Edition |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
Data for this line of evidence for Klamath River HU, Shasta River HA was collected at 1 monitoring site [ Yreka Creek at Highway 3 - 105YREHW3] |
Temporal Representation: |
Data was collected over the time period 10/21/2004-6/20/2005. |
Environmental Conditions: |
There are no known environmental conditions (e.g., seasonality, land use practices, fire events, storms, etc.) that are related to these data. |
QAPP Information: |
Quality control was conducted in accordance with the SWAMP Quality Assurance Management Plan (SWAMP 2002). |
QAPP Information Reference(s): |
Quality Assurance Management Plan for the State of California's Surface Water Ambient Monitoring Program. Sacramento, CA. State Water Resources Control Board. SWAMP. December 2002 (1st version)
|
|
Line of Evidence (LOE) for Decision ID 101152, Aldrin
|
Region 1 |
Klamath River HU, Shasta River HA |
|
|
LOE ID: |
46910 |
|
Pollutant: |
Aldrin |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
None |
|
Beneficial Use: |
Municipal & Domestic Supply |
|
Number of Samples: |
0 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Thirty-five non-detect sample results were not used in the assessment because the laboratory data reporting limit was above the objective and therefore the results could not be quantified with the level of certainty required by the Listing Policy. The samples were collected as part of the Surface Water Ambient Water Monitoring Program (SWAMP). The data are found in the 5-Year Monitoring Report (NCRWQCB 2008). This LOE re-assesses data from LOE 25613 from the 2010 Integrated Report, in order to reflect that the non-detect data could not be quantified with the level of certainty required by the Listing Policy. |
Data Reference: |
Surface Water Ambient Monitoring Program (SWAMP). Summary Report for the North Coast Region (RWQCB-1) for years 2000-2006. North Coast Regional Water Quality Control Board. March 2008 |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
Water Quality Control Plan, North Coast Region (NCRWQCB 2011): All waters shall be maintained free of toxic substances in concentrations that are toxic to, or that produce detrimental physiological responses in human, plant, animal, or aquatic life. The established numeric criteria for aldrin to protect of human health from the consumption of water and organisms is 0.00013 ug/L (California Toxics Rule, 2000). |
Objective/Criterion Reference: |
Code of Federal Regulations 40 part 131.38 Establishment of numeric criteria for priority toxic pollutants for the State of California. 7/1/2011 Edition |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
Samples were collected in the Shasta River watershed from 5 locations as follows: (1) near Edgewood Road (SWAMP Station ID 105SHAEDG), (2) at Montague Grenada Road (SWAMP Station ID 105SHAMON), (3) at Highway 263 (SWAMP Station ID 105SHA263), (4) in Yreka Creek at Highway 3 (SWAMP Station ID 105YREHW3), and (5) in Yreka Creek at Anderson Grade Road (SWAMP Station
ID 105YREAND). Samples were collected in well-mixed flows in glides or riffles. |
Temporal Representation: |
The samples from Edgewood Road and Montague Grenada Road were collected as grab samples during 5 site visits at each site during the 2002 - 2003 fiscal years. Samples from Highway 263 were collected as grab samples during 22 site visits during the 2000 - 2006 fiscal years. Samples in Yreka Creek were collected from October 2004 to June 2005. The site visits corresponded to fall, winter, spring and early summer seasonal conditions. |
Environmental Conditions: |
There are no known environmental conditions (e.g., seasonality, land use practices, fire events, storms, etc.) that are related to these data. |
QAPP Information: |
Quality control was conducted in accordance with the SWAMP Quality Assurance Management Plan (SWAMP 2002). |
QAPP Information Reference(s): |
Quality Assurance Management Plan for the State of California's Surface Water Ambient Monitoring Program. Sacramento, CA. State Water Resources Control Board. SWAMP. December 2002 (1st version)
|
|
Line of Evidence (LOE) for Decision ID 101152, Aldrin
|
Region 1 |
Klamath River HU, Shasta River HA |
|
|
LOE ID: |
25613 |
|
Pollutant: |
Aldrin |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
None |
|
Beneficial Use: |
Municipal & Domestic Supply |
|
Number of Samples: |
35 |
Number of Exceedances: |
1 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
One of the 35 aldrin samples collected in the Shasta River watershed exceed the evaluation guideline. Sample concentrations range from non-detect (with a reporting limit of 0.002 ug/l) to detected but not quantified with a concentration of at least 0.002 ug/l. The samples were collected as part of the Surface Water Ambient Water Monitoring Program (SWAMP). The data are found in the 5-Year Monitoring Report (NCRWQCB 2008). |
Data Reference: |
Surface Water Ambient Monitoring Program (SWAMP). Summary Report for the North Coast Region (RWQCB-1) for years 2000-2006. North Coast Regional Water Quality Control Board. March 2008 |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
Per the Basin Plan (NCRWQCB 2007): No individual pesticide or combination of pesticides shall be present in concentrations that adversely affect beneficial uses. There shall be no bioaccumulation of pesticide concentrations found in bottom sediments or aquatic life. Waters designated for use as domestic or municipal supply shall not contain concentrations of pesticides in excess of the limiting concentrations set forth in California Code of Regulations, Title 22, Division 4, Chapter 15, Article 4, Section 64444, and listed in Table 3.2 of the Basin Plan. |
Objective/Criterion Reference: |
Water Quality Control Plan (Basin Plan) - North Coast Region (Region 1) |
|
Evaluation Guideline: |
Per the National Recommended Water Quality Criteria (USEPA 2006): The recommended criterion for aldrin for the protection of source waters for human health consumption of water and organisms is 0.000049 ug/l. |
Guideline Reference: |
National Recommended Water Quality Criteria. United States Environmental Protection Agency. Office of Water. Office of Science and Technology |
|
Spatial Representation: |
Samples were collected in the Shasta River watershed from 5 locations as follows: (1) near Edgewood Road (SWAMP Station ID 105SHAEDG), (2) at Montague Grenada Road (SWAMP Station ID 105SHAMON), (3) at Highway 263 (SWAMP Station ID 105SHA263), (4) in Yreka Creek at Highway 3 (SWAMP Station ID 105YREHW3), and (5) in Yreka Creek at Anderson Grade Road (SWAMP Station ID 105YREAND). Samples were collected in well-mixed flows in glides or riffles. |
Temporal Representation: |
The samples from Edgewood Road and Montague Grenada Road were collected as grab samples during 5 site visits at each site during the 2002 - 2003 fiscal years. Samples from Highway 263 were collected as grab samples during 22 site visits during the 2000 - 2006 fiscal years. Samples in Yreka Creek were collected from October 2004 to June 2005. The site visits corresponded to fall, winter, spring and early summer seasonal conditions. |
Environmental Conditions: |
There are no known environmental conditions (e.g., seasonality, land use practices, fire events, storms, etc.) that are related to these data. |
QAPP Information: |
Quality control was conducted in accordance with the SWAMP Quality Assurance Management Plan (SWAMP 2002). |
QAPP Information Reference(s): |
Quality Assurance Management Plan for the State of California's Surface Water Ambient Monitoring Program. Sacramento, CA. State Water Resources Control Board. SWAMP. December 2002 (1st version)
|
|
Line of Evidence (LOE) for Decision ID 101152, Aldrin
|
Region 1 |
Klamath River HU, Shasta River HA |
|
|
LOE ID: |
103099 |
|
Pollutant: |
Aldrin |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Total |
|
Beneficial Use: |
Cold Freshwater Habitat |
|
Number of Samples: |
1 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP RWB1 Monitoring data for Klamath River HU, Shasta River HA to determine beneficial use support and results are as follows: 0 of 1 samples exceeded the water quality standard for Aldrin. |
Data Reference: |
Water Quality Assessment Data for the 2018 solicitation cycle submitted through CEDEN for SWAMP RWB1 Monitoring .
|
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
Water Quality Control Plan, North Coast Region (NCRWQCB 2018): All waters shall be maintained free of toxic substances in concentrations that are toxic to, or that produce detrimental physiological responses in human, plant, animal, or aquatic life. The established numeric criteria for aldrin to protect aquatic life in freshwater as criterion maximum concentration is 3 ug/L . This established criteria was divided by 2 in order to better represent a CMC value as specified in footnote g of Table (b)(1) of the California Toxics Rule, 2000. |
Objective/Criterion Reference: |
Water Quality Standards 2000. Establishment of numeric criteria for priority toxic pollutants for the State of California: Rules and regulations. Federal Register Vol. 65, No. 97. Washington, D.C.: Environmental Protection Agency |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
The samples were collected at 1 monitoring site(s) (105SH9274) |
Temporal Representation: |
The samples were collected between the dates of 2013-04-29 and 2013-04-29 |
Environmental Conditions: |
|
QAPP Information: |
Quality Assurance Program Plan and Standard Operating Procedures for SWAMP program |
QAPP Information Reference(s): |
Quality Assurance Program Plans, Quality Assurance Project Plans, and Standard Operating Procedures for the SWAMP program |
|
Line of Evidence (LOE) for Decision ID 101152, Aldrin
|
Region 1 |
Klamath River HU, Shasta River HA |
|
|
LOE ID: |
40972 |
|
Pollutant: |
Aldrin |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Total |
|
Beneficial Use: |
Cold Freshwater Habitat |
|
Number of Samples: |
3 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP data for Klamath River HU, Shasta River HA to determine beneficial use support and results are as follows: 0 of 3 samples exceed the criterion for Aldrin. |
Data Reference: |
RWB1 Trend Maintenance Periods FYs 2007 2008 |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
Water Quality Control Plan, North Coast Region (NCRWQCB 2011): All waters shall be maintained free of toxic substances in concentrations that are toxic to, or that produce detrimental physiological responses in human, plant, animal, or aquatic life. The established numeric criteria for aldrin to protect aquatic life in freshwater as criterion maximum concentration is 3 ug/L (California Toxics Rule, 2000). |
Objective/Criterion Reference: |
Code of Federal Regulations 40 part 131.38 Establishment of numeric criteria for priority toxic pollutants for the State of California. 7/1/2011 Edition |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
Data for this line of evidence for Klamath River HU, Shasta River HA was collected at 1 monitoring site [ Shasta River at Hwy 263 - 105SHA263] |
Temporal Representation: |
Data was collected over the time period 11/15/2007-7/16/2008. |
Environmental Conditions: |
Staff is not aware of any special conditions that might affect interpretation of the data. |
QAPP Information: |
The SWAMP QAPP (2008) was followed. |
QAPP Information Reference(s): |
Surface Water Ambient Monitoring Program Quality Assurance Program Plan |
|
Line of Evidence (LOE) for Decision ID 101152, Aldrin
|
Region 1 |
Klamath River HU, Shasta River HA |
|
|
LOE ID: |
114237 |
|
Pollutant: |
Aldrin |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Total |
|
Beneficial Use: |
Municipal & Domestic Supply |
|
Number of Samples: |
0 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP RWB1 Monitoring data for Klamath River HU, Shasta River HA to determine beneficial use support, and the results are as follows: 0 of the 0 samples exceeded the evaluation guideline for Aldrin. Although a total of 1 samples were collected, 1 of these samples were not included in the assessment because the laboratory data reporting limit(s) was above the objective and therefore the results could not be quantified with the level of certainty required by the Listing Policy Section 6.1.5.5. |
Data Reference: |
Water Quality Assessment Data for the 2018 solicitation cycle submitted through CEDEN for SWAMP RWB1 Monitoring .
|
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
Water Quality Control Plan, North Coast Region (NCRWQCB 2018): All waters shall be maintained free of toxic substances in concentrations that are toxic to, or that produce detrimental physiological responses in human, plant, animal, or aquatic life. The established numeric criteria for aldrin to protect of human health from the consumption of water and organisms is 0.00013 ug/L (California Toxics Rule, 2000). |
Objective/Criterion Reference: |
Water Quality Standards 2000. Establishment of numeric criteria for priority toxic pollutants for the State of California: Rules and regulations. Federal Register Vol. 65, No. 97. Washington, D.C.: Environmental Protection Agency |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
Data was collected from 1 station(s) (Station Code(s) 105SH9274). |
Temporal Representation: |
Date for this waterbody was collected over the date range 2013-04-29 to 2013-04-29 |
Environmental Conditions: |
|
QAPP Information: |
Quality Assurance Program Plan and Standard Operating Procedures for SWAMP program |
QAPP Information Reference(s): |
Quality Assurance Program Plans, Quality Assurance Project Plans, and Standard Operating Procedures for the SWAMP program |
|
Line of Evidence (LOE) for Decision ID 101152, Aldrin
|
Region 1 |
Klamath River HU, Shasta River HA |
|
|
LOE ID: |
40926 |
|
Pollutant: |
Aldrin |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Total |
|
Beneficial Use: |
Commercial or recreational collection of fish, shellfish, or organisms |
|
Number of Samples: |
0 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Three non-detect sample results were not used in the assessment because the laboratory data reporting limit was above the objective and therefore the results could not be quantified with the level of certainty required by the Listing Policy. |
Data Reference: |
RWB1 Trend Maintenance Periods FYs 2007 2008 |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
Water Quality Control Plan, North Coast Region (NCRWQCB 2011): All waters shall be maintained free of toxic substances in concentrations that are toxic to, or that produce detrimental physiological responses in human, plant, animal, or aquatic life. The established numeric criteria for aldrin criteria for the protection of human health from consumption of organisms only is 0.00014 ug/L (California Toxics Rule, 2000). |
Objective/Criterion Reference: |
Code of Federal Regulations 40 part 131.38 Establishment of numeric criteria for priority toxic pollutants for the State of California. 7/1/2011 Edition |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
Data for this line of evidence for Klamath River HU, Shasta River HA was collected at 1 monitoring site [ Shasta River at Hwy 263 - 105SHA263] |
Temporal Representation: |
Data was collected over the time period 11/15/2007-7/16/2008. |
Environmental Conditions: |
Staff is not aware of any special conditions that might affect interpretation of the data. |
QAPP Information: |
The SWAMP QAPP (2008) was followed. |
QAPP Information Reference(s): |
Surface Water Ambient Monitoring Program Quality Assurance Program Plan |
|
Line of Evidence (LOE) for Decision ID 101152, Aldrin
|
Region 1 |
Klamath River HU, Shasta River HA |
|
|
LOE ID: |
107673 |
|
Pollutant: |
Aldrin |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Total |
|
Beneficial Use: |
Commercial or recreational collection of fish, shellfish, or organisms |
|
Number of Samples: |
0 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP RWB1 Monitoring data for Klamath River HU, Shasta River HA to determine beneficial use support, and the results are as follows: 0 of the 0 samples exceeded the evaluation guideline for Aldrin. Although a total of 1 samples were collected, 1 of these samples were not included in the assessment because the laboratory data reporting limit(s) was above the objective and therefore the results could not be quantified with the level of certainty required by the Listing Policy Section 6.1.5.5. |
Data Reference: |
Water Quality Assessment Data for the 2018 solicitation cycle submitted through CEDEN for SWAMP RWB1 Monitoring .
|
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
Water Quality Control Plan, North Coast Region (NCRWQCB 2018): All waters shall be maintained free of toxic substances in concentrations that are toxic to, or that produce detrimental physiological responses in human, plant, animal, or aquatic life. The established numeric criteria for aldrin criteria for the protection of human health from consumption of organisms only is 0.00014 ug/L (California Toxics Rule, 2000). |
Objective/Criterion Reference: |
Water Quality Standards 2000. Establishment of numeric criteria for priority toxic pollutants for the State of California: Rules and regulations. Federal Register Vol. 65, No. 97. Washington, D.C.: Environmental Protection Agency |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
Data was collected from 1 station(s) (Station Code(s) 105SH9274). |
Temporal Representation: |
Date for this waterbody was collected over the date range 2013-04-29 to 2013-04-29 |
Environmental Conditions: |
|
QAPP Information: |
Quality Assurance Program Plan and Standard Operating Procedures for SWAMP program |
QAPP Information Reference(s): |
Quality Assurance Program Plans, Quality Assurance Project Plans, and Standard Operating Procedures for the SWAMP program |
|
Line of Evidence (LOE) for Decision ID 101152, Aldrin
|
Region 1 |
Klamath River HU, Shasta River HA |
|
|
LOE ID: |
40925 |
|
Pollutant: |
Aldrin |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Total |
|
Beneficial Use: |
Commercial or recreational collection of fish, shellfish, or organisms |
|
Number of Samples: |
0 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Three non-detect sample results were not used in the assessment because the laboratory data reporting limit was above the objective and therefore the results could not be quantified with the level of certainty required by the Listing Policy. |
Data Reference: |
RWB1 Trend Maintenance Periods FYs 2007 2008 |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
Water Quality Control Plan, North Coast Region (NCRWQCB 2011): All waters shall be maintained free of toxic substances in concentrations that are toxic to, or that produce detrimental physiological responses in human, plant, animal, or aquatic life. The established numeric criteria for aldrin criteria for the protection of human health from consumption of organisms only is 0.00014 ug/L (California Toxics Rule, 2000). |
Objective/Criterion Reference: |
Code of Federal Regulations 40 part 131.38 Establishment of numeric criteria for priority toxic pollutants for the State of California. 7/1/2011 Edition |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
Data for this line of evidence for Klamath River HU, Shasta River HA was collected at 1 monitoring site [ Shasta River near Edgewood - 105SHAEDG] |
Temporal Representation: |
Data was collected over the time period 11/15/2007-7/16/2008. |
Environmental Conditions: |
Staff is not aware of any special conditions that might affect interpretation of the data. |
QAPP Information: |
The SWAMP QAPP (2008) was followed. |
QAPP Information Reference(s): |
Surface Water Ambient Monitoring Program Quality Assurance Program Plan |
|
Line of Evidence (LOE) for Decision ID 101152, Aldrin
|
Region 1 |
Klamath River HU, Shasta River HA |
|
|
LOE ID: |
123341 |
|
Pollutant: |
Aldrin |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
None |
|
Beneficial Use: |
Municipal & Domestic Supply |
|
Number of Samples: |
0 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
State Water Board staff re-assessed SWAMP data for Klamath River HU, Shasta River HA to determine beneficial use support and results are as follows: 0 of 0 samples exceed the criterion for Aldrin, Total. Four sample results were not used in the assessment because the laboratory data reporting limit(s) was above the objective and therefore the results could not be quantified with the level of certainty required by the Listing Policy. This LOE re-assesses data from LOE 29849 from the 2010 Integrated Report. Data were re-assessed in order to (1) update the numeric objective, and (2) evaluate these data in their own LOE, instead of being evaluated in the same LOE as other pesticide data. |
Data Reference: |
Surface Water Ambient Monitoring Program (SWAMP). Summary Report for the North Coast Region (RWQCB-1) for years 2000-2006. North Coast Regional Water Quality Control Board. March 2008 |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
Water Quality Control Plan, North Coast Region (NCRWQCB 2011): All waters shall be maintained free of toxic substances in concentrations that are toxic to, or that produce detrimental physiological responses in human, plant, animal, or aquatic life. The established numeric criteria for aldrin to protect of human health from the consumption of water and organisms is 0.00013 ug/L (California Toxics Rule, 2000). |
Objective/Criterion Reference: |
Water Quality Control Plan (Basin Plan) for the North Coast Region |
Objective/Criterion Reference: |
Code of Federal Regulations 40 part 131.38 Establishment of numeric criteria for priority toxic pollutants for the State of California. 7/1/2011 Edition |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
Data for this line of evidence for Klamath River HU, Shasta River HA was collected at 1 monitoring site [ Shasta River at Montague - 105SHAMON] |
Temporal Representation: |
Data was collected over the time period 10/7/2002-6/19/2003. |
Environmental Conditions: |
There are no known environmental conditions (e.g., seasonality, land use practices, fire events, storms, etc.) that are related to these data. |
QAPP Information: |
Quality control was conducted in accordance with the SWAMP Quality Assurance Management Plan (SWAMP 2002). |
QAPP Information Reference(s): |
Quality Assurance Management Plan for the State of California's Surface Water Ambient Monitoring Program. Sacramento, CA. State Water Resources Control Board. SWAMP. December 2002 (1st version)
|
|
Line of Evidence (LOE) for Decision ID 101152, Aldrin
|
Region 1 |
Klamath River HU, Shasta River HA |
|
|
LOE ID: |
123327 |
|
Pollutant: |
Aldrin |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
None |
|
Beneficial Use: |
Municipal & Domestic Supply |
|
Number of Samples: |
0 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
State Water Board staff re-assessed SWAMP data for Klamath River HU, Shasta River HA to determine beneficial use support and results are as follows: 0 of 0 samples exceed the criterion for Aldrin, Total. Eight sample results were not used in the assessment because the laboratory data reporting limit(s) was above the objective and therefore the results could not be quantified with the level of certainty required by the Listing Policy. This LOE re-assesses data from LOE 29849 from the 2010 Integrated Report. Data were re-assessed in order to (1) update the numeric objective, and (2) evaluate these data in their own LOE, instead of being evaluated in the same LOE as other pesticide data. |
Data Reference: |
Surface Water Ambient Monitoring Program (SWAMP). Summary Report for the North Coast Region (RWQCB-1) for years 2000-2006. North Coast Regional Water Quality Control Board. March 2008 |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
Water Quality Control Plan, North Coast Region (NCRWQCB 2011): All waters shall be maintained free of toxic substances in concentrations that are toxic to, or that produce detrimental physiological responses in human, plant, animal, or aquatic life. The established numeric criteria for aldrin to protect of human health from the consumption of water and organisms is 0.00013 ug/L (California Toxics Rule, 2000). |
Objective/Criterion Reference: |
Water Quality Control Plan (Basin Plan) for the North Coast Region |
Objective/Criterion Reference: |
Code of Federal Regulations 40 part 131.38 Establishment of numeric criteria for priority toxic pollutants for the State of California. 7/1/2011 Edition |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
Data for this line of evidence for Klamath River HU, Shasta River HA was collected at 1 monitoring site [ Yreka Creek at Anderson Rd - 105YREAND] |
Temporal Representation: |
Data was collected over the time period 10/9/2002-6/20/2005. |
Environmental Conditions: |
There are no known environmental conditions (e.g., seasonality, land use practices, fire events, storms, etc.) that are related to these data. |
QAPP Information: |
Quality control was conducted in accordance with the SWAMP Quality Assurance Management Plan (SWAMP 2002). |
QAPP Information Reference(s): |
Quality Assurance Management Plan for the State of California's Surface Water Ambient Monitoring Program. Sacramento, CA. State Water Resources Control Board. SWAMP. December 2002 (1st version)
|
|
Line of Evidence (LOE) for Decision ID 101152, Aldrin
|
Region 1 |
Klamath River HU, Shasta River HA |
|
|
LOE ID: |
123329 |
|
Pollutant: |
Aldrin |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
None |
|
Beneficial Use: |
Municipal & Domestic Supply |
|
Number of Samples: |
0 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
State Water Board staff re-assessed SWAMP data for Klamath River HU, Shasta River HA to determine beneficial use support and results are as follows: 0 of 0 samples exceed the criterion for Aldrin, Total. Seventeen sample results were not used in the assessment because the laboratory data reporting limit(s) was above the objective and therefore the results could not be quantified with the level of certainty required by the Listing Policy. This LOE re-assesses data from LOE 29849 from the 2010 Integrated Report. Data were re-assessed in order to (1) update the numeric objective, and (2) evaluate these data in their own LOE, instead of being evaluated in the same LOE as other pesticide data. |
Data Reference: |
Surface Water Ambient Monitoring Program (SWAMP). Summary Report for the North Coast Region (RWQCB-1) for years 2000-2006. North Coast Regional Water Quality Control Board. March 2008 |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
Water Quality Control Plan, North Coast Region (NCRWQCB 2011): All waters shall be maintained free of toxic substances in concentrations that are toxic to, or that produce detrimental physiological responses in human, plant, animal, or aquatic life. The established numeric criteria for aldrin to protect of human health from the consumption of water and organisms is 0.00013 ug/L (California Toxics Rule, 2000). |
Objective/Criterion Reference: |
Water Quality Control Plan (Basin Plan) for the North Coast Region |
Objective/Criterion Reference: |
Code of Federal Regulations 40 part 131.38 Establishment of numeric criteria for priority toxic pollutants for the State of California. 7/1/2011 Edition |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
Data for this line of evidence for Klamath River HU, Shasta River HA was collected at 1 monitoring site [ Shasta River at Hwy 263 - 105SH1452] |
Temporal Representation: |
Data was collected over the time period 4/24/2001-11/16/2006. |
Environmental Conditions: |
There are no known environmental conditions (e.g., seasonality, land use practices, fire events, storms, etc.) that are related to these data. |
QAPP Information: |
Quality control was conducted in accordance with the SWAMP Quality Assurance Management Plan (SWAMP 2002). |
QAPP Information Reference(s): |
Quality Assurance Management Plan for the State of California's Surface Water Ambient Monitoring Program. Sacramento, CA. State Water Resources Control Board. SWAMP. December 2002 (1st version)
|
|
Line of Evidence (LOE) for Decision ID 161417, Ammonia
|
Region 1 |
Klamath River HU, Shasta River HA |
|
|
LOE ID: |
103117 |
|
Pollutant: |
Nitrogen, ammonia (Total Ammonia) |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Total |
|
Beneficial Use: |
Municipal & Domestic Supply |
|
Number of Samples: |
5 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP RWB1 Monitoring data for Klamath River HU, Shasta River HA to determine beneficial use support and results are as follows: 0 of 5 samples exceeded the water quality standard for Ammonia as N. |
Data Reference: |
Water Quality Assessment Data for the 2018 solicitation cycle submitted through CEDEN for SWAMP RWB1 Monitoring .
|
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
All waters shall be maintained free of toxic substances in concentrations that are toxic to, or that produce detrimental physiological responses in human, plant, animal, or aquatic life (North Coast Regional Water Quality Control Board). |
Objective/Criterion Reference: |
Water Quality Control Plan (Basin Plan) for the North Coast Region |
|
Evaluation Guideline: |
The USEPA Health Advisory for lifetime exposure to Ammonia as a drinking water level is a concentration of 30 mg/L |
Guideline Reference: |
2012 Edition of the Drinking Water Standards and Health Advisories |
|
Spatial Representation: |
The samples were collected at 1 monitoring site(s) (105SH9274) |
Temporal Representation: |
The samples were collected between the dates of 2013-03-07 and 2013-11-20 |
Environmental Conditions: |
|
QAPP Information: |
Quality Assurance Program Plan and Standard Operating Procedures for SWAMP program |
QAPP Information Reference(s): |
Quality Assurance Program Plans, Quality Assurance Project Plans, and Standard Operating Procedures for the SWAMP program |
|
Line of Evidence (LOE) for Decision ID 161417, Ammonia
|
Region 1 |
Klamath River HU, Shasta River HA |
|
|
LOE ID: |
115056 |
|
Pollutant: |
Nitrogen, ammonia (Total Ammonia) |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Total |
|
Beneficial Use: |
Municipal & Domestic Supply |
|
Number of Samples: |
1 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed Shasta Tailwater Reduction data for Klamath River HU, Shasta River HA to determine beneficial use support and results are as follows: 0 of 1 samples exceeded the water quality standard for Ammonia as N. |
Data Reference: |
Water Quality Assessment Data for the 2018 solicitation cycle submitted through CEDEN for Shasta Tailwater Reduction .
|
|
SWAMP Data: |
Non-SWAMP |
|
Water Quality Objective/Criterion: |
All waters shall be maintained free of toxic substances in concentrations that are toxic to, or that produce detrimental physiological responses in human, plant, animal, or aquatic life (North Coast Regional Water Quality Control Board). |
Objective/Criterion Reference: |
Water Quality Control Plan (Basin Plan) for the North Coast Region |
|
Evaluation Guideline: |
The USEPA Health Advisory for lifetime exposure to Ammonia as a drinking water level is a concentration of 30 mg/L |
Guideline Reference: |
2012 Edition of the Drinking Water Standards and Health Advisories |
|
Spatial Representation: |
The samples were collected at 1 monitoring site(s) (105SR6074_2DS) |
Temporal Representation: |
The samples were collected between the dates of 2015-08-24 and 2015-08-24 |
Environmental Conditions: |
|
QAPP Information: |
Quality Assurance Project Plan for Shasta Tailwater Reduction |
QAPP Information Reference(s): |
Quality Assurance Project Plans for the Shasta River Watershed Tailwater Projects |
|
Line of Evidence (LOE) for Decision ID 161417, Ammonia
|
Region 1 |
Klamath River HU, Shasta River HA |
|
|
LOE ID: |
115317 |
|
Pollutant: |
Nitrogen, ammonia (Total Ammonia) |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Total |
|
Beneficial Use: |
Municipal & Domestic Supply |
|
Number of Samples: |
1 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP Perennial Stream Surveys data for Klamath River HU, Shasta River HA to determine beneficial use support and results are as follows: 0 of 1 samples exceeded the water quality standard for Ammonia as N. |
Data Reference: |
Water Quality Assessment Data for the 2018 solicitation cycle submitted through CEDEN for SWAMP Perennial Stream Surveys .
|
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
All waters shall be maintained free of toxic substances in concentrations that are toxic to, or that produce detrimental physiological responses in human, plant, animal, or aquatic life (North Coast Regional Water Quality Control Board). |
Objective/Criterion Reference: |
Water Quality Control Plan (Basin Plan) for the North Coast Region |
|
Evaluation Guideline: |
The USEPA Health Advisory for lifetime exposure to Ammonia as a drinking water level is a concentration of 30 mg/L |
Guideline Reference: |
2012 Edition of the Drinking Water Standards and Health Advisories |
|
Spatial Representation: |
The samples were collected at 1 monitoring site(s) (105PS0231) |
Temporal Representation: |
The samples were collected between the dates of 2013-08-29 and 2013-08-29 |
Environmental Conditions: |
|
QAPP Information: |
Quality Assurance Program Plan and Standard Operating Procedures for SWAMP program |
QAPP Information Reference(s): |
Quality Assurance Program Plans, Quality Assurance Project Plans, and Standard Operating Procedures for the SWAMP program |
|
Line of Evidence (LOE) for Decision ID 161417, Ammonia
|
Region 1 |
Klamath River HU, Shasta River HA |
|
|
LOE ID: |
102834 |
|
Pollutant: |
Nitrogen, ammonia (Total Ammonia) |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Total |
|
Beneficial Use: |
Municipal & Domestic Supply |
|
Number of Samples: |
1 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed Shasta Tailwater Reduction data for Klamath River HU, Shasta River HA to determine beneficial use support and results are as follows: 0 of 1 samples exceeded the water quality standard for Ammonia as N. |
Data Reference: |
Water Quality Assessment Data for the 2018 solicitation cycle submitted through CEDEN for Shasta Tailwater Reduction .
|
|
SWAMP Data: |
Non-SWAMP |
|
Water Quality Objective/Criterion: |
All waters shall be maintained free of toxic substances in concentrations that are toxic to, or that produce detrimental physiological responses in human, plant, animal, or aquatic life (North Coast Regional Water Quality Control Board). |
Objective/Criterion Reference: |
Water Quality Control Plan (Basin Plan) for the North Coast Region |
|
Evaluation Guideline: |
The USEPA Health Advisory for lifetime exposure to Ammonia as a drinking water level is a concentration of 30 mg/L |
Guideline Reference: |
2012 Edition of the Drinking Water Standards and Health Advisories |
|
Spatial Representation: |
The samples were collected at 1 monitoring site(s) (105SR7174DS) |
Temporal Representation: |
The samples were collected between the dates of 2015-08-25 and 2015-08-25 |
Environmental Conditions: |
|
QAPP Information: |
Quality Assurance Project Plan for Shasta Tailwater Reduction |
QAPP Information Reference(s): |
Quality Assurance Project Plans for the Shasta River Watershed Tailwater Projects |
|
Line of Evidence (LOE) for Decision ID 161417, Ammonia
|
Region 1 |
Klamath River HU, Shasta River HA |
|
|
LOE ID: |
102779 |
|
Pollutant: |
Nitrogen, ammonia (Total Ammonia) |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Total |
|
Beneficial Use: |
Municipal & Domestic Supply |
|
Number of Samples: |
1 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed Shasta Tailwater Reduction data for Klamath River HU, Shasta River HA to determine beneficial use support and results are as follows: 0 of 1 samples exceeded the water quality standard for Ammonia as N. |
Data Reference: |
Water Quality Assessment Data for the 2018 solicitation cycle submitted through CEDEN for Shasta Tailwater Reduction .
|
|
SWAMP Data: |
Non-SWAMP |
|
Water Quality Objective/Criterion: |
All waters shall be maintained free of toxic substances in concentrations that are toxic to, or that produce detrimental physiological responses in human, plant, animal, or aquatic life (North Coast Regional Water Quality Control Board). |
Objective/Criterion Reference: |
Water Quality Control Plan (Basin Plan) for the North Coast Region |
|
Evaluation Guideline: |
The USEPA Health Advisory for lifetime exposure to Ammonia as a drinking water level is a concentration of 30 mg/L |
Guideline Reference: |
2012 Edition of the Drinking Water Standards and Health Advisories |
|
Spatial Representation: |
The samples were collected at 1 monitoring site(s) (105SR6355DS) |
Temporal Representation: |
The samples were collected between the dates of 2015-08-25 and 2015-08-25 |
Environmental Conditions: |
|
QAPP Information: |
Quality Assurance Project Plan for Shasta Tailwater Reduction |
QAPP Information Reference(s): |
Quality Assurance Project Plans for the Shasta River Watershed Tailwater Projects |
|
Line of Evidence (LOE) for Decision ID 161417, Ammonia
|
Region 1 |
Klamath River HU, Shasta River HA |
|
|
LOE ID: |
103114 |
|
Pollutant: |
Nitrogen, ammonia (Total Ammonia) |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Total |
|
Beneficial Use: |
Municipal & Domestic Supply |
|
Number of Samples: |
5 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP RWB1 Monitoring data for Klamath River HU, Shasta River HA to determine beneficial use support and results are as follows: 0 of 5 samples exceeded the water quality standard for Ammonia as N. |
Data Reference: |
Water Quality Assessment Data for the 2018 solicitation cycle submitted through CEDEN for SWAMP RWB1 Monitoring .
|
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
All waters shall be maintained free of toxic substances in concentrations that are toxic to, or that produce detrimental physiological responses in human, plant, animal, or aquatic life (North Coast Regional Water Quality Control Board). |
Objective/Criterion Reference: |
Water Quality Control Plan (Basin Plan) for the North Coast Region |
|
Evaluation Guideline: |
The USEPA Health Advisory for lifetime exposure to Ammonia as a drinking water level is a concentration of 30 mg/L |
Guideline Reference: |
2012 Edition of the Drinking Water Standards and Health Advisories |
|
Spatial Representation: |
The samples were collected at 1 monitoring site(s) (105SH1452) |
Temporal Representation: |
The samples were collected between the dates of 2013-03-06 and 2013-11-20 |
Environmental Conditions: |
|
QAPP Information: |
Quality Assurance Program Plan and Standard Operating Procedures for SWAMP program |
QAPP Information Reference(s): |
Quality Assurance Program Plans, Quality Assurance Project Plans, and Standard Operating Procedures for the SWAMP program |
|
Line of Evidence (LOE) for Decision ID 161417, Ammonia
|
Region 1 |
Klamath River HU, Shasta River HA |
|
|
LOE ID: |
102790 |
|
Pollutant: |
Nitrogen, ammonia (Total Ammonia) |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Total |
|
Beneficial Use: |
Municipal & Domestic Supply |
|
Number of Samples: |
1 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed Shasta Tailwater Reduction data for Klamath River HU, Shasta River HA to determine beneficial use support and results are as follows: 0 of 1 samples exceeded the water quality standard for Ammonia as N. |
Data Reference: |
Water Quality Assessment Data for the 2018 solicitation cycle submitted through CEDEN for Shasta Tailwater Reduction .
|
|
SWAMP Data: |
Non-SWAMP |
|
Water Quality Objective/Criterion: |
All waters shall be maintained free of toxic substances in concentrations that are toxic to, or that produce detrimental physiological responses in human, plant, animal, or aquatic life (North Coast Regional Water Quality Control Board). |
Objective/Criterion Reference: |
Water Quality Control Plan (Basin Plan) for the North Coast Region |
|
Evaluation Guideline: |
The USEPA Health Advisory for lifetime exposure to Ammonia as a drinking water level is a concentration of 30 mg/L |
Guideline Reference: |
2012 Edition of the Drinking Water Standards and Health Advisories |
|
Spatial Representation: |
The samples were collected at 1 monitoring site(s) (105SR6355TW) |
Temporal Representation: |
The samples were collected between the dates of 2015-08-25 and 2015-08-25 |
Environmental Conditions: |
|
QAPP Information: |
Quality Assurance Project Plan for Shasta Tailwater Reduction |
QAPP Information Reference(s): |
Quality Assurance Project Plans for the Shasta River Watershed Tailwater Projects |
|
Line of Evidence (LOE) for Decision ID 161417, Ammonia
|
Region 1 |
Klamath River HU, Shasta River HA |
|
|
LOE ID: |
107291 |
|
Pollutant: |
Nitrogen, ammonia (Total Ammonia) |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Total |
|
Beneficial Use: |
Warm Freshwater Habitat |
|
Number of Samples: |
1 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP Perennial Stream Surveys data for Klamath River HU, Shasta River HA to determine beneficial use support and results are as follows: 0 of 1 samples exceeded the water quality standard for Ammonia as N. |
Data Reference: |
Water Quality Assessment Data for the 2018 solicitation cycle submitted through CEDEN for SWAMP Perennial Stream Surveys .
|
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
The Total Ammonia criterion continuous concentration (expressed as a 30-day average) to protect aquatic life in freshwater is Temperature and pH dependent, and was calculated according to the formula listed in the Aquatic Life Ambient Water Quality Criteria for Ammonia - Freshwater 2013 document. |
Objective/Criterion Reference: |
Aquatic Life Ambient Water Quality Criteria for Ammonia - Freshwater 2013 |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
The samples were collected at 1 monitoring site(s) (105PS0231) |
Temporal Representation: |
The samples were collected between the dates of 2013-08-29 and 2013-08-29 |
Environmental Conditions: |
|
QAPP Information: |
Quality Assurance Program Plan and Standard Operating Procedures for SWAMP program |
QAPP Information Reference(s): |
Quality Assurance Program Plans, Quality Assurance Project Plans, and Standard Operating Procedures for the SWAMP program |
|
Line of Evidence (LOE) for Decision ID 161417, Ammonia
|
Region 1 |
Klamath River HU, Shasta River HA |
|
|
LOE ID: |
103118 |
|
Pollutant: |
Nitrogen, ammonia (Total Ammonia) |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Total |
|
Beneficial Use: |
Warm Freshwater Habitat |
|
Number of Samples: |
4 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP RWB1 Monitoring data for Klamath River HU, Shasta River HA to determine beneficial use support and results are as follows: 0 of 4 samples exceeded the water quality standard for Ammonia as N. |
Data Reference: |
Water Quality Assessment Data for the 2018 solicitation cycle submitted through CEDEN for SWAMP RWB1 Monitoring .
|
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
The Total Ammonia criterion continuous concentration (expressed as a 30-day average) to protect aquatic life in freshwater is Temperature and pH dependent, and was calculated according to the formula listed in the Aquatic Life Ambient Water Quality Criteria for Ammonia - Freshwater 2013 document. |
Objective/Criterion Reference: |
Aquatic Life Ambient Water Quality Criteria for Ammonia - Freshwater 2013 |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
The samples were collected at 1 monitoring site(s) (105SH9274) |
Temporal Representation: |
The samples were collected between the dates of 2013-03-07 and 2013-11-20 |
Environmental Conditions: |
|
QAPP Information: |
Quality Assurance Program Plan and Standard Operating Procedures for SWAMP program |
QAPP Information Reference(s): |
Quality Assurance Program Plans, Quality Assurance Project Plans, and Standard Operating Procedures for the SWAMP program |
|
Line of Evidence (LOE) for Decision ID 161417, Ammonia
|
Region 1 |
Klamath River HU, Shasta River HA |
|
|
LOE ID: |
103115 |
|
Pollutant: |
Nitrogen, ammonia (Total Ammonia) |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Total |
|
Beneficial Use: |
Warm Freshwater Habitat |
|
Number of Samples: |
4 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP RWB1 Monitoring data for Klamath River HU, Shasta River HA to determine beneficial use support and results are as follows: 0 of 4 samples exceeded the water quality standard for Ammonia as N. |
Data Reference: |
Water Quality Assessment Data for the 2018 solicitation cycle submitted through CEDEN for SWAMP RWB1 Monitoring .
|
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
The Total Ammonia criterion continuous concentration (expressed as a 30-day average) to protect aquatic life in freshwater is Temperature and pH dependent, and was calculated according to the formula listed in the Aquatic Life Ambient Water Quality Criteria for Ammonia - Freshwater 2013 document. |
Objective/Criterion Reference: |
Aquatic Life Ambient Water Quality Criteria for Ammonia - Freshwater 2013 |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
The samples were collected at 1 monitoring site(s) (105SH1452) |
Temporal Representation: |
The samples were collected between the dates of 2013-03-06 and 2013-11-20 |
Environmental Conditions: |
|
QAPP Information: |
Quality Assurance Program Plan and Standard Operating Procedures for SWAMP program |
QAPP Information Reference(s): |
Quality Assurance Program Plans, Quality Assurance Project Plans, and Standard Operating Procedures for the SWAMP program |
|
Line of Evidence (LOE) for Decision ID 161417, Ammonia
|
Region 1 |
Klamath River HU, Shasta River HA |
|
|
LOE ID: |
323374 |
|
Pollutant: |
Nitrogen, ammonia (Total Ammonia) |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Dissolved |
|
Beneficial Use: |
Warm Freshwater Habitat |
|
Number of Samples: |
1 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP Perennial Stream Surveys data for Klamath River HU, Shasta River HA to determine beneficial use support and results are as follows: 0 of 1 samples exceeded the water quality threshold for Ammonia as N. |
Data Reference: |
Benthic, Field, Habitat, WQ from the Surface Water Ambient Monitoring Program for the 2026 Integrated Report in Region 1 |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
The Total Ammonia criterion continuous concentration (expressed as a 30-day average) to protect aquatic life in freshwater is Temperature and pH dependent, and was calculated according to the formula listed in the Aquatic Life Ambient Water Quality Criteria for AmmoniaNAFreshwater 2013 document. |
Objective/Criterion Reference: |
Aquatic Life Ambient Water Quality Criteria for Ammonia - Freshwater 2013 |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
The samples were collected at 1 monitoring site: 105PS0295 (Shasta River ~1mi above Cooley Gulch). |
Temporal Representation: |
The samples were collected between the dates of 2016-06-15 and 2016-06-15 |
Environmental Conditions: |
|
QAPP Information: |
QAPP for Surface Water Ambient Monitoring Program (SWAMP) |
QAPP Information Reference(s): |
Generic SWAMP QAPrP |
|
Line of Evidence (LOE) for Decision ID 161417, Ammonia
|
Region 1 |
Klamath River HU, Shasta River HA |
|
|
LOE ID: |
323394 |
|
Pollutant: |
Nitrogen, ammonia (Total Ammonia) |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Dissolved |
|
Beneficial Use: |
Municipal & Domestic Supply |
|
Number of Samples: |
1 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP Reference Condition Management Plan data for Klamath River HU, Shasta River HA to determine beneficial use support and results are as follows: 0 of 1 samples exceeded the water quality threshold for Ammonia as N. |
Data Reference: |
Benthic, Field, Habitat, WQ from the Surface Water Ambient Monitoring Program for the 2026 Integrated Report in Region 1 |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
All waters shall be maintained free of toxic substances in concentrations that are toxic to, or that produce detrimental physiological responses in human, plant, animal, or aquatic life (North Coast Regional Water Quality Control Board). |
Objective/Criterion Reference: |
Water Quality Control Plan (Basin Plan) for the North Coast Region |
|
Evaluation Guideline: |
The USEPA Health Advisory for lifetime exposure to Ammonia as a drinking water level is a concentration of 30 mg/L |
Guideline Reference: |
2012 Edition of the Drinking Water Standards and Health Advisories |
|
Spatial Representation: |
The samples were collected at 1 monitoring site: 105WE0592 (Eddy Creek ~0.8 miles downstream from end of 4WD road.). |
Temporal Representation: |
The samples were collected between the dates of 2015-07-13 and 2015-07-13 |
Environmental Conditions: |
|
QAPP Information: |
QAPP for Surface Water Ambient Monitoring Program (SWAMP) |
QAPP Information Reference(s): |
Generic SWAMP QAPrP |
|
Line of Evidence (LOE) for Decision ID 161417, Ammonia
|
Region 1 |
Klamath River HU, Shasta River HA |
|
|
LOE ID: |
323434 |
|
Pollutant: |
Nitrogen, ammonia (Total Ammonia) |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Dissolved |
|
Beneficial Use: |
Cold Freshwater Habitat |
|
Number of Samples: |
1 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP Reference Condition Management Plan data for Klamath River HU, Shasta River HA to determine beneficial use support and results are as follows: 0 of 1 samples exceeded the water quality threshold for Ammonia as N. |
Data Reference: |
Benthic, Field, Habitat, WQ from the Surface Water Ambient Monitoring Program for the 2026 Integrated Report in Region 1 |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
The Total Ammonia criterion continuous concentration (expressed as a 30-day average) to protect aquatic life in freshwater is Temperature and pH dependent, and was calculated according to the formula listed in the Aquatic Life Ambient Water Quality Criteria for AmmoniaNAFreshwater 2013 document. |
Objective/Criterion Reference: |
Aquatic Life Ambient Water Quality Criteria for Ammonia - Freshwater 2013 |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
The samples were collected at 1 monitoring site: 105WE0592 (Eddy Creek ~0.8 miles downstream from end of 4WD road.). |
Temporal Representation: |
The samples were collected between the dates of 2015-07-13 and 2015-07-13 |
Environmental Conditions: |
|
QAPP Information: |
QAPP for Surface Water Ambient Monitoring Program (SWAMP) |
QAPP Information Reference(s): |
Generic SWAMP QAPrP |
|
Line of Evidence (LOE) for Decision ID 161417, Ammonia
|
Region 1 |
Klamath River HU, Shasta River HA |
|
|
LOE ID: |
323354 |
|
Pollutant: |
Nitrogen, ammonia (Total Ammonia) |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Dissolved |
|
Beneficial Use: |
Warm Freshwater Habitat |
|
Number of Samples: |
1 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP Reference Condition Management Plan data for Klamath River HU, Shasta River HA to determine beneficial use support and results are as follows: 0 of 1 samples exceeded the water quality threshold for Ammonia as N. |
Data Reference: |
Benthic, Field, Habitat, WQ from the Surface Water Ambient Monitoring Program for the 2026 Integrated Report in Region 1 |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
The Total Ammonia criterion continuous concentration (expressed as a 30-day average) to protect aquatic life in freshwater is Temperature and pH dependent, and was calculated according to the formula listed in the Aquatic Life Ambient Water Quality Criteria for AmmoniaNAFreshwater 2013 document. |
Objective/Criterion Reference: |
Aquatic Life Ambient Water Quality Criteria for Ammonia - Freshwater 2013 |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
The samples were collected at 1 monitoring site: 105WE0592 (Eddy Creek ~0.8 miles downstream from end of 4WD road.). |
Temporal Representation: |
The samples were collected between the dates of 2015-07-13 and 2015-07-13 |
Environmental Conditions: |
|
QAPP Information: |
QAPP for Surface Water Ambient Monitoring Program (SWAMP) |
QAPP Information Reference(s): |
Generic SWAMP QAPrP |
|
Line of Evidence (LOE) for Decision ID 161417, Ammonia
|
Region 1 |
Klamath River HU, Shasta River HA |
|
|
LOE ID: |
323453 |
|
Pollutant: |
Nitrogen, ammonia (Total Ammonia) |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Dissolved |
|
Beneficial Use: |
Municipal & Domestic Supply |
|
Number of Samples: |
1 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP Perennial Stream Surveys data for Klamath River HU, Shasta River HA to determine beneficial use support and results are as follows: 0 of 1 samples exceeded the water quality threshold for Ammonia as N. |
Data Reference: |
Benthic, Field, Habitat, WQ from the Surface Water Ambient Monitoring Program for the 2026 Integrated Report in Region 1 |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
All waters shall be maintained free of toxic substances in concentrations that are toxic to, or that produce detrimental physiological responses in human, plant, animal, or aquatic life (North Coast Regional Water Quality Control Board). |
Objective/Criterion Reference: |
Water Quality Control Plan (Basin Plan) for the North Coast Region |
|
Evaluation Guideline: |
The USEPA Health Advisory for lifetime exposure to Ammonia as a drinking water level is a concentration of 30 mg/L |
Guideline Reference: |
2012 Edition of the Drinking Water Standards and Health Advisories |
|
Spatial Representation: |
The samples were collected at 1 monitoring site: 105PS0295 (Shasta River ~1mi above Cooley Gulch). |
Temporal Representation: |
The samples were collected between the dates of 2016-06-15 and 2016-06-15 |
Environmental Conditions: |
|
QAPP Information: |
QAPP for Surface Water Ambient Monitoring Program (SWAMP) |
QAPP Information Reference(s): |
Generic SWAMP QAPrP |
|
Line of Evidence (LOE) for Decision ID 161417, Ammonia
|
Region 1 |
Klamath River HU, Shasta River HA |
|
|
LOE ID: |
323493 |
|
Pollutant: |
Nitrogen, ammonia (Total Ammonia) |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Dissolved |
|
Beneficial Use: |
Cold Freshwater Habitat |
|
Number of Samples: |
1 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP Perennial Stream Surveys data for Klamath River HU, Shasta River HA to determine beneficial use support and results are as follows: 0 of 1 samples exceeded the water quality threshold for Ammonia as N. |
Data Reference: |
Benthic, Field, Habitat, WQ from the Surface Water Ambient Monitoring Program for the 2026 Integrated Report in Region 1 |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
The Total Ammonia criterion continuous concentration (expressed as a 30-day average) to protect aquatic life in freshwater is Temperature and pH dependent, and was calculated according to the formula listed in the Aquatic Life Ambient Water Quality Criteria for AmmoniaNAFreshwater 2013 document. |
Objective/Criterion Reference: |
Aquatic Life Ambient Water Quality Criteria for Ammonia - Freshwater 2013 |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
The samples were collected at 1 monitoring site: 105PS0295 (Shasta River ~1mi above Cooley Gulch). |
Temporal Representation: |
The samples were collected between the dates of 2016-06-15 and 2016-06-15 |
Environmental Conditions: |
|
QAPP Information: |
QAPP for Surface Water Ambient Monitoring Program (SWAMP) |
QAPP Information Reference(s): |
Generic SWAMP QAPrP |
|
Line of Evidence (LOE) for Decision ID 161417, Ammonia
|
Region 1 |
Klamath River HU, Shasta River HA |
|
|
LOE ID: |
26299 |
|
Pollutant: |
Ammonia as Nitrogen |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Total |
|
Beneficial Use: |
Cold Freshwater Habitat |
Aquatic Life Use: |
Fish Migration | Fish Spawning | Freshwater Replenishment | Preservation of Rare & Endangered Species | Warm Freshwater Habitat | Wildlife Habitat |
|
Number of Samples: |
41 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
None of the 41 ammonia as nitrogen samples collected from the Shasta River Watershed exceed the objective. The samples were collected as part of the Surface Water Ambient Water Monitoring Program (SWAMP). The data are found in the SWAMP Summary Report for the North Coast Region for Years 2000-2006 (NCRWQCB 2008). |
Data Reference: |
Surface Water Ambient Monitoring Program (SWAMP). Summary Report for the North Coast Region (RWQCB-1) for years 2000-2006. North Coast Regional Water Quality Control Board. March 2008 |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
Per the Basin Plan (NCRWQCB 2007): All waters shall be maintained free of toxic substances in concentrations that are toxic to, or that produce detrimental physiological responses in human, plant, animal, or aquatic life. |
Objective/Criterion Reference: |
Water Quality Control Plan (Basin Plan) - North Coast Region (Region 1) |
|
Evaluation Guideline: |
Per the National Recommended Water Quality Criteria (USEPA 2006): The 1-hour average concentration (acute criterion or CMC) of total ammonia nitrogen (in mg N/L) for freshwater where salmonid fish are present, which is not to be exceeded more than once every three years on average, is calculated using the following equation: CMC=0.275/(1+10^(7.204 - pH)) + 39.0/(1+10^(pH - 7.204)). |
Guideline Reference: |
National Recommended Water Quality Criteria. United States Environmental Protection Agency. Office of Water. Office of Science and Technology |
|
Spatial Representation: |
Samples were collected in the Shasta River Watershed from 5 locations as follows: (1) mainstem Shasta River near Edgewood Road (SWAMP Station ID 105SHAEDG), (2) mainstem Shasta River at Montague Grenada Road (SWAMP Station ID 105SHAMON), (3) mainstem Shasta River at Highway 263 (SWAMP Station ID 105SHA263), (4) Yreka Creek at Highway 3 (SWAMP Station ID 105YREHW3), and (5) Yreka Creek at Anderson Grade Road (SWAMP Station ID 105YREAND). Samples were collected in well-mixed flows in glides or riffles. |
Temporal Representation: |
The samples from Edgewood Road and Montague Grenada Road were collected as grab samples during 5 site visits at each site during the 2002 - 2003 fiscal years. Samples from Highway 263 were collected as grab samples during 22 site visits during the 2000 - 2006 fiscal years. Samples in Yreka Creek were collected from October 2004 to June 2005. The site visits corresponded to fall, winter, spring and early summer seasonal conditions. |
Environmental Conditions: |
There are no known environmental conditions (e.g., seasonality, land use practices, fire events, storms, etc.) that are related to these data. |
QAPP Information: |
Quality control was conducted in accordance with the SWAMP Quality Assurance Management Plan (Puckett 2002). |
QAPP Information Reference(s): |
Quality Assurance Management Plan for the State of California's Surface Water Ambient Monitoring Program. Sacramento, CA. State Water Resources Control Board. SWAMP. December 2002 (1st version)
|
|
Line of Evidence (LOE) for Decision ID 161417, Ammonia
|
Region 1 |
Klamath River HU, Shasta River HA |
|
|
LOE ID: |
115100 |
|
Pollutant: |
Nitrogen, ammonia (Total Ammonia) |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Total |
|
Beneficial Use: |
Municipal & Domestic Supply |
|
Number of Samples: |
1 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed Shasta Tailwater Reduction data for Klamath River HU, Shasta River HA to determine beneficial use support and results are as follows: 0 of 1 samples exceeded the water quality standard for Ammonia as N. |
Data Reference: |
Water Quality Assessment Data for the 2018 solicitation cycle submitted through CEDEN for Shasta Tailwater Reduction .
|
|
SWAMP Data: |
Non-SWAMP |
|
Water Quality Objective/Criterion: |
All waters shall be maintained free of toxic substances in concentrations that are toxic to, or that produce detrimental physiological responses in human, plant, animal, or aquatic life (North Coast Regional Water Quality Control Board). |
Objective/Criterion Reference: |
Water Quality Control Plan (Basin Plan) for the North Coast Region |
|
Evaluation Guideline: |
The USEPA Health Advisory for lifetime exposure to Ammonia as a drinking water level is a concentration of 30 mg/L |
Guideline Reference: |
2012 Edition of the Drinking Water Standards and Health Advisories |
|
Spatial Representation: |
The samples were collected at 1 monitoring site(s) (105SR6074_2TW) |
Temporal Representation: |
The samples were collected between the dates of 2015-08-24 and 2015-08-24 |
Environmental Conditions: |
|
QAPP Information: |
Quality Assurance Project Plan for Shasta Tailwater Reduction |
QAPP Information Reference(s): |
Quality Assurance Project Plans for the Shasta River Watershed Tailwater Projects |
|
Line of Evidence (LOE) for Decision ID 161417, Ammonia
|
Region 1 |
Klamath River HU, Shasta River HA |
|
|
LOE ID: |
34537 |
|
Pollutant: |
Nitrogen, ammonia (Total Ammonia) |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Total |
|
Beneficial Use: |
Fish Spawning |
|
Number of Samples: |
4 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
None of the samples exceed the water USEPA Temperature and pH-Dependent values of the CCC (Chronic Criterion) for Fish Early Life Stages Present for ammonia. 2 of the 4 data are reported as non-detect limits. These non-detect limits are less than or equal to the water quality standard, the value will be considered as meeting the water quality standard, objective, criterion, or evaluation guideline. |
Data Reference: |
RWB1 Trend Maintenance Periods FYs 2007 2008 |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
Water Quality Control Plan, North Coast Region (NCRWQCB 2011): All waters shall be maintained free of toxic substances in concentrations that are toxic to, or that produce detrimental physiological responses in human, plant, animal, or aquatic life. |
Objective/Criterion Reference: |
Water Quality Control Plan (Basin Plan) for the North Coast Region |
|
Evaluation Guideline: |
Update of Ambient Water Quality Criteria for Ammonia (USEPA 1999): Where salmonids and fish early life stages are present, the 30-day average concentration (criterion continuous concentration or CCC) of total ammonia (as mg N/L) in freshwater are not to be exceeded more than once every three years on average. The CCC values are based on pH, temperature, and the presence of early life stages of fish. The CCC formula is found on p.83 and the table of CCC values are found on p.87. |
Guideline Reference: |
1999 Update of Ambient Water Quality Criteria for Ammonia |
|
Spatial Representation: |
Sample was collected at 105SHAEDG (Klamath River HU, Shasta River HA). |
Temporal Representation: |
Samples collected between 11/15/2007 and 2/27/2008. |
Environmental Conditions: |
|
QAPP Information: |
SWAMP QAPP (2008) was followed. |
QAPP Information Reference(s): |
Surface Water Ambient Monitoring Program Quality Assurance Program Plan |
|
Line of Evidence (LOE) for Decision ID 161417, Ammonia
|
Region 1 |
Klamath River HU, Shasta River HA |
|
|
LOE ID: |
34536 |
|
Pollutant: |
Nitrogen, ammonia (Total Ammonia) |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Total |
|
Beneficial Use: |
Fish Spawning |
|
Number of Samples: |
4 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
None of the samples exceed the water USEPA Temperature and pH-Dependent values of the CCC (Chronic Criterion) for Fish Early Life Stages Present for ammonia. 1 of the 4 data are reported as non-detect limits. These non-detect limits are less than or equal to the water quality standard, the value will be considered as meeting the water quality standard, objective, criterion, or evaluation guideline. |
Data Reference: |
RWB1 Trend Maintenance Periods FYs 2007 2008 |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
Water Quality Control Plan, North Coast Region (NCRWQCB 2011): All waters shall be maintained free of toxic substances in concentrations that are toxic to, or that produce detrimental physiological responses in human, plant, animal, or aquatic life. |
Objective/Criterion Reference: |
Water Quality Control Plan (Basin Plan) for the North Coast Region |
|
Evaluation Guideline: |
Update of Ambient Water Quality Criteria for Ammonia (USEPA 1999): Where salmonids and fish early life stages are present, the 30-day average concentration (criterion continuous concentration or CCC) of total ammonia (as mg N/L) in freshwater are not to be exceeded more than once every three years on average. The CCC values are based on pH, temperature, and the presence of early life stages of fish. The CCC formula is found on p.83 and the table of CCC values are found on p.87. |
Guideline Reference: |
1999 Update of Ambient Water Quality Criteria for Ammonia |
|
Spatial Representation: |
Sample was collected at 105SHA263 (Shasta River at Hwy 263). |
Temporal Representation: |
Samples collected between 11/15/2007 and 2/27/2008. |
Environmental Conditions: |
|
QAPP Information: |
SWAMP QAPP (2008) was followed. |
QAPP Information Reference(s): |
Surface Water Ambient Monitoring Program Quality Assurance Program Plan |
|
Line of Evidence (LOE) for Decision ID 161417, Ammonia
|
Region 1 |
Klamath River HU, Shasta River HA |
|
|
LOE ID: |
34554 |
|
Pollutant: |
Nitrogen, ammonia (Total Ammonia) |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Total |
|
Beneficial Use: |
Fish Spawning |
|
Number of Samples: |
1 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
The sample does not exceed the water USEPA Temperature and pH-Dependent values of the CCC (Chronic Criterion) for Fish Early Life Stages Present for ammonia. The datum is reported as a non-detect limit. The non-detect limit is less than or equal to the water quality standard, the value will be considered as meeting the water quality standard, objective, criterion, or evaluation guideline. |
Data Reference: |
Statewide Perennial Streams Assessment 2008 |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
Water Quality Control Plan, North Coast Region (NCRWQCB 2011): All waters shall be maintained free of toxic substances in concentrations that are toxic to, or that produce detrimental physiological responses in human, plant, animal, or aquatic life. |
Objective/Criterion Reference: |
Water Quality Control Plan (Basin Plan) for the North Coast Region |
|
Evaluation Guideline: |
Update of Ambient Water Quality Criteria for Ammonia (USEPA 1999): Where salmonids and fish early life stages are present, the 30-day average concentration (criterion continuous concentration or CCC) of total ammonia (as mg N/L) in freshwater are not to be exceeded more than once every three years on average. The CCC values are based on pH, temperature, and the presence of early life stages of fish. The CCC formula is found on p.83 and the table of CCC values are found on p.87. |
Guideline Reference: |
1999 Update of Ambient Water Quality Criteria for Ammonia |
|
Spatial Representation: |
Samples were collected at 105PS0188 (Evans Ditch). |
Temporal Representation: |
The sample was collected on 8/26/2008. |
Environmental Conditions: |
|
QAPP Information: |
SWAMP QAPP (2008) was followed. |
QAPP Information Reference(s): |
Surface Water Ambient Monitoring Program Quality Assurance Program Plan |
|
Line of Evidence (LOE) for Decision ID 161417, Ammonia
|
Region 1 |
Klamath River HU, Shasta River HA |
|
|
LOE ID: |
115306 |
|
Pollutant: |
Nitrogen, ammonia (Total Ammonia) |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Total |
|
Beneficial Use: |
Cold Freshwater Habitat |
|
Number of Samples: |
1 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP Perennial Stream Surveys data for Klamath River HU, Shasta River HA to determine beneficial use support and results are as follows: 0 of 1 samples exceeded the water quality standard for Ammonia as N. |
Data Reference: |
Water Quality Assessment Data for the 2018 solicitation cycle submitted through CEDEN for SWAMP Perennial Stream Surveys .
|
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
The Total Ammonia criterion continuous concentration (expressed as a 30-day average) to protect aquatic life in freshwater is Temperature and pH dependent, and was calculated according to the formula listed in the Aquatic Life Ambient Water Quality Criteria for Ammonia - Freshwater 2013 document. |
Objective/Criterion Reference: |
Aquatic Life Ambient Water Quality Criteria for Ammonia - Freshwater 2013 |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
The samples were collected at 1 monitoring site(s) (105PS0231) |
Temporal Representation: |
The samples were collected between the dates of 2013-08-29 and 2013-08-29 |
Environmental Conditions: |
|
QAPP Information: |
Quality Assurance Program Plan and Standard Operating Procedures for SWAMP program |
QAPP Information Reference(s): |
Quality Assurance Program Plans, Quality Assurance Project Plans, and Standard Operating Procedures for the SWAMP program |
|
Line of Evidence (LOE) for Decision ID 161417, Ammonia
|
Region 1 |
Klamath River HU, Shasta River HA |
|
|
LOE ID: |
103113 |
|
Pollutant: |
Nitrogen, ammonia (Total Ammonia) |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Total |
|
Beneficial Use: |
Cold Freshwater Habitat |
|
Number of Samples: |
4 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP RWB1 Monitoring data for Klamath River HU, Shasta River HA to determine beneficial use support and results are as follows: 0 of 4 samples exceeded the water quality standard for Ammonia as N. |
Data Reference: |
Water Quality Assessment Data for the 2018 solicitation cycle submitted through CEDEN for SWAMP RWB1 Monitoring .
|
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
The Total Ammonia criterion continuous concentration (expressed as a 30-day average) to protect aquatic life in freshwater is Temperature and pH dependent, and was calculated according to the formula listed in the Aquatic Life Ambient Water Quality Criteria for Ammonia - Freshwater 2013 document. |
Objective/Criterion Reference: |
Aquatic Life Ambient Water Quality Criteria for Ammonia - Freshwater 2013 |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
The samples were collected at 1 monitoring site(s) (105SH1452) |
Temporal Representation: |
The samples were collected between the dates of 2013-03-06 and 2013-11-20 |
Environmental Conditions: |
|
QAPP Information: |
Quality Assurance Program Plan and Standard Operating Procedures for SWAMP program |
QAPP Information Reference(s): |
Quality Assurance Program Plans, Quality Assurance Project Plans, and Standard Operating Procedures for the SWAMP program |
|
Line of Evidence (LOE) for Decision ID 161417, Ammonia
|
Region 1 |
Klamath River HU, Shasta River HA |
|
|
LOE ID: |
103116 |
|
Pollutant: |
Nitrogen, ammonia (Total Ammonia) |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Total |
|
Beneficial Use: |
Cold Freshwater Habitat |
|
Number of Samples: |
4 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP RWB1 Monitoring data for Klamath River HU, Shasta River HA to determine beneficial use support and results are as follows: 0 of 4 samples exceeded the water quality standard for Ammonia as N. |
Data Reference: |
Water Quality Assessment Data for the 2018 solicitation cycle submitted through CEDEN for SWAMP RWB1 Monitoring .
|
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
The Total Ammonia criterion continuous concentration (expressed as a 30-day average) to protect aquatic life in freshwater is Temperature and pH dependent, and was calculated according to the formula listed in the Aquatic Life Ambient Water Quality Criteria for Ammonia - Freshwater 2013 document. |
Objective/Criterion Reference: |
Aquatic Life Ambient Water Quality Criteria for Ammonia - Freshwater 2013 |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
The samples were collected at 1 monitoring site(s) (105SH9274) |
Temporal Representation: |
The samples were collected between the dates of 2013-03-07 and 2013-11-20 |
Environmental Conditions: |
|
QAPP Information: |
Quality Assurance Program Plan and Standard Operating Procedures for SWAMP program |
QAPP Information Reference(s): |
Quality Assurance Program Plans, Quality Assurance Project Plans, and Standard Operating Procedures for the SWAMP program |
|
Line of Evidence (LOE) for Decision ID 100736, Arsenic
|
Region 1 |
Klamath River HU, Shasta River HA |
|
|
LOE ID: |
103133 |
|
Pollutant: |
Arsenic |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Total |
|
Beneficial Use: |
Cold Freshwater Habitat |
|
Number of Samples: |
5 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP RWB1 Monitoring data for Klamath River HU, Shasta River HA to determine beneficial use support and results are as follows: 0 of 5 samples exceeded the water quality standard for Arsenic. |
Data Reference: |
Water Quality Assessment Data for the 2018 solicitation cycle submitted through CEDEN for SWAMP RWB1 Monitoring .
|
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
The dissolved arsenic criterion continuous concentration (expressed as a 4-day average) to protect aquatic life in freshwater for dissolved arsenic is 150 ug/L (California Toxics Rule, 2000). |
Objective/Criterion Reference: |
Water Quality Standards 2000. Establishment of numeric criteria for priority toxic pollutants for the State of California: Rules and regulations. Federal Register Vol. 65, No. 97. Washington, D.C.: Environmental Protection Agency |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
The samples were collected at 1 monitoring site(s) (105SH9274) |
Temporal Representation: |
The samples were collected between the dates of 2013-03-07 and 2013-11-20 |
Environmental Conditions: |
|
QAPP Information: |
Quality Assurance Program Plan and Standard Operating Procedures for SWAMP program |
QAPP Information Reference(s): |
Quality Assurance Program Plans, Quality Assurance Project Plans, and Standard Operating Procedures for the SWAMP program |
|
Line of Evidence (LOE) for Decision ID 100736, Arsenic
|
Region 1 |
Klamath River HU, Shasta River HA |
|
|
LOE ID: |
103129 |
|
Pollutant: |
Arsenic |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Total |
|
Beneficial Use: |
Cold Freshwater Habitat |
|
Number of Samples: |
5 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP RWB1 Monitoring data for Klamath River HU, Shasta River HA to determine beneficial use support and results are as follows: 0 of 5 samples exceeded the water quality standard for Arsenic. |
Data Reference: |
Water Quality Assessment Data for the 2018 solicitation cycle submitted through CEDEN for SWAMP RWB1 Monitoring .
|
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
The dissolved arsenic criterion continuous concentration (expressed as a 4-day average) to protect aquatic life in freshwater for dissolved arsenic is 150 ug/L (California Toxics Rule, 2000). |
Objective/Criterion Reference: |
Water Quality Standards 2000. Establishment of numeric criteria for priority toxic pollutants for the State of California: Rules and regulations. Federal Register Vol. 65, No. 97. Washington, D.C.: Environmental Protection Agency |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
The samples were collected at 1 monitoring site(s) (105SH1452) |
Temporal Representation: |
The samples were collected between the dates of 2013-03-06 and 2013-11-20 |
Environmental Conditions: |
|
QAPP Information: |
Quality Assurance Program Plan and Standard Operating Procedures for SWAMP program |
QAPP Information Reference(s): |
Quality Assurance Program Plans, Quality Assurance Project Plans, and Standard Operating Procedures for the SWAMP program |
|
Line of Evidence (LOE) for Decision ID 100736, Arsenic
|
Region 1 |
Klamath River HU, Shasta River HA |
|
|
LOE ID: |
123185 |
|
Pollutant: |
Arsenic |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Total |
|
Beneficial Use: |
Municipal & Domestic Supply |
|
Number of Samples: |
3 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
State Water Board staff re-assessed SWAMP data for Klamath River HU, Shasta River HA to determine beneficial use support and results are as follows: 0 of 3 samples exceed the criterion for Arsenic, Total. This LOE re-assesses data from LOE 21509 from the 2010 Integrated Report. Data were re-assessed in order to (1) update the numeric objective, and (2) evaluate these data in their own LOE, instead of being evaluated in the same LOE as other metals data. |
Data Reference: |
Surface Water Ambient Monitoring Program (SWAMP). Summary Report for the North Coast Region (RWQCB-1) for years 2000-2006. North Coast Regional Water Quality Control Board. March 2008 |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
Water Quality Control Plan, North Coast Region (NCRWQCB 2011): Waters designated for use as domestic or municipal supply (MUN) shall not contain concentrations of chemical constituents in excess of the limits specified in California Code of Regulations, Title 22, Chapter 15. The maximum contaminant level listed in Table 64431-A for arsenic is 0.010 mg/L. |
Objective/Criterion Reference: |
Water Quality Control Plan (Basin Plan) for the North Coast Region |
Objective/Criterion Reference: |
Maximum Contaminant Levels for organic and inorganic chemicals. CCR Title 22 |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
Data for this line of evidence for Klamath River HU, Shasta River HA was collected at 1 monitoring site [ Yreka Creek at Highway 3 - 105YREHW3] |
Temporal Representation: |
Data was collected over the time period 10/21/2004-6/20/2005. |
Environmental Conditions: |
There are no known environmental conditions (e.g., seasonality, land use practices, fire events, storms, etc.) that are related to these data. |
QAPP Information: |
Quality control was conducted in accordance with the SWAMP Quality Assurance Management Plan (SWAMP 2002). |
QAPP Information Reference(s): |
Quality Assurance Management Plan for the State of California's Surface Water Ambient Monitoring Program. Sacramento, CA. State Water Resources Control Board. SWAMP. December 2002 (1st version)
|
|
Line of Evidence (LOE) for Decision ID 100736, Arsenic
|
Region 1 |
Klamath River HU, Shasta River HA |
|
|
LOE ID: |
123184 |
|
Pollutant: |
Arsenic |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Total |
|
Beneficial Use: |
Municipal & Domestic Supply |
|
Number of Samples: |
7 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
State Water Board staff re-assessed SWAMP data for Klamath River HU, Shasta River HA to determine beneficial use support and results are as follows: 0 of 7 samples exceed the criterion for Arsenic, Total. This LOE re-assesses data from LOE 21509 from the 2010 Integrated Report. Data were re-assessed in order to (1) update the numeric objective, and (2) evaluate these data in their own LOE, instead of being evaluated in the same LOE as other metals data. |
Data Reference: |
Surface Water Ambient Monitoring Program (SWAMP). Summary Report for the North Coast Region (RWQCB-1) for years 2000-2006. North Coast Regional Water Quality Control Board. March 2008 |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
Water Quality Control Plan, North Coast Region (NCRWQCB 2011): Waters designated for use as domestic or municipal supply (MUN) shall not contain concentrations of chemical constituents in excess of the limits specified in California Code of Regulations, Title 22, Chapter 15. The maximum contaminant level listed in Table 64431-A for arsenic is 0.010 mg/L. |
Objective/Criterion Reference: |
Water Quality Control Plan (Basin Plan) for the North Coast Region |
Objective/Criterion Reference: |
Maximum Contaminant Levels for organic and inorganic chemicals. CCR Title 22 |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
Data for this line of evidence for Klamath River HU, Shasta River HA was collected at 1 monitoring site [ Yreka Creek at Anderson Rd - 105YREAND] |
Temporal Representation: |
Data was collected over the time period 10/9/2002-6/20/2005. |
Environmental Conditions: |
There are no known environmental conditions (e.g., seasonality, land use practices, fire events, storms, etc.) that are related to these data. |
QAPP Information: |
Quality control was conducted in accordance with the SWAMP Quality Assurance Management Plan (SWAMP 2002). |
QAPP Information Reference(s): |
Quality Assurance Management Plan for the State of California's Surface Water Ambient Monitoring Program. Sacramento, CA. State Water Resources Control Board. SWAMP. December 2002 (1st version)
|
|
Line of Evidence (LOE) for Decision ID 100736, Arsenic
|
Region 1 |
Klamath River HU, Shasta River HA |
|
|
LOE ID: |
123183 |
|
Pollutant: |
Arsenic |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Total |
|
Beneficial Use: |
Municipal & Domestic Supply |
|
Number of Samples: |
5 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
State Water Board staff re-assessed SWAMP data for Klamath River HU, Shasta River HA to determine beneficial use support and results are as follows: 0 of 5 samples exceed the criterion for Arsenic, Total. This LOE re-assesses data from LOE 21509 from the 2010 Integrated Report. Data were re-assessed in order to (1) update the numeric objective, and (2) evaluate these data in their own LOE, instead of being evaluated in the same LOE as other metals data. |
Data Reference: |
Surface Water Ambient Monitoring Program (SWAMP). Summary Report for the North Coast Region (RWQCB-1) for years 2000-2006. North Coast Regional Water Quality Control Board. March 2008 |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
Water Quality Control Plan, North Coast Region (NCRWQCB 2011): Waters designated for use as domestic or municipal supply (MUN) shall not contain concentrations of chemical constituents in excess of the limits specified in California Code of Regulations, Title 22, Chapter 15. The maximum contaminant level listed in Table 64431-A for arsenic is 0.010 mg/L. |
Objective/Criterion Reference: |
Water Quality Control Plan (Basin Plan) for the North Coast Region |
Objective/Criterion Reference: |
Maximum Contaminant Levels for organic and inorganic chemicals. CCR Title 22 |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
Data for this line of evidence for Klamath River HU, Shasta River HA was collected at 1 monitoring site [ Shasta River near Edgewood - 105SH9274] |
Temporal Representation: |
Data was collected over the time period 10/7/2002-6/19/2003. |
Environmental Conditions: |
There are no known environmental conditions (e.g., seasonality, land use practices, fire events, storms, etc.) that are related to these data. |
QAPP Information: |
Quality control was conducted in accordance with the SWAMP Quality Assurance Management Plan (SWAMP 2002). |
QAPP Information Reference(s): |
Quality Assurance Management Plan for the State of California's Surface Water Ambient Monitoring Program. Sacramento, CA. State Water Resources Control Board. SWAMP. December 2002 (1st version)
|
|
Line of Evidence (LOE) for Decision ID 100736, Arsenic
|
Region 1 |
Klamath River HU, Shasta River HA |
|
|
LOE ID: |
123173 |
|
Pollutant: |
Arsenic |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Total |
|
Beneficial Use: |
Municipal & Domestic Supply |
|
Number of Samples: |
5 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
State Water Board staff re-assessed SWAMP data for Klamath River HU, Shasta River HA to determine beneficial use support and results are as follows: 0 of 5 samples exceed the criterion for Arsenic, Total. This LOE re-assesses data from LOE 21509 from the 2010 Integrated Report. Data were re-assessed in order to (1) update the numeric objective, and (2) evaluate these data in their own LOE, instead of being evaluated in the same LOE as other metals data. |
Data Reference: |
Surface Water Ambient Monitoring Program (SWAMP). Summary Report for the North Coast Region (RWQCB-1) for years 2000-2006. North Coast Regional Water Quality Control Board. March 2008 |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
Water Quality Control Plan, North Coast Region (NCRWQCB 2011): Waters designated for use as domestic or municipal supply (MUN) shall not contain concentrations of chemical constituents in excess of the limits specified in California Code of Regulations, Title 22, Chapter 15. The maximum contaminant level listed in Table 64431-A for arsenic is 0.010 mg/L. |
Objective/Criterion Reference: |
Water Quality Control Plan (Basin Plan) for the North Coast Region |
Objective/Criterion Reference: |
Maximum Contaminant Levels for organic and inorganic chemicals. CCR Title 22 |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
Data for this line of evidence for Klamath River HU, Shasta River HA was collected at 1 monitoring site [ Shasta River at Montague - 105SHAMON] |
Temporal Representation: |
Data was collected over the time period 10/7/2002-6/19/2003. |
Environmental Conditions: |
There are no known environmental conditions (e.g., seasonality, land use practices, fire events, storms, etc.) that are related to these data. |
QAPP Information: |
Quality control was conducted in accordance with the SWAMP Quality Assurance Management Plan (SWAMP 2002). |
QAPP Information Reference(s): |
Quality Assurance Management Plan for the State of California's Surface Water Ambient Monitoring Program. Sacramento, CA. State Water Resources Control Board. SWAMP. December 2002 (1st version)
|
|
Line of Evidence (LOE) for Decision ID 100736, Arsenic
|
Region 1 |
Klamath River HU, Shasta River HA |
|
|
LOE ID: |
103132 |
|
Pollutant: |
Arsenic |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Total |
|
Beneficial Use: |
Warm Freshwater Habitat |
|
Number of Samples: |
5 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP RWB1 Monitoring data for Klamath River HU, Shasta River HA to determine beneficial use support and results are as follows: 0 of 5 samples exceeded the water quality standard for Arsenic. |
Data Reference: |
Water Quality Assessment Data for the 2018 solicitation cycle submitted through CEDEN for SWAMP RWB1 Monitoring .
|
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
The dissolved arsenic criterion continuous concentration (expressed as a 4-day average) to protect aquatic life in freshwater for dissolved arsenic is 150 ug/L (California Toxics Rule, 2000). |
Objective/Criterion Reference: |
Water Quality Standards 2000. Establishment of numeric criteria for priority toxic pollutants for the State of California: Rules and regulations. Federal Register Vol. 65, No. 97. Washington, D.C.: Environmental Protection Agency |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
The samples were collected at 1 monitoring site(s) (105SH1452) |
Temporal Representation: |
The samples were collected between the dates of 2013-03-06 and 2013-11-20 |
Environmental Conditions: |
|
QAPP Information: |
Quality Assurance Program Plan and Standard Operating Procedures for SWAMP program |
QAPP Information Reference(s): |
Quality Assurance Program Plans, Quality Assurance Project Plans, and Standard Operating Procedures for the SWAMP program |
|
Line of Evidence (LOE) for Decision ID 100736, Arsenic
|
Region 1 |
Klamath River HU, Shasta River HA |
|
|
LOE ID: |
41405 |
|
Pollutant: |
Arsenic |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Total |
|
Beneficial Use: |
Municipal & Domestic Supply |
|
Number of Samples: |
4 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP data for Klamath River HU, Shasta River HA to determine beneficial use support and results are as follows: 0 of 4 samples exceed the criterion for Arsenic. |
Data Reference: |
RWB1 Trend Maintenance Periods FYs 2007 2008 |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
Water Quality Control Plan, North Coast Region (NCRWQCB 2011): Waters designated for use as domestic or municipal supply (MUN) shall not contain concentrations of chemical constituents in excess of the limits specified in California Code of Regulations, Title 22, Chapter 15. The maximum contaminant level listed in Table 64431-A for arsenic is 0.010 mg/L. |
Objective/Criterion Reference: |
Maximum Contaminant Levels for organic and inorganic chemicals. CCR Title 22 |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
Data for this line of evidence for Klamath River HU, Shasta River HA was collected at 1 monitoring site [ Shasta River at Hwy 263 - 105SHA263] |
Temporal Representation: |
Data was collected over the time period 11/15/2007-7/16/2008. |
Environmental Conditions: |
Staff is not aware of any special conditions that might affect interpretation of the data. |
QAPP Information: |
The SWAMP QAPP (2008) was followed. |
QAPP Information Reference(s): |
Surface Water Ambient Monitoring Program Quality Assurance Program Plan |
|
Line of Evidence (LOE) for Decision ID 100736, Arsenic
|
Region 1 |
Klamath River HU, Shasta River HA |
|
|
LOE ID: |
103134 |
|
Pollutant: |
Arsenic |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Total |
|
Beneficial Use: |
Municipal & Domestic Supply |
|
Number of Samples: |
5 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP RWB1 Monitoring data for Klamath River HU, Shasta River HA to determine beneficial use support and results are as follows: 0 of 5 samples exceeded the water quality standard for Arsenic. |
Data Reference: |
Water Quality Assessment Data for the 2018 solicitation cycle submitted through CEDEN for SWAMP RWB1 Monitoring .
|
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
Water Quality Control Plan, North Coast Region (NCRWQCB 2018): Waters designated for use as domestic or municipal supply (MUN) shall not contain concentrations of chemical constituents in excess of the limits specified in California Code of Regulations, Title 22, Chapter 15. The maximum contaminant level listed in Table 64431-A for arsenic is 0.010 mg/L. |
Objective/Criterion Reference: |
Water Quality Control Plan (Basin Plan) for the North Coast Region |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
The samples were collected at 1 monitoring site(s) (105SH9274) |
Temporal Representation: |
The samples were collected between the dates of 2013-03-07 and 2013-11-20 |
Environmental Conditions: |
|
QAPP Information: |
Quality Assurance Program Plan and Standard Operating Procedures for SWAMP program |
QAPP Information Reference(s): |
Quality Assurance Program Plans, Quality Assurance Project Plans, and Standard Operating Procedures for the SWAMP program |
|
Line of Evidence (LOE) for Decision ID 100736, Arsenic
|
Region 1 |
Klamath River HU, Shasta River HA |
|
|
LOE ID: |
103131 |
|
Pollutant: |
Arsenic |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Total |
|
Beneficial Use: |
Municipal & Domestic Supply |
|
Number of Samples: |
5 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP RWB1 Monitoring data for Klamath River HU, Shasta River HA to determine beneficial use support and results are as follows: 0 of 5 samples exceeded the water quality standard for Arsenic. |
Data Reference: |
Water Quality Assessment Data for the 2018 solicitation cycle submitted through CEDEN for SWAMP RWB1 Monitoring .
|
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
Water Quality Control Plan, North Coast Region (NCRWQCB 2018): Waters designated for use as domestic or municipal supply (MUN) shall not contain concentrations of chemical constituents in excess of the limits specified in California Code of Regulations, Title 22, Chapter 15. The maximum contaminant level listed in Table 64431-A for arsenic is 0.010 mg/L. |
Objective/Criterion Reference: |
Water Quality Control Plan (Basin Plan) for the North Coast Region |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
The samples were collected at 1 monitoring site(s) (105SH1452) |
Temporal Representation: |
The samples were collected between the dates of 2013-03-06 and 2013-11-20 |
Environmental Conditions: |
|
QAPP Information: |
Quality Assurance Program Plan and Standard Operating Procedures for SWAMP program |
QAPP Information Reference(s): |
Quality Assurance Program Plans, Quality Assurance Project Plans, and Standard Operating Procedures for the SWAMP program |
|
Line of Evidence (LOE) for Decision ID 100736, Arsenic
|
Region 1 |
Klamath River HU, Shasta River HA |
|
|
LOE ID: |
123172 |
|
Pollutant: |
Arsenic |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Total |
|
Beneficial Use: |
Municipal & Domestic Supply |
|
Number of Samples: |
5 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
State Water Board staff re-assessed SWAMP data for Klamath River HU, Shasta River HA to determine beneficial use support and results are as follows: 0 of 5 samples exceed the criterion for Arsenic, Total. This LOE re-assesses data from LOE 21509 from the 2010 Integrated Report. Data were re-assessed in order to (1) update the numeric objective, and (2) evaluate these data in their own LOE, instead of being evaluated in the same LOE as other metals data. |
Data Reference: |
Surface Water Ambient Monitoring Program (SWAMP). Summary Report for the North Coast Region (RWQCB-1) for years 2000-2006. North Coast Regional Water Quality Control Board. March 2008 |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
Water Quality Control Plan, North Coast Region (NCRWQCB 2011): Waters designated for use as domestic or municipal supply (MUN) shall not contain concentrations of chemical constituents in excess of the limits specified in California Code of Regulations, Title 22, Chapter 15. The maximum contaminant level listed in Table 64431-A for arsenic is 0.010 mg/L. |
Objective/Criterion Reference: |
Water Quality Control Plan (Basin Plan) for the North Coast Region |
Objective/Criterion Reference: |
Maximum Contaminant Levels for organic and inorganic chemicals. CCR Title 22 |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
Data for this line of evidence for Klamath River HU, Shasta River HA was collected at 1 monitoring site [ Shasta River at Hwy 263 - 105SH1452] |
Temporal Representation: |
Data was collected over the time period 2/27/2002-11/16/2006. |
Environmental Conditions: |
There are no known environmental conditions (e.g., seasonality, land use practices, fire events, storms, etc.) that are related to these data. |
QAPP Information: |
Quality control was conducted in accordance with the SWAMP Quality Assurance Management Plan (SWAMP 2002). |
QAPP Information Reference(s): |
Quality Assurance Management Plan for the State of California's Surface Water Ambient Monitoring Program. Sacramento, CA. State Water Resources Control Board. SWAMP. December 2002 (1st version)
|
|
Line of Evidence (LOE) for Decision ID 100736, Arsenic
|
Region 1 |
Klamath River HU, Shasta River HA |
|
|
LOE ID: |
103135 |
|
Pollutant: |
Arsenic |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Total |
|
Beneficial Use: |
Warm Freshwater Habitat |
|
Number of Samples: |
5 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP RWB1 Monitoring data for Klamath River HU, Shasta River HA to determine beneficial use support and results are as follows: 0 of 5 samples exceeded the water quality standard for Arsenic. |
Data Reference: |
Water Quality Assessment Data for the 2018 solicitation cycle submitted through CEDEN for SWAMP RWB1 Monitoring .
|
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
The dissolved arsenic criterion continuous concentration (expressed as a 4-day average) to protect aquatic life in freshwater for dissolved arsenic is 150 ug/L (California Toxics Rule, 2000). |
Objective/Criterion Reference: |
Water Quality Standards 2000. Establishment of numeric criteria for priority toxic pollutants for the State of California: Rules and regulations. Federal Register Vol. 65, No. 97. Washington, D.C.: Environmental Protection Agency |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
The samples were collected at 1 monitoring site(s) (105SH9274) |
Temporal Representation: |
The samples were collected between the dates of 2013-03-07 and 2013-11-20 |
Environmental Conditions: |
|
QAPP Information: |
Quality Assurance Program Plan and Standard Operating Procedures for SWAMP program |
QAPP Information Reference(s): |
Quality Assurance Program Plans, Quality Assurance Project Plans, and Standard Operating Procedures for the SWAMP program |
|
Line of Evidence (LOE) for Decision ID 100736, Arsenic
|
Region 1 |
Klamath River HU, Shasta River HA |
|
|
LOE ID: |
41402 |
|
Pollutant: |
Arsenic |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Total |
|
Beneficial Use: |
Municipal & Domestic Supply |
|
Number of Samples: |
4 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP data for Klamath River HU, Shasta River HA to determine beneficial use support and results are as follows: 0 of 4 samples exceed the criterion for Arsenic. |
Data Reference: |
RWB1 Trend Maintenance Periods FYs 2007 2008 |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
Water Quality Control Plan, North Coast Region (NCRWQCB 2011): Waters designated for use as domestic or municipal supply (MUN) shall not contain concentrations of chemical constituents in excess of the limits specified in California Code of Regulations, Title 22, Chapter 15. The maximum contaminant level listed in Table 64431-A for arsenic is 0.010 mg/L. |
Objective/Criterion Reference: |
Maximum Contaminant Levels for organic and inorganic chemicals. CCR Title 22 |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
Data for this line of evidence for Klamath River HU, Shasta River HA was collected at 1 monitoring site [ Shasta River near Edgewood - 105SHAEDG] |
Temporal Representation: |
Data was collected over the time period 11/15/2007-7/16/2008. |
Environmental Conditions: |
Staff is not aware of any special conditions that might affect interpretation of the data. |
QAPP Information: |
The SWAMP QAPP (2008) was followed. |
QAPP Information Reference(s): |
Surface Water Ambient Monitoring Program Quality Assurance Program Plan |
|
Line of Evidence (LOE) for Decision ID 169748, Atrazine
|
Region 1 |
Klamath River HU, Shasta River HA |
|
|
LOE ID: |
41344 |
|
Pollutant: |
Atrazine |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Total |
|
Beneficial Use: |
Municipal & Domestic Supply |
|
Number of Samples: |
3 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP data for Klamath River HU, Shasta River HA to determine beneficial use support and results are as follows: 0 of 3 samples exceed the criterion for Atrazine. |
Data Reference: |
RWB1 Trend Maintenance Periods FYs 2007 2008 |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
Water Quality Control Plan, North Coast Region (NCRWQCB 2011): Waters designated for use as domestic or municipal supply (MUN) shall not contain concentrations of chemical constituents in excess of the limits specified in California Code of Regulations, Title 22, Chapter 15. The maximum contaminant level listed in Table 64431-A for atrazine is 1 ug/L. |
Objective/Criterion Reference: |
Maximum Contaminant Levels for organic and inorganic chemicals. CCR Title 22 |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
Data for this line of evidence for Klamath River HU, Shasta River HA was collected at 1 monitoring site [ Shasta River at Hwy 263 - 105SHA263] |
Temporal Representation: |
Data was collected over the time period 11/15/2007-7/16/2008. |
Environmental Conditions: |
Staff is not aware of any special conditions that might affect interpretation of the data. |
QAPP Information: |
The SWAMP QAPP (2008) was followed. |
QAPP Information Reference(s): |
Surface Water Ambient Monitoring Program Quality Assurance Program Plan |
|
Line of Evidence (LOE) for Decision ID 169748, Atrazine
|
Region 1 |
Klamath River HU, Shasta River HA |
|
|
LOE ID: |
103138 |
|
Pollutant: |
Atrazine |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Total |
|
Beneficial Use: |
Warm Freshwater Habitat |
|
Number of Samples: |
3 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP RWB1 Monitoring data for Klamath River HU, Shasta River HA to determine beneficial use support and results are as follows: 0 of 3 samples exceeded the water quality standard for Atrazine. |
Data Reference: |
Water Quality Assessment Data for the 2018 solicitation cycle submitted through CEDEN for SWAMP RWB1 Monitoring .
|
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
All waters shall be maintained free of toxic substances in concentrations which are toxic to, or which produce detrimental physiological responses in, human, plant, animal, or aquatic life. (Basin Plan). |
Objective/Criterion Reference: |
Water Quality Control Plan (Basin Plan) for the North Coast Region |
|
Evaluation Guideline: |
The evaluation guideline for Atrazine is the USEPA Aquatic Life Benchmark of < 1 ug/L for a nonvascular plant (acute). The benchmark was derived from a \less-than\" value (for example, <1,500) and may underestimate toxicity." |
Guideline Reference: |
OPP Aquatic Life Benchmarks |
|
Spatial Representation: |
The samples were collected at 1 monitoring site(s) (105SH1452) |
Temporal Representation: |
The samples were collected between the dates of 2013-03-06 and 2013-11-20 |
Environmental Conditions: |
|
QAPP Information: |
Quality Assurance Program Plan and Standard Operating Procedures for SWAMP program |
QAPP Information Reference(s): |
Quality Assurance Program Plans, Quality Assurance Project Plans, and Standard Operating Procedures for the SWAMP program |
|
Line of Evidence (LOE) for Decision ID 169748, Atrazine
|
Region 1 |
Klamath River HU, Shasta River HA |
|
|
LOE ID: |
103142 |
|
Pollutant: |
Atrazine |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Total |
|
Beneficial Use: |
Warm Freshwater Habitat |
|
Number of Samples: |
3 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP RWB1 Monitoring data for Klamath River HU, Shasta River HA to determine beneficial use support and results are as follows: 0 of 3 samples exceeded the water quality standard for Atrazine. |
Data Reference: |
Water Quality Assessment Data for the 2018 solicitation cycle submitted through CEDEN for SWAMP RWB1 Monitoring .
|
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
All waters shall be maintained free of toxic substances in concentrations which are toxic to, or which produce detrimental physiological responses in, human, plant, animal, or aquatic life. (Basin Plan). |
Objective/Criterion Reference: |
Water Quality Control Plan (Basin Plan) for the North Coast Region |
|
Evaluation Guideline: |
The evaluation guideline for Atrazine is the USEPA Aquatic Life Benchmark of < 1 ug/L for a nonvascular plant (acute). The benchmark was derived from a \less-than\" value (for example, <1,500) and may underestimate toxicity." |
Guideline Reference: |
OPP Aquatic Life Benchmarks |
|
Spatial Representation: |
The samples were collected at 1 monitoring site(s) (105SH9274) |
Temporal Representation: |
The samples were collected between the dates of 2013-03-07 and 2013-11-20 |
Environmental Conditions: |
|
QAPP Information: |
Quality Assurance Program Plan and Standard Operating Procedures for SWAMP program |
QAPP Information Reference(s): |
Quality Assurance Program Plans, Quality Assurance Project Plans, and Standard Operating Procedures for the SWAMP program |
|
Line of Evidence (LOE) for Decision ID 169748, Atrazine
|
Region 1 |
Klamath River HU, Shasta River HA |
|
|
LOE ID: |
123198 |
|
Pollutant: |
Atrazine |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
None |
|
Beneficial Use: |
Municipal & Domestic Supply |
|
Number of Samples: |
0 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
State Water Board staff re-assessed SWAMP data for Klamath River HU, Shasta River HA to determine beneficial use support and results are as follows: 0 of 0 samples exceed the criterion for Atrazine, Total. Eight sample results were not used in the assessment because the laboratory data reporting limit(s) was above the objective and therefore the results could not be quantified with the level of certainty required by the Listing Policy. This LOE re-assesses data from LOE 29849 from the 2010 Integrated Report. Data were re-assessed in order to (1) update the numeric objective, and (2) evaluate these data in their own LOE, instead of being evaluated in the same LOE as other pesticide data. |
Data Reference: |
Surface Water Ambient Monitoring Program (SWAMP). Summary Report for the North Coast Region (RWQCB-1) for years 2000-2006. North Coast Regional Water Quality Control Board. March 2008 |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
Water Quality Control Plan, North Coast Region (NCRWQCB 2011): Waters designated for use as domestic or municipal supply (MUN) shall not contain concentrations of chemical constituents in excess of the limits specified in California Code of Regulations, Title 22, Chapter 15. The maximum contaminant level listed in Table 64431-A for atrazine is 1 ug/L. |
Objective/Criterion Reference: |
Water Quality Control Plan (Basin Plan) for the North Coast Region |
Objective/Criterion Reference: |
Maximum Contaminant Levels for organic and inorganic chemicals. CCR Title 22 |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
Data for this line of evidence for Klamath River HU, Shasta River HA was collected at 1 monitoring site [ Yreka Creek at Anderson Rd - 105YREAND] |
Temporal Representation: |
Data was collected over the time period 10/9/2002-6/20/2005. |
Environmental Conditions: |
There are no known environmental conditions (e.g., seasonality, land use practices, fire events, storms, etc.) that are related to these data. |
QAPP Information: |
Quality control was conducted in accordance with the SWAMP Quality Assurance Management Plan (SWAMP 2002). |
QAPP Information Reference(s): |
Quality Assurance Management Plan for the State of California's Surface Water Ambient Monitoring Program. Sacramento, CA. State Water Resources Control Board. SWAMP. December 2002 (1st version)
|
|
Line of Evidence (LOE) for Decision ID 169748, Atrazine
|
Region 1 |
Klamath River HU, Shasta River HA |
|
|
LOE ID: |
123199 |
|
Pollutant: |
Atrazine |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
None |
|
Beneficial Use: |
Municipal & Domestic Supply |
|
Number of Samples: |
0 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
State Water Board staff re-assessed SWAMP data for Klamath River HU, Shasta River HA to determine beneficial use support and results are as follows: 0 of 0 samples exceed the criterion for Atrazine, Total. Four sample results were not used in the assessment because the laboratory data reporting limit(s) was above the objective and therefore the results could not be quantified with the level of certainty required by the Listing Policy. This LOE re-assesses data from LOE 29849 from the 2010 Integrated Report. Data were re-assessed in order to (1) update the numeric objective, and (2) evaluate these data in their own LOE, instead of being evaluated in the same LOE as other pesticide data. |
Data Reference: |
Surface Water Ambient Monitoring Program (SWAMP). Summary Report for the North Coast Region (RWQCB-1) for years 2000-2006. North Coast Regional Water Quality Control Board. March 2008 |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
Water Quality Control Plan, North Coast Region (NCRWQCB 2011): Waters designated for use as domestic or municipal supply (MUN) shall not contain concentrations of chemical constituents in excess of the limits specified in California Code of Regulations, Title 22, Chapter 15. The maximum contaminant level listed in Table 64431-A for atrazine is 1 ug/L. |
Objective/Criterion Reference: |
Water Quality Control Plan (Basin Plan) for the North Coast Region |
Objective/Criterion Reference: |
Maximum Contaminant Levels for organic and inorganic chemicals. CCR Title 22 |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
Data for this line of evidence for Klamath River HU, Shasta River HA was collected at 1 monitoring site [ Yreka Creek at Highway 3 - 105YREHW3] |
Temporal Representation: |
Data was collected over the time period 10/21/2004-6/20/2005. |
Environmental Conditions: |
There are no known environmental conditions (e.g., seasonality, land use practices, fire events, storms, etc.) that are related to these data. |
QAPP Information: |
Quality control was conducted in accordance with the SWAMP Quality Assurance Management Plan (SWAMP 2002). |
QAPP Information Reference(s): |
Quality Assurance Management Plan for the State of California's Surface Water Ambient Monitoring Program. Sacramento, CA. State Water Resources Control Board. SWAMP. December 2002 (1st version)
|
|
Line of Evidence (LOE) for Decision ID 169748, Atrazine
|
Region 1 |
Klamath River HU, Shasta River HA |
|
|
LOE ID: |
123196 |
|
Pollutant: |
Atrazine |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
None |
|
Beneficial Use: |
Municipal & Domestic Supply |
|
Number of Samples: |
0 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
State Water Board staff re-assessed SWAMP data for Klamath River HU, Shasta River HA to determine beneficial use support and results are as follows: 0 of 0 samples exceed the criterion for Atrazine, Total. Four sample results were not used in the assessment because the laboratory data reporting limit(s) was above the objective and therefore the results could not be quantified with the level of certainty required by the Listing Policy. This LOE re-assesses data from LOE 29849 from the 2010 Integrated Report. Data were re-assessed in order to (1) update the numeric objective, and (2) evaluate these data in their own LOE, instead of being evaluated in the same LOE as other pesticide data. |
Data Reference: |
Surface Water Ambient Monitoring Program (SWAMP). Summary Report for the North Coast Region (RWQCB-1) for years 2000-2006. North Coast Regional Water Quality Control Board. March 2008 |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
Water Quality Control Plan, North Coast Region (NCRWQCB 2011): Waters designated for use as domestic or municipal supply (MUN) shall not contain concentrations of chemical constituents in excess of the limits specified in California Code of Regulations, Title 22, Chapter 15. The maximum contaminant level listed in Table 64431-A for atrazine is 1 ug/L. |
Objective/Criterion Reference: |
Water Quality Control Plan (Basin Plan) for the North Coast Region |
Objective/Criterion Reference: |
Maximum Contaminant Levels for organic and inorganic chemicals. CCR Title 22 |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
Data for this line of evidence for Klamath River HU, Shasta River HA was collected at 1 monitoring site [ Shasta River at Montague - 105SHAMON] |
Temporal Representation: |
Data was collected over the time period 10/7/2002-6/19/2003. |
Environmental Conditions: |
There are no known environmental conditions (e.g., seasonality, land use practices, fire events, storms, etc.) that are related to these data. |
QAPP Information: |
Quality control was conducted in accordance with the SWAMP Quality Assurance Management Plan (SWAMP 2002). |
QAPP Information Reference(s): |
Quality Assurance Management Plan for the State of California's Surface Water Ambient Monitoring Program. Sacramento, CA. State Water Resources Control Board. SWAMP. December 2002 (1st version)
|
|
Line of Evidence (LOE) for Decision ID 169748, Atrazine
|
Region 1 |
Klamath River HU, Shasta River HA |
|
|
LOE ID: |
123197 |
|
Pollutant: |
Atrazine |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
None |
|
Beneficial Use: |
Municipal & Domestic Supply |
|
Number of Samples: |
0 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
State Water Board staff re-assessed SWAMP data for Klamath River HU, Shasta River HA to determine beneficial use support and results are as follows: 0 of 0 samples exceed the criterion for Atrazine, Total. Four sample results were not used in the assessment because the laboratory data reporting limit(s) was above the objective and therefore the results could not be quantified with the level of certainty required by the Listing Policy. This LOE re-assesses data from LOE 29849 from the 2010 Integrated Report. Data were re-assessed in order to (1) update the numeric objective, and (2) evaluate these data in their own LOE, instead of being evaluated in the same LOE as other pesticide data. |
Data Reference: |
Surface Water Ambient Monitoring Program (SWAMP). Summary Report for the North Coast Region (RWQCB-1) for years 2000-2006. North Coast Regional Water Quality Control Board. March 2008 |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
Water Quality Control Plan, North Coast Region (NCRWQCB 2011): Waters designated for use as domestic or municipal supply (MUN) shall not contain concentrations of chemical constituents in excess of the limits specified in California Code of Regulations, Title 22, Chapter 15. The maximum contaminant level listed in Table 64431-A for atrazine is 1 ug/L. |
Objective/Criterion Reference: |
Water Quality Control Plan (Basin Plan) for the North Coast Region |
Objective/Criterion Reference: |
Maximum Contaminant Levels for organic and inorganic chemicals. CCR Title 22 |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
Data for this line of evidence for Klamath River HU, Shasta River HA was collected at 1 monitoring site [ Shasta River near Edgewood - 105SH9274] |
Temporal Representation: |
Data was collected over the time period 10/7/2002-6/19/2003. |
Environmental Conditions: |
There are no known environmental conditions (e.g., seasonality, land use practices, fire events, storms, etc.) that are related to these data. |
QAPP Information: |
Quality control was conducted in accordance with the SWAMP Quality Assurance Management Plan (SWAMP 2002). |
QAPP Information Reference(s): |
Quality Assurance Management Plan for the State of California's Surface Water Ambient Monitoring Program. Sacramento, CA. State Water Resources Control Board. SWAMP. December 2002 (1st version)
|
|
Line of Evidence (LOE) for Decision ID 169748, Atrazine
|
Region 1 |
Klamath River HU, Shasta River HA |
|
|
LOE ID: |
123186 |
|
Pollutant: |
Atrazine |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
None |
|
Beneficial Use: |
Municipal & Domestic Supply |
|
Number of Samples: |
13 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
State Water Board staff re-assessed SWAMP data for Klamath River HU, Shasta River HA to determine beneficial use support and results are as follows: 0 of 13 samples exceed the criterion for Atrazine, Total. This LOE re-assesses data from LOE 29849 from the 2010 Integrated Report. Data were re-assessed in order to (1) update the numeric objective, and (2) evaluate these data in their own LOE, instead of being evaluated in the same LOE as other pesticide data. |
Data Reference: |
Surface Water Ambient Monitoring Program (SWAMP). Summary Report for the North Coast Region (RWQCB-1) for years 2000-2006. North Coast Regional Water Quality Control Board. March 2008 |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
Water Quality Control Plan, North Coast Region (NCRWQCB 2011): Waters designated for use as domestic or municipal supply (MUN) shall not contain concentrations of chemical constituents in excess of the limits specified in California Code of Regulations, Title 22, Chapter 15. The maximum contaminant level listed in Table 64431-A for atrazine is 1 ug/L. |
Objective/Criterion Reference: |
Water Quality Control Plan (Basin Plan) for the North Coast Region |
Objective/Criterion Reference: |
Maximum Contaminant Levels for organic and inorganic chemicals. CCR Title 22 |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
Data for this line of evidence for Klamath River HU, Shasta River HA was collected at 1 monitoring site [ Shasta River at Hwy 263 - 105SH1452] |
Temporal Representation: |
Data was collected over the time period 4/24/2001-11/16/2006. |
Environmental Conditions: |
There are no known environmental conditions (e.g., seasonality, land use practices, fire events, storms, etc.) that are related to these data. |
QAPP Information: |
Quality control was conducted in accordance with the SWAMP Quality Assurance Management Plan (SWAMP 2002). |
QAPP Information Reference(s): |
Quality Assurance Management Plan for the State of California's Surface Water Ambient Monitoring Program. Sacramento, CA. State Water Resources Control Board. SWAMP. December 2002 (1st version)
|
|
Line of Evidence (LOE) for Decision ID 169748, Atrazine
|
Region 1 |
Klamath River HU, Shasta River HA |
|
|
LOE ID: |
103139 |
|
Pollutant: |
Atrazine |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Total |
|
Beneficial Use: |
Cold Freshwater Habitat |
|
Number of Samples: |
3 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP RWB1 Monitoring data for Klamath River HU, Shasta River HA to determine beneficial use support and results are as follows: 0 of 3 samples exceeded the water quality standard for Atrazine. |
Data Reference: |
Water Quality Assessment Data for the 2018 solicitation cycle submitted through CEDEN for SWAMP RWB1 Monitoring .
|
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
All waters shall be maintained free of toxic substances in concentrations which are toxic to, or which produce detrimental physiological responses in, human, plant, animal, or aquatic life. (Basin Plan). |
Objective/Criterion Reference: |
Water Quality Control Plan (Basin Plan) for the North Coast Region |
|
Evaluation Guideline: |
The evaluation guideline for Atrazine is the USEPA Aquatic Life Benchmark of < 1 ug/L for a nonvascular plant (acute). The benchmark was derived from a \less-than\" value (for example, <1,500) and may underestimate toxicity." |
Guideline Reference: |
OPP Aquatic Life Benchmarks |
|
Spatial Representation: |
The samples were collected at 1 monitoring site(s) (105SH9274) |
Temporal Representation: |
The samples were collected between the dates of 2013-03-07 and 2013-11-20 |
Environmental Conditions: |
|
QAPP Information: |
Quality Assurance Program Plan and Standard Operating Procedures for SWAMP program |
QAPP Information Reference(s): |
Quality Assurance Program Plans, Quality Assurance Project Plans, and Standard Operating Procedures for the SWAMP program |
|
Line of Evidence (LOE) for Decision ID 169748, Atrazine
|
Region 1 |
Klamath River HU, Shasta River HA |
|
|
LOE ID: |
103136 |
|
Pollutant: |
Atrazine |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Total |
|
Beneficial Use: |
Cold Freshwater Habitat |
|
Number of Samples: |
3 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP RWB1 Monitoring data for Klamath River HU, Shasta River HA to determine beneficial use support and results are as follows: 0 of 3 samples exceeded the water quality standard for Atrazine. |
Data Reference: |
Water Quality Assessment Data for the 2018 solicitation cycle submitted through CEDEN for SWAMP RWB1 Monitoring .
|
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
All waters shall be maintained free of toxic substances in concentrations which are toxic to, or which produce detrimental physiological responses in, human, plant, animal, or aquatic life. (Basin Plan). |
Objective/Criterion Reference: |
Water Quality Control Plan (Basin Plan) for the North Coast Region |
|
Evaluation Guideline: |
The evaluation guideline for Atrazine is the USEPA Aquatic Life Benchmark of < 1 ug/L for a nonvascular plant (acute). The benchmark was derived from a \less-than\" value (for example, <1,500) and may underestimate toxicity." |
Guideline Reference: |
OPP Aquatic Life Benchmarks |
|
Spatial Representation: |
The samples were collected at 1 monitoring site(s) (105SH1452) |
Temporal Representation: |
The samples were collected between the dates of 2013-03-06 and 2013-11-20 |
Environmental Conditions: |
|
QAPP Information: |
Quality Assurance Program Plan and Standard Operating Procedures for SWAMP program |
QAPP Information Reference(s): |
Quality Assurance Program Plans, Quality Assurance Project Plans, and Standard Operating Procedures for the SWAMP program |
|
Line of Evidence (LOE) for Decision ID 169748, Atrazine
|
Region 1 |
Klamath River HU, Shasta River HA |
|
|
LOE ID: |
41343 |
|
Pollutant: |
Atrazine |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Total |
|
Beneficial Use: |
Municipal & Domestic Supply |
|
Number of Samples: |
3 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP data for Klamath River HU, Shasta River HA to determine beneficial use support and results are as follows: 0 of 3 samples exceed the criterion for Atrazine. |
Data Reference: |
RWB1 Trend Maintenance Periods FYs 2007 2008 |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
Water Quality Control Plan, North Coast Region (NCRWQCB 2011): Waters designated for use as domestic or municipal supply (MUN) shall not contain concentrations of chemical constituents in excess of the limits specified in California Code of Regulations, Title 22, Chapter 15. The maximum contaminant level listed in Table 64431-A for atrazine is 1 ug/L. |
Objective/Criterion Reference: |
Maximum Contaminant Levels for organic and inorganic chemicals. CCR Title 22 |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
Data for this line of evidence for Klamath River HU, Shasta River HA was collected at 1 monitoring site [ Shasta River near Edgewood - 105SHAEDG] |
Temporal Representation: |
Data was collected over the time period 11/15/2007-7/16/2008. |
Environmental Conditions: |
Staff is not aware of any special conditions that might affect interpretation of the data. |
QAPP Information: |
The SWAMP QAPP (2008) was followed. |
QAPP Information Reference(s): |
Surface Water Ambient Monitoring Program Quality Assurance Program Plan |
|
Line of Evidence (LOE) for Decision ID 169748, Atrazine
|
Region 1 |
Klamath River HU, Shasta River HA |
|
|
LOE ID: |
103140 |
|
Pollutant: |
Atrazine |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Total |
|
Beneficial Use: |
Municipal & Domestic Supply |
|
Number of Samples: |
3 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP RWB1 Monitoring data for Klamath River HU, Shasta River HA to determine beneficial use support and results are as follows: 0 of 3 samples exceeded the water quality standard for Atrazine. |
Data Reference: |
Water Quality Assessment Data for the 2018 solicitation cycle submitted through CEDEN for SWAMP RWB1 Monitoring .
|
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
Water Quality Control Plan, North Coast Region (NCRWQCB 2018): Waters designated for use as domestic or municipal supply (MUN) shall not contain concentrations of chemical constituents in excess of the limits specified in California Code of Regulations, Title 22, Chapter 15. The maximum contaminant level listed in Table 64431-A for atrazine is 1 ug/L. |
Objective/Criterion Reference: |
Water Quality Control Plan (Basin Plan) for the North Coast Region |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
The samples were collected at 1 monitoring site(s) (105SH9274) |
Temporal Representation: |
The samples were collected between the dates of 2013-03-07 and 2013-11-20 |
Environmental Conditions: |
|
QAPP Information: |
Quality Assurance Program Plan and Standard Operating Procedures for SWAMP program |
QAPP Information Reference(s): |
Quality Assurance Program Plans, Quality Assurance Project Plans, and Standard Operating Procedures for the SWAMP program |
|
Line of Evidence (LOE) for Decision ID 169748, Atrazine
|
Region 1 |
Klamath River HU, Shasta River HA |
|
|
LOE ID: |
103137 |
|
Pollutant: |
Atrazine |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Total |
|
Beneficial Use: |
Municipal & Domestic Supply |
|
Number of Samples: |
3 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP RWB1 Monitoring data for Klamath River HU, Shasta River HA to determine beneficial use support and results are as follows: 0 of 3 samples exceeded the water quality standard for Atrazine. |
Data Reference: |
Water Quality Assessment Data for the 2018 solicitation cycle submitted through CEDEN for SWAMP RWB1 Monitoring .
|
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
Water Quality Control Plan, North Coast Region (NCRWQCB 2018): Waters designated for use as domestic or municipal supply (MUN) shall not contain concentrations of chemical constituents in excess of the limits specified in California Code of Regulations, Title 22, Chapter 15. The maximum contaminant level listed in Table 64431-A for atrazine is 1 ug/L. |
Objective/Criterion Reference: |
Water Quality Control Plan (Basin Plan) for the North Coast Region |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
The samples were collected at 1 monitoring site(s) (105SH1452) |
Temporal Representation: |
The samples were collected between the dates of 2013-03-06 and 2013-11-20 |
Environmental Conditions: |
|
QAPP Information: |
Quality Assurance Program Plan and Standard Operating Procedures for SWAMP program |
QAPP Information Reference(s): |
Quality Assurance Program Plans, Quality Assurance Project Plans, and Standard Operating Procedures for the SWAMP program |
|
Line of Evidence (LOE) for Decision ID 169748, Atrazine
|
Region 1 |
Klamath River HU, Shasta River HA |
|
|
LOE ID: |
349011 |
|
Pollutant: |
Atrazine |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Total |
|
Beneficial Use: |
Cold Freshwater Habitat |
|
Number of Samples: |
3 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed RWB1 Trend Maintenance Periods FYs 2007 2008 data for Klamath River HU, Shasta River HA to determine beneficial use support and results are as follows: 0 of 3 samples exceeded the water quality threshold for Atrazine. |
Data Reference: |
RWB1 Trend Maintenance Periods FYs 2007 2008 |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
All waters shall be maintained free of toxic substances in concentrations which are toxic to, or which produce detrimental physiological responses in, human, plant, animal, or aquatic life. (Basin Plan). |
Objective/Criterion Reference: |
Water Quality Control Plan (Basin Plan) for the North Coast Region |
|
Evaluation Guideline: |
The evaluation guideline for Atrazine is the USEPA Aquatic Life Benchmark of < 1 ug/L for a nonvascular plant (acute). The benchmark was derived from a 'less-than' value (for example, <1,500) and may underestimate toxicity. |
Guideline Reference: |
OPP Aquatic Life Benchmarks |
|
Spatial Representation: |
The samples were collected at 1 monitoring site: 105SHA263 (Shasta River at Hwy 263). |
Temporal Representation: |
The samples were collected between the dates of 2007-11-15 and 2008-07-16 |
Environmental Conditions: |
|
QAPP Information: |
Generic SWAMP QAPrP |
QAPP Information Reference(s): |
Generic SWAMP QAPrP |
|
Line of Evidence (LOE) for Decision ID 169748, Atrazine
|
Region 1 |
Klamath River HU, Shasta River HA |
|
|
LOE ID: |
349013 |
|
Pollutant: |
Atrazine |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Total |
|
Beneficial Use: |
Warm Freshwater Habitat |
|
Number of Samples: |
3 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed RWB1 Trend Maintenance Periods FYs 2007 2008 data for Klamath River HU, Shasta River HA to determine beneficial use support and results are as follows: 0 of 3 samples exceeded the water quality threshold for Atrazine. |
Data Reference: |
RWB1 Trend Maintenance Periods FYs 2007 2008 |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
All waters shall be maintained free of toxic substances in concentrations which are toxic to, or which produce detrimental physiological responses in, human, plant, animal, or aquatic life. (Basin Plan). |
Objective/Criterion Reference: |
Water Quality Control Plan (Basin Plan) for the North Coast Region |
|
Evaluation Guideline: |
The evaluation guideline for Atrazine is the USEPA Aquatic Life Benchmark of < 1 ug/L for a nonvascular plant (acute). The benchmark was derived from a 'less-than' value (for example, <1,500) and may underestimate toxicity. |
Guideline Reference: |
OPP Aquatic Life Benchmarks |
|
Spatial Representation: |
The samples were collected at 1 monitoring site: 105SHAEDG (Shasta River near Edgewood). |
Temporal Representation: |
The samples were collected between the dates of 2007-11-15 and 2008-07-16 |
Environmental Conditions: |
|
QAPP Information: |
Generic SWAMP QAPrP |
QAPP Information Reference(s): |
Generic SWAMP QAPrP |
|
Line of Evidence (LOE) for Decision ID 169748, Atrazine
|
Region 1 |
Klamath River HU, Shasta River HA |
|
|
LOE ID: |
349009 |
|
Pollutant: |
Atrazine |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Total |
|
Beneficial Use: |
Cold Freshwater Habitat |
|
Number of Samples: |
3 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed RWB1 Trend Maintenance Periods FYs 2007 2008 data for Klamath River HU, Shasta River HA to determine beneficial use support and results are as follows: 0 of 3 samples exceeded the water quality threshold for Atrazine. |
Data Reference: |
RWB1 Trend Maintenance Periods FYs 2007 2008 |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
All waters shall be maintained free of toxic substances in concentrations which are toxic to, or which produce detrimental physiological responses in, human, plant, animal, or aquatic life. (Basin Plan). |
Objective/Criterion Reference: |
Water Quality Control Plan (Basin Plan) for the North Coast Region |
|
Evaluation Guideline: |
The evaluation guideline for Atrazine is the USEPA Aquatic Life Benchmark of < 1 ug/L for a nonvascular plant (acute). The benchmark was derived from a 'less-than' value (for example, <1,500) and may underestimate toxicity. |
Guideline Reference: |
OPP Aquatic Life Benchmarks |
|
Spatial Representation: |
The samples were collected at 1 monitoring site: 105SHAEDG (Shasta River near Edgewood). |
Temporal Representation: |
The samples were collected between the dates of 2007-11-15 and 2008-07-16 |
Environmental Conditions: |
|
QAPP Information: |
Generic SWAMP QAPrP |
QAPP Information Reference(s): |
Generic SWAMP QAPrP |
|
Line of Evidence (LOE) for Decision ID 169748, Atrazine
|
Region 1 |
Klamath River HU, Shasta River HA |
|
|
LOE ID: |
349010 |
|
Pollutant: |
Atrazine |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Total |
|
Beneficial Use: |
Warm Freshwater Habitat |
|
Number of Samples: |
3 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed RWB1 Trend Maintenance Periods FYs 2007 2008 data for Klamath River HU, Shasta River HA to determine beneficial use support and results are as follows: 0 of 3 samples exceeded the water quality threshold for Atrazine. |
Data Reference: |
RWB1 Trend Maintenance Periods FYs 2007 2008 |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
All waters shall be maintained free of toxic substances in concentrations which are toxic to, or which produce detrimental physiological responses in, human, plant, animal, or aquatic life. (Basin Plan). |
Objective/Criterion Reference: |
Water Quality Control Plan (Basin Plan) for the North Coast Region |
|
Evaluation Guideline: |
The evaluation guideline for Atrazine is the USEPA Aquatic Life Benchmark of < 1 ug/L for a nonvascular plant (acute). The benchmark was derived from a 'less-than' value (for example, <1,500) and may underestimate toxicity. |
Guideline Reference: |
OPP Aquatic Life Benchmarks |
|
Spatial Representation: |
The samples were collected at 1 monitoring site: 105SHA263 (Shasta River at Hwy 263). |
Temporal Representation: |
The samples were collected between the dates of 2007-11-15 and 2008-07-16 |
Environmental Conditions: |
|
QAPP Information: |
Generic SWAMP QAPrP |
QAPP Information Reference(s): |
Generic SWAMP QAPrP |
|
Line of Evidence (LOE) for Decision ID 104946, Cadmium
|
Region 1 |
Klamath River HU, Shasta River HA |
|
|
LOE ID: |
103145 |
|
Pollutant: |
Cadmium |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Dissolved |
|
Beneficial Use: |
Cold Freshwater Habitat |
|
Number of Samples: |
5 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP RWB1 Monitoring data for Klamath River HU, Shasta River HA to determine beneficial use support and results are as follows: 0 of 5 samples exceeded the water quality standard for Cadmium. |
Data Reference: |
Water Quality Assessment Data for the 2018 solicitation cycle submitted through CEDEN for SWAMP RWB1 Monitoring .
|
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
California Toxics Rule (CTR) lists criterion continuous concentrations to protect aquatic life in freshwater. The criterion in freshwater is hardness dependent for each sample and varies based on the ambient hardness during sampling. Section (b)(1) in CTR contains the hardness dependent formula for the metals criterion. |
Objective/Criterion Reference: |
Water Quality Standards 2000. Establishment of numeric criteria for priority toxic pollutants for the State of California: Rules and regulations. Federal Register Vol. 65, No. 97. Washington, D.C.: Environmental Protection Agency |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
The samples were collected at 1 monitoring site(s) (105SH1452) |
Temporal Representation: |
The samples were collected between the dates of 2013-03-06 and 2013-11-20 |
Environmental Conditions: |
|
QAPP Information: |
Quality Assurance Program Plan and Standard Operating Procedures for SWAMP program |
QAPP Information Reference(s): |
Quality Assurance Program Plans, Quality Assurance Project Plans, and Standard Operating Procedures for the SWAMP program |
|
Line of Evidence (LOE) for Decision ID 104946, Cadmium
|
Region 1 |
Klamath River HU, Shasta River HA |
|
|
LOE ID: |
32580 |
|
Pollutant: |
Cadmium |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Total |
|
Beneficial Use: |
Cold Freshwater Habitat |
|
Number of Samples: |
4 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
None of the 4 samples exceeded the hardness based criteria calculated for cadmium. |
Data Reference: |
RWB1 Trend Maintenance Periods FYs 2007 2008 |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
Water Quality Control Plan, North Coast Region (NCRWQCB 2011): All waters shall be maintained free of toxic substances in concentrations that are toxic to, or that produce detrimental physiological responses in human, plant, animal, or aquatic life. California Toxics Rule (CTR) lists criterion continuous concentrations (4-day average) to protect aquatic life in freshwater. The criterion in freshwater is hardness dependent for each sample and varies based on the ambient hardness during sampling. Section (b)(1) in CTR contains the hardness dependent formula for the metals criterion. |
Objective/Criterion Reference: |
Code of Federal Regulations 40 part 131.38 Establishment of numeric criteria for priority toxic pollutants for the State of California. 7/1/2011 Edition |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
Samples collected at station 105SHAEDG (Shasta River near Edgewood). |
Temporal Representation: |
Samples collected between 11/15/2007 and 7/16/2008. |
Environmental Conditions: |
|
QAPP Information: |
SWAMP QAPP (2008) was followed. |
QAPP Information Reference(s): |
Surface Water Ambient Monitoring Program Quality Assurance Program Plan |
|
Line of Evidence (LOE) for Decision ID 104946, Cadmium
|
Region 1 |
Klamath River HU, Shasta River HA |
|
|
LOE ID: |
103146 |
|
Pollutant: |
Cadmium |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Dissolved |
|
Beneficial Use: |
Warm Freshwater Habitat |
|
Number of Samples: |
5 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP RWB1 Monitoring data for Klamath River HU, Shasta River HA to determine beneficial use support and results are as follows: 0 of 5 samples exceeded the water quality standard for Cadmium. |
Data Reference: |
Water Quality Assessment Data for the 2018 solicitation cycle submitted through CEDEN for SWAMP RWB1 Monitoring .
|
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
California Toxics Rule (CTR) lists criterion continuous concentrations to protect aquatic life in freshwater. The criterion in freshwater is hardness dependent for each sample and varies based on the ambient hardness during sampling. Section (b)(1) in CTR contains the hardness dependent formula for the metals criterion. |
Objective/Criterion Reference: |
Water Quality Standards 2000. Establishment of numeric criteria for priority toxic pollutants for the State of California: Rules and regulations. Federal Register Vol. 65, No. 97. Washington, D.C.: Environmental Protection Agency |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
The samples were collected at 1 monitoring site(s) (105SH1452) |
Temporal Representation: |
The samples were collected between the dates of 2013-03-06 and 2013-11-20 |
Environmental Conditions: |
|
QAPP Information: |
Quality Assurance Program Plan and Standard Operating Procedures for SWAMP program |
QAPP Information Reference(s): |
Quality Assurance Program Plans, Quality Assurance Project Plans, and Standard Operating Procedures for the SWAMP program |
|
Line of Evidence (LOE) for Decision ID 104946, Cadmium
|
Region 1 |
Klamath River HU, Shasta River HA |
|
|
LOE ID: |
103148 |
|
Pollutant: |
Cadmium |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Dissolved |
|
Beneficial Use: |
Warm Freshwater Habitat |
|
Number of Samples: |
5 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP RWB1 Monitoring data for Klamath River HU, Shasta River HA to determine beneficial use support and results are as follows: 0 of 5 samples exceeded the water quality standard for Cadmium. |
Data Reference: |
Water Quality Assessment Data for the 2018 solicitation cycle submitted through CEDEN for SWAMP RWB1 Monitoring .
|
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
California Toxics Rule (CTR) lists criterion continuous concentrations to protect aquatic life in freshwater. The criterion in freshwater is hardness dependent for each sample and varies based on the ambient hardness during sampling. Section (b)(1) in CTR contains the hardness dependent formula for the metals criterion. |
Objective/Criterion Reference: |
Water Quality Standards 2000. Establishment of numeric criteria for priority toxic pollutants for the State of California: Rules and regulations. Federal Register Vol. 65, No. 97. Washington, D.C.: Environmental Protection Agency |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
The samples were collected at 1 monitoring site(s) (105SH9274) |
Temporal Representation: |
The samples were collected between the dates of 2013-03-07 and 2013-11-20 |
Environmental Conditions: |
|
QAPP Information: |
Quality Assurance Program Plan and Standard Operating Procedures for SWAMP program |
QAPP Information Reference(s): |
Quality Assurance Program Plans, Quality Assurance Project Plans, and Standard Operating Procedures for the SWAMP program |
|
Line of Evidence (LOE) for Decision ID 104946, Cadmium
|
Region 1 |
Klamath River HU, Shasta River HA |
|
|
LOE ID: |
32975 |
|
Pollutant: |
Cadmium |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Total |
|
Beneficial Use: |
Cold Freshwater Habitat |
|
Number of Samples: |
4 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
None of the 4 samples exceeded the hardness based criteria calculated for cadmium. |
Data Reference: |
RWB1 Trend Maintenance Periods FYs 2007 2008 |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
Water Quality Control Plan, North Coast Region (NCRWQCB 2011): All waters shall be maintained free of toxic substances in concentrations that are toxic to, or that produce detrimental physiological responses in human, plant, animal, or aquatic life. California Toxics Rule (CTR) lists criterion continuous concentrations (4-day average) to protect aquatic life in freshwater. The criterion in freshwater is hardness dependent for each sample and varies based on the ambient hardness during sampling. Section (b)(1) in CTR contains the hardness dependent formula for the metals criterion. |
Objective/Criterion Reference: |
Code of Federal Regulations 40 part 131.38 Establishment of numeric criteria for priority toxic pollutants for the State of California. 7/1/2011 Edition |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
Samples collected at station 105SHA263 (Shasta River at Hwy 263). |
Temporal Representation: |
Samples collected between 11/15/2007 and 7/16/2008. |
Environmental Conditions: |
|
QAPP Information: |
SWAMP QAPP (2008) was followed. |
QAPP Information Reference(s): |
Surface Water Ambient Monitoring Program Quality Assurance Program Plan |
|
Line of Evidence (LOE) for Decision ID 104946, Cadmium
|
Region 1 |
Klamath River HU, Shasta River HA |
|
|
LOE ID: |
41459 |
|
Pollutant: |
Cadmium |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Total |
|
Beneficial Use: |
Municipal & Domestic Supply |
|
Number of Samples: |
4 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP data for Klamath River HU, Shasta River HA to determine beneficial use support and results are as follows: 0 of 4 samples exceed the criterion for Cadmium. |
Data Reference: |
RWB1 Trend Maintenance Periods FYs 2007 2008 |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
Water Quality Control Plan, North Coast Region (NCRWQCB 2011): Waters designated for use as domestic or municipal supply (MUN) shall not contain concentrations of chemical constituents in excess of the limits specified in California Code of Regulations, Title 22, Chapter 15. The maximum contaminant level listed in Table 64431-A for cadmium 0.005 mg/L. |
Objective/Criterion Reference: |
Maximum Contaminant Levels for organic and inorganic chemicals. CCR Title 22 |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
Data for this line of evidence for Klamath River HU, Shasta River HA was collected at 1 monitoring site [ Shasta River near Edgewood - 105SHAEDG] |
Temporal Representation: |
Data was collected over the time period 11/15/2007-7/16/2008. |
Environmental Conditions: |
Staff is not aware of any special conditions that might affect interpretation of the data. |
QAPP Information: |
The SWAMP QAPP (2008) was followed. |
QAPP Information Reference(s): |
Surface Water Ambient Monitoring Program Quality Assurance Program Plan |
|
Line of Evidence (LOE) for Decision ID 104946, Cadmium
|
Region 1 |
Klamath River HU, Shasta River HA |
|
|
LOE ID: |
103149 |
|
Pollutant: |
Cadmium |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Total |
|
Beneficial Use: |
Municipal & Domestic Supply |
|
Number of Samples: |
5 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP RWB1 Monitoring data for Klamath River HU, Shasta River HA to determine beneficial use support and results are as follows: 0 of 5 samples exceeded the water quality standard for Cadmium. |
Data Reference: |
Water Quality Assessment Data for the 2018 solicitation cycle submitted through CEDEN for SWAMP RWB1 Monitoring .
|
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
Water Quality Control Plan, North Coast Region (NCRWQCB 2018): Waters designated for use as domestic or municipal supply (MUN) shall not contain concentrations of chemical constituents in excess of the limits specified in California Code of Regulations, Title 22, Chapter 15. The maximum contaminant level listed in Table 64431-A for cadmium 0.005 mg/L. |
Objective/Criterion Reference: |
Water Quality Control Plan (Basin Plan) for the North Coast Region |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
The samples were collected at 1 monitoring site(s) (105SH1452) |
Temporal Representation: |
The samples were collected between the dates of 2013-03-06 and 2013-11-20 |
Environmental Conditions: |
|
QAPP Information: |
Quality Assurance Program Plan and Standard Operating Procedures for SWAMP program |
QAPP Information Reference(s): |
Quality Assurance Program Plans, Quality Assurance Project Plans, and Standard Operating Procedures for the SWAMP program |
|
Line of Evidence (LOE) for Decision ID 104946, Cadmium
|
Region 1 |
Klamath River HU, Shasta River HA |
|
|
LOE ID: |
123202 |
|
Pollutant: |
Cadmium |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Total |
|
Beneficial Use: |
Municipal & Domestic Supply |
|
Number of Samples: |
5 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
State Water Board staff re-assessed SWAMP data for Klamath River HU, Shasta River HA to determine beneficial use support and results are as follows: 0 of 5 samples exceed the criterion for Cadmium, Total. This LOE re-assesses data from LOE 21509 from the 2010 Integrated Report. Data were re-assessed in order to (1) update the numeric objective, and (2) evaluate these data in their own LOE, instead of being evaluated in the same LOE as other metals data. |
Data Reference: |
Surface Water Ambient Monitoring Program (SWAMP). Summary Report for the North Coast Region (RWQCB-1) for years 2000-2006. North Coast Regional Water Quality Control Board. March 2008 |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
Water Quality Control Plan, North Coast Region (NCRWQCB 2011): Waters designated for use as domestic or municipal supply (MUN) shall not contain concentrations of chemical constituents in excess of the limits specified in California Code of Regulations, Title 22, Chapter 15. The maximum contaminant level listed in Table 64431-A for cadmium 0.005 mg/L. |
Objective/Criterion Reference: |
Water Quality Control Plan (Basin Plan) for the North Coast Region |
Objective/Criterion Reference: |
Maximum Contaminant Levels for organic and inorganic chemicals. CCR Title 22 |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
Data for this line of evidence for Klamath River HU, Shasta River HA was collected at 1 monitoring site [ Shasta River at Montague - 105SHAMON] |
Temporal Representation: |
Data was collected over the time period 10/7/2002-6/19/2003. |
Environmental Conditions: |
There are no known environmental conditions (e.g., seasonality, land use practices, fire events, storms, etc.) that are related to these data. |
QAPP Information: |
Quality control was conducted in accordance with the SWAMP Quality Assurance Management Plan (SWAMP 2002). |
QAPP Information Reference(s): |
Quality Assurance Management Plan for the State of California's Surface Water Ambient Monitoring Program. Sacramento, CA. State Water Resources Control Board. SWAMP. December 2002 (1st version)
|
|
Line of Evidence (LOE) for Decision ID 104946, Cadmium
|
Region 1 |
Klamath River HU, Shasta River HA |
|
|
LOE ID: |
123201 |
|
Pollutant: |
Cadmium |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Total |
|
Beneficial Use: |
Municipal & Domestic Supply |
|
Number of Samples: |
19 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
State Water Board staff re-assessed SWAMP data for Klamath River HU, Shasta River HA to determine beneficial use support and results are as follows: 0 of 19 samples exceed the criterion for Cadmium, Total. Three sample results were not used in this assessment because the laboratory data reporting limit was above the objective and therefore the results could not be quantified with the level of certainty required by the Listing Policy. This LOE re-assesses data from LOE 21509 from the 2010 Integrated Report. Data were re-assessed in order to (1) update the numeric objective, and (2) evaluate these data in their own LOE, instead of being evaluated in the same LOE as other metals data. |
Data Reference: |
Surface Water Ambient Monitoring Program (SWAMP). Summary Report for the North Coast Region (RWQCB-1) for years 2000-2006. North Coast Regional Water Quality Control Board. March 2008 |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
Water Quality Control Plan, North Coast Region (NCRWQCB 2011): Waters designated for use as domestic or municipal supply (MUN) shall not contain concentrations of chemical constituents in excess of the limits specified in California Code of Regulations, Title 22, Chapter 15. The maximum contaminant level listed in Table 64431-A for cadmium 0.005 mg/L. |
Objective/Criterion Reference: |
Water Quality Control Plan (Basin Plan) for the North Coast Region |
Objective/Criterion Reference: |
Maximum Contaminant Levels for organic and inorganic chemicals. CCR Title 22 |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
Data for this line of evidence for Klamath River HU, Shasta River HA was collected at 1 monitoring site [ Shasta River at Hwy 263 - 105SH1452] |
Temporal Representation: |
Data was collected over the time period 3/20/2001-11/16/2006. |
Environmental Conditions: |
There are no known environmental conditions (e.g., seasonality, land use practices, fire events, storms, etc.) that are related to these data. |
QAPP Information: |
Quality control was conducted in accordance with the SWAMP Quality Assurance Management Plan (SWAMP 2002). |
QAPP Information Reference(s): |
Quality Assurance Management Plan for the State of California's Surface Water Ambient Monitoring Program. Sacramento, CA. State Water Resources Control Board. SWAMP. December 2002 (1st version)
|
|
Line of Evidence (LOE) for Decision ID 104946, Cadmium
|
Region 1 |
Klamath River HU, Shasta River HA |
|
|
LOE ID: |
103150 |
|
Pollutant: |
Cadmium |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Total |
|
Beneficial Use: |
Municipal & Domestic Supply |
|
Number of Samples: |
5 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP RWB1 Monitoring data for Klamath River HU, Shasta River HA to determine beneficial use support and results are as follows: 0 of 5 samples exceeded the water quality standard for Cadmium. |
Data Reference: |
Water Quality Assessment Data for the 2018 solicitation cycle submitted through CEDEN for SWAMP RWB1 Monitoring .
|
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
Water Quality Control Plan, North Coast Region (NCRWQCB 2018): Waters designated for use as domestic or municipal supply (MUN) shall not contain concentrations of chemical constituents in excess of the limits specified in California Code of Regulations, Title 22, Chapter 15. The maximum contaminant level listed in Table 64431-A for cadmium 0.005 mg/L. |
Objective/Criterion Reference: |
Water Quality Control Plan (Basin Plan) for the North Coast Region |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
The samples were collected at 1 monitoring site(s) (105SH9274) |
Temporal Representation: |
The samples were collected between the dates of 2013-03-07 and 2013-11-20 |
Environmental Conditions: |
|
QAPP Information: |
Quality Assurance Program Plan and Standard Operating Procedures for SWAMP program |
QAPP Information Reference(s): |
Quality Assurance Program Plans, Quality Assurance Project Plans, and Standard Operating Procedures for the SWAMP program |
|
Line of Evidence (LOE) for Decision ID 104946, Cadmium
|
Region 1 |
Klamath River HU, Shasta River HA |
|
|
LOE ID: |
123203 |
|
Pollutant: |
Cadmium |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Total |
|
Beneficial Use: |
Municipal & Domestic Supply |
|
Number of Samples: |
5 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
State Water Board staff re-assessed SWAMP data for Klamath River HU, Shasta River HA to determine beneficial use support and results are as follows: 0 of 5 samples exceed the criterion for Cadmium, Total. This LOE re-assesses data from LOE 21509 from the 2010 Integrated Report. Data were re-assessed in order to (1) update the numeric objective, and (2) evaluate these data in their own LOE, instead of being evaluated in the same LOE as other metals data. |
Data Reference: |
Surface Water Ambient Monitoring Program (SWAMP). Summary Report for the North Coast Region (RWQCB-1) for years 2000-2006. North Coast Regional Water Quality Control Board. March 2008 |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
Water Quality Control Plan, North Coast Region (NCRWQCB 2011): Waters designated for use as domestic or municipal supply (MUN) shall not contain concentrations of chemical constituents in excess of the limits specified in California Code of Regulations, Title 22, Chapter 15. The maximum contaminant level listed in Table 64431-A for cadmium 0.005 mg/L. |
Objective/Criterion Reference: |
Water Quality Control Plan (Basin Plan) for the North Coast Region |
Objective/Criterion Reference: |
Maximum Contaminant Levels for organic and inorganic chemicals. CCR Title 22 |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
Data for this line of evidence for Klamath River HU, Shasta River HA was collected at 1 monitoring site [ Shasta River near Edgewood - 105SH9274] |
Temporal Representation: |
Data was collected over the time period 10/7/2002-6/19/2003. |
Environmental Conditions: |
There are no known environmental conditions (e.g., seasonality, land use practices, fire events, storms, etc.) that are related to these data. |
QAPP Information: |
Quality control was conducted in accordance with the SWAMP Quality Assurance Management Plan (SWAMP 2002). |
QAPP Information Reference(s): |
Quality Assurance Management Plan for the State of California's Surface Water Ambient Monitoring Program. Sacramento, CA. State Water Resources Control Board. SWAMP. December 2002 (1st version)
|
|
Line of Evidence (LOE) for Decision ID 104946, Cadmium
|
Region 1 |
Klamath River HU, Shasta River HA |
|
|
LOE ID: |
41478 |
|
Pollutant: |
Cadmium |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Total |
|
Beneficial Use: |
Municipal & Domestic Supply |
|
Number of Samples: |
4 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP data for Klamath River HU, Shasta River HA to determine beneficial use support and results are as follows: 0 of 4 samples exceed the criterion for Cadmium. |
Data Reference: |
RWB1 Trend Maintenance Periods FYs 2007 2008 |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
Water Quality Control Plan, North Coast Region (NCRWQCB 2011): Waters designated for use as domestic or municipal supply (MUN) shall not contain concentrations of chemical constituents in excess of the limits specified in California Code of Regulations, Title 22, Chapter 15. The maximum contaminant level listed in Table 64431-A for cadmium 0.005 mg/L. |
Objective/Criterion Reference: |
Maximum Contaminant Levels for organic and inorganic chemicals. CCR Title 22 |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
Data for this line of evidence for Klamath River HU, Shasta River HA was collected at 1 monitoring site [ Shasta River at Hwy 263 - 105SHA263] |
Temporal Representation: |
Data was collected over the time period 11/15/2007-7/16/2008. |
Environmental Conditions: |
Staff is not aware of any special conditions that might affect interpretation of the data. |
QAPP Information: |
The SWAMP QAPP (2008) was followed. |
QAPP Information Reference(s): |
Surface Water Ambient Monitoring Program Quality Assurance Program Plan |
|
Line of Evidence (LOE) for Decision ID 104946, Cadmium
|
Region 1 |
Klamath River HU, Shasta River HA |
|
|
LOE ID: |
123213 |
|
Pollutant: |
Cadmium |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Total |
|
Beneficial Use: |
Municipal & Domestic Supply |
|
Number of Samples: |
7 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
State Water Board staff re-assessed SWAMP data for Klamath River HU, Shasta River HA to determine beneficial use support and results are as follows: 0 of 7 samples exceed the criterion for Cadmium, Total. This LOE re-assesses data from LOE 21509 from the 2010 Integrated Report. Data were re-assessed in order to (1) update the numeric objective, and (2) evaluate these data in their own LOE, instead of being evaluated in the same LOE as other metals data. |
Data Reference: |
Surface Water Ambient Monitoring Program (SWAMP). Summary Report for the North Coast Region (RWQCB-1) for years 2000-2006. North Coast Regional Water Quality Control Board. March 2008 |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
Water Quality Control Plan, North Coast Region (NCRWQCB 2011): Waters designated for use as domestic or municipal supply (MUN) shall not contain concentrations of chemical constituents in excess of the limits specified in California Code of Regulations, Title 22, Chapter 15. The maximum contaminant level listed in Table 64431-A for cadmium 0.005 mg/L. |
Objective/Criterion Reference: |
Water Quality Control Plan (Basin Plan) for the North Coast Region |
Objective/Criterion Reference: |
Maximum Contaminant Levels for organic and inorganic chemicals. CCR Title 22 |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
Data for this line of evidence for Klamath River HU, Shasta River HA was collected at 1 monitoring site [ Yreka Creek at Anderson Rd - 105YREAND] |
Temporal Representation: |
Data was collected over the time period 10/9/2002-6/20/2005. |
Environmental Conditions: |
There are no known environmental conditions (e.g., seasonality, land use practices, fire events, storms, etc.) that are related to these data. |
QAPP Information: |
Quality control was conducted in accordance with the SWAMP Quality Assurance Management Plan (SWAMP 2002). |
QAPP Information Reference(s): |
Quality Assurance Management Plan for the State of California's Surface Water Ambient Monitoring Program. Sacramento, CA. State Water Resources Control Board. SWAMP. December 2002 (1st version)
|
|
Line of Evidence (LOE) for Decision ID 104946, Cadmium
|
Region 1 |
Klamath River HU, Shasta River HA |
|
|
LOE ID: |
123214 |
|
Pollutant: |
Cadmium |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Total |
|
Beneficial Use: |
Municipal & Domestic Supply |
|
Number of Samples: |
3 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
State Water Board staff re-assessed SWAMP data for Klamath River HU, Shasta River HA to determine beneficial use support and results are as follows: 0 of 3 samples exceed the criterion for Cadmium, Total. This LOE re-assesses data from LOE 21509 from the 2010 Integrated Report. Data were re-assessed in order to (1) update the numeric objective, and (2) evaluate these data in their own LOE, instead of being evaluated in the same LOE as other metals data. |
Data Reference: |
Surface Water Ambient Monitoring Program (SWAMP). Summary Report for the North Coast Region (RWQCB-1) for years 2000-2006. North Coast Regional Water Quality Control Board. March 2008 |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
Water Quality Control Plan, North Coast Region (NCRWQCB 2011): Waters designated for use as domestic or municipal supply (MUN) shall not contain concentrations of chemical constituents in excess of the limits specified in California Code of Regulations, Title 22, Chapter 15. The maximum contaminant level listed in Table 64431-A for cadmium 0.005 mg/L. |
Objective/Criterion Reference: |
Water Quality Control Plan (Basin Plan) for the North Coast Region |
Objective/Criterion Reference: |
Maximum Contaminant Levels for organic and inorganic chemicals. CCR Title 22 |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
Data for this line of evidence for Klamath River HU, Shasta River HA was collected at 1 monitoring site [ Yreka Creek at Highway 3 - 105YREHW3] |
Temporal Representation: |
Data was collected over the time period 10/21/2004-6/20/2005. |
Environmental Conditions: |
There are no known environmental conditions (e.g., seasonality, land use practices, fire events, storms, etc.) that are related to these data. |
QAPP Information: |
Quality control was conducted in accordance with the SWAMP Quality Assurance Management Plan (SWAMP 2002). |
QAPP Information Reference(s): |
Letter requesting acceptance of late submittal |
|
Line of Evidence (LOE) for Decision ID 104946, Cadmium
|
Region 1 |
Klamath River HU, Shasta River HA |
|
|
LOE ID: |
103147 |
|
Pollutant: |
Cadmium |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Dissolved |
|
Beneficial Use: |
Cold Freshwater Habitat |
|
Number of Samples: |
5 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP RWB1 Monitoring data for Klamath River HU, Shasta River HA to determine beneficial use support and results are as follows: 0 of 5 samples exceeded the water quality standard for Cadmium. |
Data Reference: |
Water Quality Assessment Data for the 2018 solicitation cycle submitted through CEDEN for SWAMP RWB1 Monitoring .
|
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
California Toxics Rule (CTR) lists criterion continuous concentrations to protect aquatic life in freshwater. The criterion in freshwater is hardness dependent for each sample and varies based on the ambient hardness during sampling. Section (b)(1) in CTR contains the hardness dependent formula for the metals criterion. |
Objective/Criterion Reference: |
Water Quality Standards 2000. Establishment of numeric criteria for priority toxic pollutants for the State of California: Rules and regulations. Federal Register Vol. 65, No. 97. Washington, D.C.: Environmental Protection Agency |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
The samples were collected at 1 monitoring site(s) (105SH9274) |
Temporal Representation: |
The samples were collected between the dates of 2013-03-07 and 2013-11-20 |
Environmental Conditions: |
|
QAPP Information: |
Quality Assurance Program Plan and Standard Operating Procedures for SWAMP program |
QAPP Information Reference(s): |
Quality Assurance Program Plans, Quality Assurance Project Plans, and Standard Operating Procedures for the SWAMP program |
|
Line of Evidence (LOE) for Decision ID 157120, Chloride
|
Region 1 |
Klamath River HU, Shasta River HA |
|
|
LOE ID: |
46927 |
|
Pollutant: |
Chloride |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Not Recorded |
|
Beneficial Use: |
Municipal & Domestic Supply |
|
Number of Samples: |
9 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
None of the 9 chloride samples collected in Yreka Creek exceed the evaluation guideline. The samples were collected as part of the Surface Water Ambient Water Monitoring Program (SWAMP). The data are found in the SWAMP Summary Report for the North Coast Region for Years 2000-2006 (NCRWQCB 2008). This LOE and LOE 46926 replace LOE 25416 from the 2010 Integrated Report cycle. The data were reevaluated in order to separate the date from the maintem Shasta River and Yreka Creek into two, separate LOEs. |
Data Reference: |
Surface Water Ambient Monitoring Program (SWAMP). Summary Report for the North Coast Region (RWQCB-1) for years 2000-2006. North Coast Regional Water Quality Control Board. March 2008 |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
Per the Basin Plan (NCRWQCB 2007): Waters shall not contain taste- or odorproducing substances in concentrations that impart undesirable tastes or odors to fish flesh or other edible products of aquatic origin, or that cause nuisance or adversely affect beneficial uses. |
Objective/Criterion Reference: |
Water Quality Control Plan (Basin Plan) - North Coast Region (Region 1) |
|
Evaluation Guideline: |
Per 22 CCR 64449: The recommended Secondary Maximum Contaminant Level for chloride is 250 mg/L. |
Guideline Reference: |
Title 22. Division 4. Chapter 15. Sections 64400 et seq. California Code of Regulations |
|
Spatial Representation: |
Samples were collected in Yreka Creek from 2 locations as follows: (1) at Highway 3 (SWAMP Station ID 105YREHW3), and (2) at Anderson Grade Road (SWAMP Station ID 105YREAND). Samples were
collected in well-mixed flows in glides or riffles. |
Temporal Representation: |
Samples in Yreka Creek were collected from October 2004 to June 2005. The site visits corresponded to fall, winter, spring and early summer seasonal conditions. |
Environmental Conditions: |
There are no known environmental conditions (e.g., seasonality, land use practices, fire events, storms, etc.) that are related to these data. |
QAPP Information: |
Quality control was conducted in accordance with the SWAMP Quality Assurance Management Plan (SWAMP 2002). |
QAPP Information Reference(s): |
Quality Assurance Management Plan for the State of California's Surface Water Ambient Monitoring Program. Sacramento, CA. State Water Resources Control Board. SWAMP. December 2002 (1st version)
|
|
Line of Evidence (LOE) for Decision ID 157120, Chloride
|
Region 1 |
Klamath River HU, Shasta River HA |
|
|
LOE ID: |
324022 |
|
Pollutant: |
Chloride |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Dissolved |
|
Beneficial Use: |
Municipal & Domestic Supply |
|
Number of Samples: |
1 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP Reference Condition Management Plan data for Klamath River HU, Shasta River HA to determine beneficial use support and results are as follows: 0 of 1 samples exceeded the water quality threshold for Chloride. |
Data Reference: |
Benthic, Field, Habitat, WQ from the Surface Water Ambient Monitoring Program for the 2026 Integrated Report in Region 1 |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
Water Quality Control Plan, North Coast Region (NCRWQCB 2018): Waters designated for use as domestic or municipal supply (MUN) shall not contain concentrations of chemical constituents in excess of the limits specified in California Code of Regulations, Title 22, Chapter 15. The secondary maximum contaminant level listed in Table 64449-B for chloride is 250 mg/L. |
Objective/Criterion Reference: |
Water Quality Control Plan (Basin Plan) for the North Coast Region |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
The samples were collected at 1 monitoring site: 105WE0592 (Eddy Creek ~0.8 miles downstream from end of 4WD road.). |
Temporal Representation: |
The samples were collected between the dates of 2015-07-13 and 2015-07-13 |
Environmental Conditions: |
|
QAPP Information: |
QAPP for Surface Water Ambient Monitoring Program (SWAMP) |
QAPP Information Reference(s): |
Generic SWAMP QAPrP |
|
Line of Evidence (LOE) for Decision ID 157120, Chloride
|
Region 1 |
Klamath River HU, Shasta River HA |
|
|
LOE ID: |
324084 |
|
Pollutant: |
Chloride |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Dissolved |
|
Beneficial Use: |
Municipal & Domestic Supply |
|
Number of Samples: |
1 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP Perennial Stream Surveys data for Klamath River HU, Shasta River HA to determine beneficial use support and results are as follows: 0 of 1 samples exceeded the water quality threshold for Chloride. |
Data Reference: |
Benthic, Field, Habitat, WQ from the Surface Water Ambient Monitoring Program for the 2026 Integrated Report in Region 1 |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
Water Quality Control Plan, North Coast Region (NCRWQCB 2018): Waters designated for use as domestic or municipal supply (MUN) shall not contain concentrations of chemical constituents in excess of the limits specified in California Code of Regulations, Title 22, Chapter 15. The secondary maximum contaminant level listed in Table 64449-B for chloride is 250 mg/L. |
Objective/Criterion Reference: |
Water Quality Control Plan (Basin Plan) for the North Coast Region |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
The samples were collected at 1 monitoring site: 105PS0295 (Shasta River ~1mi above Cooley Gulch). |
Temporal Representation: |
The samples were collected between the dates of 2016-06-15 and 2016-06-15 |
Environmental Conditions: |
|
QAPP Information: |
QAPP for Surface Water Ambient Monitoring Program (SWAMP) |
QAPP Information Reference(s): |
Generic SWAMP QAPrP |
|
Line of Evidence (LOE) for Decision ID 157120, Chloride
|
Region 1 |
Klamath River HU, Shasta River HA |
|
|
LOE ID: |
324097 |
|
Pollutant: |
Chloride |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Dissolved |
|
Beneficial Use: |
Warm Freshwater Habitat |
|
Number of Samples: |
1 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP Perennial Stream Surveys data for Klamath River HU, Shasta River HA to determine beneficial use support and results are as follows: 0 of 1 samples exceeded the water quality threshold for Chloride. |
Data Reference: |
Benthic, Field, Habitat, WQ from the Surface Water Ambient Monitoring Program for the 2026 Integrated Report in Region 1 |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
Water Quality Control Plan, North Coast Region (NCRWQCB 2018): Waters designated for use as domestic or municipal supply (MUN) shall not contain concentrations of chemical constituents in excess of the limits specified in California Code of Regulations, Title 22, Chapter 15. The secondary maximum contaminant level listed in Table 64449-A for Aluminum is 0.2 mg/L. |
Objective/Criterion Reference: |
Water Quality Control Plan (Basin Plan) for the North Coast Region |
|
Evaluation Guideline: |
The chloride criterion continuous concentration (expressed as a 4-day average) to protect aquatic life in freshwater is 230000 ug/L (230 mg/L)(USEPA National Recommended Water Quality Criteria, 2006). |
Guideline Reference: |
National Recommended Water Quality Criteria. United States Environmental Protection Agency. Office of Water. Current as of 08/03/2016. |
|
Spatial Representation: |
The samples were collected at 1 monitoring site: 105PS0295 (Shasta River ~1mi above Cooley Gulch). |
Temporal Representation: |
The samples were collected between the dates of 2016-06-15 and 2016-06-15 |
Environmental Conditions: |
|
QAPP Information: |
QAPP for Surface Water Ambient Monitoring Program (SWAMP) |
QAPP Information Reference(s): |
Generic SWAMP QAPrP |
|
Line of Evidence (LOE) for Decision ID 157120, Chloride
|
Region 1 |
Klamath River HU, Shasta River HA |
|
|
LOE ID: |
324007 |
|
Pollutant: |
Chloride |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Dissolved |
|
Beneficial Use: |
Warm Freshwater Habitat |
|
Number of Samples: |
1 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP Reference Condition Management Plan data for Klamath River HU, Shasta River HA to determine beneficial use support and results are as follows: 0 of 1 samples exceeded the water quality threshold for Chloride. |
Data Reference: |
Benthic, Field, Habitat, WQ from the Surface Water Ambient Monitoring Program for the 2026 Integrated Report in Region 1 |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
Water Quality Control Plan, North Coast Region (NCRWQCB 2018): Waters designated for use as domestic or municipal supply (MUN) shall not contain concentrations of chemical constituents in excess of the limits specified in California Code of Regulations, Title 22, Chapter 15. The secondary maximum contaminant level listed in Table 64449-A for Aluminum is 0.2 mg/L. |
Objective/Criterion Reference: |
Water Quality Control Plan (Basin Plan) for the North Coast Region |
|
Evaluation Guideline: |
The chloride criterion continuous concentration (expressed as a 4-day average) to protect aquatic life in freshwater is 230000 ug/L (230 mg/L)(USEPA National Recommended Water Quality Criteria, 2006). |
Guideline Reference: |
National Recommended Water Quality Criteria. United States Environmental Protection Agency. Office of Water. Current as of 08/03/2016. |
|
Spatial Representation: |
The samples were collected at 1 monitoring site: 105WE0592 (Eddy Creek ~0.8 miles downstream from end of 4WD road.). |
Temporal Representation: |
The samples were collected between the dates of 2015-07-13 and 2015-07-13 |
Environmental Conditions: |
|
QAPP Information: |
QAPP for Surface Water Ambient Monitoring Program (SWAMP) |
QAPP Information Reference(s): |
Generic SWAMP QAPrP |
|
Line of Evidence (LOE) for Decision ID 157120, Chloride
|
Region 1 |
Klamath River HU, Shasta River HA |
|
|
LOE ID: |
46926 |
|
Pollutant: |
Chloride |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Not Recorded |
|
Beneficial Use: |
Municipal & Domestic Supply |
|
Number of Samples: |
32 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
None of the 32 chloride samples collected in the mainstem Shasta River exceed the evaluation guideline. The samples were collected as part of the Surface Water Ambient Water Monitoring Program (SWAMP). The data are found in the SWAMP Summary Report for the North Coast Region for Years 2000-2006 (NCRWQCB 2008). This LOE and LOE 46927 replace LOE 25416 from the 2010 Integrated Report cycle. The data were reevaluated in order to separate the date from the maintem Shasta River and Yreka Creek into two, separate LOEs. |
Data Reference: |
Surface Water Ambient Monitoring Program (SWAMP). Summary Report for the North Coast Region (RWQCB-1) for years 2000-2006. North Coast Regional Water Quality Control Board. March 2008 |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
Per the Basin Plan (NCRWQCB 2007): Waters shall not contain taste- or odorproducing substances in concentrations that impart undesirable tastes or odors to fish flesh or other edible products of aquatic origin, or that cause nuisance or adversely affect beneficial uses. |
Objective/Criterion Reference: |
Water Quality Control Plan (Basin Plan) - North Coast Region (Region 1) |
|
Evaluation Guideline: |
Per 22 CCR 64449: The recommended Secondary Maximum Contaminant Level for chloride is 250 mg/L. |
Guideline Reference: |
Title 22. Division 4. Chapter 15. Sections 64400 et seq. California Code of Regulations |
|
Spatial Representation: |
Samples were collected in the mainstem Shasta River from 3 locations as follows: (1) near Edgewood Road (SWAMP Station ID 105SHAEDG), (2) at Montague Grenada Road (SWAMP Station ID 105SHAMON), and (3) at Highway 263 (SWAMP Station ID 105SHA263). Samples were
collected in well-mixed flows in glides or riffles. |
Temporal Representation: |
The samples from Edgewood Road and Montague Grenada Road were collected as grab samples during 5 site visits at each site during the 2002 - 2003 fiscal years. Samples from Highway 263 were collected as grab samples during 22 site visits during the 2000 - 2006 fiscal years. |
Environmental Conditions: |
There are no known environmental conditions (e.g., seasonality, land use practices, fire events, storms, etc.) that are related to these data. |
QAPP Information: |
Quality control was conducted in accordance with the SWAMP Quality Assurance Management Plan (SWAMP 2002). |
QAPP Information Reference(s): |
Quality Assurance Management Plan for the State of California's Surface Water Ambient Monitoring Program. Sacramento, CA. State Water Resources Control Board. SWAMP. December 2002 (1st version)
|
|
Line of Evidence (LOE) for Decision ID 157120, Chloride
|
Region 1 |
Klamath River HU, Shasta River HA |
|
|
LOE ID: |
103164 |
|
Pollutant: |
Chloride |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Dissolved |
|
Beneficial Use: |
Municipal & Domestic Supply |
|
Number of Samples: |
5 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP RWB1 Monitoring data for Klamath River HU, Shasta River HA to determine beneficial use support and results are as follows: 0 of 5 samples exceeded the water quality standard for Chloride. |
Data Reference: |
Water Quality Assessment Data for the 2018 solicitation cycle submitted through CEDEN for SWAMP RWB1 Monitoring .
|
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
Water Quality Control Plan, North Coast Region (NCRWQCB 2018): Waters designated for use as domestic or municipal supply (MUN) shall not contain concentrations of chemical constituents in excess of the limits specified in California Code of Regulations, Title 22, Chapter 15. The secondary maximum contaminant level listed in Table 64449-B for chloride is 250 mg/L. |
Objective/Criterion Reference: |
Water Quality Control Plan (Basin Plan) for the North Coast Region |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
The samples were collected at 1 monitoring site(s) (105SH1452) |
Temporal Representation: |
The samples were collected between the dates of 2013-03-06 and 2013-11-20 |
Environmental Conditions: |
|
QAPP Information: |
Quality Assurance Program Plan and Standard Operating Procedures for SWAMP program |
QAPP Information Reference(s): |
Quality Assurance Program Plans, Quality Assurance Project Plans, and Standard Operating Procedures for the SWAMP program |
|
Line of Evidence (LOE) for Decision ID 157120, Chloride
|
Region 1 |
Klamath River HU, Shasta River HA |
|
|
LOE ID: |
103165 |
|
Pollutant: |
Chloride |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Dissolved |
|
Beneficial Use: |
Municipal & Domestic Supply |
|
Number of Samples: |
5 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP RWB1 Monitoring data for Klamath River HU, Shasta River HA to determine beneficial use support and results are as follows: 0 of 5 samples exceeded the water quality standard for Chloride. |
Data Reference: |
Water Quality Assessment Data for the 2018 solicitation cycle submitted through CEDEN for SWAMP RWB1 Monitoring .
|
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
Water Quality Control Plan, North Coast Region (NCRWQCB 2018): Waters designated for use as domestic or municipal supply (MUN) shall not contain concentrations of chemical constituents in excess of the limits specified in California Code of Regulations, Title 22, Chapter 15. The secondary maximum contaminant level listed in Table 64449-B for chloride is 250 mg/L. |
Objective/Criterion Reference: |
Water Quality Control Plan (Basin Plan) for the North Coast Region |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
The samples were collected at 1 monitoring site(s) (105SH9274) |
Temporal Representation: |
The samples were collected between the dates of 2013-03-07 and 2013-11-20 |
Environmental Conditions: |
|
QAPP Information: |
Quality Assurance Program Plan and Standard Operating Procedures for SWAMP program |
QAPP Information Reference(s): |
Quality Assurance Program Plans, Quality Assurance Project Plans, and Standard Operating Procedures for the SWAMP program |
|
Line of Evidence (LOE) for Decision ID 157120, Chloride
|
Region 1 |
Klamath River HU, Shasta River HA |
|
|
LOE ID: |
104459 |
|
Pollutant: |
Chloride |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Dissolved |
|
Beneficial Use: |
Municipal & Domestic Supply |
|
Number of Samples: |
1 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP Perennial Stream Surveys data for Klamath River HU, Shasta River HA to determine beneficial use support and results are as follows: 0 of 1 samples exceeded the water quality standard for Chloride. |
Data Reference: |
Water Quality Assessment Data for the 2018 solicitation cycle submitted through CEDEN for SWAMP Perennial Stream Surveys .
|
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
Water Quality Control Plan, North Coast Region (NCRWQCB 2018): Waters designated for use as domestic or municipal supply (MUN) shall not contain concentrations of chemical constituents in excess of the limits specified in California Code of Regulations, Title 22, Chapter 15. The secondary maximum contaminant level listed in Table 64449-B for chloride is 250 mg/L. |
Objective/Criterion Reference: |
Water Quality Control Plan (Basin Plan) for the North Coast Region |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
The samples were collected at 1 monitoring site(s) (105PS0231) |
Temporal Representation: |
The samples were collected between the dates of 2013-08-29 and 2013-08-29 |
Environmental Conditions: |
|
QAPP Information: |
Quality Assurance Program Plan and Standard Operating Procedures for SWAMP program |
QAPP Information Reference(s): |
Quality Assurance Program Plans, Quality Assurance Project Plans, and Standard Operating Procedures for the SWAMP program |
|
Line of Evidence (LOE) for Decision ID 157120, Chloride
|
Region 1 |
Klamath River HU, Shasta River HA |
|
|
LOE ID: |
43795 |
|
Pollutant: |
Chloride |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Not Recorded |
|
Beneficial Use: |
Municipal & Domestic Supply |
|
Number of Samples: |
1 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP data for Klamath River HU, Shasta River HA to determine beneficial use support and results are as follows: 0 of 1 samples exceed the criterion for Chloride. |
Data Reference: |
Statewide Perennial Streams Assessment 2008 |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
Water Quality Control Plan, North Coast Region (NCRWQCB 2011): Waters designated for use as domestic or municipal supply (MUN) shall not contain concentrations of chemical constituents in excess of the limits specified in California Code of Regulations, Title 22, Chapter 15. The secondary maximum contaminant level listed in Table 64449-A for chloride is 250 mg/L. |
Objective/Criterion Reference: |
Secondary Maximum Contaminant Levels and Compliance. CCR Title 22 section 64449. |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
Data for this line of evidence for Klamath River HU, Shasta River HA was collected at 1 monitoring site [ Evans Ditch - 105PS0188 ] |
Temporal Representation: |
Data was collected on a single day 8/26/2008. |
Environmental Conditions: |
Staff is not aware of any special conditions that might affect interpretation of the data. |
QAPP Information: |
The SWAMP QAPP (2008) was followed. |
QAPP Information Reference(s): |
Surface Water Ambient Monitoring Program Quality Assurance Program Plan |
|
Line of Evidence (LOE) for Decision ID 157120, Chloride
|
Region 1 |
Klamath River HU, Shasta River HA |
|
|
LOE ID: |
25416 |
|
Pollutant: |
Chloride |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Not Recorded |
|
Beneficial Use: |
Municipal & Domestic Supply |
|
Number of Samples: |
41 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
None of the 41 chloride samples collected in the Shasta River exceed the evaluation guideline. The samples were collected as part of the Surface Water Ambient Water Monitoring Program (SWAMP). The data are found in the SWAMP Summary Report for the North Coast Region for Years 2000-2006 (NCRWQCB 2008). |
Data Reference: |
Surface Water Ambient Monitoring Program (SWAMP). Summary Report for the North Coast Region (RWQCB-1) for years 2000-2006. North Coast Regional Water Quality Control Board. March 2008 |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
Per the Basin Plan (NCRWQCB 2007): Waters shall not contain taste- or odor-producing substances in concentrations that impart undesirable tastes or odors to fish flesh or other edible products of aquatic origin, or that cause nuisance or adversely affect beneficial uses. |
Objective/Criterion Reference: |
Water Quality Control Plan (Basin Plan) - North Coast Region (Region 1) |
|
Evaluation Guideline: |
Per 22 CCR 64449: The recommended Secondary Maximum Contaminant Level for chloride is 250 mg/L. |
Guideline Reference: |
Title 22. Division 4. Chapter 15. Sections 64400 et seq. California Code of Regulations |
|
Spatial Representation: |
Samples were collected in the mainstem Shasta River from 3 locations as follows: (1) near Edgewood Road (SWAMP Station ID 105SHAEDG), (2) at Montague Grenada Road (SWAMP Station ID 105SHAMON), (3) at Highway 263 (SWAMP Station ID 105SHA263), (4) at Highway 3 (SWAMP Station ID 105YREHW3), and (5) at Anderson Grade Road (SWAMP Station ID 105YREAND). Samples were collected in well-mixed flows in glides or riffles. |
Temporal Representation: |
The samples from Edgewood Road and Montague Grenada Road were collected as grab samples during 5 site visits at each site during the 2002 - 2003 fiscal years. Samples from Highway 263 were collected as grab samples during 22 site visits during the 2000 - 2006 fiscal years. Samples in Yreka Creek were collected from October 2004 to June 2005. The site visits corresponded to fall, winter, spring and early summer seasonal conditions. |
Environmental Conditions: |
There are no known environmental conditions (e.g., seasonality, land use practices, fire events, storms, etc.) that are related to these data. |
QAPP Information: |
Quality control was conducted in accordance with the SWAMP Quality Assurance Management Plan (SWAMP 2002). |
QAPP Information Reference(s): |
Quality Assurance Management Plan for the State of California's Surface Water Ambient Monitoring Program. Sacramento, CA. State Water Resources Control Board. SWAMP. December 2002 (1st version)
|
|
Line of Evidence (LOE) for Decision ID 157120, Chloride
|
Region 1 |
Klamath River HU, Shasta River HA |
|
|
LOE ID: |
34235 |
|
Pollutant: |
Chloride |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Not Recorded |
|
Beneficial Use: |
Municipal & Domestic Supply |
|
Number of Samples: |
4 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
None of the 4 samples collected exceeded the evaluation guideline. |
Data Reference: |
RWB1 Trend Maintenance Periods FYs 2007 2008 |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
Per the Basin Plan (NCRWQCB 2011): Waters shall not contain taste- or odor-producing substances in concentrations that impart undesirable tastes or odors to fish flesh or other edible products of aquatic origin, or that cause nuisance or adversely affect beneficial uses. |
Objective/Criterion Reference: |
Water Quality Control Plan (Basin Plan) for the North Coast Region |
|
Evaluation Guideline: |
Per 22 CCR 64449: The recommended Secondary Maximum Contaminant Level for chloride is 250 mg/L. |
Guideline Reference: |
Title 22. Division 4. Chapter 15. Sections 64400 et seq. California Code of Regulations |
|
Spatial Representation: |
Samples were collected from the Shasta River at Hwy 263 station (105SHA263). |
Temporal Representation: |
Samples were collected approximately once per quarter year from November 2007 to July 2008. |
Environmental Conditions: |
|
QAPP Information: |
SWAMP QAPP |
QAPP Information Reference(s): |
Surface Water Ambient Monitoring Program Quality Assurance Program Plan |
|
Line of Evidence (LOE) for Decision ID 157120, Chloride
|
Region 1 |
Klamath River HU, Shasta River HA |
|
|
LOE ID: |
34256 |
|
Pollutant: |
Chloride |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Not Recorded |
|
Beneficial Use: |
Municipal & Domestic Supply |
|
Number of Samples: |
4 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
None of the 4 samples collected exceeded the evaluation guideline. |
Data Reference: |
RWB1 Trend Maintenance Periods FYs 2007 2008 |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
Per the Basin Plan (NCRWQCB 2011): Waters shall not contain taste- or odor-producing substances in concentrations that impart undesirable tastes or odors to fish flesh or other edible products of aquatic origin, or that cause nuisance or adversely affect beneficial uses. |
Objective/Criterion Reference: |
Water Quality Control Plan (Basin Plan) for the North Coast Region |
|
Evaluation Guideline: |
Per 22 CCR 64449: The recommended Secondary Maximum Contaminant Level for chloride is 250 mg/L. |
Guideline Reference: |
Title 22. Division 4. Chapter 15. Sections 64400 et seq. California Code of Regulations |
|
Spatial Representation: |
Samples were collected from the Shasta River near Edgewood station (105SHAEDG). |
Temporal Representation: |
Samples were collected approximately once per quarter year from November 2007 to July 2008. |
Environmental Conditions: |
|
QAPP Information: |
SWAMP QAPP |
QAPP Information Reference(s): |
Surface Water Ambient Monitoring Program Quality Assurance Program Plan |
|
Line of Evidence (LOE) for Decision ID 168788, Chlorpyrifos, methyl
|
Region 1 |
Klamath River HU, Shasta River HA |
|
|
LOE ID: |
123230 |
|
Pollutant: |
Chlorpyrifos, methyl |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
None |
|
Beneficial Use: |
Municipal & Domestic Supply |
|
Number of Samples: |
8 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
State Water Board staff re-assessed SWAMP data for Klamath River HU, Shasta River HA to determine beneficial use support and results are as follows: 0 of 8 samples exceed the criterion for Chlorpyrifos Methyl, Total. This LOE re-assesses data from LOE 29849 from the 2010 Integrated Report. Data were re-assessed in order to evaluate these data in their own LOE, instead of being evaluated in the same LOE as other pesticide data. |
Data Reference: |
Surface Water Ambient Monitoring Program (SWAMP). Summary Report for the North Coast Region (RWQCB-1) for years 2000-2006. North Coast Regional Water Quality Control Board. March 2008 |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
Water Quality Control Plan, North Coast Region (NCRWQCB 2011): All waters shall be maintained free of toxic substances in concentrations that are toxic to, or that produce detrimental physiological responses in human, plant, animal, or aquatic life. The USEPA Health Advisory for life time exposure to Chlorpyrifos is 0.002 mg/L (EPA 820-R-11-002 Drinking Water Standards and Health Advisories, 2011). |
Objective/Criterion Reference: |
Water Quality Control Plan (Basin Plan) for the North Coast Region |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
Data for this line of evidence for Klamath River HU, Shasta River HA was collected at 1 monitoring site [ Yreka Creek at Highway 3 - 105YREHW3] |
Temporal Representation: |
Data was collected over the time period 10/21/2004-6/20/2005. |
Environmental Conditions: |
There are no known environmental conditions (e.g., seasonality, land use practices, fire events, storms, etc.) that are related to these data. |
QAPP Information: |
Quality control was conducted in accordance with the SWAMP Quality Assurance Management Plan (SWAMP 2002). |
QAPP Information Reference(s): |
Quality Assurance Management Plan for the State of California's Surface Water Ambient Monitoring Program. Sacramento, CA. State Water Resources Control Board. SWAMP. December 2002 (1st version)
|
|
Line of Evidence (LOE) for Decision ID 168788, Chlorpyrifos, methyl
|
Region 1 |
Klamath River HU, Shasta River HA |
|
|
LOE ID: |
123216 |
|
Pollutant: |
Chlorpyrifos, methyl |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
None |
|
Beneficial Use: |
Municipal & Domestic Supply |
|
Number of Samples: |
32 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
State Water Board staff re-assessed SWAMP data for Klamath River HU, Shasta River HA to determine beneficial use support and results are as follows: 0 of 32 samples exceed the criterion for Chlorpyrifos Methyl, Total. This LOE re-assesses data from LOE 29849 from the 2010 Integrated Report. Data were re-assessed in order to evaluate these data in their own LOE, instead of being evaluated in the same LOE as other pesticide data. |
Data Reference: |
Surface Water Ambient Monitoring Program (SWAMP). Summary Report for the North Coast Region (RWQCB-1) for years 2000-2006. North Coast Regional Water Quality Control Board. March 2008 |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
Water Quality Control Plan, North Coast Region (NCRWQCB 2011): All waters shall be maintained free of toxic substances in concentrations that are toxic to, or that produce detrimental physiological responses in human, plant, animal, or aquatic life. The USEPA Health Advisory for life time exposure to Chlorpyrifos is 0.002 mg/L (EPA 820-R-11-002 Drinking Water Standards and Health Advisories, 2011). |
Objective/Criterion Reference: |
Water Quality Control Plan (Basin Plan) for the North Coast Region |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
Data for this line of evidence for Klamath River HU, Shasta River HA was collected at 1 monitoring site [ Shasta River at Hwy 263 - 105SH1452] |
Temporal Representation: |
Data was collected over the time period 2/27/2002-11/16/2006. |
Environmental Conditions: |
There are no known environmental conditions (e.g., seasonality, land use practices, fire events, storms, etc.) that are related to these data. |
QAPP Information: |
Quality control was conducted in accordance with the SWAMP Quality Assurance Management Plan (SWAMP 2002). |
QAPP Information Reference(s): |
Quality Assurance Management Plan for the State of California's Surface Water Ambient Monitoring Program. Sacramento, CA. State Water Resources Control Board. SWAMP. December 2002 (1st version)
|
|
Line of Evidence (LOE) for Decision ID 168788, Chlorpyrifos, methyl
|
Region 1 |
Klamath River HU, Shasta River HA |
|
|
LOE ID: |
103166 |
|
Pollutant: |
Chlorpyrifos, methyl |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Total |
|
Beneficial Use: |
Cold Freshwater Habitat |
|
Number of Samples: |
3 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP RWB1 Monitoring data for Klamath River HU, Shasta River HA to determine beneficial use support and results are as follows: 0 of 3 samples exceeded the water quality standard for Chlorpyrifos Methyl. |
Data Reference: |
Water Quality Assessment Data for the 2018 solicitation cycle submitted through CEDEN for SWAMP RWB1 Monitoring .
|
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
All waters shall be maintained free of toxic substances in concentrations which are toxic to, or which produce detrimental physiological responses in, human, plant, animal, or aquatic life. (Basin Plan). |
Objective/Criterion Reference: |
Water Quality Control Plan (Basin Plan) for the North Coast Region |
|
Evaluation Guideline: |
The evaluation guideline for Chlorpyrifos Methyl is the USEPA Aquatic Life Benchmark of 0.085 ug/L for an invertebrate (acute). |
Guideline Reference: |
OPP Aquatic Life Benchmarks |
|
Spatial Representation: |
The samples were collected at 1 monitoring site(s) (105SH1452) |
Temporal Representation: |
The samples were collected between the dates of 2013-03-06 and 2013-11-20 |
Environmental Conditions: |
|
QAPP Information: |
Quality Assurance Program Plan and Standard Operating Procedures for SWAMP program |
QAPP Information Reference(s): |
Quality Assurance Program Plans, Quality Assurance Project Plans, and Standard Operating Procedures for the SWAMP program |
|
Line of Evidence (LOE) for Decision ID 168788, Chlorpyrifos, methyl
|
Region 1 |
Klamath River HU, Shasta River HA |
|
|
LOE ID: |
103169 |
|
Pollutant: |
Chlorpyrifos, methyl |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Total |
|
Beneficial Use: |
Warm Freshwater Habitat |
|
Number of Samples: |
3 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP RWB1 Monitoring data for Klamath River HU, Shasta River HA to determine beneficial use support and results are as follows: 0 of 3 samples exceeded the water quality standard for Chlorpyrifos Methyl. |
Data Reference: |
Water Quality Assessment Data for the 2018 solicitation cycle submitted through CEDEN for SWAMP RWB1 Monitoring .
|
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
All waters shall be maintained free of toxic substances in concentrations which are toxic to, or which produce detrimental physiological responses in, human, plant, animal, or aquatic life. (Basin Plan). |
Objective/Criterion Reference: |
Water Quality Control Plan (Basin Plan) for the North Coast Region |
|
Evaluation Guideline: |
The evaluation guideline for Chlorpyrifos Methyl is the USEPA Aquatic Life Benchmark of 0.085 ug/L for an invertebrate (acute). |
Guideline Reference: |
OPP Aquatic Life Benchmarks |
|
Spatial Representation: |
The samples were collected at 1 monitoring site(s) (105SH9274) |
Temporal Representation: |
The samples were collected between the dates of 2013-03-07 and 2013-11-20 |
Environmental Conditions: |
|
QAPP Information: |
Quality Assurance Program Plan and Standard Operating Procedures for SWAMP program |
QAPP Information Reference(s): |
Quality Assurance Program Plans, Quality Assurance Project Plans, and Standard Operating Procedures for the SWAMP program |
|
Line of Evidence (LOE) for Decision ID 168788, Chlorpyrifos, methyl
|
Region 1 |
Klamath River HU, Shasta River HA |
|
|
LOE ID: |
103168 |
|
Pollutant: |
Chlorpyrifos, methyl |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Total |
|
Beneficial Use: |
Cold Freshwater Habitat |
|
Number of Samples: |
3 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP RWB1 Monitoring data for Klamath River HU, Shasta River HA to determine beneficial use support and results are as follows: 0 of 3 samples exceeded the water quality standard for Chlorpyrifos Methyl. |
Data Reference: |
Water Quality Assessment Data for the 2018 solicitation cycle submitted through CEDEN for SWAMP RWB1 Monitoring .
|
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
All waters shall be maintained free of toxic substances in concentrations which are toxic to, or which produce detrimental physiological responses in, human, plant, animal, or aquatic life. (Basin Plan). |
Objective/Criterion Reference: |
Water Quality Control Plan (Basin Plan) for the North Coast Region |
|
Evaluation Guideline: |
The evaluation guideline for Chlorpyrifos Methyl is the USEPA Aquatic Life Benchmark of 0.085 ug/L for an invertebrate (acute). |
Guideline Reference: |
OPP Aquatic Life Benchmarks |
|
Spatial Representation: |
The samples were collected at 1 monitoring site(s) (105SH9274) |
Temporal Representation: |
The samples were collected between the dates of 2013-03-07 and 2013-11-20 |
Environmental Conditions: |
|
QAPP Information: |
Quality Assurance Program Plan and Standard Operating Procedures for SWAMP program |
QAPP Information Reference(s): |
Quality Assurance Program Plans, Quality Assurance Project Plans, and Standard Operating Procedures for the SWAMP program |
|
Line of Evidence (LOE) for Decision ID 168788, Chlorpyrifos, methyl
|
Region 1 |
Klamath River HU, Shasta River HA |
|
|
LOE ID: |
103167 |
|
Pollutant: |
Chlorpyrifos, methyl |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Total |
|
Beneficial Use: |
Warm Freshwater Habitat |
|
Number of Samples: |
3 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP RWB1 Monitoring data for Klamath River HU, Shasta River HA to determine beneficial use support and results are as follows: 0 of 3 samples exceeded the water quality standard for Chlorpyrifos Methyl. |
Data Reference: |
Water Quality Assessment Data for the 2018 solicitation cycle submitted through CEDEN for SWAMP RWB1 Monitoring .
|
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
All waters shall be maintained free of toxic substances in concentrations which are toxic to, or which produce detrimental physiological responses in, human, plant, animal, or aquatic life. (Basin Plan). |
Objective/Criterion Reference: |
Water Quality Control Plan (Basin Plan) for the North Coast Region |
|
Evaluation Guideline: |
The evaluation guideline for Chlorpyrifos Methyl is the USEPA Aquatic Life Benchmark of 0.085 ug/L for an invertebrate (acute). |
Guideline Reference: |
OPP Aquatic Life Benchmarks |
|
Spatial Representation: |
The samples were collected at 1 monitoring site(s) (105SH1452) |
Temporal Representation: |
The samples were collected between the dates of 2013-03-06 and 2013-11-20 |
Environmental Conditions: |
|
QAPP Information: |
Quality Assurance Program Plan and Standard Operating Procedures for SWAMP program |
QAPP Information Reference(s): |
Quality Assurance Program Plans, Quality Assurance Project Plans, and Standard Operating Procedures for the SWAMP program |
|
Line of Evidence (LOE) for Decision ID 168788, Chlorpyrifos, methyl
|
Region 1 |
Klamath River HU, Shasta River HA |
|
|
LOE ID: |
123228 |
|
Pollutant: |
Chlorpyrifos, methyl |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
None |
|
Beneficial Use: |
Municipal & Domestic Supply |
|
Number of Samples: |
8 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
State Water Board staff re-assessed SWAMP data for Klamath River HU, Shasta River HA to determine beneficial use support and results are as follows: 0 of 8 samples exceed the criterion for Chlorpyrifos Methyl, Total. This LOE re-assesses data from LOE 29849 from the 2010 Integrated Report. Data were re-assessed in order to evaluate these data in their own LOE, instead of being evaluated in the same LOE as other pesticide data. |
Data Reference: |
Surface Water Ambient Monitoring Program (SWAMP). Summary Report for the North Coast Region (RWQCB-1) for years 2000-2006. North Coast Regional Water Quality Control Board. March 2008 |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
Water Quality Control Plan, North Coast Region (NCRWQCB 2011): All waters shall be maintained free of toxic substances in concentrations that are toxic to, or that produce detrimental physiological responses in human, plant, animal, or aquatic life. The USEPA Health Advisory for life time exposure to Chlorpyrifos is 0.002 mg/L (EPA 820-R-11-002 Drinking Water Standards and Health Advisories, 2011). |
Objective/Criterion Reference: |
Water Quality Control Plan (Basin Plan) for the North Coast Region |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
Data for this line of evidence for Klamath River HU, Shasta River HA was collected at 1 monitoring site [ Shasta River near Edgewood - 105SH9274] |
Temporal Representation: |
Data was collected over the time period 10/7/2002-6/19/2003. |
Environmental Conditions: |
There are no known environmental conditions (e.g., seasonality, land use practices, fire events, storms, etc.) that are related to these data. |
QAPP Information: |
Quality control was conducted in accordance with the SWAMP Quality Assurance Management Plan (SWAMP 2002). |
QAPP Information Reference(s): |
Quality Assurance Management Plan for the State of California's Surface Water Ambient Monitoring Program. Sacramento, CA. State Water Resources Control Board. SWAMP. December 2002 (1st version)
|
|
Line of Evidence (LOE) for Decision ID 168788, Chlorpyrifos, methyl
|
Region 1 |
Klamath River HU, Shasta River HA |
|
|
LOE ID: |
123227 |
|
Pollutant: |
Chlorpyrifos, methyl |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
None |
|
Beneficial Use: |
Municipal & Domestic Supply |
|
Number of Samples: |
8 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
State Water Board staff re-assessed SWAMP data for Klamath River HU, Shasta River HA to determine beneficial use support and results are as follows: 0 of 8 samples exceed the criterion for Chlorpyrifos Methyl, Total. This LOE re-assesses data from LOE 29849 from the 2010 Integrated Report. Data were re-assessed in order to evaluate these data in their own LOE, instead of being evaluated in the same LOE as other pesticide data. |
Data Reference: |
Surface Water Ambient Monitoring Program (SWAMP). Summary Report for the North Coast Region (RWQCB-1) for years 2000-2006. North Coast Regional Water Quality Control Board. March 2008 |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
Water Quality Control Plan, North Coast Region (NCRWQCB 2011): All waters shall be maintained free of toxic substances in concentrations that are toxic to, or that produce detrimental physiological responses in human, plant, animal, or aquatic life. The USEPA Health Advisory for life time exposure to Chlorpyrifos is 0.002 mg/L (EPA 820-R-11-002 Drinking Water Standards and Health Advisories, 2011). |
Objective/Criterion Reference: |
Water Quality Control Plan (Basin Plan) for the North Coast Region |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
Data for this line of evidence for Klamath River HU, Shasta River HA was collected at 1 monitoring site [ Shasta River at Montague - 105SHAMON] |
Temporal Representation: |
Data was collected over the time period 10/7/2002-6/19/2003. |
Environmental Conditions: |
There are no known environmental conditions (e.g., seasonality, land use practices, fire events, storms, etc.) that are related to these data. |
QAPP Information: |
Quality control was conducted in accordance with the SWAMP Quality Assurance Management Plan (SWAMP 2002). |
QAPP Information Reference(s): |
Quality Assurance Management Plan for the State of California's Surface Water Ambient Monitoring Program. Sacramento, CA. State Water Resources Control Board. SWAMP. December 2002 (1st version)
|
|
Line of Evidence (LOE) for Decision ID 168788, Chlorpyrifos, methyl
|
Region 1 |
Klamath River HU, Shasta River HA |
|
|
LOE ID: |
123229 |
|
Pollutant: |
Chlorpyrifos, methyl |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
None |
|
Beneficial Use: |
Municipal & Domestic Supply |
|
Number of Samples: |
16 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
State Water Board staff re-assessed SWAMP data for Klamath River HU, Shasta River HA to determine beneficial use support and results are as follows: 0 of 16 samples exceed the criterion for Chlorpyrifos Methyl, Total. This LOE re-assesses data from LOE 29849 from the 2010 Integrated Report. Data were re-assessed in order to evaluate these data in their own LOE, instead of being evaluated in the same LOE as other pesticide data. |
Data Reference: |
Surface Water Ambient Monitoring Program (SWAMP). Summary Report for the North Coast Region (RWQCB-1) for years 2000-2006. North Coast Regional Water Quality Control Board. March 2008 |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
Water Quality Control Plan, North Coast Region (NCRWQCB 2011): All waters shall be maintained free of toxic substances in concentrations that are toxic to, or that produce detrimental physiological responses in human, plant, animal, or aquatic life. The USEPA Health Advisory for life time exposure to Chlorpyrifos is 0.002 mg/L (EPA 820-R-11-002 Drinking Water Standards and Health Advisories, 2011). |
Objective/Criterion Reference: |
Water Quality Control Plan (Basin Plan) for the North Coast Region |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
Data for this line of evidence for Klamath River HU, Shasta River HA was collected at 1 monitoring site [ Yreka Creek at Anderson Rd - 105YREAND] |
Temporal Representation: |
Data was collected over the time period 10/9/2002-6/20/2005. |
Environmental Conditions: |
There are no known environmental conditions (e.g., seasonality, land use practices, fire events, storms, etc.) that are related to these data. |
QAPP Information: |
Quality control was conducted in accordance with the SWAMP Quality Assurance Management Plan (SWAMP 2002). |
QAPP Information Reference(s): |
Quality Assurance Management Plan for the State of California's Surface Water Ambient Monitoring Program. Sacramento, CA. State Water Resources Control Board. SWAMP. December 2002 (1st version)
|
|
Line of Evidence (LOE) for Decision ID 100785, Chromium
|
Region 1 |
Klamath River HU, Shasta River HA |
|
|
LOE ID: |
103172 |
|
Pollutant: |
Chromium |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Dissolved |
|
Beneficial Use: |
Cold Freshwater Habitat |
|
Number of Samples: |
1 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP RWB1 Monitoring data for Klamath River HU, Shasta River HA to determine beneficial use support and results are as follows: 0 of 1 samples exceeded the water quality standard for Chromium. |
Data Reference: |
Water Quality Assessment Data for the 2018 solicitation cycle submitted through CEDEN for SWAMP RWB1 Monitoring .
|
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
California Toxics Rule (CTR) lists criterion continuous concentrations to protect aquatic life in freshwater. The criterion in freshwater is hardness dependent for each sample and varies based on the ambient hardness during sampling. Section (b)(1) in CTR contains the hardness dependent formula for the metals criterion. |
Objective/Criterion Reference: |
Water Quality Standards 2000. Establishment of numeric criteria for priority toxic pollutants for the State of California: Rules and regulations. Federal Register Vol. 65, No. 97. Washington, D.C.: Environmental Protection Agency |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
The samples were collected at 1 monitoring site(s) (105SH1452) |
Temporal Representation: |
The samples were collected between the dates of 2013-07-30 and 2013-07-30 |
Environmental Conditions: |
|
QAPP Information: |
Quality Assurance Program Plan and Standard Operating Procedures for SWAMP program |
QAPP Information Reference(s): |
Quality Assurance Program Plans, Quality Assurance Project Plans, and Standard Operating Procedures for the SWAMP program |
|
Line of Evidence (LOE) for Decision ID 100785, Chromium
|
Region 1 |
Klamath River HU, Shasta River HA |
|
|
LOE ID: |
103175 |
|
Pollutant: |
Chromium |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Dissolved |
|
Beneficial Use: |
Cold Freshwater Habitat |
|
Number of Samples: |
1 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP RWB1 Monitoring data for Klamath River HU, Shasta River HA to determine beneficial use support and results are as follows: 0 of 1 samples exceeded the water quality standard for Chromium. |
Data Reference: |
Water Quality Assessment Data for the 2018 solicitation cycle submitted through CEDEN for SWAMP RWB1 Monitoring .
|
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
California Toxics Rule (CTR) lists criterion continuous concentrations to protect aquatic life in freshwater. The criterion in freshwater is hardness dependent for each sample and varies based on the ambient hardness during sampling. Section (b)(1) in CTR contains the hardness dependent formula for the metals criterion. |
Objective/Criterion Reference: |
Water Quality Standards 2000. Establishment of numeric criteria for priority toxic pollutants for the State of California: Rules and regulations. Federal Register Vol. 65, No. 97. Washington, D.C.: Environmental Protection Agency |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
The samples were collected at 1 monitoring site(s) (105SH9274) |
Temporal Representation: |
The samples were collected between the dates of 2013-07-30 and 2013-07-30 |
Environmental Conditions: |
|
QAPP Information: |
Quality Assurance Program Plan and Standard Operating Procedures for SWAMP program |
QAPP Information Reference(s): |
Quality Assurance Program Plans, Quality Assurance Project Plans, and Standard Operating Procedures for the SWAMP program |
|
Line of Evidence (LOE) for Decision ID 100785, Chromium
|
Region 1 |
Klamath River HU, Shasta River HA |
|
|
LOE ID: |
41177 |
|
Pollutant: |
Chromium |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Total |
|
Beneficial Use: |
Municipal & Domestic Supply |
|
Number of Samples: |
4 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP data for Klamath River HU, Shasta River HA to determine beneficial use support and results are as follows: 0 of 4 samples exceed the criterion for Chromium. |
Data Reference: |
RWB1 Trend Maintenance Periods FYs 2007 2008 |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
Water Quality Control Plan, North Coast Region (NCRWQCB 2011): Waters designated for use as domestic or municipal supply (MUN) shall not contain concentrations of chemical constituents in excess of the limits specified in California Code of Regulations, Title 22, Chapter 15. The maximum contaminant level listed in Table 64431-A for chromium 0.05 mg/L. |
Objective/Criterion Reference: |
Maximum Contaminant Levels for organic and inorganic chemicals. CCR Title 22 |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
Data for this line of evidence for Klamath River HU, Shasta River HA was collected at 1 monitoring site [ Shasta River at Hwy 263 - 105SHA263] |
Temporal Representation: |
Data was collected over the time period 11/15/2007-7/16/2008. |
Environmental Conditions: |
Staff is not aware of any special conditions that might affect interpretation of the data. |
QAPP Information: |
The SWAMP QAPP (2008) was followed. |
QAPP Information Reference(s): |
Surface Water Ambient Monitoring Program Quality Assurance Program Plan |
|
Line of Evidence (LOE) for Decision ID 100785, Chromium
|
Region 1 |
Klamath River HU, Shasta River HA |
|
|
LOE ID: |
123240 |
|
Pollutant: |
Chromium |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Total |
|
Beneficial Use: |
Municipal & Domestic Supply |
|
Number of Samples: |
22 |
Number of Exceedances: |
3 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
State Water Board staff re-assessed SWAMP data for Klamath River HU, Shasta River HA to determine beneficial use support and results are as follows: 3 of 22 samples exceed the criterion for Chromium, Total. This LOE re-assesses data from LOE 21509 from the 2010 Integrated Report. Data were re-assessed in order to evaluate these data in their own LOE, instead of being evaluated in the same LOE as other metals data. |
Data Reference: |
Surface Water Ambient Monitoring Program (SWAMP). Summary Report for the North Coast Region (RWQCB-1) for years 2000-2006. North Coast Regional Water Quality Control Board. March 2008 |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
Water Quality Control Plan, North Coast Region (NCRWQCB 2011): Waters designated for use as domestic or municipal supply (MUN) shall not contain concentrations of chemical constituents in excess of the limits specified in California Code of Regulations, Title 22, Chapter 15. The maximum contaminant level listed in Table 64431-A for chromium 0.05 mg/L. |
Objective/Criterion Reference: |
Water Quality Control Plan (Basin Plan) for the North Coast Region |
Objective/Criterion Reference: |
Maximum Contaminant Levels for organic and inorganic chemicals. CCR Title 22 |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
Data for this line of evidence for Klamath River HU, Shasta River HA was collected at 1 monitoring site [ Shasta River at Hwy 263 - 105SH1452] |
Temporal Representation: |
Data was collected over the time period 3/20/2001-11/16/2006. |
Environmental Conditions: |
There are no known environmental conditions (e.g., seasonality, land use practices, fire events, storms, etc.) that are related to these data. |
QAPP Information: |
Quality control was conducted in accordance with the SWAMP Quality Assurance Management Plan (SWAMP 2002). |
QAPP Information Reference(s): |
Quality Assurance Management Plan for the State of California's Surface Water Ambient Monitoring Program. Sacramento, CA. State Water Resources Control Board. SWAMP. December 2002 (1st version)
|
|
Line of Evidence (LOE) for Decision ID 100785, Chromium
|
Region 1 |
Klamath River HU, Shasta River HA |
|
|
LOE ID: |
34014 |
|
Pollutant: |
Chromium |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Total |
|
Beneficial Use: |
Cold Freshwater Habitat |
|
Number of Samples: |
4 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
None of the 4 samples exceeded the hardness based criteria calculated for chromium III or the criteria for chromium VI. |
Data Reference: |
RWB1 Trend Maintenance Periods FYs 2007 2008 |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
Water Quality Control Plan, North Coast Region (NCRWQCB 2011): All waters shall be maintained free of toxic substances in concentrations that are toxic to, or that produce detrimental physiological responses in human, plant, animal, or aquatic life. California Toxics Rule (CTR) lists criterion continuous concentrations (4-day average) to protect aquatic life in freshwater. The criterion in freshwater is hardness dependent for each chromium III sample and varies based on the ambient hardness during sampling. Section (b)(1) in CTR contains the hardness dependent formula for the metals criterion. The criterion continuous concentration (4-day average) to protect aquatic life in freshwater for chromium VI is 11 ug/L and is not hardness dependent. |
Objective/Criterion Reference: |
Code of Federal Regulations 40 part 131.38 Establishment of numeric criteria for priority toxic pollutants for the State of California. 7/1/2011 Edition |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
Samples collected at station 105SHAEDG (Shasta River near Edgewood). |
Temporal Representation: |
Samples collected between 11/15/07 and 7/16/08. |
Environmental Conditions: |
|
QAPP Information: |
SWAMP QAPP (2008) was followed. |
QAPP Information Reference(s): |
Surface Water Ambient Monitoring Program Quality Assurance Program Plan |
|
Line of Evidence (LOE) for Decision ID 100785, Chromium
|
Region 1 |
Klamath River HU, Shasta River HA |
|
|
LOE ID: |
103176 |
|
Pollutant: |
Chromium |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Dissolved |
|
Beneficial Use: |
Warm Freshwater Habitat |
|
Number of Samples: |
1 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP RWB1 Monitoring data for Klamath River HU, Shasta River HA to determine beneficial use support and results are as follows: 0 of 1 samples exceeded the water quality standard for Chromium. |
Data Reference: |
Water Quality Assessment Data for the 2018 solicitation cycle submitted through CEDEN for SWAMP RWB1 Monitoring .
|
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
California Toxics Rule (CTR) lists criterion continuous concentrations to protect aquatic life in freshwater. The criterion in freshwater is hardness dependent for each sample and varies based on the ambient hardness during sampling. Section (b)(1) in CTR contains the hardness dependent formula for the metals criterion. |
Objective/Criterion Reference: |
Water Quality Standards 2000. Establishment of numeric criteria for priority toxic pollutants for the State of California: Rules and regulations. Federal Register Vol. 65, No. 97. Washington, D.C.: Environmental Protection Agency |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
The samples were collected at 1 monitoring site(s) (105SH9274) |
Temporal Representation: |
The samples were collected between the dates of 2013-07-30 and 2013-07-30 |
Environmental Conditions: |
|
QAPP Information: |
Quality Assurance Program Plan and Standard Operating Procedures for SWAMP program |
QAPP Information Reference(s): |
Quality Assurance Program Plans, Quality Assurance Project Plans, and Standard Operating Procedures for the SWAMP program |
|
Line of Evidence (LOE) for Decision ID 100785, Chromium
|
Region 1 |
Klamath River HU, Shasta River HA |
|
|
LOE ID: |
103178 |
|
Pollutant: |
Chromium |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Total |
|
Beneficial Use: |
Municipal & Domestic Supply |
|
Number of Samples: |
5 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP RWB1 Monitoring data for Klamath River HU, Shasta River HA to determine beneficial use support and results are as follows: 0 of 5 samples exceeded the water quality standard for Chromium. |
Data Reference: |
Water Quality Assessment Data for the 2018 solicitation cycle submitted through CEDEN for SWAMP RWB1 Monitoring .
|
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
Water Quality Control Plan, North Coast Region (NCRWQCB 2018): Waters designated for use as domestic or municipal supply (MUN) shall not contain concentrations of chemical constituents in excess of the limits specified in California Code of Regulations, Title 22, Chapter 15. The maximum contaminant level listed in Table 64431-A for chromium 0.05 mg/L. |
Objective/Criterion Reference: |
Water Quality Control Plan (Basin Plan) for the North Coast Region |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
The samples were collected at 1 monitoring site(s) (105SH9274) |
Temporal Representation: |
The samples were collected between the dates of 2013-03-07 and 2013-11-20 |
Environmental Conditions: |
|
QAPP Information: |
Quality Assurance Program Plan and Standard Operating Procedures for SWAMP program |
QAPP Information Reference(s): |
Quality Assurance Program Plans, Quality Assurance Project Plans, and Standard Operating Procedures for the SWAMP program |
|
Line of Evidence (LOE) for Decision ID 100785, Chromium
|
Region 1 |
Klamath River HU, Shasta River HA |
|
|
LOE ID: |
123242 |
|
Pollutant: |
Chromium |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Total |
|
Beneficial Use: |
Municipal & Domestic Supply |
|
Number of Samples: |
5 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
State Water Board staff re-assessed SWAMP data for Klamath River HU, Shasta River HA to determine beneficial use support and results are as follows: 0 of 5 samples exceed the criterion for Chromium, Total. This LOE re-assesses data from LOE 21509 from the 2010 Integrated Report. Data were re-assessed in order to evaluate these data in their own LOE, instead of being evaluated in the same LOE as other metals data. |
Data Reference: |
Surface Water Ambient Monitoring Program (SWAMP). Summary Report for the North Coast Region (RWQCB-1) for years 2000-2006. North Coast Regional Water Quality Control Board. March 2008 |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
Water Quality Control Plan, North Coast Region (NCRWQCB 2011): Waters designated for use as domestic or municipal supply (MUN) shall not contain concentrations of chemical constituents in excess of the limits specified in California Code of Regulations, Title 22, Chapter 15. The maximum contaminant level listed in Table 64431-A for chromium 0.05 mg/L. |
Objective/Criterion Reference: |
Water Quality Control Plan (Basin Plan) for the North Coast Region |
Objective/Criterion Reference: |
Maximum Contaminant Levels for organic and inorganic chemicals. CCR Title 22 |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
Data for this line of evidence for Klamath River HU, Shasta River HA was collected at 1 monitoring site [ Shasta River near Edgewood - 105SH9274] |
Temporal Representation: |
Data was collected over the time period 10/7/2002-6/19/2003. |
Environmental Conditions: |
There are no known environmental conditions (e.g., seasonality, land use practices, fire events, storms, etc.) that are related to these data. |
QAPP Information: |
Quality control was conducted in accordance with the SWAMP Quality Assurance Management Plan (SWAMP 2002). |
QAPP Information Reference(s): |
Quality Assurance Management Plan for the State of California's Surface Water Ambient Monitoring Program. Sacramento, CA. State Water Resources Control Board. SWAMP. December 2002 (1st version)
|
|
Line of Evidence (LOE) for Decision ID 100785, Chromium
|
Region 1 |
Klamath River HU, Shasta River HA |
|
|
LOE ID: |
123253 |
|
Pollutant: |
Chromium |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Total |
|
Beneficial Use: |
Municipal & Domestic Supply |
|
Number of Samples: |
3 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
State Water Board staff re-assessed SWAMP data for Klamath River HU, Shasta River HA to determine beneficial use support and results are as follows: 0 of 3 samples exceed the criterion for Chromium, Total. This LOE re-assesses data from LOE 21509 from the 2010 Integrated Report. Data were re-assessed in order to evaluate these data in their own LOE, instead of being evaluated in the same LOE as other metals data. |
Data Reference: |
Surface Water Ambient Monitoring Program (SWAMP). Summary Report for the North Coast Region (RWQCB-1) for years 2000-2006. North Coast Regional Water Quality Control Board. March 2008 |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
Water Quality Control Plan, North Coast Region (NCRWQCB 2011): Waters designated for use as domestic or municipal supply (MUN) shall not contain concentrations of chemical constituents in excess of the limits specified in California Code of Regulations, Title 22, Chapter 15. The maximum contaminant level listed in Table 64431-A for chromium 0.05 mg/L. |
Objective/Criterion Reference: |
Water Quality Control Plan (Basin Plan) for the North Coast Region |
Objective/Criterion Reference: |
Maximum Contaminant Levels for organic and inorganic chemicals. CCR Title 22 |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
Data for this line of evidence for Klamath River HU, Shasta River HA was collected at 1 monitoring site [ Yreka Creek at Highway 3 - 105YREHW3] |
Temporal Representation: |
Data was collected over the time period 10/21/2004-6/20/2005. |
Environmental Conditions: |
There are no known environmental conditions (e.g., seasonality, land use practices, fire events, storms, etc.) that are related to these data. |
QAPP Information: |
Quality control was conducted in accordance with the SWAMP Quality Assurance Management Plan (SWAMP 2002). |
QAPP Information Reference(s): |
Quality Assurance Management Plan for the State of California's Surface Water Ambient Monitoring Program. Sacramento, CA. State Water Resources Control Board. SWAMP. December 2002 (1st version)
|
|
Line of Evidence (LOE) for Decision ID 100785, Chromium
|
Region 1 |
Klamath River HU, Shasta River HA |
|
|
LOE ID: |
123241 |
|
Pollutant: |
Chromium |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Total |
|
Beneficial Use: |
Municipal & Domestic Supply |
|
Number of Samples: |
5 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
State Water Board staff re-assessed SWAMP data for Klamath River HU, Shasta River HA to determine beneficial use support and results are as follows: 0 of 5 samples exceed the criterion for Chromium, Total. This LOE re-assesses data from LOE 21509 from the 2010 Integrated Report. Data were re-assessed in order to evaluate these data in their own LOE, instead of being evaluated in the same LOE as other metals data. |
Data Reference: |
Surface Water Ambient Monitoring Program (SWAMP). Summary Report for the North Coast Region (RWQCB-1) for years 2000-2006. North Coast Regional Water Quality Control Board. March 2008 |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
Water Quality Control Plan, North Coast Region (NCRWQCB 2011): Waters designated for use as domestic or municipal supply (MUN) shall not contain concentrations of chemical constituents in excess of the limits specified in California Code of Regulations, Title 22, Chapter 15. The maximum contaminant level listed in Table 64431-A for chromium 0.05 mg/L. |
Objective/Criterion Reference: |
Water Quality Control Plan (Basin Plan) for the North Coast Region |
Objective/Criterion Reference: |
Maximum Contaminant Levels for organic and inorganic chemicals. CCR Title 22 |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
Data for this line of evidence for Klamath River HU, Shasta River HA was collected at 1 monitoring site [ Shasta River at Montague - 105SHAMON] |
Temporal Representation: |
Data was collected over the time period 10/7/2002-6/19/2003. |
Environmental Conditions: |
There are no known environmental conditions (e.g., seasonality, land use practices, fire events, storms, etc.) that are related to these data. |
QAPP Information: |
Quality control was conducted in accordance with the SWAMP Quality Assurance Management Plan (SWAMP 2002). |
QAPP Information Reference(s): |
Quality Assurance Management Plan for the State of California's Surface Water Ambient Monitoring Program. Sacramento, CA. State Water Resources Control Board. SWAMP. December 2002 (1st version)
|
|
Line of Evidence (LOE) for Decision ID 100785, Chromium
|
Region 1 |
Klamath River HU, Shasta River HA |
|
|
LOE ID: |
103177 |
|
Pollutant: |
Chromium |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Total |
|
Beneficial Use: |
Municipal & Domestic Supply |
|
Number of Samples: |
5 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP RWB1 Monitoring data for Klamath River HU, Shasta River HA to determine beneficial use support and results are as follows: 0 of 5 samples exceeded the water quality standard for Chromium. |
Data Reference: |
Water Quality Assessment Data for the 2018 solicitation cycle submitted through CEDEN for SWAMP RWB1 Monitoring .
|
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
Water Quality Control Plan, North Coast Region (NCRWQCB 2018): Waters designated for use as domestic or municipal supply (MUN) shall not contain concentrations of chemical constituents in excess of the limits specified in California Code of Regulations, Title 22, Chapter 15. The maximum contaminant level listed in Table 64431-A for chromium 0.05 mg/L. |
Objective/Criterion Reference: |
Water Quality Control Plan (Basin Plan) for the North Coast Region |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
The samples were collected at 1 monitoring site(s) (105SH1452) |
Temporal Representation: |
The samples were collected between the dates of 2013-03-06 and 2013-11-20 |
Environmental Conditions: |
|
QAPP Information: |
Quality Assurance Program Plan and Standard Operating Procedures for SWAMP program |
QAPP Information Reference(s): |
Quality Assurance Program Plans, Quality Assurance Project Plans, and Standard Operating Procedures for the SWAMP program |
|
Line of Evidence (LOE) for Decision ID 100785, Chromium
|
Region 1 |
Klamath River HU, Shasta River HA |
|
|
LOE ID: |
123243 |
|
Pollutant: |
Chromium |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Total |
|
Beneficial Use: |
Municipal & Domestic Supply |
|
Number of Samples: |
7 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
State Water Board staff re-assessed SWAMP data for Klamath River HU, Shasta River HA to determine beneficial use support and results are as follows: 0 of 7 samples exceed the criterion for Chromium, Total. This LOE re-assesses data from LOE 21509 from the 2010 Integrated Report. Data were re-assessed in order to evaluate these data in their own LOE, instead of being evaluated in the same LOE as other metals data. |
Data Reference: |
Surface Water Ambient Monitoring Program (SWAMP). Summary Report for the North Coast Region (RWQCB-1) for years 2000-2006. North Coast Regional Water Quality Control Board. March 2008 |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
Water Quality Control Plan, North Coast Region (NCRWQCB 2011): Waters designated for use as domestic or municipal supply (MUN) shall not contain concentrations of chemical constituents in excess of the limits specified in California Code of Regulations, Title 22, Chapter 15. The maximum contaminant level listed in Table 64431-A for chromium 0.05 mg/L. |
Objective/Criterion Reference: |
Water Quality Control Plan (Basin Plan) for the North Coast Region |
Objective/Criterion Reference: |
Maximum Contaminant Levels for organic and inorganic chemicals. CCR Title 22 |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
Data for this line of evidence for Klamath River HU, Shasta River HA was collected at 1 monitoring site [ Yreka Creek at Anderson Rd - 105YREAND] |
Temporal Representation: |
Data was collected over the time period 10/9/2002-6/20/2005. |
Environmental Conditions: |
There are no known environmental conditions (e.g., seasonality, land use practices, fire events, storms, etc.) that are related to these data. |
QAPP Information: |
Quality control was conducted in accordance with the SWAMP Quality Assurance Management Plan (SWAMP 2002). |
QAPP Information Reference(s): |
Quality Assurance Management Plan for the State of California's Surface Water Ambient Monitoring Program. Sacramento, CA. State Water Resources Control Board. SWAMP. December 2002 (1st version)
|
|
Line of Evidence (LOE) for Decision ID 100785, Chromium
|
Region 1 |
Klamath River HU, Shasta River HA |
|
|
LOE ID: |
41173 |
|
Pollutant: |
Chromium |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Total |
|
Beneficial Use: |
Municipal & Domestic Supply |
|
Number of Samples: |
4 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP data for Klamath River HU, Shasta River HA to determine beneficial use support and results are as follows: 0 of 4 samples exceed the criterion for Chromium. |
Data Reference: |
RWB1 Trend Maintenance Periods FYs 2007 2008 |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
Water Quality Control Plan, North Coast Region (NCRWQCB 2011): Waters designated for use as domestic or municipal supply (MUN) shall not contain concentrations of chemical constituents in excess of the limits specified in California Code of Regulations, Title 22, Chapter 15. The maximum contaminant level listed in Table 64431-A for chromium 0.05 mg/L. |
Objective/Criterion Reference: |
Maximum Contaminant Levels for organic and inorganic chemicals. CCR Title 22 |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
Data for this line of evidence for Klamath River HU, Shasta River HA was collected at 1 monitoring site [ Shasta River near Edgewood - 105SHAEDG] |
Temporal Representation: |
Data was collected over the time period 11/15/2007-7/16/2008. |
Environmental Conditions: |
Staff is not aware of any special conditions that might affect interpretation of the data. |
QAPP Information: |
The SWAMP QAPP (2008) was followed. |
QAPP Information Reference(s): |
Surface Water Ambient Monitoring Program Quality Assurance Program Plan |
|
Line of Evidence (LOE) for Decision ID 100785, Chromium
|
Region 1 |
Klamath River HU, Shasta River HA |
|
|
LOE ID: |
103173 |
|
Pollutant: |
Chromium |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Dissolved |
|
Beneficial Use: |
Warm Freshwater Habitat |
|
Number of Samples: |
1 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP RWB1 Monitoring data for Klamath River HU, Shasta River HA to determine beneficial use support and results are as follows: 0 of 1 samples exceeded the water quality standard for Chromium. |
Data Reference: |
Water Quality Assessment Data for the 2018 solicitation cycle submitted through CEDEN for SWAMP RWB1 Monitoring .
|
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
California Toxics Rule (CTR) lists criterion continuous concentrations to protect aquatic life in freshwater. The criterion in freshwater is hardness dependent for each sample and varies based on the ambient hardness during sampling. Section (b)(1) in CTR contains the hardness dependent formula for the metals criterion. |
Objective/Criterion Reference: |
Water Quality Standards 2000. Establishment of numeric criteria for priority toxic pollutants for the State of California: Rules and regulations. Federal Register Vol. 65, No. 97. Washington, D.C.: Environmental Protection Agency |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
The samples were collected at 1 monitoring site(s) (105SH1452) |
Temporal Representation: |
The samples were collected between the dates of 2013-07-30 and 2013-07-30 |
Environmental Conditions: |
|
QAPP Information: |
Quality Assurance Program Plan and Standard Operating Procedures for SWAMP program |
QAPP Information Reference(s): |
Quality Assurance Program Plans, Quality Assurance Project Plans, and Standard Operating Procedures for the SWAMP program |
|
Line of Evidence (LOE) for Decision ID 100744, Copper
|
Region 1 |
Klamath River HU, Shasta River HA |
|
|
LOE ID: |
123304 |
|
Pollutant: |
Copper |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Total |
|
Beneficial Use: |
Municipal & Domestic Supply |
|
Number of Samples: |
5 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
State Water Board staff re-assessed SWAMP data for Klamath River HU, Shasta River HA to determine beneficial use support and results are as follows: 0 of 5 samples exceed the criterion for Copper, Total. This LOE re-assesses data from LOE 21509 from the 2010 Integrated Report. Data were re-assessed in order to evaluate these data in their own LOE, instead of being evaluated in the same LOE as other metals data. |
Data Reference: |
Surface Water Ambient Monitoring Program (SWAMP). Summary Report for the North Coast Region (RWQCB-1) for years 2000-2006. North Coast Regional Water Quality Control Board. March 2008 |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
Water Quality Control Plan, North Coast Region (NCRWQCB 2011): Waters designated for use as domestic or municipal supply (MUN) shall not contain concentrations of chemical constituents in excess of the limits specified in California Code of Regulations, Title 22, Chapter 15. The secondary maximum contaminant level listed in Table 64449-A copper is 1.0 mg/L. |
Objective/Criterion Reference: |
Water Quality Control Plan (Basin Plan) for the North Coast Region |
Objective/Criterion Reference: |
Secondary Maximum Contaminant Levels and Compliance. CCR Title 22 section 64449. |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
Data for this line of evidence for Klamath River HU, Shasta River HA was collected at 1 monitoring site [ Shasta River at Montague - 105SHAMON] |
Temporal Representation: |
Data was collected over the time period 10/7/2002-6/19/2003. |
Environmental Conditions: |
There are no known environmental conditions (e.g., seasonality, land use practices, fire events, storms, etc.) that are related to these data. |
QAPP Information: |
Quality control was conducted in accordance with the SWAMP Quality Assurance Management Plan (SWAMP 2002). |
QAPP Information Reference(s): |
Quality Assurance Management Plan for the State of California's Surface Water Ambient Monitoring Program. Sacramento, CA. State Water Resources Control Board. SWAMP. December 2002 (1st version)
|
|
Line of Evidence (LOE) for Decision ID 100744, Copper
|
Region 1 |
Klamath River HU, Shasta River HA |
|
|
LOE ID: |
123302 |
|
Pollutant: |
Copper |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Total |
|
Beneficial Use: |
Municipal & Domestic Supply |
|
Number of Samples: |
3 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
State Water Board staff re-assessed SWAMP data for Klamath River HU, Shasta River HA to determine beneficial use support and results are as follows: 0 of 3 samples exceed the criterion for Copper, Total. This LOE re-assesses data from LOE 21509 from the 2010 Integrated Report. Data were re-assessed in order to evaluate these data in their own LOE, instead of being evaluated in the same LOE as other metals data. |
Data Reference: |
Surface Water Ambient Monitoring Program (SWAMP). Summary Report for the North Coast Region (RWQCB-1) for years 2000-2006. North Coast Regional Water Quality Control Board. March 2008 |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
Water Quality Control Plan, North Coast Region (NCRWQCB 2011): Waters designated for use as domestic or municipal supply (MUN) shall not contain concentrations of chemical constituents in excess of the limits specified in California Code of Regulations, Title 22, Chapter 15. The secondary maximum contaminant level listed in Table 64449-A copper is 1.0 mg/L. |
Objective/Criterion Reference: |
Water Quality Control Plan (Basin Plan) for the North Coast Region |
Objective/Criterion Reference: |
Secondary Maximum Contaminant Levels and Compliance. CCR Title 22 section 64449. |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
Data for this line of evidence for Klamath River HU, Shasta River HA was collected at 1 monitoring site [ Yreka Creek at Highway 3 - 105YREHW3] |
Temporal Representation: |
Data was collected over the time period 10/21/2004-6/20/2005. |
Environmental Conditions: |
There are no known environmental conditions (e.g., seasonality, land use practices, fire events, storms, etc.) that are related to these data. |
QAPP Information: |
Quality control was conducted in accordance with the SWAMP Quality Assurance Management Plan (SWAMP 2002). |
QAPP Information Reference(s): |
Quality Assurance Management Plan for the State of California's Surface Water Ambient Monitoring Program. Sacramento, CA. State Water Resources Control Board. SWAMP. December 2002 (1st version)
|
|
Line of Evidence (LOE) for Decision ID 100744, Copper
|
Region 1 |
Klamath River HU, Shasta River HA |
|
|
LOE ID: |
41209 |
|
Pollutant: |
Copper |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Total |
|
Beneficial Use: |
Municipal & Domestic Supply |
|
Number of Samples: |
4 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP data for Klamath River HU, Shasta River HA to determine beneficial use support and results are as follows: 0 of 4 samples exceed the criterion for Copper. |
Data Reference: |
RWB1 Trend Maintenance Periods FYs 2007 2008 |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
Water Quality Control Plan, North Coast Region (NCRWQCB 2011): Waters designated for use as domestic or municipal supply (MUN) shall not contain concentrations of chemical constituents in excess of the limits specified in California Code of Regulations, Title 22, Chapter 15. The secondary maximum contaminant level listed in Table 64449-A copper is 1.0 mg/L. |
Objective/Criterion Reference: |
Secondary Maximum Contaminant Levels and Compliance. CCR Title 22 section 64449. |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
Data for this line of evidence for Klamath River HU, Shasta River HA was collected at 1 monitoring site [ Shasta River near Edgewood - 105SHAEDG] |
Temporal Representation: |
Data was collected over the time period 11/15/2007-7/16/2008. |
Environmental Conditions: |
Staff is not aware of any special conditions that might affect interpretation of the data. |
QAPP Information: |
The SWAMP QAPP (2008) was followed. |
QAPP Information Reference(s): |
Surface Water Ambient Monitoring Program Quality Assurance Program Plan |
|
Line of Evidence (LOE) for Decision ID 100744, Copper
|
Region 1 |
Klamath River HU, Shasta River HA |
|
|
LOE ID: |
103192 |
|
Pollutant: |
Copper |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Total |
|
Beneficial Use: |
Municipal & Domestic Supply |
|
Number of Samples: |
5 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP RWB1 Monitoring data for Klamath River HU, Shasta River HA to determine beneficial use support and results are as follows: 0 of 5 samples exceeded the water quality standard for Copper. |
Data Reference: |
Water Quality Assessment Data for the 2018 solicitation cycle submitted through CEDEN for SWAMP RWB1 Monitoring .
|
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
Water Quality Control Plan, North Coast Region (NCRWQCB 2018): Waters designated for use as domestic or municipal supply (MUN) shall not contain concentrations of chemical constituents in excess of the limits specified in California Code of Regulations, Title 22, Chapter 15. The secondary maximum contaminant level listed in Table 64449-A copper is 1.0 mg/L. |
Objective/Criterion Reference: |
Water Quality Control Plan (Basin Plan) for the North Coast Region |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
The samples were collected at 1 monitoring site(s) (105SH9274) |
Temporal Representation: |
The samples were collected between the dates of 2013-03-07 and 2013-11-20 |
Environmental Conditions: |
|
QAPP Information: |
Quality Assurance Program Plan and Standard Operating Procedures for SWAMP program |
QAPP Information Reference(s): |
Quality Assurance Program Plans, Quality Assurance Project Plans, and Standard Operating Procedures for the SWAMP program |
|
Line of Evidence (LOE) for Decision ID 100744, Copper
|
Region 1 |
Klamath River HU, Shasta River HA |
|
|
LOE ID: |
103191 |
|
Pollutant: |
Copper |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Total |
|
Beneficial Use: |
Municipal & Domestic Supply |
|
Number of Samples: |
5 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP RWB1 Monitoring data for Klamath River HU, Shasta River HA to determine beneficial use support and results are as follows: 0 of 5 samples exceeded the water quality standard for Copper. |
Data Reference: |
Water Quality Assessment Data for the 2018 solicitation cycle submitted through CEDEN for SWAMP RWB1 Monitoring .
|
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
Water Quality Control Plan, North Coast Region (NCRWQCB 2018): Waters designated for use as domestic or municipal supply (MUN) shall not contain concentrations of chemical constituents in excess of the limits specified in California Code of Regulations, Title 22, Chapter 15. The secondary maximum contaminant level listed in Table 64449-A copper is 1.0 mg/L. |
Objective/Criterion Reference: |
Water Quality Control Plan (Basin Plan) for the North Coast Region |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
The samples were collected at 1 monitoring site(s) (105SH1452) |
Temporal Representation: |
The samples were collected between the dates of 2013-03-06 and 2013-11-20 |
Environmental Conditions: |
|
QAPP Information: |
Quality Assurance Program Plan and Standard Operating Procedures for SWAMP program |
QAPP Information Reference(s): |
Quality Assurance Program Plans, Quality Assurance Project Plans, and Standard Operating Procedures for the SWAMP program |
|
Line of Evidence (LOE) for Decision ID 100744, Copper
|
Region 1 |
Klamath River HU, Shasta River HA |
|
|
LOE ID: |
123303 |
|
Pollutant: |
Copper |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Total |
|
Beneficial Use: |
Municipal & Domestic Supply |
|
Number of Samples: |
22 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
State Water Board staff re-assessed SWAMP data for Klamath River HU, Shasta River HA to determine beneficial use support and results are as follows: 0 of 22 samples exceed the criterion for Copper, Total. This LOE re-assesses data from LOE 21509 from the 2010 Integrated Report. Data were re-assessed in order to evaluate these data in their own LOE, instead of being evaluated in the same LOE as other metals data. |
Data Reference: |
Surface Water Ambient Monitoring Program (SWAMP). Summary Report for the North Coast Region (RWQCB-1) for years 2000-2006. North Coast Regional Water Quality Control Board. March 2008 |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
Water Quality Control Plan, North Coast Region (NCRWQCB 2011): Waters designated for use as domestic or municipal supply (MUN) shall not contain concentrations of chemical constituents in excess of the limits specified in California Code of Regulations, Title 22, Chapter 15. The secondary maximum contaminant level listed in Table 64449-A copper is 1.0 mg/L. |
Objective/Criterion Reference: |
Water Quality Control Plan (Basin Plan) for the North Coast Region |
Objective/Criterion Reference: |
Secondary Maximum Contaminant Levels and Compliance. CCR Title 22 section 64449. |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
Data for this line of evidence for Klamath River HU, Shasta River HA was collected at 1 monitoring site [ Shasta River at Hwy 263 - 105SH1452] |
Temporal Representation: |
Data was collected over the time period 3/20/2001-11/16/2006. |
Environmental Conditions: |
There are no known environmental conditions (e.g., seasonality, land use practices, fire events, storms, etc.) that are related to these data. |
QAPP Information: |
Quality control was conducted in accordance with the SWAMP Quality Assurance Management Plan (SWAMP 2002). |
QAPP Information Reference(s): |
Quality Assurance Management Plan for the State of California's Surface Water Ambient Monitoring Program. Sacramento, CA. State Water Resources Control Board. SWAMP. December 2002 (1st version)
|
|
Line of Evidence (LOE) for Decision ID 100744, Copper
|
Region 1 |
Klamath River HU, Shasta River HA |
|
|
LOE ID: |
123291 |
|
Pollutant: |
Copper |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Total |
|
Beneficial Use: |
Municipal & Domestic Supply |
|
Number of Samples: |
5 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
State Water Board staff re-assessed SWAMP data for Klamath River HU, Shasta River HA to determine beneficial use support and results are as follows: 0 of 5 samples exceed the criterion for Copper, Total. This LOE re-assesses data from LOE 21509 from the 2010 Integrated Report. Data were re-assessed in order to evaluate these data in their own LOE, instead of being evaluated in the same LOE as other metals data. |
Data Reference: |
Surface Water Ambient Monitoring Program (SWAMP). Summary Report for the North Coast Region (RWQCB-1) for years 2000-2006. North Coast Regional Water Quality Control Board. March 2008 |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
Water Quality Control Plan, North Coast Region (NCRWQCB 2011): Waters designated for use as domestic or municipal supply (MUN) shall not contain concentrations of chemical constituents in excess of the limits specified in California Code of Regulations, Title 22, Chapter 15. The secondary maximum contaminant level listed in Table 64449-A copper is 1.0 mg/L. |
Objective/Criterion Reference: |
Water Quality Control Plan (Basin Plan) for the North Coast Region |
Objective/Criterion Reference: |
Secondary Maximum Contaminant Levels and Compliance. CCR Title 22 section 64449. |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
Data for this line of evidence for Klamath River HU, Shasta River HA was collected at 1 monitoring site [ Shasta River near Edgewood - 105SH9274] |
Temporal Representation: |
Data was collected over the time period 10/7/2002-6/19/2003. |
Environmental Conditions: |
There are no known environmental conditions (e.g., seasonality, land use practices, fire events, storms, etc.) that are related to these data. |
QAPP Information: |
Quality control was conducted in accordance with the SWAMP Quality Assurance Management Plan (SWAMP 2002). |
QAPP Information Reference(s): |
Quality Assurance Management Plan for the State of California's Surface Water Ambient Monitoring Program. Sacramento, CA. State Water Resources Control Board. SWAMP. December 2002 (1st version)
|
|
Line of Evidence (LOE) for Decision ID 100744, Copper
|
Region 1 |
Klamath River HU, Shasta River HA |
|
|
LOE ID: |
41212 |
|
Pollutant: |
Copper |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Total |
|
Beneficial Use: |
Municipal & Domestic Supply |
|
Number of Samples: |
4 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP data for Klamath River HU, Shasta River HA to determine beneficial use support and results are as follows: 0 of 4 samples exceed the criterion for Copper. |
Data Reference: |
RWB1 Trend Maintenance Periods FYs 2007 2008 |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
Water Quality Control Plan, North Coast Region (NCRWQCB 2011): Waters designated for use as domestic or municipal supply (MUN) shall not contain concentrations of chemical constituents in excess of the limits specified in California Code of Regulations, Title 22, Chapter 15. The secondary maximum contaminant level listed in Table 64449-A copper is 1.0 mg/L. |
Objective/Criterion Reference: |
Secondary Maximum Contaminant Levels and Compliance. CCR Title 22 section 64449. |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
Data for this line of evidence for Klamath River HU, Shasta River HA was collected at 1 monitoring site [ Shasta River at Hwy 263 - 105SHA263] |
Temporal Representation: |
Data was collected over the time period 11/15/2007-7/16/2008. |
Environmental Conditions: |
Staff is not aware of any special conditions that might affect interpretation of the data. |
QAPP Information: |
The SWAMP QAPP (2008) was followed. |
QAPP Information Reference(s): |
Surface Water Ambient Monitoring Program Quality Assurance Program Plan |
|
Line of Evidence (LOE) for Decision ID 100744, Copper
|
Region 1 |
Klamath River HU, Shasta River HA |
|
|
LOE ID: |
123292 |
|
Pollutant: |
Copper |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Total |
|
Beneficial Use: |
Municipal & Domestic Supply |
|
Number of Samples: |
7 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
State Water Board staff re-assessed SWAMP data for Klamath River HU, Shasta River HA to determine beneficial use support and results are as follows: 0 of 7 samples exceed the criterion for Copper, Total. This LOE re-assesses data from LOE 21509 from the 2010 Integrated Report. Data were re-assessed in order to evaluate these data in their own LOE, instead of being evaluated in the same LOE as other metals data. |
Data Reference: |
Surface Water Ambient Monitoring Program (SWAMP). Summary Report for the North Coast Region (RWQCB-1) for years 2000-2006. North Coast Regional Water Quality Control Board. March 2008 |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
Water Quality Control Plan, North Coast Region (NCRWQCB 2011): Waters designated for use as domestic or municipal supply (MUN) shall not contain concentrations of chemical constituents in excess of the limits specified in California Code of Regulations, Title 22, Chapter 15. The secondary maximum contaminant level listed in Table 64449-A copper is 1.0 mg/L. |
Objective/Criterion Reference: |
Water Quality Control Plan (Basin Plan) for the North Coast Region |
Objective/Criterion Reference: |
Secondary Maximum Contaminant Levels and Compliance. CCR Title 22 section 64449. |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
Data for this line of evidence for Klamath River HU, Shasta River HA was collected at 1 monitoring site [ Yreka Creek at Anderson Rd - 105YREAND] |
Temporal Representation: |
Data was collected over the time period 10/9/2002-6/20/2005. |
Environmental Conditions: |
There are no known environmental conditions (e.g., seasonality, land use practices, fire events, storms, etc.) that are related to these data. |
QAPP Information: |
Quality control was conducted in accordance with the SWAMP Quality Assurance Management Plan (SWAMP 2002). |
QAPP Information Reference(s): |
Quality Assurance Management Plan for the State of California's Surface Water Ambient Monitoring Program. Sacramento, CA. State Water Resources Control Board. SWAMP. December 2002 (1st version)
|
|
Line of Evidence (LOE) for Decision ID 100744, Copper
|
Region 1 |
Klamath River HU, Shasta River HA |
|
|
LOE ID: |
32976 |
|
Pollutant: |
Copper |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Total |
|
Beneficial Use: |
Cold Freshwater Habitat |
|
Number of Samples: |
4 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
None of the 4 samples exceeded the hardness based criteria calculated for copper. |
Data Reference: |
RWB1 Trend Maintenance Periods FYs 2007 2008 |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
Water Quality Control Plan, North Coast Region (NCRWQCB 2011): All waters shall be maintained free of toxic substances in concentrations that are toxic to, or that produce detrimental physiological responses in human, plant, animal, or aquatic life. California Toxics Rule (CTR) lists criterion continuous concentrations (4-day average) to protect aquatic life in freshwater. The criterion in freshwater is hardness dependent for each sample and varies based on the ambient hardness during sampling. Section (b)(1) in CTR contains the hardness dependent formula for the metals criterion. |
Objective/Criterion Reference: |
Code of Federal Regulations 40 part 131.38 Establishment of numeric criteria for priority toxic pollutants for the State of California. 7/1/2011 Edition |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
Samples collected at station 105SHA263 (Shasta River at Hwy 263). |
Temporal Representation: |
Samples collected between 11/15/2007 and 7/16/2008. |
Environmental Conditions: |
|
QAPP Information: |
SWAMP QAPP (2008) was followed. |
QAPP Information Reference(s): |
Surface Water Ambient Monitoring Program Quality Assurance Program Plan |
|
Line of Evidence (LOE) for Decision ID 100744, Copper
|
Region 1 |
Klamath River HU, Shasta River HA |
|
|
LOE ID: |
32581 |
|
Pollutant: |
Copper |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Total |
|
Beneficial Use: |
Cold Freshwater Habitat |
|
Number of Samples: |
4 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
None of the 4 samples exceeded the hardness based criteria calculated for copper. |
Data Reference: |
RWB1 Trend Maintenance Periods FYs 2007 2008 |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
Water Quality Control Plan, North Coast Region (NCRWQCB 2011): All waters shall be maintained free of toxic substances in concentrations that are toxic to, or that produce detrimental physiological responses in human, plant, animal, or aquatic life. California Toxics Rule (CTR) lists criterion continuous concentrations (4-day average) to protect aquatic life in freshwater. The criterion in freshwater is hardness dependent for each sample and varies based on the ambient hardness during sampling. Section (b)(1) in CTR contains the hardness dependent formula for the metals criterion. |
Objective/Criterion Reference: |
Code of Federal Regulations 40 part 131.38 Establishment of numeric criteria for priority toxic pollutants for the State of California. 7/1/2011 Edition |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
Samples collected at station 105SHAEDG (Shasta River near Edgewood). |
Temporal Representation: |
Samples collected between 11/15/2007 and 7/16/2008. |
Environmental Conditions: |
|
QAPP Information: |
SWAMP QAPP (2008) was followed. |
QAPP Information Reference(s): |
Surface Water Ambient Monitoring Program Quality Assurance Program Plan |
|
Line of Evidence (LOE) for Decision ID 100744, Copper
|
Region 1 |
Klamath River HU, Shasta River HA |
|
|
LOE ID: |
103187 |
|
Pollutant: |
Copper |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Dissolved |
|
Beneficial Use: |
Warm Freshwater Habitat |
|
Number of Samples: |
5 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP RWB1 Monitoring data for Klamath River HU, Shasta River HA to determine beneficial use support and results are as follows: 0 of 5 samples exceeded the water quality standard for Copper. |
Data Reference: |
Water Quality Assessment Data for the 2018 solicitation cycle submitted through CEDEN for SWAMP RWB1 Monitoring .
|
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
California Toxics Rule (CTR) lists criterion continuous concentrations to protect aquatic life in freshwater. The criterion in freshwater is hardness dependent for each sample and varies based on the ambient hardness during sampling. Section (b)(1) in CTR contains the hardness dependent formula for the metals criterion. |
Objective/Criterion Reference: |
Water Quality Standards 2000. Establishment of numeric criteria for priority toxic pollutants for the State of California: Rules and regulations. Federal Register Vol. 65, No. 97. Washington, D.C.: Environmental Protection Agency |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
The samples were collected at 1 monitoring site(s) (105SH1452) |
Temporal Representation: |
The samples were collected between the dates of 2013-03-06 and 2013-11-20 |
Environmental Conditions: |
|
QAPP Information: |
Quality Assurance Program Plan and Standard Operating Procedures for SWAMP program |
QAPP Information Reference(s): |
Quality Assurance Program Plans, Quality Assurance Project Plans, and Standard Operating Procedures for the SWAMP program |
|
Line of Evidence (LOE) for Decision ID 100744, Copper
|
Region 1 |
Klamath River HU, Shasta River HA |
|
|
LOE ID: |
103190 |
|
Pollutant: |
Copper |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Dissolved |
|
Beneficial Use: |
Warm Freshwater Habitat |
|
Number of Samples: |
5 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP RWB1 Monitoring data for Klamath River HU, Shasta River HA to determine beneficial use support and results are as follows: 0 of 5 samples exceeded the water quality standard for Copper. |
Data Reference: |
Water Quality Assessment Data for the 2018 solicitation cycle submitted through CEDEN for SWAMP RWB1 Monitoring .
|
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
California Toxics Rule (CTR) lists criterion continuous concentrations to protect aquatic life in freshwater. The criterion in freshwater is hardness dependent for each sample and varies based on the ambient hardness during sampling. Section (b)(1) in CTR contains the hardness dependent formula for the metals criterion. |
Objective/Criterion Reference: |
Water Quality Standards 2000. Establishment of numeric criteria for priority toxic pollutants for the State of California: Rules and regulations. Federal Register Vol. 65, No. 97. Washington, D.C.: Environmental Protection Agency |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
The samples were collected at 1 monitoring site(s) (105SH9274) |
Temporal Representation: |
The samples were collected between the dates of 2013-03-07 and 2013-11-20 |
Environmental Conditions: |
|
QAPP Information: |
Quality Assurance Program Plan and Standard Operating Procedures for SWAMP program |
QAPP Information Reference(s): |
Quality Assurance Program Plans, Quality Assurance Project Plans, and Standard Operating Procedures for the SWAMP program |
|
Line of Evidence (LOE) for Decision ID 100744, Copper
|
Region 1 |
Klamath River HU, Shasta River HA |
|
|
LOE ID: |
103184 |
|
Pollutant: |
Copper |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Dissolved |
|
Beneficial Use: |
Municipal & Domestic Supply |
|
Number of Samples: |
5 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP RWB1 Monitoring data for Klamath River HU, Shasta River HA to determine beneficial use support and results are as follows: 0 of 5 samples exceeded the water quality standard for Copper. |
Data Reference: |
Water Quality Assessment Data for the 2018 solicitation cycle submitted through CEDEN for SWAMP RWB1 Monitoring .
|
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
Water Quality Control Plan, North Coast Region (NCRWQCB 2018): Waters designated for use as domestic or municipal supply (MUN) shall not contain concentrations of chemical constituents in excess of the limits specified in California Code of Regulations, Title 22, Chapter 15. The secondary maximum contaminant level listed in Table 64449-A copper is 1.0 mg/L. |
Objective/Criterion Reference: |
Water Quality Control Plan (Basin Plan) for the North Coast Region |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
The samples were collected at 1 monitoring site(s) (105SH1452) |
Temporal Representation: |
The samples were collected between the dates of 2013-03-06 and 2013-11-20 |
Environmental Conditions: |
|
QAPP Information: |
Quality Assurance Program Plan and Standard Operating Procedures for SWAMP program |
QAPP Information Reference(s): |
Quality Assurance Program Plans, Quality Assurance Project Plans, and Standard Operating Procedures for the SWAMP program |
|
Line of Evidence (LOE) for Decision ID 100744, Copper
|
Region 1 |
Klamath River HU, Shasta River HA |
|
|
LOE ID: |
103189 |
|
Pollutant: |
Copper |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Dissolved |
|
Beneficial Use: |
Municipal & Domestic Supply |
|
Number of Samples: |
5 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP RWB1 Monitoring data for Klamath River HU, Shasta River HA to determine beneficial use support and results are as follows: 0 of 5 samples exceeded the water quality standard for Copper. |
Data Reference: |
Water Quality Assessment Data for the 2018 solicitation cycle submitted through CEDEN for SWAMP RWB1 Monitoring .
|
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
Water Quality Control Plan, North Coast Region (NCRWQCB 2018): Waters designated for use as domestic or municipal supply (MUN) shall not contain concentrations of chemical constituents in excess of the limits specified in California Code of Regulations, Title 22, Chapter 15. The secondary maximum contaminant level listed in Table 64449-A copper is 1.0 mg/L. |
Objective/Criterion Reference: |
Water Quality Control Plan (Basin Plan) for the North Coast Region |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
The samples were collected at 1 monitoring site(s) (105SH9274) |
Temporal Representation: |
The samples were collected between the dates of 2013-03-07 and 2013-11-20 |
Environmental Conditions: |
|
QAPP Information: |
Quality Assurance Program Plan and Standard Operating Procedures for SWAMP program |
QAPP Information Reference(s): |
Quality Assurance Program Plans, Quality Assurance Project Plans, and Standard Operating Procedures for the SWAMP program |
|
Line of Evidence (LOE) for Decision ID 100744, Copper
|
Region 1 |
Klamath River HU, Shasta River HA |
|
|
LOE ID: |
103183 |
|
Pollutant: |
Copper |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Dissolved |
|
Beneficial Use: |
Cold Freshwater Habitat |
|
Number of Samples: |
5 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP RWB1 Monitoring data for Klamath River HU, Shasta River HA to determine beneficial use support and results are as follows: 0 of 5 samples exceeded the water quality standard for Copper. |
Data Reference: |
Water Quality Assessment Data for the 2018 solicitation cycle submitted through CEDEN for SWAMP RWB1 Monitoring .
|
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
California Toxics Rule (CTR) lists criterion continuous concentrations to protect aquatic life in freshwater. The criterion in freshwater is hardness dependent for each sample and varies based on the ambient hardness during sampling. Section (b)(1) in CTR contains the hardness dependent formula for the metals criterion. |
Objective/Criterion Reference: |
Water Quality Standards 2000. Establishment of numeric criteria for priority toxic pollutants for the State of California: Rules and regulations. Federal Register Vol. 65, No. 97. Washington, D.C.: Environmental Protection Agency |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
The samples were collected at 1 monitoring site(s) (105SH1452) |
Temporal Representation: |
The samples were collected between the dates of 2013-03-06 and 2013-11-20 |
Environmental Conditions: |
|
QAPP Information: |
Quality Assurance Program Plan and Standard Operating Procedures for SWAMP program |
QAPP Information Reference(s): |
Quality Assurance Program Plans, Quality Assurance Project Plans, and Standard Operating Procedures for the SWAMP program |
|
Line of Evidence (LOE) for Decision ID 100744, Copper
|
Region 1 |
Klamath River HU, Shasta River HA |
|
|
LOE ID: |
103188 |
|
Pollutant: |
Copper |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Dissolved |
|
Beneficial Use: |
Cold Freshwater Habitat |
|
Number of Samples: |
5 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP RWB1 Monitoring data for Klamath River HU, Shasta River HA to determine beneficial use support and results are as follows: 0 of 5 samples exceeded the water quality standard for Copper. |
Data Reference: |
Water Quality Assessment Data for the 2018 solicitation cycle submitted through CEDEN for SWAMP RWB1 Monitoring .
|
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
California Toxics Rule (CTR) lists criterion continuous concentrations to protect aquatic life in freshwater. The criterion in freshwater is hardness dependent for each sample and varies based on the ambient hardness during sampling. Section (b)(1) in CTR contains the hardness dependent formula for the metals criterion. |
Objective/Criterion Reference: |
Water Quality Standards 2000. Establishment of numeric criteria for priority toxic pollutants for the State of California: Rules and regulations. Federal Register Vol. 65, No. 97. Washington, D.C.: Environmental Protection Agency |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
The samples were collected at 1 monitoring site(s) (105SH9274) |
Temporal Representation: |
The samples were collected between the dates of 2013-03-07 and 2013-11-20 |
Environmental Conditions: |
|
QAPP Information: |
Quality Assurance Program Plan and Standard Operating Procedures for SWAMP program |
QAPP Information Reference(s): |
Quality Assurance Program Plans, Quality Assurance Project Plans, and Standard Operating Procedures for the SWAMP program |
|
Line of Evidence (LOE) for Decision ID 74010, DDD (Dichlorodiphenyldichloroethane)
|
Region 1 |
Klamath River HU, Shasta River HA |
|
|
LOE ID: |
108668 |
|
Pollutant: |
DDD (Dichlorodiphenyldichloroethane) |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Total |
|
Beneficial Use: |
Commercial or recreational collection of fish, shellfish, or organisms |
|
Number of Samples: |
0 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP RWB1 Monitoring data for Klamath River HU, Shasta River HA to determine beneficial use support, and the results are as follows: 0 of the 0 samples exceeded the evaluation guideline for DDD(p,p'). Although a total of 1 samples were collected, 1 of these samples were not included in the assessment because the laboratory data reporting limit(s) was above the objective and therefore the results could not be quantified with the level of certainty required by the Listing Policy Section 6.1.5.5. |
Data Reference: |
Water Quality Assessment Data for the 2018 solicitation cycle submitted through CEDEN for SWAMP RWB1 Monitoring .
|
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
The 4,4'-DDD criterion for the protection of human health from consumption of organisms only is 0.00084 ug/L (California Toxics Rule, 2000). |
Objective/Criterion Reference: |
Water Quality Standards 2000. Establishment of numeric criteria for priority toxic pollutants for the State of California: Rules and regulations. Federal Register Vol. 65, No. 97. Washington, D.C.: Environmental Protection Agency |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
Data was collected from 1 station(s) (Station Code(s) 105SH9274). |
Temporal Representation: |
Date for this waterbody was collected over the date range 2013-04-29 to 2013-04-29 |
Environmental Conditions: |
|
QAPP Information: |
Quality Assurance Program Plan and Standard Operating Procedures for SWAMP program |
QAPP Information Reference(s): |
Quality Assurance Program Plans, Quality Assurance Project Plans, and Standard Operating Procedures for the SWAMP program |
|
Line of Evidence (LOE) for Decision ID 74010, DDD (Dichlorodiphenyldichloroethane)
|
Region 1 |
Klamath River HU, Shasta River HA |
|
|
LOE ID: |
105791 |
|
Pollutant: |
DDD (Dichlorodiphenyldichloroethane) |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Total |
|
Beneficial Use: |
Municipal & Domestic Supply |
|
Number of Samples: |
0 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP RWB1 Monitoring data for Klamath River HU, Shasta River HA to determine beneficial use support, and the results are as follows: 0 of the 0 samples exceeded the evaluation guideline for DDD(p,p'). Although a total of 1 samples were collected, 1 of these samples were not included in the assessment because the laboratory data reporting limit(s) was above the objective and therefore the results could not be quantified with the level of certainty required by the Listing Policy Section 6.1.5.5. |
Data Reference: |
Water Quality Assessment Data for the 2018 solicitation cycle submitted through CEDEN for SWAMP RWB1 Monitoring .
|
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
The 4,4'-DDD criterion for the protection of human health from the consumption of water and organisms is 0.00083 ug/L (California Toxics Rule, 2000). |
Objective/Criterion Reference: |
Water Quality Standards 2000. Establishment of numeric criteria for priority toxic pollutants for the State of California: Rules and regulations. Federal Register Vol. 65, No. 97. Washington, D.C.: Environmental Protection Agency |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
Data was collected from 1 station(s) (Station Code(s) 105SH1452). |
Temporal Representation: |
Date for this waterbody was collected over the date range 2013-04-29 to 2013-04-29 |
Environmental Conditions: |
|
QAPP Information: |
Quality Assurance Program Plan and Standard Operating Procedures for SWAMP program |
QAPP Information Reference(s): |
Quality Assurance Program Plans, Quality Assurance Project Plans, and Standard Operating Procedures for the SWAMP program |
|
Line of Evidence (LOE) for Decision ID 74010, DDD (Dichlorodiphenyldichloroethane)
|
Region 1 |
Klamath River HU, Shasta River HA |
|
|
LOE ID: |
34522 |
|
Pollutant: |
DDD (Dichlorodiphenyldichloroethane) |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Total |
|
Beneficial Use: |
Municipal & Domestic Supply |
|
Number of Samples: |
0 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
The method detection limit for all 3 of the non-detect samples was greater than the criteria: thus the data was not used in this assessment. |
Data Reference: |
RWB1 Trend Maintenance Periods FYs 2007 2008 |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
Per the Basin Plan (NCRWQCB 2011): All waters shall be maintained free of toxic substances in concentrations that are toxic to, or that produce detrimental physiological responses in human, plant, animal, or aquatic life. The 4,4'-DDD criterion for the protection of human health from the consumption of water and organisms is 0.00031 ug/L (USEPA Nationally Recommended Criteria, 2006). |
Objective/Criterion Reference: |
National Recommended Water Quality Criteria. United States Environmental Protection Agency. Office of Water. Office of Science and Technology |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
Samples collected at station 105SHA263 (Shasta River at Hwy 263). |
Temporal Representation: |
Samples were collected on 11/15/2007, 4/9/2008, and 7/16/2008. |
Environmental Conditions: |
|
QAPP Information: |
SWAMP QAPP (2008) was followed. |
QAPP Information Reference(s): |
Surface Water Ambient Monitoring Program Quality Assurance Program Plan |
|
Line of Evidence (LOE) for Decision ID 74010, DDD (Dichlorodiphenyldichloroethane)
|
Region 1 |
Klamath River HU, Shasta River HA |
|
|
LOE ID: |
105793 |
|
Pollutant: |
DDD (Dichlorodiphenyldichloroethane) |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Total |
|
Beneficial Use: |
Municipal & Domestic Supply |
|
Number of Samples: |
0 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP RWB1 Monitoring data for Klamath River HU, Shasta River HA to determine beneficial use support, and the results are as follows: 0 of the 0 samples exceeded the evaluation guideline for DDD(p,p'). Although a total of 1 samples were collected, 1 of these samples were not included in the assessment because the laboratory data reporting limit(s) was above the objective and therefore the results could not be quantified with the level of certainty required by the Listing Policy Section 6.1.5.5. |
Data Reference: |
Water Quality Assessment Data for the 2018 solicitation cycle submitted through CEDEN for SWAMP RWB1 Monitoring .
|
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
The 4,4'-DDD criterion for the protection of human health from the consumption of water and organisms is 0.00083 ug/L (California Toxics Rule, 2000). |
Objective/Criterion Reference: |
Water Quality Standards 2000. Establishment of numeric criteria for priority toxic pollutants for the State of California: Rules and regulations. Federal Register Vol. 65, No. 97. Washington, D.C.: Environmental Protection Agency |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
Data was collected from 1 station(s) (Station Code(s) 105SH9274). |
Temporal Representation: |
Date for this waterbody was collected over the date range 2013-04-29 to 2013-04-29 |
Environmental Conditions: |
|
QAPP Information: |
Quality Assurance Program Plan and Standard Operating Procedures for SWAMP program |
QAPP Information Reference(s): |
Quality Assurance Program Plans, Quality Assurance Project Plans, and Standard Operating Procedures for the SWAMP program |
|
Line of Evidence (LOE) for Decision ID 74010, DDD (Dichlorodiphenyldichloroethane)
|
Region 1 |
Klamath River HU, Shasta River HA |
|
|
LOE ID: |
123330 |
|
Pollutant: |
DDD (Dichlorodiphenyldichloroethane) |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
None |
|
Beneficial Use: |
Municipal & Domestic Supply |
|
Number of Samples: |
0 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
State Water Board staff re-assessed SWAMP data for Klamath River HU, Shasta River HA to determine beneficial use support and results are as follows: 0 of 0 samples exceed the criterion for DDD(o,p'), Total. Thirty-three samples were removed from assessment because an appropriate evaluation guideline for the water body-pollutant combination could not be obtained for this listing cycle. This LOE re-assesses data from LOE 29849 from the 2010 Integrated Report. Data were re-assessed in order to evaluate these data in their own LOE, instead of being evaluated in the same LOE as other pesticide data. |
Data Reference: |
Surface Water Ambient Monitoring Program (SWAMP). Summary Report for the North Coast Region (RWQCB-1) for years 2000-2006. North Coast Regional Water Quality Control Board. March 2008 |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
Per the Basin Plan (NCRWQCB 2011): No individual pesticide or combination of pesticides shall be present in concentrations that adversely affect beneficial uses. There shall be no bioaccumulation of pesticide concentrations found in bottom sediments or aquatic life. Waters designated for use as domestic or municipal supply shall not contain concentrations of pesticides in excess of the limiting concentrations set forth in California Code of Regulations, Title 22, Division 4, Chapter 15, Article 4, Section 64444, and listed in Table 3.2 of the Basin Plan. No evaluation guideline could be found to evaluate protection of the MUN beneficial use that meets the requirements of Section 6.1.3 of the Listing Policy. |
Objective/Criterion Reference: |
Water Quality Control Plan (Basin Plan) for the North Coast Region |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
Data for this line of evidence for Klamath River HU, Shasta River HA was collected at 1 monitoring site [ Shasta River at Hwy 263 - 105SH1452] |
Temporal Representation: |
Data was collected over the time period 4/24/2001-11/16/2006. |
Environmental Conditions: |
There are no known environmental conditions (e.g., seasonality, land use practices, fire events, storms, etc.) that are related to these data. |
QAPP Information: |
Quality control was conducted in accordance with the SWAMP Quality Assurance Management Plan (SWAMP 2002). |
QAPP Information Reference(s): |
Quality Assurance Management Plan for the State of California's Surface Water Ambient Monitoring Program. Sacramento, CA. State Water Resources Control Board. SWAMP. December 2002 (1st version)
|
|
Line of Evidence (LOE) for Decision ID 74010, DDD (Dichlorodiphenyldichloroethane)
|
Region 1 |
Klamath River HU, Shasta River HA |
|
|
LOE ID: |
123331 |
|
Pollutant: |
DDD (Dichlorodiphenyldichloroethane) |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
None |
|
Beneficial Use: |
Municipal & Domestic Supply |
|
Number of Samples: |
0 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
State Water Board staff re-assessed SWAMP data for Klamath River HU, Shasta River HA to determine beneficial use support and results are as follows: 0 of 0 samples exceed the criterion for DDD(o,p'), Total. Eight samples were removed from assessment because an appropriate evaluation guideline for the water body-pollutant combination could not be obtained for this listing cycle. This LOE re-assesses data from LOE 29849 from the 2010 Integrated Report. Data were re-assessed in order to evaluate these data in their own LOE, instead of being evaluated in the same LOE as other pesticide data. |
Data Reference: |
Surface Water Ambient Monitoring Program (SWAMP). Summary Report for the North Coast Region (RWQCB-1) for years 2000-2006. North Coast Regional Water Quality Control Board. March 2008 |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
Per the Basin Plan (NCRWQCB 2011): No individual pesticide or combination of pesticides shall be present in concentrations that adversely affect beneficial uses. There shall be no bioaccumulation of pesticide concentrations found in bottom sediments or aquatic life. Waters designated for use as domestic or municipal supply shall not contain concentrations of pesticides in excess of the limiting concentrations set forth in California Code of Regulations, Title 22, Division 4, Chapter 15, Article 4, Section 64444, and listed in Table 3.2 of the Basin Plan. No evaluation guideline could be found to evaluate protection of the MUN beneficial use that meets the requirements of Section 6.1.3 of the Listing Policy. |
Objective/Criterion Reference: |
Water Quality Control Plan (Basin Plan) for the North Coast Region |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
Data for this line of evidence for Klamath River HU, Shasta River HA was collected at 1 monitoring site [ Shasta River at Montague - 105SHAMON] |
Temporal Representation: |
Data was collected over the time period 10/7/2002-6/19/2003. |
Environmental Conditions: |
There are no known environmental conditions (e.g., seasonality, land use practices, fire events, storms, etc.) that are related to these data. |
QAPP Information: |
Quality control was conducted in accordance with the SWAMP Quality Assurance Management Plan (SWAMP 2002). |
QAPP Information Reference(s): |
Quality Assurance Management Plan for the State of California's Surface Water Ambient Monitoring Program. Sacramento, CA. State Water Resources Control Board. SWAMP. December 2002 (1st version)
|
|
Line of Evidence (LOE) for Decision ID 74010, DDD (Dichlorodiphenyldichloroethane)
|
Region 1 |
Klamath River HU, Shasta River HA |
|
|
LOE ID: |
123345 |
|
Pollutant: |
DDD (Dichlorodiphenyldichloroethane) |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
None |
|
Beneficial Use: |
Municipal & Domestic Supply |
|
Number of Samples: |
0 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
State Water Board staff re-assessed SWAMP data for Klamath River HU, Shasta River HA to determine beneficial use support and results are as follows: 0 of 0 samples exceed the criterion for DDD(o,p'), Total. Eight samples were removed from assessment because an appropriate evaluation guideline for the water body-pollutant combination could not be obtained for this listing cycle. This LOE re-assesses data from LOE 29849 from the 2010 Integrated Report. Data were re-assessed in order to evaluate these data in their own LOE, instead of being evaluated in the same LOE as other pesticide data. |
Data Reference: |
Surface Water Ambient Monitoring Program (SWAMP). Summary Report for the North Coast Region (RWQCB-1) for years 2000-2006. North Coast Regional Water Quality Control Board. March 2008 |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
Per the Basin Plan (NCRWQCB 2011): No individual pesticide or combination of pesticides shall be present in concentrations that adversely affect beneficial uses. There shall be no bioaccumulation of pesticide concentrations found in bottom sediments or aquatic life. Waters designated for use as domestic or municipal supply shall not contain concentrations of pesticides in excess of the limiting concentrations set forth in California Code of Regulations, Title 22, Division 4, Chapter 15, Article 4, Section 64444, and listed in Table 3.2 of the Basin Plan. No evaluation guideline could be found to evaluate protection of the MUN beneficial use that meets the requirements of Section 6.1.3 of the Listing Policy. |
Objective/Criterion Reference: |
Water Quality Control Plan (Basin Plan) for the North Coast Region |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
Data for this line of evidence for Klamath River HU, Shasta River HA was collected at 1 monitoring site [ Yreka Creek at Highway 3 - 105YREHW3] |
Temporal Representation: |
Data was collected over the time period 10/21/2004-6/20/2005. |
Environmental Conditions: |
There are no known environmental conditions (e.g., seasonality, land use practices, fire events, storms, etc.) that are related to these data. |
QAPP Information: |
Quality control was conducted in accordance with the SWAMP Quality Assurance Management Plan (SWAMP 2002). |
QAPP Information Reference(s): |
Quality Assurance Management Plan for the State of California's Surface Water Ambient Monitoring Program. Sacramento, CA. State Water Resources Control Board. SWAMP. December 2002 (1st version)
|
|
Line of Evidence (LOE) for Decision ID 74010, DDD (Dichlorodiphenyldichloroethane)
|
Region 1 |
Klamath River HU, Shasta River HA |
|
|
LOE ID: |
123344 |
|
Pollutant: |
DDD (Dichlorodiphenyldichloroethane) |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
None |
|
Beneficial Use: |
Municipal & Domestic Supply |
|
Number of Samples: |
0 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
State Water Board staff re-assessed SWAMP data for Klamath River HU, Shasta River HA to determine beneficial use support and results are as follows: 0 of 0 samples exceed the criterion for DDD(o,p'), Total. Sixteen samples were removed from assessment because an appropriate evaluation guideline for the water body-pollutant combination could not be obtained for this listing cycle. This LOE re-assesses data from LOE 29849 from the 2010 Integrated Report. Data were re-assessed in order to evaluate these data in their own LOE, instead of being evaluated in the same LOE as other pesticide data. |
Data Reference: |
Surface Water Ambient Monitoring Program (SWAMP). Summary Report for the North Coast Region (RWQCB-1) for years 2000-2006. North Coast Regional Water Quality Control Board. March 2008 |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
Per the Basin Plan (NCRWQCB 2011): No individual pesticide or combination of pesticides shall be present in concentrations that adversely affect beneficial uses. There shall be no bioaccumulation of pesticide concentrations found in bottom sediments or aquatic life. Waters designated for use as domestic or municipal supply shall not contain concentrations of pesticides in excess of the limiting concentrations set forth in California Code of Regulations, Title 22, Division 4, Chapter 15, Article 4, Section 64444, and listed in Table 3.2 of the Basin Plan. No evaluation guideline could be found to evaluate protection of the MUN beneficial use that meets the requirements of Section 6.1.3 of the Listing Policy. |
Objective/Criterion Reference: |
Water Quality Control Plan (Basin Plan) for the North Coast Region |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
Data for this line of evidence for Klamath River HU, Shasta River HA was collected at 1 monitoring site [ Yreka Creek at Anderson Rd - 105YREAND] |
Temporal Representation: |
Data was collected over the time period 10/9/2002-6/20/2005. |
Environmental Conditions: |
There are no known environmental conditions (e.g., seasonality, land use practices, fire events, storms, etc.) that are related to these data. |
QAPP Information: |
Quality control was conducted in accordance with the SWAMP Quality Assurance Management Plan (SWAMP 2002). |
QAPP Information Reference(s): |
Quality Assurance Management Plan for the State of California's Surface Water Ambient Monitoring Program. Sacramento, CA. State Water Resources Control Board. SWAMP. December 2002 (1st version)
|
|
Line of Evidence (LOE) for Decision ID 74010, DDD (Dichlorodiphenyldichloroethane)
|
Region 1 |
Klamath River HU, Shasta River HA |
|
|
LOE ID: |
123332 |
|
Pollutant: |
DDD (Dichlorodiphenyldichloroethane) |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
None |
|
Beneficial Use: |
Municipal & Domestic Supply |
|
Number of Samples: |
0 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
State Water Board staff re-assessed SWAMP data for Klamath River HU, Shasta River HA to determine beneficial use support and results are as follows: 0 of 0 samples exceed the criterion for DDD(o,p'), Total. Eight samples were removed from assessment because an appropriate evaluation guideline for the water body-pollutant combination could not be obtained for this listing cycle. This LOE re-assesses data from LOE 29849 from the 2010 Integrated Report. Data were re-assessed in order to evaluate these data in their own LOE, instead of being evaluated in the same LOE as other pesticide data. |
Data Reference: |
Surface Water Ambient Monitoring Program (SWAMP). Summary Report for the North Coast Region (RWQCB-1) for years 2000-2006. North Coast Regional Water Quality Control Board. March 2008 |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
Per the Basin Plan (NCRWQCB 2011): No individual pesticide or combination of pesticides shall be present in concentrations that adversely affect beneficial uses. There shall be no bioaccumulation of pesticide concentrations found in bottom sediments or aquatic life. Waters designated for use as domestic or municipal supply shall not contain concentrations of pesticides in excess of the limiting concentrations set forth in California Code of Regulations, Title 22, Division 4, Chapter 15, Article 4, Section 64444, and listed in Table 3.2 of the Basin Plan. No evaluation guideline could be found to evaluate protection of the MUN beneficial use that meets the requirements of Section 6.1.3 of the Listing Policy. |
Objective/Criterion Reference: |
Water Quality Control Plan (Basin Plan) for the North Coast Region |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
Data for this line of evidence for Klamath River HU, Shasta River HA was collected at 1 monitoring site [ Shasta River near Edgewood - 105SH9274] |
Temporal Representation: |
Data was collected over the time period 10/7/2002-6/19/2003. |
Environmental Conditions: |
There are no known environmental conditions (e.g., seasonality, land use practices, fire events, storms, etc.) that are related to these data. |
QAPP Information: |
Quality control was conducted in accordance with the SWAMP Quality Assurance Management Plan (SWAMP 2002). |
QAPP Information Reference(s): |
Quality Assurance Management Plan for the State of California's Surface Water Ambient Monitoring Program. Sacramento, CA. State Water Resources Control Board. SWAMP. December 2002 (1st version)
|
|
Line of Evidence (LOE) for Decision ID 74010, DDD (Dichlorodiphenyldichloroethane)
|
Region 1 |
Klamath River HU, Shasta River HA |
|
|
LOE ID: |
106124 |
|
Pollutant: |
DDD (Dichlorodiphenyldichloroethane) |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Total |
|
Beneficial Use: |
Commercial or recreational collection of fish, shellfish, or organisms |
|
Number of Samples: |
0 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP RWB1 Monitoring data for Klamath River HU, Shasta River HA to determine beneficial use support, and the results are as follows: 0 of the 0 samples exceeded the evaluation guideline for DDD(p,p'). Although a total of 1 samples were collected, 1 of these samples were not included in the assessment because the laboratory data reporting limit(s) was above the objective and therefore the results could not be quantified with the level of certainty required by the Listing Policy Section 6.1.5.5. |
Data Reference: |
Water Quality Assessment Data for the 2018 solicitation cycle submitted through CEDEN for SWAMP RWB1 Monitoring .
|
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
The 4,4'-DDD criterion for the protection of human health from consumption of organisms only is 0.00084 ug/L (California Toxics Rule, 2000). |
Objective/Criterion Reference: |
Water Quality Standards 2000. Establishment of numeric criteria for priority toxic pollutants for the State of California: Rules and regulations. Federal Register Vol. 65, No. 97. Washington, D.C.: Environmental Protection Agency |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
Data was collected from 1 station(s) (Station Code(s) 105SH1452). |
Temporal Representation: |
Date for this waterbody was collected over the date range 2013-04-29 to 2013-04-29 |
Environmental Conditions: |
|
QAPP Information: |
Quality Assurance Program Plan and Standard Operating Procedures for SWAMP program |
QAPP Information Reference(s): |
Quality Assurance Program Plans, Quality Assurance Project Plans, and Standard Operating Procedures for the SWAMP program |
|
Line of Evidence (LOE) for Decision ID 168794, Dacthal
|
Region 1 |
Klamath River HU, Shasta River HA |
|
|
LOE ID: |
349322 |
|
Pollutant: |
Dacthal |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Total |
|
Beneficial Use: |
Warm Freshwater Habitat |
|
Number of Samples: |
3 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed RWB1 Trend Maintenance Periods FYs 2007 2008 data for Klamath River HU, Shasta River HA to determine beneficial use support and results are as follows: 0 of 3 samples exceeded the water quality threshold for Dacthal. |
Data Reference: |
RWB1 Trend Maintenance Periods FYs 2007 2008 |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
All waters shall be maintained free of toxic substances in concentrations which are toxic to, or which produce detrimental physiological responses in, human, plant, animal, or aquatic life. (Basin Plan). |
Objective/Criterion Reference: |
Water Quality Control Plan (Basin Plan) for the North Coast Region |
|
Evaluation Guideline: |
The evaluation guideline for Dacthal is the USEPA Aquatic Life Benchmark of >11000 ug/L for a nonvascular plant (acute) and vascular plant (acute). The benchmark was derived from a greater-than value (for example, > 265,000) and may overestimate toxicity. |
Guideline Reference: |
OPP Aquatic Life Benchmarks |
|
Spatial Representation: |
The samples were collected at 1 monitoring site: 105SHAEDG (Shasta River near Edgewood). |
Temporal Representation: |
The samples were collected between the dates of 2007-11-15 and 2008-07-16 |
Environmental Conditions: |
|
QAPP Information: |
Generic SWAMP QAPrP |
QAPP Information Reference(s): |
Generic SWAMP QAPrP |
|
Line of Evidence (LOE) for Decision ID 168794, Dacthal
|
Region 1 |
Klamath River HU, Shasta River HA |
|
|
LOE ID: |
349323 |
|
Pollutant: |
Dacthal |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Total |
|
Beneficial Use: |
Cold Freshwater Habitat |
|
Number of Samples: |
3 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed RWB1 Trend Maintenance Periods FYs 2007 2008 data for Klamath River HU, Shasta River HA to determine beneficial use support and results are as follows: 0 of 3 samples exceeded the water quality threshold for Dacthal. |
Data Reference: |
RWB1 Trend Maintenance Periods FYs 2007 2008 |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
All waters shall be maintained free of toxic substances in concentrations which are toxic to, or which produce detrimental physiological responses in, human, plant, animal, or aquatic life. (Basin Plan). |
Objective/Criterion Reference: |
Water Quality Control Plan (Basin Plan) for the North Coast Region |
|
Evaluation Guideline: |
The evaluation guideline for Dacthal is the USEPA Aquatic Life Benchmark of >11000 ug/L for a nonvascular plant (acute) and vascular plant (acute). The benchmark was derived from a greater-than value (for example, > 265,000) and may overestimate toxicity. |
Guideline Reference: |
OPP Aquatic Life Benchmarks |
|
Spatial Representation: |
The samples were collected at 1 monitoring site: 105SHA263 (Shasta River at Hwy 263). |
Temporal Representation: |
The samples were collected between the dates of 2007-11-15 and 2008-07-16 |
Environmental Conditions: |
|
QAPP Information: |
Generic SWAMP QAPrP |
QAPP Information Reference(s): |
Generic SWAMP QAPrP |
|
Line of Evidence (LOE) for Decision ID 168794, Dacthal
|
Region 1 |
Klamath River HU, Shasta River HA |
|
|
LOE ID: |
123318 |
|
Pollutant: |
Dacthal |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
None |
|
Beneficial Use: |
Municipal & Domestic Supply |
|
Number of Samples: |
0 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
State Water Board staff re-assessed SWAMP data for Klamath River HU, Shasta River HA to determine beneficial use support and results are as follows: 0 of 0 samples exceed the criterion for Dacthal, Total. Eight sample results were not used in the assessment because the laboratory data reporting limit(s) was above the objective and therefore the results could not be quantified with the level of certainty required by the Listing Policy. This LOE re-assesses data from LOE 29849 from the 2010 Integrated Report. Data were re-assessed in order to evaluate these data in their own LOE, instead of being evaluated in the same LOE as other pesticide data. |
Data Reference: |
Surface Water Ambient Monitoring Program (SWAMP). Summary Report for the North Coast Region (RWQCB-1) for years 2000-2006. North Coast Regional Water Quality Control Board. March 2008 |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
Water Quality Control Plan, North Coast Region (NCRWQCB 2011): All waters shall be maintained free of toxic substances in concentrations that are toxic to, or that produce detrimental physiological responses in human, plant, animal, or aquatic life. USEPA's Lifetime Health advisory level for Dacthal is 0.07 mg/L as stated on page 3 of the 2011 edition of the drinking water standards and health advisories. |
Objective/Criterion Reference: |
Water Quality Control Plan (Basin Plan) for the North Coast Region |
Objective/Criterion Reference: |
2011 Edition of the Drinking Water Standards and Health Advisories |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
Data for this line of evidence for Klamath River HU, Shasta River HA was collected at 1 monitoring site [ Yreka Creek at Anderson Rd - 105YREAND] |
Temporal Representation: |
Data was collected over the time period 10/9/2002-6/20/2005. |
Environmental Conditions: |
There are no known environmental conditions (e.g., seasonality, land use practices, fire events, storms, etc.) that are related to these data. |
QAPP Information: |
Quality control was conducted in accordance with the SWAMP Quality Assurance Management Plan (SWAMP 2002). |
QAPP Information Reference(s): |
Quality Assurance Management Plan for the State of California's Surface Water Ambient Monitoring Program. Sacramento, CA. State Water Resources Control Board. SWAMP. December 2002 (1st version)
|
|
Line of Evidence (LOE) for Decision ID 168794, Dacthal
|
Region 1 |
Klamath River HU, Shasta River HA |
|
|
LOE ID: |
103200 |
|
Pollutant: |
Dacthal |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Total |
|
Beneficial Use: |
Municipal & Domestic Supply |
|
Number of Samples: |
1 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP RWB1 Monitoring data for Klamath River HU, Shasta River HA to determine beneficial use support and results are as follows: 0 of 1 samples exceeded the water quality standard for Dacthal. |
Data Reference: |
Water Quality Assessment Data for the 2018 solicitation cycle submitted through CEDEN for SWAMP RWB1 Monitoring .
|
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
No individual pesticide or combination of pesticides shall be present in concentrations that adversely affect beneficial uses (Water Quality Control Plan, North Coast Basin). |
Objective/Criterion Reference: |
Water Quality Control Plan (Basin Plan) for the North Coast Region |
|
Evaluation Guideline: |
The USEPA Lifetime Health advisory level for Dacthal is 0.07 mg/L. |
Guideline Reference: |
2012 Edition of the Drinking Water Standards and Health Advisories |
|
Spatial Representation: |
The samples were collected at 1 monitoring site(s) (105SH9274) |
Temporal Representation: |
The samples were collected between the dates of 2013-04-29 and 2013-04-29 |
Environmental Conditions: |
|
QAPP Information: |
Quality Assurance Program Plan and Standard Operating Procedures for SWAMP program |
QAPP Information Reference(s): |
Quality Assurance Program Plans, Quality Assurance Project Plans, and Standard Operating Procedures for the SWAMP program |
|
Line of Evidence (LOE) for Decision ID 168794, Dacthal
|
Region 1 |
Klamath River HU, Shasta River HA |
|
|
LOE ID: |
103199 |
|
Pollutant: |
Dacthal |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Total |
|
Beneficial Use: |
Cold Freshwater Habitat |
|
Number of Samples: |
1 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP RWB1 Monitoring data for Klamath River HU, Shasta River HA to determine beneficial use support and results are as follows: 0 of 1 samples exceeded the water quality standard for Dacthal. |
Data Reference: |
Water Quality Assessment Data for the 2018 solicitation cycle submitted through CEDEN for SWAMP RWB1 Monitoring .
|
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
All waters shall be maintained free of toxic substances in concentrations which are toxic to, or which produce detrimental physiological responses in, human, plant, animal, or aquatic life. (Basin Plan). |
Objective/Criterion Reference: |
Water Quality Control Plan (Basin Plan) for the North Coast Region |
|
Evaluation Guideline: |
The evaluation guideline for Dacthal is the USEPA Aquatic Life Benchmark of > 11000 ug/L for a nonvascular plant (acute) and vascular plant (acute). The benchmark was derived from a \greater-than\" value (for example, > 265,000) and may overestimate toxicity." |
Guideline Reference: |
OPP Aquatic Life Benchmarks |
|
Spatial Representation: |
The samples were collected at 1 monitoring site(s) (105SH9274) |
Temporal Representation: |
The samples were collected between the dates of 2013-04-29 and 2013-04-29 |
Environmental Conditions: |
|
QAPP Information: |
Quality Assurance Program Plan and Standard Operating Procedures for SWAMP program |
QAPP Information Reference(s): |
Quality Assurance Program Plans, Quality Assurance Project Plans, and Standard Operating Procedures for the SWAMP program |
|
Line of Evidence (LOE) for Decision ID 168794, Dacthal
|
Region 1 |
Klamath River HU, Shasta River HA |
|
|
LOE ID: |
103195 |
|
Pollutant: |
Dacthal |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Total |
|
Beneficial Use: |
Cold Freshwater Habitat |
|
Number of Samples: |
1 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP RWB1 Monitoring data for Klamath River HU, Shasta River HA to determine beneficial use support and results are as follows: 0 of 1 samples exceeded the water quality standard for Dacthal. |
Data Reference: |
Water Quality Assessment Data for the 2018 solicitation cycle submitted through CEDEN for SWAMP RWB1 Monitoring .
|
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
All waters shall be maintained free of toxic substances in concentrations which are toxic to, or which produce detrimental physiological responses in, human, plant, animal, or aquatic life. (Basin Plan). |
Objective/Criterion Reference: |
Water Quality Control Plan (Basin Plan) for the North Coast Region |
|
Evaluation Guideline: |
The evaluation guideline for Dacthal is the USEPA Aquatic Life Benchmark of > 11000 ug/L for a nonvascular plant (acute) and vascular plant (acute). The benchmark was derived from a \greater-than\" value (for example, > 265,000) and may overestimate toxicity." |
Guideline Reference: |
OPP Aquatic Life Benchmarks |
|
Spatial Representation: |
The samples were collected at 1 monitoring site(s) (105SH1452) |
Temporal Representation: |
The samples were collected between the dates of 2013-04-29 and 2013-04-29 |
Environmental Conditions: |
|
QAPP Information: |
Quality Assurance Program Plan and Standard Operating Procedures for SWAMP program |
QAPP Information Reference(s): |
Quality Assurance Program Plans, Quality Assurance Project Plans, and Standard Operating Procedures for the SWAMP program |
|
Line of Evidence (LOE) for Decision ID 168794, Dacthal
|
Region 1 |
Klamath River HU, Shasta River HA |
|
|
LOE ID: |
103201 |
|
Pollutant: |
Dacthal |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Total |
|
Beneficial Use: |
Warm Freshwater Habitat |
|
Number of Samples: |
1 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP RWB1 Monitoring data for Klamath River HU, Shasta River HA to determine beneficial use support and results are as follows: 0 of 1 samples exceeded the water quality standard for Dacthal. |
Data Reference: |
Water Quality Assessment Data for the 2018 solicitation cycle submitted through CEDEN for SWAMP RWB1 Monitoring .
|
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
All waters shall be maintained free of toxic substances in concentrations which are toxic to, or which produce detrimental physiological responses in, human, plant, animal, or aquatic life. (Basin Plan). |
Objective/Criterion Reference: |
Water Quality Control Plan (Basin Plan) for the North Coast Region |
|
Evaluation Guideline: |
The evaluation guideline for Dacthal is the USEPA Aquatic Life Benchmark of > 11000 ug/L for a nonvascular plant (acute) and vascular plant (acute). The benchmark was derived from a \greater-than\" value (for example, > 265,000) and may overestimate toxicity." |
Guideline Reference: |
OPP Aquatic Life Benchmarks |
|
Spatial Representation: |
The samples were collected at 1 monitoring site(s) (105SH9274) |
Temporal Representation: |
The samples were collected between the dates of 2013-04-29 and 2013-04-29 |
Environmental Conditions: |
|
QAPP Information: |
Quality Assurance Program Plan and Standard Operating Procedures for SWAMP program |
QAPP Information Reference(s): |
Quality Assurance Program Plans, Quality Assurance Project Plans, and Standard Operating Procedures for the SWAMP program |
|
Line of Evidence (LOE) for Decision ID 168794, Dacthal
|
Region 1 |
Klamath River HU, Shasta River HA |
|
|
LOE ID: |
103196 |
|
Pollutant: |
Dacthal |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Total |
|
Beneficial Use: |
Municipal & Domestic Supply |
|
Number of Samples: |
1 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP RWB1 Monitoring data for Klamath River HU, Shasta River HA to determine beneficial use support and results are as follows: 0 of 1 samples exceeded the water quality standard for Dacthal. |
Data Reference: |
Water Quality Assessment Data for the 2018 solicitation cycle submitted through CEDEN for SWAMP RWB1 Monitoring .
|
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
No individual pesticide or combination of pesticides shall be present in concentrations that adversely affect beneficial uses (Water Quality Control Plan, North Coast Basin). |
Objective/Criterion Reference: |
Water Quality Control Plan (Basin Plan) for the North Coast Region |
|
Evaluation Guideline: |
The USEPA Lifetime Health advisory level for Dacthal is 0.07 mg/L. |
Guideline Reference: |
2012 Edition of the Drinking Water Standards and Health Advisories |
|
Spatial Representation: |
The samples were collected at 1 monitoring site(s) (105SH1452) |
Temporal Representation: |
The samples were collected between the dates of 2013-04-29 and 2013-04-29 |
Environmental Conditions: |
|
QAPP Information: |
Quality Assurance Program Plan and Standard Operating Procedures for SWAMP program |
QAPP Information Reference(s): |
Quality Assurance Program Plans, Quality Assurance Project Plans, and Standard Operating Procedures for the SWAMP program |
|
Line of Evidence (LOE) for Decision ID 168794, Dacthal
|
Region 1 |
Klamath River HU, Shasta River HA |
|
|
LOE ID: |
103198 |
|
Pollutant: |
Dacthal |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Total |
|
Beneficial Use: |
Warm Freshwater Habitat |
|
Number of Samples: |
1 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP RWB1 Monitoring data for Klamath River HU, Shasta River HA to determine beneficial use support and results are as follows: 0 of 1 samples exceeded the water quality standard for Dacthal. |
Data Reference: |
Water Quality Assessment Data for the 2018 solicitation cycle submitted through CEDEN for SWAMP RWB1 Monitoring .
|
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
All waters shall be maintained free of toxic substances in concentrations which are toxic to, or which produce detrimental physiological responses in, human, plant, animal, or aquatic life. (Basin Plan). |
Objective/Criterion Reference: |
Water Quality Control Plan (Basin Plan) for the North Coast Region |
|
Evaluation Guideline: |
The evaluation guideline for Dacthal is the USEPA Aquatic Life Benchmark of > 11000 ug/L for a nonvascular plant (acute) and vascular plant (acute). The benchmark was derived from a \greater-than\" value (for example, > 265,000) and may overestimate toxicity." |
Guideline Reference: |
OPP Aquatic Life Benchmarks |
|
Spatial Representation: |
The samples were collected at 1 monitoring site(s) (105SH1452) |
Temporal Representation: |
The samples were collected between the dates of 2013-04-29 and 2013-04-29 |
Environmental Conditions: |
|
QAPP Information: |
Quality Assurance Program Plan and Standard Operating Procedures for SWAMP program |
QAPP Information Reference(s): |
Quality Assurance Program Plans, Quality Assurance Project Plans, and Standard Operating Procedures for the SWAMP program |
|
Line of Evidence (LOE) for Decision ID 168794, Dacthal
|
Region 1 |
Klamath River HU, Shasta River HA |
|
|
LOE ID: |
123317 |
|
Pollutant: |
Dacthal |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
None |
|
Beneficial Use: |
Municipal & Domestic Supply |
|
Number of Samples: |
0 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
State Water Board staff re-assessed SWAMP data for Klamath River HU, Shasta River HA to determine beneficial use support and results are as follows: 0 of 0 samples exceed the criterion for Dacthal, Total. Four sample results were not used in the assessment because the laboratory data reporting limit(s) was above the objective and therefore the results could not be quantified with the level of certainty required by the Listing Policy. This LOE re-assesses data from LOE 29849 from the 2010 Integrated Report. Data were re-assessed in order to evaluate these data in their own LOE, instead of being evaluated in the same LOE as other pesticide data. |
Data Reference: |
Surface Water Ambient Monitoring Program (SWAMP). Summary Report for the North Coast Region (RWQCB-1) for years 2000-2006. North Coast Regional Water Quality Control Board. March 2008 |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
Water Quality Control Plan, North Coast Region (NCRWQCB 2011): All waters shall be maintained free of toxic substances in concentrations that are toxic to, or that produce detrimental physiological responses in human, plant, animal, or aquatic life. USEPA's Lifetime Health advisory level for Dacthal is 0.07 mg/L as stated on page 3 of the 2011 edition of the drinking water standards and health advisories. |
Objective/Criterion Reference: |
Water Quality Control Plan (Basin Plan) for the North Coast Region |
Objective/Criterion Reference: |
2011 Edition of the Drinking Water Standards and Health Advisories |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
Data for this line of evidence for Klamath River HU, Shasta River HA was collected at 1 monitoring site [ Shasta River near Edgewood - 105SH9274] |
Temporal Representation: |
Data was collected over the time period 10/7/2002-6/19/2003. |
Environmental Conditions: |
There are no known environmental conditions (e.g., seasonality, land use practices, fire events, storms, etc.) that are related to these data. |
QAPP Information: |
Quality control was conducted in accordance with the SWAMP Quality Assurance Management Plan (SWAMP 2002). |
QAPP Information Reference(s): |
Quality Assurance Management Plan for the State of California's Surface Water Ambient Monitoring Program. Sacramento, CA. State Water Resources Control Board. SWAMP. December 2002 (1st version)
|
|
Line of Evidence (LOE) for Decision ID 168794, Dacthal
|
Region 1 |
Klamath River HU, Shasta River HA |
|
|
LOE ID: |
123316 |
|
Pollutant: |
Dacthal |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
None |
|
Beneficial Use: |
Municipal & Domestic Supply |
|
Number of Samples: |
0 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
State Water Board staff re-assessed SWAMP data for Klamath River HU, Shasta River HA to determine beneficial use support and results are as follows: 0 of 0 samples exceed the criterion for Dacthal, Total. Four sample results were not used in the assessment because the laboratory data reporting limit(s) was above the objective and therefore the results could not be quantified with the level of certainty required by the Listing Policy. This LOE re-assesses data from LOE 29849 from the 2010 Integrated Report. Data were re-assessed in order to evaluate these data in their own LOE, instead of being evaluated in the same LOE as other pesticide data. |
Data Reference: |
Surface Water Ambient Monitoring Program (SWAMP). Summary Report for the North Coast Region (RWQCB-1) for years 2000-2006. North Coast Regional Water Quality Control Board. March 2008 |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
Water Quality Control Plan, North Coast Region (NCRWQCB 2011): All waters shall be maintained free of toxic substances in concentrations that are toxic to, or that produce detrimental physiological responses in human, plant, animal, or aquatic life. USEPA's Lifetime Health advisory level for Dacthal is 0.07 mg/L as stated on page 3 of the 2011 edition of the drinking water standards and health advisories. |
Objective/Criterion Reference: |
Water Quality Control Plan (Basin Plan) for the North Coast Region |
Objective/Criterion Reference: |
2011 Edition of the Drinking Water Standards and Health Advisories |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
Data for this line of evidence for Klamath River HU, Shasta River HA was collected at 1 monitoring site [ Shasta River at Montague - 105SHAMON] |
Temporal Representation: |
Data was collected over the time period 10/7/2002-6/19/2003. |
Environmental Conditions: |
There are no known environmental conditions (e.g., seasonality, land use practices, fire events, storms, etc.) that are related to these data. |
QAPP Information: |
Quality control was conducted in accordance with the SWAMP Quality Assurance Management Plan (SWAMP 2002). |
QAPP Information Reference(s): |
Quality Assurance Management Plan for the State of California's Surface Water Ambient Monitoring Program. Sacramento, CA. State Water Resources Control Board. SWAMP. December 2002 (1st version)
|
|
Line of Evidence (LOE) for Decision ID 168794, Dacthal
|
Region 1 |
Klamath River HU, Shasta River HA |
|
|
LOE ID: |
123319 |
|
Pollutant: |
Dacthal |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
None |
|
Beneficial Use: |
Municipal & Domestic Supply |
|
Number of Samples: |
0 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
State Water Board staff re-assessed SWAMP data for Klamath River HU, Shasta River HA to determine beneficial use support and results are as follows: 0 of 0 samples exceed the criterion for Dacthal, Total. Four sample results were not used in the assessment because the laboratory data reporting limit(s) was above the objective and therefore the results could not be quantified with the level of certainty required by the Listing Policy. This LOE re-assesses data from LOE 29849 from the 2010 Integrated Report. Data were re-assessed in order to evaluate these data in their own LOE, instead of being evaluated in the same LOE as other pesticide data. |
Data Reference: |
Surface Water Ambient Monitoring Program (SWAMP). Summary Report for the North Coast Region (RWQCB-1) for years 2000-2006. North Coast Regional Water Quality Control Board. March 2008 |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
Water Quality Control Plan, North Coast Region (NCRWQCB 2011): All waters shall be maintained free of toxic substances in concentrations that are toxic to, or that produce detrimental physiological responses in human, plant, animal, or aquatic life. USEPA's Lifetime Health advisory level for Dacthal is 0.07 mg/L as stated on page 3 of the 2011 edition of the drinking water standards and health advisories. |
Objective/Criterion Reference: |
Water Quality Control Plan (Basin Plan) for the North Coast Region |
Objective/Criterion Reference: |
2011 Edition of the Drinking Water Standards and Health Advisories |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
Data for this line of evidence for Klamath River HU, Shasta River HA was collected at 1 monitoring site [ Yreka Creek at Highway 3 - 105YREHW3] |
Temporal Representation: |
Data was collected over the time period 10/21/2004-6/20/2005. |
Environmental Conditions: |
There are no known environmental conditions (e.g., seasonality, land use practices, fire events, storms, etc.) that are related to these data. |
QAPP Information: |
Quality control was conducted in accordance with the SWAMP Quality Assurance Management Plan (SWAMP 2002). |
QAPP Information Reference(s): |
Quality Assurance Management Plan for the State of California's Surface Water Ambient Monitoring Program. Sacramento, CA. State Water Resources Control Board. SWAMP. December 2002 (1st version)
|
|
Line of Evidence (LOE) for Decision ID 168794, Dacthal
|
Region 1 |
Klamath River HU, Shasta River HA |
|
|
LOE ID: |
349316 |
|
Pollutant: |
Dacthal |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Total |
|
Beneficial Use: |
Cold Freshwater Habitat |
|
Number of Samples: |
3 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed RWB1 Trend Maintenance Periods FYs 2007 2008 data for Klamath River HU, Shasta River HA to determine beneficial use support and results are as follows: 0 of 3 samples exceeded the water quality threshold for Dacthal. |
Data Reference: |
RWB1 Trend Maintenance Periods FYs 2007 2008 |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
All waters shall be maintained free of toxic substances in concentrations which are toxic to, or which produce detrimental physiological responses in, human, plant, animal, or aquatic life. (Basin Plan). |
Objective/Criterion Reference: |
Water Quality Control Plan (Basin Plan) for the North Coast Region |
|
Evaluation Guideline: |
The evaluation guideline for Dacthal is the USEPA Aquatic Life Benchmark of >11000 ug/L for a nonvascular plant (acute) and vascular plant (acute). The benchmark was derived from a greater-than value (for example, > 265,000) and may overestimate toxicity. |
Guideline Reference: |
OPP Aquatic Life Benchmarks |
|
Spatial Representation: |
The samples were collected at 1 monitoring site: 105SHAEDG (Shasta River near Edgewood). |
Temporal Representation: |
The samples were collected between the dates of 2007-11-15 and 2008-07-16 |
Environmental Conditions: |
|
QAPP Information: |
Generic SWAMP QAPrP |
QAPP Information Reference(s): |
Generic SWAMP QAPrP |
|
Line of Evidence (LOE) for Decision ID 168794, Dacthal
|
Region 1 |
Klamath River HU, Shasta River HA |
|
|
LOE ID: |
349319 |
|
Pollutant: |
Dacthal |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Total |
|
Beneficial Use: |
Warm Freshwater Habitat |
|
Number of Samples: |
3 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed RWB1 Trend Maintenance Periods FYs 2007 2008 data for Klamath River HU, Shasta River HA to determine beneficial use support and results are as follows: 0 of 3 samples exceeded the water quality threshold for Dacthal. |
Data Reference: |
RWB1 Trend Maintenance Periods FYs 2007 2008 |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
All waters shall be maintained free of toxic substances in concentrations which are toxic to, or which produce detrimental physiological responses in, human, plant, animal, or aquatic life. (Basin Plan). |
Objective/Criterion Reference: |
Water Quality Control Plan (Basin Plan) for the North Coast Region |
|
Evaluation Guideline: |
The evaluation guideline for Dacthal is the USEPA Aquatic Life Benchmark of >11000 ug/L for a nonvascular plant (acute) and vascular plant (acute). The benchmark was derived from a greater-than value (for example, > 265,000) and may overestimate toxicity. |
Guideline Reference: |
OPP Aquatic Life Benchmarks |
|
Spatial Representation: |
The samples were collected at 1 monitoring site: 105SHA263 (Shasta River at Hwy 263). |
Temporal Representation: |
The samples were collected between the dates of 2007-11-15 and 2008-07-16 |
Environmental Conditions: |
|
QAPP Information: |
Generic SWAMP QAPrP |
QAPP Information Reference(s): |
Generic SWAMP QAPrP |
|
Line of Evidence (LOE) for Decision ID 168794, Dacthal
|
Region 1 |
Klamath River HU, Shasta River HA |
|
|
LOE ID: |
123305 |
|
Pollutant: |
Dacthal |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
None |
|
Beneficial Use: |
Municipal & Domestic Supply |
|
Number of Samples: |
0 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
State Water Board staff re-assessed SWAMP data for Klamath River HU, Shasta River HA to determine beneficial use support and results are as follows: 0 of 0 samples exceed the criterion for Dacthal, Total. Sixteen sample results were not used in the assessment because the laboratory data reporting limit(s) was above the objective and therefore the results could not be quantified with the level of certainty required by the Listing Policy. This LOE re-assesses data from LOE 29849 from the 2010 Integrated Report. Data were re-assessed in order to evaluate these data in their own LOE, instead of being evaluated in the same LOE as other pesticide data. |
Data Reference: |
Surface Water Ambient Monitoring Program (SWAMP). Summary Report for the North Coast Region (RWQCB-1) for years 2000-2006. North Coast Regional Water Quality Control Board. March 2008 |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
Water Quality Control Plan, North Coast Region (NCRWQCB 2011): All waters shall be maintained free of toxic substances in concentrations that are toxic to, or that produce detrimental physiological responses in human, plant, animal, or aquatic life. USEPA's Lifetime Health advisory level for Dacthal is 0.07 mg/L as stated on page 3 of the 2011 edition of the drinking water standards and health advisories. |
Objective/Criterion Reference: |
Water Quality Control Plan (Basin Plan) for the North Coast Region |
Objective/Criterion Reference: |
2011 Edition of the Drinking Water Standards and Health Advisories |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
Data for this line of evidence for Klamath River HU, Shasta River HA was collected at 1 monitoring site [ Shasta River at Hwy 263 - 105SH1452] |
Temporal Representation: |
Data was collected over the time period 2/27/2002-11/16/2006. |
Environmental Conditions: |
There are no known environmental conditions (e.g., seasonality, land use practices, fire events, storms, etc.) that are related to these data. |
QAPP Information: |
Quality control was conducted in accordance with the SWAMP Quality Assurance Management Plan (SWAMP 2002). |
QAPP Information Reference(s): |
Quality Assurance Management Plan for the State of California's Surface Water Ambient Monitoring Program. Sacramento, CA. State Water Resources Control Board. SWAMP. December 2002 (1st version)
|
|
Line of Evidence (LOE) for Decision ID 105199, Dieldrin
|
Region 1 |
Klamath River HU, Shasta River HA |
|
|
LOE ID: |
117936 |
|
Pollutant: |
Dieldrin |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Total |
|
Beneficial Use: |
Commercial or recreational collection of fish, shellfish, or organisms |
|
Number of Samples: |
0 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP RWB1 Monitoring data for Klamath River HU, Shasta River HA to determine beneficial use support, and the results are as follows: 0 of the 0 samples exceeded the evaluation guideline for Dieldrin. Although a total of 1 samples were collected, 1 of these samples were not included in the assessment because the laboratory data reporting limit(s) was above the objective and therefore the results could not be quantified with the level of certainty required by the Listing Policy Section 6.1.5.5. |
Data Reference: |
Water Quality Assessment Data for the 2018 solicitation cycle submitted through CEDEN for SWAMP RWB1 Monitoring .
|
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
Water Quality Control Plan, North Coast Region (NCRWQCB 2018): All waters shall be maintained free of toxic substances in concentrations that are toxic to, or that produce detrimental physiological responses in human, plant, animal, or aquatic life. The established numeric criteria for dieldrin to protection of human health from consumption of organisms only is 0.00014 ug/L (California Toxics Rule, 2000). |
Objective/Criterion Reference: |
Water Quality Standards 2000. Establishment of numeric criteria for priority toxic pollutants for the State of California: Rules and regulations. Federal Register Vol. 65, No. 97. Washington, D.C.: Environmental Protection Agency |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
Data was collected from 1 station(s) (Station Code(s) 105SH1452). |
Temporal Representation: |
Date for this waterbody was collected over the date range 2013-04-29 to 2013-04-29 |
Environmental Conditions: |
|
QAPP Information: |
Quality Assurance Program Plan and Standard Operating Procedures for SWAMP program |
QAPP Information Reference(s): |
Quality Assurance Program Plans, Quality Assurance Project Plans, and Standard Operating Procedures for the SWAMP program |
|
Line of Evidence (LOE) for Decision ID 105199, Dieldrin
|
Region 1 |
Klamath River HU, Shasta River HA |
|
|
LOE ID: |
41754 |
|
Pollutant: |
Dieldrin |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Total |
|
Beneficial Use: |
Commercial or recreational collection of fish, shellfish, or organisms |
|
Number of Samples: |
0 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Three non-detect sample results were not used in the assessment because the laboratory data reporting limit was above the objective and therefore the results could not be quantified with the level of certainty required by the Listing Policy. |
Data Reference: |
RWB1 Trend Maintenance Periods FYs 2007 2008 |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
Water Quality Control Plan, North Coast Region (NCRWQCB 2011): All waters shall be maintained free of toxic substances in concentrations that are toxic to, or that produce detrimental physiological responses in human, plant, animal, or aquatic life. The established numeric criteria for dieldrin to protection of human health from consumption of organisms only is 0.00014 ug/L (California Toxics Rule, 2000). |
Objective/Criterion Reference: |
Code of Federal Regulations 40 part 131.38 Establishment of numeric criteria for priority toxic pollutants for the State of California. 7/1/2011 Edition |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
Data for this line of evidence for Klamath River HU, Shasta River HA was collected at 1 monitoring site [ Shasta River near Edgewood - 105SHAEDG] |
Temporal Representation: |
Data was collected over the time period 11/15/2007-7/16/2008. |
Environmental Conditions: |
Staff is not aware of any special conditions that might affect interpretation of the data. |
QAPP Information: |
The SWAMP QAPP (2008) was followed. |
QAPP Information Reference(s): |
Surface Water Ambient Monitoring Program Quality Assurance Program Plan |
|
Line of Evidence (LOE) for Decision ID 105199, Dieldrin
|
Region 1 |
Klamath River HU, Shasta River HA |
|
|
LOE ID: |
41755 |
|
Pollutant: |
Dieldrin |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Total |
|
Beneficial Use: |
Commercial or recreational collection of fish, shellfish, or organisms |
|
Number of Samples: |
0 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Three non-detect sample results were not used in the assessment because the laboratory data reporting limit was above the objective and therefore the results could not be quantified with the level of certainty required by the Listing Policy. |
Data Reference: |
RWB1 Trend Maintenance Periods FYs 2007 2008 |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
Water Quality Control Plan, North Coast Region (NCRWQCB 2011): All waters shall be maintained free of toxic substances in concentrations that are toxic to, or that produce detrimental physiological responses in human, plant, animal, or aquatic life. The established numeric criteria for dieldrin to protection of human health from consumption of organisms only is 0.00014 ug/L (California Toxics Rule, 2000). |
Objective/Criterion Reference: |
Code of Federal Regulations 40 part 131.38 Establishment of numeric criteria for priority toxic pollutants for the State of California. 7/1/2011 Edition |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
Data for this line of evidence for Klamath River HU, Shasta River HA was collected at 1 monitoring site [ Shasta River at Hwy 263 - 105SHA263] |
Temporal Representation: |
Data was collected over the time period 11/15/2007-7/16/2008. |
Environmental Conditions: |
Staff is not aware of any special conditions that might affect interpretation of the data. |
QAPP Information: |
The SWAMP QAPP (2008) was followed. |
QAPP Information Reference(s): |
Surface Water Ambient Monitoring Program Quality Assurance Program Plan |
|
Line of Evidence (LOE) for Decision ID 105199, Dieldrin
|
Region 1 |
Klamath River HU, Shasta River HA |
|
|
LOE ID: |
117937 |
|
Pollutant: |
Dieldrin |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Total |
|
Beneficial Use: |
Municipal & Domestic Supply |
|
Number of Samples: |
0 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP RWB1 Monitoring data for Klamath River HU, Shasta River HA to determine beneficial use support, and the results are as follows: 0 of the 0 samples exceeded the evaluation guideline for Dieldrin. Although a total of 1 samples were collected, 1 of these samples were not included in the assessment because the laboratory data reporting limit(s) was above the objective and therefore the results could not be quantified with the level of certainty required by the Listing Policy Section 6.1.5.5. |
Data Reference: |
Water Quality Assessment Data for the 2018 solicitation cycle submitted through CEDEN for SWAMP RWB1 Monitoring .
|
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
Water Quality Control Plan, North Coast Region (NCRWQCB 2018): All waters shall be maintained free of toxic substances in concentrations that are toxic to, or that produce detrimental physiological responses in human, plant, animal, or aquatic life. The established numeric criteria for dieldrin to protect human health from the consumption of water and organisms is 0.00014 ug/L (California Toxics Rule, 2000). |
Objective/Criterion Reference: |
Water Quality Standards 2000. Establishment of numeric criteria for priority toxic pollutants for the State of California: Rules and regulations. Federal Register Vol. 65, No. 97. Washington, D.C.: Environmental Protection Agency |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
Data was collected from 1 station(s) (Station Code(s) 105SH1452). |
Temporal Representation: |
Date for this waterbody was collected over the date range 2013-04-29 to 2013-04-29 |
Environmental Conditions: |
|
QAPP Information: |
Quality Assurance Program Plan and Standard Operating Procedures for SWAMP program |
QAPP Information Reference(s): |
Quality Assurance Program Plans, Quality Assurance Project Plans, and Standard Operating Procedures for the SWAMP program |
|
Line of Evidence (LOE) for Decision ID 105199, Dieldrin
|
Region 1 |
Klamath River HU, Shasta River HA |
|
|
LOE ID: |
41781 |
|
Pollutant: |
Dieldrin |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Total |
|
Beneficial Use: |
Municipal & Domestic Supply |
|
Number of Samples: |
0 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Three non-detect sample results were not used in the assessment because the laboratory data reporting limit was above the objective and therefore the results could not be quantified with the level of certainty required by the Listing Policy. |
Data Reference: |
RWB1 Trend Maintenance Periods FYs 2007 2008 |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
Water Quality Control Plan, North Coast Region (NCRWQCB 2011): All waters shall be maintained free of toxic substances in concentrations that are toxic to, or that produce detrimental physiological responses in human, plant, animal, or aquatic life. The established numeric criteria for dieldrin to protect human health from the consumption of water and organisms is 0.00014 ug/L (California Toxics Rule, 2000). |
Objective/Criterion Reference: |
Code of Federal Regulations 40 part 131.38 Establishment of numeric criteria for priority toxic pollutants for the State of California. 7/1/2011 Edition |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
Data for this line of evidence for Klamath River HU, Shasta River HA was collected at 1 monitoring site [ Shasta River at Hwy 263 - 105SHA263] |
Temporal Representation: |
Data was collected over the time period 11/15/2007-7/16/2008. |
Environmental Conditions: |
Staff is not aware of any special conditions that might affect interpretation of the data. |
QAPP Information: |
The SWAMP QAPP (2008) was followed. |
QAPP Information Reference(s): |
Surface Water Ambient Monitoring Program Quality Assurance Program Plan |
|
Line of Evidence (LOE) for Decision ID 105199, Dieldrin
|
Region 1 |
Klamath River HU, Shasta River HA |
|
|
LOE ID: |
123534 |
|
Pollutant: |
Dieldrin |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
None |
|
Beneficial Use: |
Municipal & Domestic Supply |
|
Number of Samples: |
0 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
State Water Board staff re-assessed SWAMP data for Klamath River HU, Shasta River HA to determine beneficial use support and results are as follows: 0 of 0 samples exceed the criterion for Dieldrin, Total. Four sample results were not used in the assessment because the laboratory data reporting limit(s) was above the objective and therefore the results could not be quantified with the level of certainty required by the Listing Policy. This LOE re-assesses data from LOE 29849 from the 2010 Integrated Report. Data were re-assessed in order to evaluate these data in their own LOE, instead of being evaluated in the same LOE as other pesticide data. |
Data Reference: |
Surface Water Ambient Monitoring Program (SWAMP). Summary Report for the North Coast Region (RWQCB-1) for years 2000-2006. North Coast Regional Water Quality Control Board. March 2008 |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
Water Quality Control Plan, North Coast Region (NCRWQCB 2011): All waters shall be maintained free of toxic substances in concentrations that are toxic to, or that produce detrimental physiological responses in human, plant, animal, or aquatic life. The established numeric criteria for dieldrin to protect human health from the consumption of water and organisms is 0.00014 ug/L (California Toxics Rule, 2000). |
Objective/Criterion Reference: |
Code of Federal Regulations 40 part 131.38 Establishment of numeric criteria for priority toxic pollutants for the State of California. 7/1/2011 Edition |
Objective/Criterion Reference: |
Water Quality Control Plan (Basin Plan) for the North Coast Region |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
Data for this line of evidence for Klamath River HU, Shasta River HA was collected at 1 monitoring site [ Shasta River at Montague - 105SHAMON] |
Temporal Representation: |
Data was collected over the time period 10/7/2002-6/19/2003. |
Environmental Conditions: |
There are no known environmental conditions (e.g., seasonality, land use practices, fire events, storms, etc.) that are related to these data. |
QAPP Information: |
Quality control was conducted in accordance with the SWAMP Quality Assurance Management Plan (SWAMP 2002). |
QAPP Information Reference(s): |
Quality Assurance Management Plan for the State of California's Surface Water Ambient Monitoring Program. Sacramento, CA. State Water Resources Control Board. SWAMP. December 2002 (1st version)
|
|
Line of Evidence (LOE) for Decision ID 105199, Dieldrin
|
Region 1 |
Klamath River HU, Shasta River HA |
|
|
LOE ID: |
41496 |
|
Pollutant: |
Dieldrin |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Total |
|
Beneficial Use: |
Cold Freshwater Habitat |
|
Number of Samples: |
3 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP data for Klamath River HU, Shasta River HA to determine beneficial use support and results are as follows: 0 of 3 samples exceed the criterion for Dieldrin. |
Data Reference: |
RWB1 Trend Maintenance Periods FYs 2007 2008 |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
Water Quality Control Plan, North Coast Region (NCRWQCB 2011): All waters shall be maintained free of toxic substances in concentrations that are toxic to, or that produce detrimental physiological responses in human, plant, animal, or aquatic life. The established numeric criteria for dieldrin to protect aquatic life in freshwater as criterion continuous concentration (expressed as a 4-day average) is 0.056 ug/L (California Toxics Rule, 2000). |
Objective/Criterion Reference: |
Code of Federal Regulations 40 part 131.38 Establishment of numeric criteria for priority toxic pollutants for the State of California. 7/1/2011 Edition |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
Data for this line of evidence for Klamath River HU, Shasta River HA was collected at 1 monitoring site [ Shasta River at Hwy 263 - 105SHA263] |
Temporal Representation: |
Data was collected over the time period 11/15/2007-7/16/2008. |
Environmental Conditions: |
Staff is not aware of any special conditions that might affect interpretation of the data. |
QAPP Information: |
The SWAMP QAPP (2008) was followed. |
QAPP Information Reference(s): |
Surface Water Ambient Monitoring Program Quality Assurance Program Plan |
|
Line of Evidence (LOE) for Decision ID 105199, Dieldrin
|
Region 1 |
Klamath River HU, Shasta River HA |
|
|
LOE ID: |
41494 |
|
Pollutant: |
Dieldrin |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Total |
|
Beneficial Use: |
Cold Freshwater Habitat |
|
Number of Samples: |
3 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP data for Klamath River HU, Shasta River HA to determine beneficial use support and results are as follows: 0 of 3 samples exceed the criterion for Dieldrin. |
Data Reference: |
RWB1 Trend Maintenance Periods FYs 2007 2008 |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
Water Quality Control Plan, North Coast Region (NCRWQCB 2011): All waters shall be maintained free of toxic substances in concentrations that are toxic to, or that produce detrimental physiological responses in human, plant, animal, or aquatic life. The established numeric criteria for dieldrin to protect aquatic life in freshwater as criterion continuous concentration (expressed as a 4-day average) is 0.056 ug/L (California Toxics Rule, 2000). |
Objective/Criterion Reference: |
Code of Federal Regulations 40 part 131.38 Establishment of numeric criteria for priority toxic pollutants for the State of California. 7/1/2011 Edition |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
Data for this line of evidence for Klamath River HU, Shasta River HA was collected at 1 monitoring site [ Shasta River near Edgewood - 105SHAEDG] |
Temporal Representation: |
Data was collected over the time period 11/15/2007-7/16/2008. |
Environmental Conditions: |
Staff is not aware of any special conditions that might affect interpretation of the data. |
QAPP Information: |
The SWAMP QAPP (2008) was followed. |
QAPP Information Reference(s): |
Surface Water Ambient Monitoring Program Quality Assurance Program Plan |
|
Line of Evidence (LOE) for Decision ID 105199, Dieldrin
|
Region 1 |
Klamath River HU, Shasta River HA |
|
|
LOE ID: |
103209 |
|
Pollutant: |
Dieldrin |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Total |
|
Beneficial Use: |
Cold Freshwater Habitat |
|
Number of Samples: |
1 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP RWB1 Monitoring data for Klamath River HU, Shasta River HA to determine beneficial use support and results are as follows: 0 of 1 samples exceeded the water quality standard for Dieldrin. |
Data Reference: |
Water Quality Assessment Data for the 2018 solicitation cycle submitted through CEDEN for SWAMP RWB1 Monitoring .
|
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
Water Quality Control Plan, North Coast Region (NCRWQCB 2018): All waters shall be maintained free of toxic substances in concentrations that are toxic to, or that produce detrimental physiological responses in human, plant, animal, or aquatic life. The established numeric criteria for dieldrin to protect aquatic life in freshwater as criterion continuous concentration (expressed as a 4-day average) is 0.056 ug/L (California Toxics Rule, 2000). |
Objective/Criterion Reference: |
Water Quality Standards 2000. Establishment of numeric criteria for priority toxic pollutants for the State of California: Rules and regulations. Federal Register Vol. 65, No. 97. Washington, D.C.: Environmental Protection Agency |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
The samples were collected at 1 monitoring site(s) (105SH1452) |
Temporal Representation: |
The samples were collected between the dates of 2013-04-29 and 2013-04-29 |
Environmental Conditions: |
|
QAPP Information: |
Quality Assurance Program Plan and Standard Operating Procedures for SWAMP program |
QAPP Information Reference(s): |
Quality Assurance Program Plans, Quality Assurance Project Plans, and Standard Operating Procedures for the SWAMP program |
|
Line of Evidence (LOE) for Decision ID 105199, Dieldrin
|
Region 1 |
Klamath River HU, Shasta River HA |
|
|
LOE ID: |
103210 |
|
Pollutant: |
Dieldrin |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Total |
|
Beneficial Use: |
Cold Freshwater Habitat |
|
Number of Samples: |
1 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP RWB1 Monitoring data for Klamath River HU, Shasta River HA to determine beneficial use support and results are as follows: 0 of 1 samples exceeded the water quality standard for Dieldrin. |
Data Reference: |
Water Quality Assessment Data for the 2018 solicitation cycle submitted through CEDEN for SWAMP RWB1 Monitoring .
|
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
Water Quality Control Plan, North Coast Region (NCRWQCB 2018): All waters shall be maintained free of toxic substances in concentrations that are toxic to, or that produce detrimental physiological responses in human, plant, animal, or aquatic life. The established numeric criteria for dieldrin to protect aquatic life in freshwater as criterion continuous concentration (expressed as a 4-day average) is 0.056 ug/L (California Toxics Rule, 2000). |
Objective/Criterion Reference: |
Water Quality Standards 2000. Establishment of numeric criteria for priority toxic pollutants for the State of California: Rules and regulations. Federal Register Vol. 65, No. 97. Washington, D.C.: Environmental Protection Agency |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
The samples were collected at 1 monitoring site(s) (105SH9274) |
Temporal Representation: |
The samples were collected between the dates of 2013-04-29 and 2013-04-29 |
Environmental Conditions: |
|
QAPP Information: |
Quality Assurance Program Plan and Standard Operating Procedures for SWAMP program |
QAPP Information Reference(s): |
Quality Assurance Program Plans, Quality Assurance Project Plans, and Standard Operating Procedures for the SWAMP program |
|
Line of Evidence (LOE) for Decision ID 105199, Dieldrin
|
Region 1 |
Klamath River HU, Shasta River HA |
|
|
LOE ID: |
123535 |
|
Pollutant: |
Dieldrin |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
None |
|
Beneficial Use: |
Municipal & Domestic Supply |
|
Number of Samples: |
0 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
State Water Board staff re-assessed SWAMP data for Klamath River HU, Shasta River HA to determine beneficial use support and results are as follows: 0 of 0 samples exceed the criterion for Dieldrin, Total. Four sample results were not used in the assessment because the laboratory data reporting limit(s) was above the objective and therefore the results could not be quantified with the level of certainty required by the Listing Policy. This LOE re-assesses data from LOE 29849 from the 2010 Integrated Report. Data were re-assessed in order to evaluate these data in their own LOE, instead of being evaluated in the same LOE as other pesticide data. |
Data Reference: |
Surface Water Ambient Monitoring Program (SWAMP). Summary Report for the North Coast Region (RWQCB-1) for years 2000-2006. North Coast Regional Water Quality Control Board. March 2008 |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
Water Quality Control Plan, North Coast Region (NCRWQCB 2011): All waters shall be maintained free of toxic substances in concentrations that are toxic to, or that produce detrimental physiological responses in human, plant, animal, or aquatic life. The established numeric criteria for dieldrin to protect human health from the consumption of water and organisms is 0.00014 ug/L (California Toxics Rule, 2000). |
Objective/Criterion Reference: |
Water Quality Control Plan (Basin Plan) for the North Coast Region |
Objective/Criterion Reference: |
Code of Federal Regulations 40 part 131.38 Establishment of numeric criteria for priority toxic pollutants for the State of California. 7/1/2011 Edition |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
Data for this line of evidence for Klamath River HU, Shasta River HA was collected at 1 monitoring site [ Shasta River near Edgewood - 105SH9274] |
Temporal Representation: |
Data was collected over the time period 10/7/2002-6/19/2003. |
Environmental Conditions: |
There are no known environmental conditions (e.g., seasonality, land use practices, fire events, storms, etc.) that are related to these data. |
QAPP Information: |
Quality control was conducted in accordance with the SWAMP Quality Assurance Management Plan (SWAMP 2002). |
QAPP Information Reference(s): |
Quality Assurance Management Plan for the State of California's Surface Water Ambient Monitoring Program. Sacramento, CA. State Water Resources Control Board. SWAMP. December 2002 (1st version)
|
|
Line of Evidence (LOE) for Decision ID 105199, Dieldrin
|
Region 1 |
Klamath River HU, Shasta River HA |
|
|
LOE ID: |
123206 |
|
Pollutant: |
Dieldrin |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
None |
|
Beneficial Use: |
Municipal & Domestic Supply |
|
Number of Samples: |
0 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
State Water Board staff re-assessed SWAMP data for Klamath River HU, Shasta River HA to determine beneficial use support and results are as follows: 0 of 0 samples exceed the criterion for Dieldrin, Total. Seventeen sample results were not used in the assessment because the laboratory data reporting limit(s) was above the objective and therefore the results could not be quantified with the level of certainty required by the Listing Policy. This LOE re-assesses data from LOE 29849 from the 2010 Integrated Report. Data were re-assessed in order to evaluate these data in their own LOE, instead of being evaluated in the same LOE as other pesticide data. |
Data Reference: |
Surface Water Ambient Monitoring Program (SWAMP). Summary Report for the North Coast Region (RWQCB-1) for years 2000-2006. North Coast Regional Water Quality Control Board. March 2008 |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
Water Quality Control Plan, North Coast Region (NCRWQCB 2011): All waters shall be maintained free of toxic substances in concentrations that are toxic to, or that produce detrimental physiological responses in human, plant, animal, or aquatic life. The established numeric criteria for dieldrin to protect human health from the consumption of water and organisms is 0.00014 ug/L (California Toxics Rule, 2000). |
Objective/Criterion Reference: |
Water Quality Control Plan (Basin Plan) for the North Coast Region |
Objective/Criterion Reference: |
Code of Federal Regulations 40 part 131.38 Establishment of numeric criteria for priority toxic pollutants for the State of California. 7/1/2011 Edition |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
Data for this line of evidence for Klamath River HU, Shasta River HA was collected at 1 monitoring site [ Shasta River at Hwy 263 - 105SH1452] |
Temporal Representation: |
Data was collected over the time period 4/24/2001-11/16/2006. |
Environmental Conditions: |
There are no known environmental conditions (e.g., seasonality, land use practices, fire events, storms, etc.) that are related to these data. |
QAPP Information: |
Quality control was conducted in accordance with the SWAMP Quality Assurance Management Plan (SWAMP 2002). |
QAPP Information Reference(s): |
Quality Assurance Management Plan for the State of California's Surface Water Ambient Monitoring Program. Sacramento, CA. State Water Resources Control Board. SWAMP. December 2002 (1st version)
|
|
Line of Evidence (LOE) for Decision ID 105199, Dieldrin
|
Region 1 |
Klamath River HU, Shasta River HA |
|
|
LOE ID: |
123537 |
|
Pollutant: |
Dieldrin |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
None |
|
Beneficial Use: |
Municipal & Domestic Supply |
|
Number of Samples: |
0 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
State Water Board staff re-assessed SWAMP data for Klamath River HU, Shasta River HA to determine beneficial use support and results are as follows: 0 of 0 samples exceed the criterion for Dieldrin, Total. Four sample results were not used in the assessment because the laboratory data reporting limit(s) was above the objective and therefore the results could not be quantified with the level of certainty required by the Listing Policy. This LOE re-assesses data from LOE 29849 from the 2010 Integrated Report. Data were re-assessed in order to evaluate these data in their own LOE, instead of being evaluated in the same LOE as other pesticide data. |
Data Reference: |
Surface Water Ambient Monitoring Program (SWAMP). Summary Report for the North Coast Region (RWQCB-1) for years 2000-2006. North Coast Regional Water Quality Control Board. March 2008 |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
Water Quality Control Plan, North Coast Region (NCRWQCB 2011): All waters shall be maintained free of toxic substances in concentrations that are toxic to, or that produce detrimental physiological responses in human, plant, animal, or aquatic life. The established numeric criteria for dieldrin to protect human health from the consumption of water and organisms is 0.00014 ug/L (California Toxics Rule, 2000). |
Objective/Criterion Reference: |
Water Quality Control Plan (Basin Plan) for the North Coast Region |
Objective/Criterion Reference: |
Code of Federal Regulations 40 part 131.38 Establishment of numeric criteria for priority toxic pollutants for the State of California. 7/1/2011 Edition |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
Data for this line of evidence for Klamath River HU, Shasta River HA was collected at 1 monitoring site [ Yreka Creek at Highway 3 - 105YREHW3] |
Temporal Representation: |
Data was collected over the time period 10/21/2004-6/20/2005. |
Environmental Conditions: |
There are no known environmental conditions (e.g., seasonality, land use practices, fire events, storms, etc.) that are related to these data. |
QAPP Information: |
Quality control was conducted in accordance with the SWAMP Quality Assurance Management Plan (SWAMP 2002). |
QAPP Information Reference(s): |
Quality Assurance Management Plan for the State of California's Surface Water Ambient Monitoring Program. Sacramento, CA. State Water Resources Control Board. SWAMP. December 2002 (1st version)
|
|
Line of Evidence (LOE) for Decision ID 105199, Dieldrin
|
Region 1 |
Klamath River HU, Shasta River HA |
|
|
LOE ID: |
123536 |
|
Pollutant: |
Dieldrin |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
None |
|
Beneficial Use: |
Municipal & Domestic Supply |
|
Number of Samples: |
0 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
State Water Board staff re-assessed SWAMP data for Klamath River HU, Shasta River HA to determine beneficial use support and results are as follows: 0 of 0 samples exceed the criterion for Dieldrin, Total. Eight sample results were not used in the assessment because the laboratory data reporting limit(s) was above the objective and therefore the results could not be quantified with the level of certainty required by the Listing Policy. This LOE re-assesses data from LOE 29849 from the 2010 Integrated Report. Data were re-assessed in order to evaluate these data in their own LOE, instead of being evaluated in the same LOE as other pesticide data. |
Data Reference: |
Surface Water Ambient Monitoring Program (SWAMP). Summary Report for the North Coast Region (RWQCB-1) for years 2000-2006. North Coast Regional Water Quality Control Board. March 2008 |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
Water Quality Control Plan, North Coast Region (NCRWQCB 2011): All waters shall be maintained free of toxic substances in concentrations that are toxic to, or that produce detrimental physiological responses in human, plant, animal, or aquatic life. The established numeric criteria for dieldrin to protect human health from the consumption of water and organisms is 0.00014 ug/L (California Toxics Rule, 2000). |
Objective/Criterion Reference: |
Water Quality Control Plan (Basin Plan) for the North Coast Region |
Objective/Criterion Reference: |
Code of Federal Regulations 40 part 131.38 Establishment of numeric criteria for priority toxic pollutants for the State of California. 7/1/2011 Edition |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
Data for this line of evidence for Klamath River HU, Shasta River HA was collected at 1 monitoring site [ Yreka Creek at Anderson Rd - 105YREAND] |
Temporal Representation: |
Data was collected over the time period 10/9/2002-6/20/2005. |
Environmental Conditions: |
There are no known environmental conditions (e.g., seasonality, land use practices, fire events, storms, etc.) that are related to these data. |
QAPP Information: |
Quality control was conducted in accordance with the SWAMP Quality Assurance Management Plan (SWAMP 2002). |
QAPP Information Reference(s): |
Quality Assurance Management Plan for the State of California's Surface Water Ambient Monitoring Program. Sacramento, CA. State Water Resources Control Board. SWAMP. December 2002 (1st version)
|
|
Line of Evidence (LOE) for Decision ID 105199, Dieldrin
|
Region 1 |
Klamath River HU, Shasta River HA |
|
|
LOE ID: |
41780 |
|
Pollutant: |
Dieldrin |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Total |
|
Beneficial Use: |
Municipal & Domestic Supply |
|
Number of Samples: |
0 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Three non-detect sample results were not used in the assessment because the laboratory data reporting limit was above the objective and therefore the results could not be quantified with the level of certainty required by the Listing Policy. |
Data Reference: |
RWB1 Trend Maintenance Periods FYs 2007 2008 |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
Water Quality Control Plan, North Coast Region (NCRWQCB 2011): All waters shall be maintained free of toxic substances in concentrations that are toxic to, or that produce detrimental physiological responses in human, plant, animal, or aquatic life. The established numeric criteria for dieldrin to protect human health from the consumption of water and organisms is 0.00014 ug/L (California Toxics Rule, 2000). |
Objective/Criterion Reference: |
Code of Federal Regulations 40 part 131.38 Establishment of numeric criteria for priority toxic pollutants for the State of California. 7/1/2011 Edition |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
Data for this line of evidence for Klamath River HU, Shasta River HA was collected at 1 monitoring site [ Shasta River near Edgewood - 105SHAEDG] |
Temporal Representation: |
Data was collected over the time period 11/15/2007-7/16/2008. |
Environmental Conditions: |
Staff is not aware of any special conditions that might affect interpretation of the data. |
QAPP Information: |
The SWAMP QAPP (2008) was followed. |
QAPP Information Reference(s): |
Surface Water Ambient Monitoring Program Quality Assurance Program Plan |
|
Line of Evidence (LOE) for Decision ID 105199, Dieldrin
|
Region 1 |
Klamath River HU, Shasta River HA |
|
|
LOE ID: |
41660 |
|
Pollutant: |
Dieldrin |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Total |
|
Beneficial Use: |
Warm Freshwater Habitat |
|
Number of Samples: |
3 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP data for Klamath River HU, Shasta River HA to determine beneficial use support and results are as follows: 0 of 3 samples exceed the criterion for Dieldrin. |
Data Reference: |
RWB1 Trend Maintenance Periods FYs 2007 2008 |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
Water Quality Control Plan, North Coast Region (NCRWQCB 2011): All waters shall be maintained free of toxic substances in concentrations that are toxic to, or that produce detrimental physiological responses in human, plant, animal, or aquatic life. The established numeric criteria for dieldrin to protect aquatic life in freshwater as criterion continuous concentration (expressed as a 4-day average) is 0.056 ug/L (California Toxics Rule, 2000). |
Objective/Criterion Reference: |
Code of Federal Regulations 40 part 131.38 Establishment of numeric criteria for priority toxic pollutants for the State of California. 7/1/2011 Edition |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
Data for this line of evidence for Klamath River HU, Shasta River HA was collected at 1 monitoring site [ Shasta River at Hwy 263 - 105SHA263] |
Temporal Representation: |
Data was collected over the time period 11/15/2007-7/16/2008. |
Environmental Conditions: |
Staff is not aware of any special conditions that might affect interpretation of the data. |
QAPP Information: |
The SWAMP QAPP (2008) was followed. |
QAPP Information Reference(s): |
Surface Water Ambient Monitoring Program Quality Assurance Program Plan |
|
Line of Evidence (LOE) for Decision ID 105199, Dieldrin
|
Region 1 |
Klamath River HU, Shasta River HA |
|
|
LOE ID: |
41659 |
|
Pollutant: |
Dieldrin |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Total |
|
Beneficial Use: |
Warm Freshwater Habitat |
|
Number of Samples: |
3 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP data for Klamath River HU, Shasta River HA to determine beneficial use support and results are as follows: 0 of 3 samples exceed the criterion for Dieldrin. |
Data Reference: |
RWB1 Trend Maintenance Periods FYs 2007 2008 |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
Water Quality Control Plan, North Coast Region (NCRWQCB 2011): All waters shall be maintained free of toxic substances in concentrations that are toxic to, or that produce detrimental physiological responses in human, plant, animal, or aquatic life. The established numeric criteria for dieldrin to protect aquatic life in freshwater as criterion continuous concentration (expressed as a 4-day average) is 0.056 ug/L (California Toxics Rule, 2000). |
Objective/Criterion Reference: |
Code of Federal Regulations 40 part 131.38 Establishment of numeric criteria for priority toxic pollutants for the State of California. 7/1/2011 Edition |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
Data for this line of evidence for Klamath River HU, Shasta River HA was collected at 1 monitoring site [ Shasta River near Edgewood - 105SHAEDG] |
Temporal Representation: |
Data was collected over the time period 11/15/2007-7/16/2008. |
Environmental Conditions: |
Staff is not aware of any special conditions that might affect interpretation of the data. |
QAPP Information: |
The SWAMP QAPP (2008) was followed. |
QAPP Information Reference(s): |
Surface Water Ambient Monitoring Program Quality Assurance Program Plan |
|
Line of Evidence (LOE) for Decision ID 105199, Dieldrin
|
Region 1 |
Klamath River HU, Shasta River HA |
|
|
LOE ID: |
117940 |
|
Pollutant: |
Dieldrin |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Total |
|
Beneficial Use: |
Municipal & Domestic Supply |
|
Number of Samples: |
0 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP RWB1 Monitoring data for Klamath River HU, Shasta River HA to determine beneficial use support, and the results are as follows: 0 of the 0 samples exceeded the evaluation guideline for Dieldrin. Although a total of 1 samples were collected, 1 of these samples were not included in the assessment because the laboratory data reporting limit(s) was above the objective and therefore the results could not be quantified with the level of certainty required by the Listing Policy Section 6.1.5.5. |
Data Reference: |
Water Quality Assessment Data for the 2018 solicitation cycle submitted through CEDEN for SWAMP RWB1 Monitoring .
|
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
Water Quality Control Plan, North Coast Region (NCRWQCB 2018): All waters shall be maintained free of toxic substances in concentrations that are toxic to, or that produce detrimental physiological responses in human, plant, animal, or aquatic life. The established numeric criteria for dieldrin to protect human health from the consumption of water and organisms is 0.00014 ug/L (California Toxics Rule, 2000). |
Objective/Criterion Reference: |
Water Quality Standards 2000. Establishment of numeric criteria for priority toxic pollutants for the State of California: Rules and regulations. Federal Register Vol. 65, No. 97. Washington, D.C.: Environmental Protection Agency |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
Data was collected from 1 station(s) (Station Code(s) 105SH9274). |
Temporal Representation: |
Date for this waterbody was collected over the date range 2013-04-29 to 2013-04-29 |
Environmental Conditions: |
|
QAPP Information: |
Quality Assurance Program Plan and Standard Operating Procedures for SWAMP program |
QAPP Information Reference(s): |
Quality Assurance Program Plans, Quality Assurance Project Plans, and Standard Operating Procedures for the SWAMP program |
|
Line of Evidence (LOE) for Decision ID 105199, Dieldrin
|
Region 1 |
Klamath River HU, Shasta River HA |
|
|
LOE ID: |
117939 |
|
Pollutant: |
Dieldrin |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Total |
|
Beneficial Use: |
Commercial or recreational collection of fish, shellfish, or organisms |
|
Number of Samples: |
0 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP RWB1 Monitoring data for Klamath River HU, Shasta River HA to determine beneficial use support, and the results are as follows: 0 of the 0 samples exceeded the evaluation guideline for Dieldrin. Although a total of 1 samples were collected, 1 of these samples were not included in the assessment because the laboratory data reporting limit(s) was above the objective and therefore the results could not be quantified with the level of certainty required by the Listing Policy Section 6.1.5.5. |
Data Reference: |
Water Quality Assessment Data for the 2018 solicitation cycle submitted through CEDEN for SWAMP RWB1 Monitoring .
|
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
Water Quality Control Plan, North Coast Region (NCRWQCB 2018): All waters shall be maintained free of toxic substances in concentrations that are toxic to, or that produce detrimental physiological responses in human, plant, animal, or aquatic life. The established numeric criteria for dieldrin to protection of human health from consumption of organisms only is 0.00014 ug/L (California Toxics Rule, 2000). |
Objective/Criterion Reference: |
Water Quality Standards 2000. Establishment of numeric criteria for priority toxic pollutants for the State of California: Rules and regulations. Federal Register Vol. 65, No. 97. Washington, D.C.: Environmental Protection Agency |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
Data was collected from 1 station(s) (Station Code(s) 105SH9274). |
Temporal Representation: |
Date for this waterbody was collected over the date range 2013-04-29 to 2013-04-29 |
Environmental Conditions: |
|
QAPP Information: |
Quality Assurance Program Plan and Standard Operating Procedures for SWAMP program |
QAPP Information Reference(s): |
Quality Assurance Program Plans, Quality Assurance Project Plans, and Standard Operating Procedures for the SWAMP program |
|
Line of Evidence (LOE) for Decision ID 168801, Dimethoate
|
Region 1 |
Klamath River HU, Shasta River HA |
|
|
LOE ID: |
123541 |
|
Pollutant: |
Dimethoate |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
None |
|
Beneficial Use: |
Municipal & Domestic Supply |
|
Number of Samples: |
0 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
State Water Board staff re-assessed SWAMP data for Klamath River HU, Shasta River HA to determine beneficial use support and results are as follows: 0 of 0 samples exceed the criterion for Dimethoate, Total. Eight samples were removed from assessment because an appropriate evaluation guideline for the water body-pollutant combination could not be obtained for this listing cycle. This LOE re-assesses data from LOE 29849 from the 2010 Integrated Report. Data were re-assessed in order to evaluate these data in their own LOE, instead of being evaluated in the same LOE as other pesticide data. |
Data Reference: |
Surface Water Ambient Monitoring Program (SWAMP). Summary Report for the North Coast Region (RWQCB-1) for years 2000-2006. North Coast Regional Water Quality Control Board. March 2008 |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
Per the Basin Plan (NCRWQCB 2011): No individual pesticide or combination of pesticides shall be present in concentrations that adversely affect beneficial uses. There shall be no bioaccumulation of pesticide concentrations found in bottom sediments or aquatic life. Waters designated for use as domestic or municipal supply shall not contain concentrations of pesticides in excess of the limiting concentrations set forth in California Code of Regulations, Title 22, Division 4, Chapter 15, Article 4, Section 64444, and listed in Table 3.2 of the Basin Plan. No evaluation guideline could be found to evaluate protection of the MUN beneficial use that meets the requirements of Section 6.1.3 of the Listing Policy. |
Objective/Criterion Reference: |
Water Quality Control Plan (Basin Plan) for the North Coast Region |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
Data for this line of evidence for Klamath River HU, Shasta River HA was collected at 1 monitoring site [ Yreka Creek at Anderson Rd - 105YREAND] |
Temporal Representation: |
Data was collected over the time period 10/9/2002-6/20/2005. |
Environmental Conditions: |
There are no known environmental conditions (e.g., seasonality, land use practices, fire events, storms, etc.) that are related to these data. |
QAPP Information: |
Quality control was conducted in accordance with the SWAMP Quality Assurance Management Plan (SWAMP 2002). |
QAPP Information Reference(s): |
Quality Assurance Management Plan for the State of California's Surface Water Ambient Monitoring Program. Sacramento, CA. State Water Resources Control Board. SWAMP. December 2002 (1st version)
|
|
Line of Evidence (LOE) for Decision ID 168801, Dimethoate
|
Region 1 |
Klamath River HU, Shasta River HA |
|
|
LOE ID: |
103214 |
|
Pollutant: |
Dimethoate |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Total |
|
Beneficial Use: |
Warm Freshwater Habitat |
|
Number of Samples: |
3 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP RWB1 Monitoring data for Klamath River HU, Shasta River HA to determine beneficial use support and results are as follows: 0 of 3 samples exceeded the water quality standard for Dimethoate. |
Data Reference: |
Water Quality Assessment Data for the 2018 solicitation cycle submitted through CEDEN for SWAMP RWB1 Monitoring .
|
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
All waters shall be maintained free of toxic substances in concentrations which are toxic to, or which produce detrimental physiological responses in, human, plant, animal, or aquatic life. (Basin Plan). |
Objective/Criterion Reference: |
Water Quality Control Plan (Basin Plan) for the North Coast Region |
|
Evaluation Guideline: |
The evaluation guideline for Dimethoate is the USEPA Aquatic Life Benchmark of 0.5 ug/L for an invertebrate (chronic). |
Guideline Reference: |
OPP Aquatic Life Benchmarks |
|
Spatial Representation: |
The samples were collected at 1 monitoring site(s) (105SH9274) |
Temporal Representation: |
The samples were collected between the dates of 2013-03-07 and 2013-11-20 |
Environmental Conditions: |
|
QAPP Information: |
Quality Assurance Program Plan and Standard Operating Procedures for SWAMP program |
QAPP Information Reference(s): |
Quality Assurance Program Plans, Quality Assurance Project Plans, and Standard Operating Procedures for the SWAMP program |
|
Line of Evidence (LOE) for Decision ID 168801, Dimethoate
|
Region 1 |
Klamath River HU, Shasta River HA |
|
|
LOE ID: |
103213 |
|
Pollutant: |
Dimethoate |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Total |
|
Beneficial Use: |
Cold Freshwater Habitat |
|
Number of Samples: |
3 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP RWB1 Monitoring data for Klamath River HU, Shasta River HA to determine beneficial use support and results are as follows: 0 of 3 samples exceeded the water quality standard for Dimethoate. |
Data Reference: |
Water Quality Assessment Data for the 2018 solicitation cycle submitted through CEDEN for SWAMP RWB1 Monitoring .
|
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
All waters shall be maintained free of toxic substances in concentrations which are toxic to, or which produce detrimental physiological responses in, human, plant, animal, or aquatic life. (Basin Plan). |
Objective/Criterion Reference: |
Water Quality Control Plan (Basin Plan) for the North Coast Region |
|
Evaluation Guideline: |
The evaluation guideline for Dimethoate is the USEPA Aquatic Life Benchmark of 0.5 ug/L for an invertebrate (chronic). |
Guideline Reference: |
OPP Aquatic Life Benchmarks |
|
Spatial Representation: |
The samples were collected at 1 monitoring site(s) (105SH9274) |
Temporal Representation: |
The samples were collected between the dates of 2013-03-07 and 2013-11-20 |
Environmental Conditions: |
|
QAPP Information: |
Quality Assurance Program Plan and Standard Operating Procedures for SWAMP program |
QAPP Information Reference(s): |
Quality Assurance Program Plans, Quality Assurance Project Plans, and Standard Operating Procedures for the SWAMP program |
|
Line of Evidence (LOE) for Decision ID 168801, Dimethoate
|
Region 1 |
Klamath River HU, Shasta River HA |
|
|
LOE ID: |
123540 |
|
Pollutant: |
Dimethoate |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
None |
|
Beneficial Use: |
Municipal & Domestic Supply |
|
Number of Samples: |
0 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
State Water Board staff re-assessed SWAMP data for Klamath River HU, Shasta River HA to determine beneficial use support and results are as follows: 0 of 0 samples exceed the criterion for Dimethoate, Total. Four samples were removed from assessment because an appropriate evaluation guideline for the water body-pollutant combination could not be obtained for this listing cycle. This LOE re-assesses data from LOE 29849 from the 2010 Integrated Report. Data were re-assessed in order to evaluate these data in their own LOE, instead of being evaluated in the same LOE as other pesticide data. |
Data Reference: |
Surface Water Ambient Monitoring Program (SWAMP). Summary Report for the North Coast Region (RWQCB-1) for years 2000-2006. North Coast Regional Water Quality Control Board. March 2008 |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
Per the Basin Plan (NCRWQCB 2011): No individual pesticide or combination of pesticides shall be present in concentrations that adversely affect beneficial uses. There shall be no bioaccumulation of pesticide concentrations found in bottom sediments or aquatic life. Waters designated for use as domestic or municipal supply shall not contain concentrations of pesticides in excess of the limiting concentrations set forth in California Code of Regulations, Title 22, Division 4, Chapter 15, Article 4, Section 64444, and listed in Table 3.2 of the Basin Plan. No evaluation guideline could be found to evaluate protection of the MUN beneficial use that meets the requirements of Section 6.1.3 of the Listing Policy. |
Objective/Criterion Reference: |
Water Quality Control Plan (Basin Plan) for the North Coast Region |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
Data for this line of evidence for Klamath River HU, Shasta River HA was collected at 1 monitoring site [ Shasta River near Edgewood - 105SH9274] |
Temporal Representation: |
Data was collected over the time period 10/7/2002-6/19/2003. |
Environmental Conditions: |
There are no known environmental conditions (e.g., seasonality, land use practices, fire events, storms, etc.) that are related to these data. |
QAPP Information: |
Quality control was conducted in accordance with the SWAMP Quality Assurance Management Plan (SWAMP 2002). |
QAPP Information Reference(s): |
Quality Assurance Management Plan for the State of California's Surface Water Ambient Monitoring Program. Sacramento, CA. State Water Resources Control Board. SWAMP. December 2002 (1st version)
|
|
Line of Evidence (LOE) for Decision ID 168801, Dimethoate
|
Region 1 |
Klamath River HU, Shasta River HA |
|
|
LOE ID: |
123538 |
|
Pollutant: |
Dimethoate |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
None |
|
Beneficial Use: |
Municipal & Domestic Supply |
|
Number of Samples: |
0 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
State Water Board staff re-assessed SWAMP data for Klamath River HU, Shasta River HA to determine beneficial use support and results are as follows: 0 of 0 samples exceed the criterion for Dimethoate, Total. Sixteen samples were removed from assessment because an appropriate evaluation guideline for the water body-pollutant combination could not be obtained for this listing cycle. This LOE re-assesses data from LOE 29849 from the 2010 Integrated Report. Data were re-assessed in order to evaluate these data in their own LOE, instead of being evaluated in the same LOE as other pesticide data. |
Data Reference: |
Surface Water Ambient Monitoring Program (SWAMP). Summary Report for the North Coast Region (RWQCB-1) for years 2000-2006. North Coast Regional Water Quality Control Board. March 2008 |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
Per the Basin Plan (NCRWQCB 2011): No individual pesticide or combination of pesticides shall be present in concentrations that adversely affect beneficial uses. There shall be no bioaccumulation of pesticide concentrations found in bottom sediments or aquatic life. Waters designated for use as domestic or municipal supply shall not contain concentrations of pesticides in excess of the limiting concentrations set forth in California Code of Regulations, Title 22, Division 4, Chapter 15, Article 4, Section 64444, and listed in Table 3.2 of the Basin Plan. No evaluation guideline could be found to evaluate protection of the MUN beneficial use that meets the requirements of Section 6.1.3 of the Listing Policy. |
Objective/Criterion Reference: |
Water Quality Control Plan (Basin Plan) for the North Coast Region |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
Data for this line of evidence for Klamath River HU, Shasta River HA was collected at 1 monitoring site [ Shasta River at Hwy 263 - 105SH1452] |
Temporal Representation: |
Data was collected over the time period 2/27/2002-11/16/2006. |
Environmental Conditions: |
There are no known environmental conditions (e.g., seasonality, land use practices, fire events, storms, etc.) that are related to these data. |
QAPP Information: |
Quality control was conducted in accordance with the SWAMP Quality Assurance Management Plan (SWAMP 2002). |
QAPP Information Reference(s): |
Quality Assurance Management Plan for the State of California's Surface Water Ambient Monitoring Program. Sacramento, CA. State Water Resources Control Board. SWAMP. December 2002 (1st version)
|
|
Line of Evidence (LOE) for Decision ID 168801, Dimethoate
|
Region 1 |
Klamath River HU, Shasta River HA |
|
|
LOE ID: |
123539 |
|
Pollutant: |
Dimethoate |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
None |
|
Beneficial Use: |
Municipal & Domestic Supply |
|
Number of Samples: |
0 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
State Water Board staff re-assessed SWAMP data for Klamath River HU, Shasta River HA to determine beneficial use support and results are as follows: 0 of 0 samples exceed the criterion for Dimethoate, Total. Four samples were removed from assessment because an appropriate evaluation guideline for the water body-pollutant combination could not be obtained for this listing cycle. This LOE re-assesses data from LOE 29849 from the 2010 Integrated Report. Data were re-assessed in order to evaluate these data in their own LOE, instead of being evaluated in the same LOE as other pesticide data. |
Data Reference: |
Surface Water Ambient Monitoring Program (SWAMP). Summary Report for the North Coast Region (RWQCB-1) for years 2000-2006. North Coast Regional Water Quality Control Board. March 2008 |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
Per the Basin Plan (NCRWQCB 2011): No individual pesticide or combination of pesticides shall be present in concentrations that adversely affect beneficial uses. There shall be no bioaccumulation of pesticide concentrations found in bottom sediments or aquatic life. Waters designated for use as domestic or municipal supply shall not contain concentrations of pesticides in excess of the limiting concentrations set forth in California Code of Regulations, Title 22, Division 4, Chapter 15, Article 4, Section 64444, and listed in Table 3.2 of the Basin Plan. No evaluation guideline could be found to evaluate protection of the MUN beneficial use that meets the requirements of Section 6.1.3 of the Listing Policy. |
Objective/Criterion Reference: |
Water Quality Control Plan (Basin Plan) for the North Coast Region |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
Data for this line of evidence for Klamath River HU, Shasta River HA was collected at 1 monitoring site [ Shasta River at Montague - 105SHAMON] |
Temporal Representation: |
Data was collected over the time period 10/7/2002-6/19/2003. |
Environmental Conditions: |
There are no known environmental conditions (e.g., seasonality, land use practices, fire events, storms, etc.) that are related to these data. |
QAPP Information: |
Quality control was conducted in accordance with the SWAMP Quality Assurance Management Plan (SWAMP 2002). |
QAPP Information Reference(s): |
Quality Assurance Management Plan for the State of California's Surface Water Ambient Monitoring Program. Sacramento, CA. State Water Resources Control Board. SWAMP. December 2002 (1st version)
|
|
Line of Evidence (LOE) for Decision ID 168801, Dimethoate
|
Region 1 |
Klamath River HU, Shasta River HA |
|
|
LOE ID: |
123542 |
|
Pollutant: |
Dimethoate |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
None |
|
Beneficial Use: |
Municipal & Domestic Supply |
|
Number of Samples: |
0 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
State Water Board staff re-assessed SWAMP data for Klamath River HU, Shasta River HA to determine beneficial use support and results are as follows: 0 of 0 samples exceed the criterion for Dimethoate, Total. Four samples were removed from assessment because an appropriate evaluation guideline for the water body-pollutant combination could not be obtained for this listing cycle. This LOE re-assesses data from LOE 29849 from the 2010 Integrated Report. Data were re-assessed in order to evaluate these data in their own LOE, instead of being evaluated in the same LOE as other pesticide data. |
Data Reference: |
Surface Water Ambient Monitoring Program (SWAMP). Summary Report for the North Coast Region (RWQCB-1) for years 2000-2006. North Coast Regional Water Quality Control Board. March 2008 |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
Per the Basin Plan (NCRWQCB 2011): No individual pesticide or combination of pesticides shall be present in concentrations that adversely affect beneficial uses. There shall be no bioaccumulation of pesticide concentrations found in bottom sediments or aquatic life. Waters designated for use as domestic or municipal supply shall not contain concentrations of pesticides in excess of the limiting concentrations set forth in California Code of Regulations, Title 22, Division 4, Chapter 15, Article 4, Section 64444, and listed in Table 3.2 of the Basin Plan. No evaluation guideline could be found to evaluate protection of the MUN beneficial use that meets the requirements of Section 6.1.3 of the Listing Policy. |
Objective/Criterion Reference: |
Water Quality Control Plan (Basin Plan) for the North Coast Region |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
Data for this line of evidence for Klamath River HU, Shasta River HA was collected at 1 monitoring site [ Yreka Creek at Highway 3 - 105YREHW3] |
Temporal Representation: |
Data was collected over the time period 10/21/2004-6/20/2005. |
Environmental Conditions: |
There are no known environmental conditions (e.g., seasonality, land use practices, fire events, storms, etc.) that are related to these data. |
QAPP Information: |
Quality control was conducted in accordance with the SWAMP Quality Assurance Management Plan (SWAMP 2002). |
QAPP Information Reference(s): |
Quality Assurance Management Plan for the State of California's Surface Water Ambient Monitoring Program. Sacramento, CA. State Water Resources Control Board. SWAMP. December 2002 (1st version)
|
|
Line of Evidence (LOE) for Decision ID 168801, Dimethoate
|
Region 1 |
Klamath River HU, Shasta River HA |
|
|
LOE ID: |
349456 |
|
Pollutant: |
Dimethoate |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Total |
|
Beneficial Use: |
Warm Freshwater Habitat |
|
Number of Samples: |
3 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed RWB1 Trend Maintenance Periods FYs 2007 2008 data for Klamath River HU, Shasta River HA to determine beneficial use support and results are as follows: 0 of 3 samples exceeded the water quality threshold for Dimethoate. |
Data Reference: |
RWB1 Trend Maintenance Periods FYs 2007 2008 |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
All waters shall be maintained free of toxic substances in concentrations which are toxic to, or which produce detrimental physiological responses in, human, plant, animal, or aquatic life. (Basin Plan). |
Objective/Criterion Reference: |
Water Quality Control Plan (Basin Plan) for the North Coast Region |
|
Evaluation Guideline: |
The evaluation guideline for dimethoate is the USEPA Aquatic Life Benchmark of 0.5 ug/L for an invertebrate (chronic). |
Guideline Reference: |
OPP Aquatic Life Benchmarks |
|
Spatial Representation: |
The samples were collected at 1 monitoring site: 105SHA263 (Shasta River at Hwy 263). |
Temporal Representation: |
The samples were collected between the dates of 2007-11-15 and 2008-07-16 |
Environmental Conditions: |
|
QAPP Information: |
Generic SWAMP QAPrP |
QAPP Information Reference(s): |
Generic SWAMP QAPrP |
|
Line of Evidence (LOE) for Decision ID 168801, Dimethoate
|
Region 1 |
Klamath River HU, Shasta River HA |
|
|
LOE ID: |
349439 |
|
Pollutant: |
Dimethoate |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Total |
|
Beneficial Use: |
Warm Freshwater Habitat |
|
Number of Samples: |
3 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed RWB1 Trend Maintenance Periods FYs 2007 2008 data for Klamath River HU, Shasta River HA to determine beneficial use support and results are as follows: 0 of 3 samples exceeded the water quality threshold for Dimethoate. |
Data Reference: |
RWB1 Trend Maintenance Periods FYs 2007 2008 |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
All waters shall be maintained free of toxic substances in concentrations which are toxic to, or which produce detrimental physiological responses in, human, plant, animal, or aquatic life. (Basin Plan). |
Objective/Criterion Reference: |
Water Quality Control Plan (Basin Plan) for the North Coast Region |
|
Evaluation Guideline: |
The evaluation guideline for dimethoate is the USEPA Aquatic Life Benchmark of 0.5 ug/L for an invertebrate (chronic). |
Guideline Reference: |
OPP Aquatic Life Benchmarks |
|
Spatial Representation: |
The samples were collected at 1 monitoring site: 105SHAEDG (Shasta River near Edgewood). |
Temporal Representation: |
The samples were collected between the dates of 2007-11-15 and 2008-07-16 |
Environmental Conditions: |
|
QAPP Information: |
Generic SWAMP QAPrP |
QAPP Information Reference(s): |
Generic SWAMP QAPrP |
|
Line of Evidence (LOE) for Decision ID 168801, Dimethoate
|
Region 1 |
Klamath River HU, Shasta River HA |
|
|
LOE ID: |
349467 |
|
Pollutant: |
Dimethoate |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Total |
|
Beneficial Use: |
Cold Freshwater Habitat |
|
Number of Samples: |
3 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed RWB1 Trend Maintenance Periods FYs 2007 2008 data for Klamath River HU, Shasta River HA to determine beneficial use support and results are as follows: 0 of 3 samples exceeded the water quality threshold for Dimethoate. |
Data Reference: |
RWB1 Trend Maintenance Periods FYs 2007 2008 |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
All waters shall be maintained free of toxic substances in concentrations which are toxic to, or which produce detrimental physiological responses in, human, plant, animal, or aquatic life. (Basin Plan). |
Objective/Criterion Reference: |
Water Quality Control Plan (Basin Plan) for the North Coast Region |
|
Evaluation Guideline: |
The evaluation guideline for dimethoate is the USEPA Aquatic Life Benchmark of 0.5 ug/L for an invertebrate (chronic). |
Guideline Reference: |
OPP Aquatic Life Benchmarks |
|
Spatial Representation: |
The samples were collected at 1 monitoring site: 105SHA263 (Shasta River at Hwy 263). |
Temporal Representation: |
The samples were collected between the dates of 2007-11-15 and 2008-07-16 |
Environmental Conditions: |
|
QAPP Information: |
Generic SWAMP QAPrP |
QAPP Information Reference(s): |
Generic SWAMP QAPrP |
|
Line of Evidence (LOE) for Decision ID 168801, Dimethoate
|
Region 1 |
Klamath River HU, Shasta River HA |
|
|
LOE ID: |
349451 |
|
Pollutant: |
Dimethoate |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Total |
|
Beneficial Use: |
Cold Freshwater Habitat |
|
Number of Samples: |
3 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed RWB1 Trend Maintenance Periods FYs 2007 2008 data for Klamath River HU, Shasta River HA to determine beneficial use support and results are as follows: 0 of 3 samples exceeded the water quality threshold for Dimethoate. |
Data Reference: |
RWB1 Trend Maintenance Periods FYs 2007 2008 |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
All waters shall be maintained free of toxic substances in concentrations which are toxic to, or which produce detrimental physiological responses in, human, plant, animal, or aquatic life. (Basin Plan). |
Objective/Criterion Reference: |
Water Quality Control Plan (Basin Plan) for the North Coast Region |
|
Evaluation Guideline: |
The evaluation guideline for dimethoate is the USEPA Aquatic Life Benchmark of 0.5 ug/L for an invertebrate (chronic). |
Guideline Reference: |
OPP Aquatic Life Benchmarks |
|
Spatial Representation: |
The samples were collected at 1 monitoring site: 105SHAEDG (Shasta River near Edgewood). |
Temporal Representation: |
The samples were collected between the dates of 2007-11-15 and 2008-07-16 |
Environmental Conditions: |
|
QAPP Information: |
Generic SWAMP QAPrP |
QAPP Information Reference(s): |
Generic SWAMP QAPrP |
|
Line of Evidence (LOE) for Decision ID 168801, Dimethoate
|
Region 1 |
Klamath River HU, Shasta River HA |
|
|
LOE ID: |
103212 |
|
Pollutant: |
Dimethoate |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Total |
|
Beneficial Use: |
Warm Freshwater Habitat |
|
Number of Samples: |
3 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP RWB1 Monitoring data for Klamath River HU, Shasta River HA to determine beneficial use support and results are as follows: 0 of 3 samples exceeded the water quality standard for Dimethoate. |
Data Reference: |
Water Quality Assessment Data for the 2018 solicitation cycle submitted through CEDEN for SWAMP RWB1 Monitoring .
|
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
All waters shall be maintained free of toxic substances in concentrations which are toxic to, or which produce detrimental physiological responses in, human, plant, animal, or aquatic life. (Basin Plan). |
Objective/Criterion Reference: |
Water Quality Control Plan (Basin Plan) for the North Coast Region |
|
Evaluation Guideline: |
The evaluation guideline for Dimethoate is the USEPA Aquatic Life Benchmark of 0.5 ug/L for an invertebrate (chronic). |
Guideline Reference: |
OPP Aquatic Life Benchmarks |
|
Spatial Representation: |
The samples were collected at 1 monitoring site(s) (105SH1452) |
Temporal Representation: |
The samples were collected between the dates of 2013-03-06 and 2013-11-20 |
Environmental Conditions: |
|
QAPP Information: |
Quality Assurance Program Plan and Standard Operating Procedures for SWAMP program |
QAPP Information Reference(s): |
Quality Assurance Program Plans, Quality Assurance Project Plans, and Standard Operating Procedures for the SWAMP program |
|
Line of Evidence (LOE) for Decision ID 168801, Dimethoate
|
Region 1 |
Klamath River HU, Shasta River HA |
|
|
LOE ID: |
103211 |
|
Pollutant: |
Dimethoate |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Total |
|
Beneficial Use: |
Cold Freshwater Habitat |
|
Number of Samples: |
3 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP RWB1 Monitoring data for Klamath River HU, Shasta River HA to determine beneficial use support and results are as follows: 0 of 3 samples exceeded the water quality standard for Dimethoate. |
Data Reference: |
Water Quality Assessment Data for the 2018 solicitation cycle submitted through CEDEN for SWAMP RWB1 Monitoring .
|
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
All waters shall be maintained free of toxic substances in concentrations which are toxic to, or which produce detrimental physiological responses in, human, plant, animal, or aquatic life. (Basin Plan). |
Objective/Criterion Reference: |
Water Quality Control Plan (Basin Plan) for the North Coast Region |
|
Evaluation Guideline: |
The evaluation guideline for Dimethoate is the USEPA Aquatic Life Benchmark of 0.5 ug/L for an invertebrate (chronic). |
Guideline Reference: |
OPP Aquatic Life Benchmarks |
|
Spatial Representation: |
The samples were collected at 1 monitoring site(s) (105SH1452) |
Temporal Representation: |
The samples were collected between the dates of 2013-03-06 and 2013-11-20 |
Environmental Conditions: |
|
QAPP Information: |
Quality Assurance Program Plan and Standard Operating Procedures for SWAMP program |
QAPP Information Reference(s): |
Quality Assurance Program Plans, Quality Assurance Project Plans, and Standard Operating Procedures for the SWAMP program |
|
Line of Evidence (LOE) for Decision ID 168806, Endosulfan sulfate
|
Region 1 |
Klamath River HU, Shasta River HA |
|
|
LOE ID: |
42137 |
|
Pollutant: |
Endosulfan sulfate |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Total |
|
Beneficial Use: |
Warm Freshwater Habitat |
|
Number of Samples: |
3 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP data for Klamath River HU, Shasta River HA to determine beneficial use support and results are as follows: 0 of 3 samples exceed the criterion for Endosulfan sulfate. |
Data Reference: |
RWB1 Trend Maintenance Periods FYs 2007 2008 |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
Water Quality Control Plan, North Coast Region (NCRWQCB 2011): All waters shall be maintained free of toxic substances in concentrations that are toxic to, or that produce detrimental physiological responses in human, plant, animal, or aquatic life. |
Objective/Criterion Reference: |
Water Quality Control Plan (Basin Plan) for the North Coast Region |
|
Evaluation Guideline: |
The USEPA national ambient water quality criterion for freshwater aquatic life 24 hour average maximum for endodulfan sulfate is 0.056 µg/L. |
Guideline Reference: |
National Recommended Water Quality Criteria. United States Environmental Protection Agency. Office of Water. Office of Science and Technology |
|
Spatial Representation: |
Data for this line of evidence for Klamath River HU, Shasta River HA was collected at 1 monitoring site [ Shasta River near Edgewood - 105SHAEDG] |
Temporal Representation: |
Data was collected over the time period 11/15/2007-7/16/2008. |
Environmental Conditions: |
Staff is not aware of any special conditions that might affect interpretation of the data. |
QAPP Information: |
The SWAMP QAPP (2008) was followed. |
QAPP Information Reference(s): |
Surface Water Ambient Monitoring Program Quality Assurance Program Plan |
|
Line of Evidence (LOE) for Decision ID 168806, Endosulfan sulfate
|
Region 1 |
Klamath River HU, Shasta River HA |
|
|
LOE ID: |
42074 |
|
Pollutant: |
Endosulfan sulfate |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Total |
|
Beneficial Use: |
Municipal & Domestic Supply |
|
Number of Samples: |
3 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP data for Klamath River HU, Shasta River HA to determine beneficial use support and results are as follows: 0 of 3 samples exceed the criterion for Endosulfan sulfate. |
Data Reference: |
RWB1 Trend Maintenance Periods FYs 2007 2008 |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
Water Quality Control Plan, North Coast Region (NCRWQCB 2011): All waters shall be maintained free of toxic substances in concentrations that are toxic to, or that produce detrimental physiological responses in human, plant, animal, or aquatic life. The established numeric criteria for endosulfan sulfate to protect of human health from the consumption of water and organisms is 110 ug/L (California Toxics Rule, 2000). |
Objective/Criterion Reference: |
Code of Federal Regulations 40 part 131.38 Establishment of numeric criteria for priority toxic pollutants for the State of California. 7/1/2011 Edition |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
Data for this line of evidence for Klamath River HU, Shasta River HA was collected at 1 monitoring site [ Shasta River near Edgewood - 105SHAEDG] |
Temporal Representation: |
Data was collected over the time period 11/15/2007-7/16/2008. |
Environmental Conditions: |
Staff is not aware of any special conditions that might affect interpretation of the data. |
QAPP Information: |
The SWAMP QAPP (2008) was followed. |
QAPP Information Reference(s): |
Surface Water Ambient Monitoring Program Quality Assurance Program Plan |
|
Line of Evidence (LOE) for Decision ID 168806, Endosulfan sulfate
|
Region 1 |
Klamath River HU, Shasta River HA |
|
|
LOE ID: |
109504 |
|
Pollutant: |
Endosulfan sulfate |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Total |
|
Beneficial Use: |
Commercial or recreational collection of fish, shellfish, or organisms |
|
Number of Samples: |
1 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP RWB1 Monitoring data for Klamath River HU, Shasta River HA to determine beneficial use support and results are as follows: 0 of 1 samples exceeded the water quality standard for Endosulfan Sulfate. |
Data Reference: |
Water Quality Assessment Data for the 2018 solicitation cycle submitted through CEDEN for SWAMP RWB1 Monitoring .
|
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
The established numeric criteria for endosulfan sulfate to protection of human health from consumption of organisms only is 240 ug/L (California Toxics Rule, 2000). |
Objective/Criterion Reference: |
Water Quality Standards 2000. Establishment of numeric criteria for priority toxic pollutants for the State of California: Rules and regulations. Federal Register Vol. 65, No. 97. Washington, D.C.: Environmental Protection Agency |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
The samples were collected at 1 monitoring site(s) (105SH1452) |
Temporal Representation: |
The samples were collected between the dates of 2013-04-29 and 2013-04-29 |
Environmental Conditions: |
|
QAPP Information: |
Quality Assurance Program Plan and Standard Operating Procedures for SWAMP program |
QAPP Information Reference(s): |
Quality Assurance Program Plans, Quality Assurance Project Plans, and Standard Operating Procedures for the SWAMP program |
|
Line of Evidence (LOE) for Decision ID 168806, Endosulfan sulfate
|
Region 1 |
Klamath River HU, Shasta River HA |
|
|
LOE ID: |
108024 |
|
Pollutant: |
Endosulfan sulfate |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Total |
|
Beneficial Use: |
Municipal & Domestic Supply |
|
Number of Samples: |
1 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP RWB1 Monitoring data for Klamath River HU, Shasta River HA to determine beneficial use support and results are as follows: 0 of 1 samples exceeded the water quality standard for Endosulfan Sulfate. |
Data Reference: |
Water Quality Assessment Data for the 2018 solicitation cycle submitted through CEDEN for SWAMP RWB1 Monitoring .
|
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
The established numeric criteria for endosulfan sulfate to protect of human health from the consumption of water and organisms is 110 ug/L (California Toxics Rule, 2000). |
Objective/Criterion Reference: |
Water Quality Standards 2000. Establishment of numeric criteria for priority toxic pollutants for the State of California: Rules and regulations. Federal Register Vol. 65, No. 97. Washington, D.C.: Environmental Protection Agency |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
The samples were collected at 1 monitoring site(s) (105SH1452) |
Temporal Representation: |
The samples were collected between the dates of 2013-04-29 and 2013-04-29 |
Environmental Conditions: |
|
QAPP Information: |
Quality Assurance Program Plan and Standard Operating Procedures for SWAMP program |
QAPP Information Reference(s): |
Quality Assurance Program Plans, Quality Assurance Project Plans, and Standard Operating Procedures for the SWAMP program |
|
Line of Evidence (LOE) for Decision ID 168806, Endosulfan sulfate
|
Region 1 |
Klamath River HU, Shasta River HA |
|
|
LOE ID: |
41996 |
|
Pollutant: |
Endosulfan sulfate |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Total |
|
Beneficial Use: |
Cold Freshwater Habitat |
|
Number of Samples: |
3 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP data for Klamath River HU, Shasta River HA to determine beneficial use support and results are as follows: 0 of 3 samples exceed the criterion for Endosulfan sulfate. |
Data Reference: |
RWB1 Trend Maintenance Periods FYs 2007 2008 |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
Water Quality Control Plan, North Coast Region (NCRWQCB 2011): All waters shall be maintained free of toxic substances in concentrations that are toxic to, or that produce detrimental physiological responses in human, plant, animal, or aquatic life. |
Objective/Criterion Reference: |
Water Quality Control Plan (Basin Plan) for the North Coast Region |
|
Evaluation Guideline: |
The USEPA national ambient water quality criterion for freshwater aquatic life 24 hour average maximum for endodulfan sulfate is 0.056 µg/L. |
Guideline Reference: |
National Recommended Water Quality Criteria. United States Environmental Protection Agency. Office of Water. Office of Science and Technology |
|
Spatial Representation: |
Data for this line of evidence for Klamath River HU, Shasta River HA was collected at 1 monitoring site [ Shasta River at Hwy 263 - 105SHA263] |
Temporal Representation: |
Data was collected over the time period 11/15/2007-7/16/2008. |
Environmental Conditions: |
Staff is not aware of any special conditions that might affect interpretation of the data. |
QAPP Information: |
The SWAMP QAPP (2008) was followed. |
QAPP Information Reference(s): |
Surface Water Ambient Monitoring Program Quality Assurance Program Plan |
|
Line of Evidence (LOE) for Decision ID 168806, Endosulfan sulfate
|
Region 1 |
Klamath River HU, Shasta River HA |
|
|
LOE ID: |
42138 |
|
Pollutant: |
Endosulfan sulfate |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Total |
|
Beneficial Use: |
Warm Freshwater Habitat |
|
Number of Samples: |
3 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP data for Klamath River HU, Shasta River HA to determine beneficial use support and results are as follows: 0 of 3 samples exceed the criterion for Endosulfan sulfate. |
Data Reference: |
RWB1 Trend Maintenance Periods FYs 2007 2008 |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
Water Quality Control Plan, North Coast Region (NCRWQCB 2011): All waters shall be maintained free of toxic substances in concentrations that are toxic to, or that produce detrimental physiological responses in human, plant, animal, or aquatic life. |
Objective/Criterion Reference: |
Water Quality Control Plan (Basin Plan) for the North Coast Region |
|
Evaluation Guideline: |
The USEPA national ambient water quality criterion for freshwater aquatic life 24 hour average maximum for endodulfan sulfate is 0.056 µg/L. |
Guideline Reference: |
National Recommended Water Quality Criteria. United States Environmental Protection Agency. Office of Water. Office of Science and Technology |
|
Spatial Representation: |
Data for this line of evidence for Klamath River HU, Shasta River HA was collected at 1 monitoring site [ Shasta River at Hwy 263 - 105SHA263] |
Temporal Representation: |
Data was collected over the time period 11/15/2007-7/16/2008. |
Environmental Conditions: |
Staff is not aware of any special conditions that might affect interpretation of the data. |
QAPP Information: |
The SWAMP QAPP (2008) was followed. |
QAPP Information Reference(s): |
Surface Water Ambient Monitoring Program Quality Assurance Program Plan |
|
Line of Evidence (LOE) for Decision ID 168806, Endosulfan sulfate
|
Region 1 |
Klamath River HU, Shasta River HA |
|
|
LOE ID: |
41995 |
|
Pollutant: |
Endosulfan sulfate |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Total |
|
Beneficial Use: |
Cold Freshwater Habitat |
|
Number of Samples: |
3 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP data for Klamath River HU, Shasta River HA to determine beneficial use support and results are as follows: 0 of 3 samples exceed the criterion for Endosulfan sulfate. |
Data Reference: |
RWB1 Trend Maintenance Periods FYs 2007 2008 |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
Water Quality Control Plan, North Coast Region (NCRWQCB 2011): All waters shall be maintained free of toxic substances in concentrations that are toxic to, or that produce detrimental physiological responses in human, plant, animal, or aquatic life. |
Objective/Criterion Reference: |
Water Quality Control Plan (Basin Plan) for the North Coast Region |
|
Evaluation Guideline: |
The USEPA national ambient water quality criterion for freshwater aquatic life 24 hour average maximum for endodulfan sulfate is 0.056 µg/L. |
Guideline Reference: |
National Recommended Water Quality Criteria. United States Environmental Protection Agency. Office of Water. Office of Science and Technology |
|
Spatial Representation: |
Data for this line of evidence for Klamath River HU, Shasta River HA was collected at 1 monitoring site [ Shasta River near Edgewood - 105SHAEDG] |
Temporal Representation: |
Data was collected over the time period 11/15/2007-7/16/2008. |
Environmental Conditions: |
Staff is not aware of any special conditions that might affect interpretation of the data. |
QAPP Information: |
The SWAMP QAPP (2008) was followed. |
QAPP Information Reference(s): |
Surface Water Ambient Monitoring Program Quality Assurance Program Plan |
|
Line of Evidence (LOE) for Decision ID 168806, Endosulfan sulfate
|
Region 1 |
Klamath River HU, Shasta River HA |
|
|
LOE ID: |
109507 |
|
Pollutant: |
Endosulfan sulfate |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Total |
|
Beneficial Use: |
Municipal & Domestic Supply |
|
Number of Samples: |
1 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP RWB1 Monitoring data for Klamath River HU, Shasta River HA to determine beneficial use support and results are as follows: 0 of 1 samples exceeded the water quality standard for Endosulfan Sulfate. |
Data Reference: |
Water Quality Assessment Data for the 2018 solicitation cycle submitted through CEDEN for SWAMP RWB1 Monitoring .
|
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
The established numeric criteria for endosulfan sulfate to protect of human health from the consumption of water and organisms is 110 ug/L (California Toxics Rule, 2000). |
Objective/Criterion Reference: |
Water Quality Standards 2000. Establishment of numeric criteria for priority toxic pollutants for the State of California: Rules and regulations. Federal Register Vol. 65, No. 97. Washington, D.C.: Environmental Protection Agency |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
The samples were collected at 1 monitoring site(s) (105SH9274) |
Temporal Representation: |
The samples were collected between the dates of 2013-04-29 and 2013-04-29 |
Environmental Conditions: |
|
QAPP Information: |
Quality Assurance Program Plan and Standard Operating Procedures for SWAMP program |
QAPP Information Reference(s): |
Quality Assurance Program Plans, Quality Assurance Project Plans, and Standard Operating Procedures for the SWAMP program |
|
Line of Evidence (LOE) for Decision ID 168806, Endosulfan sulfate
|
Region 1 |
Klamath River HU, Shasta River HA |
|
|
LOE ID: |
109506 |
|
Pollutant: |
Endosulfan sulfate |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Total |
|
Beneficial Use: |
Commercial or recreational collection of fish, shellfish, or organisms |
|
Number of Samples: |
1 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP RWB1 Monitoring data for Klamath River HU, Shasta River HA to determine beneficial use support and results are as follows: 0 of 1 samples exceeded the water quality standard for Endosulfan Sulfate. |
Data Reference: |
Water Quality Assessment Data for the 2018 solicitation cycle submitted through CEDEN for SWAMP RWB1 Monitoring .
|
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
The established numeric criteria for endosulfan sulfate to protection of human health from consumption of organisms only is 240 ug/L (California Toxics Rule, 2000). |
Objective/Criterion Reference: |
Water Quality Standards 2000. Establishment of numeric criteria for priority toxic pollutants for the State of California: Rules and regulations. Federal Register Vol. 65, No. 97. Washington, D.C.: Environmental Protection Agency |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
The samples were collected at 1 monitoring site(s) (105SH9274) |
Temporal Representation: |
The samples were collected between the dates of 2013-04-29 and 2013-04-29 |
Environmental Conditions: |
|
QAPP Information: |
Quality Assurance Program Plan and Standard Operating Procedures for SWAMP program |
QAPP Information Reference(s): |
Quality Assurance Program Plans, Quality Assurance Project Plans, and Standard Operating Procedures for the SWAMP program |
|
Line of Evidence (LOE) for Decision ID 168806, Endosulfan sulfate
|
Region 1 |
Klamath River HU, Shasta River HA |
|
|
LOE ID: |
41615 |
|
Pollutant: |
Endosulfan sulfate |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Total |
|
Beneficial Use: |
Commercial or recreational collection of fish, shellfish, or organisms |
|
Number of Samples: |
3 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP data for Klamath River HU, Shasta River HA to determine beneficial use support and results are as follows: 0 of 3 samples exceed the criterion for Endosulfan sulfate. |
Data Reference: |
RWB1 Trend Maintenance Periods FYs 2007 2008 |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
Water Quality Control Plan, North Coast Region (NCRWQCB 2011): All waters shall be maintained free of toxic substances in concentrations that are toxic to, or that produce detrimental physiological responses in human, plant, animal, or aquatic life. The established numeric criteria for endosulfan sulfate to protection of human health from consumption of organisms only is 240 ug/L (California Toxics Rule, 2000). |
Objective/Criterion Reference: |
Code of Federal Regulations 40 part 131.38 Establishment of numeric criteria for priority toxic pollutants for the State of California. 7/1/2011 Edition |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
Data for this line of evidence for Klamath River HU, Shasta River HA was collected at 1 monitoring site [ Shasta River near Edgewood - 105SHAEDG] |
Temporal Representation: |
Data was collected over the time period 11/15/2007-7/16/2008. |
Environmental Conditions: |
Staff is not aware of any special conditions that might affect interpretation of the data. |
QAPP Information: |
The SWAMP QAPP (2008) was followed. |
QAPP Information Reference(s): |
Surface Water Ambient Monitoring Program Quality Assurance Program Plan |
|
Line of Evidence (LOE) for Decision ID 168806, Endosulfan sulfate
|
Region 1 |
Klamath River HU, Shasta River HA |
|
|
LOE ID: |
41616 |
|
Pollutant: |
Endosulfan sulfate |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Total |
|
Beneficial Use: |
Commercial or recreational collection of fish, shellfish, or organisms |
|
Number of Samples: |
3 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP data for Klamath River HU, Shasta River HA to determine beneficial use support and results are as follows: 0 of 3 samples exceed the criterion for Endosulfan sulfate. |
Data Reference: |
RWB1 Trend Maintenance Periods FYs 2007 2008 |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
Water Quality Control Plan, North Coast Region (NCRWQCB 2011): All waters shall be maintained free of toxic substances in concentrations that are toxic to, or that produce detrimental physiological responses in human, plant, animal, or aquatic life. The established numeric criteria for endosulfan sulfate to protection of human health from consumption of organisms only is 240 ug/L (California Toxics Rule, 2000). |
Objective/Criterion Reference: |
Code of Federal Regulations 40 part 131.38 Establishment of numeric criteria for priority toxic pollutants for the State of California. 7/1/2011 Edition |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
Data for this line of evidence for Klamath River HU, Shasta River HA was collected at 1 monitoring site [ Shasta River at Hwy 263 - 105SHA263] |
Temporal Representation: |
Data was collected over the time period 11/15/2007-7/16/2008. |
Environmental Conditions: |
Staff is not aware of any special conditions that might affect interpretation of the data. |
QAPP Information: |
The SWAMP QAPP (2008) was followed. |
QAPP Information Reference(s): |
Surface Water Ambient Monitoring Program Quality Assurance Program Plan |
|
Line of Evidence (LOE) for Decision ID 168806, Endosulfan sulfate
|
Region 1 |
Klamath River HU, Shasta River HA |
|
|
LOE ID: |
42075 |
|
Pollutant: |
Endosulfan sulfate |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Total |
|
Beneficial Use: |
Municipal & Domestic Supply |
|
Number of Samples: |
3 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP data for Klamath River HU, Shasta River HA to determine beneficial use support and results are as follows: 0 of 3 samples exceed the criterion for Endosulfan sulfate. |
Data Reference: |
RWB1 Trend Maintenance Periods FYs 2007 2008 |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
Water Quality Control Plan, North Coast Region (NCRWQCB 2011): All waters shall be maintained free of toxic substances in concentrations that are toxic to, or that produce detrimental physiological responses in human, plant, animal, or aquatic life. The established numeric criteria for endosulfan sulfate to protect of human health from the consumption of water and organisms is 110 ug/L (California Toxics Rule, 2000). |
Objective/Criterion Reference: |
Code of Federal Regulations 40 part 131.38 Establishment of numeric criteria for priority toxic pollutants for the State of California. 7/1/2011 Edition |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
Data for this line of evidence for Klamath River HU, Shasta River HA was collected at 1 monitoring site [ Shasta River at Hwy 263 - 105SHA263] |
Temporal Representation: |
Data was collected over the time period 11/15/2007-7/16/2008. |
Environmental Conditions: |
Staff is not aware of any special conditions that might affect interpretation of the data. |
QAPP Information: |
The SWAMP QAPP (2008) was followed. |
QAPP Information Reference(s): |
Surface Water Ambient Monitoring Program Quality Assurance Program Plan |
|
Line of Evidence (LOE) for Decision ID 168807, Endrin
|
Region 1 |
Klamath River HU, Shasta River HA |
|
|
LOE ID: |
42103 |
|
Pollutant: |
Endrin |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Total |
|
Beneficial Use: |
Warm Freshwater Habitat |
|
Number of Samples: |
3 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP data for Klamath River HU, Shasta River HA to determine beneficial use support and results are as follows: 0 of 3 samples exceed the criterion for Endrin. |
Data Reference: |
RWB1 Trend Maintenance Periods FYs 2007 2008 |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
Water Quality Control Plan, North Coast Region (NCRWQCB 2011): All waters shall be maintained free of toxic substances in concentrations that are toxic to, or that produce detrimental physiological responses in human, plant, animal, or aquatic life. The established numeric criteria for endrin to protect aquatic life in freshwater as criterion continuous concentration (expressed as a 4-day average) is 0.036 ug/L (California Toxics Rule, 2000). |
Objective/Criterion Reference: |
Code of Federal Regulations 40 part 131.38 Establishment of numeric criteria for priority toxic pollutants for the State of California. 7/1/2011 Edition |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
Data for this line of evidence for Klamath River HU, Shasta River HA was collected at 1 monitoring site [ Shasta River near Edgewood - 105SHAEDG] |
Temporal Representation: |
Data was collected over the time period 11/15/2007-7/16/2008. |
Environmental Conditions: |
Staff is not aware of any special conditions that might affect interpretation of the data. |
QAPP Information: |
The SWAMP QAPP (2008) was followed. |
QAPP Information Reference(s): |
Surface Water Ambient Monitoring Program Quality Assurance Program Plan |
|
Line of Evidence (LOE) for Decision ID 168807, Endrin
|
Region 1 |
Klamath River HU, Shasta River HA |
|
|
LOE ID: |
108036 |
|
Pollutant: |
Endrin |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Total |
|
Beneficial Use: |
Commercial or recreational collection of fish, shellfish, or organisms |
|
Number of Samples: |
1 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP RWB1 Monitoring data for Klamath River HU, Shasta River HA to determine beneficial use support and results are as follows: 0 of 1 samples exceeded the water quality standard for Endrin. |
Data Reference: |
Water Quality Assessment Data for the 2018 solicitation cycle submitted through CEDEN for SWAMP RWB1 Monitoring .
|
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
Water Quality Control Plan, North Coast Region (NCRWQCB 2018): All waters shall be maintained free of toxic substances in concentrations that are toxic to, or that produce detrimental physiological responses in human, plant, animal, or aquatic life. The established numeric criteria for endrin to protect human health from consumption of organisms only is 0.81ug/L (California Toxics Rule, 2000). |
Objective/Criterion Reference: |
Water Quality Standards 2000. Establishment of numeric criteria for priority toxic pollutants for the State of California: Rules and regulations. Federal Register Vol. 65, No. 97. Washington, D.C.: Environmental Protection Agency |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
The samples were collected at 1 monitoring site(s) (105SH1452) |
Temporal Representation: |
The samples were collected between the dates of 2013-04-29 and 2013-04-29 |
Environmental Conditions: |
|
QAPP Information: |
Quality Assurance Program Plan and Standard Operating Procedures for SWAMP program |
QAPP Information Reference(s): |
Quality Assurance Program Plans, Quality Assurance Project Plans, and Standard Operating Procedures for the SWAMP program |
|
Line of Evidence (LOE) for Decision ID 168807, Endrin
|
Region 1 |
Klamath River HU, Shasta River HA |
|
|
LOE ID: |
109520 |
|
Pollutant: |
Endrin |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Total |
|
Beneficial Use: |
Municipal & Domestic Supply |
|
Number of Samples: |
1 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP RWB1 Monitoring data for Klamath River HU, Shasta River HA to determine beneficial use support and results are as follows: 0 of 1 samples exceeded the water quality standard for Endrin. |
Data Reference: |
Water Quality Assessment Data for the 2018 solicitation cycle submitted through CEDEN for SWAMP RWB1 Monitoring .
|
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
Water Quality Control Plan, North Coast Region (NCRWQCB 2018): All waters shall be maintained free of toxic substances in concentrations that are toxic to, or that produce detrimental physiological responses in human, plant, animal, or aquatic life. The established numeric criteria for endrin to protect of human health from the consumption of water and organisms is 0.76 ug/L (California Toxics Rule, 2000). |
Objective/Criterion Reference: |
Water Quality Standards 2000. Establishment of numeric criteria for priority toxic pollutants for the State of California: Rules and regulations. Federal Register Vol. 65, No. 97. Washington, D.C.: Environmental Protection Agency |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
The samples were collected at 1 monitoring site(s) (105SH1452) |
Temporal Representation: |
The samples were collected between the dates of 2013-04-29 and 2013-04-29 |
Environmental Conditions: |
|
QAPP Information: |
Quality Assurance Program Plan and Standard Operating Procedures for SWAMP program |
QAPP Information Reference(s): |
Quality Assurance Program Plans, Quality Assurance Project Plans, and Standard Operating Procedures for the SWAMP program |
|
Line of Evidence (LOE) for Decision ID 168807, Endrin
|
Region 1 |
Klamath River HU, Shasta River HA |
|
|
LOE ID: |
42027 |
|
Pollutant: |
Endrin |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Total |
|
Beneficial Use: |
Municipal & Domestic Supply |
|
Number of Samples: |
3 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP data for Klamath River HU, Shasta River HA to determine beneficial use support and results are as follows: 0 of 3 samples exceed the criterion for Endrin. |
Data Reference: |
RWB1 Trend Maintenance Periods FYs 2007 2008 |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
Water Quality Control Plan, North Coast Region (NCRWQCB 2011): All waters shall be maintained free of toxic substances in concentrations that are toxic to, or that produce detrimental physiological responses in human, plant, animal, or aquatic life. The established numeric criteria for endrin to protect of human health from the consumption of water and organisms is 0.76 ug/L (California Toxics Rule, 2000). |
Objective/Criterion Reference: |
Code of Federal Regulations 40 part 131.38 Establishment of numeric criteria for priority toxic pollutants for the State of California. 7/1/2011 Edition |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
Data for this line of evidence for Klamath River HU, Shasta River HA was collected at 1 monitoring site [ Shasta River at Hwy 263 - 105SHA263] |
Temporal Representation: |
Data was collected over the time period 11/15/2007-7/16/2008. |
Environmental Conditions: |
Staff is not aware of any special conditions that might affect interpretation of the data. |
QAPP Information: |
The SWAMP QAPP (2008) was followed. |
QAPP Information Reference(s): |
Surface Water Ambient Monitoring Program Quality Assurance Program Plan |
|
Line of Evidence (LOE) for Decision ID 168807, Endrin
|
Region 1 |
Klamath River HU, Shasta River HA |
|
|
LOE ID: |
42104 |
|
Pollutant: |
Endrin |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Total |
|
Beneficial Use: |
Warm Freshwater Habitat |
|
Number of Samples: |
3 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP data for Klamath River HU, Shasta River HA to determine beneficial use support and results are as follows: 0 of 3 samples exceed the criterion for Endrin. |
Data Reference: |
RWB1 Trend Maintenance Periods FYs 2007 2008 |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
Water Quality Control Plan, North Coast Region (NCRWQCB 2011): All waters shall be maintained free of toxic substances in concentrations that are toxic to, or that produce detrimental physiological responses in human, plant, animal, or aquatic life. The established numeric criteria for endrin to protect aquatic life in freshwater as criterion continuous concentration (expressed as a 4-day average) is 0.036 ug/L (California Toxics Rule, 2000). |
Objective/Criterion Reference: |
Code of Federal Regulations 40 part 131.38 Establishment of numeric criteria for priority toxic pollutants for the State of California. 7/1/2011 Edition |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
Data for this line of evidence for Klamath River HU, Shasta River HA was collected at 1 monitoring site [ Shasta River at Hwy 263 - 105SHA263] |
Temporal Representation: |
Data was collected over the time period 11/15/2007-7/16/2008. |
Environmental Conditions: |
Staff is not aware of any special conditions that might affect interpretation of the data. |
QAPP Information: |
The SWAMP QAPP (2008) was followed. |
QAPP Information Reference(s): |
Surface Water Ambient Monitoring Program Quality Assurance Program Plan |
|
Line of Evidence (LOE) for Decision ID 168807, Endrin
|
Region 1 |
Klamath River HU, Shasta River HA |
|
|
LOE ID: |
109521 |
|
Pollutant: |
Endrin |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Total |
|
Beneficial Use: |
Commercial or recreational collection of fish, shellfish, or organisms |
|
Number of Samples: |
1 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP RWB1 Monitoring data for Klamath River HU, Shasta River HA to determine beneficial use support and results are as follows: 0 of 1 samples exceeded the water quality standard for Endrin. |
Data Reference: |
Water Quality Assessment Data for the 2018 solicitation cycle submitted through CEDEN for SWAMP RWB1 Monitoring .
|
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
Water Quality Control Plan, North Coast Region (NCRWQCB 2018): All waters shall be maintained free of toxic substances in concentrations that are toxic to, or that produce detrimental physiological responses in human, plant, animal, or aquatic life. The established numeric criteria for endrin to protect human health from consumption of organisms only is 0.81ug/L (California Toxics Rule, 2000). |
Objective/Criterion Reference: |
Water Quality Standards 2000. Establishment of numeric criteria for priority toxic pollutants for the State of California: Rules and regulations. Federal Register Vol. 65, No. 97. Washington, D.C.: Environmental Protection Agency |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
The samples were collected at 1 monitoring site(s) (105SH9274) |
Temporal Representation: |
The samples were collected between the dates of 2013-04-29 and 2013-04-29 |
Environmental Conditions: |
|
QAPP Information: |
Quality Assurance Program Plan and Standard Operating Procedures for SWAMP program |
QAPP Information Reference(s): |
Quality Assurance Program Plans, Quality Assurance Project Plans, and Standard Operating Procedures for the SWAMP program |
|
Line of Evidence (LOE) for Decision ID 168807, Endrin
|
Region 1 |
Klamath River HU, Shasta River HA |
|
|
LOE ID: |
42001 |
|
Pollutant: |
Endrin |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Total |
|
Beneficial Use: |
Commercial or recreational collection of fish, shellfish, or organisms |
|
Number of Samples: |
3 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP data for Klamath River HU, Shasta River HA to determine beneficial use support and results are as follows: 0 of 3 samples exceed the criterion for Endrin. |
Data Reference: |
RWB1 Trend Maintenance Periods FYs 2007 2008 |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
Water Quality Control Plan, North Coast Region (NCRWQCB 2011): All waters shall be maintained free of toxic substances in concentrations that are toxic to, or that produce detrimental physiological responses in human, plant, animal, or aquatic life. The established numeric criteria for endrin to protect human health from consumption of organisms only is 0.81ug/L (California Toxics Rule, 2000). |
Objective/Criterion Reference: |
Code of Federal Regulations 40 part 131.38 Establishment of numeric criteria for priority toxic pollutants for the State of California. 7/1/2011 Edition |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
Data for this line of evidence for Klamath River HU, Shasta River HA was collected at 1 monitoring site [ Shasta River near Edgewood - 105SHAEDG] |
Temporal Representation: |
Data was collected over the time period 11/15/2007-7/16/2008. |
Environmental Conditions: |
Staff is not aware of any special conditions that might affect interpretation of the data. |
QAPP Information: |
The SWAMP QAPP (2008) was followed. |
QAPP Information Reference(s): |
Surface Water Ambient Monitoring Program Quality Assurance Program Plan |
|
Line of Evidence (LOE) for Decision ID 168807, Endrin
|
Region 1 |
Klamath River HU, Shasta River HA |
|
|
LOE ID: |
42002 |
|
Pollutant: |
Endrin |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Total |
|
Beneficial Use: |
Commercial or recreational collection of fish, shellfish, or organisms |
|
Number of Samples: |
3 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP data for Klamath River HU, Shasta River HA to determine beneficial use support and results are as follows: 0 of 3 samples exceed the criterion for Endrin. |
Data Reference: |
RWB1 Trend Maintenance Periods FYs 2007 2008 |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
Water Quality Control Plan, North Coast Region (NCRWQCB 2011): All waters shall be maintained free of toxic substances in concentrations that are toxic to, or that produce detrimental physiological responses in human, plant, animal, or aquatic life. The established numeric criteria for endrin to protect human health from consumption of organisms only is 0.81ug/L (California Toxics Rule, 2000). |
Objective/Criterion Reference: |
Code of Federal Regulations 40 part 131.38 Establishment of numeric criteria for priority toxic pollutants for the State of California. 7/1/2011 Edition |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
Data for this line of evidence for Klamath River HU, Shasta River HA was collected at 1 monitoring site [ Shasta River at Hwy 263 - 105SHA263] |
Temporal Representation: |
Data was collected over the time period 11/15/2007-7/16/2008. |
Environmental Conditions: |
Staff is not aware of any special conditions that might affect interpretation of the data. |
QAPP Information: |
The SWAMP QAPP (2008) was followed. |
QAPP Information Reference(s): |
Surface Water Ambient Monitoring Program Quality Assurance Program Plan |
|
Line of Evidence (LOE) for Decision ID 168807, Endrin
|
Region 1 |
Klamath River HU, Shasta River HA |
|
|
LOE ID: |
109522 |
|
Pollutant: |
Endrin |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Total |
|
Beneficial Use: |
Cold Freshwater Habitat |
|
Number of Samples: |
1 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP RWB1 Monitoring data for Klamath River HU, Shasta River HA to determine beneficial use support and results are as follows: 0 of 1 samples exceeded the water quality standard for Endrin. |
Data Reference: |
Water Quality Assessment Data for the 2018 solicitation cycle submitted through CEDEN for SWAMP RWB1 Monitoring .
|
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
Water Quality Control Plan, North Coast Region (NCRWQCB 2018): All waters shall be maintained free of toxic substances in concentrations that are toxic to, or that produce detrimental physiological responses in human, plant, animal, or aquatic life. The established numeric criteria for endrin to protect aquatic life in freshwater as criterion continuous concentration (expressed as a 4-day average) is 0.036 ug/L (California Toxics Rule, 2000). |
Objective/Criterion Reference: |
Water Quality Standards 2000. Establishment of numeric criteria for priority toxic pollutants for the State of California: Rules and regulations. Federal Register Vol. 65, No. 97. Washington, D.C.: Environmental Protection Agency |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
The samples were collected at 1 monitoring site(s) (105SH9274) |
Temporal Representation: |
The samples were collected between the dates of 2013-04-29 and 2013-04-29 |
Environmental Conditions: |
|
QAPP Information: |
Quality Assurance Program Plan and Standard Operating Procedures for SWAMP program |
QAPP Information Reference(s): |
Quality Assurance Program Plans, Quality Assurance Project Plans, and Standard Operating Procedures for the SWAMP program |
|
Line of Evidence (LOE) for Decision ID 168807, Endrin
|
Region 1 |
Klamath River HU, Shasta River HA |
|
|
LOE ID: |
109523 |
|
Pollutant: |
Endrin |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Total |
|
Beneficial Use: |
Municipal & Domestic Supply |
|
Number of Samples: |
1 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP RWB1 Monitoring data for Klamath River HU, Shasta River HA to determine beneficial use support and results are as follows: 0 of 1 samples exceeded the water quality standard for Endrin. |
Data Reference: |
Water Quality Assessment Data for the 2018 solicitation cycle submitted through CEDEN for SWAMP RWB1 Monitoring .
|
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
Water Quality Control Plan, North Coast Region (NCRWQCB 2018): All waters shall be maintained free of toxic substances in concentrations that are toxic to, or that produce detrimental physiological responses in human, plant, animal, or aquatic life. The established numeric criteria for endrin to protect of human health from the consumption of water and organisms is 0.76 ug/L (California Toxics Rule, 2000). |
Objective/Criterion Reference: |
Water Quality Standards 2000. Establishment of numeric criteria for priority toxic pollutants for the State of California: Rules and regulations. Federal Register Vol. 65, No. 97. Washington, D.C.: Environmental Protection Agency |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
The samples were collected at 1 monitoring site(s) (105SH9274) |
Temporal Representation: |
The samples were collected between the dates of 2013-04-29 and 2013-04-29 |
Environmental Conditions: |
|
QAPP Information: |
Quality Assurance Program Plan and Standard Operating Procedures for SWAMP program |
QAPP Information Reference(s): |
Quality Assurance Program Plans, Quality Assurance Project Plans, and Standard Operating Procedures for the SWAMP program |
|
Line of Evidence (LOE) for Decision ID 168807, Endrin
|
Region 1 |
Klamath River HU, Shasta River HA |
|
|
LOE ID: |
42026 |
|
Pollutant: |
Endrin |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Total |
|
Beneficial Use: |
Municipal & Domestic Supply |
|
Number of Samples: |
3 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP data for Klamath River HU, Shasta River HA to determine beneficial use support and results are as follows: 0 of 3 samples exceed the criterion for Endrin. |
Data Reference: |
RWB1 Trend Maintenance Periods FYs 2007 2008 |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
Water Quality Control Plan, North Coast Region (NCRWQCB 2011): All waters shall be maintained free of toxic substances in concentrations that are toxic to, or that produce detrimental physiological responses in human, plant, animal, or aquatic life. The established numeric criteria for endrin to protect of human health from the consumption of water and organisms is 0.76 ug/L (California Toxics Rule, 2000). |
Objective/Criterion Reference: |
Code of Federal Regulations 40 part 131.38 Establishment of numeric criteria for priority toxic pollutants for the State of California. 7/1/2011 Edition |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
Data for this line of evidence for Klamath River HU, Shasta River HA was collected at 1 monitoring site [ Shasta River near Edgewood - 105SHAEDG] |
Temporal Representation: |
Data was collected over the time period 11/15/2007-7/16/2008. |
Environmental Conditions: |
Staff is not aware of any special conditions that might affect interpretation of the data. |
QAPP Information: |
The SWAMP QAPP (2008) was followed. |
QAPP Information Reference(s): |
Surface Water Ambient Monitoring Program Quality Assurance Program Plan |
|
Line of Evidence (LOE) for Decision ID 168807, Endrin
|
Region 1 |
Klamath River HU, Shasta River HA |
|
|
LOE ID: |
42080 |
|
Pollutant: |
Endrin |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Total |
|
Beneficial Use: |
Cold Freshwater Habitat |
|
Number of Samples: |
3 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP data for Klamath River HU, Shasta River HA to determine beneficial use support and results are as follows: 0 of 3 samples exceed the criterion for Endrin. |
Data Reference: |
RWB1 Trend Maintenance Periods FYs 2007 2008 |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
Water Quality Control Plan, North Coast Region (NCRWQCB 2011): All waters shall be maintained free of toxic substances in concentrations that are toxic to, or that produce detrimental physiological responses in human, plant, animal, or aquatic life. The established numeric criteria for endrin to protect aquatic life in freshwater as criterion continuous concentration (expressed as a 4-day average) is 0.036 ug/L (California Toxics Rule, 2000). |
Objective/Criterion Reference: |
Code of Federal Regulations 40 part 131.38 Establishment of numeric criteria for priority toxic pollutants for the State of California. 7/1/2011 Edition |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
Data for this line of evidence for Klamath River HU, Shasta River HA was collected at 1 monitoring site [ Shasta River near Edgewood - 105SHAEDG] |
Temporal Representation: |
Data was collected over the time period 11/15/2007-7/16/2008. |
Environmental Conditions: |
Staff is not aware of any special conditions that might affect interpretation of the data. |
QAPP Information: |
The SWAMP QAPP (2008) was followed. |
QAPP Information Reference(s): |
Surface Water Ambient Monitoring Program Quality Assurance Program Plan |
|
Line of Evidence (LOE) for Decision ID 168807, Endrin
|
Region 1 |
Klamath River HU, Shasta River HA |
|
|
LOE ID: |
109518 |
|
Pollutant: |
Endrin |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Total |
|
Beneficial Use: |
Cold Freshwater Habitat |
|
Number of Samples: |
1 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP RWB1 Monitoring data for Klamath River HU, Shasta River HA to determine beneficial use support and results are as follows: 0 of 1 samples exceeded the water quality standard for Endrin. |
Data Reference: |
Water Quality Assessment Data for the 2018 solicitation cycle submitted through CEDEN for SWAMP RWB1 Monitoring .
|
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
Water Quality Control Plan, North Coast Region (NCRWQCB 2018): All waters shall be maintained free of toxic substances in concentrations that are toxic to, or that produce detrimental physiological responses in human, plant, animal, or aquatic life. The established numeric criteria for endrin to protect aquatic life in freshwater as criterion continuous concentration (expressed as a 4-day average) is 0.036 ug/L (California Toxics Rule, 2000). |
Objective/Criterion Reference: |
Water Quality Standards 2000. Establishment of numeric criteria for priority toxic pollutants for the State of California: Rules and regulations. Federal Register Vol. 65, No. 97. Washington, D.C.: Environmental Protection Agency |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
The samples were collected at 1 monitoring site(s) (105SH1452) |
Temporal Representation: |
The samples were collected between the dates of 2013-04-29 and 2013-04-29 |
Environmental Conditions: |
|
QAPP Information: |
Quality Assurance Program Plan and Standard Operating Procedures for SWAMP program |
QAPP Information Reference(s): |
Quality Assurance Program Plans, Quality Assurance Project Plans, and Standard Operating Procedures for the SWAMP program |
|
Line of Evidence (LOE) for Decision ID 168807, Endrin
|
Region 1 |
Klamath River HU, Shasta River HA |
|
|
LOE ID: |
42081 |
|
Pollutant: |
Endrin |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Total |
|
Beneficial Use: |
Cold Freshwater Habitat |
|
Number of Samples: |
3 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP data for Klamath River HU, Shasta River HA to determine beneficial use support and results are as follows: 0 of 3 samples exceed the criterion for Endrin. |
Data Reference: |
RWB1 Trend Maintenance Periods FYs 2007 2008 |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
Water Quality Control Plan, North Coast Region (NCRWQCB 2011): All waters shall be maintained free of toxic substances in concentrations that are toxic to, or that produce detrimental physiological responses in human, plant, animal, or aquatic life. The established numeric criteria for endrin to protect aquatic life in freshwater as criterion continuous concentration (expressed as a 4-day average) is 0.036 ug/L (California Toxics Rule, 2000). |
Objective/Criterion Reference: |
Code of Federal Regulations 40 part 131.38 Establishment of numeric criteria for priority toxic pollutants for the State of California. 7/1/2011 Edition |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
Data for this line of evidence for Klamath River HU, Shasta River HA was collected at 1 monitoring site [ Shasta River at Hwy 263 - 105SHA263] |
Temporal Representation: |
Data was collected over the time period 11/15/2007-7/16/2008. |
Environmental Conditions: |
Staff is not aware of any special conditions that might affect interpretation of the data. |
QAPP Information: |
The SWAMP QAPP (2008) was followed. |
QAPP Information Reference(s): |
Surface Water Ambient Monitoring Program Quality Assurance Program Plan |
|
Line of Evidence (LOE) for Decision ID 169751, Ethion
|
Region 1 |
Klamath River HU, Shasta River HA |
|
|
LOE ID: |
123549 |
|
Pollutant: |
Ethion |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
None |
|
Beneficial Use: |
Municipal & Domestic Supply |
|
Number of Samples: |
0 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
State Water Board staff re-assessed SWAMP data for Klamath River HU, Shasta River HA to determine beneficial use support and results are as follows: 0 of 0 samples exceed the criterion for Ethion, Total. Four samples were removed from assessment because an appropriate evaluation guideline for the water body-pollutant combination could not be obtained for this listing cycle. This LOE re-assesses data from LOE 29849 from the 2010 Integrated Report. Data were re-assessed in order to evaluate these data in their own LOE, instead of being evaluated in the same LOE as other pesticide data. |
Data Reference: |
Surface Water Ambient Monitoring Program (SWAMP). Summary Report for the North Coast Region (RWQCB-1) for years 2000-2006. North Coast Regional Water Quality Control Board. March 2008 |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
Per the Basin Plan (NCRWQCB 2011): No individual pesticide or combination of pesticides shall be present in concentrations that adversely affect beneficial uses. There shall be no bioaccumulation of pesticide concentrations found in bottom sediments or aquatic life. Waters designated for use as domestic or municipal supply shall not contain concentrations of pesticides in excess of the limiting concentrations set forth in California Code of Regulations, Title 22, Division 4, Chapter 15, Article 4, Section 64444, and listed in Table 3.2 of the Basin Plan. No evaluation guideline could be found to evaluate protection of the MUN beneficial use that meets the requirements of Section 6.1.3 of the Listing Policy. |
Objective/Criterion Reference: |
Water Quality Control Plan (Basin Plan) for the North Coast Region |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
Data for this line of evidence for Klamath River HU, Shasta River HA was collected at 1 monitoring site [ Shasta River at Montague - 105SHAMON] |
Temporal Representation: |
Data was collected over the time period 10/7/2002-6/19/2003. |
Environmental Conditions: |
There are no known environmental conditions (e.g., seasonality, land use practices, fire events, storms, etc.) that are related to these data. |
QAPP Information: |
Quality control was conducted in accordance with the SWAMP Quality Assurance Management Plan (SWAMP 2002). |
QAPP Information Reference(s): |
Quality Assurance Management Plan for the State of California's Surface Water Ambient Monitoring Program. Sacramento, CA. State Water Resources Control Board. SWAMP. December 2002 (1st version)
|
|
Line of Evidence (LOE) for Decision ID 169751, Ethion
|
Region 1 |
Klamath River HU, Shasta River HA |
|
|
LOE ID: |
123551 |
|
Pollutant: |
Ethion |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
None |
|
Beneficial Use: |
Municipal & Domestic Supply |
|
Number of Samples: |
0 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
State Water Board staff re-assessed SWAMP data for Klamath River HU, Shasta River HA to determine beneficial use support and results are as follows: 0 of 0 samples exceed the criterion for Ethion, Total. Eight samples were removed from assessment because an appropriate evaluation guideline for the water body-pollutant combination could not be obtained for this listing cycle. This LOE re-assesses data from LOE 29849 from the 2010 Integrated Report. Data were re-assessed in order to evaluate these data in their own LOE, instead of being evaluated in the same LOE as other pesticide data. |
Data Reference: |
Surface Water Ambient Monitoring Program (SWAMP). Summary Report for the North Coast Region (RWQCB-1) for years 2000-2006. North Coast Regional Water Quality Control Board. March 2008 |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
Per the Basin Plan (NCRWQCB 2011): No individual pesticide or combination of pesticides shall be present in concentrations that adversely affect beneficial uses. There shall be no bioaccumulation of pesticide concentrations found in bottom sediments or aquatic life. Waters designated for use as domestic or municipal supply shall not contain concentrations of pesticides in excess of the limiting concentrations set forth in California Code of Regulations, Title 22, Division 4, Chapter 15, Article 4, Section 64444, and listed in Table 3.2 of the Basin Plan. No evaluation guideline could be found to evaluate protection of the MUN beneficial use that meets the requirements of Section 6.1.3 of the Listing Policy. |
Objective/Criterion Reference: |
Water Quality Control Plan (Basin Plan) for the North Coast Region |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
Data for this line of evidence for Klamath River HU, Shasta River HA was collected at 1 monitoring site [ Yreka Creek at Anderson Rd - 105YREAND] |
Temporal Representation: |
Data was collected over the time period 10/9/2002-6/20/2005. |
Environmental Conditions: |
There are no known environmental conditions (e.g., seasonality, land use practices, fire events, storms, etc.) that are related to these data. |
QAPP Information: |
Quality control was conducted in accordance with the SWAMP Quality Assurance Management Plan (SWAMP 2002). |
QAPP Information Reference(s): |
Quality Assurance Management Plan for the State of California's Surface Water Ambient Monitoring Program. Sacramento, CA. State Water Resources Control Board. SWAMP. December 2002 (1st version)
|
|
Line of Evidence (LOE) for Decision ID 169751, Ethion
|
Region 1 |
Klamath River HU, Shasta River HA |
|
|
LOE ID: |
109525 |
|
Pollutant: |
Ethion |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Total |
|
Beneficial Use: |
Municipal & Domestic Supply |
|
Number of Samples: |
3 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP RWB1 Monitoring data for Klamath River HU, Shasta River HA to determine beneficial use support and results are as follows: 0 of 3 samples exceeded the water quality standard for Ethion. |
Data Reference: |
Water Quality Assessment Data for the 2018 solicitation cycle submitted through CEDEN for SWAMP RWB1 Monitoring .
|
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
All waters shall be maintained free of toxic substances in concentrations that are toxic to, or that produce detrimental physiological responses in human, plant, animal, or aquatic life (North Coast Regional Water Quality Control Board). |
Objective/Criterion Reference: |
Water Quality Control Plan (Basin Plan) for the North Coast Region |
|
Evaluation Guideline: |
The USEPA expected safe lifetime exposure limit in drinking water for Ethion, calculated using the IRIS Reference Dose, is 3.5 ug/L. This was calculated assuming 70 kg body weight, 2 liters/day water consumption, 20% relative source contribution from drinking water, and 0.0005 mg/kg/day as the reference dose. |
Guideline Reference: |
IRIS Reference Summary (Various Pollutants) |
|
Spatial Representation: |
The samples were collected at 1 monitoring site(s) (105SH9274) |
Temporal Representation: |
The samples were collected between the dates of 2013-03-07 and 2013-11-20 |
Environmental Conditions: |
|
QAPP Information: |
Quality Assurance Program Plan and Standard Operating Procedures for SWAMP program |
QAPP Information Reference(s): |
Quality Assurance Program Plans, Quality Assurance Project Plans, and Standard Operating Procedures for the SWAMP program |
|
Line of Evidence (LOE) for Decision ID 169751, Ethion
|
Region 1 |
Klamath River HU, Shasta River HA |
|
|
LOE ID: |
109524 |
|
Pollutant: |
Ethion |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Total |
|
Beneficial Use: |
Municipal & Domestic Supply |
|
Number of Samples: |
3 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP RWB1 Monitoring data for Klamath River HU, Shasta River HA to determine beneficial use support and results are as follows: 0 of 3 samples exceeded the water quality standard for Ethion. |
Data Reference: |
Water Quality Assessment Data for the 2018 solicitation cycle submitted through CEDEN for SWAMP RWB1 Monitoring .
|
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
All waters shall be maintained free of toxic substances in concentrations that are toxic to, or that produce detrimental physiological responses in human, plant, animal, or aquatic life (North Coast Regional Water Quality Control Board). |
Objective/Criterion Reference: |
Water Quality Control Plan (Basin Plan) for the North Coast Region |
|
Evaluation Guideline: |
The USEPA expected safe lifetime exposure limit in drinking water for Ethion, calculated using the IRIS Reference Dose, is 3.5 ug/L. This was calculated assuming 70 kg body weight, 2 liters/day water consumption, 20% relative source contribution from drinking water, and 0.0005 mg/kg/day as the reference dose. |
Guideline Reference: |
IRIS Reference Summary (Various Pollutants) |
|
Spatial Representation: |
The samples were collected at 1 monitoring site(s) (105SH1452) |
Temporal Representation: |
The samples were collected between the dates of 2013-03-06 and 2013-11-20 |
Environmental Conditions: |
|
QAPP Information: |
Quality Assurance Program Plan and Standard Operating Procedures for SWAMP program |
QAPP Information Reference(s): |
Quality Assurance Program Plans, Quality Assurance Project Plans, and Standard Operating Procedures for the SWAMP program |
|
Line of Evidence (LOE) for Decision ID 169751, Ethion
|
Region 1 |
Klamath River HU, Shasta River HA |
|
|
LOE ID: |
123552 |
|
Pollutant: |
Ethion |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
None |
|
Beneficial Use: |
Municipal & Domestic Supply |
|
Number of Samples: |
0 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
State Water Board staff re-assessed SWAMP data for Klamath River HU, Shasta River HA to determine beneficial use support and results are as follows: 0 of 0 samples exceed the criterion for Ethion, Total. Four samples were removed from assessment because an appropriate evaluation guideline for the water body-pollutant combination could not be obtained for this listing cycle. This LOE re-assesses data from LOE 29849 from the 2010 Integrated Report. Data were re-assessed in order to evaluate these data in their own LOE, instead of being evaluated in the same LOE as other pesticide data. |
Data Reference: |
Surface Water Ambient Monitoring Program (SWAMP). Summary Report for the North Coast Region (RWQCB-1) for years 2000-2006. North Coast Regional Water Quality Control Board. March 2008 |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
Per the Basin Plan (NCRWQCB 2011): No individual pesticide or combination of pesticides shall be present in concentrations that adversely affect beneficial uses. There shall be no bioaccumulation of pesticide concentrations found in bottom sediments or aquatic life. Waters designated for use as domestic or municipal supply shall not contain concentrations of pesticides in excess of the limiting concentrations set forth in California Code of Regulations, Title 22, Division 4, Chapter 15, Article 4, Section 64444, and listed in Table 3.2 of the Basin Plan. No evaluation guideline could be found to evaluate protection of the MUN beneficial use that meets the requirements of Section 6.1.3 of the Listing Policy. |
Objective/Criterion Reference: |
Water Quality Control Plan (Basin Plan) for the North Coast Region |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
Data for this line of evidence for Klamath River HU, Shasta River HA was collected at 1 monitoring site [ Yreka Creek at Highway 3 - 105YREHW3] |
Temporal Representation: |
Data was collected over the time period 10/21/2004-6/20/2005. |
Environmental Conditions: |
There are no known environmental conditions (e.g., seasonality, land use practices, fire events, storms, etc.) that are related to these data. |
QAPP Information: |
Quality control was conducted in accordance with the SWAMP Quality Assurance Management Plan (SWAMP 2002). |
QAPP Information Reference(s): |
Quality Assurance Management Plan for the State of California's Surface Water Ambient Monitoring Program. Sacramento, CA. State Water Resources Control Board. SWAMP. December 2002 (1st version)
|
|
Line of Evidence (LOE) for Decision ID 169751, Ethion
|
Region 1 |
Klamath River HU, Shasta River HA |
|
|
LOE ID: |
25614 |
|
Pollutant: |
Ethion |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
None |
|
Beneficial Use: |
Municipal & Domestic Supply |
|
Number of Samples: |
34 |
Number of Exceedances: |
1 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
One of the 34 ethion samples collected in the Shasta River watershed exceeds the evaluation guideline. Sample concentrations range from non-detect (with a reporting limit of 0.050 ug/l) to detected but not quantified with a concentration of at least 0.050 ug/l. The samples were collected as part of the Surface Water Ambient Water Monitoring Program (SWAMP). The data are found in the 5-Year Monitoring Report (NCRWQCB 2008). |
Data Reference: |
Surface Water Ambient Monitoring Program (SWAMP). Summary Report for the North Coast Region (RWQCB-1) for years 2000-2006. North Coast Regional Water Quality Control Board. March 2008 |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
Per the Basin Plan (NCRWQCB 2007): No individual pesticide or combination of pesticides shall be present in concentrations that adversely affect beneficial uses. There shall be no bioaccumulation of pesticide concentrations found in bottom sediments or aquatic life. Waters designated for use as domestic or municipal supply shall not contain concentrations of pesticides in excess of the limiting concentrations set forth in California Code of Regulations, Title 22, Division 4, Chapter 15, Article 4, Section 64444, and listed in Table 3.2 of the Basin Plan. |
Objective/Criterion Reference: |
Water Quality Control Plan (Basin Plan) - North Coast Region (Region 1) |
|
Evaluation Guideline: |
Per "Water Quality Criteria 1972" (USEPA 1973): The instantaneous maximum water quality criterion for ethion for the protection of freshwater aquatic life is 0.02 ug/l. |
Guideline Reference: |
National Academy of Sciences. Water Quality Criteria 1972. EPA-R3-73-033. Washington, D.C.: U.S. Environmental Protection Agency |
|
Spatial Representation: |
Samples were collected in the Shasta River watershed from 5 locations as follows: (1) near Edgewood Road (SWAMP Station ID 105SHAEDG), (2) at Montague Grenada Road (SWAMP Station ID 105SHAMON), (3) at Highway 263 (SWAMP Station ID 105SHA263), (4) in Yreka Creek at Highway 3 (SWAMP Station ID 105YREHW3), and (5) in Yreka Creek at Anderson Grade Road (SWAMP Station ID 105YREAND). Samples were collected in well-mixed flows in glides or riffles. |
Temporal Representation: |
The samples from Edgewood Road and Montague Grenada Road were collected as grab samples during 5 site visits at each site during the 2002 - 2003 fiscal years. Samples from Highway 263 were collected as grab samples during 22 site visits during the 2000 - 2006 fiscal years. Samples in Yreka Creek were collected from October 2004 to June 2005. The site visits corresponded to fall, winter, spring and early summer seasonal conditions. |
Environmental Conditions: |
There are no known environmental conditions (e.g., seasonality, land use practices, fire events, storms, etc.) that are related to these data. |
QAPP Information: |
Quality control was conducted in accordance with the SWAMP Quality Assurance Management Plan (SWAMP 2002). |
QAPP Information Reference(s): |
Quality Assurance Management Plan for the State of California's Surface Water Ambient Monitoring Program. Sacramento, CA. State Water Resources Control Board. SWAMP. December 2002 (1st version)
|
|
Line of Evidence (LOE) for Decision ID 169751, Ethion
|
Region 1 |
Klamath River HU, Shasta River HA |
|
|
LOE ID: |
123548 |
|
Pollutant: |
Ethion |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
None |
|
Beneficial Use: |
Municipal & Domestic Supply |
|
Number of Samples: |
0 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
State Water Board staff re-assessed SWAMP data for Klamath River HU, Shasta River HA to determine beneficial use support and results are as follows: 0 of 0 samples exceed the criterion for Ethion, Total. Sixteen samples were removed from assessment because an appropriate evaluation guideline for the water body-pollutant combination could not be obtained for this listing cycle. This LOE re-assesses data from LOE 29849 from the 2010 Integrated Report. Data were re-assessed in order to evaluate these data in their own LOE, instead of being evaluated in the same LOE as other pesticide data. |
Data Reference: |
Surface Water Ambient Monitoring Program (SWAMP). Summary Report for the North Coast Region (RWQCB-1) for years 2000-2006. North Coast Regional Water Quality Control Board. March 2008 |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
Per the Basin Plan (NCRWQCB 2011): No individual pesticide or combination of pesticides shall be present in concentrations that adversely affect beneficial uses. There shall be no bioaccumulation of pesticide concentrations found in bottom sediments or aquatic life. Waters designated for use as domestic or municipal supply shall not contain concentrations of pesticides in excess of the limiting concentrations set forth in California Code of Regulations, Title 22, Division 4, Chapter 15, Article 4, Section 64444, and listed in Table 3.2 of the Basin Plan. No evaluation guideline could be found to evaluate protection of the MUN beneficial use that meets the requirements of Section 6.1.3 of the Listing Policy. |
Objective/Criterion Reference: |
Water Quality Control Plan (Basin Plan) for the North Coast Region |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
Data for this line of evidence for Klamath River HU, Shasta River HA was collected at 1 monitoring site [ Shasta River at Hwy 263 - 105SH1452] |
Temporal Representation: |
Data was collected over the time period 2/27/2002-11/16/2006. |
Environmental Conditions: |
There are no known environmental conditions (e.g., seasonality, land use practices, fire events, storms, etc.) that are related to these data. |
QAPP Information: |
Quality control was conducted in accordance with the SWAMP Quality Assurance Management Plan (SWAMP 2002). |
QAPP Information Reference(s): |
Quality Assurance Management Plan for the State of California's Surface Water Ambient Monitoring Program. Sacramento, CA. State Water Resources Control Board. SWAMP. December 2002 (1st version)
|
|
Line of Evidence (LOE) for Decision ID 169751, Ethion
|
Region 1 |
Klamath River HU, Shasta River HA |
|
|
LOE ID: |
123550 |
|
Pollutant: |
Ethion |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
None |
|
Beneficial Use: |
Municipal & Domestic Supply |
|
Number of Samples: |
0 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
State Water Board staff re-assessed SWAMP data for Klamath River HU, Shasta River HA to determine beneficial use support and results are as follows: 0 of 0 samples exceed the criterion for Ethion, Total. Four samples were removed from assessment because an appropriate evaluation guideline for the water body-pollutant combination could not be obtained for this listing cycle. This LOE re-assesses data from LOE 29849 from the 2010 Integrated Report. Data were re-assessed in order to evaluate these data in their own LOE, instead of being evaluated in the same LOE as other pesticide data. |
Data Reference: |
Surface Water Ambient Monitoring Program (SWAMP). Summary Report for the North Coast Region (RWQCB-1) for years 2000-2006. North Coast Regional Water Quality Control Board. March 2008 |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
Per the Basin Plan (NCRWQCB 2011): No individual pesticide or combination of pesticides shall be present in concentrations that adversely affect beneficial uses. There shall be no bioaccumulation of pesticide concentrations found in bottom sediments or aquatic life. Waters designated for use as domestic or municipal supply shall not contain concentrations of pesticides in excess of the limiting concentrations set forth in California Code of Regulations, Title 22, Division 4, Chapter 15, Article 4, Section 64444, and listed in Table 3.2 of the Basin Plan. No evaluation guideline could be found to evaluate protection of the MUN beneficial use that meets the requirements of Section 6.1.3 of the Listing Policy. |
Objective/Criterion Reference: |
Water Quality Control Plan (Basin Plan) for the North Coast Region |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
Data for this line of evidence for Klamath River HU, Shasta River HA was collected at 1 monitoring site [ Shasta River near Edgewood - 105SH9274] |
Temporal Representation: |
Data was collected over the time period 10/7/2002-6/19/2003. |
Environmental Conditions: |
There are no known environmental conditions (e.g., seasonality, land use practices, fire events, storms, etc.) that are related to these data. |
QAPP Information: |
Quality control was conducted in accordance with the SWAMP Quality Assurance Management Plan (SWAMP 2002). |
QAPP Information Reference(s): |
Quality Assurance Management Plan for the State of California's Surface Water Ambient Monitoring Program. Sacramento, CA. State Water Resources Control Board. SWAMP. December 2002 (1st version)
|
|
Line of Evidence (LOE) for Decision ID 169751, Ethion
|
Region 1 |
Klamath River HU, Shasta River HA |
|
|
LOE ID: |
349633 |
|
Pollutant: |
Ethion |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Total |
|
Beneficial Use: |
Warm Freshwater Habitat |
|
Number of Samples: |
0 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP RWB1 Monitoring data for Klamath River HU, Shasta River HA to determine beneficial use support, and the results are as follows: 0 of the 0 samples exceeded the evaluation guideline for Ethion. Although a total of 3 samples were collected, 3 of these samples were not included in the assessment because the laboratory data reporting limit(s) was above the water quality threshold and therefore the results could not be quantified with the level of certainty required by the Listing Policy Section 6.1.5.5. |
Data Reference: |
Water Quality Assessment Data for the 2018 solicitation cycle submitted through CEDEN for SWAMP RWB1 Monitoring .
|
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
All waters shall be maintained free of toxic substances in concentrations that are toxic to, or that produce detrimental physiological responses in human, plant, animal, or aquatic life (North Coast Regional Water Quality Control Board). |
Objective/Criterion Reference: |
Water Quality Control Plan (Basin Plan) for the North Coast Region |
|
Evaluation Guideline: |
The evaluation guideline for ethion is the USEPA Aquatic Life Benchmark of 0.028 ug/L for invertebrates (acute). |
Guideline Reference: |
OPP Aquatic Life Benchmarks |
|
Spatial Representation: |
The samples were collected at 1 monitoring site: 105SH1452 (Shasta River at Hwy 263). |
Temporal Representation: |
The samples were collected between the dates of 2013-03-06 and 2013-11-20 |
Environmental Conditions: |
|
QAPP Information: |
Generic SWAMP QAPrP |
QAPP Information Reference(s): |
Generic SWAMP QAPrP |
|
Line of Evidence (LOE) for Decision ID 169751, Ethion
|
Region 1 |
Klamath River HU, Shasta River HA |
|
|
LOE ID: |
349622 |
|
Pollutant: |
Ethion |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Total |
|
Beneficial Use: |
Cold Freshwater Habitat |
|
Number of Samples: |
0 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP RWB1 Monitoring data for Klamath River HU, Shasta River HA to determine beneficial use support, and the results are as follows: 0 of the 0 samples exceeded the evaluation guideline for Ethion. Although a total of 3 samples were collected, 3 of these samples were not included in the assessment because the laboratory data reporting limit(s) was above the water quality threshold and therefore the results could not be quantified with the level of certainty required by the Listing Policy Section 6.1.5.5. |
Data Reference: |
Water Quality Assessment Data for the 2018 solicitation cycle submitted through CEDEN for SWAMP RWB1 Monitoring .
|
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
All waters shall be maintained free of toxic substances in concentrations that are toxic to, or that produce detrimental physiological responses in human, plant, animal, or aquatic life (North Coast Regional Water Quality Control Board). |
Objective/Criterion Reference: |
Water Quality Control Plan (Basin Plan) for the North Coast Region |
|
Evaluation Guideline: |
The evaluation guideline for ethion is the USEPA Aquatic Life Benchmark of 0.028 ug/L for invertebrates (acute). |
Guideline Reference: |
OPP Aquatic Life Benchmarks |
|
Spatial Representation: |
The samples were collected at 1 monitoring site: 105SH1452 (Shasta River at Hwy 263). |
Temporal Representation: |
The samples were collected between the dates of 2013-03-06 and 2013-11-20 |
Environmental Conditions: |
|
QAPP Information: |
Generic SWAMP QAPrP |
QAPP Information Reference(s): |
Generic SWAMP QAPrP |
|
Line of Evidence (LOE) for Decision ID 169751, Ethion
|
Region 1 |
Klamath River HU, Shasta River HA |
|
|
LOE ID: |
349704 |
|
Pollutant: |
Ethion |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Total |
|
Beneficial Use: |
Cold Freshwater Habitat |
|
Number of Samples: |
0 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP RWB1 Monitoring data for Klamath River HU, Shasta River HA to determine beneficial use support, and the results are as follows: 0 of the 0 samples exceeded the evaluation guideline for Ethion. Although a total of 3 samples were collected, 3 of these samples were not included in the assessment because the laboratory data reporting limit(s) was above the water quality threshold and therefore the results could not be quantified with the level of certainty required by the Listing Policy Section 6.1.5.5. |
Data Reference: |
Water Quality Assessment Data for the 2018 solicitation cycle submitted through CEDEN for SWAMP RWB1 Monitoring .
|
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
All waters shall be maintained free of toxic substances in concentrations that are toxic to, or that produce detrimental physiological responses in human, plant, animal, or aquatic life (North Coast Regional Water Quality Control Board). |
Objective/Criterion Reference: |
Water Quality Control Plan (Basin Plan) for the North Coast Region |
|
Evaluation Guideline: |
The evaluation guideline for ethion is the USEPA Aquatic Life Benchmark of 0.028 ug/L for invertebrates (acute). |
Guideline Reference: |
OPP Aquatic Life Benchmarks |
|
Spatial Representation: |
The samples were collected at 1 monitoring site: 105SH9274 (Shasta River near Edgewood). |
Temporal Representation: |
The samples were collected between the dates of 2013-03-07 and 2013-11-20 |
Environmental Conditions: |
|
QAPP Information: |
Generic SWAMP QAPrP |
QAPP Information Reference(s): |
Generic SWAMP QAPrP |
|
Line of Evidence (LOE) for Decision ID 169751, Ethion
|
Region 1 |
Klamath River HU, Shasta River HA |
|
|
LOE ID: |
349728 |
|
Pollutant: |
Ethion |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Total |
|
Beneficial Use: |
Warm Freshwater Habitat |
|
Number of Samples: |
0 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP RWB1 Monitoring data for Klamath River HU, Shasta River HA to determine beneficial use support, and the results are as follows: 0 of the 0 samples exceeded the evaluation guideline for Ethion. Although a total of 3 samples were collected, 3 of these samples were not included in the assessment because the laboratory data reporting limit(s) was above the water quality threshold and therefore the results could not be quantified with the level of certainty required by the Listing Policy Section 6.1.5.5. |
Data Reference: |
Water Quality Assessment Data for the 2018 solicitation cycle submitted through CEDEN for SWAMP RWB1 Monitoring .
|
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
All waters shall be maintained free of toxic substances in concentrations that are toxic to, or that produce detrimental physiological responses in human, plant, animal, or aquatic life (North Coast Regional Water Quality Control Board). |
Objective/Criterion Reference: |
Water Quality Control Plan (Basin Plan) for the North Coast Region |
|
Evaluation Guideline: |
The evaluation guideline for ethion is the USEPA Aquatic Life Benchmark of 0.028 ug/L for invertebrates (acute). |
Guideline Reference: |
OPP Aquatic Life Benchmarks |
|
Spatial Representation: |
The samples were collected at 1 monitoring site: 105SH9274 (Shasta River near Edgewood). |
Temporal Representation: |
The samples were collected between the dates of 2013-03-07 and 2013-11-20 |
Environmental Conditions: |
|
QAPP Information: |
Generic SWAMP QAPrP |
QAPP Information Reference(s): |
Generic SWAMP QAPrP |
|
Line of Evidence (LOE) for Decision ID 168809, Ethoprop
|
Region 1 |
Klamath River HU, Shasta River HA |
|
|
LOE ID: |
123553 |
|
Pollutant: |
Ethoprop |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
None |
|
Beneficial Use: |
Municipal & Domestic Supply |
|
Number of Samples: |
0 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
State Water Board staff re-assessed SWAMP data for Klamath River HU, Shasta River HA to determine beneficial use support and results are as follows: 0 of 0 samples exceed the criterion for Ethoprop, Total. Sixteen samples were removed from assessment because an appropriate evaluation guideline for the water body-pollutant combination could not be obtained for this listing cycle. This LOE re-assesses data from LOE 29849 from the 2010 Integrated Report. Data were re-assessed in order to evaluate these data in their own LOE, instead of being evaluated in the same LOE as other pesticide data. |
Data Reference: |
Surface Water Ambient Monitoring Program (SWAMP). Summary Report for the North Coast Region (RWQCB-1) for years 2000-2006. North Coast Regional Water Quality Control Board. March 2008 |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
Per the Basin Plan (NCRWQCB 2011): No individual pesticide or combination of pesticides shall be present in concentrations that adversely affect beneficial uses. There shall be no bioaccumulation of pesticide concentrations found in bottom sediments or aquatic life. Waters designated for use as domestic or municipal supply shall not contain concentrations of pesticides in excess of the limiting concentrations set forth in California Code of Regulations, Title 22, Division 4, Chapter 15, Article 4, Section 64444, and listed in Table 3.2 of the Basin Plan. No evaluation guideline could be found to evaluate protection of the MUN beneficial use that meets the requirements of Section 6.1.3 of the Listing Policy. |
Objective/Criterion Reference: |
Water Quality Control Plan (Basin Plan) for the North Coast Region |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
Data for this line of evidence for Klamath River HU, Shasta River HA was collected at 1 monitoring site [ Shasta River at Hwy 263 - 105SH1452] |
Temporal Representation: |
Data was collected over the time period 2/27/2002-11/16/2006. |
Environmental Conditions: |
There are no known environmental conditions (e.g., seasonality, land use practices, fire events, storms, etc.) that are related to these data. |
QAPP Information: |
Quality control was conducted in accordance with the SWAMP Quality Assurance Management Plan (SWAMP 2002). |
QAPP Information Reference(s): |
Quality Assurance Management Plan for the State of California's Surface Water Ambient Monitoring Program. Sacramento, CA. State Water Resources Control Board. SWAMP. December 2002 (1st version)
|
|
Line of Evidence (LOE) for Decision ID 168809, Ethoprop
|
Region 1 |
Klamath River HU, Shasta River HA |
|
|
LOE ID: |
109527 |
|
Pollutant: |
Ethoprop |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Total |
|
Beneficial Use: |
Warm Freshwater Habitat |
|
Number of Samples: |
3 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP RWB1 Monitoring data for Klamath River HU, Shasta River HA to determine beneficial use support and results are as follows: 0 of 3 samples exceeded the water quality standard for Ethoprop. |
Data Reference: |
Water Quality Assessment Data for the 2018 solicitation cycle submitted through CEDEN for SWAMP RWB1 Monitoring .
|
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
All waters shall be maintained free of toxic substances in concentrations which are toxic to, or which produce detrimental physiological responses in, human, plant, animal, or aquatic life. (Basin Plan). |
Objective/Criterion Reference: |
Water Quality Control Plan (Basin Plan) for the North Coast Region |
|
Evaluation Guideline: |
The evaluation guideline for Ethoprop is the USEPA Aquatic Life Benchmark of 0.8 ug/L for an invertebrate (chronic). |
Guideline Reference: |
OPP Aquatic Life Benchmarks |
|
Spatial Representation: |
The samples were collected at 1 monitoring site(s) (105SH1452) |
Temporal Representation: |
The samples were collected between the dates of 2013-03-06 and 2013-11-20 |
Environmental Conditions: |
|
QAPP Information: |
Quality Assurance Program Plan and Standard Operating Procedures for SWAMP program |
QAPP Information Reference(s): |
Quality Assurance Program Plans, Quality Assurance Project Plans, and Standard Operating Procedures for the SWAMP program |
|
Line of Evidence (LOE) for Decision ID 168809, Ethoprop
|
Region 1 |
Klamath River HU, Shasta River HA |
|
|
LOE ID: |
109526 |
|
Pollutant: |
Ethoprop |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Total |
|
Beneficial Use: |
Cold Freshwater Habitat |
|
Number of Samples: |
3 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP RWB1 Monitoring data for Klamath River HU, Shasta River HA to determine beneficial use support and results are as follows: 0 of 3 samples exceeded the water quality standard for Ethoprop. |
Data Reference: |
Water Quality Assessment Data for the 2018 solicitation cycle submitted through CEDEN for SWAMP RWB1 Monitoring .
|
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
All waters shall be maintained free of toxic substances in concentrations which are toxic to, or which produce detrimental physiological responses in, human, plant, animal, or aquatic life. (Basin Plan). |
Objective/Criterion Reference: |
Water Quality Control Plan (Basin Plan) for the North Coast Region |
|
Evaluation Guideline: |
The evaluation guideline for Ethoprop is the USEPA Aquatic Life Benchmark of 0.8 ug/L for an invertebrate (chronic). |
Guideline Reference: |
OPP Aquatic Life Benchmarks |
|
Spatial Representation: |
The samples were collected at 1 monitoring site(s) (105SH1452) |
Temporal Representation: |
The samples were collected between the dates of 2013-03-06 and 2013-11-20 |
Environmental Conditions: |
|
QAPP Information: |
Quality Assurance Program Plan and Standard Operating Procedures for SWAMP program |
QAPP Information Reference(s): |
Quality Assurance Program Plans, Quality Assurance Project Plans, and Standard Operating Procedures for the SWAMP program |
|
Line of Evidence (LOE) for Decision ID 168809, Ethoprop
|
Region 1 |
Klamath River HU, Shasta River HA |
|
|
LOE ID: |
123557 |
|
Pollutant: |
Ethoprop |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
None |
|
Beneficial Use: |
Municipal & Domestic Supply |
|
Number of Samples: |
0 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
State Water Board staff re-assessed SWAMP data for Klamath River HU, Shasta River HA to determine beneficial use support and results are as follows: 0 of 0 samples exceed the criterion for Ethoprop, Total. Four samples were removed from assessment because an appropriate evaluation guideline for the water body-pollutant combination could not be obtained for this listing cycle. This LOE re-assesses data from LOE 29849 from the 2010 Integrated Report. Data were re-assessed in order to evaluate these data in their own LOE, instead of being evaluated in the same LOE as other pesticide data. |
Data Reference: |
Surface Water Ambient Monitoring Program (SWAMP). Summary Report for the North Coast Region (RWQCB-1) for years 2000-2006. North Coast Regional Water Quality Control Board. March 2008 |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
Per the Basin Plan (NCRWQCB 2011): No individual pesticide or combination of pesticides shall be present in concentrations that adversely affect beneficial uses. There shall be no bioaccumulation of pesticide concentrations found in bottom sediments or aquatic life. Waters designated for use as domestic or municipal supply shall not contain concentrations of pesticides in excess of the limiting concentrations set forth in California Code of Regulations, Title 22, Division 4, Chapter 15, Article 4, Section 64444, and listed in Table 3.2 of the Basin Plan. No evaluation guideline could be found to evaluate protection of the MUN beneficial use that meets the requirements of Section 6.1.3 of the Listing Policy. |
Objective/Criterion Reference: |
Water Quality Control Plan (Basin Plan) for the North Coast Region |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
Data for this line of evidence for Klamath River HU, Shasta River HA was collected at 1 monitoring site [ Yreka Creek at Highway 3 - 105YREHW3] |
Temporal Representation: |
Data was collected over the time period 10/21/2004-6/20/2005. |
Environmental Conditions: |
There are no known environmental conditions (e.g., seasonality, land use practices, fire events, storms, etc.) that are related to these data. |
QAPP Information: |
Quality control was conducted in accordance with the SWAMP Quality Assurance Management Plan (SWAMP 2002). |
QAPP Information Reference(s): |
Quality Assurance Management Plan for the State of California's Surface Water Ambient Monitoring Program. Sacramento, CA. State Water Resources Control Board. SWAMP. December 2002 (1st version)
|
|
Line of Evidence (LOE) for Decision ID 168809, Ethoprop
|
Region 1 |
Klamath River HU, Shasta River HA |
|
|
LOE ID: |
123556 |
|
Pollutant: |
Ethoprop |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
None |
|
Beneficial Use: |
Municipal & Domestic Supply |
|
Number of Samples: |
0 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
State Water Board staff re-assessed SWAMP data for Klamath River HU, Shasta River HA to determine beneficial use support and results are as follows: 0 of 0 samples exceed the criterion for Ethoprop, Total. Eight samples were removed from assessment because an appropriate evaluation guideline for the water body-pollutant combination could not be obtained for this listing cycle. This LOE re-assesses data from LOE 29849 from the 2010 Integrated Report. Data were re-assessed in order to evaluate these data in their own LOE, instead of being evaluated in the same LOE as other pesticide data. |
Data Reference: |
Surface Water Ambient Monitoring Program (SWAMP). Summary Report for the North Coast Region (RWQCB-1) for years 2000-2006. North Coast Regional Water Quality Control Board. March 2008 |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
Per the Basin Plan (NCRWQCB 2011): No individual pesticide or combination of pesticides shall be present in concentrations that adversely affect beneficial uses. There shall be no bioaccumulation of pesticide concentrations found in bottom sediments or aquatic life. Waters designated for use as domestic or municipal supply shall not contain concentrations of pesticides in excess of the limiting concentrations set forth in California Code of Regulations, Title 22, Division 4, Chapter 15, Article 4, Section 64444, and listed in Table 3.2 of the Basin Plan. No evaluation guideline could be found to evaluate protection of the MUN beneficial use that meets the requirements of Section 6.1.3 of the Listing Policy. |
Objective/Criterion Reference: |
Water Quality Control Plan (Basin Plan) for the North Coast Region |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
Data for this line of evidence for Klamath River HU, Shasta River HA was collected at 1 monitoring site [ Yreka Creek at Anderson Rd - 105YREAND] |
Temporal Representation: |
Data was collected over the time period 10/9/2002-6/20/2005. |
Environmental Conditions: |
There are no known environmental conditions (e.g., seasonality, land use practices, fire events, storms, etc.) that are related to these data. |
QAPP Information: |
Quality control was conducted in accordance with the SWAMP Quality Assurance Management Plan (SWAMP 2002). |
QAPP Information Reference(s): |
Quality Assurance Management Plan for the State of California's Surface Water Ambient Monitoring Program. Sacramento, CA. State Water Resources Control Board. SWAMP. December 2002 (1st version)
|
|
Line of Evidence (LOE) for Decision ID 168809, Ethoprop
|
Region 1 |
Klamath River HU, Shasta River HA |
|
|
LOE ID: |
123555 |
|
Pollutant: |
Ethoprop |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
None |
|
Beneficial Use: |
Municipal & Domestic Supply |
|
Number of Samples: |
0 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
State Water Board staff re-assessed SWAMP data for Klamath River HU, Shasta River HA to determine beneficial use support and results are as follows: 0 of 0 samples exceed the criterion for Ethoprop, Total. Four samples were removed from assessment because an appropriate evaluation guideline for the water body-pollutant combination could not be obtained for this listing cycle. This LOE re-assesses data from LOE 29849 from the 2010 Integrated Report. Data were re-assessed in order to evaluate these data in their own LOE, instead of being evaluated in the same LOE as other pesticide data. |
Data Reference: |
Surface Water Ambient Monitoring Program (SWAMP). Summary Report for the North Coast Region (RWQCB-1) for years 2000-2006. North Coast Regional Water Quality Control Board. March 2008 |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
Per the Basin Plan (NCRWQCB 2011): No individual pesticide or combination of pesticides shall be present in concentrations that adversely affect beneficial uses. There shall be no bioaccumulation of pesticide concentrations found in bottom sediments or aquatic life. Waters designated for use as domestic or municipal supply shall not contain concentrations of pesticides in excess of the limiting concentrations set forth in California Code of Regulations, Title 22, Division 4, Chapter 15, Article 4, Section 64444, and listed in Table 3.2 of the Basin Plan. No evaluation guideline could be found to evaluate protection of the MUN beneficial use that meets the requirements of Section 6.1.3 of the Listing Policy. |
Objective/Criterion Reference: |
Water Quality Control Plan (Basin Plan) for the North Coast Region |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
Data for this line of evidence for Klamath River HU, Shasta River HA was collected at 1 monitoring site [ Shasta River near Edgewood - 105SH9274] |
Temporal Representation: |
Data was collected over the time period 10/7/2002-6/19/2003. |
Environmental Conditions: |
There are no known environmental conditions (e.g., seasonality, land use practices, fire events, storms, etc.) that are related to these data. |
QAPP Information: |
Quality control was conducted in accordance with the SWAMP Quality Assurance Management Plan (SWAMP 2002). |
QAPP Information Reference(s): |
Quality Assurance Management Plan for the State of California's Surface Water Ambient Monitoring Program. Sacramento, CA. State Water Resources Control Board. SWAMP. December 2002 (1st version)
|
|
Line of Evidence (LOE) for Decision ID 168809, Ethoprop
|
Region 1 |
Klamath River HU, Shasta River HA |
|
|
LOE ID: |
109528 |
|
Pollutant: |
Ethoprop |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Total |
|
Beneficial Use: |
Cold Freshwater Habitat |
|
Number of Samples: |
3 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP RWB1 Monitoring data for Klamath River HU, Shasta River HA to determine beneficial use support and results are as follows: 0 of 3 samples exceeded the water quality standard for Ethoprop. |
Data Reference: |
Water Quality Assessment Data for the 2018 solicitation cycle submitted through CEDEN for SWAMP RWB1 Monitoring .
|
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
All waters shall be maintained free of toxic substances in concentrations which are toxic to, or which produce detrimental physiological responses in, human, plant, animal, or aquatic life. (Basin Plan). |
Objective/Criterion Reference: |
Water Quality Control Plan (Basin Plan) for the North Coast Region |
|
Evaluation Guideline: |
The evaluation guideline for Ethoprop is the USEPA Aquatic Life Benchmark of 0.8 ug/L for an invertebrate (chronic). |
Guideline Reference: |
OPP Aquatic Life Benchmarks |
|
Spatial Representation: |
The samples were collected at 1 monitoring site(s) (105SH9274) |
Temporal Representation: |
The samples were collected between the dates of 2013-03-07 and 2013-11-20 |
Environmental Conditions: |
|
QAPP Information: |
Quality Assurance Program Plan and Standard Operating Procedures for SWAMP program |
QAPP Information Reference(s): |
Quality Assurance Program Plans, Quality Assurance Project Plans, and Standard Operating Procedures for the SWAMP program |
|
Line of Evidence (LOE) for Decision ID 168809, Ethoprop
|
Region 1 |
Klamath River HU, Shasta River HA |
|
|
LOE ID: |
109529 |
|
Pollutant: |
Ethoprop |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Total |
|
Beneficial Use: |
Warm Freshwater Habitat |
|
Number of Samples: |
3 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP RWB1 Monitoring data for Klamath River HU, Shasta River HA to determine beneficial use support and results are as follows: 0 of 3 samples exceeded the water quality standard for Ethoprop. |
Data Reference: |
Water Quality Assessment Data for the 2018 solicitation cycle submitted through CEDEN for SWAMP RWB1 Monitoring .
|
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
All waters shall be maintained free of toxic substances in concentrations which are toxic to, or which produce detrimental physiological responses in, human, plant, animal, or aquatic life. (Basin Plan). |
Objective/Criterion Reference: |
Water Quality Control Plan (Basin Plan) for the North Coast Region |
|
Evaluation Guideline: |
The evaluation guideline for Ethoprop is the USEPA Aquatic Life Benchmark of 0.8 ug/L for an invertebrate (chronic). |
Guideline Reference: |
OPP Aquatic Life Benchmarks |
|
Spatial Representation: |
The samples were collected at 1 monitoring site(s) (105SH9274) |
Temporal Representation: |
The samples were collected between the dates of 2013-03-07 and 2013-11-20 |
Environmental Conditions: |
|
QAPP Information: |
Quality Assurance Program Plan and Standard Operating Procedures for SWAMP program |
QAPP Information Reference(s): |
Quality Assurance Program Plans, Quality Assurance Project Plans, and Standard Operating Procedures for the SWAMP program |
|
Line of Evidence (LOE) for Decision ID 168809, Ethoprop
|
Region 1 |
Klamath River HU, Shasta River HA |
|
|
LOE ID: |
123554 |
|
Pollutant: |
Ethoprop |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
None |
|
Beneficial Use: |
Municipal & Domestic Supply |
|
Number of Samples: |
0 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
State Water Board staff re-assessed SWAMP data for Klamath River HU, Shasta River HA to determine beneficial use support and results are as follows: 0 of 0 samples exceed the criterion for Ethoprop, Total. Four samples were removed from assessment because an appropriate evaluation guideline for the water body-pollutant combination could not be obtained for this listing cycle. This LOE re-assesses data from LOE 29849 from the 2010 Integrated Report. Data were re-assessed in order to evaluate these data in their own LOE, instead of being evaluated in the same LOE as other pesticide data. |
Data Reference: |
Surface Water Ambient Monitoring Program (SWAMP). Summary Report for the North Coast Region (RWQCB-1) for years 2000-2006. North Coast Regional Water Quality Control Board. March 2008 |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
Per the Basin Plan (NCRWQCB 2011): No individual pesticide or combination of pesticides shall be present in concentrations that adversely affect beneficial uses. There shall be no bioaccumulation of pesticide concentrations found in bottom sediments or aquatic life. Waters designated for use as domestic or municipal supply shall not contain concentrations of pesticides in excess of the limiting concentrations set forth in California Code of Regulations, Title 22, Division 4, Chapter 15, Article 4, Section 64444, and listed in Table 3.2 of the Basin Plan. No evaluation guideline could be found to evaluate protection of the MUN beneficial use that meets the requirements of Section 6.1.3 of the Listing Policy. |
Objective/Criterion Reference: |
Water Quality Control Plan (Basin Plan) for the North Coast Region |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
Data for this line of evidence for Klamath River HU, Shasta River HA was collected at 1 monitoring site [ Shasta River at Montague - 105SHAMON] |
Temporal Representation: |
Data was collected over the time period 10/7/2002-6/19/2003. |
Environmental Conditions: |
There are no known environmental conditions (e.g., seasonality, land use practices, fire events, storms, etc.) that are related to these data. |
QAPP Information: |
Quality control was conducted in accordance with the SWAMP Quality Assurance Management Plan (SWAMP 2002). |
QAPP Information Reference(s): |
Quality Assurance Management Plan for the State of California's Surface Water Ambient Monitoring Program. Sacramento, CA. State Water Resources Control Board. SWAMP. December 2002 (1st version)
|
|
Line of Evidence (LOE) for Decision ID 168813, Fenitrothion
|
Region 1 |
Klamath River HU, Shasta River HA |
|
|
LOE ID: |
123571 |
|
Pollutant: |
Fenitrothion |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
None |
|
Beneficial Use: |
Municipal & Domestic Supply |
|
Number of Samples: |
0 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
State Water Board staff re-assessed SWAMP data for Klamath River HU, Shasta River HA to determine beneficial use support and results are as follows: 0 of 0 samples exceed the criterion for Fenitrothion, Total. Eight samples were removed from assessment because an appropriate evaluation guideline for the water body-pollutant combination could not be obtained for this listing cycle. This LOE re-assesses data from LOE 29849 from the 2010 Integrated Report. Data were re-assessed in order to evaluate these data in their own LOE, instead of being evaluated in the same LOE as other pesticide data. |
Data Reference: |
Surface Water Ambient Monitoring Program (SWAMP). Summary Report for the North Coast Region (RWQCB-1) for years 2000-2006. North Coast Regional Water Quality Control Board. March 2008 |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
Per the Basin Plan (NCRWQCB 2011): No individual pesticide or combination of pesticides shall be present in concentrations that adversely affect beneficial uses. There shall be no bioaccumulation of pesticide concentrations found in bottom sediments or aquatic life. Waters designated for use as domestic or municipal supply shall not contain concentrations of pesticides in excess of the limiting concentrations set forth in California Code of Regulations, Title 22, Division 4, Chapter 15, Article 4, Section 64444, and listed in Table 3.2 of the Basin Plan. No evaluation guideline could be found to evaluate protection of the MUN beneficial use that meets the requirements of Section 6.1.3 of the Listing Policy. |
Objective/Criterion Reference: |
Water Quality Control Plan (Basin Plan) for the North Coast Region |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
Data for this line of evidence for Klamath River HU, Shasta River HA was collected at 1 monitoring site [ Yreka Creek at Anderson Rd - 105YREAND] |
Temporal Representation: |
Data was collected over the time period 10/9/2002-6/20/2005. |
Environmental Conditions: |
There are no known environmental conditions (e.g., seasonality, land use practices, fire events, storms, etc.) that are related to these data. |
QAPP Information: |
Quality control was conducted in accordance with the SWAMP Quality Assurance Management Plan (SWAMP 2002). |
QAPP Information Reference(s): |
Quality Assurance Management Plan for the State of California's Surface Water Ambient Monitoring Program. Sacramento, CA. State Water Resources Control Board. SWAMP. December 2002 (1st version)
|
|
Line of Evidence (LOE) for Decision ID 168813, Fenitrothion
|
Region 1 |
Klamath River HU, Shasta River HA |
|
|
LOE ID: |
103611 |
|
Pollutant: |
Fenitrothion |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Total |
|
Beneficial Use: |
Warm Freshwater Habitat |
|
Number of Samples: |
3 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP RWB1 Monitoring data for Klamath River HU, Shasta River HA to determine beneficial use support and results are as follows: 0 of 3 samples exceeded the water quality standard for Fenitrothion. |
Data Reference: |
Water Quality Assessment Data for the 2018 solicitation cycle submitted through CEDEN for SWAMP RWB1 Monitoring .
|
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
All waters shall be maintained free of toxic substances in concentrations which are toxic to, or which produce detrimental physiological responses in, human, plant, animal, or aquatic life. (Basin Plan). |
Objective/Criterion Reference: |
Water Quality Control Plan (Basin Plan) for the North Coast Region |
|
Evaluation Guideline: |
The evaluation guideline for Fenitrothion is the USEPA Aquatic Life Benchmark of 0.087 ug/L for an invertebrate (chronic). |
Guideline Reference: |
OPP Aquatic Life Benchmarks |
|
Spatial Representation: |
The samples were collected at 1 monitoring site(s) (105SH9274) |
Temporal Representation: |
The samples were collected between the dates of 2013-03-07 and 2013-11-20 |
Environmental Conditions: |
|
QAPP Information: |
Quality Assurance Program Plan and Standard Operating Procedures for SWAMP program |
QAPP Information Reference(s): |
Quality Assurance Program Plans, Quality Assurance Project Plans, and Standard Operating Procedures for the SWAMP program |
|
Line of Evidence (LOE) for Decision ID 168813, Fenitrothion
|
Region 1 |
Klamath River HU, Shasta River HA |
|
|
LOE ID: |
108052 |
|
Pollutant: |
Fenitrothion |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Total |
|
Beneficial Use: |
Cold Freshwater Habitat |
|
Number of Samples: |
3 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP RWB1 Monitoring data for Klamath River HU, Shasta River HA to determine beneficial use support and results are as follows: 0 of 3 samples exceeded the water quality standard for Fenitrothion. |
Data Reference: |
Water Quality Assessment Data for the 2018 solicitation cycle submitted through CEDEN for SWAMP RWB1 Monitoring .
|
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
All waters shall be maintained free of toxic substances in concentrations which are toxic to, or which produce detrimental physiological responses in, human, plant, animal, or aquatic life. (Basin Plan). |
Objective/Criterion Reference: |
Water Quality Control Plan (Basin Plan) for the North Coast Region |
|
Evaluation Guideline: |
The evaluation guideline for Fenitrothion is the USEPA Aquatic Life Benchmark of 0.087 ug/L for an invertebrate (chronic). |
Guideline Reference: |
OPP Aquatic Life Benchmarks |
|
Spatial Representation: |
The samples were collected at 1 monitoring site(s) (105SH9274) |
Temporal Representation: |
The samples were collected between the dates of 2013-03-07 and 2013-11-20 |
Environmental Conditions: |
|
QAPP Information: |
Quality Assurance Program Plan and Standard Operating Procedures for SWAMP program |
QAPP Information Reference(s): |
Quality Assurance Program Plans, Quality Assurance Project Plans, and Standard Operating Procedures for the SWAMP program |
|
Line of Evidence (LOE) for Decision ID 168813, Fenitrothion
|
Region 1 |
Klamath River HU, Shasta River HA |
|
|
LOE ID: |
123568 |
|
Pollutant: |
Fenitrothion |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
None |
|
Beneficial Use: |
Municipal & Domestic Supply |
|
Number of Samples: |
0 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
State Water Board staff re-assessed SWAMP data for Klamath River HU, Shasta River HA to determine beneficial use support and results are as follows: 0 of 0 samples exceed the criterion for Fenitrothion, Total. Sixteen samples were removed from assessment because an appropriate evaluation guideline for the water body-pollutant combination could not be obtained for this listing cycle. This LOE re-assesses data from LOE 29849 from the 2010 Integrated Report. Data were re-assessed in order to evaluate these data in their own LOE, instead of being evaluated in the same LOE as other pesticide data. |
Data Reference: |
Surface Water Ambient Monitoring Program (SWAMP). Summary Report for the North Coast Region (RWQCB-1) for years 2000-2006. North Coast Regional Water Quality Control Board. March 2008 |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
Per the Basin Plan (NCRWQCB 2011): No individual pesticide or combination of pesticides shall be present in concentrations that adversely affect beneficial uses. There shall be no bioaccumulation of pesticide concentrations found in bottom sediments or aquatic life. Waters designated for use as domestic or municipal supply shall not contain concentrations of pesticides in excess of the limiting concentrations set forth in California Code of Regulations, Title 22, Division 4, Chapter 15, Article 4, Section 64444, and listed in Table 3.2 of the Basin Plan. No evaluation guideline could be found to evaluate protection of the MUN beneficial use that meets the requirements of Section 6.1.3 of the Listing Policy. |
Objective/Criterion Reference: |
Water Quality Control Plan (Basin Plan) for the North Coast Region |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
Data for this line of evidence for Klamath River HU, Shasta River HA was collected at 1 monitoring site [ Shasta River at Hwy 263 - 105SH1452] |
Temporal Representation: |
Data was collected over the time period 2/27/2002-11/16/2006. |
Environmental Conditions: |
There are no known environmental conditions (e.g., seasonality, land use practices, fire events, storms, etc.) that are related to these data. |
QAPP Information: |
Quality control was conducted in accordance with the SWAMP Quality Assurance Management Plan (SWAMP 2002). |
QAPP Information Reference(s): |
Quality Assurance Management Plan for the State of California's Surface Water Ambient Monitoring Program. Sacramento, CA. State Water Resources Control Board. SWAMP. December 2002 (1st version)
|
|
Line of Evidence (LOE) for Decision ID 168813, Fenitrothion
|
Region 1 |
Klamath River HU, Shasta River HA |
|
|
LOE ID: |
109531 |
|
Pollutant: |
Fenitrothion |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Total |
|
Beneficial Use: |
Cold Freshwater Habitat |
|
Number of Samples: |
3 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP RWB1 Monitoring data for Klamath River HU, Shasta River HA to determine beneficial use support and results are as follows: 0 of 3 samples exceeded the water quality standard for Fenitrothion. |
Data Reference: |
Water Quality Assessment Data for the 2018 solicitation cycle submitted through CEDEN for SWAMP RWB1 Monitoring .
|
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
All waters shall be maintained free of toxic substances in concentrations which are toxic to, or which produce detrimental physiological responses in, human, plant, animal, or aquatic life. (Basin Plan). |
Objective/Criterion Reference: |
Water Quality Control Plan (Basin Plan) for the North Coast Region |
|
Evaluation Guideline: |
The evaluation guideline for Fenitrothion is the USEPA Aquatic Life Benchmark of 0.087 ug/L for an invertebrate (chronic). |
Guideline Reference: |
OPP Aquatic Life Benchmarks |
|
Spatial Representation: |
The samples were collected at 1 monitoring site(s) (105SH1452) |
Temporal Representation: |
The samples were collected between the dates of 2013-03-06 and 2013-11-20 |
Environmental Conditions: |
|
QAPP Information: |
Quality Assurance Program Plan and Standard Operating Procedures for SWAMP program |
QAPP Information Reference(s): |
Quality Assurance Program Plans, Quality Assurance Project Plans, and Standard Operating Procedures for the SWAMP program |
|
Line of Evidence (LOE) for Decision ID 168813, Fenitrothion
|
Region 1 |
Klamath River HU, Shasta River HA |
|
|
LOE ID: |
109532 |
|
Pollutant: |
Fenitrothion |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Total |
|
Beneficial Use: |
Warm Freshwater Habitat |
|
Number of Samples: |
3 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP RWB1 Monitoring data for Klamath River HU, Shasta River HA to determine beneficial use support and results are as follows: 0 of 3 samples exceeded the water quality standard for Fenitrothion. |
Data Reference: |
Water Quality Assessment Data for the 2018 solicitation cycle submitted through CEDEN for SWAMP RWB1 Monitoring .
|
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
All waters shall be maintained free of toxic substances in concentrations which are toxic to, or which produce detrimental physiological responses in, human, plant, animal, or aquatic life. (Basin Plan). |
Objective/Criterion Reference: |
Water Quality Control Plan (Basin Plan) for the North Coast Region |
|
Evaluation Guideline: |
The evaluation guideline for Fenitrothion is the USEPA Aquatic Life Benchmark of 0.087 ug/L for an invertebrate (chronic). |
Guideline Reference: |
OPP Aquatic Life Benchmarks |
|
Spatial Representation: |
The samples were collected at 1 monitoring site(s) (105SH1452) |
Temporal Representation: |
The samples were collected between the dates of 2013-03-06 and 2013-11-20 |
Environmental Conditions: |
|
QAPP Information: |
Quality Assurance Program Plan and Standard Operating Procedures for SWAMP program |
QAPP Information Reference(s): |
Quality Assurance Program Plans, Quality Assurance Project Plans, and Standard Operating Procedures for the SWAMP program |
|
Line of Evidence (LOE) for Decision ID 168813, Fenitrothion
|
Region 1 |
Klamath River HU, Shasta River HA |
|
|
LOE ID: |
123569 |
|
Pollutant: |
Fenitrothion |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
None |
|
Beneficial Use: |
Municipal & Domestic Supply |
|
Number of Samples: |
0 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
State Water Board staff re-assessed SWAMP data for Klamath River HU, Shasta River HA to determine beneficial use support and results are as follows: 0 of 0 samples exceed the criterion for Fenitrothion, Total. Four samples were removed from assessment because an appropriate evaluation guideline for the water body-pollutant combination could not be obtained for this listing cycle. This LOE re-assesses data from LOE 29849 from the 2010 Integrated Report. Data were re-assessed in order to evaluate these data in their own LOE, instead of being evaluated in the same LOE as other pesticide data. |
Data Reference: |
Surface Water Ambient Monitoring Program (SWAMP). Summary Report for the North Coast Region (RWQCB-1) for years 2000-2006. North Coast Regional Water Quality Control Board. March 2008 |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
Per the Basin Plan (NCRWQCB 2011): No individual pesticide or combination of pesticides shall be present in concentrations that adversely affect beneficial uses. There shall be no bioaccumulation of pesticide concentrations found in bottom sediments or aquatic life. Waters designated for use as domestic or municipal supply shall not contain concentrations of pesticides in excess of the limiting concentrations set forth in California Code of Regulations, Title 22, Division 4, Chapter 15, Article 4, Section 64444, and listed in Table 3.2 of the Basin Plan. No evaluation guideline could be found to evaluate protection of the MUN beneficial use that meets the requirements of Section 6.1.3 of the Listing Policy. |
Objective/Criterion Reference: |
Water Quality Control Plan (Basin Plan) for the North Coast Region |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
Data for this line of evidence for Klamath River HU, Shasta River HA was collected at 1 monitoring site [ Shasta River at Montague - 105SHAMON] |
Temporal Representation: |
Data was collected over the time period 10/7/2002-6/19/2003. |
Environmental Conditions: |
There are no known environmental conditions (e.g., seasonality, land use practices, fire events, storms, etc.) that are related to these data. |
QAPP Information: |
Quality control was conducted in accordance with the SWAMP Quality Assurance Management Plan (SWAMP 2002). |
QAPP Information Reference(s): |
Quality Assurance Management Plan for the State of California's Surface Water Ambient Monitoring Program. Sacramento, CA. State Water Resources Control Board. SWAMP. December 2002 (1st version)
|
|
Line of Evidence (LOE) for Decision ID 168813, Fenitrothion
|
Region 1 |
Klamath River HU, Shasta River HA |
|
|
LOE ID: |
123530 |
|
Pollutant: |
Fenitrothion |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
None |
|
Beneficial Use: |
Municipal & Domestic Supply |
|
Number of Samples: |
0 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
State Water Board staff re-assessed SWAMP data for Klamath River HU, Shasta River HA to determine beneficial use support and results are as follows: 0 of 0 samples exceed the criterion for Fenitrothion, Total. Four samples were removed from assessment because an appropriate evaluation guideline for the water body-pollutant combination could not be obtained for this listing cycle. This LOE re-assesses data from LOE 29849 from the 2010 Integrated Report. Data were re-assessed in order to evaluate these data in their own LOE, instead of being evaluated in the same LOE as other pesticide data. |
Data Reference: |
Surface Water Ambient Monitoring Program (SWAMP). Summary Report for the North Coast Region (RWQCB-1) for years 2000-2006. North Coast Regional Water Quality Control Board. March 2008 |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
Per the Basin Plan (NCRWQCB 2011): No individual pesticide or combination of pesticides shall be present in concentrations that adversely affect beneficial uses. There shall be no bioaccumulation of pesticide concentrations found in bottom sediments or aquatic life. Waters designated for use as domestic or municipal supply shall not contain concentrations of pesticides in excess of the limiting concentrations set forth in California Code of Regulations, Title 22, Division 4, Chapter 15, Article 4, Section 64444, and listed in Table 3.2 of the Basin Plan. No evaluation guideline could be found to evaluate protection of the MUN beneficial use that meets the requirements of Section 6.1.3 of the Listing Policy. |
Objective/Criterion Reference: |
Water Quality Control Plan (Basin Plan) for the North Coast Region |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
Data for this line of evidence for Klamath River HU, Shasta River HA was collected at 1 monitoring site [ Yreka Creek at Highway 3 - 105YREHW3] |
Temporal Representation: |
Data was collected over the time period 10/21/2004-6/20/2005. |
Environmental Conditions: |
There are no known environmental conditions (e.g., seasonality, land use practices, fire events, storms, etc.) that are related to these data. |
QAPP Information: |
Quality control was conducted in accordance with the SWAMP Quality Assurance Management Plan (SWAMP 2002). |
QAPP Information Reference(s): |
Quality Assurance Management Plan for the State of California's Surface Water Ambient Monitoring Program. Sacramento, CA. State Water Resources Control Board. SWAMP. December 2002 (1st version)
|
|
Line of Evidence (LOE) for Decision ID 168813, Fenitrothion
|
Region 1 |
Klamath River HU, Shasta River HA |
|
|
LOE ID: |
123570 |
|
Pollutant: |
Fenitrothion |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
None |
|
Beneficial Use: |
Municipal & Domestic Supply |
|
Number of Samples: |
0 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
State Water Board staff re-assessed SWAMP data for Klamath River HU, Shasta River HA to determine beneficial use support and results are as follows: 0 of 0 samples exceed the criterion for Fenitrothion, Total. Four samples were removed from assessment because an appropriate evaluation guideline for the water body-pollutant combination could not be obtained for this listing cycle. This LOE re-assesses data from LOE 29849 from the 2010 Integrated Report. Data were re-assessed in order to evaluate these data in their own LOE, instead of being evaluated in the same LOE as other pesticide data. |
Data Reference: |
Surface Water Ambient Monitoring Program (SWAMP). Summary Report for the North Coast Region (RWQCB-1) for years 2000-2006. North Coast Regional Water Quality Control Board. March 2008 |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
Per the Basin Plan (NCRWQCB 2011): No individual pesticide or combination of pesticides shall be present in concentrations that adversely affect beneficial uses. There shall be no bioaccumulation of pesticide concentrations found in bottom sediments or aquatic life. Waters designated for use as domestic or municipal supply shall not contain concentrations of pesticides in excess of the limiting concentrations set forth in California Code of Regulations, Title 22, Division 4, Chapter 15, Article 4, Section 64444, and listed in Table 3.2 of the Basin Plan. No evaluation guideline could be found to evaluate protection of the MUN beneficial use that meets the requirements of Section 6.1.3 of the Listing Policy. |
Objective/Criterion Reference: |
Water Quality Control Plan (Basin Plan) for the North Coast Region |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
Data for this line of evidence for Klamath River HU, Shasta River HA was collected at 1 monitoring site [ Shasta River near Edgewood - 105SH9274] |
Temporal Representation: |
Data was collected over the time period 10/7/2002-6/19/2003. |
Environmental Conditions: |
There are no known environmental conditions (e.g., seasonality, land use practices, fire events, storms, etc.) that are related to these data. |
QAPP Information: |
Quality control was conducted in accordance with the SWAMP Quality Assurance Management Plan (SWAMP 2002). |
QAPP Information Reference(s): |
Quality Assurance Management Plan for the State of California's Surface Water Ambient Monitoring Program. Sacramento, CA. State Water Resources Control Board. SWAMP. December 2002 (1st version)
|
|
Line of Evidence (LOE) for Decision ID 168815, Fenthion
|
Region 1 |
Klamath River HU, Shasta River HA |
|
|
LOE ID: |
116093 |
|
Pollutant: |
Fenthion |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Total |
|
Beneficial Use: |
Warm Freshwater Habitat |
|
Number of Samples: |
0 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP RWB1 Monitoring data for Klamath River HU, Shasta River HA to determine beneficial use support, and the results are as follows: 0 of the 0 samples exceeded the evaluation guideline for Fenthion. Although a total of 2 samples were collected, 2 of these samples were not included in the assessment because the laboratory data reporting limit(s) was above the objective and therefore the results could not be quantified with the level of certainty required by the Listing Policy Section 6.1.5.5. |
Data Reference: |
Water Quality Assessment Data for the 2018 solicitation cycle submitted through CEDEN for SWAMP RWB1 Monitoring .
|
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
All waters shall be maintained free of toxic substances in concentrations which are toxic to, or which produce detrimental physiological responses in, human, plant, animal, or aquatic life. (Basin Plan). |
Objective/Criterion Reference: |
Water Quality Control Plan (Basin Plan) for the North Coast Region |
|
Evaluation Guideline: |
The evaluation guideline for Fenthion is the USEPA Aquatic Life Benchmark of 0.013 ug/L for an invertebrate (chronic). |
Guideline Reference: |
OPP Aquatic Life Benchmarks |
|
Spatial Representation: |
Data was collected from 1 station(s) (Station Code(s) 105SH9274). |
Temporal Representation: |
Date for this waterbody was collected over the date range 2013-03-07 to 2013-04-29 |
Environmental Conditions: |
|
QAPP Information: |
Quality Assurance Program Plan and Standard Operating Procedures for SWAMP program |
QAPP Information Reference(s): |
Quality Assurance Program Plans, Quality Assurance Project Plans, and Standard Operating Procedures for the SWAMP program |
|
Line of Evidence (LOE) for Decision ID 168815, Fenthion
|
Region 1 |
Klamath River HU, Shasta River HA |
|
|
LOE ID: |
106137 |
|
Pollutant: |
Fenthion |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Total |
|
Beneficial Use: |
Cold Freshwater Habitat |
|
Number of Samples: |
0 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP RWB1 Monitoring data for Klamath River HU, Shasta River HA to determine beneficial use support, and the results are as follows: 0 of the 0 samples exceeded the evaluation guideline for Fenthion. Although a total of 2 samples were collected, 2 of these samples were not included in the assessment because the laboratory data reporting limit(s) was above the objective and therefore the results could not be quantified with the level of certainty required by the Listing Policy Section 6.1.5.5. |
Data Reference: |
Water Quality Assessment Data for the 2018 solicitation cycle submitted through CEDEN for SWAMP RWB1 Monitoring .
|
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
All waters shall be maintained free of toxic substances in concentrations which are toxic to, or which produce detrimental physiological responses in, human, plant, animal, or aquatic life. (Basin Plan). |
Objective/Criterion Reference: |
Water Quality Control Plan (Basin Plan) for the North Coast Region |
|
Evaluation Guideline: |
The evaluation guideline for Fenthion is the USEPA Aquatic Life Benchmark of 0.013 ug/L for an invertebrate (chronic). |
Guideline Reference: |
OPP Aquatic Life Benchmarks |
|
Spatial Representation: |
Data was collected from 1 station(s) (Station Code(s) 105SH1452). |
Temporal Representation: |
Date for this waterbody was collected over the date range 2013-03-06 to 2013-04-29 |
Environmental Conditions: |
|
QAPP Information: |
Quality Assurance Program Plan and Standard Operating Procedures for SWAMP program |
QAPP Information Reference(s): |
Quality Assurance Program Plans, Quality Assurance Project Plans, and Standard Operating Procedures for the SWAMP program |
|
Line of Evidence (LOE) for Decision ID 168815, Fenthion
|
Region 1 |
Klamath River HU, Shasta River HA |
|
|
LOE ID: |
123430 |
|
Pollutant: |
Fenthion |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
None |
|
Beneficial Use: |
Municipal & Domestic Supply |
|
Number of Samples: |
0 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
State Water Board staff re-assessed SWAMP data for Klamath River HU, Shasta River HA to determine beneficial use support and results are as follows: 0 of 0 samples exceed the criterion for Fenthion, Total. Four samples were removed from assessment because an appropriate evaluation guideline for the water body-pollutant combination could not be obtained for this listing cycle. This LOE re-assesses data from LOE 29849 from the 2010 Integrated Report. Data were re-assessed in order to evaluate these data in their own LOE, instead of being evaluated in the same LOE as other pesticide data. |
Data Reference: |
Surface Water Ambient Monitoring Program (SWAMP). Summary Report for the North Coast Region (RWQCB-1) for years 2000-2006. North Coast Regional Water Quality Control Board. March 2008 |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
Per the Basin Plan (NCRWQCB 2011): No individual pesticide or combination of pesticides shall be present in concentrations that adversely affect beneficial uses. There shall be no bioaccumulation of pesticide concentrations found in bottom sediments or aquatic life. Waters designated for use as domestic or municipal supply shall not contain concentrations of pesticides in excess of the limiting concentrations set forth in California Code of Regulations, Title 22, Division 4, Chapter 15, Article 4, Section 64444, and listed in Table 3.2 of the Basin Plan. No evaluation guideline could be found to evaluate protection of the MUN beneficial use that meets the requirements of Section 6.1.3 of the Listing Policy. |
Objective/Criterion Reference: |
Water Quality Control Plan (Basin Plan) for the North Coast Region |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
Data for this line of evidence for Klamath River HU, Shasta River HA was collected at 1 monitoring site [ Shasta River near Edgewood - 105SH9274] |
Temporal Representation: |
Data was collected over the time period 10/7/2002-6/19/2003. |
Environmental Conditions: |
There are no known environmental conditions (e.g., seasonality, land use practices, fire events, storms, etc.) that are related to these data. |
QAPP Information: |
Quality control was conducted in accordance with the SWAMP Quality Assurance Management Plan (SWAMP 2002). |
QAPP Information Reference(s): |
Quality Assurance Management Plan for the State of California's Surface Water Ambient Monitoring Program. Sacramento, CA. State Water Resources Control Board. SWAMP. December 2002 (1st version)
|
|
Line of Evidence (LOE) for Decision ID 168815, Fenthion
|
Region 1 |
Klamath River HU, Shasta River HA |
|
|
LOE ID: |
123431 |
|
Pollutant: |
Fenthion |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
None |
|
Beneficial Use: |
Municipal & Domestic Supply |
|
Number of Samples: |
0 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
State Water Board staff re-assessed SWAMP data for Klamath River HU, Shasta River HA to determine beneficial use support and results are as follows: 0 of 0 samples exceed the criterion for Fenthion, Total. Eight samples were removed from assessment because an appropriate evaluation guideline for the water body-pollutant combination could not be obtained for this listing cycle. This LOE re-assesses data from LOE 29849 from the 2010 Integrated Report. Data were re-assessed in order to evaluate these data in their own LOE, instead of being evaluated in the same LOE as other pesticide data. |
Data Reference: |
Surface Water Ambient Monitoring Program (SWAMP). Summary Report for the North Coast Region (RWQCB-1) for years 2000-2006. North Coast Regional Water Quality Control Board. March 2008 |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
Per the Basin Plan (NCRWQCB 2011): No individual pesticide or combination of pesticides shall be present in concentrations that adversely affect beneficial uses. There shall be no bioaccumulation of pesticide concentrations found in bottom sediments or aquatic life. Waters designated for use as domestic or municipal supply shall not contain concentrations of pesticides in excess of the limiting concentrations set forth in California Code of Regulations, Title 22, Division 4, Chapter 15, Article 4, Section 64444, and listed in Table 3.2 of the Basin Plan. No evaluation guideline could be found to evaluate protection of the MUN beneficial use that meets the requirements of Section 6.1.3 of the Listing Policy. |
Objective/Criterion Reference: |
Water Quality Control Plan (Basin Plan) for the North Coast Region |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
Data for this line of evidence for Klamath River HU, Shasta River HA was collected at 1 monitoring site [ Yreka Creek at Anderson Rd - 105YREAND] |
Temporal Representation: |
Data was collected over the time period 10/9/2002-6/20/2005. |
Environmental Conditions: |
There are no known environmental conditions (e.g., seasonality, land use practices, fire events, storms, etc.) that are related to these data. |
QAPP Information: |
Quality control was conducted in accordance with the SWAMP Quality Assurance Management Plan (SWAMP 2002). |
QAPP Information Reference(s): |
Quality Assurance Management Plan for the State of California's Surface Water Ambient Monitoring Program. Sacramento, CA. State Water Resources Control Board. SWAMP. December 2002 (1st version)
|
|
Line of Evidence (LOE) for Decision ID 168815, Fenthion
|
Region 1 |
Klamath River HU, Shasta River HA |
|
|
LOE ID: |
123444 |
|
Pollutant: |
Fenthion |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
None |
|
Beneficial Use: |
Municipal & Domestic Supply |
|
Number of Samples: |
0 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
State Water Board staff re-assessed SWAMP data for Klamath River HU, Shasta River HA to determine beneficial use support and results are as follows: 0 of 0 samples exceed the criterion for Fenthion, Total. Four samples were removed from assessment because an appropriate evaluation guideline for the water body-pollutant combination could not be obtained for this listing cycle. This LOE re-assesses data from LOE 29849 from the 2010 Integrated Report. Data were re-assessed in order to evaluate these data in their own LOE, instead of being evaluated in the same LOE as other pesticide data. |
Data Reference: |
Surface Water Ambient Monitoring Program (SWAMP). Summary Report for the North Coast Region (RWQCB-1) for years 2000-2006. North Coast Regional Water Quality Control Board. March 2008 |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
Per the Basin Plan (NCRWQCB 2011): No individual pesticide or combination of pesticides shall be present in concentrations that adversely affect beneficial uses. There shall be no bioaccumulation of pesticide concentrations found in bottom sediments or aquatic life. Waters designated for use as domestic or municipal supply shall not contain concentrations of pesticides in excess of the limiting concentrations set forth in California Code of Regulations, Title 22, Division 4, Chapter 15, Article 4, Section 64444, and listed in Table 3.2 of the Basin Plan. No evaluation guideline could be found to evaluate protection of the MUN beneficial use that meets the requirements of Section 6.1.3 of the Listing Policy. |
Objective/Criterion Reference: |
Water Quality Control Plan (Basin Plan) for the North Coast Region |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
Data for this line of evidence for Klamath River HU, Shasta River HA was collected at 1 monitoring site [ Yreka Creek at Highway 3 - 105YREHW3] |
Temporal Representation: |
Data was collected over the time period 10/21/2004-6/20/2005. |
Environmental Conditions: |
There are no known environmental conditions (e.g., seasonality, land use practices, fire events, storms, etc.) that are related to these data. |
QAPP Information: |
Quality control was conducted in accordance with the SWAMP Quality Assurance Management Plan (SWAMP 2002). |
QAPP Information Reference(s): |
Quality Assurance Management Plan for the State of California's Surface Water Ambient Monitoring Program. Sacramento, CA. State Water Resources Control Board. SWAMP. December 2002 (1st version)
|
|
Line of Evidence (LOE) for Decision ID 168815, Fenthion
|
Region 1 |
Klamath River HU, Shasta River HA |
|
|
LOE ID: |
119100 |
|
Pollutant: |
Fenthion |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Total |
|
Beneficial Use: |
Warm Freshwater Habitat |
|
Number of Samples: |
0 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP RWB1 Monitoring data for Klamath River HU, Shasta River HA to determine beneficial use support, and the results are as follows: 0 of the 0 samples exceeded the evaluation guideline for Fenthion. Although a total of 2 samples were collected, 2 of these samples were not included in the assessment because the laboratory data reporting limit(s) was above the objective and therefore the results could not be quantified with the level of certainty required by the Listing Policy Section 6.1.5.5. |
Data Reference: |
Water Quality Assessment Data for the 2018 solicitation cycle submitted through CEDEN for SWAMP RWB1 Monitoring .
|
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
All waters shall be maintained free of toxic substances in concentrations which are toxic to, or which produce detrimental physiological responses in, human, plant, animal, or aquatic life. (Basin Plan). |
Objective/Criterion Reference: |
Water Quality Control Plan (Basin Plan) for the North Coast Region |
|
Evaluation Guideline: |
The evaluation guideline for Fenthion is the USEPA Aquatic Life Benchmark of 0.013 ug/L for an invertebrate (chronic). |
Guideline Reference: |
OPP Aquatic Life Benchmarks |
|
Spatial Representation: |
Data was collected from 1 station(s) (Station Code(s) 105SH1452). |
Temporal Representation: |
Date for this waterbody was collected over the date range 2013-03-06 to 2013-04-29 |
Environmental Conditions: |
|
QAPP Information: |
Quality Assurance Program Plan and Standard Operating Procedures for SWAMP program |
QAPP Information Reference(s): |
Quality Assurance Program Plans, Quality Assurance Project Plans, and Standard Operating Procedures for the SWAMP program |
|
Line of Evidence (LOE) for Decision ID 168815, Fenthion
|
Region 1 |
Klamath River HU, Shasta River HA |
|
|
LOE ID: |
123429 |
|
Pollutant: |
Fenthion |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
None |
|
Beneficial Use: |
Municipal & Domestic Supply |
|
Number of Samples: |
0 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
State Water Board staff re-assessed SWAMP data for Klamath River HU, Shasta River HA to determine beneficial use support and results are as follows: 0 of 0 samples exceed the criterion for Fenthion, Total. Four samples were removed from assessment because an appropriate evaluation guideline for the water body-pollutant combination could not be obtained for this listing cycle. This LOE re-assesses data from LOE 29849 from the 2010 Integrated Report. Data were re-assessed in order to evaluate these data in their own LOE, instead of being evaluated in the same LOE as other pesticide data. |
Data Reference: |
Surface Water Ambient Monitoring Program (SWAMP). Summary Report for the North Coast Region (RWQCB-1) for years 2000-2006. North Coast Regional Water Quality Control Board. March 2008 |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
Per the Basin Plan (NCRWQCB 2011): No individual pesticide or combination of pesticides shall be present in concentrations that adversely affect beneficial uses. There shall be no bioaccumulation of pesticide concentrations found in bottom sediments or aquatic life. Waters designated for use as domestic or municipal supply shall not contain concentrations of pesticides in excess of the limiting concentrations set forth in California Code of Regulations, Title 22, Division 4, Chapter 15, Article 4, Section 64444, and listed in Table 3.2 of the Basin Plan. No evaluation guideline could be found to evaluate protection of the MUN beneficial use that meets the requirements of Section 6.1.3 of the Listing Policy. |
Objective/Criterion Reference: |
Water Quality Control Plan (Basin Plan) for the North Coast Region |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
Data for this line of evidence for Klamath River HU, Shasta River HA was collected at 1 monitoring site [ Shasta River at Montague - 105SHAMON] |
Temporal Representation: |
Data was collected over the time period 10/7/2002-6/19/2003. |
Environmental Conditions: |
There are no known environmental conditions (e.g., seasonality, land use practices, fire events, storms, etc.) that are related to these data. |
QAPP Information: |
Quality control was conducted in accordance with the SWAMP Quality Assurance Management Plan (SWAMP 2002). |
QAPP Information Reference(s): |
Quality Assurance Management Plan for the State of California's Surface Water Ambient Monitoring Program. Sacramento, CA. State Water Resources Control Board. SWAMP. December 2002 (1st version)
|
|
Line of Evidence (LOE) for Decision ID 168815, Fenthion
|
Region 1 |
Klamath River HU, Shasta River HA |
|
|
LOE ID: |
111160 |
|
Pollutant: |
Fenthion |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Total |
|
Beneficial Use: |
Cold Freshwater Habitat |
|
Number of Samples: |
0 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP RWB1 Monitoring data for Klamath River HU, Shasta River HA to determine beneficial use support, and the results are as follows: 0 of the 0 samples exceeded the evaluation guideline for Fenthion. Although a total of 2 samples were collected, 2 of these samples were not included in the assessment because the laboratory data reporting limit(s) was above the objective and therefore the results could not be quantified with the level of certainty required by the Listing Policy Section 6.1.5.5. |
Data Reference: |
Water Quality Assessment Data for the 2018 solicitation cycle submitted through CEDEN for SWAMP RWB1 Monitoring .
|
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
All waters shall be maintained free of toxic substances in concentrations which are toxic to, or which produce detrimental physiological responses in, human, plant, animal, or aquatic life. (Basin Plan). |
Objective/Criterion Reference: |
Water Quality Control Plan (Basin Plan) for the North Coast Region |
|
Evaluation Guideline: |
The evaluation guideline for Fenthion is the USEPA Aquatic Life Benchmark of 0.013 ug/L for an invertebrate (chronic). |
Guideline Reference: |
OPP Aquatic Life Benchmarks |
|
Spatial Representation: |
Data was collected from 1 station(s) (Station Code(s) 105SH9274). |
Temporal Representation: |
Date for this waterbody was collected over the date range 2013-03-07 to 2013-04-29 |
Environmental Conditions: |
|
QAPP Information: |
Quality Assurance Program Plan and Standard Operating Procedures for SWAMP program |
QAPP Information Reference(s): |
Quality Assurance Program Plans, Quality Assurance Project Plans, and Standard Operating Procedures for the SWAMP program |
|
Line of Evidence (LOE) for Decision ID 168815, Fenthion
|
Region 1 |
Klamath River HU, Shasta River HA |
|
|
LOE ID: |
123417 |
|
Pollutant: |
Fenthion |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
None |
|
Beneficial Use: |
Municipal & Domestic Supply |
|
Number of Samples: |
0 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
State Water Board staff re-assessed SWAMP data for Klamath River HU, Shasta River HA to determine beneficial use support and results are as follows: 0 of 0 samples exceed the criterion for Fenthion, Total. Sixteen samples were removed from assessment because an appropriate evaluation guideline for the water body-pollutant combination could not be obtained for this listing cycle. This LOE re-assesses data from LOE 29849 from the 2010 Integrated Report. Data were re-assessed in order to evaluate these data in their own LOE, instead of being evaluated in the same LOE as other pesticide data. |
Data Reference: |
Surface Water Ambient Monitoring Program (SWAMP). Summary Report for the North Coast Region (RWQCB-1) for years 2000-2006. North Coast Regional Water Quality Control Board. March 2008 |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
Per the Basin Plan (NCRWQCB 2011): No individual pesticide or combination of pesticides shall be present in concentrations that adversely affect beneficial uses. There shall be no bioaccumulation of pesticide concentrations found in bottom sediments or aquatic life. Waters designated for use as domestic or municipal supply shall not contain concentrations of pesticides in excess of the limiting concentrations set forth in California Code of Regulations, Title 22, Division 4, Chapter 15, Article 4, Section 64444, and listed in Table 3.2 of the Basin Plan. No evaluation guideline could be found to evaluate protection of the MUN beneficial use that meets the requirements of Section 6.1.3 of the Listing Policy. |
Objective/Criterion Reference: |
Water Quality Control Plan (Basin Plan) for the North Coast Region |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
Data for this line of evidence for Klamath River HU, Shasta River HA was collected at 1 monitoring site [ Shasta River at Hwy 263 - 105SH1452] |
Temporal Representation: |
Data was collected over the time period 2/27/2002-11/16/2006. |
Environmental Conditions: |
There are no known environmental conditions (e.g., seasonality, land use practices, fire events, storms, etc.) that are related to these data. |
QAPP Information: |
Quality control was conducted in accordance with the SWAMP Quality Assurance Management Plan (SWAMP 2002). |
QAPP Information Reference(s): |
Quality Assurance Management Plan for the State of California's Surface Water Ambient Monitoring Program. Sacramento, CA. State Water Resources Control Board. SWAMP. December 2002 (1st version)
|
|
Line of Evidence (LOE) for Decision ID 168816, Glyphosate
|
Region 1 |
Klamath River HU, Shasta River HA |
|
|
LOE ID: |
349823 |
|
Pollutant: |
Glyphosate |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Total |
|
Beneficial Use: |
Warm Freshwater Habitat |
|
Number of Samples: |
3 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed RWB1 Trend Maintenance Periods FYs 2007 2008 data for Klamath River HU, Shasta River HA to determine beneficial use support and results are as follows: 0 of 3 samples exceeded the water quality threshold for Glyphosate. |
Data Reference: |
RWB1 Trend Maintenance Periods FYs 2007 2008 |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
All waters shall be maintained free of toxic substances in concentrations which are toxic to, or which produce detrimental physiological responses in, human, plant, animal, or aquatic life. (Basin Plan). |
Objective/Criterion Reference: |
Water Quality Control Plan (Basin Plan) for the North Coast Region |
|
Evaluation Guideline: |
The evaluation guideline for Glyphosate is the USEPA Aquatic Life Benchmark of 11900 ug/L for a vascular plant (acute). |
Guideline Reference: |
OPP Aquatic Life Benchmarks |
|
Spatial Representation: |
The samples were collected at 1 monitoring site: 105SHA263 (Shasta River at Hwy 263). |
Temporal Representation: |
The samples were collected between the dates of 2007-11-15 and 2008-07-16 |
Environmental Conditions: |
|
QAPP Information: |
Generic SWAMP QAPrP |
QAPP Information Reference(s): |
Generic SWAMP QAPrP |
|
Line of Evidence (LOE) for Decision ID 168816, Glyphosate
|
Region 1 |
Klamath River HU, Shasta River HA |
|
|
LOE ID: |
103620 |
|
Pollutant: |
Glyphosate |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Total |
|
Beneficial Use: |
Municipal & Domestic Supply |
|
Number of Samples: |
3 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP RWB1 Monitoring data for Klamath River HU, Shasta River HA to determine beneficial use support and results are as follows: 0 of 3 samples exceeded the water quality standard for Glyphosate. |
Data Reference: |
Water Quality Assessment Data for the 2018 solicitation cycle submitted through CEDEN for SWAMP RWB1 Monitoring .
|
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
Water Quality Control Plan, North Coast Region (NCRWQCB 2018): Waters designated for use as domestic or municipal supply (MUN) shall not contain concentrations of chemical constituents in excess of the limits specified in California Code of Regulations, Title 22, Chapter 15. The maximum contaminant level listed in Table 64444-A for glyphosate is 700 ug/L. |
Objective/Criterion Reference: |
Water Quality Control Plan (Basin Plan) for the North Coast Region |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
The samples were collected at 1 monitoring site(s) (105SH1452) |
Temporal Representation: |
The samples were collected between the dates of 2013-03-06 and 2013-11-20 |
Environmental Conditions: |
|
QAPP Information: |
Quality Assurance Program Plan and Standard Operating Procedures for SWAMP program |
QAPP Information Reference(s): |
Quality Assurance Program Plans, Quality Assurance Project Plans, and Standard Operating Procedures for the SWAMP program |
|
Line of Evidence (LOE) for Decision ID 168816, Glyphosate
|
Region 1 |
Klamath River HU, Shasta River HA |
|
|
LOE ID: |
349819 |
|
Pollutant: |
Glyphosate |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Total |
|
Beneficial Use: |
Warm Freshwater Habitat |
|
Number of Samples: |
3 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed RWB1 Trend Maintenance Periods FYs 2007 2008 data for Klamath River HU, Shasta River HA to determine beneficial use support and results are as follows: 0 of 3 samples exceeded the water quality threshold for Glyphosate. |
Data Reference: |
RWB1 Trend Maintenance Periods FYs 2007 2008 |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
All waters shall be maintained free of toxic substances in concentrations which are toxic to, or which produce detrimental physiological responses in, human, plant, animal, or aquatic life. (Basin Plan). |
Objective/Criterion Reference: |
Water Quality Control Plan (Basin Plan) for the North Coast Region |
|
Evaluation Guideline: |
The evaluation guideline for Glyphosate is the USEPA Aquatic Life Benchmark of 11900 ug/L for a vascular plant (acute). |
Guideline Reference: |
OPP Aquatic Life Benchmarks |
|
Spatial Representation: |
The samples were collected at 1 monitoring site: 105SHAEDG (Shasta River near Edgewood). |
Temporal Representation: |
The samples were collected between the dates of 2007-11-15 and 2008-07-16 |
Environmental Conditions: |
|
QAPP Information: |
Generic SWAMP QAPrP |
QAPP Information Reference(s): |
Generic SWAMP QAPrP |
|
Line of Evidence (LOE) for Decision ID 168816, Glyphosate
|
Region 1 |
Klamath River HU, Shasta River HA |
|
|
LOE ID: |
349830 |
|
Pollutant: |
Glyphosate |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Total |
|
Beneficial Use: |
Cold Freshwater Habitat |
|
Number of Samples: |
3 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed RWB1 Trend Maintenance Periods FYs 2007 2008 data for Klamath River HU, Shasta River HA to determine beneficial use support and results are as follows: 0 of 3 samples exceeded the water quality threshold for Glyphosate. |
Data Reference: |
RWB1 Trend Maintenance Periods FYs 2007 2008 |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
All waters shall be maintained free of toxic substances in concentrations which are toxic to, or which produce detrimental physiological responses in, human, plant, animal, or aquatic life. (Basin Plan). |
Objective/Criterion Reference: |
Water Quality Control Plan (Basin Plan) for the North Coast Region |
|
Evaluation Guideline: |
The evaluation guideline for Glyphosate is the USEPA Aquatic Life Benchmark of 11900 ug/L for a vascular plant (acute). |
Guideline Reference: |
OPP Aquatic Life Benchmarks |
|
Spatial Representation: |
The samples were collected at 1 monitoring site: 105SHA263 (Shasta River at Hwy 263). |
Temporal Representation: |
The samples were collected between the dates of 2007-11-15 and 2008-07-16 |
Environmental Conditions: |
|
QAPP Information: |
Generic SWAMP QAPrP |
QAPP Information Reference(s): |
Generic SWAMP QAPrP |
|
Line of Evidence (LOE) for Decision ID 168816, Glyphosate
|
Region 1 |
Klamath River HU, Shasta River HA |
|
|
LOE ID: |
123456 |
|
Pollutant: |
Glyphosate |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
None |
|
Beneficial Use: |
Municipal & Domestic Supply |
|
Number of Samples: |
0 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
State Water Board staff re-assessed SWAMP data for Klamath River HU, Shasta River HA to determine beneficial use support and results are as follows: 0 of 0 samples exceed the criterion for Glyphosate, Total. Three sample results were not used in the assessment because the laboratory data reporting limit(s) was above the objective and therefore the results could not be quantified with the level of certainty required by the Listing Policy. This LOE re-assesses data from LOE 29849 from the 2010 Integrated Report. Data were re-assessed in order to evaluate these data in their own LOE, instead of being evaluated in the same LOE as other pesticide data. |
Data Reference: |
Surface Water Ambient Monitoring Program (SWAMP). Summary Report for the North Coast Region (RWQCB-1) for years 2000-2006. North Coast Regional Water Quality Control Board. March 2008 |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
Water Quality Control Plan, North Coast Region (NCRWQCB 2011): Waters designated for use as domestic or municipal supply (MUN) shall not contain concentrations of chemical constituents in excess of the limits specified in California Code of Regulations, Title 22, Chapter 15. The maximum contaminant level listed in Table 64431-A for glyphosate is 700 ug/L. |
Objective/Criterion Reference: |
Water Quality Control Plan (Basin Plan) for the North Coast Region |
Objective/Criterion Reference: |
Maximum Contaminant Levels for organic and inorganic chemicals. CCR Title 22 |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
Data for this line of evidence for Klamath River HU, Shasta River HA was collected at 1 monitoring site [ Shasta River near Edgewood - 105SH9274] |
Temporal Representation: |
Data was collected over the time period 2/10/2003-6/19/2003. |
Environmental Conditions: |
There are no known environmental conditions (e.g., seasonality, land use practices, fire events, storms, etc.) that are related to these data. |
QAPP Information: |
Quality control was conducted in accordance with the SWAMP Quality Assurance Management Plan (SWAMP 2002). |
QAPP Information Reference(s): |
Quality Assurance Management Plan for the State of California's Surface Water Ambient Monitoring Program. Sacramento, CA. State Water Resources Control Board. SWAMP. December 2002 (1st version)
|
|
Line of Evidence (LOE) for Decision ID 168816, Glyphosate
|
Region 1 |
Klamath River HU, Shasta River HA |
|
|
LOE ID: |
103623 |
|
Pollutant: |
Glyphosate |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Total |
|
Beneficial Use: |
Municipal & Domestic Supply |
|
Number of Samples: |
3 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP RWB1 Monitoring data for Klamath River HU, Shasta River HA to determine beneficial use support and results are as follows: 0 of 3 samples exceeded the water quality standard for Glyphosate. |
Data Reference: |
Water Quality Assessment Data for the 2018 solicitation cycle submitted through CEDEN for SWAMP RWB1 Monitoring .
|
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
Water Quality Control Plan, North Coast Region (NCRWQCB 2018): Waters designated for use as domestic or municipal supply (MUN) shall not contain concentrations of chemical constituents in excess of the limits specified in California Code of Regulations, Title 22, Chapter 15. The maximum contaminant level listed in Table 64444-A for glyphosate is 700 ug/L. |
Objective/Criterion Reference: |
Water Quality Control Plan (Basin Plan) for the North Coast Region |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
The samples were collected at 1 monitoring site(s) (105SH9274) |
Temporal Representation: |
The samples were collected between the dates of 2013-03-07 and 2013-11-20 |
Environmental Conditions: |
|
QAPP Information: |
Quality Assurance Program Plan and Standard Operating Procedures for SWAMP program |
QAPP Information Reference(s): |
Quality Assurance Program Plans, Quality Assurance Project Plans, and Standard Operating Procedures for the SWAMP program |
|
Line of Evidence (LOE) for Decision ID 168816, Glyphosate
|
Region 1 |
Klamath River HU, Shasta River HA |
|
|
LOE ID: |
123445 |
|
Pollutant: |
Glyphosate |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
None |
|
Beneficial Use: |
Municipal & Domestic Supply |
|
Number of Samples: |
0 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
State Water Board staff re-assessed SWAMP data for Klamath River HU, Shasta River HA to determine beneficial use support and results are as follows: 0 of 0 samples exceed the criterion for Glyphosate, Total. Three sample results were not used in the assessment because the laboratory data reporting limit(s) was above the objective and therefore the results could not be quantified with the level of certainty required by the Listing Policy. This LOE re-assesses data from LOE 29849 from the 2010 Integrated Report. Data were re-assessed in order to evaluate these data in their own LOE, instead of being evaluated in the same LOE as other pesticide data. |
Data Reference: |
Surface Water Ambient Monitoring Program (SWAMP). Summary Report for the North Coast Region (RWQCB-1) for years 2000-2006. North Coast Regional Water Quality Control Board. March 2008 |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
Water Quality Control Plan, North Coast Region (NCRWQCB 2011): Waters designated for use as domestic or municipal supply (MUN) shall not contain concentrations of chemical constituents in excess of the limits specified in California Code of Regulations, Title 22, Chapter 15. The maximum contaminant level listed in Table 64431-A for glyphosate is 700 ug/L. |
Objective/Criterion Reference: |
Water Quality Control Plan (Basin Plan) for the North Coast Region |
Objective/Criterion Reference: |
Maximum Contaminant Levels for organic and inorganic chemicals. CCR Title 22 |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
Data for this line of evidence for Klamath River HU, Shasta River HA was collected at 1 monitoring site [ Shasta River at Hwy 263 - 105SH1452] |
Temporal Representation: |
Data was collected over the time period 2/12/2003-6/18/2003. |
Environmental Conditions: |
There are no known environmental conditions (e.g., seasonality, land use practices, fire events, storms, etc.) that are related to these data. |
QAPP Information: |
Quality control was conducted in accordance with the SWAMP Quality Assurance Management Plan (SWAMP 2002). |
QAPP Information Reference(s): |
Quality Assurance Management Plan for the State of California's Surface Water Ambient Monitoring Program. Sacramento, CA. State Water Resources Control Board. SWAMP. December 2002 (1st version)
|
|
Line of Evidence (LOE) for Decision ID 168816, Glyphosate
|
Region 1 |
Klamath River HU, Shasta River HA |
|
|
LOE ID: |
103622 |
|
Pollutant: |
Glyphosate |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Total |
|
Beneficial Use: |
Cold Freshwater Habitat |
|
Number of Samples: |
3 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP RWB1 Monitoring data for Klamath River HU, Shasta River HA to determine beneficial use support and results are as follows: 0 of 3 samples exceeded the water quality standard for Glyphosate. |
Data Reference: |
Water Quality Assessment Data for the 2018 solicitation cycle submitted through CEDEN for SWAMP RWB1 Monitoring .
|
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
All waters shall be maintained free of toxic substances in concentrations which are toxic to, or which produce detrimental physiological responses in, human, plant, animal, or aquatic life. (Basin Plan). |
Objective/Criterion Reference: |
Water Quality Control Plan (Basin Plan) for the North Coast Region |
|
Evaluation Guideline: |
The evaluation guideline for Glyphosate is the USEPA Aquatic Life Benchmark of 11900 ug/L for a vascular plant (acute). |
Guideline Reference: |
OPP Aquatic Life Benchmarks |
|
Spatial Representation: |
The samples were collected at 1 monitoring site(s) (105SH9274) |
Temporal Representation: |
The samples were collected between the dates of 2013-03-07 and 2013-11-20 |
Environmental Conditions: |
|
QAPP Information: |
Quality Assurance Program Plan and Standard Operating Procedures for SWAMP program |
QAPP Information Reference(s): |
Quality Assurance Program Plans, Quality Assurance Project Plans, and Standard Operating Procedures for the SWAMP program |
|
Line of Evidence (LOE) for Decision ID 168816, Glyphosate
|
Region 1 |
Klamath River HU, Shasta River HA |
|
|
LOE ID: |
103619 |
|
Pollutant: |
Glyphosate |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Total |
|
Beneficial Use: |
Cold Freshwater Habitat |
|
Number of Samples: |
3 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP RWB1 Monitoring data for Klamath River HU, Shasta River HA to determine beneficial use support and results are as follows: 0 of 3 samples exceeded the water quality standard for Glyphosate. |
Data Reference: |
Water Quality Assessment Data for the 2018 solicitation cycle submitted through CEDEN for SWAMP RWB1 Monitoring .
|
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
All waters shall be maintained free of toxic substances in concentrations which are toxic to, or which produce detrimental physiological responses in, human, plant, animal, or aquatic life. (Basin Plan). |
Objective/Criterion Reference: |
Water Quality Control Plan (Basin Plan) for the North Coast Region |
|
Evaluation Guideline: |
The evaluation guideline for Glyphosate is the USEPA Aquatic Life Benchmark of 11900 ug/L for a vascular plant (acute). |
Guideline Reference: |
OPP Aquatic Life Benchmarks |
|
Spatial Representation: |
The samples were collected at 1 monitoring site(s) (105SH1452) |
Temporal Representation: |
The samples were collected between the dates of 2013-03-06 and 2013-11-20 |
Environmental Conditions: |
|
QAPP Information: |
Quality Assurance Program Plan and Standard Operating Procedures for SWAMP program |
QAPP Information Reference(s): |
Quality Assurance Program Plans, Quality Assurance Project Plans, and Standard Operating Procedures for the SWAMP program |
|
Line of Evidence (LOE) for Decision ID 168816, Glyphosate
|
Region 1 |
Klamath River HU, Shasta River HA |
|
|
LOE ID: |
123457 |
|
Pollutant: |
Glyphosate |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
None |
|
Beneficial Use: |
Municipal & Domestic Supply |
|
Number of Samples: |
0 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
State Water Board staff re-assessed SWAMP data for Klamath River HU, Shasta River HA to determine beneficial use support and results are as follows: 0 of 0 samples exceed the criterion for Glyphosate, Total. Three sample results were not used in the assessment because the laboratory data reporting limit(s) was above the objective and therefore the results could not be quantified with the level of certainty required by the Listing Policy. This LOE re-assesses data from LOE 29849 from the 2010 Integrated Report. Data were re-assessed in order to evaluate these data in their own LOE, instead of being evaluated in the same LOE as other pesticide data. |
Data Reference: |
Surface Water Ambient Monitoring Program (SWAMP). Summary Report for the North Coast Region (RWQCB-1) for years 2000-2006. North Coast Regional Water Quality Control Board. March 2008 |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
Water Quality Control Plan, North Coast Region (NCRWQCB 2011): Waters designated for use as domestic or municipal supply (MUN) shall not contain concentrations of chemical constituents in excess of the limits specified in California Code of Regulations, Title 22, Chapter 15. The maximum contaminant level listed in Table 64431-A for glyphosate is 700 ug/L. |
Objective/Criterion Reference: |
Water Quality Control Plan (Basin Plan) for the North Coast Region |
Objective/Criterion Reference: |
Maximum Contaminant Levels for organic and inorganic chemicals. CCR Title 22 |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
Data for this line of evidence for Klamath River HU, Shasta River HA was collected at 1 monitoring site [ Yreka Creek at Anderson Rd - 105YREAND] |
Temporal Representation: |
Data was collected over the time period 2/12/2003-6/18/2003. |
Environmental Conditions: |
There are no known environmental conditions (e.g., seasonality, land use practices, fire events, storms, etc.) that are related to these data. |
QAPP Information: |
Quality control was conducted in accordance with the SWAMP Quality Assurance Management Plan (SWAMP 2002). |
QAPP Information Reference(s): |
Quality Assurance Management Plan for the State of California's Surface Water Ambient Monitoring Program. Sacramento, CA. State Water Resources Control Board. SWAMP. December 2002 (1st version)
|
|
Line of Evidence (LOE) for Decision ID 168816, Glyphosate
|
Region 1 |
Klamath River HU, Shasta River HA |
|
|
LOE ID: |
103621 |
|
Pollutant: |
Glyphosate |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Total |
|
Beneficial Use: |
Warm Freshwater Habitat |
|
Number of Samples: |
3 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP RWB1 Monitoring data for Klamath River HU, Shasta River HA to determine beneficial use support and results are as follows: 0 of 3 samples exceeded the water quality standard for Glyphosate. |
Data Reference: |
Water Quality Assessment Data for the 2018 solicitation cycle submitted through CEDEN for SWAMP RWB1 Monitoring .
|
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
All waters shall be maintained free of toxic substances in concentrations which are toxic to, or which produce detrimental physiological responses in, human, plant, animal, or aquatic life. (Basin Plan). |
Objective/Criterion Reference: |
Water Quality Control Plan (Basin Plan) for the North Coast Region |
|
Evaluation Guideline: |
The evaluation guideline for Glyphosate is the USEPA Aquatic Life Benchmark of 11900 ug/L for a vascular plant (acute). |
Guideline Reference: |
OPP Aquatic Life Benchmarks |
|
Spatial Representation: |
The samples were collected at 1 monitoring site(s) (105SH1452) |
Temporal Representation: |
The samples were collected between the dates of 2013-03-06 and 2013-11-20 |
Environmental Conditions: |
|
QAPP Information: |
Quality Assurance Program Plan and Standard Operating Procedures for SWAMP program |
QAPP Information Reference(s): |
Quality Assurance Program Plans, Quality Assurance Project Plans, and Standard Operating Procedures for the SWAMP program |
|
Line of Evidence (LOE) for Decision ID 168816, Glyphosate
|
Region 1 |
Klamath River HU, Shasta River HA |
|
|
LOE ID: |
123446 |
|
Pollutant: |
Glyphosate |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
None |
|
Beneficial Use: |
Municipal & Domestic Supply |
|
Number of Samples: |
0 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
State Water Board staff re-assessed SWAMP data for Klamath River HU, Shasta River HA to determine beneficial use support and results are as follows: 0 of 0 samples exceed the criterion for Glyphosate, Total. Three sample results were not used in the assessment because the laboratory data reporting limit(s) was above the objective and therefore the results could not be quantified with the level of certainty required by the Listing Policy. This LOE re-assesses data from LOE 29849 from the 2010 Integrated Report. Data were re-assessed in order to evaluate these data in their own LOE, instead of being evaluated in the same LOE as other pesticide data. |
Data Reference: |
Surface Water Ambient Monitoring Program (SWAMP). Summary Report for the North Coast Region (RWQCB-1) for years 2000-2006. North Coast Regional Water Quality Control Board. March 2008 |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
Water Quality Control Plan, North Coast Region (NCRWQCB 2011): Waters designated for use as domestic or municipal supply (MUN) shall not contain concentrations of chemical constituents in excess of the limits specified in California Code of Regulations, Title 22, Chapter 15. The maximum contaminant level listed in Table 64431-A for glyphosate is 700 ug/L. |
Objective/Criterion Reference: |
Water Quality Control Plan (Basin Plan) for the North Coast Region |
Objective/Criterion Reference: |
Maximum Contaminant Levels for organic and inorganic chemicals. CCR Title 22 |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
Data for this line of evidence for Klamath River HU, Shasta River HA was collected at 1 monitoring site [ Shasta River at Montague - 105SHAMON] |
Temporal Representation: |
Data was collected over the time period 2/12/2003-6/19/2003. |
Environmental Conditions: |
There are no known environmental conditions (e.g., seasonality, land use practices, fire events, storms, etc.) that are related to these data. |
QAPP Information: |
Quality control was conducted in accordance with the SWAMP Quality Assurance Management Plan (SWAMP 2002). |
QAPP Information Reference(s): |
Quality Assurance Management Plan for the State of California's Surface Water Ambient Monitoring Program. Sacramento, CA. State Water Resources Control Board. SWAMP. December 2002 (1st version)
|
|
Line of Evidence (LOE) for Decision ID 168816, Glyphosate
|
Region 1 |
Klamath River HU, Shasta River HA |
|
|
LOE ID: |
103624 |
|
Pollutant: |
Glyphosate |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Total |
|
Beneficial Use: |
Warm Freshwater Habitat |
|
Number of Samples: |
3 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP RWB1 Monitoring data for Klamath River HU, Shasta River HA to determine beneficial use support and results are as follows: 0 of 3 samples exceeded the water quality standard for Glyphosate. |
Data Reference: |
Water Quality Assessment Data for the 2018 solicitation cycle submitted through CEDEN for SWAMP RWB1 Monitoring .
|
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
All waters shall be maintained free of toxic substances in concentrations which are toxic to, or which produce detrimental physiological responses in, human, plant, animal, or aquatic life. (Basin Plan). |
Objective/Criterion Reference: |
Water Quality Control Plan (Basin Plan) for the North Coast Region |
|
Evaluation Guideline: |
The evaluation guideline for Glyphosate is the USEPA Aquatic Life Benchmark of 11900 ug/L for a vascular plant (acute). |
Guideline Reference: |
OPP Aquatic Life Benchmarks |
|
Spatial Representation: |
The samples were collected at 1 monitoring site(s) (105SH9274) |
Temporal Representation: |
The samples were collected between the dates of 2013-03-07 and 2013-11-20 |
Environmental Conditions: |
|
QAPP Information: |
Quality Assurance Program Plan and Standard Operating Procedures for SWAMP program |
QAPP Information Reference(s): |
Quality Assurance Program Plans, Quality Assurance Project Plans, and Standard Operating Procedures for the SWAMP program |
|
Line of Evidence (LOE) for Decision ID 168816, Glyphosate
|
Region 1 |
Klamath River HU, Shasta River HA |
|
|
LOE ID: |
41875 |
|
Pollutant: |
Glyphosate |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Total |
|
Beneficial Use: |
Municipal & Domestic Supply |
|
Number of Samples: |
3 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP data for Klamath River HU, Shasta River HA to determine beneficial use support and results are as follows: 0 of 3 samples exceed the criterion for Glyphosate. |
Data Reference: |
RWB1 Trend Maintenance Periods FYs 2007 2008 |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
Water Quality Control Plan, North Coast Region (NCRWQCB 2011): Waters designated for use as domestic or municipal supply (MUN) shall not contain concentrations of chemical constituents in excess of the limits specified in California Code of Regulations, Title 22, Chapter 15. The maximum contaminant level listed in Table 64431-A for glyphosate is 700 ug/L. |
Objective/Criterion Reference: |
Maximum Contaminant Levels for organic and inorganic chemicals. CCR Title 22 |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
Data for this line of evidence for Klamath River HU, Shasta River HA was collected at 1 monitoring site [ Shasta River near Edgewood - 105SHAEDG] |
Temporal Representation: |
Data was collected over the time period 11/15/2007-7/16/2008. |
Environmental Conditions: |
Staff is not aware of any special conditions that might affect interpretation of the data. |
QAPP Information: |
The SWAMP QAPP (2008) was followed. |
QAPP Information Reference(s): |
Surface Water Ambient Monitoring Program Quality Assurance Program Plan |
|
Line of Evidence (LOE) for Decision ID 168816, Glyphosate
|
Region 1 |
Klamath River HU, Shasta River HA |
|
|
LOE ID: |
41876 |
|
Pollutant: |
Glyphosate |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Total |
|
Beneficial Use: |
Municipal & Domestic Supply |
|
Number of Samples: |
3 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP data for Klamath River HU, Shasta River HA to determine beneficial use support and results are as follows: 0 of 3 samples exceed the criterion for Glyphosate. |
Data Reference: |
RWB1 Trend Maintenance Periods FYs 2007 2008 |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
Water Quality Control Plan, North Coast Region (NCRWQCB 2011): Waters designated for use as domestic or municipal supply (MUN) shall not contain concentrations of chemical constituents in excess of the limits specified in California Code of Regulations, Title 22, Chapter 15. The maximum contaminant level listed in Table 64431-A for glyphosate is 700 ug/L. |
Objective/Criterion Reference: |
Maximum Contaminant Levels for organic and inorganic chemicals. CCR Title 22 |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
Data for this line of evidence for Klamath River HU, Shasta River HA was collected at 1 monitoring site [ Shasta River at Hwy 263 - 105SHA263] |
Temporal Representation: |
Data was collected over the time period 11/15/2007-7/16/2008. |
Environmental Conditions: |
Staff is not aware of any special conditions that might affect interpretation of the data. |
QAPP Information: |
The SWAMP QAPP (2008) was followed. |
QAPP Information Reference(s): |
Surface Water Ambient Monitoring Program Quality Assurance Program Plan |
|
Line of Evidence (LOE) for Decision ID 168816, Glyphosate
|
Region 1 |
Klamath River HU, Shasta River HA |
|
|
LOE ID: |
349810 |
|
Pollutant: |
Glyphosate |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Total |
|
Beneficial Use: |
Cold Freshwater Habitat |
|
Number of Samples: |
3 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed RWB1 Trend Maintenance Periods FYs 2007 2008 data for Klamath River HU, Shasta River HA to determine beneficial use support and results are as follows: 0 of 3 samples exceeded the water quality threshold for Glyphosate. |
Data Reference: |
RWB1 Trend Maintenance Periods FYs 2007 2008 |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
All waters shall be maintained free of toxic substances in concentrations which are toxic to, or which produce detrimental physiological responses in, human, plant, animal, or aquatic life. (Basin Plan). |
Objective/Criterion Reference: |
Water Quality Control Plan (Basin Plan) for the North Coast Region |
|
Evaluation Guideline: |
The evaluation guideline for Glyphosate is the USEPA Aquatic Life Benchmark of 11900 ug/L for a vascular plant (acute). |
Guideline Reference: |
OPP Aquatic Life Benchmarks |
|
Spatial Representation: |
The samples were collected at 1 monitoring site: 105SHAEDG (Shasta River near Edgewood). |
Temporal Representation: |
The samples were collected between the dates of 2007-11-15 and 2008-07-16 |
Environmental Conditions: |
|
QAPP Information: |
Generic SWAMP QAPrP |
QAPP Information Reference(s): |
Generic SWAMP QAPrP |
|
Line of Evidence (LOE) for Decision ID 168817, Heptachlor
|
Region 1 |
Klamath River HU, Shasta River HA |
|
|
LOE ID: |
42387 |
|
Pollutant: |
Heptachlor |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Total |
|
Beneficial Use: |
Cold Freshwater Habitat |
|
Number of Samples: |
3 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP data for Klamath River HU, Shasta River HA to determine beneficial use support and results are as follows: 0 of 3 samples exceed the criterion for Heptachlor. |
Data Reference: |
RWB1 Trend Maintenance Periods FYs 2007 2008 |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
Water Quality Control Plan, North Coast Region (NCRWQCB 2011): All waters shall be maintained free of toxic substances in concentrations that are toxic to, or that produce detrimental physiological responses in human, plant, animal, or aquatic life. The established numeric criteria for heptachlor to protect aquatic life in freshwater criterion continuous concentration (expressed as a 4-day average) is 0.0038 ug/L (California Toxics Rule, 2000). |
Objective/Criterion Reference: |
Code of Federal Regulations 40 part 131.38 Establishment of numeric criteria for priority toxic pollutants for the State of California. 7/1/2011 Edition |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
Data for this line of evidence for Klamath River HU, Shasta River HA was collected at 1 monitoring site [ Shasta River at Hwy 263 - 105SHA263] |
Temporal Representation: |
Data was collected over the time period 11/15/2007-7/16/2008. |
Environmental Conditions: |
Staff is not aware of any special conditions that might affect interpretation of the data. |
QAPP Information: |
The SWAMP QAPP (2008) was followed. |
QAPP Information Reference(s): |
Surface Water Ambient Monitoring Program Quality Assurance Program Plan |
|
Line of Evidence (LOE) for Decision ID 168817, Heptachlor
|
Region 1 |
Klamath River HU, Shasta River HA |
|
|
LOE ID: |
119979 |
|
Pollutant: |
Heptachlor |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Total |
|
Beneficial Use: |
Cold Freshwater Habitat |
|
Number of Samples: |
1 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP RWB1 Monitoring data for Klamath River HU, Shasta River HA to determine beneficial use support and results are as follows: 0 of 1 samples exceeded the water quality standard for Heptachlor. |
Data Reference: |
Water Quality Assessment Data for the 2018 solicitation cycle submitted through CEDEN for SWAMP RWB1 Monitoring .
|
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
Water Quality Control Plan, North Coast Region (NCRWQCB 2018): All waters shall be maintained free of toxic substances in concentrations that are toxic to, or that produce detrimental physiological responses in human, plant, animal, or aquatic life. The established numeric criteria for heptachlor to protect aquatic life in freshwater criterion continuous concentration (expressed as a 4-day average) is 0.0038 ug/L (California Toxics Rule, 2000). |
Objective/Criterion Reference: |
Water Quality Standards 2000. Establishment of numeric criteria for priority toxic pollutants for the State of California: Rules and regulations. Federal Register Vol. 65, No. 97. Washington, D.C.: Environmental Protection Agency |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
The samples were collected at 1 monitoring site(s) (105SH9274) |
Temporal Representation: |
The samples were collected between the dates of 2013-04-29 and 2013-04-29 |
Environmental Conditions: |
|
QAPP Information: |
Quality Assurance Program Plan and Standard Operating Procedures for SWAMP program |
QAPP Information Reference(s): |
Quality Assurance Program Plans, Quality Assurance Project Plans, and Standard Operating Procedures for the SWAMP program |
|
Line of Evidence (LOE) for Decision ID 168817, Heptachlor
|
Region 1 |
Klamath River HU, Shasta River HA |
|
|
LOE ID: |
119978 |
|
Pollutant: |
Heptachlor |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Total |
|
Beneficial Use: |
Cold Freshwater Habitat |
|
Number of Samples: |
1 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP RWB1 Monitoring data for Klamath River HU, Shasta River HA to determine beneficial use support and results are as follows: 0 of 1 samples exceeded the water quality standard for Heptachlor. |
Data Reference: |
Water Quality Assessment Data for the 2018 solicitation cycle submitted through CEDEN for SWAMP RWB1 Monitoring .
|
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
Water Quality Control Plan, North Coast Region (NCRWQCB 2018): All waters shall be maintained free of toxic substances in concentrations that are toxic to, or that produce detrimental physiological responses in human, plant, animal, or aquatic life. The established numeric criteria for heptachlor to protect aquatic life in freshwater criterion continuous concentration (expressed as a 4-day average) is 0.0038 ug/L (California Toxics Rule, 2000). |
Objective/Criterion Reference: |
Water Quality Standards 2000. Establishment of numeric criteria for priority toxic pollutants for the State of California: Rules and regulations. Federal Register Vol. 65, No. 97. Washington, D.C.: Environmental Protection Agency |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
The samples were collected at 1 monitoring site(s) (105SH1452) |
Temporal Representation: |
The samples were collected between the dates of 2013-04-29 and 2013-04-29 |
Environmental Conditions: |
|
QAPP Information: |
Quality Assurance Program Plan and Standard Operating Procedures for SWAMP program |
QAPP Information Reference(s): |
Quality Assurance Program Plans, Quality Assurance Project Plans, and Standard Operating Procedures for the SWAMP program |
|
Line of Evidence (LOE) for Decision ID 168817, Heptachlor
|
Region 1 |
Klamath River HU, Shasta River HA |
|
|
LOE ID: |
110643 |
|
Pollutant: |
Heptachlor |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Total |
|
Beneficial Use: |
Municipal & Domestic Supply |
|
Number of Samples: |
0 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP RWB1 Monitoring data for Klamath River HU, Shasta River HA to determine beneficial use support, and the results are as follows: 0 of the 0 samples exceeded the evaluation guideline for Heptachlor. Although a total of 1 samples were collected, 1 of these samples were not included in the assessment because the laboratory data reporting limit(s) was above the objective and therefore the results could not be quantified with the level of certainty required by the Listing Policy Section 6.1.5.5. |
Data Reference: |
Water Quality Assessment Data for the 2018 solicitation cycle submitted through CEDEN for SWAMP RWB1 Monitoring .
|
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
Water Quality Control Plan, North Coast Region (NCRWQCB 2018): All waters shall be maintained free of toxic substances in concentrations that are toxic to, or that produce detrimental physiological responses in human, plant, animal, or aquatic life. The established numeric criteria for heptachlor to protect of human health from the consumption of water and organisms is 0.00021 ug/L (California Toxics Rule, 2000). |
Objective/Criterion Reference: |
Water Quality Standards 2000. Establishment of numeric criteria for priority toxic pollutants for the State of California: Rules and regulations. Federal Register Vol. 65, No. 97. Washington, D.C.: Environmental Protection Agency |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
Data was collected from 1 station(s) (Station Code(s) 105SH1452). |
Temporal Representation: |
Date for this waterbody was collected over the date range 2013-04-29 to 2013-04-29 |
Environmental Conditions: |
|
QAPP Information: |
Quality Assurance Program Plan and Standard Operating Procedures for SWAMP program |
QAPP Information Reference(s): |
Quality Assurance Program Plans, Quality Assurance Project Plans, and Standard Operating Procedures for the SWAMP program |
|
Line of Evidence (LOE) for Decision ID 168817, Heptachlor
|
Region 1 |
Klamath River HU, Shasta River HA |
|
|
LOE ID: |
106144 |
|
Pollutant: |
Heptachlor |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Total |
|
Beneficial Use: |
Commercial or recreational collection of fish, shellfish, or organisms |
|
Number of Samples: |
0 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP RWB1 Monitoring data for Klamath River HU, Shasta River HA to determine beneficial use support, and the results are as follows: 0 of the 0 samples exceeded the evaluation guideline for Heptachlor. Although a total of 1 samples were collected, 1 of these samples were not included in the assessment because the laboratory data reporting limit(s) was above the objective and therefore the results could not be quantified with the level of certainty required by the Listing Policy Section 6.1.5.5. |
Data Reference: |
Water Quality Assessment Data for the 2018 solicitation cycle submitted through CEDEN for SWAMP RWB1 Monitoring .
|
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
Water Quality Control Plan, North Coast Region (NCRWQCB 2018): All waters shall be maintained free of toxic substances in concentrations that are toxic to, or that produce detrimental physiological responses in human, plant, animal, or aquatic life. The established numeric criteria for heptachlor to protect human health from consumption of organisms only is 0.00021 ug/L (California Toxics Rule, 2000). |
Objective/Criterion Reference: |
Water Quality Standards 2000. Establishment of numeric criteria for priority toxic pollutants for the State of California: Rules and regulations. Federal Register Vol. 65, No. 97. Washington, D.C.: Environmental Protection Agency |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
Data was collected from 1 station(s) (Station Code(s) 105SH1452). |
Temporal Representation: |
Date for this waterbody was collected over the date range 2013-04-29 to 2013-04-29 |
Environmental Conditions: |
|
QAPP Information: |
Quality Assurance Program Plan and Standard Operating Procedures for SWAMP program |
QAPP Information Reference(s): |
Quality Assurance Program Plans, Quality Assurance Project Plans, and Standard Operating Procedures for the SWAMP program |
|
Line of Evidence (LOE) for Decision ID 168817, Heptachlor
|
Region 1 |
Klamath River HU, Shasta River HA |
|
|
LOE ID: |
42393 |
|
Pollutant: |
Heptachlor |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Total |
|
Beneficial Use: |
Warm Freshwater Habitat |
|
Number of Samples: |
3 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP data for Klamath River HU, Shasta River HA to determine beneficial use support and results are as follows: 0 of 3 samples exceed the criterion for Heptachlor. |
Data Reference: |
RWB1 Trend Maintenance Periods FYs 2007 2008 |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
Water Quality Control Plan, North Coast Region (NCRWQCB 2011): All waters shall be maintained free of toxic substances in concentrations that are toxic to, or that produce detrimental physiological responses in human, plant, animal, or aquatic life. The established numeric criteria for heptachlor to protect aquatic life in freshwater criterion continuous concentration (expressed as a 4-day average) is 0.0038 ug/L (California Toxics Rule, 2000). |
Objective/Criterion Reference: |
Code of Federal Regulations 40 part 131.38 Establishment of numeric criteria for priority toxic pollutants for the State of California. 7/1/2011 Edition |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
Data for this line of evidence for Klamath River HU, Shasta River HA was collected at 1 monitoring site [ Shasta River near Edgewood - 105SHAEDG] |
Temporal Representation: |
Data was collected over the time period 11/15/2007-7/16/2008. |
Environmental Conditions: |
Staff is not aware of any special conditions that might affect interpretation of the data. |
QAPP Information: |
The SWAMP QAPP (2008) was followed. |
QAPP Information Reference(s): |
Surface Water Ambient Monitoring Program Quality Assurance Program Plan |
|
Line of Evidence (LOE) for Decision ID 168817, Heptachlor
|
Region 1 |
Klamath River HU, Shasta River HA |
|
|
LOE ID: |
42386 |
|
Pollutant: |
Heptachlor |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Total |
|
Beneficial Use: |
Cold Freshwater Habitat |
|
Number of Samples: |
3 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP data for Klamath River HU, Shasta River HA to determine beneficial use support and results are as follows: 0 of 3 samples exceed the criterion for Heptachlor. |
Data Reference: |
RWB1 Trend Maintenance Periods FYs 2007 2008 |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
Water Quality Control Plan, North Coast Region (NCRWQCB 2011): All waters shall be maintained free of toxic substances in concentrations that are toxic to, or that produce detrimental physiological responses in human, plant, animal, or aquatic life. The established numeric criteria for heptachlor to protect aquatic life in freshwater criterion continuous concentration (expressed as a 4-day average) is 0.0038 ug/L (California Toxics Rule, 2000). |
Objective/Criterion Reference: |
Code of Federal Regulations 40 part 131.38 Establishment of numeric criteria for priority toxic pollutants for the State of California. 7/1/2011 Edition |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
Data for this line of evidence for Klamath River HU, Shasta River HA was collected at 1 monitoring site [ Shasta River near Edgewood - 105SHAEDG] |
Temporal Representation: |
Data was collected over the time period 11/15/2007-7/16/2008. |
Environmental Conditions: |
Staff is not aware of any special conditions that might affect interpretation of the data. |
QAPP Information: |
The SWAMP QAPP (2008) was followed. |
QAPP Information Reference(s): |
Surface Water Ambient Monitoring Program Quality Assurance Program Plan |
|
Line of Evidence (LOE) for Decision ID 168817, Heptachlor
|
Region 1 |
Klamath River HU, Shasta River HA |
|
|
LOE ID: |
42333 |
|
Pollutant: |
Heptachlor |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Total |
|
Beneficial Use: |
Municipal & Domestic Supply |
|
Number of Samples: |
0 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Three non-detect sample results were not used in the assessment because the laboratory data reporting limit was above the objective and therefore the results could not be quantified with the level of certainty required by the Listing Policy. |
Data Reference: |
RWB1 Trend Maintenance Periods FYs 2007 2008 |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
Water Quality Control Plan, North Coast Region (NCRWQCB 2011): All waters shall be maintained free of toxic substances in concentrations that are toxic to, or that produce detrimental physiological responses in human, plant, animal, or aquatic life. The established numeric criteria for heptachlor to protect of human health from the consumption of water and organisms is 0.00021 ug/L (California Toxics Rule, 2000). |
Objective/Criterion Reference: |
Code of Federal Regulations 40 part 131.38 Establishment of numeric criteria for priority toxic pollutants for the State of California. 7/1/2011 Edition |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
Data for this line of evidence for Klamath River HU, Shasta River HA was collected at 1 monitoring site [ Shasta River near Edgewood - 105SHAEDG] |
Temporal Representation: |
Data was collected over the time period 11/15/2007-7/16/2008. |
Environmental Conditions: |
Staff is not aware of any special conditions that might affect interpretation of the data. |
QAPP Information: |
The SWAMP QAPP (2008) was followed. |
QAPP Information Reference(s): |
Surface Water Ambient Monitoring Program Quality Assurance Program Plan |
|
Line of Evidence (LOE) for Decision ID 168817, Heptachlor
|
Region 1 |
Klamath River HU, Shasta River HA |
|
|
LOE ID: |
42308 |
|
Pollutant: |
Heptachlor |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Total |
|
Beneficial Use: |
Commercial or recreational collection of fish, shellfish, or organisms |
|
Number of Samples: |
0 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Three non-detect sample results were not used in the assessment because the laboratory data reporting limit was above the objective and therefore the results could not be quantified with the level of certainty required by the Listing Policy. |
Data Reference: |
RWB1 Trend Maintenance Periods FYs 2007 2008 |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
Water Quality Control Plan, North Coast Region (NCRWQCB 2011): All waters shall be maintained free of toxic substances in concentrations that are toxic to, or that produce detrimental physiological responses in human, plant, animal, or aquatic life. The established numeric criteria for heptachlor to protect human health from consumption of organisms only is 0.00021 ug/L (California Toxics Rule, 2000). |
Objective/Criterion Reference: |
Code of Federal Regulations 40 part 131.38 Establishment of numeric criteria for priority toxic pollutants for the State of California. 7/1/2011 Edition |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
Data for this line of evidence for Klamath River HU, Shasta River HA was collected at 1 monitoring site [ Shasta River near Edgewood - 105SHAEDG] |
Temporal Representation: |
Data was collected over the time period 11/15/2007-7/16/2008. |
Environmental Conditions: |
Staff is not aware of any special conditions that might affect interpretation of the data. |
QAPP Information: |
The SWAMP QAPP (2008) was followed. |
QAPP Information Reference(s): |
Surface Water Ambient Monitoring Program Quality Assurance Program Plan |
|
Line of Evidence (LOE) for Decision ID 168817, Heptachlor
|
Region 1 |
Klamath River HU, Shasta River HA |
|
|
LOE ID: |
42394 |
|
Pollutant: |
Heptachlor |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Total |
|
Beneficial Use: |
Warm Freshwater Habitat |
|
Number of Samples: |
3 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP data for Klamath River HU, Shasta River HA to determine beneficial use support and results are as follows: 0 of 3 samples exceed the criterion for Heptachlor. |
Data Reference: |
RWB1 Trend Maintenance Periods FYs 2007 2008 |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
Water Quality Control Plan, North Coast Region (NCRWQCB 2011): All waters shall be maintained free of toxic substances in concentrations that are toxic to, or that produce detrimental physiological responses in human, plant, animal, or aquatic life. The established numeric criteria for heptachlor to protect aquatic life in freshwater criterion continuous concentration (expressed as a 4-day average) is 0.0038 ug/L (California Toxics Rule, 2000). |
Objective/Criterion Reference: |
Code of Federal Regulations 40 part 131.38 Establishment of numeric criteria for priority toxic pollutants for the State of California. 7/1/2011 Edition |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
Data for this line of evidence for Klamath River HU, Shasta River HA was collected at 1 monitoring site [ Shasta River at Hwy 263 - 105SHA263] |
Temporal Representation: |
Data was collected over the time period 11/15/2007-7/16/2008. |
Environmental Conditions: |
Staff is not aware of any special conditions that might affect interpretation of the data. |
QAPP Information: |
The SWAMP QAPP (2008) was followed. |
QAPP Information Reference(s): |
Surface Water Ambient Monitoring Program Quality Assurance Program Plan |
|
Line of Evidence (LOE) for Decision ID 168817, Heptachlor
|
Region 1 |
Klamath River HU, Shasta River HA |
|
|
LOE ID: |
115847 |
|
Pollutant: |
Heptachlor |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Total |
|
Beneficial Use: |
Commercial or recreational collection of fish, shellfish, or organisms |
|
Number of Samples: |
0 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP RWB1 Monitoring data for Klamath River HU, Shasta River HA to determine beneficial use support, and the results are as follows: 0 of the 0 samples exceeded the evaluation guideline for Heptachlor. Although a total of 1 samples were collected, 1 of these samples were not included in the assessment because the laboratory data reporting limit(s) was above the objective and therefore the results could not be quantified with the level of certainty required by the Listing Policy Section 6.1.5.5. |
Data Reference: |
Water Quality Assessment Data for the 2018 solicitation cycle submitted through CEDEN for SWAMP RWB1 Monitoring .
|
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
Water Quality Control Plan, North Coast Region (NCRWQCB 2018): All waters shall be maintained free of toxic substances in concentrations that are toxic to, or that produce detrimental physiological responses in human, plant, animal, or aquatic life. The established numeric criteria for heptachlor to protect human health from consumption of organisms only is 0.00021 ug/L (California Toxics Rule, 2000). |
Objective/Criterion Reference: |
Water Quality Standards 2000. Establishment of numeric criteria for priority toxic pollutants for the State of California: Rules and regulations. Federal Register Vol. 65, No. 97. Washington, D.C.: Environmental Protection Agency |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
Data was collected from 1 station(s) (Station Code(s) 105SH9274). |
Temporal Representation: |
Date for this waterbody was collected over the date range 2013-04-29 to 2013-04-29 |
Environmental Conditions: |
|
QAPP Information: |
Quality Assurance Program Plan and Standard Operating Procedures for SWAMP program |
QAPP Information Reference(s): |
Quality Assurance Program Plans, Quality Assurance Project Plans, and Standard Operating Procedures for the SWAMP program |
|
Line of Evidence (LOE) for Decision ID 168817, Heptachlor
|
Region 1 |
Klamath River HU, Shasta River HA |
|
|
LOE ID: |
42309 |
|
Pollutant: |
Heptachlor |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Total |
|
Beneficial Use: |
Commercial or recreational collection of fish, shellfish, or organisms |
|
Number of Samples: |
0 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Three non-detect sample results were not used in the assessment because the laboratory data reporting limit was above the objective and therefore the results could not be quantified with the level of certainty required by the Listing Policy. |
Data Reference: |
RWB1 Trend Maintenance Periods FYs 2007 2008 |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
Water Quality Control Plan, North Coast Region (NCRWQCB 2011): All waters shall be maintained free of toxic substances in concentrations that are toxic to, or that produce detrimental physiological responses in human, plant, animal, or aquatic life. The established numeric criteria for heptachlor to protect human health from consumption of organisms only is 0.00021 ug/L (California Toxics Rule, 2000). |
Objective/Criterion Reference: |
Code of Federal Regulations 40 part 131.38 Establishment of numeric criteria for priority toxic pollutants for the State of California. 7/1/2011 Edition |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
Data for this line of evidence for Klamath River HU, Shasta River HA was collected at 1 monitoring site [ Shasta River at Hwy 263 - 105SHA263] |
Temporal Representation: |
Data was collected over the time period 11/15/2007-7/16/2008. |
Environmental Conditions: |
Staff is not aware of any special conditions that might affect interpretation of the data. |
QAPP Information: |
The SWAMP QAPP (2008) was followed. |
QAPP Information Reference(s): |
Surface Water Ambient Monitoring Program Quality Assurance Program Plan |
|
Line of Evidence (LOE) for Decision ID 168817, Heptachlor
|
Region 1 |
Klamath River HU, Shasta River HA |
|
|
LOE ID: |
110646 |
|
Pollutant: |
Heptachlor |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Total |
|
Beneficial Use: |
Municipal & Domestic Supply |
|
Number of Samples: |
0 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP RWB1 Monitoring data for Klamath River HU, Shasta River HA to determine beneficial use support, and the results are as follows: 0 of the 0 samples exceeded the evaluation guideline for Heptachlor. Although a total of 1 samples were collected, 1 of these samples were not included in the assessment because the laboratory data reporting limit(s) was above the objective and therefore the results could not be quantified with the level of certainty required by the Listing Policy Section 6.1.5.5. |
Data Reference: |
Water Quality Assessment Data for the 2018 solicitation cycle submitted through CEDEN for SWAMP RWB1 Monitoring .
|
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
Water Quality Control Plan, North Coast Region (NCRWQCB 2018): All waters shall be maintained free of toxic substances in concentrations that are toxic to, or that produce detrimental physiological responses in human, plant, animal, or aquatic life. The established numeric criteria for heptachlor to protect of human health from the consumption of water and organisms is 0.00021 ug/L (California Toxics Rule, 2000). |
Objective/Criterion Reference: |
Water Quality Standards 2000. Establishment of numeric criteria for priority toxic pollutants for the State of California: Rules and regulations. Federal Register Vol. 65, No. 97. Washington, D.C.: Environmental Protection Agency |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
Data was collected from 1 station(s) (Station Code(s) 105SH9274). |
Temporal Representation: |
Date for this waterbody was collected over the date range 2013-04-29 to 2013-04-29 |
Environmental Conditions: |
|
QAPP Information: |
Quality Assurance Program Plan and Standard Operating Procedures for SWAMP program |
QAPP Information Reference(s): |
Quality Assurance Program Plans, Quality Assurance Project Plans, and Standard Operating Procedures for the SWAMP program |
|
Line of Evidence (LOE) for Decision ID 168817, Heptachlor
|
Region 1 |
Klamath River HU, Shasta River HA |
|
|
LOE ID: |
42334 |
|
Pollutant: |
Heptachlor |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Total |
|
Beneficial Use: |
Municipal & Domestic Supply |
|
Number of Samples: |
0 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Three non-detect sample results were not used in the assessment because the laboratory data reporting limit was above the objective and therefore the results could not be quantified with the level of certainty required by the Listing Policy. |
Data Reference: |
RWB1 Trend Maintenance Periods FYs 2007 2008 |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
Water Quality Control Plan, North Coast Region (NCRWQCB 2011): All waters shall be maintained free of toxic substances in concentrations that are toxic to, or that produce detrimental physiological responses in human, plant, animal, or aquatic life. The established numeric criteria for heptachlor to protect of human health from the consumption of water and organisms is 0.00021 ug/L (California Toxics Rule, 2000). |
Objective/Criterion Reference: |
Code of Federal Regulations 40 part 131.38 Establishment of numeric criteria for priority toxic pollutants for the State of California. 7/1/2011 Edition |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
Data for this line of evidence for Klamath River HU, Shasta River HA was collected at 1 monitoring site [ Shasta River at Hwy 263 - 105SHA263] |
Temporal Representation: |
Data was collected over the time period 11/15/2007-7/16/2008. |
Environmental Conditions: |
Staff is not aware of any special conditions that might affect interpretation of the data. |
QAPP Information: |
The SWAMP QAPP (2008) was followed. |
QAPP Information Reference(s): |
Surface Water Ambient Monitoring Program Quality Assurance Program Plan |
|
Line of Evidence (LOE) for Decision ID 105200, Heptachlor epoxide
|
Region 1 |
Klamath River HU, Shasta River HA |
|
|
LOE ID: |
114141 |
|
Pollutant: |
Heptachlor epoxide |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Total |
|
Beneficial Use: |
Commercial or recreational collection of fish, shellfish, or organisms |
|
Number of Samples: |
0 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP RWB1 Monitoring data for Klamath River HU, Shasta River HA to determine beneficial use support, and the results are as follows: 0 of the 0 samples exceeded the evaluation guideline for Heptachlor Epoxide. Although a total of 1 samples were collected, 1 of these samples were not included in the assessment because the laboratory data reporting limit(s) was above the objective and therefore the results could not be quantified with the level of certainty required by the Listing Policy Section 6.1.5.5. |
Data Reference: |
Water Quality Assessment Data for the 2018 solicitation cycle submitted through CEDEN for SWAMP RWB1 Monitoring .
|
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
Water Quality Control Plan, North Coast Region (NCRWQCB 2018): All waters shall be maintained free of toxic substances in concentrations that are toxic to, or that produce detrimental physiological responses in human, plant, animal, or aquatic life. The established numeric criteria for heptachlor epoxide to protect human health from consumption of organisms only is 0.00011 ug/L (California Toxics Rule, 2000). |
Objective/Criterion Reference: |
Water Quality Standards 2000. Establishment of numeric criteria for priority toxic pollutants for the State of California: Rules and regulations. Federal Register Vol. 65, No. 97. Washington, D.C.: Environmental Protection Agency |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
Data was collected from 1 station(s) (Station Code(s) 105SH1452). |
Temporal Representation: |
Date for this waterbody was collected over the date range 2013-04-29 to 2013-04-29 |
Environmental Conditions: |
|
QAPP Information: |
Quality Assurance Program Plan and Standard Operating Procedures for SWAMP program |
QAPP Information Reference(s): |
Quality Assurance Program Plans, Quality Assurance Project Plans, and Standard Operating Procedures for the SWAMP program |
|
Line of Evidence (LOE) for Decision ID 105200, Heptachlor epoxide
|
Region 1 |
Klamath River HU, Shasta River HA |
|
|
LOE ID: |
123468 |
|
Pollutant: |
Heptachlor epoxide |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
None |
|
Beneficial Use: |
Municipal & Domestic Supply |
|
Number of Samples: |
0 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
State Water Board staff re-assessed SWAMP data for Klamath River HU, Shasta River HA to determine beneficial use support and results are as follows: 0 of 0 samples exceed the criterion for Heptachlor Epoxide, Total. Eight sample results were not used in the assessment because the laboratory data reporting limit(s) was above the objective and therefore the results could not be quantified with the level of certainty required by the Listing Policy. This LOE re-assesses data from LOE 29849 from the 2010 Integrated Report. Data were re-assessed in order to (1) update the numeric objective, and (2) evaluate these data in their own LOE, instead of being evaluated in the same LOE as other pesticide data. |
Data Reference: |
Surface Water Ambient Monitoring Program (SWAMP). Summary Report for the North Coast Region (RWQCB-1) for years 2000-2006. North Coast Regional Water Quality Control Board. March 2008 |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
Water Quality Control Plan, North Coast Region (NCRWQCB 2011): All waters shall be maintained free of toxic substances in concentrations that are toxic to, or that produce detrimental physiological responses in human, plant, animal, or aquatic life. The established numeric criteria for heptachlor to protect of human health from the consumption of water and organisms is 0.00021 ug/L (California Toxics Rule, 2000). |
Objective/Criterion Reference: |
Water Quality Control Plan (Basin Plan) for the North Coast Region |
Objective/Criterion Reference: |
Code of Federal Regulations 40 part 131.38 Establishment of numeric criteria for priority toxic pollutants for the State of California. 7/1/2011 Edition |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
Data for this line of evidence for Klamath River HU, Shasta River HA was collected at 1 monitoring site [ Yreka Creek at Highway 3 - 105YREHW3] |
Temporal Representation: |
Data was collected over the time period 10/21/2004-6/20/2005. |
Environmental Conditions: |
There are no known environmental conditions (e.g., seasonality, land use practices, fire events, storms, etc.) that are related to these data. |
QAPP Information: |
Quality control was conducted in accordance with the SWAMP Quality Assurance Management Plan (SWAMP 2002). |
QAPP Information Reference(s): |
Quality Assurance Management Plan for the State of California's Surface Water Ambient Monitoring Program. Sacramento, CA. State Water Resources Control Board. SWAMP. December 2002 (1st version)
|
|
Line of Evidence (LOE) for Decision ID 105200, Heptachlor epoxide
|
Region 1 |
Klamath River HU, Shasta River HA |
|
|
LOE ID: |
42219 |
|
Pollutant: |
Heptachlor epoxide |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Total |
|
Beneficial Use: |
Municipal & Domestic Supply |
|
Number of Samples: |
0 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Three non-detect sample results were not used in the assessment because the laboratory data reporting limit was above the objective and therefore the results could not be quantified with the level of certainty required by the Listing Policy. |
Data Reference: |
RWB1 Trend Maintenance Periods FYs 2007 2008 |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
Water Quality Control Plan, North Coast Region (NCRWQCB 2011): All waters shall be maintained free of toxic substances in concentrations that are toxic to, or that produce detrimental physiological responses in human, plant, animal, or aquatic life. The established numeric criteria for heptachlor epoxide to protect of human health from the consumption of water and organisms is 0.00010 ug/L (California Toxics Rule, 2000). |
Objective/Criterion Reference: |
Code of Federal Regulations 40 part 131.38 Establishment of numeric criteria for priority toxic pollutants for the State of California. 7/1/2011 Edition |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
Data for this line of evidence for Klamath River HU, Shasta River HA was collected at 1 monitoring site [ Shasta River at Hwy 263 - 105SHA263] |
Temporal Representation: |
Data was collected over the time period 11/15/2007-7/16/2008. |
Environmental Conditions: |
Staff is not aware of any special conditions that might affect interpretation of the data. |
QAPP Information: |
The SWAMP QAPP (2008) was followed. |
QAPP Information Reference(s): |
Surface Water Ambient Monitoring Program Quality Assurance Program Plan |
|
Line of Evidence (LOE) for Decision ID 105200, Heptachlor epoxide
|
Region 1 |
Klamath River HU, Shasta River HA |
|
|
LOE ID: |
115865 |
|
Pollutant: |
Heptachlor epoxide |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Total |
|
Beneficial Use: |
Municipal & Domestic Supply |
|
Number of Samples: |
0 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP RWB1 Monitoring data for Klamath River HU, Shasta River HA to determine beneficial use support, and the results are as follows: 0 of the 0 samples exceeded the evaluation guideline for Heptachlor Epoxide. Although a total of 1 samples were collected, 1 of these samples were not included in the assessment because the laboratory data reporting limit(s) was above the objective and therefore the results could not be quantified with the level of certainty required by the Listing Policy Section 6.1.5.5. |
Data Reference: |
Water Quality Assessment Data for the 2018 solicitation cycle submitted through CEDEN for SWAMP RWB1 Monitoring .
|
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
Water Quality Control Plan, North Coast Region (NCRWQCB 2018): All waters shall be maintained free of toxic substances in concentrations that are toxic to, or that produce detrimental physiological responses in human, plant, animal, or aquatic life. The established numeric criteria for heptachlor epoxide to protect of human health from the consumption of water and organisms is 0.00010 ug/L (California Toxics Rule, 2000). |
Objective/Criterion Reference: |
Water Quality Standards 2000. Establishment of numeric criteria for priority toxic pollutants for the State of California: Rules and regulations. Federal Register Vol. 65, No. 97. Washington, D.C.: Environmental Protection Agency |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
Data was collected from 1 station(s) (Station Code(s) 105SH1452). |
Temporal Representation: |
Date for this waterbody was collected over the date range 2013-04-29 to 2013-04-29 |
Environmental Conditions: |
|
QAPP Information: |
Quality Assurance Program Plan and Standard Operating Procedures for SWAMP program |
QAPP Information Reference(s): |
Quality Assurance Program Plans, Quality Assurance Project Plans, and Standard Operating Procedures for the SWAMP program |
|
Line of Evidence (LOE) for Decision ID 105200, Heptachlor epoxide
|
Region 1 |
Klamath River HU, Shasta River HA |
|
|
LOE ID: |
120109 |
|
Pollutant: |
Heptachlor epoxide |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Total |
|
Beneficial Use: |
Municipal & Domestic Supply |
|
Number of Samples: |
0 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP RWB1 Monitoring data for Klamath River HU, Shasta River HA to determine beneficial use support, and the results are as follows: 0 of the 0 samples exceeded the evaluation guideline for Heptachlor Epoxide. Although a total of 1 samples were collected, 1 of these samples were not included in the assessment because the laboratory data reporting limit(s) was above the objective and therefore the results could not be quantified with the level of certainty required by the Listing Policy Section 6.1.5.5. |
Data Reference: |
Water Quality Assessment Data for the 2018 solicitation cycle submitted through CEDEN for SWAMP RWB1 Monitoring .
|
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
Water Quality Control Plan, North Coast Region (NCRWQCB 2018): All waters shall be maintained free of toxic substances in concentrations that are toxic to, or that produce detrimental physiological responses in human, plant, animal, or aquatic life. The established numeric criteria for heptachlor epoxide to protect of human health from the consumption of water and organisms is 0.00010 ug/L (California Toxics Rule, 2000). |
Objective/Criterion Reference: |
Water Quality Standards 2000. Establishment of numeric criteria for priority toxic pollutants for the State of California: Rules and regulations. Federal Register Vol. 65, No. 97. Washington, D.C.: Environmental Protection Agency |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
Data was collected from 1 station(s) (Station Code(s) 105SH9274). |
Temporal Representation: |
Date for this waterbody was collected over the date range 2013-04-29 to 2013-04-29 |
Environmental Conditions: |
|
QAPP Information: |
Quality Assurance Program Plan and Standard Operating Procedures for SWAMP program |
QAPP Information Reference(s): |
Quality Assurance Program Plans, Quality Assurance Project Plans, and Standard Operating Procedures for the SWAMP program |
|
Line of Evidence (LOE) for Decision ID 105200, Heptachlor epoxide
|
Region 1 |
Klamath River HU, Shasta River HA |
|
|
LOE ID: |
42208 |
|
Pollutant: |
Heptachlor epoxide |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Total |
|
Beneficial Use: |
Municipal & Domestic Supply |
|
Number of Samples: |
0 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Three non-detect sample results were not used in the assessment because the laboratory data reporting limit was above the objective and therefore the results could not be quantified with the level of certainty required by the Listing Policy. |
Data Reference: |
RWB1 Trend Maintenance Periods FYs 2007 2008 |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
Water Quality Control Plan, North Coast Region (NCRWQCB 2011): All waters shall be maintained free of toxic substances in concentrations that are toxic to, or that produce detrimental physiological responses in human, plant, animal, or aquatic life. The established numeric criteria for heptachlor epoxide to protect of human health from the consumption of water and organisms is 0.00010 ug/L (California Toxics Rule, 2000). |
Objective/Criterion Reference: |
Code of Federal Regulations 40 part 131.38 Establishment of numeric criteria for priority toxic pollutants for the State of California. 7/1/2011 Edition |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
Data for this line of evidence for Klamath River HU, Shasta River HA was collected at 1 monitoring site [ Shasta River near Edgewood - 105SHAEDG] |
Temporal Representation: |
Data was collected over the time period 11/15/2007-7/16/2008. |
Environmental Conditions: |
Staff is not aware of any special conditions that might affect interpretation of the data. |
QAPP Information: |
The SWAMP QAPP (2008) was followed. |
QAPP Information Reference(s): |
Surface Water Ambient Monitoring Program Quality Assurance Program Plan |
|
Line of Evidence (LOE) for Decision ID 105200, Heptachlor epoxide
|
Region 1 |
Klamath River HU, Shasta River HA |
|
|
LOE ID: |
42253 |
|
Pollutant: |
Heptachlor epoxide |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Total |
|
Beneficial Use: |
Warm Freshwater Habitat |
|
Number of Samples: |
3 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP data for Klamath River HU, Shasta River HA to determine beneficial use support and results are as follows: 0 of 3 samples exceed the criterion for Heptachlor epoxide. |
Data Reference: |
RWB1 Trend Maintenance Periods FYs 2007 2008 |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
Water Quality Control Plan, North Coast Region (NCRWQCB 2011): All waters shall be maintained free of toxic substances in concentrations that are toxic to, or that produce detrimental physiological responses in human, plant, animal, or aquatic life. The established numeric criteria for heptachlor epoxide to protect aquatic life in freshwater criterion continuous concentration (expressed as a 4-day average) is 0.0038 ug/L (California Toxics Rule, 2000). |
Objective/Criterion Reference: |
Code of Federal Regulations 40 part 131.38 Establishment of numeric criteria for priority toxic pollutants for the State of California. 7/1/2011 Edition |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
Data for this line of evidence for Klamath River HU, Shasta River HA was collected at 1 monitoring site [ Shasta River near Edgewood - 105SHAEDG] |
Temporal Representation: |
Data was collected over the time period 11/15/2007-7/16/2008. |
Environmental Conditions: |
Staff is not aware of any special conditions that might affect interpretation of the data. |
QAPP Information: |
The SWAMP QAPP (2008) was followed. |
QAPP Information Reference(s): |
Surface Water Ambient Monitoring Program Quality Assurance Program Plan |
|
Line of Evidence (LOE) for Decision ID 105200, Heptachlor epoxide
|
Region 1 |
Klamath River HU, Shasta River HA |
|
|
LOE ID: |
42264 |
|
Pollutant: |
Heptachlor epoxide |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Total |
|
Beneficial Use: |
Warm Freshwater Habitat |
|
Number of Samples: |
3 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP data for Klamath River HU, Shasta River HA to determine beneficial use support and results are as follows: 0 of 3 samples exceed the criterion for Heptachlor epoxide. |
Data Reference: |
RWB1 Trend Maintenance Periods FYs 2007 2008 |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
Water Quality Control Plan, North Coast Region (NCRWQCB 2011): All waters shall be maintained free of toxic substances in concentrations that are toxic to, or that produce detrimental physiological responses in human, plant, animal, or aquatic life. The established numeric criteria for heptachlor epoxide to protect aquatic life in freshwater criterion continuous concentration (expressed as a 4-day average) is 0.0038 ug/L (California Toxics Rule, 2000). |
Objective/Criterion Reference: |
Code of Federal Regulations 40 part 131.38 Establishment of numeric criteria for priority toxic pollutants for the State of California. 7/1/2011 Edition |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
Data for this line of evidence for Klamath River HU, Shasta River HA was collected at 1 monitoring site [ Shasta River at Hwy 263 - 105SHA263] |
Temporal Representation: |
Data was collected over the time period 11/15/2007-7/16/2008. |
Environmental Conditions: |
Staff is not aware of any special conditions that might affect interpretation of the data. |
QAPP Information: |
The SWAMP QAPP (2008) was followed. |
QAPP Information Reference(s): |
Surface Water Ambient Monitoring Program Quality Assurance Program Plan |
|
Line of Evidence (LOE) for Decision ID 105200, Heptachlor epoxide
|
Region 1 |
Klamath River HU, Shasta River HA |
|
|
LOE ID: |
42159 |
|
Pollutant: |
Heptachlor epoxide |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Total |
|
Beneficial Use: |
Commercial or recreational collection of fish, shellfish, or organisms |
|
Number of Samples: |
0 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Three non-detect sample results were not used in the assessment because the laboratory data reporting limit was above the objective and therefore the results could not be quantified with the level of certainty required by the Listing Policy. |
Data Reference: |
RWB1 Trend Maintenance Periods FYs 2007 2008 |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
Water Quality Control Plan, North Coast Region (NCRWQCB 2011): All waters shall be maintained free of toxic substances in concentrations that are toxic to, or that produce detrimental physiological responses in human, plant, animal, or aquatic life. The established numeric criteria for heptachlor epoxide to protect human health from consumption of organisms only is 0.00011 ug/L (California Toxics Rule, 2000). |
Objective/Criterion Reference: |
Code of Federal Regulations 40 part 131.38 Establishment of numeric criteria for priority toxic pollutants for the State of California. 7/1/2011 Edition |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
Data for this line of evidence for Klamath River HU, Shasta River HA was collected at 1 monitoring site [ Shasta River at Hwy 263 - 105SHA263] |
Temporal Representation: |
Data was collected over the time period 11/15/2007-7/16/2008. |
Environmental Conditions: |
Staff is not aware of any special conditions that might affect interpretation of the data. |
QAPP Information: |
The SWAMP QAPP (2008) was followed. |
QAPP Information Reference(s): |
Surface Water Ambient Monitoring Program Quality Assurance Program Plan |
|
Line of Evidence (LOE) for Decision ID 105200, Heptachlor epoxide
|
Region 1 |
Klamath River HU, Shasta River HA |
|
|
LOE ID: |
123459 |
|
Pollutant: |
Heptachlor epoxide |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
None |
|
Beneficial Use: |
Municipal & Domestic Supply |
|
Number of Samples: |
0 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
State Water Board staff re-assessed SWAMP data for Klamath River HU, Shasta River HA to determine beneficial use support and results are as follows: 0 of 0 samples exceed the criterion for Heptachlor Epoxide, Total. Eight sample results were not used in the assessment because the laboratory data reporting limit(s) was above the objective and therefore the results could not be quantified with the level of certainty required by the Listing Policy. This LOE re-assesses data from LOE 29849 from the 2010 Integrated Report. Data were re-assessed in order to (1) update the numeric objective, and (2) evaluate these data in their own LOE, instead of being evaluated in the same LOE as other pesticide data. |
Data Reference: |
Surface Water Ambient Monitoring Program (SWAMP). Summary Report for the North Coast Region (RWQCB-1) for years 2000-2006. North Coast Regional Water Quality Control Board. March 2008 |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
Water Quality Control Plan, North Coast Region (NCRWQCB 2011): All waters shall be maintained free of toxic substances in concentrations that are toxic to, or that produce detrimental physiological responses in human, plant, animal, or aquatic life. The established numeric criteria for heptachlor to protect of human health from the consumption of water and organisms is 0.00021 ug/L (California Toxics Rule, 2000). |
Objective/Criterion Reference: |
Water Quality Control Plan (Basin Plan) for the North Coast Region |
Objective/Criterion Reference: |
Code of Federal Regulations 40 part 131.38 Establishment of numeric criteria for priority toxic pollutants for the State of California. 7/1/2011 Edition |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
Data for this line of evidence for Klamath River HU, Shasta River HA was collected at 1 monitoring site [ Shasta River at Montague - 105SHAMON] |
Temporal Representation: |
Data was collected over the time period 10/7/2002-6/19/2003. |
Environmental Conditions: |
There are no known environmental conditions (e.g., seasonality, land use practices, fire events, storms, etc.) that are related to these data. |
QAPP Information: |
Quality control was conducted in accordance with the SWAMP Quality Assurance Management Plan (SWAMP 2002). |
QAPP Information Reference(s): |
Quality Assurance Management Plan for the State of California's Surface Water Ambient Monitoring Program. Sacramento, CA. State Water Resources Control Board. SWAMP. December 2002 (1st version)
|
|
Line of Evidence (LOE) for Decision ID 105200, Heptachlor epoxide
|
Region 1 |
Klamath River HU, Shasta River HA |
|
|
LOE ID: |
123466 |
|
Pollutant: |
Heptachlor epoxide |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
None |
|
Beneficial Use: |
Municipal & Domestic Supply |
|
Number of Samples: |
0 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
State Water Board staff re-assessed SWAMP data for Klamath River HU, Shasta River HA to determine beneficial use support and results are as follows: 0 of 0 samples exceed the criterion for Heptachlor Epoxide, Total. Eight sample results were not used in the assessment because the laboratory data reporting limit(s) was above the objective and therefore the results could not be quantified with the level of certainty required by the Listing Policy. This LOE re-assesses data from LOE 29849 from the 2010 Integrated Report. Data were re-assessed in order to (1) update the numeric objective, and (2) evaluate these data in their own LOE, instead of being evaluated in the same LOE as other pesticide data. |
Data Reference: |
Surface Water Ambient Monitoring Program (SWAMP). Summary Report for the North Coast Region (RWQCB-1) for years 2000-2006. North Coast Regional Water Quality Control Board. March 2008 |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
Water Quality Control Plan, North Coast Region (NCRWQCB 2011): All waters shall be maintained free of toxic substances in concentrations that are toxic to, or that produce detrimental physiological responses in human, plant, animal, or aquatic life. The established numeric criteria for heptachlor to protect of human health from the consumption of water and organisms is 0.00021 ug/L (California Toxics Rule, 2000). |
Objective/Criterion Reference: |
Water Quality Control Plan (Basin Plan) for the North Coast Region |
Objective/Criterion Reference: |
Code of Federal Regulations 40 part 131.38 Establishment of numeric criteria for priority toxic pollutants for the State of California. 7/1/2011 Edition |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
Data for this line of evidence for Klamath River HU, Shasta River HA was collected at 1 monitoring site [ Shasta River near Edgewood - 105SH9274] |
Temporal Representation: |
Data was collected over the time period 10/7/2002-6/19/2003. |
Environmental Conditions: |
There are no known environmental conditions (e.g., seasonality, land use practices, fire events, storms, etc.) that are related to these data. |
QAPP Information: |
Quality control was conducted in accordance with the SWAMP Quality Assurance Management Plan (SWAMP 2002). |
QAPP Information Reference(s): |
Quality Assurance Management Plan for the State of California's Surface Water Ambient Monitoring Program. Sacramento, CA. State Water Resources Control Board. SWAMP. December 2002 (1st version)
|
|
Line of Evidence (LOE) for Decision ID 105200, Heptachlor epoxide
|
Region 1 |
Klamath River HU, Shasta River HA |
|
|
LOE ID: |
123458 |
|
Pollutant: |
Heptachlor epoxide |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
None |
|
Beneficial Use: |
Municipal & Domestic Supply |
|
Number of Samples: |
0 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
State Water Board staff re-assessed SWAMP data for Klamath River HU, Shasta River HA to determine beneficial use support and results are as follows: 0 of 0 samples exceed the criterion for Heptachlor Epoxide, Total. Seventeen sample results were not used in the assessment because the laboratory data reporting limit(s) was above the objective and therefore the results could not be quantified with the level of certainty required by the Listing Policy. This LOE re-assesses data from LOE 29849 from the 2010 Integrated Report. Data were re-assessed in order to (1) update the numeric objective, and (2) evaluate these data in their own LOE, instead of being evaluated in the same LOE as other pesticide data. |
Data Reference: |
Surface Water Ambient Monitoring Program (SWAMP). Summary Report for the North Coast Region (RWQCB-1) for years 2000-2006. North Coast Regional Water Quality Control Board. March 2008 |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
Water Quality Control Plan, North Coast Region (NCRWQCB 2011): All waters shall be maintained free of toxic substances in concentrations that are toxic to, or that produce detrimental physiological responses in human, plant, animal, or aquatic life. The established numeric criteria for heptachlor epoxide to protect of human health from the consumption of water and organisms is 0.00010 ug/L (California Toxics Rule, 2000). |
Objective/Criterion Reference: |
Water Quality Control Plan (Basin Plan) for the North Coast Region |
Objective/Criterion Reference: |
Code of Federal Regulations 40 part 131.38 Establishment of numeric criteria for priority toxic pollutants for the State of California. 7/1/2011 Edition |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
Data for this line of evidence for Klamath River HU, Shasta River HA was collected at 1 monitoring site [ Shasta River at Hwy 263 - 105SH1452] |
Temporal Representation: |
Data was collected over the time period 4/24/2001-11/16/2006. |
Environmental Conditions: |
There are no known environmental conditions (e.g., seasonality, land use practices, fire events, storms, etc.) that are related to these data. |
QAPP Information: |
Quality control was conducted in accordance with the SWAMP Quality Assurance Management Plan (SWAMP 2002). |
QAPP Information Reference(s): |
Quality Assurance Management Plan for the State of California's Surface Water Ambient Monitoring Program. Sacramento, CA. State Water Resources Control Board. SWAMP. December 2002 (1st version)
|
|
Line of Evidence (LOE) for Decision ID 105200, Heptachlor epoxide
|
Region 1 |
Klamath River HU, Shasta River HA |
|
|
LOE ID: |
109566 |
|
Pollutant: |
Heptachlor epoxide |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Total |
|
Beneficial Use: |
Cold Freshwater Habitat |
|
Number of Samples: |
1 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP RWB1 Monitoring data for Klamath River HU, Shasta River HA to determine beneficial use support and results are as follows: 0 of 1 samples exceeded the water quality standard for Heptachlor Epoxide. |
Data Reference: |
Water Quality Assessment Data for the 2018 solicitation cycle submitted through CEDEN for SWAMP RWB1 Monitoring .
|
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
Water Quality Control Plan, North Coast Region (NCRWQCB 2018): All waters shall be maintained free of toxic substances in concentrations that are toxic to, or that produce detrimental physiological responses in human, plant, animal, or aquatic life. The established numeric criteria for heptachlor epoxide to protect aquatic life in freshwater criterion continuous concentration (expressed as a 4-day average) is 0.0038 ug/L (California Toxics Rule, 2000). |
Objective/Criterion Reference: |
Water Quality Standards 2000. Establishment of numeric criteria for priority toxic pollutants for the State of California: Rules and regulations. Federal Register Vol. 65, No. 97. Washington, D.C.: Environmental Protection Agency |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
The samples were collected at 1 monitoring site(s) (105SH9274) |
Temporal Representation: |
The samples were collected between the dates of 2013-04-29 and 2013-04-29 |
Environmental Conditions: |
|
QAPP Information: |
Quality Assurance Program Plan and Standard Operating Procedures for SWAMP program |
QAPP Information Reference(s): |
Quality Assurance Program Plans, Quality Assurance Project Plans, and Standard Operating Procedures for the SWAMP program |
|
Line of Evidence (LOE) for Decision ID 105200, Heptachlor epoxide
|
Region 1 |
Klamath River HU, Shasta River HA |
|
|
LOE ID: |
42176 |
|
Pollutant: |
Heptachlor epoxide |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Total |
|
Beneficial Use: |
Cold Freshwater Habitat |
|
Number of Samples: |
3 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP data for Klamath River HU, Shasta River HA to determine beneficial use support and results are as follows: 0 of 3 samples exceed the criterion for Heptachlor epoxide. |
Data Reference: |
RWB1 Trend Maintenance Periods FYs 2007 2008 |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
Water Quality Control Plan, North Coast Region (NCRWQCB 2011): All waters shall be maintained free of toxic substances in concentrations that are toxic to, or that produce detrimental physiological responses in human, plant, animal, or aquatic life. The established numeric criteria for heptachlor epoxide to protect aquatic life in freshwater criterion continuous concentration (expressed as a 4-day average) is 0.0038 ug/L (California Toxics Rule, 2000). |
Objective/Criterion Reference: |
Code of Federal Regulations 40 part 131.38 Establishment of numeric criteria for priority toxic pollutants for the State of California. 7/1/2011 Edition |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
Data for this line of evidence for Klamath River HU, Shasta River HA was collected at 1 monitoring site [ Shasta River near Edgewood - 105SHAEDG] |
Temporal Representation: |
Data was collected over the time period 11/15/2007-7/16/2008. |
Environmental Conditions: |
Staff is not aware of any special conditions that might affect interpretation of the data. |
QAPP Information: |
The SWAMP QAPP (2008) was followed. |
QAPP Information Reference(s): |
Surface Water Ambient Monitoring Program Quality Assurance Program Plan |
|
Line of Evidence (LOE) for Decision ID 105200, Heptachlor epoxide
|
Region 1 |
Klamath River HU, Shasta River HA |
|
|
LOE ID: |
42177 |
|
Pollutant: |
Heptachlor epoxide |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Total |
|
Beneficial Use: |
Cold Freshwater Habitat |
|
Number of Samples: |
3 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP data for Klamath River HU, Shasta River HA to determine beneficial use support and results are as follows: 0 of 3 samples exceed the criterion for Heptachlor epoxide. |
Data Reference: |
RWB1 Trend Maintenance Periods FYs 2007 2008 |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
Water Quality Control Plan, North Coast Region (NCRWQCB 2011): All waters shall be maintained free of toxic substances in concentrations that are toxic to, or that produce detrimental physiological responses in human, plant, animal, or aquatic life. The established numeric criteria for heptachlor epoxide to protect aquatic life in freshwater criterion continuous concentration (expressed as a 4-day average) is 0.0038 ug/L (California Toxics Rule, 2000). |
Objective/Criterion Reference: |
Code of Federal Regulations 40 part 131.38 Establishment of numeric criteria for priority toxic pollutants for the State of California. 7/1/2011 Edition |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
Data for this line of evidence for Klamath River HU, Shasta River HA was collected at 1 monitoring site [ Shasta River at Hwy 263 - 105SHA263] |
Temporal Representation: |
Data was collected over the time period 11/15/2007-7/16/2008. |
Environmental Conditions: |
Staff is not aware of any special conditions that might affect interpretation of the data. |
QAPP Information: |
The SWAMP QAPP (2008) was followed. |
QAPP Information Reference(s): |
Surface Water Ambient Monitoring Program Quality Assurance Program Plan |
|
Line of Evidence (LOE) for Decision ID 105200, Heptachlor epoxide
|
Region 1 |
Klamath River HU, Shasta River HA |
|
|
LOE ID: |
109565 |
|
Pollutant: |
Heptachlor epoxide |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Total |
|
Beneficial Use: |
Cold Freshwater Habitat |
|
Number of Samples: |
1 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP RWB1 Monitoring data for Klamath River HU, Shasta River HA to determine beneficial use support and results are as follows: 0 of 1 samples exceeded the water quality standard for Heptachlor Epoxide. |
Data Reference: |
Water Quality Assessment Data for the 2018 solicitation cycle submitted through CEDEN for SWAMP RWB1 Monitoring .
|
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
Water Quality Control Plan, North Coast Region (NCRWQCB 2018): All waters shall be maintained free of toxic substances in concentrations that are toxic to, or that produce detrimental physiological responses in human, plant, animal, or aquatic life. The established numeric criteria for heptachlor epoxide to protect aquatic life in freshwater criterion continuous concentration (expressed as a 4-day average) is 0.0038 ug/L (California Toxics Rule, 2000). |
Objective/Criterion Reference: |
Water Quality Standards 2000. Establishment of numeric criteria for priority toxic pollutants for the State of California: Rules and regulations. Federal Register Vol. 65, No. 97. Washington, D.C.: Environmental Protection Agency |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
The samples were collected at 1 monitoring site(s) (105SH1452) |
Temporal Representation: |
The samples were collected between the dates of 2013-04-29 and 2013-04-29 |
Environmental Conditions: |
|
QAPP Information: |
Quality Assurance Program Plan and Standard Operating Procedures for SWAMP program |
QAPP Information Reference(s): |
Quality Assurance Program Plans, Quality Assurance Project Plans, and Standard Operating Procedures for the SWAMP program |
|
Line of Evidence (LOE) for Decision ID 105200, Heptachlor epoxide
|
Region 1 |
Klamath River HU, Shasta River HA |
|
|
LOE ID: |
42158 |
|
Pollutant: |
Heptachlor epoxide |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Total |
|
Beneficial Use: |
Commercial or recreational collection of fish, shellfish, or organisms |
|
Number of Samples: |
0 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Three non-detect sample results were not used in the assessment because the laboratory data reporting limit was above the objective and therefore the results could not be quantified with the level of certainty required by the Listing Policy. |
Data Reference: |
RWB1 Trend Maintenance Periods FYs 2007 2008 |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
Water Quality Control Plan, North Coast Region (NCRWQCB 2011): All waters shall be maintained free of toxic substances in concentrations that are toxic to, or that produce detrimental physiological responses in human, plant, animal, or aquatic life. The established numeric criteria for heptachlor epoxide to protect human health from consumption of organisms only is 0.00011 ug/L (California Toxics Rule, 2000). |
Objective/Criterion Reference: |
Code of Federal Regulations 40 part 131.38 Establishment of numeric criteria for priority toxic pollutants for the State of California. 7/1/2011 Edition |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
Data for this line of evidence for Klamath River HU, Shasta River HA was collected at 1 monitoring site [ Shasta River near Edgewood - 105SHAEDG] |
Temporal Representation: |
Data was collected over the time period 11/15/2007-7/16/2008. |
Environmental Conditions: |
Staff is not aware of any special conditions that might affect interpretation of the data. |
QAPP Information: |
The SWAMP QAPP (2008) was followed. |
QAPP Information Reference(s): |
Surface Water Ambient Monitoring Program Quality Assurance Program Plan |
|
Line of Evidence (LOE) for Decision ID 105200, Heptachlor epoxide
|
Region 1 |
Klamath River HU, Shasta River HA |
|
|
LOE ID: |
114143 |
|
Pollutant: |
Heptachlor epoxide |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Total |
|
Beneficial Use: |
Commercial or recreational collection of fish, shellfish, or organisms |
|
Number of Samples: |
0 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP RWB1 Monitoring data for Klamath River HU, Shasta River HA to determine beneficial use support, and the results are as follows: 0 of the 0 samples exceeded the evaluation guideline for Heptachlor Epoxide. Although a total of 1 samples were collected, 1 of these samples were not included in the assessment because the laboratory data reporting limit(s) was above the objective and therefore the results could not be quantified with the level of certainty required by the Listing Policy Section 6.1.5.5. |
Data Reference: |
Water Quality Assessment Data for the 2018 solicitation cycle submitted through CEDEN for SWAMP RWB1 Monitoring .
|
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
Water Quality Control Plan, North Coast Region (NCRWQCB 2018): All waters shall be maintained free of toxic substances in concentrations that are toxic to, or that produce detrimental physiological responses in human, plant, animal, or aquatic life. The established numeric criteria for heptachlor epoxide to protect human health from consumption of organisms only is 0.00011 ug/L (California Toxics Rule, 2000). |
Objective/Criterion Reference: |
Water Quality Standards 2000. Establishment of numeric criteria for priority toxic pollutants for the State of California: Rules and regulations. Federal Register Vol. 65, No. 97. Washington, D.C.: Environmental Protection Agency |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
Data was collected from 1 station(s) (Station Code(s) 105SH9274). |
Temporal Representation: |
Date for this waterbody was collected over the date range 2013-04-29 to 2013-04-29 |
Environmental Conditions: |
|
QAPP Information: |
Quality Assurance Program Plan and Standard Operating Procedures for SWAMP program |
QAPP Information Reference(s): |
Quality Assurance Program Plans, Quality Assurance Project Plans, and Standard Operating Procedures for the SWAMP program |
|
Line of Evidence (LOE) for Decision ID 105200, Heptachlor epoxide
|
Region 1 |
Klamath River HU, Shasta River HA |
|
|
LOE ID: |
123467 |
|
Pollutant: |
Heptachlor epoxide |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
None |
|
Beneficial Use: |
Municipal & Domestic Supply |
|
Number of Samples: |
0 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
State Water Board staff re-assessed SWAMP data for Klamath River HU, Shasta River HA to determine beneficial use support and results are as follows: 0 of 0 samples exceed the criterion for Heptachlor Epoxide, Total. Sixteen sample results were not used in the assessment because the laboratory data reporting limit(s) was above the objective and therefore the results could not be quantified with the level of certainty required by the Listing Policy. This LOE re-assesses data from LOE 29849 from the 2010 Integrated Report. Data were re-assessed in order to (1) update the numeric objective, and (2) evaluate these data in their own LOE, instead of being evaluated in the same LOE as other pesticide data. |
Data Reference: |
Surface Water Ambient Monitoring Program (SWAMP). Summary Report for the North Coast Region (RWQCB-1) for years 2000-2006. North Coast Regional Water Quality Control Board. March 2008 |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
Water Quality Control Plan, North Coast Region (NCRWQCB 2011): All waters shall be maintained free of toxic substances in concentrations that are toxic to, or that produce detrimental physiological responses in human, plant, animal, or aquatic life. The established numeric criteria for heptachlor to protect of human health from the consumption of water and organisms is 0.00021 ug/L (California Toxics Rule, 2000). |
Objective/Criterion Reference: |
Water Quality Control Plan (Basin Plan) for the North Coast Region |
Objective/Criterion Reference: |
Code of Federal Regulations 40 part 131.38 Establishment of numeric criteria for priority toxic pollutants for the State of California. 7/1/2011 Edition |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
Data for this line of evidence for Klamath River HU, Shasta River HA was collected at 1 monitoring site [ Yreka Creek at Anderson Rd - 105YREAND] |
Temporal Representation: |
Data was collected over the time period 10/9/2002-6/20/2005. |
Environmental Conditions: |
There are no known environmental conditions (e.g., seasonality, land use practices, fire events, storms, etc.) that are related to these data. |
QAPP Information: |
Quality control was conducted in accordance with the SWAMP Quality Assurance Management Plan (SWAMP 2002). |
QAPP Information Reference(s): |
Quality Assurance Management Plan for the State of California's Surface Water Ambient Monitoring Program. Sacramento, CA. State Water Resources Control Board. SWAMP. December 2002 (1st version)
|
|
Line of Evidence (LOE) for Decision ID 75453, Hexachlorobenzene/ HCB
|
Region 1 |
Klamath River HU, Shasta River HA |
|
|
LOE ID: |
42286 |
|
Pollutant: |
Hexachlorobenzene/ HCB |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Total |
|
Beneficial Use: |
Municipal & Domestic Supply |
|
Number of Samples: |
0 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Three non-detect sample results were not used in the assessment because the laboratory data reporting limit was above the objective and therefore the results could not be quantified with the level of certainty required by the Listing Policy. |
Data Reference: |
RWB1 Trend Maintenance Periods FYs 2007 2008 |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
Water Quality Control Plan, North Coast Region (NCRWQCB 2011): All waters shall be maintained free of toxic substances in concentrations that are toxic to, or that produce detrimental physiological responses in human, plant, animal, or aquatic life. The established numeric criteria for hexachlorobenzene to protect of human health from the consumption of water and organisms is 0.00075 ug/L (California Toxics Rule, 2000). |
Objective/Criterion Reference: |
Code of Federal Regulations 40 part 131.38 Establishment of numeric criteria for priority toxic pollutants for the State of California. 7/1/2011 Edition |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
Data for this line of evidence for Klamath River HU, Shasta River HA was collected at 1 monitoring site [ Shasta River at Hwy 263 - 105SHA263] |
Temporal Representation: |
Data was collected over the time period 11/15/2007-7/16/2008. |
Environmental Conditions: |
Staff is not aware of any special conditions that might affect interpretation of the data. |
QAPP Information: |
The SWAMP QAPP (2008) was followed. |
QAPP Information Reference(s): |
Surface Water Ambient Monitoring Program Quality Assurance Program Plan |
|
Line of Evidence (LOE) for Decision ID 75453, Hexachlorobenzene/ HCB
|
Region 1 |
Klamath River HU, Shasta River HA |
|
|
LOE ID: |
119240 |
|
Pollutant: |
Hexachlorobenzene/ HCB |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Total |
|
Beneficial Use: |
Municipal & Domestic Supply |
|
Number of Samples: |
0 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP RWB1 Monitoring data for Klamath River HU, Shasta River HA to determine beneficial use support, and the results are as follows: 0 of the 0 samples exceeded the evaluation guideline for Hexachlorobenzene. Although a total of 1 samples were collected, 1 of these samples were not included in the assessment because the laboratory data reporting limit(s) was above the objective and therefore the results could not be quantified with the level of certainty required by the Listing Policy Section 6.1.5.5. |
Data Reference: |
Water Quality Assessment Data for the 2018 solicitation cycle submitted through CEDEN for SWAMP RWB1 Monitoring .
|
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
Water Quality Control Plan, North Coast Region (NCRWQCB 2018): All waters shall be maintained free of toxic substances in concentrations that are toxic to, or that produce detrimental physiological responses in human, plant, animal, or aquatic life. The established numeric criteria for hexachlorobenzene to protect of human health from the consumption of water and organisms is 0.00075 ug/L (California Toxics Rule, 2000). |
Objective/Criterion Reference: |
Water Quality Standards 2000. Establishment of numeric criteria for priority toxic pollutants for the State of California: Rules and regulations. Federal Register Vol. 65, No. 97. Washington, D.C.: Environmental Protection Agency |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
Data was collected from 1 station(s) (Station Code(s) 105SH9274). |
Temporal Representation: |
Date for this waterbody was collected over the date range 2013-04-29 to 2013-04-29 |
Environmental Conditions: |
|
QAPP Information: |
Quality Assurance Program Plan and Standard Operating Procedures for SWAMP program |
QAPP Information Reference(s): |
Quality Assurance Program Plans, Quality Assurance Project Plans, and Standard Operating Procedures for the SWAMP program |
|
Line of Evidence (LOE) for Decision ID 75453, Hexachlorobenzene/ HCB
|
Region 1 |
Klamath River HU, Shasta River HA |
|
|
LOE ID: |
46911 |
|
Pollutant: |
Hexachlorobenzene/ HCB |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Total |
|
Beneficial Use: |
Municipal & Domestic Supply |
|
Number of Samples: |
1 |
Number of Exceedances: |
1 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
One of one sample collected in the Shasta River watershed exceeded the objective. The sample concentration was 0.001 ug/L. An additional 31 non-detect sample results were not used in the assessment because the laboratory data reporting limit was above the objective and therefore the results could not be quantified with the level of certainty required by the Listing Policy. The samples were collected as part of the Surface Water Ambient Water Monitoring Program (SWAMP). The data are found in the 5-Year Monitoring Report (NCRWQCB 2008). This LOE re-assesses data from LOE 25612 from the 2010 Integrated Report in order to reflect that non-detect samples could not be assessed because they could not be quantified with the level of certainty required by the Listing Policy |
Data Reference: |
Surface Water Ambient Monitoring Program (SWAMP). Summary Report for the North Coast Region (RWQCB-1) for years 2000-2006. North Coast Regional Water Quality Control Board. March 2008 |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
Water Quality Control Plan, North Coast Region (NCRWQCB 2011): All waters shall be maintained free of toxic substances in concentrations that are toxic to, or that produce detrimental physiological responses in human, plant, animal, or aquatic life. The established numeric criteria for hexachlorobenzene to protect of human health from the consumption of water and organisms is 0.00075 ug/L (California Toxics Rule, 2000). |
Objective/Criterion Reference: |
Code of Federal Regulations 40 part 131.38 Establishment of numeric criteria for priority toxic pollutants for the State of California. 7/1/2011 Edition |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
Samples were collected in the Shasta River watershed from 5 locations as follows: (1) near Edgewood Road (SWAMP Station ID 105SHAEDG), (2) at Montague Grenada Road (SWAMP Station ID 105SHAMON), (3) at Highway 263 (SWAMP Station ID 105SHA263), (4) in Yreka Creek at Highway 3 (SWAMP Station ID 105YREHW3), and (5) in Yreka Creek at Anderson Grade Road (SWAMP Station ID 105YREAND). Samples were collected in well-mixed flows in glides or riffles. |
Temporal Representation: |
The samples from Edgewood Road and Montague Grenada Road were collected s grab samples during 5 site visits at each site during the 2002 - 2003 fiscal years. Samples from Highway 263 were collected as grab samples during 22 site visits during the 2000 - 2006 fiscal years. Samples in Yreka Creek were collected from October 2004 to June 2005. The site visits corresponded to fall, winter, spring and early summer seasonal conditions. |
Environmental Conditions: |
There are no known environmental conditions (e.g., seasonality, land use practices, fire events, storms, etc.) that are related to these data. |
QAPP Information: |
Quality control was conducted in accordance with the SWAMP Quality Assurance Management Plan (SWAMP 2002). |
QAPP Information Reference(s): |
Quality Assurance Management Plan for the State of California's Surface Water Ambient Monitoring Program. Sacramento, CA. State Water Resources Control Board. SWAMP. December 2002 (1st version)
|
|
Line of Evidence (LOE) for Decision ID 75453, Hexachlorobenzene/ HCB
|
Region 1 |
Klamath River HU, Shasta River HA |
|
|
LOE ID: |
42285 |
|
Pollutant: |
Hexachlorobenzene/ HCB |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Total |
|
Beneficial Use: |
Municipal & Domestic Supply |
|
Number of Samples: |
0 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Three non-detect sample results were not used in the assessment because the laboratory data reporting limit was above the objective and therefore the results could not be quantified with the level of certainty required by the Listing Policy. |
Data Reference: |
RWB1 Trend Maintenance Periods FYs 2007 2008 |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
Water Quality Control Plan, North Coast Region (NCRWQCB 2011): All waters shall be maintained free of toxic substances in concentrations that are toxic to, or that produce detrimental physiological responses in human, plant, animal, or aquatic life. The established numeric criteria for hexachlorobenzene to protect of human health from the consumption of water and organisms is 0.00075 ug/L (California Toxics Rule, 2000). |
Objective/Criterion Reference: |
Code of Federal Regulations 40 part 131.38 Establishment of numeric criteria for priority toxic pollutants for the State of California. 7/1/2011 Edition |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
Data for this line of evidence for Klamath River HU, Shasta River HA was collected at 1 monitoring site [ Shasta River near Edgewood - 105SHAEDG] |
Temporal Representation: |
Data was collected over the time period 11/15/2007-7/16/2008. |
Environmental Conditions: |
Staff is not aware of any special conditions that might affect interpretation of the data. |
QAPP Information: |
The SWAMP QAPP (2008) was followed. |
QAPP Information Reference(s): |
Surface Water Ambient Monitoring Program Quality Assurance Program Plan |
|
Line of Evidence (LOE) for Decision ID 75453, Hexachlorobenzene/ HCB
|
Region 1 |
Klamath River HU, Shasta River HA |
|
|
LOE ID: |
25612 |
|
Pollutant: |
Hexachlorobenzene/ HCB |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
None |
|
Beneficial Use: |
Municipal & Domestic Supply |
|
Number of Samples: |
32 |
Number of Exceedances: |
2 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Two of the 32 hexachlorobenzene samples collected in the Shasta River watershed exceed the evaluation guideline. Sample concentrations range from non-detect (with a reporting limit of 0.001 ug/l) to 0.001 ug/l. The samples were collected as part of the Surface Water Ambient Water Monitoring Program (SWAMP). The data are found in the 5-Year Monitoring Report (NCRWQCB 2008). |
Data Reference: |
Surface Water Ambient Monitoring Program (SWAMP). Summary Report for the North Coast Region (RWQCB-1) for years 2000-2006. North Coast Regional Water Quality Control Board. March 2008 |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
Per the Basin Plan (NCRWQCB 2007): No individual pesticide or combination of pesticides shall be present in concentrations that adversely affect beneficial uses. There shall be no bioaccumulation of pesticide concentrations found in bottom sediments or aquatic life. Waters designated for use as domestic or municipal supply shall not contain concentrations of pesticides in excess of the limiting concentrations set forth in California Code of Regulations, Title 22, Division 4, Chapter 15, Article 4, Section 64444, and listed in Table 3.2 of the Basin Plan. |
Objective/Criterion Reference: |
Water Quality Control Plan (Basin Plan) - North Coast Region (Region 1) |
|
Evaluation Guideline: |
Per the National Recommended Water Quality Criteria (USEPA 2006): The recommended criterion for hexachlorobenzene for the protection of source waters for human health consumption of water and organisms is 0.00028 ug/l. |
Guideline Reference: |
National Recommended Water Quality Criteria. United States Environmental Protection Agency. Office of Water. Office of Science and Technology |
|
Spatial Representation: |
Samples were collected in the Shasta River watershed from 5 locations as follows: (1) near Edgewood Road (SWAMP Station ID 105SHAEDG), (2) at Montague Grenada Road (SWAMP Station ID 105SHAMON), (3) at Highway 263 (SWAMP Station ID 105SHA263), (4) in Yreka Creek at Highway 3 (SWAMP Station ID 105YREHW3), and (5) in Yreka Creek at Anderson Grade Road (SWAMP Station ID 105YREAND). Samples were collected in well-mixed flows in glides or riffles. |
Temporal Representation: |
The samples from Edgewood Road and Montague Grenada Road were collected as grab samples during 5 site visits at each site during the 2002 - 2003 fiscal years. Samples from Highway 263 were collected as grab samples during 22 site visits during the 2000 - 2006 fiscal years. Samples in Yreka Creek were collected from October 2004 to June 2005. The site visits corresponded to fall, winter, spring and early summer seasonal conditions. |
Environmental Conditions: |
There are no known environmental conditions (e.g., seasonality, land use practices, fire events, storms, etc.) that are related to these data. |
QAPP Information: |
Quality control was conducted in accordance with the SWAMP Quality Assurance Management Plan (SWAMP 2002). |
QAPP Information Reference(s): |
Quality Assurance Management Plan for the State of California's Surface Water Ambient Monitoring Program. Sacramento, CA. State Water Resources Control Board. SWAMP. December 2002 (1st version)
|
|
Line of Evidence (LOE) for Decision ID 75453, Hexachlorobenzene/ HCB
|
Region 1 |
Klamath River HU, Shasta River HA |
|
|
LOE ID: |
107679 |
|
Pollutant: |
Hexachlorobenzene/ HCB |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Total |
|
Beneficial Use: |
Commercial or recreational collection of fish, shellfish, or organisms |
|
Number of Samples: |
0 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP RWB1 Monitoring data for Klamath River HU, Shasta River HA to determine beneficial use support, and the results are as follows: 0 of the 0 samples exceeded the evaluation guideline for Hexachlorobenzene. Although a total of 1 samples were collected, 1 of these samples were not included in the assessment because the laboratory data reporting limit(s) was above the objective and therefore the results could not be quantified with the level of certainty required by the Listing Policy Section 6.1.5.5. |
Data Reference: |
Water Quality Assessment Data for the 2018 solicitation cycle submitted through CEDEN for SWAMP RWB1 Monitoring .
|
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
Water Quality Control Plan, North Coast Region (NCRWQCB 2018): All waters shall be maintained free of toxic substances in concentrations that are toxic to, or that produce detrimental physiological responses in human, plant, animal, or aquatic life. The established numeric criteria for hexachlorobenzene to protect human health from consumption of organisms only is 0.00077 ug/L (California Toxics Rule, 2000). |
Objective/Criterion Reference: |
Water Quality Standards 2000. Establishment of numeric criteria for priority toxic pollutants for the State of California: Rules and regulations. Federal Register Vol. 65, No. 97. Washington, D.C.: Environmental Protection Agency |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
Data was collected from 1 station(s) (Station Code(s) 105SH1452). |
Temporal Representation: |
Date for this waterbody was collected over the date range 2013-04-29 to 2013-04-29 |
Environmental Conditions: |
|
QAPP Information: |
Quality Assurance Program Plan and Standard Operating Procedures for SWAMP program |
QAPP Information Reference(s): |
Quality Assurance Program Plans, Quality Assurance Project Plans, and Standard Operating Procedures for the SWAMP program |
|
Line of Evidence (LOE) for Decision ID 75453, Hexachlorobenzene/ HCB
|
Region 1 |
Klamath River HU, Shasta River HA |
|
|
LOE ID: |
119239 |
|
Pollutant: |
Hexachlorobenzene/ HCB |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Total |
|
Beneficial Use: |
Commercial or recreational collection of fish, shellfish, or organisms |
|
Number of Samples: |
0 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP RWB1 Monitoring data for Klamath River HU, Shasta River HA to determine beneficial use support, and the results are as follows: 0 of the 0 samples exceeded the evaluation guideline for Hexachlorobenzene. Although a total of 1 samples were collected, 1 of these samples were not included in the assessment because the laboratory data reporting limit(s) was above the objective and therefore the results could not be quantified with the level of certainty required by the Listing Policy Section 6.1.5.5. |
Data Reference: |
Water Quality Assessment Data for the 2018 solicitation cycle submitted through CEDEN for SWAMP RWB1 Monitoring .
|
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
Water Quality Control Plan, North Coast Region (NCRWQCB 2018): All waters shall be maintained free of toxic substances in concentrations that are toxic to, or that produce detrimental physiological responses in human, plant, animal, or aquatic life. The established numeric criteria for hexachlorobenzene to protect human health from consumption of organisms only is 0.00077 ug/L (California Toxics Rule, 2000). |
Objective/Criterion Reference: |
Water Quality Standards 2000. Establishment of numeric criteria for priority toxic pollutants for the State of California: Rules and regulations. Federal Register Vol. 65, No. 97. Washington, D.C.: Environmental Protection Agency |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
Data was collected from 1 station(s) (Station Code(s) 105SH9274). |
Temporal Representation: |
Date for this waterbody was collected over the date range 2013-04-29 to 2013-04-29 |
Environmental Conditions: |
|
QAPP Information: |
Quality Assurance Program Plan and Standard Operating Procedures for SWAMP program |
QAPP Information Reference(s): |
Quality Assurance Program Plans, Quality Assurance Project Plans, and Standard Operating Procedures for the SWAMP program |
|
Line of Evidence (LOE) for Decision ID 75453, Hexachlorobenzene/ HCB
|
Region 1 |
Klamath River HU, Shasta River HA |
|
|
LOE ID: |
42225 |
|
Pollutant: |
Hexachlorobenzene/ HCB |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Total |
|
Beneficial Use: |
Commercial or recreational collection of fish, shellfish, or organisms |
|
Number of Samples: |
0 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Three non-detect sample results were not used in the assessment because the laboratory data reporting limit was above the objective and therefore the results could not be quantified with the level of certainty required by the Listing Policy. |
Data Reference: |
RWB1 Trend Maintenance Periods FYs 2007 2008 |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
Water Quality Control Plan, North Coast Region (NCRWQCB 2011): All waters shall be maintained free of toxic substances in concentrations that are toxic to, or that produce detrimental physiological responses in human, plant, animal, or aquatic life. The established numeric criteria for hexachlorobenzene to protect human health from consumption of organisms only is 0.00077 ug/L (California Toxics Rule, 2000). |
Objective/Criterion Reference: |
Code of Federal Regulations 40 part 131.38 Establishment of numeric criteria for priority toxic pollutants for the State of California. 7/1/2011 Edition |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
Data for this line of evidence for Klamath River HU, Shasta River HA was collected at 1 monitoring site [ Shasta River near Edgewood - 105SHAEDG] |
Temporal Representation: |
Data was collected over the time period 11/15/2007-7/16/2008. |
Environmental Conditions: |
Staff is not aware of any special conditions that might affect interpretation of the data. |
QAPP Information: |
The SWAMP QAPP (2008) was followed. |
QAPP Information Reference(s): |
Surface Water Ambient Monitoring Program Quality Assurance Program Plan |
|
Line of Evidence (LOE) for Decision ID 75453, Hexachlorobenzene/ HCB
|
Region 1 |
Klamath River HU, Shasta River HA |
|
|
LOE ID: |
42226 |
|
Pollutant: |
Hexachlorobenzene/ HCB |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Total |
|
Beneficial Use: |
Commercial or recreational collection of fish, shellfish, or organisms |
|
Number of Samples: |
0 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Three non-detect sample results were not used in the assessment because the laboratory data reporting limit was above the objective and therefore the results could not be quantified with the level of certainty required by the Listing Policy. |
Data Reference: |
RWB1 Trend Maintenance Periods FYs 2007 2008 |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
Water Quality Control Plan, North Coast Region (NCRWQCB 2011): All waters shall be maintained free of toxic substances in concentrations that are toxic to, or that produce detrimental physiological responses in human, plant, animal, or aquatic life. The established numeric criteria for hexachlorobenzene to protect human health from consumption of organisms only is 0.00077 ug/L (California Toxics Rule, 2000). |
Objective/Criterion Reference: |
Code of Federal Regulations 40 part 131.38 Establishment of numeric criteria for priority toxic pollutants for the State of California. 7/1/2011 Edition |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
Data for this line of evidence for Klamath River HU, Shasta River HA was collected at 1 monitoring site [ Shasta River at Hwy 263 - 105SHA263] |
Temporal Representation: |
Data was collected over the time period 11/15/2007-7/16/2008. |
Environmental Conditions: |
Staff is not aware of any special conditions that might affect interpretation of the data. |
QAPP Information: |
The SWAMP QAPP (2008) was followed. |
QAPP Information Reference(s): |
Surface Water Ambient Monitoring Program Quality Assurance Program Plan |
|
Line of Evidence (LOE) for Decision ID 75453, Hexachlorobenzene/ HCB
|
Region 1 |
Klamath River HU, Shasta River HA |
|
|
LOE ID: |
115583 |
|
Pollutant: |
Hexachlorobenzene/ HCB |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Total |
|
Beneficial Use: |
Municipal & Domestic Supply |
|
Number of Samples: |
0 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP RWB1 Monitoring data for Klamath River HU, Shasta River HA to determine beneficial use support, and the results are as follows: 0 of the 0 samples exceeded the evaluation guideline for Hexachlorobenzene. Although a total of 1 samples were collected, 1 of these samples were not included in the assessment because the laboratory data reporting limit(s) was above the objective and therefore the results could not be quantified with the level of certainty required by the Listing Policy Section 6.1.5.5. |
Data Reference: |
Water Quality Assessment Data for the 2018 solicitation cycle submitted through CEDEN for SWAMP RWB1 Monitoring .
|
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
Water Quality Control Plan, North Coast Region (NCRWQCB 2018): All waters shall be maintained free of toxic substances in concentrations that are toxic to, or that produce detrimental physiological responses in human, plant, animal, or aquatic life. The established numeric criteria for hexachlorobenzene to protect of human health from the consumption of water and organisms is 0.00075 ug/L (California Toxics Rule, 2000). |
Objective/Criterion Reference: |
Water Quality Standards 2000. Establishment of numeric criteria for priority toxic pollutants for the State of California: Rules and regulations. Federal Register Vol. 65, No. 97. Washington, D.C.: Environmental Protection Agency |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
Data was collected from 1 station(s) (Station Code(s) 105SH1452). |
Temporal Representation: |
Date for this waterbody was collected over the date range 2013-04-29 to 2013-04-29 |
Environmental Conditions: |
|
QAPP Information: |
Quality Assurance Program Plan and Standard Operating Procedures for SWAMP program |
QAPP Information Reference(s): |
Quality Assurance Program Plans, Quality Assurance Project Plans, and Standard Operating Procedures for the SWAMP program |
|
Line of Evidence (LOE) for Decision ID 104947, Lead
|
Region 1 |
Klamath River HU, Shasta River HA |
|
|
LOE ID: |
119986 |
|
Pollutant: |
Lead |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Dissolved |
|
Beneficial Use: |
Cold Freshwater Habitat |
|
Number of Samples: |
5 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP RWB1 Monitoring data for Klamath River HU, Shasta River HA to determine beneficial use support and results are as follows: 0 of 5 samples exceeded the water quality standard for Lead. |
Data Reference: |
Water Quality Assessment Data for the 2018 solicitation cycle submitted through CEDEN for SWAMP RWB1 Monitoring .
|
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
California Toxics Rule (CTR) lists criterion continuous concentrations to protect aquatic life in freshwater. The criterion in freshwater is hardness dependent for each sample and varies based on the ambient hardness during sampling. Section (b)(1) in CTR contains the hardness dependent formula for the metals criterion. |
Objective/Criterion Reference: |
Water Quality Standards 2000. Establishment of numeric criteria for priority toxic pollutants for the State of California: Rules and regulations. Federal Register Vol. 65, No. 97. Washington, D.C.: Environmental Protection Agency |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
The samples were collected at 1 monitoring site(s) (105SH1452) |
Temporal Representation: |
The samples were collected between the dates of 2013-03-06 and 2013-11-20 |
Environmental Conditions: |
|
QAPP Information: |
Quality Assurance Program Plan and Standard Operating Procedures for SWAMP program |
QAPP Information Reference(s): |
Quality Assurance Program Plans, Quality Assurance Project Plans, and Standard Operating Procedures for the SWAMP program |
|
Line of Evidence (LOE) for Decision ID 104947, Lead
|
Region 1 |
Klamath River HU, Shasta River HA |
|
|
LOE ID: |
123476 |
|
Pollutant: |
Lead |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Total |
|
Beneficial Use: |
Municipal & Domestic Supply |
|
Number of Samples: |
5 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
State Water Board staff re-assessed SWAMP data for Klamath River HU, Shasta River HA to determine beneficial use support and results are as follows: 0 of 5 samples exceed the criterion for Lead, Total. This LOE re-assesses data from LOE 21509 from the 2010 Integrated Report. Data were re-assessed in order to evaluate these data in their own LOE, instead of being evaluated in the same LOE as other metals data. |
Data Reference: |
Surface Water Ambient Monitoring Program (SWAMP). Summary Report for the North Coast Region (RWQCB-1) for years 2000-2006. North Coast Regional Water Quality Control Board. March 2008 |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
Water Quality Control Plan, North Coast Region (NCRWQCB 2011): Waters designated for MUN shall not contain concentrations of chemical constituents in excess of values listed in Table 3-2 of the Basin Plan. The value for lead is 0.05 mg/L. |
Objective/Criterion Reference: |
Water Quality Control Plan (Basin Plan) for the North Coast Region |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
Data for this line of evidence for Klamath River HU, Shasta River HA was collected at 1 monitoring site [ Shasta River at Montague - 105SHAMON] |
Temporal Representation: |
Data was collected over the time period 10/7/2002-6/19/2003. |
Environmental Conditions: |
There are no known environmental conditions (e.g., seasonality, land use practices, fire events, storms, etc.) that are related to these data. |
QAPP Information: |
Quality control was conducted in accordance with the SWAMP Quality Assurance Management Plan (SWAMP 2002). |
QAPP Information Reference(s): |
Quality Assurance Management Plan for the State of California's Surface Water Ambient Monitoring Program. Sacramento, CA. State Water Resources Control Board. SWAMP. December 2002 (1st version)
|
|
Line of Evidence (LOE) for Decision ID 104947, Lead
|
Region 1 |
Klamath River HU, Shasta River HA |
|
|
LOE ID: |
123469 |
|
Pollutant: |
Lead |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Total |
|
Beneficial Use: |
Municipal & Domestic Supply |
|
Number of Samples: |
21 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
State Water Board staff re-assessed SWAMP data for Klamath River HU, Shasta River HA to determine beneficial use support and results are as follows: 0 of 21 samples exceed the criterion for Lead, Total. This LOE re-assesses data from LOE 21509 from the 2010 Integrated Report. Data were re-assessed in order to evaluate these data in their own LOE, instead of being evaluated in the same LOE as other metals data. |
Data Reference: |
Surface Water Ambient Monitoring Program (SWAMP). Summary Report for the North Coast Region (RWQCB-1) for years 2000-2006. North Coast Regional Water Quality Control Board. March 2008 |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
Water Quality Control Plan, North Coast Region (NCRWQCB 2011): Waters designated for MUN shall not contain concentrations of chemical constituents in excess of values listed in Table 3-2 of the Basin Plan. The value for lead is 0.05 mg/L. |
Objective/Criterion Reference: |
Water Quality Control Plan (Basin Plan) for the North Coast Region |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
Data for this line of evidence for Klamath River HU, Shasta River HA was collected at 1 monitoring site [ Shasta River at Hwy 263 - 105SH1452] |
Temporal Representation: |
Data was collected over the time period 3/20/2001-11/16/2006. |
Environmental Conditions: |
There are no known environmental conditions (e.g., seasonality, land use practices, fire events, storms, etc.) that are related to these data. |
QAPP Information: |
Quality control was conducted in accordance with the SWAMP Quality Assurance Management Plan (SWAMP 2002). |
QAPP Information Reference(s): |
Letter requesting acceptance of late submittal |
|
Line of Evidence (LOE) for Decision ID 104947, Lead
|
Region 1 |
Klamath River HU, Shasta River HA |
|
|
LOE ID: |
103296 |
|
Pollutant: |
Lead |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Total |
|
Beneficial Use: |
Municipal & Domestic Supply |
|
Number of Samples: |
5 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP RWB1 Monitoring data for Klamath River HU, Shasta River HA to determine beneficial use support and results are as follows: 0 of 5 samples exceeded the water quality standard for Lead. |
Data Reference: |
Water Quality Assessment Data for the 2018 solicitation cycle submitted through CEDEN for SWAMP RWB1 Monitoring .
|
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
Water Quality Control Plan, North Coast Region (NCRWQCB 2018): Waters designated for MUN shall not contain concentrations of chemical constituents in excess of values listed in Table 3-2 of the Basin Plan. The value for lead is 0.05 mg/L. |
Objective/Criterion Reference: |
Water Quality Control Plan (Basin Plan) for the North Coast Region |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
The samples were collected at 1 monitoring site(s) (105SH9274) |
Temporal Representation: |
The samples were collected between the dates of 2013-03-07 and 2013-11-20 |
Environmental Conditions: |
|
QAPP Information: |
Quality Assurance Program Plan and Standard Operating Procedures for SWAMP program |
QAPP Information Reference(s): |
Quality Assurance Program Plans, Quality Assurance Project Plans, and Standard Operating Procedures for the SWAMP program |
|
Line of Evidence (LOE) for Decision ID 104947, Lead
|
Region 1 |
Klamath River HU, Shasta River HA |
|
|
LOE ID: |
119988 |
|
Pollutant: |
Lead |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Dissolved |
|
Beneficial Use: |
Cold Freshwater Habitat |
|
Number of Samples: |
5 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP RWB1 Monitoring data for Klamath River HU, Shasta River HA to determine beneficial use support and results are as follows: 0 of 5 samples exceeded the water quality standard for Lead. |
Data Reference: |
Water Quality Assessment Data for the 2018 solicitation cycle submitted through CEDEN for SWAMP RWB1 Monitoring .
|
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
California Toxics Rule (CTR) lists criterion continuous concentrations to protect aquatic life in freshwater. The criterion in freshwater is hardness dependent for each sample and varies based on the ambient hardness during sampling. Section (b)(1) in CTR contains the hardness dependent formula for the metals criterion. |
Objective/Criterion Reference: |
Water Quality Standards 2000. Establishment of numeric criteria for priority toxic pollutants for the State of California: Rules and regulations. Federal Register Vol. 65, No. 97. Washington, D.C.: Environmental Protection Agency |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
The samples were collected at 1 monitoring site(s) (105SH9274) |
Temporal Representation: |
The samples were collected between the dates of 2013-03-07 and 2013-11-20 |
Environmental Conditions: |
|
QAPP Information: |
Quality Assurance Program Plan and Standard Operating Procedures for SWAMP program |
QAPP Information Reference(s): |
Quality Assurance Program Plans, Quality Assurance Project Plans, and Standard Operating Procedures for the SWAMP program |
|
Line of Evidence (LOE) for Decision ID 104947, Lead
|
Region 1 |
Klamath River HU, Shasta River HA |
|
|
LOE ID: |
123478 |
|
Pollutant: |
Lead |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Total |
|
Beneficial Use: |
Municipal & Domestic Supply |
|
Number of Samples: |
7 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
State Water Board staff re-assessed SWAMP data for Klamath River HU, Shasta River HA to determine beneficial use support and results are as follows: 0 of 7 samples exceed the criterion for Lead, Total. This LOE re-assesses data from LOE 21509 from the 2010 Integrated Report. Data were re-assessed in order to evaluate these data in their own LOE, instead of being evaluated in the same LOE as other metals data. |
Data Reference: |
Surface Water Ambient Monitoring Program (SWAMP). Summary Report for the North Coast Region (RWQCB-1) for years 2000-2006. North Coast Regional Water Quality Control Board. March 2008 |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
Water Quality Control Plan, North Coast Region (NCRWQCB 2011): Waters designated for MUN shall not contain concentrations of chemical constituents in excess of values listed in Table 3-2 of the Basin Plan. The value for lead is 0.05 mg/L. |
Objective/Criterion Reference: |
Water Quality Control Plan (Basin Plan) for the North Coast Region |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
Data for this line of evidence for Klamath River HU, Shasta River HA was collected at 1 monitoring site [ Yreka Creek at Anderson Rd - 105YREAND] |
Temporal Representation: |
Data was collected over the time period 10/9/2002-6/20/2005. |
Environmental Conditions: |
There are no known environmental conditions (e.g., seasonality, land use practices, fire events, storms, etc.) that are related to these data. |
QAPP Information: |
Quality control was conducted in accordance with the SWAMP Quality Assurance Management Plan (SWAMP 2002). |
QAPP Information Reference(s): |
Quality Assurance Management Plan for the State of California's Surface Water Ambient Monitoring Program. Sacramento, CA. State Water Resources Control Board. SWAMP. December 2002 (1st version)
|
|
Line of Evidence (LOE) for Decision ID 104947, Lead
|
Region 1 |
Klamath River HU, Shasta River HA |
|
|
LOE ID: |
123479 |
|
Pollutant: |
Lead |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Total |
|
Beneficial Use: |
Municipal & Domestic Supply |
|
Number of Samples: |
3 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
State Water Board staff re-assessed SWAMP data for Klamath River HU, Shasta River HA to determine beneficial use support and results are as follows: 0 of 3 samples exceed the criterion for Lead, Total. This LOE re-assesses data from LOE 21509 from the 2010 Integrated Report. Data were re-assessed in order to evaluate these data in their own LOE, instead of being evaluated in the same LOE as other metals data. |
Data Reference: |
Surface Water Ambient Monitoring Program (SWAMP). Summary Report for the North Coast Region (RWQCB-1) for years 2000-2006. North Coast Regional Water Quality Control Board. March 2008 |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
Water Quality Control Plan, North Coast Region (NCRWQCB 2011): Waters designated for MUN shall not contain concentrations of chemical constituents in excess of values listed in Table 3-2 of the Basin Plan. The value for lead is 0.05 mg/L. |
Objective/Criterion Reference: |
Water Quality Control Plan (Basin Plan) for the North Coast Region |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
Data for this line of evidence for Klamath River HU, Shasta River HA was collected at 1 monitoring site [ Yreka Creek at Highway 3 - 105YREHW3] |
Temporal Representation: |
Data was collected over the time period 10/21/2004-6/20/2005. |
Environmental Conditions: |
There are no known environmental conditions (e.g., seasonality, land use practices, fire events, storms, etc.) that are related to these data. |
QAPP Information: |
Quality control was conducted in accordance with the SWAMP Quality Assurance Management Plan (SWAMP 2002). |
QAPP Information Reference(s): |
Quality Assurance Management Plan for the State of California's Surface Water Ambient Monitoring Program. Sacramento, CA. State Water Resources Control Board. SWAMP. December 2002 (1st version)
|
|
Line of Evidence (LOE) for Decision ID 104947, Lead
|
Region 1 |
Klamath River HU, Shasta River HA |
|
|
LOE ID: |
123477 |
|
Pollutant: |
Lead |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Total |
|
Beneficial Use: |
Municipal & Domestic Supply |
|
Number of Samples: |
5 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
State Water Board staff re-assessed SWAMP data for Klamath River HU, Shasta River HA to determine beneficial use support and results are as follows: 0 of 5 samples exceed the criterion for Lead, Total. This LOE re-assesses data from LOE 21509 from the 2010 Integrated Report. Data were re-assessed in order to evaluate these data in their own LOE, instead of being evaluated in the same LOE as other metals data. |
Data Reference: |
Surface Water Ambient Monitoring Program (SWAMP). Summary Report for the North Coast Region (RWQCB-1) for years 2000-2006. North Coast Regional Water Quality Control Board. March 2008 |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
Water Quality Control Plan, North Coast Region (NCRWQCB 2011): Waters designated for MUN shall not contain concentrations of chemical constituents in excess of values listed in Table 3-2 of the Basin Plan. The value for lead is 0.05 mg/L. |
Objective/Criterion Reference: |
Water Quality Control Plan (Basin Plan) for the North Coast Region |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
Data for this line of evidence for Klamath River HU, Shasta River HA was collected at 1 monitoring site [ Shasta River near Edgewood - 105SH9274] |
Temporal Representation: |
Data was collected over the time period 10/7/2002-6/19/2003. |
Environmental Conditions: |
There are no known environmental conditions (e.g., seasonality, land use practices, fire events, storms, etc.) that are related to these data. |
QAPP Information: |
Quality control was conducted in accordance with the SWAMP Quality Assurance Management Plan (SWAMP 2002). |
QAPP Information Reference(s): |
Quality Assurance Management Plan for the State of California's Surface Water Ambient Monitoring Program. Sacramento, CA. State Water Resources Control Board. SWAMP. December 2002 (1st version)
|
|
Line of Evidence (LOE) for Decision ID 104947, Lead
|
Region 1 |
Klamath River HU, Shasta River HA |
|
|
LOE ID: |
42290 |
|
Pollutant: |
Lead |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Total |
|
Beneficial Use: |
Municipal & Domestic Supply |
|
Number of Samples: |
4 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP data for Klamath River HU, Shasta River HA to determine beneficial use support and results are as follows: 0 of 4 samples exceed the criterion for Lead. |
Data Reference: |
RWB1 Trend Maintenance Periods FYs 2007 2008 |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
Water Quality Control Plan, North Coast Region (NCRWQCB 2011): Waters designated for MUN shall not contain concentrations of chemical constituents in excess of values listed in Table 3-2 of the Basin Plan. The value for lead is 0.05 mg/L. |
Objective/Criterion Reference: |
Water Quality Control Plan (Basin Plan) for the North Coast Region |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
Data for this line of evidence for Klamath River HU, Shasta River HA was collected at 1 monitoring site [ Shasta River near Edgewood - 105SHAEDG] |
Temporal Representation: |
Data was collected over the time period 11/15/2007-7/16/2008. |
Environmental Conditions: |
Staff is not aware of any special conditions that might affect interpretation of the data. |
QAPP Information: |
The SWAMP QAPP (2008) was followed. |
QAPP Information Reference(s): |
Surface Water Ambient Monitoring Program Quality Assurance Program Plan |
|
Line of Evidence (LOE) for Decision ID 104947, Lead
|
Region 1 |
Klamath River HU, Shasta River HA |
|
|
LOE ID: |
119987 |
|
Pollutant: |
Lead |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Dissolved |
|
Beneficial Use: |
Warm Freshwater Habitat |
|
Number of Samples: |
5 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP RWB1 Monitoring data for Klamath River HU, Shasta River HA to determine beneficial use support and results are as follows: 0 of 5 samples exceeded the water quality standard for Lead. |
Data Reference: |
Water Quality Assessment Data for the 2018 solicitation cycle submitted through CEDEN for SWAMP RWB1 Monitoring .
|
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
California Toxics Rule (CTR) lists criterion continuous concentrations to protect aquatic life in freshwater. The criterion in freshwater is hardness dependent for each sample and varies based on the ambient hardness during sampling. Section (b)(1) in CTR contains the hardness dependent formula for the metals criterion. |
Objective/Criterion Reference: |
Water Quality Standards 2000. Establishment of numeric criteria for priority toxic pollutants for the State of California: Rules and regulations. Federal Register Vol. 65, No. 97. Washington, D.C.: Environmental Protection Agency |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
The samples were collected at 1 monitoring site(s) (105SH1452) |
Temporal Representation: |
The samples were collected between the dates of 2013-03-06 and 2013-11-20 |
Environmental Conditions: |
|
QAPP Information: |
Quality Assurance Program Plan and Standard Operating Procedures for SWAMP program |
QAPP Information Reference(s): |
Quality Assurance Program Plans, Quality Assurance Project Plans, and Standard Operating Procedures for the SWAMP program |
|
Line of Evidence (LOE) for Decision ID 104947, Lead
|
Region 1 |
Klamath River HU, Shasta River HA |
|
|
LOE ID: |
119989 |
|
Pollutant: |
Lead |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Dissolved |
|
Beneficial Use: |
Warm Freshwater Habitat |
|
Number of Samples: |
5 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP RWB1 Monitoring data for Klamath River HU, Shasta River HA to determine beneficial use support and results are as follows: 0 of 5 samples exceeded the water quality standard for Lead. |
Data Reference: |
Water Quality Assessment Data for the 2018 solicitation cycle submitted through CEDEN for SWAMP RWB1 Monitoring .
|
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
California Toxics Rule (CTR) lists criterion continuous concentrations to protect aquatic life in freshwater. The criterion in freshwater is hardness dependent for each sample and varies based on the ambient hardness during sampling. Section (b)(1) in CTR contains the hardness dependent formula for the metals criterion. |
Objective/Criterion Reference: |
Water Quality Standards 2000. Establishment of numeric criteria for priority toxic pollutants for the State of California: Rules and regulations. Federal Register Vol. 65, No. 97. Washington, D.C.: Environmental Protection Agency |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
The samples were collected at 1 monitoring site(s) (105SH9274) |
Temporal Representation: |
The samples were collected between the dates of 2013-03-07 and 2013-11-20 |
Environmental Conditions: |
|
QAPP Information: |
Quality Assurance Program Plan and Standard Operating Procedures for SWAMP program |
QAPP Information Reference(s): |
Quality Assurance Program Plans, Quality Assurance Project Plans, and Standard Operating Procedures for the SWAMP program |
|
Line of Evidence (LOE) for Decision ID 104947, Lead
|
Region 1 |
Klamath River HU, Shasta River HA |
|
|
LOE ID: |
32977 |
|
Pollutant: |
Lead |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Total |
|
Beneficial Use: |
Cold Freshwater Habitat |
|
Number of Samples: |
4 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
None of the 4 samples exceeded the hardness based criteria calculated for lead. |
Data Reference: |
RWB1 Trend Maintenance Periods FYs 2007 2008 |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
Water Quality Control Plan, North Coast Region (NCRWQCB 2011): All waters shall be maintained free of toxic substances in concentrations that are toxic to, or that produce detrimental physiological responses in human, plant, animal, or aquatic life. California Toxics Rule (CTR) lists criterion continuous concentrations (4-day average) to protect aquatic life in freshwater. The criterion in freshwater is hardness dependent for each sample and varies based on the ambient hardness during sampling. Section (b)(1) in CTR contains the hardness dependent formula for the metals criterion. |
Objective/Criterion Reference: |
Code of Federal Regulations 40 part 131.38 Establishment of numeric criteria for priority toxic pollutants for the State of California. 7/1/2011 Edition |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
Samples collected at station 105SHA263 (Shasta River at Hwy 263). |
Temporal Representation: |
Samples collected between 11/15/2007 and 7/16/2008. |
Environmental Conditions: |
|
QAPP Information: |
SWAMP QAPP (2008) was followed. |
QAPP Information Reference(s): |
Surface Water Ambient Monitoring Program Quality Assurance Program Plan |
|
Line of Evidence (LOE) for Decision ID 104947, Lead
|
Region 1 |
Klamath River HU, Shasta River HA |
|
|
LOE ID: |
32582 |
|
Pollutant: |
Lead |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Total |
|
Beneficial Use: |
Cold Freshwater Habitat |
|
Number of Samples: |
4 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
None of the 4 samples exceeded the hardness based criteria calculated for lead. |
Data Reference: |
RWB1 Trend Maintenance Periods FYs 2007 2008 |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
Water Quality Control Plan, North Coast Region (NCRWQCB 2011): All waters shall be maintained free of toxic substances in concentrations that are toxic to, or that produce detrimental physiological responses in human, plant, animal, or aquatic life. California Toxics Rule (CTR) lists criterion continuous concentrations (4-day average) to protect aquatic life in freshwater. The criterion in freshwater is hardness dependent for each sample and varies based on the ambient hardness during sampling. Section (b)(1) in CTR contains the hardness dependent formula for the metals criterion. |
Objective/Criterion Reference: |
Code of Federal Regulations 40 part 131.38 Establishment of numeric criteria for priority toxic pollutants for the State of California. 7/1/2011 Edition |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
Samples collected at station 105SHAEDG (Shasta River near Edgewood). |
Temporal Representation: |
Samples collected between 11/15/2007 and 7/16/2008. |
Environmental Conditions: |
|
QAPP Information: |
SWAMP QAPP (2008) was followed. |
QAPP Information Reference(s): |
Surface Water Ambient Monitoring Program Quality Assurance Program Plan |
|
Line of Evidence (LOE) for Decision ID 104947, Lead
|
Region 1 |
Klamath River HU, Shasta River HA |
|
|
LOE ID: |
103295 |
|
Pollutant: |
Lead |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Total |
|
Beneficial Use: |
Municipal & Domestic Supply |
|
Number of Samples: |
5 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP RWB1 Monitoring data for Klamath River HU, Shasta River HA to determine beneficial use support and results are as follows: 0 of 5 samples exceeded the water quality standard for Lead. |
Data Reference: |
Water Quality Assessment Data for the 2018 solicitation cycle submitted through CEDEN for SWAMP RWB1 Monitoring .
|
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
Water Quality Control Plan, North Coast Region (NCRWQCB 2018): Waters designated for MUN shall not contain concentrations of chemical constituents in excess of values listed in Table 3-2 of the Basin Plan. The value for lead is 0.05 mg/L. |
Objective/Criterion Reference: |
Water Quality Control Plan (Basin Plan) for the North Coast Region |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
The samples were collected at 1 monitoring site(s) (105SH1452) |
Temporal Representation: |
The samples were collected between the dates of 2013-03-06 and 2013-11-20 |
Environmental Conditions: |
|
QAPP Information: |
Quality Assurance Program Plan and Standard Operating Procedures for SWAMP program |
QAPP Information Reference(s): |
Quality Assurance Program Plans, Quality Assurance Project Plans, and Standard Operating Procedures for the SWAMP program |
|
Line of Evidence (LOE) for Decision ID 104947, Lead
|
Region 1 |
Klamath River HU, Shasta River HA |
|
|
LOE ID: |
42294 |
|
Pollutant: |
Lead |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Total |
|
Beneficial Use: |
Municipal & Domestic Supply |
|
Number of Samples: |
4 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP data for Klamath River HU, Shasta River HA to determine beneficial use support and results are as follows: 0 of 4 samples exceed the criterion for Lead. |
Data Reference: |
RWB1 Trend Maintenance Periods FYs 2007 2008 |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
Water Quality Control Plan, North Coast Region (NCRWQCB 2011): Waters designated for MUN shall not contain concentrations of chemical constituents in excess of values listed in Table 3-2 of the Basin Plan. The value for lead is 0.05 mg/L. |
Objective/Criterion Reference: |
Water Quality Control Plan (Basin Plan) for the North Coast Region |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
Data for this line of evidence for Klamath River HU, Shasta River HA was collected at 1 monitoring site [ Shasta River at Hwy 263 - 105SHA263] |
Temporal Representation: |
Data was collected over the time period 11/15/2007-7/16/2008. |
Environmental Conditions: |
Staff is not aware of any special conditions that might affect interpretation of the data. |
QAPP Information: |
The SWAMP QAPP (2008) was followed. |
QAPP Information Reference(s): |
Surface Water Ambient Monitoring Program Quality Assurance Program Plan |
|
Line of Evidence (LOE) for Decision ID 168823, Lindane/gamma Hexachlorocyclohexane (gamma-HCH)
|
Region 1 |
Klamath River HU, Shasta River HA |
|
|
LOE ID: |
42400 |
|
Pollutant: |
Lindane/gamma Hexachlorocyclohexane (gamma-HCH) |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Total |
|
Beneficial Use: |
Cold Freshwater Habitat |
|
Number of Samples: |
3 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP data for Klamath River HU, Shasta River HA to determine beneficial use support and results are as follows: 0 of 3 samples exceed the criterion for HCH, gamma. |
Data Reference: |
RWB1 Trend Maintenance Periods FYs 2007 2008 |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
Water Quality Control Plan, North Coast Region (NCRWQCB 2011): All waters shall be maintained free of toxic substances in concentrations that are toxic to, or that produce detrimental physiological responses in human, plant, animal, or aquatic life. The established numeric criteria for HCH, gamma (Lindane or gamma-BHC) to protect aquatic life in freshwater criterion maximum concentration is 0.95 ug/L (California Toxics Rule, 2000). |
Objective/Criterion Reference: |
Code of Federal Regulations 40 part 131.38 Establishment of numeric criteria for priority toxic pollutants for the State of California. 7/1/2011 Edition |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
Data for this line of evidence for Klamath River HU, Shasta River HA was collected at 1 monitoring site [ Shasta River at Hwy 263 - 105SHA263] |
Temporal Representation: |
Data was collected over the time period 11/15/2007-7/16/2008. |
Environmental Conditions: |
Staff is not aware of any special conditions that might affect interpretation of the data. |
QAPP Information: |
The SWAMP QAPP (2008) was followed. |
QAPP Information Reference(s): |
Surface Water Ambient Monitoring Program Quality Assurance Program Plan |
|
Line of Evidence (LOE) for Decision ID 168823, Lindane/gamma Hexachlorocyclohexane (gamma-HCH)
|
Region 1 |
Klamath River HU, Shasta River HA |
|
|
LOE ID: |
42361 |
|
Pollutant: |
Lindane/gamma Hexachlorocyclohexane (gamma-HCH) |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Total |
|
Beneficial Use: |
Municipal & Domestic Supply |
|
Number of Samples: |
3 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP data for Klamath River HU, Shasta River HA to determine beneficial use support and results are as follows: 0 of 3 samples exceed the criterion for HCH, gamma. |
Data Reference: |
RWB1 Trend Maintenance Periods FYs 2007 2008 |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
Water Quality Control Plan, North Coast Region (NCRWQCB 2011): All waters shall be maintained free of toxic substances in concentrations that are toxic to, or that produce detrimental physiological responses in human, plant, animal, or aquatic life. The established numeric criteria for gamma-BHC (Lindane, gamma-HCH) to protect human health from the consumption of water and organisms is 0.019 ug/L (California Toxics Rule, 2000). |
Objective/Criterion Reference: |
Code of Federal Regulations 40 part 131.38 Establishment of numeric criteria for priority toxic pollutants for the State of California. 7/1/2011 Edition |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
Data for this line of evidence for Klamath River HU, Shasta River HA was collected at 1 monitoring site [ Shasta River at Hwy 263 - 105SHA263] |
Temporal Representation: |
Data was collected over the time period 11/15/2007-7/16/2008. |
Environmental Conditions: |
Staff is not aware of any special conditions that might affect interpretation of the data. |
QAPP Information: |
The SWAMP QAPP (2008) was followed. |
QAPP Information Reference(s): |
Surface Water Ambient Monitoring Program Quality Assurance Program Plan |
|
Line of Evidence (LOE) for Decision ID 168823, Lindane/gamma Hexachlorocyclohexane (gamma-HCH)
|
Region 1 |
Klamath River HU, Shasta River HA |
|
|
LOE ID: |
103634 |
|
Pollutant: |
Lindane/gamma Hexachlorocyclohexane (gamma-HCH) |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Total |
|
Beneficial Use: |
Commercial or recreational collection of fish, shellfish, or organisms |
|
Number of Samples: |
1 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP RWB1 Monitoring data for Klamath River HU, Shasta River HA to determine beneficial use support and results are as follows: 0 of 1 samples exceeded the water quality standard for HCH, gamma-. |
Data Reference: |
Water Quality Assessment Data for the 2018 solicitation cycle submitted through CEDEN for SWAMP RWB1 Monitoring .
|
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
Water Quality Control Plan, North Coast Region (NCRWQCB 2018): All waters shall be maintained free of toxic substances in concentrations that are toxic to, or that produce detrimental physiological responses in human, plant, animal, or aquatic life. The established numeric criteria for gamma-BHC (Lindane, gamma-HCH) to protect human health from consumption of organisms only is 0.063 ug/L (California Toxics Rule, 2000). |
Objective/Criterion Reference: |
Water Quality Standards 2000. Establishment of numeric criteria for priority toxic pollutants for the State of California: Rules and regulations. Federal Register Vol. 65, No. 97. Washington, D.C.: Environmental Protection Agency |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
The samples were collected at 1 monitoring site(s) (105SH1452) |
Temporal Representation: |
The samples were collected between the dates of 2013-04-29 and 2013-04-29 |
Environmental Conditions: |
|
QAPP Information: |
Quality Assurance Program Plan and Standard Operating Procedures for SWAMP program |
QAPP Information Reference(s): |
Quality Assurance Program Plans, Quality Assurance Project Plans, and Standard Operating Procedures for the SWAMP program |
|
Line of Evidence (LOE) for Decision ID 168823, Lindane/gamma Hexachlorocyclohexane (gamma-HCH)
|
Region 1 |
Klamath River HU, Shasta River HA |
|
|
LOE ID: |
103636 |
|
Pollutant: |
Lindane/gamma Hexachlorocyclohexane (gamma-HCH) |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Total |
|
Beneficial Use: |
Municipal & Domestic Supply |
|
Number of Samples: |
1 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP RWB1 Monitoring data for Klamath River HU, Shasta River HA to determine beneficial use support and results are as follows: 0 of 1 samples exceeded the water quality standard for HCH, gamma-. |
Data Reference: |
Water Quality Assessment Data for the 2018 solicitation cycle submitted through CEDEN for SWAMP RWB1 Monitoring .
|
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
Water Quality Control Plan, North Coast Region (NCRWQCB 2018): All waters shall be maintained free of toxic substances in concentrations that are toxic to, or that produce detrimental physiological responses in human, plant, animal, or aquatic life. The established numeric criteria for gamma-BHC (Lindane, gamma-HCH) to protect of human health from the consumption of water and organisms is 0.019 ug/L (California Toxics Rule, 2000). |
Objective/Criterion Reference: |
Water Quality Standards 2000. Establishment of numeric criteria for priority toxic pollutants for the State of California: Rules and regulations. Federal Register Vol. 65, No. 97. Washington, D.C.: Environmental Protection Agency |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
The samples were collected at 1 monitoring site(s) (105SH1452) |
Temporal Representation: |
The samples were collected between the dates of 2013-04-29 and 2013-04-29 |
Environmental Conditions: |
|
QAPP Information: |
Quality Assurance Program Plan and Standard Operating Procedures for SWAMP program |
QAPP Information Reference(s): |
Quality Assurance Program Plans, Quality Assurance Project Plans, and Standard Operating Procedures for the SWAMP program |
|
Line of Evidence (LOE) for Decision ID 168823, Lindane/gamma Hexachlorocyclohexane (gamma-HCH)
|
Region 1 |
Klamath River HU, Shasta River HA |
|
|
LOE ID: |
42399 |
|
Pollutant: |
Lindane/gamma Hexachlorocyclohexane (gamma-HCH) |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Total |
|
Beneficial Use: |
Cold Freshwater Habitat |
|
Number of Samples: |
3 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP data for Klamath River HU, Shasta River HA to determine beneficial use support and results are as follows: 0 of 3 samples exceed the criterion for HCH, gamma. |
Data Reference: |
RWB1 Trend Maintenance Periods FYs 2007 2008 |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
Water Quality Control Plan, North Coast Region (NCRWQCB 2011): All waters shall be maintained free of toxic substances in concentrations that are toxic to, or that produce detrimental physiological responses in human, plant, animal, or aquatic life. The established numeric criteria for HCH, gamma (Lindane or gamma-BHC) to protect aquatic life in freshwater criterion maximum concentration is 0.95 ug/L (California Toxics Rule, 2000). |
Objective/Criterion Reference: |
Code of Federal Regulations 40 part 131.38 Establishment of numeric criteria for priority toxic pollutants for the State of California. 7/1/2011 Edition |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
Data for this line of evidence for Klamath River HU, Shasta River HA was collected at 1 monitoring site [ Shasta River near Edgewood - 105SHAEDG] |
Temporal Representation: |
Data was collected over the time period 11/15/2007-7/16/2008. |
Environmental Conditions: |
Staff is not aware of any special conditions that might affect interpretation of the data. |
QAPP Information: |
The SWAMP QAPP (2008) was followed. |
QAPP Information Reference(s): |
Surface Water Ambient Monitoring Program Quality Assurance Program Plan |
|
Line of Evidence (LOE) for Decision ID 168823, Lindane/gamma Hexachlorocyclohexane (gamma-HCH)
|
Region 1 |
Klamath River HU, Shasta River HA |
|
|
LOE ID: |
109561 |
|
Pollutant: |
Lindane/gamma Hexachlorocyclohexane (gamma-HCH) |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Total |
|
Beneficial Use: |
Cold Freshwater Habitat |
|
Number of Samples: |
1 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP RWB1 Monitoring data for Klamath River HU, Shasta River HA to determine beneficial use support and results are as follows: 0 of 1 samples exceeded the water quality standard for HCH, gamma-. |
Data Reference: |
Water Quality Assessment Data for the 2018 solicitation cycle submitted through CEDEN for SWAMP RWB1 Monitoring .
|
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
Water Quality Control Plan, North Coast Region (NCRWQCB 2018): All waters shall be maintained free of toxic substances in concentrations that are toxic to, or that produce detrimental physiological responses in human, plant, animal, or aquatic life. The established numeric criteria for gamma-BHC (Lindane, gamma-HCH) to protect aquatic life in freshwater as criterion continuous concentration (expressed as a 4-day average) is 0.95 ug/L (California Toxics Rule, 2000). |
Objective/Criterion Reference: |
Water Quality Standards 2000. Establishment of numeric criteria for priority toxic pollutants for the State of California: Rules and regulations. Federal Register Vol. 65, No. 97. Washington, D.C.: Environmental Protection Agency |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
The samples were collected at 1 monitoring site(s) (105SH9274) |
Temporal Representation: |
The samples were collected between the dates of 2013-04-29 and 2013-04-29 |
Environmental Conditions: |
|
QAPP Information: |
Quality Assurance Program Plan and Standard Operating Procedures for SWAMP program |
QAPP Information Reference(s): |
Quality Assurance Program Plans, Quality Assurance Project Plans, and Standard Operating Procedures for the SWAMP program |
|
Line of Evidence (LOE) for Decision ID 168823, Lindane/gamma Hexachlorocyclohexane (gamma-HCH)
|
Region 1 |
Klamath River HU, Shasta River HA |
|
|
LOE ID: |
103635 |
|
Pollutant: |
Lindane/gamma Hexachlorocyclohexane (gamma-HCH) |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Total |
|
Beneficial Use: |
Cold Freshwater Habitat |
|
Number of Samples: |
1 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP RWB1 Monitoring data for Klamath River HU, Shasta River HA to determine beneficial use support and results are as follows: 0 of 1 samples exceeded the water quality standard for HCH, gamma-. |
Data Reference: |
Water Quality Assessment Data for the 2018 solicitation cycle submitted through CEDEN for SWAMP RWB1 Monitoring .
|
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
Water Quality Control Plan, North Coast Region (NCRWQCB 2018): All waters shall be maintained free of toxic substances in concentrations that are toxic to, or that produce detrimental physiological responses in human, plant, animal, or aquatic life. The established numeric criteria for gamma-BHC (Lindane, gamma-HCH) to protect aquatic life in freshwater as criterion continuous concentration (expressed as a 4-day average) is 0.95 ug/L (California Toxics Rule, 2000). |
Objective/Criterion Reference: |
Water Quality Standards 2000. Establishment of numeric criteria for priority toxic pollutants for the State of California: Rules and regulations. Federal Register Vol. 65, No. 97. Washington, D.C.: Environmental Protection Agency |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
The samples were collected at 1 monitoring site(s) (105SH1452) |
Temporal Representation: |
The samples were collected between the dates of 2013-04-29 and 2013-04-29 |
Environmental Conditions: |
|
QAPP Information: |
Quality Assurance Program Plan and Standard Operating Procedures for SWAMP program |
QAPP Information Reference(s): |
Quality Assurance Program Plans, Quality Assurance Project Plans, and Standard Operating Procedures for the SWAMP program |
|
Line of Evidence (LOE) for Decision ID 168823, Lindane/gamma Hexachlorocyclohexane (gamma-HCH)
|
Region 1 |
Klamath River HU, Shasta River HA |
|
|
LOE ID: |
42320 |
|
Pollutant: |
Lindane/gamma Hexachlorocyclohexane (gamma-HCH) |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Total |
|
Beneficial Use: |
Commercial or recreational collection of fish, shellfish, or organisms |
|
Number of Samples: |
3 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP data for Klamath River HU, Shasta River HA to determine beneficial use support and results are as follows: 0 of 3 samples exceed the criterion for HCH, gamma. |
Data Reference: |
RWB1 Trend Maintenance Periods FYs 2007 2008 |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
Water Quality Control Plan, North Coast Region (NCRWQCB 2011): All waters shall be maintained free of toxic substances in concentrations that are toxic to, or that produce detrimental physiological responses in human, plant, animal, or aquatic life. The established numeric criteria for gamma-BHC (Lindane, gamma-HCH) to protect human health from consumption of organisms only is 0.063 ug/L (California Toxics Rule, 2000). |
Objective/Criterion Reference: |
Code of Federal Regulations 40 part 131.38 Establishment of numeric criteria for priority toxic pollutants for the State of California. 7/1/2011 Edition |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
Data for this line of evidence for Klamath River HU, Shasta River HA was collected at 1 monitoring site [ Shasta River near Edgewood - 105SHAEDG] |
Temporal Representation: |
Data was collected over the time period 11/15/2007-7/16/2008. |
Environmental Conditions: |
Staff is not aware of any special conditions that might affect interpretation of the data. |
QAPP Information: |
The SWAMP QAPP (2008) was followed. |
QAPP Information Reference(s): |
Surface Water Ambient Monitoring Program Quality Assurance Program Plan |
|
Line of Evidence (LOE) for Decision ID 168823, Lindane/gamma Hexachlorocyclohexane (gamma-HCH)
|
Region 1 |
Klamath River HU, Shasta River HA |
|
|
LOE ID: |
42422 |
|
Pollutant: |
Lindane/gamma Hexachlorocyclohexane (gamma-HCH) |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Total |
|
Beneficial Use: |
Warm Freshwater Habitat |
|
Number of Samples: |
3 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP data for Klamath River HU, Shasta River HA to determine beneficial use support and results are as follows: 0 of 3 samples exceed the criterion for HCH, gamma. |
Data Reference: |
RWB1 Trend Maintenance Periods FYs 2007 2008 |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
Water Quality Control Plan, North Coast Region (NCRWQCB 2011): All waters shall be maintained free of toxic substances in concentrations that are toxic to, or that produce detrimental physiological responses in human, plant, animal, or aquatic life. The established numeric criteria for HCH, gamma (Lindane or gamma-BHC) to protect aquatic life in freshwater criterion maximum concentration is 0.95 ug/L (California Toxics Rule, 2000). |
Objective/Criterion Reference: |
Code of Federal Regulations 40 part 131.38 Establishment of numeric criteria for priority toxic pollutants for the State of California. 7/1/2011 Edition |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
Data for this line of evidence for Klamath River HU, Shasta River HA was collected at 1 monitoring site [ Shasta River at Hwy 263 - 105SHA263] |
Temporal Representation: |
Data was collected over the time period 11/15/2007-7/16/2008. |
Environmental Conditions: |
Staff is not aware of any special conditions that might affect interpretation of the data. |
QAPP Information: |
The SWAMP QAPP (2008) was followed. |
QAPP Information Reference(s): |
Surface Water Ambient Monitoring Program Quality Assurance Program Plan |
|
Line of Evidence (LOE) for Decision ID 168823, Lindane/gamma Hexachlorocyclohexane (gamma-HCH)
|
Region 1 |
Klamath River HU, Shasta River HA |
|
|
LOE ID: |
109562 |
|
Pollutant: |
Lindane/gamma Hexachlorocyclohexane (gamma-HCH) |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Total |
|
Beneficial Use: |
Municipal & Domestic Supply |
|
Number of Samples: |
1 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP RWB1 Monitoring data for Klamath River HU, Shasta River HA to determine beneficial use support and results are as follows: 0 of 1 samples exceeded the water quality standard for HCH, gamma-. |
Data Reference: |
Water Quality Assessment Data for the 2018 solicitation cycle submitted through CEDEN for SWAMP RWB1 Monitoring .
|
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
Water Quality Control Plan, North Coast Region (NCRWQCB 2018): All waters shall be maintained free of toxic substances in concentrations that are toxic to, or that produce detrimental physiological responses in human, plant, animal, or aquatic life. The established numeric criteria for gamma-BHC (Lindane, gamma-HCH) to protect of human health from the consumption of water and organisms is 0.019 ug/L (California Toxics Rule, 2000). |
Objective/Criterion Reference: |
Water Quality Standards 2000. Establishment of numeric criteria for priority toxic pollutants for the State of California: Rules and regulations. Federal Register Vol. 65, No. 97. Washington, D.C.: Environmental Protection Agency |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
The samples were collected at 1 monitoring site(s) (105SH9274) |
Temporal Representation: |
The samples were collected between the dates of 2013-04-29 and 2013-04-29 |
Environmental Conditions: |
|
QAPP Information: |
Quality Assurance Program Plan and Standard Operating Procedures for SWAMP program |
QAPP Information Reference(s): |
Quality Assurance Program Plans, Quality Assurance Project Plans, and Standard Operating Procedures for the SWAMP program |
|
Line of Evidence (LOE) for Decision ID 168823, Lindane/gamma Hexachlorocyclohexane (gamma-HCH)
|
Region 1 |
Klamath River HU, Shasta River HA |
|
|
LOE ID: |
42336 |
|
Pollutant: |
Lindane/gamma Hexachlorocyclohexane (gamma-HCH) |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Total |
|
Beneficial Use: |
Commercial or recreational collection of fish, shellfish, or organisms |
|
Number of Samples: |
3 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP data for Klamath River HU, Shasta River HA to determine beneficial use support and results are as follows: 0 of 3 samples exceed the criterion for HCH, gamma. |
Data Reference: |
RWB1 Trend Maintenance Periods FYs 2007 2008 |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
Water Quality Control Plan, North Coast Region (NCRWQCB 2011): All waters shall be maintained free of toxic substances in concentrations that are toxic to, or that produce detrimental physiological responses in human, plant, animal, or aquatic life. The established numeric criteria for gamma-BHC (Lindane, gamma-HCH) to protect human health from consumption of organisms only is 0.063 ug/L (California Toxics Rule, 2000). |
Objective/Criterion Reference: |
Code of Federal Regulations 40 part 131.38 Establishment of numeric criteria for priority toxic pollutants for the State of California. 7/1/2011 Edition |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
Data for this line of evidence for Klamath River HU, Shasta River HA was collected at 1 monitoring site [ Shasta River at Hwy 263 - 105SHA263] |
Temporal Representation: |
Data was collected over the time period 11/15/2007-7/16/2008. |
Environmental Conditions: |
Staff is not aware of any special conditions that might affect interpretation of the data. |
QAPP Information: |
The SWAMP QAPP (2008) was followed. |
QAPP Information Reference(s): |
Surface Water Ambient Monitoring Program Quality Assurance Program Plan |
|
Line of Evidence (LOE) for Decision ID 168823, Lindane/gamma Hexachlorocyclohexane (gamma-HCH)
|
Region 1 |
Klamath River HU, Shasta River HA |
|
|
LOE ID: |
42421 |
|
Pollutant: |
Lindane/gamma Hexachlorocyclohexane (gamma-HCH) |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Total |
|
Beneficial Use: |
Warm Freshwater Habitat |
|
Number of Samples: |
3 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP data for Klamath River HU, Shasta River HA to determine beneficial use support and results are as follows: 0 of 3 samples exceed the criterion for HCH, gamma. |
Data Reference: |
RWB1 Trend Maintenance Periods FYs 2007 2008 |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
Water Quality Control Plan, North Coast Region (NCRWQCB 2011): All waters shall be maintained free of toxic substances in concentrations that are toxic to, or that produce detrimental physiological responses in human, plant, animal, or aquatic life. The established numeric criteria for HCH, gamma (Lindane or gamma-BHC) to protect aquatic life in freshwater criterion maximum concentration is 0.95 ug/L (California Toxics Rule, 2000). |
Objective/Criterion Reference: |
Code of Federal Regulations 40 part 131.38 Establishment of numeric criteria for priority toxic pollutants for the State of California. 7/1/2011 Edition |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
Data for this line of evidence for Klamath River HU, Shasta River HA was collected at 1 monitoring site [ Shasta River near Edgewood - 105SHAEDG] |
Temporal Representation: |
Data was collected over the time period 11/15/2007-7/16/2008. |
Environmental Conditions: |
Staff is not aware of any special conditions that might affect interpretation of the data. |
QAPP Information: |
The SWAMP QAPP (2008) was followed. |
QAPP Information Reference(s): |
Surface Water Ambient Monitoring Program Quality Assurance Program Plan |
|
Line of Evidence (LOE) for Decision ID 168823, Lindane/gamma Hexachlorocyclohexane (gamma-HCH)
|
Region 1 |
Klamath River HU, Shasta River HA |
|
|
LOE ID: |
42345 |
|
Pollutant: |
Lindane/gamma Hexachlorocyclohexane (gamma-HCH) |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Total |
|
Beneficial Use: |
Municipal & Domestic Supply |
|
Number of Samples: |
3 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP data for Klamath River HU, Shasta River HA to determine beneficial use support and results are as follows: 0 of 3 samples exceed the criterion for HCH, gamma. |
Data Reference: |
RWB1 Trend Maintenance Periods FYs 2007 2008 |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
Water Quality Control Plan, North Coast Region (NCRWQCB 2011): All waters shall be maintained free of toxic substances in concentrations that are toxic to, or that produce detrimental physiological responses in human, plant, animal, or aquatic life. The established numeric criteria for gamma-BHC (Lindane, gamma-HCH) to protect human health from the consumption of water and organisms is 0.019 ug/L (California Toxics Rule, 2000). |
Objective/Criterion Reference: |
Code of Federal Regulations 40 part 131.38 Establishment of numeric criteria for priority toxic pollutants for the State of California. 7/1/2011 Edition |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
Data for this line of evidence for Klamath River HU, Shasta River HA was collected at 1 monitoring site [ Shasta River near Edgewood - 105SHAEDG] |
Temporal Representation: |
Data was collected over the time period 11/15/2007-7/16/2008. |
Environmental Conditions: |
Staff is not aware of any special conditions that might affect interpretation of the data. |
QAPP Information: |
The SWAMP QAPP (2008) was followed. |
QAPP Information Reference(s): |
Surface Water Ambient Monitoring Program Quality Assurance Program Plan |
|
Line of Evidence (LOE) for Decision ID 168823, Lindane/gamma Hexachlorocyclohexane (gamma-HCH)
|
Region 1 |
Klamath River HU, Shasta River HA |
|
|
LOE ID: |
103637 |
|
Pollutant: |
Lindane/gamma Hexachlorocyclohexane (gamma-HCH) |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Total |
|
Beneficial Use: |
Commercial or recreational collection of fish, shellfish, or organisms |
|
Number of Samples: |
1 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP RWB1 Monitoring data for Klamath River HU, Shasta River HA to determine beneficial use support and results are as follows: 0 of 1 samples exceeded the water quality standard for HCH, gamma-. |
Data Reference: |
Water Quality Assessment Data for the 2018 solicitation cycle submitted through CEDEN for SWAMP RWB1 Monitoring .
|
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
Water Quality Control Plan, North Coast Region (NCRWQCB 2018): All waters shall be maintained free of toxic substances in concentrations that are toxic to, or that produce detrimental physiological responses in human, plant, animal, or aquatic life. The established numeric criteria for gamma-BHC (Lindane, gamma-HCH) to protect human health from consumption of organisms only is 0.063 ug/L (California Toxics Rule, 2000). |
Objective/Criterion Reference: |
Water Quality Standards 2000. Establishment of numeric criteria for priority toxic pollutants for the State of California: Rules and regulations. Federal Register Vol. 65, No. 97. Washington, D.C.: Environmental Protection Agency |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
The samples were collected at 1 monitoring site(s) (105SH9274) |
Temporal Representation: |
The samples were collected between the dates of 2013-04-29 and 2013-04-29 |
Environmental Conditions: |
|
QAPP Information: |
Quality Assurance Program Plan and Standard Operating Procedures for SWAMP program |
QAPP Information Reference(s): |
Quality Assurance Program Plans, Quality Assurance Project Plans, and Standard Operating Procedures for the SWAMP program |
|
Line of Evidence (LOE) for Decision ID 100756, Mercury
|
Region 1 |
Klamath River HU, Shasta River HA |
|
|
LOE ID: |
103309 |
|
Pollutant: |
Mercury |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Total |
|
Beneficial Use: |
Commercial or recreational collection of fish, shellfish, or organisms |
|
Number of Samples: |
5 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP RWB1 Monitoring data for Klamath River HU, Shasta River HA to determine beneficial use support and results are as follows: 0 of 5 samples exceeded the water quality standard for Mercury. |
Data Reference: |
Water Quality Assessment Data for the 2018 solicitation cycle submitted through CEDEN for SWAMP RWB1 Monitoring .
|
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
Water Quality Control Plan, North Coast Region (NCRWQCB 2018): All waters shall be maintained free of toxic substances in concentrations that are toxic to, or that produce detrimental physiological responses in human, plant, animal, or aquatic life. The established numeric criteria for mercury to protect of human health from the consumption of organisms only is 0.051 ug/L (California Toxics Rule, 2000). |
Objective/Criterion Reference: |
Water Quality Standards 2000. Establishment of numeric criteria for priority toxic pollutants for the State of California: Rules and regulations. Federal Register Vol. 65, No. 97. Washington, D.C.: Environmental Protection Agency |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
The samples were collected at 1 monitoring site(s) (105SH9274) |
Temporal Representation: |
The samples were collected between the dates of 2013-03-07 and 2013-11-20 |
Environmental Conditions: |
|
QAPP Information: |
Quality Assurance Program Plan and Standard Operating Procedures for SWAMP program |
QAPP Information Reference(s): |
Quality Assurance Program Plans, Quality Assurance Project Plans, and Standard Operating Procedures for the SWAMP program |
|
Line of Evidence (LOE) for Decision ID 100756, Mercury
|
Region 1 |
Klamath River HU, Shasta River HA |
|
|
LOE ID: |
42691 |
|
Pollutant: |
Mercury |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Total |
|
Beneficial Use: |
Commercial or recreational collection of fish, shellfish, or organisms |
|
Number of Samples: |
4 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP data for Klamath River HU, Shasta River HA to determine beneficial use support and results are as follows: 0 of 4 samples exceed the criterion for Mercury. |
Data Reference: |
RWB1 Trend Maintenance Periods FYs 2007 2008 |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
Water Quality Control Plan, North Coast Region (NCRWQCB 2011): All waters shall be maintained free of toxic substances in concentrations that are toxic to, or that produce detrimental physiological responses in human, plant, animal, or aquatic life. The established numeric criteria for mercury to protect of human health from the consumption of organisms only is 0.051 ug/L (California Toxics Rule, 2000). |
Objective/Criterion Reference: |
Code of Federal Regulations 40 part 131.38 Establishment of numeric criteria for priority toxic pollutants for the State of California. 7/1/2011 Edition |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
Data for this line of evidence for Klamath River HU, Shasta River HA was collected at 1 monitoring site [ Shasta River near Edgewood - 105SHAEDG] |
Temporal Representation: |
Data was collected over the time period 11/15/2007-7/16/2008. |
Environmental Conditions: |
Staff is not aware of any special conditions that might affect interpretation of the data. |
QAPP Information: |
The SWAMP QAPP (2008) was followed. |
QAPP Information Reference(s): |
Surface Water Ambient Monitoring Program Quality Assurance Program Plan |
|
Line of Evidence (LOE) for Decision ID 100756, Mercury
|
Region 1 |
Klamath River HU, Shasta River HA |
|
|
LOE ID: |
123506 |
|
Pollutant: |
Mercury |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Total |
|
Beneficial Use: |
Municipal & Domestic Supply |
|
Number of Samples: |
7 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
State Water Board staff re-assessed SWAMP data for Klamath River HU, Shasta River HA to determine beneficial use support and results are as follows: 0 of 7 samples exceed the criterion for Mercury, Total. This LOE re-assesses data from LOE 21509 from the 2010 Integrated Report. Data were re-assessed in order to (1) update the numeric objective, and (2) evaluate these data in their own LOE, instead of being evaluated in the same LOE as other metals data. |
Data Reference: |
Surface Water Ambient Monitoring Program (SWAMP). Summary Report for the North Coast Region (RWQCB-1) for years 2000-2006. North Coast Regional Water Quality Control Board. March 2008 |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
Water Quality Control Plan, North Coast Region (NCRWQCB 2011): All waters shall be maintained free of toxic substances in concentrations that are toxic to, or that produce detrimental physiological responses in human, plant, animal, or aquatic life. The established numeric criteria for mercury to protect of human health from the consumption of water and organisms is 0.050 ug/L (California Toxics Rule, 2000). |
Objective/Criterion Reference: |
Water Quality Control Plan (Basin Plan) for the North Coast Region |
Objective/Criterion Reference: |
Code of Federal Regulations 40 part 131.38 Establishment of numeric criteria for priority toxic pollutants for the State of California. 7/1/2011 Edition |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
Data for this line of evidence for Klamath River HU, Shasta River HA was collected at 1 monitoring site [ Yreka Creek at Anderson Rd - 105YREAND] |
Temporal Representation: |
Data was collected over the time period 10/9/2002-6/20/2005. |
Environmental Conditions: |
There are no known environmental conditions (e.g., seasonality, land use practices, fire events, storms, etc.) that are related to these data. |
QAPP Information: |
Quality control was conducted in accordance with the SWAMP Quality Assurance Management Plan (SWAMP 2002). |
QAPP Information Reference(s): |
Quality Assurance Management Plan for the State of California's Surface Water Ambient Monitoring Program. Sacramento, CA. State Water Resources Control Board. SWAMP. December 2002 (1st version)
|
|
Line of Evidence (LOE) for Decision ID 100756, Mercury
|
Region 1 |
Klamath River HU, Shasta River HA |
|
|
LOE ID: |
123497 |
|
Pollutant: |
Mercury |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Total |
|
Beneficial Use: |
Municipal & Domestic Supply |
|
Number of Samples: |
22 |
Number of Exceedances: |
3 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
State Water Board staff re-assessed SWAMP data for Klamath River HU, Shasta River HA to determine beneficial use support and results are as follows: 3 of 22 samples exceed the criterion for Mercury, Total. This LOE re-assesses data from LOE 21509 from the 2010 Integrated Report. Data were re-assessed in order to (1) update the numeric objective, and (2) evaluate these data in their own LOE, instead of being evaluated in the same LOE as other metals data. |
Data Reference: |
Surface Water Ambient Monitoring Program (SWAMP). Summary Report for the North Coast Region (RWQCB-1) for years 2000-2006. North Coast Regional Water Quality Control Board. March 2008 |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
Water Quality Control Plan, North Coast Region (NCRWQCB 2011): All waters shall be maintained free of toxic substances in concentrations that are toxic to, or that produce detrimental physiological responses in human, plant, animal, or aquatic life. The established numeric criteria for mercury to protect of human health from the consumption of water and organisms is 0.050 ug/L (California Toxics Rule, 2000). |
Objective/Criterion Reference: |
Water Quality Control Plan (Basin Plan) for the North Coast Region |
Objective/Criterion Reference: |
Code of Federal Regulations 40 part 131.38 Establishment of numeric criteria for priority toxic pollutants for the State of California. 7/1/2011 Edition |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
Data for this line of evidence for Klamath River HU, Shasta River HA was collected at 1 monitoring site [ Shasta River at Hwy 263 - 105SH1452] |
Temporal Representation: |
Data was collected over the time period 3/20/2001-11/16/2006. |
Environmental Conditions: |
There are no known environmental conditions (e.g., seasonality, land use practices, fire events, storms, etc.) that are related to these data. |
QAPP Information: |
Quality control was conducted in accordance with the SWAMP Quality Assurance Management Plan (SWAMP 2002). |
QAPP Information Reference(s): |
Letter requesting acceptance of late submittal |
|
Line of Evidence (LOE) for Decision ID 100756, Mercury
|
Region 1 |
Klamath River HU, Shasta River HA |
|
|
LOE ID: |
103312 |
|
Pollutant: |
Mercury |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Total |
|
Beneficial Use: |
Municipal & Domestic Supply |
|
Number of Samples: |
5 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP RWB1 Monitoring data for Klamath River HU, Shasta River HA to determine beneficial use support and results are as follows: 0 of 5 samples exceeded the water quality standard for Mercury. |
Data Reference: |
Water Quality Assessment Data for the 2018 solicitation cycle submitted through CEDEN for SWAMP RWB1 Monitoring .
|
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
Water Quality Control Plan, North Coast Region (NCRWQCB 2018): All waters shall be maintained free of toxic substances in concentrations that are toxic to, or that produce detrimental physiological responses in human, plant, animal, or aquatic life. The established numeric criteria for mercury to protect of human health from the consumption of water and organisms is 0.050 ug/L (California Toxics Rule, 2000). |
Objective/Criterion Reference: |
Water Quality Standards 2000. Establishment of numeric criteria for priority toxic pollutants for the State of California: Rules and regulations. Federal Register Vol. 65, No. 97. Washington, D.C.: Environmental Protection Agency |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
The samples were collected at 1 monitoring site(s) (105SH9274) |
Temporal Representation: |
The samples were collected between the dates of 2013-03-07 and 2013-11-20 |
Environmental Conditions: |
|
QAPP Information: |
Quality Assurance Program Plan and Standard Operating Procedures for SWAMP program |
QAPP Information Reference(s): |
Quality Assurance Program Plans, Quality Assurance Project Plans, and Standard Operating Procedures for the SWAMP program |
|
Line of Evidence (LOE) for Decision ID 100756, Mercury
|
Region 1 |
Klamath River HU, Shasta River HA |
|
|
LOE ID: |
42760 |
|
Pollutant: |
Mercury |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Total |
|
Beneficial Use: |
Municipal & Domestic Supply |
|
Number of Samples: |
4 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP data for Klamath River HU, Shasta River HA to determine beneficial use support and results are as follows: 0 of 4 samples exceed the criterion for Mercury. |
Data Reference: |
RWB1 Trend Maintenance Periods FYs 2007 2008 |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
Water Quality Control Plan, North Coast Region (NCRWQCB 2011): All waters shall be maintained free of toxic substances in concentrations that are toxic to, or that produce detrimental physiological responses in human, plant, animal, or aquatic life. The established numeric criteria for mercury to protect of human health from the consumption of water and organisms is 0.050 ug/L (California Toxics Rule, 2000). |
Objective/Criterion Reference: |
Code of Federal Regulations 40 part 131.38 Establishment of numeric criteria for priority toxic pollutants for the State of California. 7/1/2011 Edition |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
Data for this line of evidence for Klamath River HU, Shasta River HA was collected at 1 monitoring site [ Shasta River at Hwy 263 - 105SHA263] |
Temporal Representation: |
Data was collected over the time period 11/15/2007-7/16/2008. |
Environmental Conditions: |
Staff is not aware of any special conditions that might affect interpretation of the data. |
QAPP Information: |
The SWAMP QAPP (2008) was followed. |
QAPP Information Reference(s): |
Surface Water Ambient Monitoring Program Quality Assurance Program Plan |
|
Line of Evidence (LOE) for Decision ID 100756, Mercury
|
Region 1 |
Klamath River HU, Shasta River HA |
|
|
LOE ID: |
103308 |
|
Pollutant: |
Mercury |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Total |
|
Beneficial Use: |
Municipal & Domestic Supply |
|
Number of Samples: |
5 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP RWB1 Monitoring data for Klamath River HU, Shasta River HA to determine beneficial use support and results are as follows: 0 of 5 samples exceeded the water quality standard for Mercury. |
Data Reference: |
Water Quality Assessment Data for the 2018 solicitation cycle submitted through CEDEN for SWAMP RWB1 Monitoring .
|
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
Water Quality Control Plan, North Coast Region (NCRWQCB 2018): All waters shall be maintained free of toxic substances in concentrations that are toxic to, or that produce detrimental physiological responses in human, plant, animal, or aquatic life. The established numeric criteria for mercury to protect of human health from the consumption of water and organisms is 0.050 ug/L (California Toxics Rule, 2000). |
Objective/Criterion Reference: |
Water Quality Standards 2000. Establishment of numeric criteria for priority toxic pollutants for the State of California: Rules and regulations. Federal Register Vol. 65, No. 97. Washington, D.C.: Environmental Protection Agency |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
The samples were collected at 1 monitoring site(s) (105SH1452) |
Temporal Representation: |
The samples were collected between the dates of 2013-03-06 and 2013-11-20 |
Environmental Conditions: |
|
QAPP Information: |
Quality Assurance Program Plan and Standard Operating Procedures for SWAMP program |
QAPP Information Reference(s): |
Quality Assurance Program Plans, Quality Assurance Project Plans, and Standard Operating Procedures for the SWAMP program |
|
Line of Evidence (LOE) for Decision ID 100756, Mercury
|
Region 1 |
Klamath River HU, Shasta River HA |
|
|
LOE ID: |
123505 |
|
Pollutant: |
Mercury |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Total |
|
Beneficial Use: |
Municipal & Domestic Supply |
|
Number of Samples: |
5 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
State Water Board staff re-assessed SWAMP data for Klamath River HU, Shasta River HA to determine beneficial use support and results are as follows: 0 of 5 samples exceed the criterion for Mercury, Total. This LOE re-assesses data from LOE 21509 from the 2010 Integrated Report. Data were re-assessed in order to (1) update the numeric objective, and (2) evaluate these data in their own LOE, instead of being evaluated in the same LOE as other metals data. |
Data Reference: |
Surface Water Ambient Monitoring Program (SWAMP). Summary Report for the North Coast Region (RWQCB-1) for years 2000-2006. North Coast Regional Water Quality Control Board. March 2008 |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
Water Quality Control Plan, North Coast Region (NCRWQCB 2011): All waters shall be maintained free of toxic substances in concentrations that are toxic to, or that produce detrimental physiological responses in human, plant, animal, or aquatic life. The established numeric criteria for mercury to protect of human health from the consumption of water and organisms is 0.050 ug/L (California Toxics Rule, 2000). |
Objective/Criterion Reference: |
Water Quality Control Plan (Basin Plan) for the North Coast Region |
Objective/Criterion Reference: |
Code of Federal Regulations 40 part 131.38 Establishment of numeric criteria for priority toxic pollutants for the State of California. 7/1/2011 Edition |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
Data for this line of evidence for Klamath River HU, Shasta River HA was collected at 1 monitoring site [ Shasta River near Edgewood - 105SH9274] |
Temporal Representation: |
Data was collected over the time period 10/7/2002-6/19/2003. |
Environmental Conditions: |
There are no known environmental conditions (e.g., seasonality, land use practices, fire events, storms, etc.) that are related to these data. |
QAPP Information: |
Quality control was conducted in accordance with the SWAMP Quality Assurance Management Plan (SWAMP 2002). |
QAPP Information Reference(s): |
Quality Assurance Management Plan for the State of California's Surface Water Ambient Monitoring Program. Sacramento, CA. State Water Resources Control Board. SWAMP. December 2002 (1st version)
|
|
Line of Evidence (LOE) for Decision ID 100756, Mercury
|
Region 1 |
Klamath River HU, Shasta River HA |
|
|
LOE ID: |
123504 |
|
Pollutant: |
Mercury |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Total |
|
Beneficial Use: |
Municipal & Domestic Supply |
|
Number of Samples: |
5 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
State Water Board staff re-assessed SWAMP data for Klamath River HU, Shasta River HA to determine beneficial use support and results are as follows: 0 of 5 samples exceed the criterion for Mercury, Total. This LOE re-assesses data from LOE 21509 from the 2010 Integrated Report. Data were re-assessed in order to (1) update the numeric objective, and (2) evaluate these data in their own LOE, instead of being evaluated in the same LOE as other metals data. |
Data Reference: |
Surface Water Ambient Monitoring Program (SWAMP). Summary Report for the North Coast Region (RWQCB-1) for years 2000-2006. North Coast Regional Water Quality Control Board. March 2008 |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
Water Quality Control Plan, North Coast Region (NCRWQCB 2011): All waters shall be maintained free of toxic substances in concentrations that are toxic to, or that produce detrimental physiological responses in human, plant, animal, or aquatic life. The established numeric criteria for mercury to protect of human health from the consumption of water and organisms is 0.050 ug/L (California Toxics Rule, 2000). |
Objective/Criterion Reference: |
Water Quality Control Plan (Basin Plan) for the North Coast Region |
Objective/Criterion Reference: |
Code of Federal Regulations 40 part 131.38 Establishment of numeric criteria for priority toxic pollutants for the State of California. 7/1/2011 Edition |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
Data for this line of evidence for Klamath River HU, Shasta River HA was collected at 1 monitoring site [ Shasta River at Montague - 105SHAMON] |
Temporal Representation: |
Data was collected over the time period 10/7/2002-6/19/2003. |
Environmental Conditions: |
There are no known environmental conditions (e.g., seasonality, land use practices, fire events, storms, etc.) that are related to these data. |
QAPP Information: |
Quality control was conducted in accordance with the SWAMP Quality Assurance Management Plan (SWAMP 2002). |
QAPP Information Reference(s): |
Letter requesting acceptance of late submittal |
|
Line of Evidence (LOE) for Decision ID 100756, Mercury
|
Region 1 |
Klamath River HU, Shasta River HA |
|
|
LOE ID: |
123507 |
|
Pollutant: |
Mercury |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Total |
|
Beneficial Use: |
Municipal & Domestic Supply |
|
Number of Samples: |
3 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
State Water Board staff re-assessed SWAMP data for Klamath River HU, Shasta River HA to determine beneficial use support and results are as follows: 0 of 3 samples exceed the criterion for Mercury, Total. This LOE re-assesses data from LOE 21509 from the 2010 Integrated Report. Data were re-assessed in order to (1) update the numeric objective, and (2) evaluate these data in their own LOE, instead of being evaluated in the same LOE as other metals data. |
Data Reference: |
Surface Water Ambient Monitoring Program (SWAMP). Summary Report for the North Coast Region (RWQCB-1) for years 2000-2006. North Coast Regional Water Quality Control Board. March 2008 |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
Water Quality Control Plan, North Coast Region (NCRWQCB 2011): All waters shall be maintained free of toxic substances in concentrations that are toxic to, or that produce detrimental physiological responses in human, plant, animal, or aquatic life. The established numeric criteria for mercury to protect of human health from the consumption of water and organisms is 0.050 ug/L (California Toxics Rule, 2000). |
Objective/Criterion Reference: |
Water Quality Control Plan (Basin Plan) for the North Coast Region |
Objective/Criterion Reference: |
Code of Federal Regulations 40 part 131.38 Establishment of numeric criteria for priority toxic pollutants for the State of California. 7/1/2011 Edition |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
Data for this line of evidence for Klamath River HU, Shasta River HA was collected at 1 monitoring site [ Yreka Creek at Highway 3 - 105YREHW3] |
Temporal Representation: |
Data was collected over the time period 10/21/2004-6/20/2005. |
Environmental Conditions: |
There are no known environmental conditions (e.g., seasonality, land use practices, fire events, storms, etc.) that are related to these data. |
QAPP Information: |
Quality control was conducted in accordance with the SWAMP Quality Assurance Management Plan (SWAMP 2002). |
QAPP Information Reference(s): |
Quality Assurance Management Plan for the State of California's Surface Water Ambient Monitoring Program. Sacramento, CA. State Water Resources Control Board. SWAMP. December 2002 (1st version)
|
|
Line of Evidence (LOE) for Decision ID 100756, Mercury
|
Region 1 |
Klamath River HU, Shasta River HA |
|
|
LOE ID: |
42742 |
|
Pollutant: |
Mercury |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Total |
|
Beneficial Use: |
Municipal & Domestic Supply |
|
Number of Samples: |
4 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP data for Klamath River HU, Shasta River HA to determine beneficial use support and results are as follows: 0 of 4 samples exceed the criterion for Mercury. |
Data Reference: |
RWB1 Trend Maintenance Periods FYs 2007 2008 |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
Water Quality Control Plan, North Coast Region (NCRWQCB 2011): All waters shall be maintained free of toxic substances in concentrations that are toxic to, or that produce detrimental physiological responses in human, plant, animal, or aquatic life. The established numeric criteria for mercury to protect of human health from the consumption of water and organisms is 0.050 ug/L (California Toxics Rule, 2000). |
Objective/Criterion Reference: |
Code of Federal Regulations 40 part 131.38 Establishment of numeric criteria for priority toxic pollutants for the State of California. 7/1/2011 Edition |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
Data for this line of evidence for Klamath River HU, Shasta River HA was collected at 1 monitoring site [ Shasta River near Edgewood - 105SHAEDG] |
Temporal Representation: |
Data was collected over the time period 11/15/2007-7/16/2008. |
Environmental Conditions: |
Staff is not aware of any special conditions that might affect interpretation of the data. |
QAPP Information: |
The SWAMP QAPP (2008) was followed. |
QAPP Information Reference(s): |
Surface Water Ambient Monitoring Program Quality Assurance Program Plan |
|
Line of Evidence (LOE) for Decision ID 100756, Mercury
|
Region 1 |
Klamath River HU, Shasta River HA |
|
|
LOE ID: |
42779 |
|
Pollutant: |
Mercury |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Total |
|
Beneficial Use: |
Cold Freshwater Habitat |
|
Number of Samples: |
4 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP data for Klamath River HU, Shasta River HA to determine beneficial use support and results are as follows: 0 of 4 samples exceed the criterion for Mercury. |
Data Reference: |
RWB1 Trend Maintenance Periods FYs 2007 2008 |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
Water Quality Control Plan, North Coast Region (NCRWQCB 2011): All waters shall be maintained free of toxic substances in concentrations that are toxic to, or that produce detrimental physiological responses in human, plant, animal, or aquatic life. |
Objective/Criterion Reference: |
Water Quality Control Plan (Basin Plan) for the North Coast Region |
|
Evaluation Guideline: |
National Recommended Water Quality Criteria Continuous Concentrations (4-day average concentrations) for freshwater aquatic organisms exposure to Total mercury is 0.77 ug/L. |
Guideline Reference: |
National Recommended Water Quality Criteria. United States Environmental Protection Agency. Office of Water. Office of Science and Technology |
|
Spatial Representation: |
Data for this line of evidence for Klamath River HU, Shasta River HA was collected at 1 monitoring site [ Shasta River near Edgewood - 105SHAEDG] |
Temporal Representation: |
Data was collected over the time period 11/15/2007-7/16/2008. |
Environmental Conditions: |
Staff is not aware of any special conditions that might affect interpretation of the data. |
QAPP Information: |
The SWAMP QAPP (2008) was followed. |
QAPP Information Reference(s): |
Surface Water Ambient Monitoring Program Quality Assurance Program Plan |
|
Line of Evidence (LOE) for Decision ID 100756, Mercury
|
Region 1 |
Klamath River HU, Shasta River HA |
|
|
LOE ID: |
103310 |
|
Pollutant: |
Mercury |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Total |
|
Beneficial Use: |
Cold Freshwater Habitat |
|
Number of Samples: |
5 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP RWB1 Monitoring data for Klamath River HU, Shasta River HA to determine beneficial use support and results are as follows: 0 of 5 samples exceeded the water quality standard for Mercury. |
Data Reference: |
Water Quality Assessment Data for the 2018 solicitation cycle submitted through CEDEN for SWAMP RWB1 Monitoring .
|
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
Water Quality Control Plan, North Coast Region (NCRWQCB 2018): All waters shall be maintained free of toxic substances in concentrations that are toxic to, or that produce detrimental physiological responses in human, plant, animal, or aquatic life. |
Objective/Criterion Reference: |
Water Quality Control Plan (Basin Plan) for the North Coast Region |
|
Evaluation Guideline: |
National Recommended Water Quality Criteria Continuous Concentrations (4-day average concentrations) for freshwater aquatic organisms exposure to total mercury is 0.77 ug/L. |
Guideline Reference: |
National Recommended Water Quality Criteria. United States Environmental Protection Agency. Office of Water. Current as of 08/03/2016. |
|
Spatial Representation: |
The samples were collected at 1 monitoring site(s) (105SH9274) |
Temporal Representation: |
The samples were collected between the dates of 2013-03-07 and 2013-11-20 |
Environmental Conditions: |
|
QAPP Information: |
Quality Assurance Program Plan and Standard Operating Procedures for SWAMP program |
QAPP Information Reference(s): |
Quality Assurance Program Plans, Quality Assurance Project Plans, and Standard Operating Procedures for the SWAMP program |
|
Line of Evidence (LOE) for Decision ID 100756, Mercury
|
Region 1 |
Klamath River HU, Shasta River HA |
|
|
LOE ID: |
103307 |
|
Pollutant: |
Mercury |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Total |
|
Beneficial Use: |
Cold Freshwater Habitat |
|
Number of Samples: |
5 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP RWB1 Monitoring data for Klamath River HU, Shasta River HA to determine beneficial use support and results are as follows: 0 of 5 samples exceeded the water quality standard for Mercury. |
Data Reference: |
Water Quality Assessment Data for the 2018 solicitation cycle submitted through CEDEN for SWAMP RWB1 Monitoring .
|
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
Water Quality Control Plan, North Coast Region (NCRWQCB 2018): All waters shall be maintained free of toxic substances in concentrations that are toxic to, or that produce detrimental physiological responses in human, plant, animal, or aquatic life. |
Objective/Criterion Reference: |
Water Quality Control Plan (Basin Plan) for the North Coast Region |
|
Evaluation Guideline: |
National Recommended Water Quality Criteria Continuous Concentrations (4-day average concentrations) for freshwater aquatic organisms exposure to total mercury is 0.77 ug/L. |
Guideline Reference: |
National Recommended Water Quality Criteria. United States Environmental Protection Agency. Office of Water. Current as of 08/03/2016. |
|
Spatial Representation: |
The samples were collected at 1 monitoring site(s) (105SH1452) |
Temporal Representation: |
The samples were collected between the dates of 2013-03-06 and 2013-11-20 |
Environmental Conditions: |
|
QAPP Information: |
Quality Assurance Program Plan and Standard Operating Procedures for SWAMP program |
QAPP Information Reference(s): |
Quality Assurance Program Plans, Quality Assurance Project Plans, and Standard Operating Procedures for the SWAMP program |
|
Line of Evidence (LOE) for Decision ID 100756, Mercury
|
Region 1 |
Klamath River HU, Shasta River HA |
|
|
LOE ID: |
42458 |
|
Pollutant: |
Mercury |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Total |
|
Beneficial Use: |
Cold Freshwater Habitat |
|
Number of Samples: |
4 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP data for Klamath River HU, Shasta River HA to determine beneficial use support and results are as follows: 0 of 4 samples exceed the criterion for Mercury. |
Data Reference: |
RWB1 Trend Maintenance Periods FYs 2007 2008 |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
Water Quality Control Plan, North Coast Region (NCRWQCB 2011): All waters shall be maintained free of toxic substances in concentrations that are toxic to, or that produce detrimental physiological responses in human, plant, animal, or aquatic life. |
Objective/Criterion Reference: |
Water Quality Control Plan (Basin Plan) for the North Coast Region |
|
Evaluation Guideline: |
National Recommended Water Quality Criteria Continuous Concentrations (4-day average concentrations) for freshwater aquatic organisms exposure to Total mercury is 0.77 ug/L. |
Guideline Reference: |
National Recommended Water Quality Criteria. United States Environmental Protection Agency. Office of Water. Office of Science and Technology |
|
Spatial Representation: |
Data for this line of evidence for Klamath River HU, Shasta River HA was collected at 1 monitoring site [ Shasta River at Hwy 263 - 105SHA263] |
Temporal Representation: |
Data was collected over the time period 11/15/2007-7/16/2008. |
Environmental Conditions: |
Staff is not aware of any special conditions that might affect interpretation of the data. |
QAPP Information: |
The SWAMP QAPP (2008) was followed. |
QAPP Information Reference(s): |
Surface Water Ambient Monitoring Program Quality Assurance Program Plan |
|
Line of Evidence (LOE) for Decision ID 100756, Mercury
|
Region 1 |
Klamath River HU, Shasta River HA |
|
|
LOE ID: |
103306 |
|
Pollutant: |
Mercury |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Total |
|
Beneficial Use: |
Commercial or recreational collection of fish, shellfish, or organisms |
|
Number of Samples: |
5 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP RWB1 Monitoring data for Klamath River HU, Shasta River HA to determine beneficial use support and results are as follows: 0 of 5 samples exceeded the water quality standard for Mercury. |
Data Reference: |
Water Quality Assessment Data for the 2018 solicitation cycle submitted through CEDEN for SWAMP RWB1 Monitoring .
|
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
Water Quality Control Plan, North Coast Region (NCRWQCB 2018): All waters shall be maintained free of toxic substances in concentrations that are toxic to, or that produce detrimental physiological responses in human, plant, animal, or aquatic life. The established numeric criteria for mercury to protect of human health from the consumption of organisms only is 0.051 ug/L (California Toxics Rule, 2000). |
Objective/Criterion Reference: |
Water Quality Standards 2000. Establishment of numeric criteria for priority toxic pollutants for the State of California: Rules and regulations. Federal Register Vol. 65, No. 97. Washington, D.C.: Environmental Protection Agency |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
The samples were collected at 1 monitoring site(s) (105SH1452) |
Temporal Representation: |
The samples were collected between the dates of 2013-03-06 and 2013-11-20 |
Environmental Conditions: |
|
QAPP Information: |
Quality Assurance Program Plan and Standard Operating Procedures for SWAMP program |
QAPP Information Reference(s): |
Quality Assurance Program Plans, Quality Assurance Project Plans, and Standard Operating Procedures for the SWAMP program |
|
Line of Evidence (LOE) for Decision ID 100756, Mercury
|
Region 1 |
Klamath River HU, Shasta River HA |
|
|
LOE ID: |
42694 |
|
Pollutant: |
Mercury |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Total |
|
Beneficial Use: |
Commercial or recreational collection of fish, shellfish, or organisms |
|
Number of Samples: |
4 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP data for Klamath River HU, Shasta River HA to determine beneficial use support and results are as follows: 0 of 4 samples exceed the criterion for Mercury. |
Data Reference: |
RWB1 Trend Maintenance Periods FYs 2007 2008 |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
Water Quality Control Plan, North Coast Region (NCRWQCB 2011): All waters shall be maintained free of toxic substances in concentrations that are toxic to, or that produce detrimental physiological responses in human, plant, animal, or aquatic life. The established numeric criteria for mercury to protect of human health from the consumption of organisms only is 0.051 ug/L (California Toxics Rule, 2000). |
Objective/Criterion Reference: |
Code of Federal Regulations 40 part 131.38 Establishment of numeric criteria for priority toxic pollutants for the State of California. 7/1/2011 Edition |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
Data for this line of evidence for Klamath River HU, Shasta River HA was collected at 1 monitoring site [ Shasta River at Hwy 263 - 105SHA263] |
Temporal Representation: |
Data was collected over the time period 11/15/2007-7/16/2008. |
Environmental Conditions: |
Staff is not aware of any special conditions that might affect interpretation of the data. |
QAPP Information: |
The SWAMP QAPP (2008) was followed. |
QAPP Information Reference(s): |
Surface Water Ambient Monitoring Program Quality Assurance Program Plan |
|
Line of Evidence (LOE) for Decision ID 169753, Methidathion
|
Region 1 |
Klamath River HU, Shasta River HA |
|
|
LOE ID: |
350008 |
|
Pollutant: |
Methidathion |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Total |
|
Beneficial Use: |
Warm Freshwater Habitat |
|
Number of Samples: |
3 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed RWB1 Trend Maintenance Periods FYs 2007 2008 data for Klamath River HU, Shasta River HA to determine beneficial use support and results are as follows: 0 of 3 samples exceeded the water quality threshold for Methidathion. |
Data Reference: |
RWB1 Trend Maintenance Periods FYs 2007 2008 |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
All waters shall be maintained free of toxic substances in concentrations which are toxic to, or which produce detrimental physiological responses in, human, plant, animal, or aquatic life. (Basin Plan). |
Objective/Criterion Reference: |
Water Quality Control Plan (Basin Plan) for the North Coast Region |
|
Evaluation Guideline: |
The evaluation guideline for methidathion is the USEPA Aquatic Life Benchmark of 0.66 ug/L for an invertebrate (chronic). |
Guideline Reference: |
OPP Aquatic Life Benchmarks |
|
Spatial Representation: |
The samples were collected at 1 monitoring site: 105SHAEDG (Shasta River near Edgewood). |
Temporal Representation: |
The samples were collected between the dates of 2007-11-15 and 2008-07-16 |
Environmental Conditions: |
|
QAPP Information: |
Generic SWAMP QAPrP |
QAPP Information Reference(s): |
Generic SWAMP QAPrP |
|
Line of Evidence (LOE) for Decision ID 169753, Methidathion
|
Region 1 |
Klamath River HU, Shasta River HA |
|
|
LOE ID: |
350020 |
|
Pollutant: |
Methidathion |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Total |
|
Beneficial Use: |
Cold Freshwater Habitat |
|
Number of Samples: |
3 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed RWB1 Trend Maintenance Periods FYs 2007 2008 data for Klamath River HU, Shasta River HA to determine beneficial use support and results are as follows: 0 of 3 samples exceeded the water quality threshold for Methidathion. |
Data Reference: |
RWB1 Trend Maintenance Periods FYs 2007 2008 |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
All waters shall be maintained free of toxic substances in concentrations which are toxic to, or which produce detrimental physiological responses in, human, plant, animal, or aquatic life. (Basin Plan). |
Objective/Criterion Reference: |
Water Quality Control Plan (Basin Plan) for the North Coast Region |
|
Evaluation Guideline: |
The evaluation guideline for methidathion is the USEPA Aquatic Life Benchmark of 0.66 ug/L for an invertebrate (chronic). |
Guideline Reference: |
OPP Aquatic Life Benchmarks |
|
Spatial Representation: |
The samples were collected at 1 monitoring site: 105SHA263 (Shasta River at Hwy 263). |
Temporal Representation: |
The samples were collected between the dates of 2007-11-15 and 2008-07-16 |
Environmental Conditions: |
|
QAPP Information: |
Generic SWAMP QAPrP |
QAPP Information Reference(s): |
Generic SWAMP QAPrP |
|
Line of Evidence (LOE) for Decision ID 169753, Methidathion
|
Region 1 |
Klamath River HU, Shasta River HA |
|
|
LOE ID: |
103314 |
|
Pollutant: |
Methidathion |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Total |
|
Beneficial Use: |
Warm Freshwater Habitat |
|
Number of Samples: |
3 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP RWB1 Monitoring data for Klamath River HU, Shasta River HA to determine beneficial use support and results are as follows: 0 of 3 samples exceeded the water quality standard for Methidathion. |
Data Reference: |
Water Quality Assessment Data for the 2018 solicitation cycle submitted through CEDEN for SWAMP RWB1 Monitoring .
|
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
All waters shall be maintained free of toxic substances in concentrations which are toxic to, or which produce detrimental physiological responses in, human, plant, animal, or aquatic life. (Basin Plan). |
Objective/Criterion Reference: |
Water Quality Control Plan (Basin Plan) for the North Coast Region |
|
Evaluation Guideline: |
The evaluation guideline for Methidathion is the USEPA Aquatic Life Benchmark of 0.66 ug/L for an invertebrate (chronic). |
Guideline Reference: |
OPP Aquatic Life Benchmarks |
|
Spatial Representation: |
The samples were collected at 1 monitoring site(s) (105SH1452) |
Temporal Representation: |
The samples were collected between the dates of 2013-03-06 and 2013-11-20 |
Environmental Conditions: |
|
QAPP Information: |
Quality Assurance Program Plan and Standard Operating Procedures for SWAMP program |
QAPP Information Reference(s): |
Quality Assurance Program Plans, Quality Assurance Project Plans, and Standard Operating Procedures for the SWAMP program |
|
Line of Evidence (LOE) for Decision ID 169753, Methidathion
|
Region 1 |
Klamath River HU, Shasta River HA |
|
|
LOE ID: |
103316 |
|
Pollutant: |
Methidathion |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Total |
|
Beneficial Use: |
Warm Freshwater Habitat |
|
Number of Samples: |
3 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP RWB1 Monitoring data for Klamath River HU, Shasta River HA to determine beneficial use support and results are as follows: 0 of 3 samples exceeded the water quality standard for Methidathion. |
Data Reference: |
Water Quality Assessment Data for the 2018 solicitation cycle submitted through CEDEN for SWAMP RWB1 Monitoring .
|
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
All waters shall be maintained free of toxic substances in concentrations which are toxic to, or which produce detrimental physiological responses in, human, plant, animal, or aquatic life. (Basin Plan). |
Objective/Criterion Reference: |
Water Quality Control Plan (Basin Plan) for the North Coast Region |
|
Evaluation Guideline: |
The evaluation guideline for Methidathion is the USEPA Aquatic Life Benchmark of 0.66 ug/L for an invertebrate (chronic). |
Guideline Reference: |
OPP Aquatic Life Benchmarks |
|
Spatial Representation: |
The samples were collected at 1 monitoring site(s) (105SH9274) |
Temporal Representation: |
The samples were collected between the dates of 2013-03-07 and 2013-11-20 |
Environmental Conditions: |
|
QAPP Information: |
Quality Assurance Program Plan and Standard Operating Procedures for SWAMP program |
QAPP Information Reference(s): |
Quality Assurance Program Plans, Quality Assurance Project Plans, and Standard Operating Procedures for the SWAMP program |
|
Line of Evidence (LOE) for Decision ID 169753, Methidathion
|
Region 1 |
Klamath River HU, Shasta River HA |
|
|
LOE ID: |
103315 |
|
Pollutant: |
Methidathion |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Total |
|
Beneficial Use: |
Cold Freshwater Habitat |
|
Number of Samples: |
3 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP RWB1 Monitoring data for Klamath River HU, Shasta River HA to determine beneficial use support and results are as follows: 0 of 3 samples exceeded the water quality standard for Methidathion. |
Data Reference: |
Water Quality Assessment Data for the 2018 solicitation cycle submitted through CEDEN for SWAMP RWB1 Monitoring .
|
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
All waters shall be maintained free of toxic substances in concentrations which are toxic to, or which produce detrimental physiological responses in, human, plant, animal, or aquatic life. (Basin Plan). |
Objective/Criterion Reference: |
Water Quality Control Plan (Basin Plan) for the North Coast Region |
|
Evaluation Guideline: |
The evaluation guideline for Methidathion is the USEPA Aquatic Life Benchmark of 0.66 ug/L for an invertebrate (chronic). |
Guideline Reference: |
OPP Aquatic Life Benchmarks |
|
Spatial Representation: |
The samples were collected at 1 monitoring site(s) (105SH9274) |
Temporal Representation: |
The samples were collected between the dates of 2013-03-07 and 2013-11-20 |
Environmental Conditions: |
|
QAPP Information: |
Quality Assurance Program Plan and Standard Operating Procedures for SWAMP program |
QAPP Information Reference(s): |
Quality Assurance Program Plans, Quality Assurance Project Plans, and Standard Operating Procedures for the SWAMP program |
|
Line of Evidence (LOE) for Decision ID 169753, Methidathion
|
Region 1 |
Klamath River HU, Shasta River HA |
|
|
LOE ID: |
103313 |
|
Pollutant: |
Methidathion |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Total |
|
Beneficial Use: |
Cold Freshwater Habitat |
|
Number of Samples: |
3 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP RWB1 Monitoring data for Klamath River HU, Shasta River HA to determine beneficial use support and results are as follows: 0 of 3 samples exceeded the water quality standard for Methidathion. |
Data Reference: |
Water Quality Assessment Data for the 2018 solicitation cycle submitted through CEDEN for SWAMP RWB1 Monitoring .
|
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
All waters shall be maintained free of toxic substances in concentrations which are toxic to, or which produce detrimental physiological responses in, human, plant, animal, or aquatic life. (Basin Plan). |
Objective/Criterion Reference: |
Water Quality Control Plan (Basin Plan) for the North Coast Region |
|
Evaluation Guideline: |
The evaluation guideline for Methidathion is the USEPA Aquatic Life Benchmark of 0.66 ug/L for an invertebrate (chronic). |
Guideline Reference: |
OPP Aquatic Life Benchmarks |
|
Spatial Representation: |
The samples were collected at 1 monitoring site(s) (105SH1452) |
Temporal Representation: |
The samples were collected between the dates of 2013-03-06 and 2013-11-20 |
Environmental Conditions: |
|
QAPP Information: |
Quality Assurance Program Plan and Standard Operating Procedures for SWAMP program |
QAPP Information Reference(s): |
Quality Assurance Program Plans, Quality Assurance Project Plans, and Standard Operating Procedures for the SWAMP program |
|
Line of Evidence (LOE) for Decision ID 169753, Methidathion
|
Region 1 |
Klamath River HU, Shasta River HA |
|
|
LOE ID: |
123525 |
|
Pollutant: |
Methidathion |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
None |
|
Beneficial Use: |
Municipal & Domestic Supply |
|
Number of Samples: |
16 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
State Water Board staff re-assessed SWAMP data for Klamath River HU, Shasta River HA to determine beneficial use support and results are as follows: 0 of 16 samples exceed the criterion for Methidathion, Total. This LOE re-assesses data from LOE 29849 from the 2010 Integrated Report. Data were re-assessed in order to evaluate these data in their own LOE, instead of being evaluated in the same LOE as other pesticide data. |
Data Reference: |
Surface Water Ambient Monitoring Program (SWAMP). Summary Report for the North Coast Region (RWQCB-1) for years 2000-2006. North Coast Regional Water Quality Control Board. March 2008 |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
Water Quality Control Plan, North Coast Region (NCRWQCB 2011): Waters designated for use as domestic or municipal supply (MUN) shall not contain concentrations of chemical constituents in excess of the limits specified in California Code of Regulations, Title 22, Chapter 15. The maximum contaminant level listed in Table 64444-A for methoxychlor is 0.03 mg/L. |
Objective/Criterion Reference: |
Water Quality Control Plan (Basin Plan) for the North Coast Region |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
Data for this line of evidence for Klamath River HU, Shasta River HA was collected at 1 monitoring site [ Shasta River at Hwy 263 - 105SH1452] |
Temporal Representation: |
Data was collected over the time period 4/24/2001-11/16/2006. |
Environmental Conditions: |
There are no known environmental conditions (e.g., seasonality, land use practices, fire events, storms, etc.) that are related to these data. |
QAPP Information: |
Quality control was conducted in accordance with the SWAMP Quality Assurance Management Plan (SWAMP 2002). |
QAPP Information Reference(s): |
Quality Assurance Management Plan for the State of California's Surface Water Ambient Monitoring Program. Sacramento, CA. State Water Resources Control Board. SWAMP. December 2002 (1st version)
|
|
Line of Evidence (LOE) for Decision ID 169753, Methidathion
|
Region 1 |
Klamath River HU, Shasta River HA |
|
|
LOE ID: |
350034 |
|
Pollutant: |
Methidathion |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Total |
|
Beneficial Use: |
Cold Freshwater Habitat |
|
Number of Samples: |
3 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed RWB1 Trend Maintenance Periods FYs 2007 2008 data for Klamath River HU, Shasta River HA to determine beneficial use support and results are as follows: 0 of 3 samples exceeded the water quality threshold for Methidathion. |
Data Reference: |
RWB1 Trend Maintenance Periods FYs 2007 2008 |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
All waters shall be maintained free of toxic substances in concentrations which are toxic to, or which produce detrimental physiological responses in, human, plant, animal, or aquatic life. (Basin Plan). |
Objective/Criterion Reference: |
Water Quality Control Plan (Basin Plan) for the North Coast Region |
|
Evaluation Guideline: |
The evaluation guideline for methidathion is the USEPA Aquatic Life Benchmark of 0.66 ug/L for an invertebrate (chronic). |
Guideline Reference: |
OPP Aquatic Life Benchmarks |
|
Spatial Representation: |
The samples were collected at 1 monitoring site: 105SHAEDG (Shasta River near Edgewood). |
Temporal Representation: |
The samples were collected between the dates of 2007-11-15 and 2008-07-16 |
Environmental Conditions: |
|
QAPP Information: |
Generic SWAMP QAPrP |
QAPP Information Reference(s): |
Generic SWAMP QAPrP |
|
Line of Evidence (LOE) for Decision ID 169753, Methidathion
|
Region 1 |
Klamath River HU, Shasta River HA |
|
|
LOE ID: |
350024 |
|
Pollutant: |
Methidathion |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Total |
|
Beneficial Use: |
Warm Freshwater Habitat |
|
Number of Samples: |
3 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed RWB1 Trend Maintenance Periods FYs 2007 2008 data for Klamath River HU, Shasta River HA to determine beneficial use support and results are as follows: 0 of 3 samples exceeded the water quality threshold for Methidathion. |
Data Reference: |
RWB1 Trend Maintenance Periods FYs 2007 2008 |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
All waters shall be maintained free of toxic substances in concentrations which are toxic to, or which produce detrimental physiological responses in, human, plant, animal, or aquatic life. (Basin Plan). |
Objective/Criterion Reference: |
Water Quality Control Plan (Basin Plan) for the North Coast Region |
|
Evaluation Guideline: |
The evaluation guideline for methidathion is the USEPA Aquatic Life Benchmark of 0.66 ug/L for an invertebrate (chronic). |
Guideline Reference: |
OPP Aquatic Life Benchmarks |
|
Spatial Representation: |
The samples were collected at 1 monitoring site: 105SHA263 (Shasta River at Hwy 263). |
Temporal Representation: |
The samples were collected between the dates of 2007-11-15 and 2008-07-16 |
Environmental Conditions: |
|
QAPP Information: |
Generic SWAMP QAPrP |
QAPP Information Reference(s): |
Generic SWAMP QAPrP |
|
Line of Evidence (LOE) for Decision ID 169753, Methidathion
|
Region 1 |
Klamath River HU, Shasta River HA |
|
|
LOE ID: |
123369 |
|
Pollutant: |
Methidathion |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
None |
|
Beneficial Use: |
Municipal & Domestic Supply |
|
Number of Samples: |
16 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
State Water Board staff re-assessed SWAMP data for Klamath River HU, Shasta River HA to determine beneficial use support and results are as follows: 0 of 16 samples exceed the criterion for Methidathion, Total. This LOE re-assesses data from LOE 29849 from the 2010 Integrated Report. Data were re-assessed in order to evaluate these data in their own LOE, instead of being evaluated in the same LOE as other pesticide data. |
Data Reference: |
Surface Water Ambient Monitoring Program (SWAMP). Summary Report for the North Coast Region (RWQCB-1) for years 2000-2006. North Coast Regional Water Quality Control Board. March 2008 |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
Water Quality Control Plan, North Coast Region (NCRWQCB 2011): Waters designated for use as domestic or municipal supply (MUN) shall not contain concentrations of chemical constituents in excess of the limits specified in California Code of Regulations, Title 22, Chapter 15. The maximum contaminant level listed in Table 64444-A for methoxychlor is 0.03 mg/L. |
Objective/Criterion Reference: |
Water Quality Control Plan (Basin Plan) for the North Coast Region |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
Data for this line of evidence for Klamath River HU, Shasta River HA was collected at 1 monitoring site [ Yreka Creek at Anderson Rd - 105YREAND] |
Temporal Representation: |
Data was collected over the time period 10/9/2002-6/20/2005. |
Environmental Conditions: |
There are no known environmental conditions (e.g., seasonality, land use practices, fire events, storms, etc.) that are related to these data. |
QAPP Information: |
Quality control was conducted in accordance with the SWAMP Quality Assurance Management Plan (SWAMP 2002). |
QAPP Information Reference(s): |
Quality Assurance Management Plan for the State of California's Surface Water Ambient Monitoring Program. Sacramento, CA. State Water Resources Control Board. SWAMP. December 2002 (1st version)
|
|
Line of Evidence (LOE) for Decision ID 169753, Methidathion
|
Region 1 |
Klamath River HU, Shasta River HA |
|
|
LOE ID: |
123368 |
|
Pollutant: |
Methidathion |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
None |
|
Beneficial Use: |
Municipal & Domestic Supply |
|
Number of Samples: |
8 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
State Water Board staff re-assessed SWAMP data for Klamath River HU, Shasta River HA to determine beneficial use support and results are as follows: 0 of 8 samples exceed the criterion for Methidathion, Total. This LOE re-assesses data from LOE 29849 from the 2010 Integrated Report. Data were re-assessed in order to evaluate these data in their own LOE, instead of being evaluated in the same LOE as other pesticide data. |
Data Reference: |
Surface Water Ambient Monitoring Program (SWAMP). Summary Report for the North Coast Region (RWQCB-1) for years 2000-2006. North Coast Regional Water Quality Control Board. March 2008 |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
Water Quality Control Plan, North Coast Region (NCRWQCB 2011): Waters designated for use as domestic or municipal supply (MUN) shall not contain concentrations of chemical constituents in excess of the limits specified in California Code of Regulations, Title 22, Chapter 15. The maximum contaminant level listed in Table 64444-A for methoxychlor is 0.03 mg/L. |
Objective/Criterion Reference: |
Water Quality Control Plan (Basin Plan) for the North Coast Region |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
Data for this line of evidence for Klamath River HU, Shasta River HA was collected at 1 monitoring site [ Shasta River near Edgewood - 105SH9274] |
Temporal Representation: |
Data was collected over the time period 10/7/2002-6/19/2003. |
Environmental Conditions: |
There are no known environmental conditions (e.g., seasonality, land use practices, fire events, storms, etc.) that are related to these data. |
QAPP Information: |
Quality control was conducted in accordance with the SWAMP Quality Assurance Management Plan (SWAMP 2002). |
QAPP Information Reference(s): |
Quality Assurance Management Plan for the State of California's Surface Water Ambient Monitoring Program. Sacramento, CA. State Water Resources Control Board. SWAMP. December 2002 (1st version)
|
|
Line of Evidence (LOE) for Decision ID 169753, Methidathion
|
Region 1 |
Klamath River HU, Shasta River HA |
|
|
LOE ID: |
123526 |
|
Pollutant: |
Methidathion |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
None |
|
Beneficial Use: |
Municipal & Domestic Supply |
|
Number of Samples: |
8 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
State Water Board staff re-assessed SWAMP data for Klamath River HU, Shasta River HA to determine beneficial use support and results are as follows: 0 of 8 samples exceed the criterion for Methidathion, Total. This LOE re-assesses data from LOE 29849 from the 2010 Integrated Report. Data were re-assessed in order to evaluate these data in their own LOE, instead of being evaluated in the same LOE as other pesticide data. |
Data Reference: |
Surface Water Ambient Monitoring Program (SWAMP). Summary Report for the North Coast Region (RWQCB-1) for years 2000-2006. North Coast Regional Water Quality Control Board. March 2008 |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
Water Quality Control Plan, North Coast Region (NCRWQCB 2011): Waters designated for use as domestic or municipal supply (MUN) shall not contain concentrations of chemical constituents in excess of the limits specified in California Code of Regulations, Title 22, Chapter 15. The maximum contaminant level listed in Table 64444-A for methoxychlor is 0.03 mg/L. |
Objective/Criterion Reference: |
Water Quality Control Plan (Basin Plan) for the North Coast Region |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
Data for this line of evidence for Klamath River HU, Shasta River HA was collected at 1 monitoring site [ Shasta River at Montague - 105SHAMON] |
Temporal Representation: |
Data was collected over the time period 10/7/2002-6/19/2003. |
Environmental Conditions: |
There are no known environmental conditions (e.g., seasonality, land use practices, fire events, storms, etc.) that are related to these data. |
QAPP Information: |
Quality control was conducted in accordance with the SWAMP Quality Assurance Management Plan (SWAMP 2002). |
QAPP Information Reference(s): |
Quality Assurance Management Plan for the State of California's Surface Water Ambient Monitoring Program. Sacramento, CA. State Water Resources Control Board. SWAMP. December 2002 (1st version)
|
|
Line of Evidence (LOE) for Decision ID 169753, Methidathion
|
Region 1 |
Klamath River HU, Shasta River HA |
|
|
LOE ID: |
123370 |
|
Pollutant: |
Methidathion |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
None |
|
Beneficial Use: |
Municipal & Domestic Supply |
|
Number of Samples: |
8 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
State Water Board staff re-assessed SWAMP data for Klamath River HU, Shasta River HA to determine beneficial use support and results are as follows: 0 of 8 samples exceed the criterion for Methidathion, Total. This LOE re-assesses data from LOE 29849 from the 2010 Integrated Report. Data were re-assessed in order to evaluate these data in their own LOE, instead of being evaluated in the same LOE as other pesticide data. |
Data Reference: |
Surface Water Ambient Monitoring Program (SWAMP). Summary Report for the North Coast Region (RWQCB-1) for years 2000-2006. North Coast Regional Water Quality Control Board. March 2008 |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
Water Quality Control Plan, North Coast Region (NCRWQCB 2011): Waters designated for use as domestic or municipal supply (MUN) shall not contain concentrations of chemical constituents in excess of the limits specified in California Code of Regulations, Title 22, Chapter 15. The maximum contaminant level listed in Table 64444-A for methoxychlor is 0.03 mg/L. |
Objective/Criterion Reference: |
Water Quality Control Plan (Basin Plan) for the North Coast Region |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
Data for this line of evidence for Klamath River HU, Shasta River HA was collected at 1 monitoring site [ Yreka Creek at Highway 3 - 105YREHW3] |
Temporal Representation: |
Data was collected over the time period 10/21/2004-6/20/2005. |
Environmental Conditions: |
There are no known environmental conditions (e.g., seasonality, land use practices, fire events, storms, etc.) that are related to these data. |
QAPP Information: |
Quality control was conducted in accordance with the SWAMP Quality Assurance Management Plan (SWAMP 2002). |
QAPP Information Reference(s): |
Quality Assurance Management Plan for the State of California's Surface Water Ambient Monitoring Program. Sacramento, CA. State Water Resources Control Board. SWAMP. December 2002 (1st version)
|
|
Line of Evidence (LOE) for Decision ID 168837, Molinate
|
Region 1 |
Klamath River HU, Shasta River HA |
|
|
LOE ID: |
350123 |
|
Pollutant: |
Molinate |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Total |
|
Beneficial Use: |
Warm Freshwater Habitat |
|
Number of Samples: |
3 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed RWB1 Trend Maintenance Periods FYs 2007 2008 data for Klamath River HU, Shasta River HA to determine beneficial use support and results are as follows: 0 of 3 samples exceeded the water quality threshold for Molinate. |
Data Reference: |
RWB1 Trend Maintenance Periods FYs 2007 2008 |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
All waters shall be maintained free of toxic substances in concentrations which are toxic to, or which produce detrimental physiological responses in, human, plant, animal, or aquatic life. (Basin Plan). |
Objective/Criterion Reference: |
Water Quality Control Plan (Basin Plan) for the North Coast Region |
|
Evaluation Guideline: |
The evaluation guideline for molinate is the USEPA Aquatic Life Benchmark of 105 ug/L for a fish (acute). |
Guideline Reference: |
OPP Aquatic Life Benchmarks |
|
Spatial Representation: |
The samples were collected at 1 monitoring site: 105SHA263 (Shasta River at Hwy 263). |
Temporal Representation: |
The samples were collected between the dates of 2007-11-15 and 2008-07-16 |
Environmental Conditions: |
|
QAPP Information: |
Generic SWAMP QAPrP |
QAPP Information Reference(s): |
Generic SWAMP QAPrP |
|
Line of Evidence (LOE) for Decision ID 168837, Molinate
|
Region 1 |
Klamath River HU, Shasta River HA |
|
|
LOE ID: |
103331 |
|
Pollutant: |
Molinate |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Total |
|
Beneficial Use: |
Cold Freshwater Habitat |
|
Number of Samples: |
3 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP RWB1 Monitoring data for Klamath River HU, Shasta River HA to determine beneficial use support and results are as follows: 0 of 3 samples exceeded the water quality standard for Molinate. |
Data Reference: |
Water Quality Assessment Data for the 2018 solicitation cycle submitted through CEDEN for SWAMP RWB1 Monitoring .
|
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
All waters shall be maintained free of toxic substances in concentrations which are toxic to, or which produce detrimental physiological responses in, human, plant, animal, or aquatic life. (Basin Plan). |
Objective/Criterion Reference: |
Water Quality Control Plan (Basin Plan) for the North Coast Region |
|
Evaluation Guideline: |
The evaluation guideline for Molinate is the USEPA Aquatic Life Benchmark of 105 ug/L for a fish (acute). |
Guideline Reference: |
OPP Aquatic Life Benchmarks |
|
Spatial Representation: |
The samples were collected at 1 monitoring site(s) (105SH9274) |
Temporal Representation: |
The samples were collected between the dates of 2013-03-07 and 2013-11-20 |
Environmental Conditions: |
|
QAPP Information: |
Quality Assurance Program Plan and Standard Operating Procedures for SWAMP program |
QAPP Information Reference(s): |
Quality Assurance Program Plans, Quality Assurance Project Plans, and Standard Operating Procedures for the SWAMP program |
|
Line of Evidence (LOE) for Decision ID 168837, Molinate
|
Region 1 |
Klamath River HU, Shasta River HA |
|
|
LOE ID: |
350134 |
|
Pollutant: |
Molinate |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Total |
|
Beneficial Use: |
Cold Freshwater Habitat |
|
Number of Samples: |
3 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed RWB1 Trend Maintenance Periods FYs 2007 2008 data for Klamath River HU, Shasta River HA to determine beneficial use support and results are as follows: 0 of 3 samples exceeded the water quality threshold for Molinate. |
Data Reference: |
RWB1 Trend Maintenance Periods FYs 2007 2008 |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
All waters shall be maintained free of toxic substances in concentrations which are toxic to, or which produce detrimental physiological responses in, human, plant, animal, or aquatic life. (Basin Plan). |
Objective/Criterion Reference: |
Water Quality Control Plan (Basin Plan) for the North Coast Region |
|
Evaluation Guideline: |
The evaluation guideline for molinate is the USEPA Aquatic Life Benchmark of 105 ug/L for a fish (acute). |
Guideline Reference: |
OPP Aquatic Life Benchmarks |
|
Spatial Representation: |
The samples were collected at 1 monitoring site: 105SHA263 (Shasta River at Hwy 263). |
Temporal Representation: |
The samples were collected between the dates of 2007-11-15 and 2008-07-16 |
Environmental Conditions: |
|
QAPP Information: |
Generic SWAMP QAPrP |
QAPP Information Reference(s): |
Generic SWAMP QAPrP |
|
Line of Evidence (LOE) for Decision ID 168837, Molinate
|
Region 1 |
Klamath River HU, Shasta River HA |
|
|
LOE ID: |
350118 |
|
Pollutant: |
Molinate |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Total |
|
Beneficial Use: |
Warm Freshwater Habitat |
|
Number of Samples: |
3 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed RWB1 Trend Maintenance Periods FYs 2007 2008 data for Klamath River HU, Shasta River HA to determine beneficial use support and results are as follows: 0 of 3 samples exceeded the water quality threshold for Molinate. |
Data Reference: |
RWB1 Trend Maintenance Periods FYs 2007 2008 |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
All waters shall be maintained free of toxic substances in concentrations which are toxic to, or which produce detrimental physiological responses in, human, plant, animal, or aquatic life. (Basin Plan). |
Objective/Criterion Reference: |
Water Quality Control Plan (Basin Plan) for the North Coast Region |
|
Evaluation Guideline: |
The evaluation guideline for molinate is the USEPA Aquatic Life Benchmark of 105 ug/L for a fish (acute). |
Guideline Reference: |
OPP Aquatic Life Benchmarks |
|
Spatial Representation: |
The samples were collected at 1 monitoring site: 105SHAEDG (Shasta River near Edgewood). |
Temporal Representation: |
The samples were collected between the dates of 2007-11-15 and 2008-07-16 |
Environmental Conditions: |
|
QAPP Information: |
Generic SWAMP QAPrP |
QAPP Information Reference(s): |
Generic SWAMP QAPrP |
|
Line of Evidence (LOE) for Decision ID 168837, Molinate
|
Region 1 |
Klamath River HU, Shasta River HA |
|
|
LOE ID: |
123398 |
|
Pollutant: |
Molinate |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
None |
|
Beneficial Use: |
Municipal & Domestic Supply |
|
Number of Samples: |
0 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
State Water Board staff re-assessed SWAMP data for Klamath River HU, Shasta River HA to determine beneficial use support and results are as follows: 0 of 0 samples exceed the criterion for Molinate, Total. Four sample results were not used in the assessment because the laboratory data reporting limit(s) was above the objective and therefore the results could not be quantified with the level of certainty required by the Listing Policy. This LOE re-assesses data from LOE 29849 from the 2010 Integrated Report. Data were re-assessed in order to evaluate these data in their own LOE, instead of being evaluated in the same LOE as other pesticide data. |
Data Reference: |
Surface Water Ambient Monitoring Program (SWAMP). Summary Report for the North Coast Region (RWQCB-1) for years 2000-2006. North Coast Regional Water Quality Control Board. March 2008 |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
Water Quality Control Plan, North Coast Region (NCRWQCB 2011): Waters designated for use as domestic or municipal supply (MUN) shall not contain concentrations of chemical constituents in excess of the limits specified in California Code of Regulations, Title 22, Chapter 15. The maximum contaminant level listed in Table 64444-A for molinate is 0.02 mg/L |
Objective/Criterion Reference: |
Water Quality Control Plan (Basin Plan) for the North Coast Region |
Objective/Criterion Reference: |
Maximum Contaminant Levels for organic and inorganic chemicals. CCR Title 22 |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
Data for this line of evidence for Klamath River HU, Shasta River HA was collected at 1 monitoring site [ Yreka Creek at Highway 3 - 105YREHW3] |
Temporal Representation: |
Data was collected over the time period 10/21/2004-6/20/2005. |
Environmental Conditions: |
There are no known environmental conditions (e.g., seasonality, land use practices, fire events, storms, etc.) that are related to these data. |
QAPP Information: |
Quality control was conducted in accordance with the SWAMP Quality Assurance Management Plan (SWAMP 2002). |
QAPP Information Reference(s): |
Quality Assurance Management Plan for the State of California's Surface Water Ambient Monitoring Program. Sacramento, CA. State Water Resources Control Board. SWAMP. December 2002 (1st version)
|
|
Line of Evidence (LOE) for Decision ID 168837, Molinate
|
Region 1 |
Klamath River HU, Shasta River HA |
|
|
LOE ID: |
103332 |
|
Pollutant: |
Molinate |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Total |
|
Beneficial Use: |
Municipal & Domestic Supply |
|
Number of Samples: |
3 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP RWB1 Monitoring data for Klamath River HU, Shasta River HA to determine beneficial use support and results are as follows: 0 of 3 samples exceeded the water quality standard for Molinate. |
Data Reference: |
Water Quality Assessment Data for the 2018 solicitation cycle submitted through CEDEN for SWAMP RWB1 Monitoring .
|
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
Water Quality Control Plan, North Coast Region (NCRWQCB 2018): Waters designated for use as domestic or municipal supply (MUN) shall not contain concentrations of chemical constituents in excess of the limits specified in California Code of Regulations, Title 22, Chapter 15. The maximum contaminant level listed in Table 64444-A for molinate is 0.02 mg/L. |
Objective/Criterion Reference: |
Water Quality Control Plan (Basin Plan) for the North Coast Region |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
The samples were collected at 1 monitoring site(s) (105SH9274) |
Temporal Representation: |
The samples were collected between the dates of 2013-03-07 and 2013-11-20 |
Environmental Conditions: |
|
QAPP Information: |
Quality Assurance Program Plan and Standard Operating Procedures for SWAMP program |
QAPP Information Reference(s): |
Quality Assurance Program Plans, Quality Assurance Project Plans, and Standard Operating Procedures for the SWAMP program |
|
Line of Evidence (LOE) for Decision ID 168837, Molinate
|
Region 1 |
Klamath River HU, Shasta River HA |
|
|
LOE ID: |
123396 |
|
Pollutant: |
Molinate |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
None |
|
Beneficial Use: |
Municipal & Domestic Supply |
|
Number of Samples: |
0 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
State Water Board staff re-assessed SWAMP data for Klamath River HU, Shasta River HA to determine beneficial use support and results are as follows: 0 of 0 samples exceed the criterion for Molinate, Total. Four sample results were not used in the assessment because the laboratory data reporting limit(s) was above the objective and therefore the results could not be quantified with the level of certainty required by the Listing Policy. This LOE re-assesses data from LOE 29849 from the 2010 Integrated Report. Data were re-assessed in order to evaluate these data in their own LOE, instead of being evaluated in the same LOE as other pesticide data. |
Data Reference: |
Surface Water Ambient Monitoring Program (SWAMP). Summary Report for the North Coast Region (RWQCB-1) for years 2000-2006. North Coast Regional Water Quality Control Board. March 2008 |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
Water Quality Control Plan, North Coast Region (NCRWQCB 2011): Waters designated for use as domestic or municipal supply (MUN) shall not contain concentrations of chemical constituents in excess of the limits specified in California Code of Regulations, Title 22, Chapter 15. The maximum contaminant level listed in Table 64444-A for molinate is 0.02 mg/L |
Objective/Criterion Reference: |
Water Quality Control Plan (Basin Plan) for the North Coast Region |
Objective/Criterion Reference: |
Maximum Contaminant Levels for organic and inorganic chemicals. CCR Title 22 |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
Data for this line of evidence for Klamath River HU, Shasta River HA was collected at 1 monitoring site [ Shasta River near Edgewood - 105SH9274] |
Temporal Representation: |
Data was collected over the time period 10/7/2002-6/19/2003. |
Environmental Conditions: |
There are no known environmental conditions (e.g., seasonality, land use practices, fire events, storms, etc.) that are related to these data. |
QAPP Information: |
Quality control was conducted in accordance with the SWAMP Quality Assurance Management Plan (SWAMP 2002). |
QAPP Information Reference(s): |
Quality Assurance Management Plan for the State of California's Surface Water Ambient Monitoring Program. Sacramento, CA. State Water Resources Control Board. SWAMP. December 2002 (1st version)
|
|
Line of Evidence (LOE) for Decision ID 168837, Molinate
|
Region 1 |
Klamath River HU, Shasta River HA |
|
|
LOE ID: |
123389 |
|
Pollutant: |
Molinate |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
None |
|
Beneficial Use: |
Municipal & Domestic Supply |
|
Number of Samples: |
0 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
State Water Board staff re-assessed SWAMP data for Klamath River HU, Shasta River HA to determine beneficial use support and results are as follows: 0 of 0 samples exceed the criterion for Molinate, Total. Four sample results were not used in the assessment because the laboratory data reporting limit(s) was above the objective and therefore the results could not be quantified with the level of certainty required by the Listing Policy. This LOE re-assesses data from LOE 29849 from the 2010 Integrated Report. Data were re-assessed in order to evaluate these data in their own LOE, instead of being evaluated in the same LOE as other pesticide data. |
Data Reference: |
Surface Water Ambient Monitoring Program (SWAMP). Summary Report for the North Coast Region (RWQCB-1) for years 2000-2006. North Coast Regional Water Quality Control Board. March 2008 |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
Water Quality Control Plan, North Coast Region (NCRWQCB 2011): Waters designated for use as domestic or municipal supply (MUN) shall not contain concentrations of chemical constituents in excess of the limits specified in California Code of Regulations, Title 22, Chapter 15. The maximum contaminant level listed in Table 64444-A for molinate is 0.02 mg/L |
Objective/Criterion Reference: |
Water Quality Control Plan (Basin Plan) for the North Coast Region |
Objective/Criterion Reference: |
Maximum Contaminant Levels for organic and inorganic chemicals. CCR Title 22 |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
Data for this line of evidence for Klamath River HU, Shasta River HA was collected at 1 monitoring site [ Shasta River at Montague - 105SHAMON] |
Temporal Representation: |
Data was collected over the time period 10/7/2002-6/19/2003. |
Environmental Conditions: |
There are no known environmental conditions (e.g., seasonality, land use practices, fire events, storms, etc.) that are related to these data. |
QAPP Information: |
Quality control was conducted in accordance with the SWAMP Quality Assurance Management Plan (SWAMP 2002). |
QAPP Information Reference(s): |
Quality Assurance Management Plan for the State of California's Surface Water Ambient Monitoring Program. Sacramento, CA. State Water Resources Control Board. SWAMP. December 2002 (1st version)
|
|
Line of Evidence (LOE) for Decision ID 168837, Molinate
|
Region 1 |
Klamath River HU, Shasta River HA |
|
|
LOE ID: |
103328 |
|
Pollutant: |
Molinate |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Total |
|
Beneficial Use: |
Cold Freshwater Habitat |
|
Number of Samples: |
3 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP RWB1 Monitoring data for Klamath River HU, Shasta River HA to determine beneficial use support and results are as follows: 0 of 3 samples exceeded the water quality standard for Molinate. |
Data Reference: |
Water Quality Assessment Data for the 2018 solicitation cycle submitted through CEDEN for SWAMP RWB1 Monitoring .
|
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
All waters shall be maintained free of toxic substances in concentrations which are toxic to, or which produce detrimental physiological responses in, human, plant, animal, or aquatic life. (Basin Plan). |
Objective/Criterion Reference: |
Water Quality Control Plan (Basin Plan) for the North Coast Region |
|
Evaluation Guideline: |
The evaluation guideline for Molinate is the USEPA Aquatic Life Benchmark of 105 ug/L for a fish (acute). |
Guideline Reference: |
OPP Aquatic Life Benchmarks |
|
Spatial Representation: |
The samples were collected at 1 monitoring site(s) (105SH1452) |
Temporal Representation: |
The samples were collected between the dates of 2013-03-06 and 2013-11-20 |
Environmental Conditions: |
|
QAPP Information: |
Quality Assurance Program Plan and Standard Operating Procedures for SWAMP program |
QAPP Information Reference(s): |
Quality Assurance Program Plans, Quality Assurance Project Plans, and Standard Operating Procedures for the SWAMP program |
|
Line of Evidence (LOE) for Decision ID 168837, Molinate
|
Region 1 |
Klamath River HU, Shasta River HA |
|
|
LOE ID: |
103334 |
|
Pollutant: |
Molinate |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Total |
|
Beneficial Use: |
Warm Freshwater Habitat |
|
Number of Samples: |
3 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP RWB1 Monitoring data for Klamath River HU, Shasta River HA to determine beneficial use support and results are as follows: 0 of 3 samples exceeded the water quality standard for Molinate. |
Data Reference: |
Water Quality Assessment Data for the 2018 solicitation cycle submitted through CEDEN for SWAMP RWB1 Monitoring .
|
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
All waters shall be maintained free of toxic substances in concentrations which are toxic to, or which produce detrimental physiological responses in, human, plant, animal, or aquatic life. (Basin Plan). |
Objective/Criterion Reference: |
Water Quality Control Plan (Basin Plan) for the North Coast Region |
|
Evaluation Guideline: |
The evaluation guideline for Molinate is the USEPA Aquatic Life Benchmark of 105 ug/L for a fish (acute). |
Guideline Reference: |
OPP Aquatic Life Benchmarks |
|
Spatial Representation: |
The samples were collected at 1 monitoring site(s) (105SH9274) |
Temporal Representation: |
The samples were collected between the dates of 2013-03-07 and 2013-11-20 |
Environmental Conditions: |
|
QAPP Information: |
Quality Assurance Program Plan and Standard Operating Procedures for SWAMP program |
QAPP Information Reference(s): |
Quality Assurance Program Plans, Quality Assurance Project Plans, and Standard Operating Procedures for the SWAMP program |
|
Line of Evidence (LOE) for Decision ID 168837, Molinate
|
Region 1 |
Klamath River HU, Shasta River HA |
|
|
LOE ID: |
123388 |
|
Pollutant: |
Molinate |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
None |
|
Beneficial Use: |
Municipal & Domestic Supply |
|
Number of Samples: |
0 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
State Water Board staff re-assessed SWAMP data for Klamath River HU, Shasta River HA to determine beneficial use support and results are as follows: 0 of 0 samples exceed the criterion for Molinate, Total. Sixteen sample results were not used in the assessment because the laboratory data reporting limit(s) was above the objective and therefore the results could not be quantified with the level of certainty required by the Listing Policy. This LOE re-assesses data from LOE 29849 from the 2010 Integrated Report. Data were re-assessed in order to evaluate these data in their own LOE, instead of being evaluated in the same LOE as other pesticide data. |
Data Reference: |
Surface Water Ambient Monitoring Program (SWAMP). Summary Report for the North Coast Region (RWQCB-1) for years 2000-2006. North Coast Regional Water Quality Control Board. March 2008 |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
Water Quality Control Plan, North Coast Region (NCRWQCB 2011): Waters designated for use as domestic or municipal supply (MUN) shall not contain concentrations of chemical constituents in excess of the limits specified in California Code of Regulations, Title 22, Chapter 15. The maximum contaminant level listed in Table 64444-A for molinate is 0.02 mg/L |
Objective/Criterion Reference: |
Water Quality Control Plan (Basin Plan) for the North Coast Region |
Objective/Criterion Reference: |
Maximum Contaminant Levels for organic and inorganic chemicals. CCR Title 22 |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
Data for this line of evidence for Klamath River HU, Shasta River HA was collected at 1 monitoring site [ Shasta River at Hwy 263 - 105SH1452] |
Temporal Representation: |
Data was collected over the time period 2/27/2002-11/16/2006. |
Environmental Conditions: |
There are no known environmental conditions (e.g., seasonality, land use practices, fire events, storms, etc.) that are related to these data. |
QAPP Information: |
Quality control was conducted in accordance with the SWAMP Quality Assurance Management Plan (SWAMP 2002). |
QAPP Information Reference(s): |
Quality Assurance Management Plan for the State of California's Surface Water Ambient Monitoring Program. Sacramento, CA. State Water Resources Control Board. SWAMP. December 2002 (1st version)
|
|
Line of Evidence (LOE) for Decision ID 168837, Molinate
|
Region 1 |
Klamath River HU, Shasta River HA |
|
|
LOE ID: |
42542 |
|
Pollutant: |
Molinate |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Total |
|
Beneficial Use: |
Municipal & Domestic Supply |
|
Number of Samples: |
3 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP data for Klamath River HU, Shasta River HA to determine beneficial use support and results are as follows: 0 of 3 samples exceed the criterion for Molinate. |
Data Reference: |
RWB1 Trend Maintenance Periods FYs 2007 2008 |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
Water Quality Control Plan, North Coast Region (NCRWQCB 2011): Waters designated for use as domestic or municipal supply (MUN) shall not contain concentrations of chemical constituents in excess of the limits specified in California Code of Regulations, Title 22, Chapter 15. The maximum contaminant level listed in Table 64444-A for molinate is 0.02 mg/L. |
Objective/Criterion Reference: |
Maximum Contaminant Levels for organic and inorganic chemicals. CCR Title 22 |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
Data for this line of evidence for Klamath River HU, Shasta River HA was collected at 1 monitoring site [ Shasta River near Edgewood - 105SHAEDG] |
Temporal Representation: |
Data was collected over the time period 11/15/2007-7/16/2008. |
Environmental Conditions: |
Staff is not aware of any special conditions that might affect interpretation of the data. |
QAPP Information: |
The SWAMP QAPP (2008) was followed. |
QAPP Information Reference(s): |
Surface Water Ambient Monitoring Program Quality Assurance Program Plan |
|
Line of Evidence (LOE) for Decision ID 168837, Molinate
|
Region 1 |
Klamath River HU, Shasta River HA |
|
|
LOE ID: |
42543 |
|
Pollutant: |
Molinate |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Total |
|
Beneficial Use: |
Municipal & Domestic Supply |
|
Number of Samples: |
3 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP data for Klamath River HU, Shasta River HA to determine beneficial use support and results are as follows: 0 of 3 samples exceed the criterion for Molinate. |
Data Reference: |
RWB1 Trend Maintenance Periods FYs 2007 2008 |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
Water Quality Control Plan, North Coast Region (NCRWQCB 2011): Waters designated for use as domestic or municipal supply (MUN) shall not contain concentrations of chemical constituents in excess of the limits specified in California Code of Regulations, Title 22, Chapter 15. The maximum contaminant level listed in Table 64444-A for molinate is 0.02 mg/L. |
Objective/Criterion Reference: |
Maximum Contaminant Levels for organic and inorganic chemicals. CCR Title 22 |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
Data for this line of evidence for Klamath River HU, Shasta River HA was collected at 1 monitoring site [ Shasta River at Hwy 263 - 105SHA263] |
Temporal Representation: |
Data was collected over the time period 11/15/2007-7/16/2008. |
Environmental Conditions: |
Staff is not aware of any special conditions that might affect interpretation of the data. |
QAPP Information: |
The SWAMP QAPP (2008) was followed. |
QAPP Information Reference(s): |
Surface Water Ambient Monitoring Program Quality Assurance Program Plan |
|
Line of Evidence (LOE) for Decision ID 168837, Molinate
|
Region 1 |
Klamath River HU, Shasta River HA |
|
|
LOE ID: |
103329 |
|
Pollutant: |
Molinate |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Total |
|
Beneficial Use: |
Municipal & Domestic Supply |
|
Number of Samples: |
3 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP RWB1 Monitoring data for Klamath River HU, Shasta River HA to determine beneficial use support and results are as follows: 0 of 3 samples exceeded the water quality standard for Molinate. |
Data Reference: |
Water Quality Assessment Data for the 2018 solicitation cycle submitted through CEDEN for SWAMP RWB1 Monitoring .
|
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
Water Quality Control Plan, North Coast Region (NCRWQCB 2018): Waters designated for use as domestic or municipal supply (MUN) shall not contain concentrations of chemical constituents in excess of the limits specified in California Code of Regulations, Title 22, Chapter 15. The maximum contaminant level listed in Table 64444-A for molinate is 0.02 mg/L. |
Objective/Criterion Reference: |
Water Quality Control Plan (Basin Plan) for the North Coast Region |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
The samples were collected at 1 monitoring site(s) (105SH1452) |
Temporal Representation: |
The samples were collected between the dates of 2013-03-06 and 2013-11-20 |
Environmental Conditions: |
|
QAPP Information: |
Quality Assurance Program Plan and Standard Operating Procedures for SWAMP program |
QAPP Information Reference(s): |
Quality Assurance Program Plans, Quality Assurance Project Plans, and Standard Operating Procedures for the SWAMP program |
|
Line of Evidence (LOE) for Decision ID 168837, Molinate
|
Region 1 |
Klamath River HU, Shasta River HA |
|
|
LOE ID: |
103330 |
|
Pollutant: |
Molinate |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Total |
|
Beneficial Use: |
Warm Freshwater Habitat |
|
Number of Samples: |
3 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP RWB1 Monitoring data for Klamath River HU, Shasta River HA to determine beneficial use support and results are as follows: 0 of 3 samples exceeded the water quality standard for Molinate. |
Data Reference: |
Water Quality Assessment Data for the 2018 solicitation cycle submitted through CEDEN for SWAMP RWB1 Monitoring .
|
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
All waters shall be maintained free of toxic substances in concentrations which are toxic to, or which produce detrimental physiological responses in, human, plant, animal, or aquatic life. (Basin Plan). |
Objective/Criterion Reference: |
Water Quality Control Plan (Basin Plan) for the North Coast Region |
|
Evaluation Guideline: |
The evaluation guideline for Molinate is the USEPA Aquatic Life Benchmark of 105 ug/L for a fish (acute). |
Guideline Reference: |
OPP Aquatic Life Benchmarks |
|
Spatial Representation: |
The samples were collected at 1 monitoring site(s) (105SH1452) |
Temporal Representation: |
The samples were collected between the dates of 2013-03-06 and 2013-11-20 |
Environmental Conditions: |
|
QAPP Information: |
Quality Assurance Program Plan and Standard Operating Procedures for SWAMP program |
QAPP Information Reference(s): |
Quality Assurance Program Plans, Quality Assurance Project Plans, and Standard Operating Procedures for the SWAMP program |
|
Line of Evidence (LOE) for Decision ID 168837, Molinate
|
Region 1 |
Klamath River HU, Shasta River HA |
|
|
LOE ID: |
123397 |
|
Pollutant: |
Molinate |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
None |
|
Beneficial Use: |
Municipal & Domestic Supply |
|
Number of Samples: |
0 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
State Water Board staff re-assessed SWAMP data for Klamath River HU, Shasta River HA to determine beneficial use support and results are as follows: 0 of 0 samples exceed the criterion for Molinate, Total. Eight sample results were not used in the assessment because the laboratory data reporting limit(s) was above the objective and therefore the results could not be quantified with the level of certainty required by the Listing Policy. This LOE re-assesses data from LOE 29849 from the 2010 Integrated Report. Data were re-assessed in order to evaluate these data in their own LOE, instead of being evaluated in the same LOE as other pesticide data. |
Data Reference: |
Surface Water Ambient Monitoring Program (SWAMP). Summary Report for the North Coast Region (RWQCB-1) for years 2000-2006. North Coast Regional Water Quality Control Board. March 2008 |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
Water Quality Control Plan, North Coast Region (NCRWQCB 2011): Waters designated for use as domestic or municipal supply (MUN) shall not contain concentrations of chemical constituents in excess of the limits specified in California Code of Regulations, Title 22, Chapter 15. The maximum contaminant level listed in Table 64444-A for molinate is 0.02 mg/L |
Objective/Criterion Reference: |
Water Quality Control Plan (Basin Plan) for the North Coast Region |
Objective/Criterion Reference: |
Maximum Contaminant Levels for organic and inorganic chemicals. CCR Title 22 |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
Data for this line of evidence for Klamath River HU, Shasta River HA was collected at 1 monitoring site [ Yreka Creek at Anderson Rd - 105YREAND] |
Temporal Representation: |
Data was collected over the time period 10/9/2002-6/20/2005. |
Environmental Conditions: |
There are no known environmental conditions (e.g., seasonality, land use practices, fire events, storms, etc.) that are related to these data. |
QAPP Information: |
Quality control was conducted in accordance with the SWAMP Quality Assurance Management Plan (SWAMP 2002). |
QAPP Information Reference(s): |
Quality Assurance Management Plan for the State of California's Surface Water Ambient Monitoring Program. Sacramento, CA. State Water Resources Control Board. SWAMP. December 2002 (1st version)
|
|
Line of Evidence (LOE) for Decision ID 168837, Molinate
|
Region 1 |
Klamath River HU, Shasta River HA |
|
|
LOE ID: |
350131 |
|
Pollutant: |
Molinate |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Total |
|
Beneficial Use: |
Cold Freshwater Habitat |
|
Number of Samples: |
3 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed RWB1 Trend Maintenance Periods FYs 2007 2008 data for Klamath River HU, Shasta River HA to determine beneficial use support and results are as follows: 0 of 3 samples exceeded the water quality threshold for Molinate. |
Data Reference: |
RWB1 Trend Maintenance Periods FYs 2007 2008 |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
All waters shall be maintained free of toxic substances in concentrations which are toxic to, or which produce detrimental physiological responses in, human, plant, animal, or aquatic life. (Basin Plan). |
Objective/Criterion Reference: |
Water Quality Control Plan (Basin Plan) for the North Coast Region |
|
Evaluation Guideline: |
The evaluation guideline for molinate is the USEPA Aquatic Life Benchmark of 105 ug/L for a fish (acute). |
Guideline Reference: |
OPP Aquatic Life Benchmarks |
|
Spatial Representation: |
The samples were collected at 1 monitoring site: 105SHAEDG (Shasta River near Edgewood). |
Temporal Representation: |
The samples were collected between the dates of 2007-11-15 and 2008-07-16 |
Environmental Conditions: |
|
QAPP Information: |
Generic SWAMP QAPrP |
QAPP Information Reference(s): |
Generic SWAMP QAPrP |
|
Line of Evidence (LOE) for Decision ID 101109, Nickel
|
Region 1 |
Klamath River HU, Shasta River HA |
|
|
LOE ID: |
103338 |
|
Pollutant: |
Nickel |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Dissolved |
|
Beneficial Use: |
Warm Freshwater Habitat |
|
Number of Samples: |
5 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP RWB1 Monitoring data for Klamath River HU, Shasta River HA to determine beneficial use support and results are as follows: 0 of 5 samples exceeded the water quality standard for Nickel. |
Data Reference: |
Water Quality Assessment Data for the 2018 solicitation cycle submitted through CEDEN for SWAMP RWB1 Monitoring .
|
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
California Toxics Rule (CTR) lists criterion continuous concentrations to protect aquatic life in freshwater. The criterion in freshwater is hardness dependent for each sample and varies based on the ambient hardness during sampling. Section (b)(1) in CTR contains the hardness dependent formula for the metals criterion. |
Objective/Criterion Reference: |
Water Quality Standards 2000. Establishment of numeric criteria for priority toxic pollutants for the State of California: Rules and regulations. Federal Register Vol. 65, No. 97. Washington, D.C.: Environmental Protection Agency |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
The samples were collected at 1 monitoring site(s) (105SH9274) |
Temporal Representation: |
The samples were collected between the dates of 2013-03-07 and 2013-11-20 |
Environmental Conditions: |
|
QAPP Information: |
Quality Assurance Program Plan and Standard Operating Procedures for SWAMP program |
QAPP Information Reference(s): |
Quality Assurance Program Plans, Quality Assurance Project Plans, and Standard Operating Procedures for the SWAMP program |
|
Line of Evidence (LOE) for Decision ID 101109, Nickel
|
Region 1 |
Klamath River HU, Shasta River HA |
|
|
LOE ID: |
43132 |
|
Pollutant: |
Nickel |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Total |
|
Beneficial Use: |
Municipal & Domestic Supply |
|
Number of Samples: |
4 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP data for Klamath River HU, Shasta River HA to determine beneficial use support and results are as follows: 0 of 4 samples exceed the criterion for Nickel. |
Data Reference: |
RWB1 Trend Maintenance Periods FYs 2007 2008 |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
Water Quality Control Plan, North Coast Region (NCRWQCB 2011): Waters designated for use as domestic or municipal supply (MUN) shall not contain concentrations of chemical constituents in excess of the limits specified in California Code of Regulations, Title 22, Chapter 15. The maximum contaminant level listed in Table 64431-A for nickel is 0.1 mg/L. |
Objective/Criterion Reference: |
Maximum Contaminant Levels for organic and inorganic chemicals. CCR Title 22 |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
Data for this line of evidence for Klamath River HU, Shasta River HA was collected at 1 monitoring site [ Shasta River near Edgewood - 105SHAEDG] |
Temporal Representation: |
Data was collected over the time period 11/15/2007-7/16/2008. |
Environmental Conditions: |
Staff is not aware of any special conditions that might affect interpretation of the data. |
QAPP Information: |
The SWAMP QAPP (2008) was followed. |
QAPP Information Reference(s): |
Surface Water Ambient Monitoring Program Quality Assurance Program Plan |
|
Line of Evidence (LOE) for Decision ID 101109, Nickel
|
Region 1 |
Klamath River HU, Shasta River HA |
|
|
LOE ID: |
123421 |
|
Pollutant: |
Nickel |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Total |
|
Beneficial Use: |
Municipal & Domestic Supply |
|
Number of Samples: |
5 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
State Water Board staff re-assessed SWAMP data for Klamath River HU, Shasta River HA to determine beneficial use support and results are as follows: 0 of 5 samples exceed the criterion for Nickel, Total. This LOE re-assesses data from LOE 21509 from the 2010 Integrated Report. Data were re-assessed in order to evaluate these data in their own LOE, instead of being evaluated in the same LOE as other metals data. |
Data Reference: |
Surface Water Ambient Monitoring Program (SWAMP). Summary Report for the North Coast Region (RWQCB-1) for years 2000-2006. North Coast Regional Water Quality Control Board. March 2008 |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
Water Quality Control Plan, North Coast Region (NCRWQCB 2011): Waters designated for use as domestic or municipal supply (MUN) shall not contain concentrations of chemical constituents in excess of the limits specified in California Code of Regulations, Title 22, Chapter 15. The maximum contaminant level listed in Table 64431-A for nickel is 0.1 mg/L. |
Objective/Criterion Reference: |
Water Quality Control Plan (Basin Plan) for the North Coast Region |
Objective/Criterion Reference: |
Maximum Contaminant Levels for organic and inorganic chemicals. CCR Title 22 |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
Data for this line of evidence for Klamath River HU, Shasta River HA was collected at 1 monitoring site [ Shasta River at Montague - 105SHAMON] |
Temporal Representation: |
Data was collected over the time period 10/7/2002-6/19/2003. |
Environmental Conditions: |
There are no known environmental conditions (e.g., seasonality, land use practices, fire events, storms, etc.) that are related to these data. |
QAPP Information: |
Quality control was conducted in accordance with the SWAMP Quality Assurance Management Plan (SWAMP 2002). |
QAPP Information Reference(s): |
Quality Assurance Management Plan for the State of California's Surface Water Ambient Monitoring Program. Sacramento, CA. State Water Resources Control Board. SWAMP. December 2002 (1st version)
|
|
Line of Evidence (LOE) for Decision ID 101109, Nickel
|
Region 1 |
Klamath River HU, Shasta River HA |
|
|
LOE ID: |
42797 |
|
Pollutant: |
Nickel |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Total |
|
Beneficial Use: |
Municipal & Domestic Supply |
|
Number of Samples: |
4 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP data for Klamath River HU, Shasta River HA to determine beneficial use support and results are as follows: 0 of 4 samples exceed the criterion for Nickel. |
Data Reference: |
RWB1 Trend Maintenance Periods FYs 2007 2008 |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
Water Quality Control Plan, North Coast Region (NCRWQCB 2011): Waters designated for use as domestic or municipal supply (MUN) shall not contain concentrations of chemical constituents in excess of the limits specified in California Code of Regulations, Title 22, Chapter 15. The maximum contaminant level listed in Table 64431-A for nickel is 0.1 mg/L. |
Objective/Criterion Reference: |
Maximum Contaminant Levels for organic and inorganic chemicals. CCR Title 22 |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
Data for this line of evidence for Klamath River HU, Shasta River HA was collected at 1 monitoring site [ Shasta River at Hwy 263 - 105SHA263] |
Temporal Representation: |
Data was collected over the time period 11/15/2007-7/16/2008. |
Environmental Conditions: |
Staff is not aware of any special conditions that might affect interpretation of the data. |
QAPP Information: |
The SWAMP QAPP (2008) was followed. |
QAPP Information Reference(s): |
Surface Water Ambient Monitoring Program Quality Assurance Program Plan |
|
Line of Evidence (LOE) for Decision ID 101109, Nickel
|
Region 1 |
Klamath River HU, Shasta River HA |
|
|
LOE ID: |
103340 |
|
Pollutant: |
Nickel |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Total |
|
Beneficial Use: |
Municipal & Domestic Supply |
|
Number of Samples: |
5 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP RWB1 Monitoring data for Klamath River HU, Shasta River HA to determine beneficial use support and results are as follows: 0 of 5 samples exceeded the water quality standard for Nickel. |
Data Reference: |
Water Quality Assessment Data for the 2018 solicitation cycle submitted through CEDEN for SWAMP RWB1 Monitoring .
|
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
Water Quality Control Plan, North Coast Region (NCRWQCB 2018): Waters designated for use as domestic or municipal supply (MUN) shall not contain concentrations of chemical constituents in excess of the limits specified in California Code of Regulations, Title 22, Chapter 15. The maximum contaminant level listed in Table 64431-A for nickel is 0.1 mg/L. |
Objective/Criterion Reference: |
Water Quality Control Plan (Basin Plan) for the North Coast Region |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
The samples were collected at 1 monitoring site(s) (105SH1452) |
Temporal Representation: |
The samples were collected between the dates of 2013-03-06 and 2013-11-20 |
Environmental Conditions: |
|
QAPP Information: |
Quality Assurance Program Plan and Standard Operating Procedures for SWAMP program |
QAPP Information Reference(s): |
Quality Assurance Program Plans, Quality Assurance Project Plans, and Standard Operating Procedures for the SWAMP program |
|
Line of Evidence (LOE) for Decision ID 101109, Nickel
|
Region 1 |
Klamath River HU, Shasta River HA |
|
|
LOE ID: |
123433 |
|
Pollutant: |
Nickel |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Total |
|
Beneficial Use: |
Municipal & Domestic Supply |
|
Number of Samples: |
7 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
State Water Board staff re-assessed SWAMP data for Klamath River HU, Shasta River HA to determine beneficial use support and results are as follows: 0 of 7 samples exceed the criterion for Nickel, Total. This LOE re-assesses data from LOE 21509 from the 2010 Integrated Report. Data were re-assessed in order to evaluate these data in their own LOE, instead of being evaluated in the same LOE as other metals data. |
Data Reference: |
Surface Water Ambient Monitoring Program (SWAMP). Summary Report for the North Coast Region (RWQCB-1) for years 2000-2006. North Coast Regional Water Quality Control Board. March 2008 |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
Water Quality Control Plan, North Coast Region (NCRWQCB 2011): Waters designated for use as domestic or municipal supply (MUN) shall not contain concentrations of chemical constituents in excess of the limits specified in California Code of Regulations, Title 22, Chapter 15. The maximum contaminant level listed in Table 64431-A for nickel is 0.1 mg/L. |
Objective/Criterion Reference: |
Water Quality Control Plan (Basin Plan) for the North Coast Region |
Objective/Criterion Reference: |
Maximum Contaminant Levels for organic and inorganic chemicals. CCR Title 22 |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
Data for this line of evidence for Klamath River HU, Shasta River HA was collected at 1 monitoring site [ Yreka Creek at Anderson Rd - 105YREAND] |
Temporal Representation: |
Data was collected over the time period 10/9/2002-6/20/2005. |
Environmental Conditions: |
There are no known environmental conditions (e.g., seasonality, land use practices, fire events, storms, etc.) that are related to these data. |
QAPP Information: |
Quality control was conducted in accordance with the SWAMP Quality Assurance Management Plan (SWAMP 2002). |
QAPP Information Reference(s): |
Letter requesting acceptance of late submittal |
|
Line of Evidence (LOE) for Decision ID 101109, Nickel
|
Region 1 |
Klamath River HU, Shasta River HA |
|
|
LOE ID: |
123432 |
|
Pollutant: |
Nickel |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Total |
|
Beneficial Use: |
Municipal & Domestic Supply |
|
Number of Samples: |
5 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
State Water Board staff re-assessed SWAMP data for Klamath River HU, Shasta River HA to determine beneficial use support and results are as follows: 0 of 5 samples exceed the criterion for Nickel, Total. This LOE re-assesses data from LOE 21509 from the 2010 Integrated Report. Data were re-assessed in order to evaluate these data in their own LOE, instead of being evaluated in the same LOE as other metals data. |
Data Reference: |
Surface Water Ambient Monitoring Program (SWAMP). Summary Report for the North Coast Region (RWQCB-1) for years 2000-2006. North Coast Regional Water Quality Control Board. March 2008 |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
Water Quality Control Plan, North Coast Region (NCRWQCB 2011): Waters designated for use as domestic or municipal supply (MUN) shall not contain concentrations of chemical constituents in excess of the limits specified in California Code of Regulations, Title 22, Chapter 15. The maximum contaminant level listed in Table 64431-A for nickel is 0.1 mg/L. |
Objective/Criterion Reference: |
Water Quality Control Plan (Basin Plan) for the North Coast Region |
Objective/Criterion Reference: |
Maximum Contaminant Levels for organic and inorganic chemicals. CCR Title 22 |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
Data for this line of evidence for Klamath River HU, Shasta River HA was collected at 1 monitoring site [ Shasta River near Edgewood - 105SH9274] |
Temporal Representation: |
Data was collected over the time period 10/7/2002-6/19/2003. |
Environmental Conditions: |
There are no known environmental conditions (e.g., seasonality, land use practices, fire events, storms, etc.) that are related to these data. |
QAPP Information: |
Quality control was conducted in accordance with the SWAMP Quality Assurance Management Plan (SWAMP 2002). |
QAPP Information Reference(s): |
Letter requesting acceptance of late submittal |
|
Line of Evidence (LOE) for Decision ID 101109, Nickel
|
Region 1 |
Klamath River HU, Shasta River HA |
|
|
LOE ID: |
123434 |
|
Pollutant: |
Nickel |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Total |
|
Beneficial Use: |
Municipal & Domestic Supply |
|
Number of Samples: |
3 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
State Water Board staff re-assessed SWAMP data for Klamath River HU, Shasta River HA to determine beneficial use support and results are as follows: 0 of 3 samples exceed the criterion for Nickel, Total. This LOE re-assesses data from LOE 21509 from the 2010 Integrated Report. Data were re-assessed in order to evaluate these data in their own LOE, instead of being evaluated in the same LOE as other metals data. |
Data Reference: |
Surface Water Ambient Monitoring Program (SWAMP). Summary Report for the North Coast Region (RWQCB-1) for years 2000-2006. North Coast Regional Water Quality Control Board. March 2008 |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
Water Quality Control Plan, North Coast Region (NCRWQCB 2011): Waters designated for use as domestic or municipal supply (MUN) shall not contain concentrations of chemical constituents in excess of the limits specified in California Code of Regulations, Title 22, Chapter 15. The maximum contaminant level listed in Table 64431-A for nickel is 0.1 mg/L. |
Objective/Criterion Reference: |
Water Quality Control Plan (Basin Plan) for the North Coast Region |
Objective/Criterion Reference: |
Maximum Contaminant Levels for organic and inorganic chemicals. CCR Title 22 |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
Data for this line of evidence for Klamath River HU, Shasta River HA was collected at 1 monitoring site [ Yreka Creek at Highway 3 - 105YREHW3] |
Temporal Representation: |
Data was collected over the time period 10/21/2004-6/20/2005. |
Environmental Conditions: |
There are no known environmental conditions (e.g., seasonality, land use practices, fire events, storms, etc.) that are related to these data. |
QAPP Information: |
Quality control was conducted in accordance with the SWAMP Quality Assurance Management Plan (SWAMP 2002). |
QAPP Information Reference(s): |
Letter requesting acceptance of late submittal |
|
Line of Evidence (LOE) for Decision ID 101109, Nickel
|
Region 1 |
Klamath River HU, Shasta River HA |
|
|
LOE ID: |
103337 |
|
Pollutant: |
Nickel |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Dissolved |
|
Beneficial Use: |
Cold Freshwater Habitat |
|
Number of Samples: |
5 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP RWB1 Monitoring data for Klamath River HU, Shasta River HA to determine beneficial use support and results are as follows: 0 of 5 samples exceeded the water quality standard for Nickel. |
Data Reference: |
Water Quality Assessment Data for the 2018 solicitation cycle submitted through CEDEN for SWAMP RWB1 Monitoring .
|
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
California Toxics Rule (CTR) lists criterion continuous concentrations to protect aquatic life in freshwater. The criterion in freshwater is hardness dependent for each sample and varies based on the ambient hardness during sampling. Section (b)(1) in CTR contains the hardness dependent formula for the metals criterion. |
Objective/Criterion Reference: |
Water Quality Standards 2000. Establishment of numeric criteria for priority toxic pollutants for the State of California: Rules and regulations. Federal Register Vol. 65, No. 97. Washington, D.C.: Environmental Protection Agency |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
The samples were collected at 1 monitoring site(s) (105SH9274) |
Temporal Representation: |
The samples were collected between the dates of 2013-03-07 and 2013-11-20 |
Environmental Conditions: |
|
QAPP Information: |
Quality Assurance Program Plan and Standard Operating Procedures for SWAMP program |
QAPP Information Reference(s): |
Quality Assurance Program Plans, Quality Assurance Project Plans, and Standard Operating Procedures for the SWAMP program |
|
Line of Evidence (LOE) for Decision ID 101109, Nickel
|
Region 1 |
Klamath River HU, Shasta River HA |
|
|
LOE ID: |
103336 |
|
Pollutant: |
Nickel |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Dissolved |
|
Beneficial Use: |
Warm Freshwater Habitat |
|
Number of Samples: |
5 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP RWB1 Monitoring data for Klamath River HU, Shasta River HA to determine beneficial use support and results are as follows: 0 of 5 samples exceeded the water quality standard for Nickel. |
Data Reference: |
Water Quality Assessment Data for the 2018 solicitation cycle submitted through CEDEN for SWAMP RWB1 Monitoring .
|
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
California Toxics Rule (CTR) lists criterion continuous concentrations to protect aquatic life in freshwater. The criterion in freshwater is hardness dependent for each sample and varies based on the ambient hardness during sampling. Section (b)(1) in CTR contains the hardness dependent formula for the metals criterion. |
Objective/Criterion Reference: |
Water Quality Standards 2000. Establishment of numeric criteria for priority toxic pollutants for the State of California: Rules and regulations. Federal Register Vol. 65, No. 97. Washington, D.C.: Environmental Protection Agency |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
The samples were collected at 1 monitoring site(s) (105SH1452) |
Temporal Representation: |
The samples were collected between the dates of 2013-03-06 and 2013-11-20 |
Environmental Conditions: |
|
QAPP Information: |
Quality Assurance Program Plan and Standard Operating Procedures for SWAMP program |
QAPP Information Reference(s): |
Quality Assurance Program Plans, Quality Assurance Project Plans, and Standard Operating Procedures for the SWAMP program |
|
Line of Evidence (LOE) for Decision ID 101109, Nickel
|
Region 1 |
Klamath River HU, Shasta River HA |
|
|
LOE ID: |
103342 |
|
Pollutant: |
Nickel |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Total |
|
Beneficial Use: |
Municipal & Domestic Supply |
|
Number of Samples: |
5 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP RWB1 Monitoring data for Klamath River HU, Shasta River HA to determine beneficial use support and results are as follows: 0 of 5 samples exceeded the water quality standard for Nickel. |
Data Reference: |
Water Quality Assessment Data for the 2018 solicitation cycle submitted through CEDEN for SWAMP RWB1 Monitoring .
|
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
Water Quality Control Plan, North Coast Region (NCRWQCB 2018): Waters designated for use as domestic or municipal supply (MUN) shall not contain concentrations of chemical constituents in excess of the limits specified in California Code of Regulations, Title 22, Chapter 15. The maximum contaminant level listed in Table 64431-A for nickel is 0.1 mg/L. |
Objective/Criterion Reference: |
Water Quality Control Plan (Basin Plan) for the North Coast Region |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
The samples were collected at 1 monitoring site(s) (105SH9274) |
Temporal Representation: |
The samples were collected between the dates of 2013-03-07 and 2013-11-20 |
Environmental Conditions: |
|
QAPP Information: |
Quality Assurance Program Plan and Standard Operating Procedures for SWAMP program |
QAPP Information Reference(s): |
Quality Assurance Program Plans, Quality Assurance Project Plans, and Standard Operating Procedures for the SWAMP program |
|
Line of Evidence (LOE) for Decision ID 101109, Nickel
|
Region 1 |
Klamath River HU, Shasta River HA |
|
|
LOE ID: |
32978 |
|
Pollutant: |
Nickel |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Total |
|
Beneficial Use: |
Cold Freshwater Habitat |
|
Number of Samples: |
4 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
None of the 4 samples exceeded the hardness based criteria calculated for nickel. |
Data Reference: |
RWB1 Trend Maintenance Periods FYs 2007 2008 |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
Water Quality Control Plan, North Coast Region (NCRWQCB 2011): All waters shall be maintained free of toxic substances in concentrations that are toxic to, or that produce detrimental physiological responses in human, plant, animal, or aquatic life. California Toxics Rule (CTR) lists criterion continuous concentrations (4-day average) to protect aquatic life in freshwater. The criterion in freshwater is hardness dependent for each sample and varies based on the ambient hardness during sampling. Section (b)(1) in CTR contains the hardness dependent formula for the metals criterion. |
Objective/Criterion Reference: |
Code of Federal Regulations 40 part 131.38 Establishment of numeric criteria for priority toxic pollutants for the State of California. 7/1/2011 Edition |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
Samples collected at station 105SHA263 (Shasta River at Hwy 263). |
Temporal Representation: |
Samples collected between 11/15/2007 and 7/16/2008. |
Environmental Conditions: |
|
QAPP Information: |
SWAMP QAPP (2008) was followed. |
QAPP Information Reference(s): |
Surface Water Ambient Monitoring Program Quality Assurance Program Plan |
|
Line of Evidence (LOE) for Decision ID 101109, Nickel
|
Region 1 |
Klamath River HU, Shasta River HA |
|
|
LOE ID: |
32583 |
|
Pollutant: |
Nickel |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Total |
|
Beneficial Use: |
Cold Freshwater Habitat |
|
Number of Samples: |
4 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
None of the 4 samples exceeded the hardness based criteria calculated for nickel. |
Data Reference: |
RWB1 Trend Maintenance Periods FYs 2007 2008 |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
Water Quality Control Plan, North Coast Region (NCRWQCB 2011): All waters shall be maintained free of toxic substances in concentrations that are toxic to, or that produce detrimental physiological responses in human, plant, animal, or aquatic life. California Toxics Rule (CTR) lists criterion continuous concentrations (4-day average) to protect aquatic life in freshwater. The criterion in freshwater is hardness dependent for each sample and varies based on the ambient hardness during sampling. Section (b)(1) in CTR contains the hardness dependent formula for the metals criterion. |
Objective/Criterion Reference: |
Code of Federal Regulations 40 part 131.38 Establishment of numeric criteria for priority toxic pollutants for the State of California. 7/1/2011 Edition |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
Samples collected at station 105SHAEDG (Shasta River near Edgewood). |
Temporal Representation: |
Samples collected between 11/15/2007 and 7/16/2008. |
Environmental Conditions: |
|
QAPP Information: |
SWAMP QAPP (2008) was followed. |
QAPP Information Reference(s): |
Surface Water Ambient Monitoring Program Quality Assurance Program Plan |
|
Line of Evidence (LOE) for Decision ID 101109, Nickel
|
Region 1 |
Klamath River HU, Shasta River HA |
|
|
LOE ID: |
103339 |
|
Pollutant: |
Nickel |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Total |
|
Beneficial Use: |
Commercial or recreational collection of fish, shellfish, or organisms |
|
Number of Samples: |
5 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP RWB1 Monitoring data for Klamath River HU, Shasta River HA to determine beneficial use support and results are as follows: 0 of 5 samples exceeded the water quality standard for Nickel. |
Data Reference: |
Water Quality Assessment Data for the 2018 solicitation cycle submitted through CEDEN for SWAMP RWB1 Monitoring .
|
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
Water Quality Control Plan, North Coast Region (NCRWQCB 2018): All waters shall be maintained free of toxic substances in concentrations that are toxic to, or that produce detrimental physiological responses in human, plant, animal, or aquatic life. The established numeric criteria for Nickel to protect human health from consumption of organisms only is 4600 ug/L (California Toxics Rule, 2000). |
Objective/Criterion Reference: |
Water Quality Standards 2000. Establishment of numeric criteria for priority toxic pollutants for the State of California: Rules and regulations. Federal Register Vol. 65, No. 97. Washington, D.C.: Environmental Protection Agency |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
The samples were collected at 1 monitoring site(s) (105SH1452) |
Temporal Representation: |
The samples were collected between the dates of 2013-03-06 and 2013-11-20 |
Environmental Conditions: |
|
QAPP Information: |
Quality Assurance Program Plan and Standard Operating Procedures for SWAMP program |
QAPP Information Reference(s): |
Quality Assurance Program Plans, Quality Assurance Project Plans, and Standard Operating Procedures for the SWAMP program |
|
Line of Evidence (LOE) for Decision ID 101109, Nickel
|
Region 1 |
Klamath River HU, Shasta River HA |
|
|
LOE ID: |
43004 |
|
Pollutant: |
Nickel |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Total |
|
Beneficial Use: |
Commercial or recreational collection of fish, shellfish, or organisms |
|
Number of Samples: |
4 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP data for Klamath River HU, Shasta River HA to determine beneficial use support and results are as follows: 0 of 4 samples exceed the criterion for Nickel. |
Data Reference: |
RWB1 Trend Maintenance Periods FYs 2007 2008 |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
Water Quality Control Plan, North Coast Region (NCRWQCB 2011): All waters shall be maintained free of toxic substances in concentrations that are toxic to, or that produce detrimental physiological responses in human, plant, animal, or aquatic life. The established numeric criteria for Nickel to protect human health from consumption of organisms only is 4.6 mg/L (California Toxics Rule, 2000). |
Objective/Criterion Reference: |
Code of Federal Regulations 40 part 131.38 Establishment of numeric criteria for priority toxic pollutants for the State of California. 7/1/2011 Edition |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
Data for this line of evidence for Klamath River HU, Shasta River HA was collected at 1 monitoring site [ Shasta River at Hwy 263 - 105SHA263] |
Temporal Representation: |
Data was collected over the time period 11/15/2007-7/16/2008. |
Environmental Conditions: |
Staff is not aware of any special conditions that might affect interpretation of the data. |
QAPP Information: |
The SWAMP QAPP (2008) was followed. |
QAPP Information Reference(s): |
Surface Water Ambient Monitoring Program Quality Assurance Program Plan |
|
Line of Evidence (LOE) for Decision ID 101109, Nickel
|
Region 1 |
Klamath River HU, Shasta River HA |
|
|
LOE ID: |
42984 |
|
Pollutant: |
Nickel |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Total |
|
Beneficial Use: |
Commercial or recreational collection of fish, shellfish, or organisms |
|
Number of Samples: |
4 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP data for Klamath River HU, Shasta River HA to determine beneficial use support and results are as follows: 0 of 4 samples exceed the criterion for Nickel. |
Data Reference: |
RWB1 Trend Maintenance Periods FYs 2007 2008 |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
Water Quality Control Plan, North Coast Region (NCRWQCB 2011): All waters shall be maintained free of toxic substances in concentrations that are toxic to, or that produce detrimental physiological responses in human, plant, animal, or aquatic life. The established numeric criteria for Nickel to protect human health from consumption of organisms only is 4.6 mg/L (California Toxics Rule, 2000). |
Objective/Criterion Reference: |
Code of Federal Regulations 40 part 131.38 Establishment of numeric criteria for priority toxic pollutants for the State of California. 7/1/2011 Edition |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
Data for this line of evidence for Klamath River HU, Shasta River HA was collected at 1 monitoring site [ Shasta River near Edgewood - 105SHAEDG] |
Temporal Representation: |
Data was collected over the time period 11/15/2007-7/16/2008. |
Environmental Conditions: |
Staff is not aware of any special conditions that might affect interpretation of the data. |
QAPP Information: |
The SWAMP QAPP (2008) was followed. |
QAPP Information Reference(s): |
Surface Water Ambient Monitoring Program Quality Assurance Program Plan |
|
Line of Evidence (LOE) for Decision ID 101109, Nickel
|
Region 1 |
Klamath River HU, Shasta River HA |
|
|
LOE ID: |
103341 |
|
Pollutant: |
Nickel |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Total |
|
Beneficial Use: |
Commercial or recreational collection of fish, shellfish, or organisms |
|
Number of Samples: |
5 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP RWB1 Monitoring data for Klamath River HU, Shasta River HA to determine beneficial use support and results are as follows: 0 of 5 samples exceeded the water quality standard for Nickel. |
Data Reference: |
Water Quality Assessment Data for the 2018 solicitation cycle submitted through CEDEN for SWAMP RWB1 Monitoring .
|
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
Water Quality Control Plan, North Coast Region (NCRWQCB 2018): All waters shall be maintained free of toxic substances in concentrations that are toxic to, or that produce detrimental physiological responses in human, plant, animal, or aquatic life. The established numeric criteria for Nickel to protect human health from consumption of organisms only is 4600 ug/L (California Toxics Rule, 2000). |
Objective/Criterion Reference: |
Water Quality Standards 2000. Establishment of numeric criteria for priority toxic pollutants for the State of California: Rules and regulations. Federal Register Vol. 65, No. 97. Washington, D.C.: Environmental Protection Agency |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
The samples were collected at 1 monitoring site(s) (105SH9274) |
Temporal Representation: |
The samples were collected between the dates of 2013-03-07 and 2013-11-20 |
Environmental Conditions: |
|
QAPP Information: |
Quality Assurance Program Plan and Standard Operating Procedures for SWAMP program |
QAPP Information Reference(s): |
Quality Assurance Program Plans, Quality Assurance Project Plans, and Standard Operating Procedures for the SWAMP program |
|
Line of Evidence (LOE) for Decision ID 101109, Nickel
|
Region 1 |
Klamath River HU, Shasta River HA |
|
|
LOE ID: |
103335 |
|
Pollutant: |
Nickel |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Dissolved |
|
Beneficial Use: |
Cold Freshwater Habitat |
|
Number of Samples: |
5 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP RWB1 Monitoring data for Klamath River HU, Shasta River HA to determine beneficial use support and results are as follows: 0 of 5 samples exceeded the water quality standard for Nickel. |
Data Reference: |
Water Quality Assessment Data for the 2018 solicitation cycle submitted through CEDEN for SWAMP RWB1 Monitoring .
|
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
California Toxics Rule (CTR) lists criterion continuous concentrations to protect aquatic life in freshwater. The criterion in freshwater is hardness dependent for each sample and varies based on the ambient hardness during sampling. Section (b)(1) in CTR contains the hardness dependent formula for the metals criterion. |
Objective/Criterion Reference: |
Water Quality Standards 2000. Establishment of numeric criteria for priority toxic pollutants for the State of California: Rules and regulations. Federal Register Vol. 65, No. 97. Washington, D.C.: Environmental Protection Agency |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
The samples were collected at 1 monitoring site(s) (105SH1452) |
Temporal Representation: |
The samples were collected between the dates of 2013-03-06 and 2013-11-20 |
Environmental Conditions: |
|
QAPP Information: |
Quality Assurance Program Plan and Standard Operating Procedures for SWAMP program |
QAPP Information Reference(s): |
Quality Assurance Program Plans, Quality Assurance Project Plans, and Standard Operating Procedures for the SWAMP program |
|
Line of Evidence (LOE) for Decision ID 101109, Nickel
|
Region 1 |
Klamath River HU, Shasta River HA |
|
|
LOE ID: |
123420 |
|
Pollutant: |
Nickel |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Total |
|
Beneficial Use: |
Municipal & Domestic Supply |
|
Number of Samples: |
22 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
State Water Board staff re-assessed SWAMP data for Klamath River HU, Shasta River HA to determine beneficial use support and results are as follows: 0 of 22 samples exceed the criterion for Nickel, Total. This LOE re-assesses data from LOE 21509 from the 2010 Integrated Report. Data were re-assessed in order to evaluate these data in their own LOE, instead of being evaluated in the same LOE as other metals data. |
Data Reference: |
Surface Water Ambient Monitoring Program (SWAMP). Summary Report for the North Coast Region (RWQCB-1) for years 2000-2006. North Coast Regional Water Quality Control Board. March 2008 |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
Water Quality Control Plan, North Coast Region (NCRWQCB 2011): Waters designated for use as domestic or municipal supply (MUN) shall not contain concentrations of chemical constituents in excess of the limits specified in California Code of Regulations, Title 22, Chapter 15. The maximum contaminant level listed in Table 64431-A for nickel is 0.1 mg/L. |
Objective/Criterion Reference: |
Water Quality Control Plan (Basin Plan) for the North Coast Region |
Objective/Criterion Reference: |
Maximum Contaminant Levels for organic and inorganic chemicals. CCR Title 22 |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
Data for this line of evidence for Klamath River HU, Shasta River HA was collected at 1 monitoring site [ Shasta River at Hwy 263 - 105SH1452] |
Temporal Representation: |
Data was collected over the time period 3/20/2001-11/16/2006. |
Environmental Conditions: |
There are no known environmental conditions (e.g., seasonality, land use practices, fire events, storms, etc.) that are related to these data. |
QAPP Information: |
Quality control was conducted in accordance with the SWAMP Quality Assurance Management Plan (SWAMP 2002). |
QAPP Information Reference(s): |
Quality Assurance Management Plan for the State of California's Surface Water Ambient Monitoring Program. Sacramento, CA. State Water Resources Control Board. SWAMP. December 2002 (1st version)
|
|
Line of Evidence (LOE) for Decision ID 168840, Oxadiazon
|
Region 1 |
Klamath River HU, Shasta River HA |
|
|
LOE ID: |
350183 |
|
Pollutant: |
Oxadiazon |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Total |
|
Beneficial Use: |
Cold Freshwater Habitat |
|
Number of Samples: |
3 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP RWB1 Monitoring data for Klamath River HU, Shasta River HA to determine beneficial use support and results are as follows: 0 of 3 samples exceeded the water quality threshold for Oxadiazon. |
Data Reference: |
Water Quality Assessment Data for the 2018 solicitation cycle submitted through CEDEN for SWAMP RWB1 Monitoring .
|
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
All waters shall be maintained free of toxic substances in concentrations which are toxic to, or which produce detrimental physiological responses in, human, plant, animal, or aquatic life. (Basin Plan). |
Objective/Criterion Reference: |
Water Quality Control Plan (Basin Plan) for the North Coast Region |
|
Evaluation Guideline: |
The evaluation guideline for Oxadiazon is the USEPA Aquatic Life Benchmark of 0.88 ug/L for a fish (chronic). |
Guideline Reference: |
OPP Aquatic Life Benchmarks |
|
Spatial Representation: |
The samples were collected at 1 monitoring site: 105SH1452 (Shasta River at Hwy 263). |
Temporal Representation: |
The samples were collected between the dates of 2013-03-06 and 2013-11-20 |
Environmental Conditions: |
|
QAPP Information: |
Generic SWAMP QAPrP |
QAPP Information Reference(s): |
Generic SWAMP QAPrP |
|
Line of Evidence (LOE) for Decision ID 168840, Oxadiazon
|
Region 1 |
Klamath River HU, Shasta River HA |
|
|
LOE ID: |
123435 |
|
Pollutant: |
Oxadiazon |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
None |
|
Beneficial Use: |
Municipal & Domestic Supply |
|
Number of Samples: |
0 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
State Water Board staff re-assessed SWAMP data for Klamath River HU, Shasta River HA to determine beneficial use support and results are as follows: 0 of 0 samples exceed the criterion for Oxadiazon, Total. Sixteen samples were removed from assessment because an appropriate evaluation guideline for the water body-pollutant combination could not be obtained for this listing cycle. This LOE re-assesses data from LOE 29849 from the 2010 Integrated Report. Data were re-assessed in order to evaluate these data in their own LOE, instead of being evaluated in the same LOE as other pesticide data. |
Data Reference: |
Surface Water Ambient Monitoring Program (SWAMP). Summary Report for the North Coast Region (RWQCB-1) for years 2000-2006. North Coast Regional Water Quality Control Board. March 2008 |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
Per the Basin Plan (NCRWQCB 2011): No individual pesticide or combination of pesticides shall be present in concentrations that adversely affect beneficial uses. There shall be no bioaccumulation of pesticide concentrations found in bottom sediments or aquatic life. Waters designated for use as domestic or municipal supply shall not contain concentrations of pesticides in excess of the limiting concentrations set forth in California Code of Regulations, Title 22, Division 4, Chapter 15, Article 4, Section 64444, and listed in Table 3.2 of the Basin Plan. No evaluation guideline could be found to evaluate protection of the MUN beneficial use that meets the requirements of Section 6.1.3 of the Listing Policy. |
Objective/Criterion Reference: |
Water Quality Control Plan (Basin Plan) for the North Coast Region |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
Data for this line of evidence for Klamath River HU, Shasta River HA was collected at 1 monitoring site [ Shasta River at Hwy 263 - 105SH1452] |
Temporal Representation: |
Data was collected over the time period 2/27/2002-11/16/2006. |
Environmental Conditions: |
There are no known environmental conditions (e.g., seasonality, land use practices, fire events, storms, etc.) that are related to these data. |
QAPP Information: |
Quality control was conducted in accordance with the SWAMP Quality Assurance Management Plan (SWAMP 2002). |
QAPP Information Reference(s): |
Quality Assurance Management Plan for the State of California's Surface Water Ambient Monitoring Program. Sacramento, CA. State Water Resources Control Board. SWAMP. December 2002 (1st version)
|
|
Line of Evidence (LOE) for Decision ID 168840, Oxadiazon
|
Region 1 |
Klamath River HU, Shasta River HA |
|
|
LOE ID: |
103361 |
|
Pollutant: |
Oxadiazon |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Total |
|
Beneficial Use: |
Municipal & Domestic Supply |
|
Number of Samples: |
1 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP RWB1 Monitoring data for Klamath River HU, Shasta River HA to determine beneficial use support and results are as follows: 0 of 1 samples exceeded the water quality standard for Oxadiazon. |
Data Reference: |
Water Quality Assessment Data for the 2018 solicitation cycle submitted through CEDEN for SWAMP RWB1 Monitoring .
|
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
All waters shall be maintained free of toxic substances in concentrations that are toxic to, or that produce detrimental physiological responses in human, plant, animal, or aquatic life (North Coast Regional Water Quality Control Board). |
Objective/Criterion Reference: |
Water Quality Control Plan (Basin Plan) for the North Coast Region |
|
Evaluation Guideline: |
The USEPA expected safe lifetime exposure limit in drinking water for Oxdiazon, calculated using the IRIS Reference Dose, is 35 ug/L. This was calculated assuming 70 kg body weight, 2 liters/day water consumption, 20% relative source contribution from drinking water, and 0.005 mg/kg/day as the reference dose. |
Guideline Reference: |
IRIS Reference Summary (Various Pollutants) |
|
Spatial Representation: |
The samples were collected at 1 monitoring site(s) (105SH1452) |
Temporal Representation: |
The samples were collected between the dates of 2013-04-29 and 2013-04-29 |
Environmental Conditions: |
|
QAPP Information: |
Quality Assurance Program Plan and Standard Operating Procedures for SWAMP program |
QAPP Information Reference(s): |
Quality Assurance Program Plans, Quality Assurance Project Plans, and Standard Operating Procedures for the SWAMP program |
|
Line of Evidence (LOE) for Decision ID 168840, Oxadiazon
|
Region 1 |
Klamath River HU, Shasta River HA |
|
|
LOE ID: |
123448 |
|
Pollutant: |
Oxadiazon |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
None |
|
Beneficial Use: |
Municipal & Domestic Supply |
|
Number of Samples: |
0 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
State Water Board staff re-assessed SWAMP data for Klamath River HU, Shasta River HA to determine beneficial use support and results are as follows: 0 of 0 samples exceed the criterion for Oxadiazon, Total. Four samples were removed from assessment because an appropriate evaluation guideline for the water body-pollutant combination could not be obtained for this listing cycle. This LOE re-assesses data from LOE 29849 from the 2010 Integrated Report. Data were re-assessed in order to evaluate these data in their own LOE, instead of being evaluated in the same LOE as other pesticide data. |
Data Reference: |
Surface Water Ambient Monitoring Program (SWAMP). Summary Report for the North Coast Region (RWQCB-1) for years 2000-2006. North Coast Regional Water Quality Control Board. March 2008 |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
Per the Basin Plan (NCRWQCB 2011): No individual pesticide or combination of pesticides shall be present in concentrations that adversely affect beneficial uses. There shall be no bioaccumulation of pesticide concentrations found in bottom sediments or aquatic life. Waters designated for use as domestic or municipal supply shall not contain concentrations of pesticides in excess of the limiting concentrations set forth in California Code of Regulations, Title 22, Division 4, Chapter 15, Article 4, Section 64444, and listed in Table 3.2 of the Basin Plan. No evaluation guideline could be found to evaluate protection of the MUN beneficial use that meets the requirements of Section 6.1.3 of the Listing Policy. |
Objective/Criterion Reference: |
Water Quality Control Plan (Basin Plan) for the North Coast Region |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
Data for this line of evidence for Klamath River HU, Shasta River HA was collected at 1 monitoring site [ Shasta River near Edgewood - 105SH9274] |
Temporal Representation: |
Data was collected over the time period 10/7/2002-6/19/2003. |
Environmental Conditions: |
There are no known environmental conditions (e.g., seasonality, land use practices, fire events, storms, etc.) that are related to these data. |
QAPP Information: |
Quality control was conducted in accordance with the SWAMP Quality Assurance Management Plan (SWAMP 2002). |
QAPP Information Reference(s): |
Quality Assurance Management Plan for the State of California's Surface Water Ambient Monitoring Program. Sacramento, CA. State Water Resources Control Board. SWAMP. December 2002 (1st version)
|
|
Line of Evidence (LOE) for Decision ID 168840, Oxadiazon
|
Region 1 |
Klamath River HU, Shasta River HA |
|
|
LOE ID: |
123460 |
|
Pollutant: |
Oxadiazon |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
None |
|
Beneficial Use: |
Municipal & Domestic Supply |
|
Number of Samples: |
0 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
State Water Board staff re-assessed SWAMP data for Klamath River HU, Shasta River HA to determine beneficial use support and results are as follows: 0 of 0 samples exceed the criterion for Oxadiazon, Total. Four samples were removed from assessment because an appropriate evaluation guideline for the water body-pollutant combination could not be obtained for this listing cycle. This LOE re-assesses data from LOE 29849 from the 2010 Integrated Report. Data were re-assessed in order to evaluate these data in their own LOE, instead of being evaluated in the same LOE as other pesticide data. |
Data Reference: |
Surface Water Ambient Monitoring Program (SWAMP). Summary Report for the North Coast Region (RWQCB-1) for years 2000-2006. North Coast Regional Water Quality Control Board. March 2008 |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
Per the Basin Plan (NCRWQCB 2011): No individual pesticide or combination of pesticides shall be present in concentrations that adversely affect beneficial uses. There shall be no bioaccumulation of pesticide concentrations found in bottom sediments or aquatic life. Waters designated for use as domestic or municipal supply shall not contain concentrations of pesticides in excess of the limiting concentrations set forth in California Code of Regulations, Title 22, Division 4, Chapter 15, Article 4, Section 64444, and listed in Table 3.2 of the Basin Plan. No evaluation guideline could be found to evaluate protection of the MUN beneficial use that meets the requirements of Section 6.1.3 of the Listing Policy. |
Objective/Criterion Reference: |
Water Quality Control Plan (Basin Plan) for the North Coast Region |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
Data for this line of evidence for Klamath River HU, Shasta River HA was collected at 1 monitoring site [ Yreka Creek at Highway 3 - 105YREHW3] |
Temporal Representation: |
Data was collected over the time period 10/21/2004-6/20/2005. |
Environmental Conditions: |
There are no known environmental conditions (e.g., seasonality, land use practices, fire events, storms, etc.) that are related to these data. |
QAPP Information: |
Quality control was conducted in accordance with the SWAMP Quality Assurance Management Plan (SWAMP 2002). |
QAPP Information Reference(s): |
Quality Assurance Management Plan for the State of California's Surface Water Ambient Monitoring Program. Sacramento, CA. State Water Resources Control Board. SWAMP. December 2002 (1st version)
|
|
Line of Evidence (LOE) for Decision ID 168840, Oxadiazon
|
Region 1 |
Klamath River HU, Shasta River HA |
|
|
LOE ID: |
123449 |
|
Pollutant: |
Oxadiazon |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
None |
|
Beneficial Use: |
Municipal & Domestic Supply |
|
Number of Samples: |
0 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
State Water Board staff re-assessed SWAMP data for Klamath River HU, Shasta River HA to determine beneficial use support and results are as follows: 0 of 0 samples exceed the criterion for Oxadiazon, Total. Eight samples were removed from assessment because an appropriate evaluation guideline for the water body-pollutant combination could not be obtained for this listing cycle. This LOE re-assesses data from LOE 29849 from the 2010 Integrated Report. Data were re-assessed in order to evaluate these data in their own LOE, instead of being evaluated in the same LOE as other pesticide data. |
Data Reference: |
Surface Water Ambient Monitoring Program (SWAMP). Summary Report for the North Coast Region (RWQCB-1) for years 2000-2006. North Coast Regional Water Quality Control Board. March 2008 |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
Per the Basin Plan (NCRWQCB 2011): No individual pesticide or combination of pesticides shall be present in concentrations that adversely affect beneficial uses. There shall be no bioaccumulation of pesticide concentrations found in bottom sediments or aquatic life. Waters designated for use as domestic or municipal supply shall not contain concentrations of pesticides in excess of the limiting concentrations set forth in California Code of Regulations, Title 22, Division 4, Chapter 15, Article 4, Section 64444, and listed in Table 3.2 of the Basin Plan. No evaluation guideline could be found to evaluate protection of the MUN beneficial use that meets the requirements of Section 6.1.3 of the Listing Policy. |
Objective/Criterion Reference: |
Water Quality Control Plan (Basin Plan) for the North Coast Region |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
Data for this line of evidence for Klamath River HU, Shasta River HA was collected at 1 monitoring site [ Yreka Creek at Anderson Rd - 105YREAND] |
Temporal Representation: |
Data was collected over the time period 10/9/2002-6/20/2005. |
Environmental Conditions: |
There are no known environmental conditions (e.g., seasonality, land use practices, fire events, storms, etc.) that are related to these data. |
QAPP Information: |
Quality control was conducted in accordance with the SWAMP Quality Assurance Management Plan (SWAMP 2002). |
QAPP Information Reference(s): |
Quality Assurance Management Plan for the State of California's Surface Water Ambient Monitoring Program. Sacramento, CA. State Water Resources Control Board. SWAMP. December 2002 (1st version)
|
|
Line of Evidence (LOE) for Decision ID 168840, Oxadiazon
|
Region 1 |
Klamath River HU, Shasta River HA |
|
|
LOE ID: |
350260 |
|
Pollutant: |
Oxadiazon |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Total |
|
Beneficial Use: |
Cold Freshwater Habitat |
|
Number of Samples: |
3 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP RWB1 Monitoring data for Klamath River HU, Shasta River HA to determine beneficial use support and results are as follows: 0 of 3 samples exceeded the water quality threshold for Oxadiazon. |
Data Reference: |
Water Quality Assessment Data for the 2018 solicitation cycle submitted through CEDEN for SWAMP RWB1 Monitoring .
|
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
All waters shall be maintained free of toxic substances in concentrations which are toxic to, or which produce detrimental physiological responses in, human, plant, animal, or aquatic life. (Basin Plan). |
Objective/Criterion Reference: |
Water Quality Control Plan (Basin Plan) for the North Coast Region |
|
Evaluation Guideline: |
The evaluation guideline for Oxadiazon is the USEPA Aquatic Life Benchmark of 0.88 ug/L for a fish (chronic). |
Guideline Reference: |
OPP Aquatic Life Benchmarks |
|
Spatial Representation: |
The samples were collected at 1 monitoring site: 105SH9274 (Shasta River near Edgewood). |
Temporal Representation: |
The samples were collected between the dates of 2013-03-07 and 2013-11-20 |
Environmental Conditions: |
|
QAPP Information: |
Generic SWAMP QAPrP |
QAPP Information Reference(s): |
Generic SWAMP QAPrP |
|
Line of Evidence (LOE) for Decision ID 168840, Oxadiazon
|
Region 1 |
Klamath River HU, Shasta River HA |
|
|
LOE ID: |
103364 |
|
Pollutant: |
Oxadiazon |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Total |
|
Beneficial Use: |
Municipal & Domestic Supply |
|
Number of Samples: |
1 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP RWB1 Monitoring data for Klamath River HU, Shasta River HA to determine beneficial use support and results are as follows: 0 of 1 samples exceeded the water quality standard for Oxadiazon. |
Data Reference: |
Water Quality Assessment Data for the 2018 solicitation cycle submitted through CEDEN for SWAMP RWB1 Monitoring .
|
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
All waters shall be maintained free of toxic substances in concentrations that are toxic to, or that produce detrimental physiological responses in human, plant, animal, or aquatic life (North Coast Regional Water Quality Control Board). |
Objective/Criterion Reference: |
Water Quality Control Plan (Basin Plan) for the North Coast Region |
|
Evaluation Guideline: |
The USEPA expected safe lifetime exposure limit in drinking water for Oxdiazon, calculated using the IRIS Reference Dose, is 35 ug/L. This was calculated assuming 70 kg body weight, 2 liters/day water consumption, 20% relative source contribution from drinking water, and 0.005 mg/kg/day as the reference dose. |
Guideline Reference: |
IRIS Reference Summary (Various Pollutants) |
|
Spatial Representation: |
The samples were collected at 1 monitoring site(s) (105SH9274) |
Temporal Representation: |
The samples were collected between the dates of 2013-04-29 and 2013-04-29 |
Environmental Conditions: |
|
QAPP Information: |
Quality Assurance Program Plan and Standard Operating Procedures for SWAMP program |
QAPP Information Reference(s): |
Quality Assurance Program Plans, Quality Assurance Project Plans, and Standard Operating Procedures for the SWAMP program |
|
Line of Evidence (LOE) for Decision ID 168840, Oxadiazon
|
Region 1 |
Klamath River HU, Shasta River HA |
|
|
LOE ID: |
123447 |
|
Pollutant: |
Oxadiazon |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
None |
|
Beneficial Use: |
Municipal & Domestic Supply |
|
Number of Samples: |
0 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
State Water Board staff re-assessed SWAMP data for Klamath River HU, Shasta River HA to determine beneficial use support and results are as follows: 0 of 0 samples exceed the criterion for Oxadiazon, Total. Four samples were removed from assessment because an appropriate evaluation guideline for the water body-pollutant combination could not be obtained for this listing cycle. This LOE re-assesses data from LOE 29849 from the 2010 Integrated Report. Data were re-assessed in order to evaluate these data in their own LOE, instead of being evaluated in the same LOE as other pesticide data. |
Data Reference: |
Surface Water Ambient Monitoring Program (SWAMP). Summary Report for the North Coast Region (RWQCB-1) for years 2000-2006. North Coast Regional Water Quality Control Board. March 2008 |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
Per the Basin Plan (NCRWQCB 2011): No individual pesticide or combination of pesticides shall be present in concentrations that adversely affect beneficial uses. There shall be no bioaccumulation of pesticide concentrations found in bottom sediments or aquatic life. Waters designated for use as domestic or municipal supply shall not contain concentrations of pesticides in excess of the limiting concentrations set forth in California Code of Regulations, Title 22, Division 4, Chapter 15, Article 4, Section 64444, and listed in Table 3.2 of the Basin Plan. No evaluation guideline could be found to evaluate protection of the MUN beneficial use that meets the requirements of Section 6.1.3 of the Listing Policy. |
Objective/Criterion Reference: |
Water Quality Control Plan (Basin Plan) for the North Coast Region |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
Data for this line of evidence for Klamath River HU, Shasta River HA was collected at 1 monitoring site [ Shasta River at Montague - 105SHAMON] |
Temporal Representation: |
Data was collected over the time period 10/7/2002-6/19/2003. |
Environmental Conditions: |
There are no known environmental conditions (e.g., seasonality, land use practices, fire events, storms, etc.) that are related to these data. |
QAPP Information: |
Quality control was conducted in accordance with the SWAMP Quality Assurance Management Plan (SWAMP 2002). |
QAPP Information Reference(s): |
Quality Assurance Management Plan for the State of California's Surface Water Ambient Monitoring Program. Sacramento, CA. State Water Resources Control Board. SWAMP. December 2002 (1st version)
|
|
Line of Evidence (LOE) for Decision ID 168840, Oxadiazon
|
Region 1 |
Klamath River HU, Shasta River HA |
|
|
LOE ID: |
350242 |
|
Pollutant: |
Oxadiazon |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Total |
|
Beneficial Use: |
Warm Freshwater Habitat |
|
Number of Samples: |
3 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP RWB1 Monitoring data for Klamath River HU, Shasta River HA to determine beneficial use support and results are as follows: 0 of 3 samples exceeded the water quality threshold for Oxadiazon. |
Data Reference: |
Water Quality Assessment Data for the 2018 solicitation cycle submitted through CEDEN for SWAMP RWB1 Monitoring .
|
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
All waters shall be maintained free of toxic substances in concentrations which are toxic to, or which produce detrimental physiological responses in, human, plant, animal, or aquatic life. (Basin Plan). |
Objective/Criterion Reference: |
Water Quality Control Plan (Basin Plan) for the North Coast Region |
|
Evaluation Guideline: |
The evaluation guideline for Oxadiazon is the USEPA Aquatic Life Benchmark of 0.88 ug/L for a fish (chronic). |
Guideline Reference: |
OPP Aquatic Life Benchmarks |
|
Spatial Representation: |
The samples were collected at 1 monitoring site: 105SH9274 (Shasta River near Edgewood). |
Temporal Representation: |
The samples were collected between the dates of 2013-03-07 and 2013-11-20 |
Environmental Conditions: |
|
QAPP Information: |
Generic SWAMP QAPrP |
QAPP Information Reference(s): |
Generic SWAMP QAPrP |
|
Line of Evidence (LOE) for Decision ID 168840, Oxadiazon
|
Region 1 |
Klamath River HU, Shasta River HA |
|
|
LOE ID: |
350154 |
|
Pollutant: |
Oxadiazon |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Total |
|
Beneficial Use: |
Warm Freshwater Habitat |
|
Number of Samples: |
3 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP RWB1 Monitoring data for Klamath River HU, Shasta River HA to determine beneficial use support and results are as follows: 0 of 3 samples exceeded the water quality threshold for Oxadiazon. |
Data Reference: |
Water Quality Assessment Data for the 2018 solicitation cycle submitted through CEDEN for SWAMP RWB1 Monitoring .
|
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
All waters shall be maintained free of toxic substances in concentrations which are toxic to, or which produce detrimental physiological responses in, human, plant, animal, or aquatic life. (Basin Plan). |
Objective/Criterion Reference: |
Water Quality Control Plan (Basin Plan) for the North Coast Region |
|
Evaluation Guideline: |
The evaluation guideline for Oxadiazon is the USEPA Aquatic Life Benchmark of 0.88 ug/L for a fish (chronic). |
Guideline Reference: |
OPP Aquatic Life Benchmarks |
|
Spatial Representation: |
The samples were collected at 1 monitoring site: 105SH1452 (Shasta River at Hwy 263). |
Temporal Representation: |
The samples were collected between the dates of 2013-03-06 and 2013-11-20 |
Environmental Conditions: |
|
QAPP Information: |
Generic SWAMP QAPrP |
QAPP Information Reference(s): |
Generic SWAMP QAPrP |
|
Line of Evidence (LOE) for Decision ID 168847, Phorate
|
Region 1 |
Klamath River HU, Shasta River HA |
|
|
LOE ID: |
123500 |
|
Pollutant: |
Phorate |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
None |
|
Beneficial Use: |
Municipal & Domestic Supply |
|
Number of Samples: |
0 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
State Water Board staff re-assessed SWAMP data for Klamath River HU, Shasta River HA to determine beneficial use support and results are as follows: 0 of 0 samples exceed the criterion for Phorate, Total. Eight samples were removed from assessment because an appropriate evaluation guideline for the water body-pollutant combination could not be obtained for this listing cycle. This LOE re-assesses data from LOE 29849 from the 2010 Integrated Report. Data were re-assessed in order to evaluate these data in their own LOE, instead of being evaluated in the same LOE as other pesticide data. |
Data Reference: |
Surface Water Ambient Monitoring Program (SWAMP). Summary Report for the North Coast Region (RWQCB-1) for years 2000-2006. North Coast Regional Water Quality Control Board. March 2008 |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
Per the Basin Plan (NCRWQCB 2011): No individual pesticide or combination of pesticides shall be present in concentrations that adversely affect beneficial uses. There shall be no bioaccumulation of pesticide concentrations found in bottom sediments or aquatic life. Waters designated for use as domestic or municipal supply shall not contain concentrations of pesticides in excess of the limiting concentrations set forth in California Code of Regulations, Title 22, Division 4, Chapter 15, Article 4, Section 64444, and listed in Table 3.2 of the Basin Plan. No evaluation guideline could be found to evaluate protection of the MUN beneficial use that meets the requirements of Section 6.1.3 of the Listing Policy. |
Objective/Criterion Reference: |
Water Quality Control Plan (Basin Plan) for the North Coast Region |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
Data for this line of evidence for Klamath River HU, Shasta River HA was collected at 1 monitoring site [ Yreka Creek at Anderson Rd - 105YREAND] |
Temporal Representation: |
Data was collected over the time period 10/9/2002-6/20/2005. |
Environmental Conditions: |
There are no known environmental conditions (e.g., seasonality, land use practices, fire events, storms, etc.) that are related to these data. |
QAPP Information: |
Quality control was conducted in accordance with the SWAMP Quality Assurance Management Plan (SWAMP 2002). |
QAPP Information Reference(s): |
Quality Assurance Management Plan for the State of California's Surface Water Ambient Monitoring Program. Sacramento, CA. State Water Resources Control Board. SWAMP. December 2002 (1st version)
|
|
Line of Evidence (LOE) for Decision ID 168847, Phorate
|
Region 1 |
Klamath River HU, Shasta River HA |
|
|
LOE ID: |
123508 |
|
Pollutant: |
Phorate |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
None |
|
Beneficial Use: |
Municipal & Domestic Supply |
|
Number of Samples: |
0 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
State Water Board staff re-assessed SWAMP data for Klamath River HU, Shasta River HA to determine beneficial use support and results are as follows: 0 of 0 samples exceed the criterion for Phorate, Total. Four samples were removed from assessment because an appropriate evaluation guideline for the water body-pollutant combination could not be obtained for this listing cycle. This LOE re-assesses data from LOE 29849 from the 2010 Integrated Report. Data were re-assessed in order to evaluate these data in their own LOE, instead of being evaluated in the same LOE as other pesticide data. |
Data Reference: |
Surface Water Ambient Monitoring Program (SWAMP). Summary Report for the North Coast Region (RWQCB-1) for years 2000-2006. North Coast Regional Water Quality Control Board. March 2008 |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
Per the Basin Plan (NCRWQCB 2011): No individual pesticide or combination of pesticides shall be present in concentrations that adversely affect beneficial uses. There shall be no bioaccumulation of pesticide concentrations found in bottom sediments or aquatic life. Waters designated for use as domestic or municipal supply shall not contain concentrations of pesticides in excess of the limiting concentrations set forth in California Code of Regulations, Title 22, Division 4, Chapter 15, Article 4, Section 64444, and listed in Table 3.2 of the Basin Plan. No evaluation guideline could be found to evaluate protection of the MUN beneficial use that meets the requirements of Section 6.1.3 of the Listing Policy. |
Objective/Criterion Reference: |
Water Quality Control Plan (Basin Plan) for the North Coast Region |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
Data for this line of evidence for Klamath River HU, Shasta River HA was collected at 1 monitoring site [ Yreka Creek at Highway 3 - 105YREHW3] |
Temporal Representation: |
Data was collected over the time period 10/21/2004-6/20/2005. |
Environmental Conditions: |
There are no known environmental conditions (e.g., seasonality, land use practices, fire events, storms, etc.) that are related to these data. |
QAPP Information: |
Quality control was conducted in accordance with the SWAMP Quality Assurance Management Plan (SWAMP 2002). |
QAPP Information Reference(s): |
Quality Assurance Management Plan for the State of California's Surface Water Ambient Monitoring Program. Sacramento, CA. State Water Resources Control Board. SWAMP. December 2002 (1st version)
|
|
Line of Evidence (LOE) for Decision ID 168847, Phorate
|
Region 1 |
Klamath River HU, Shasta River HA |
|
|
LOE ID: |
123499 |
|
Pollutant: |
Phorate |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
None |
|
Beneficial Use: |
Municipal & Domestic Supply |
|
Number of Samples: |
0 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
State Water Board staff re-assessed SWAMP data for Klamath River HU, Shasta River HA to determine beneficial use support and results are as follows: 0 of 0 samples exceed the criterion for Phorate, Total. Four samples were removed from assessment because an appropriate evaluation guideline for the water body-pollutant combination could not be obtained for this listing cycle. This LOE re-assesses data from LOE 29849 from the 2010 Integrated Report. Data were re-assessed in order to evaluate these data in their own LOE, instead of being evaluated in the same LOE as other pesticide data. |
Data Reference: |
Surface Water Ambient Monitoring Program (SWAMP). Summary Report for the North Coast Region (RWQCB-1) for years 2000-2006. North Coast Regional Water Quality Control Board. March 2008 |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
Per the Basin Plan (NCRWQCB 2011): No individual pesticide or combination of pesticides shall be present in concentrations that adversely affect beneficial uses. There shall be no bioaccumulation of pesticide concentrations found in bottom sediments or aquatic life. Waters designated for use as domestic or municipal supply shall not contain concentrations of pesticides in excess of the limiting concentrations set forth in California Code of Regulations, Title 22, Division 4, Chapter 15, Article 4, Section 64444, and listed in Table 3.2 of the Basin Plan. No evaluation guideline could be found to evaluate protection of the MUN beneficial use that meets the requirements of Section 6.1.3 of the Listing Policy. |
Objective/Criterion Reference: |
Water Quality Control Plan (Basin Plan) for the North Coast Region |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
Data for this line of evidence for Klamath River HU, Shasta River HA was collected at 1 monitoring site [ Shasta River near Edgewood - 105SH9274] |
Temporal Representation: |
Data was collected over the time period 10/7/2002-6/19/2003. |
Environmental Conditions: |
There are no known environmental conditions (e.g., seasonality, land use practices, fire events, storms, etc.) that are related to these data. |
QAPP Information: |
Quality control was conducted in accordance with the SWAMP Quality Assurance Management Plan (SWAMP 2002). |
QAPP Information Reference(s): |
Quality Assurance Management Plan for the State of California's Surface Water Ambient Monitoring Program. Sacramento, CA. State Water Resources Control Board. SWAMP. December 2002 (1st version)
|
|
Line of Evidence (LOE) for Decision ID 168847, Phorate
|
Region 1 |
Klamath River HU, Shasta River HA |
|
|
LOE ID: |
103386 |
|
Pollutant: |
Phorate |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Total |
|
Beneficial Use: |
Warm Freshwater Habitat |
|
Number of Samples: |
3 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP RWB1 Monitoring data for Klamath River HU, Shasta River HA to determine beneficial use support and results are as follows: 0 of 3 samples exceeded the water quality standard for Phorate. |
Data Reference: |
Water Quality Assessment Data for the 2018 solicitation cycle submitted through CEDEN for SWAMP RWB1 Monitoring .
|
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
All waters shall be maintained free of toxic substances in concentrations which are toxic to, or which produce detrimental physiological responses in, human, plant, animal, or aquatic life. (Basin Plan). |
Objective/Criterion Reference: |
Water Quality Control Plan (Basin Plan) for the North Coast Region |
|
Evaluation Guideline: |
The evaluation guideline for Phorate is the USEPA Aquatic Life Benchmark of 0.21 ug/L for an invertebrate (chronic). |
Guideline Reference: |
OPP Aquatic Life Benchmarks |
|
Spatial Representation: |
The samples were collected at 1 monitoring site(s) (105SH1452) |
Temporal Representation: |
The samples were collected between the dates of 2013-03-06 and 2013-11-20 |
Environmental Conditions: |
|
QAPP Information: |
Quality Assurance Program Plan and Standard Operating Procedures for SWAMP program |
QAPP Information Reference(s): |
Quality Assurance Program Plans, Quality Assurance Project Plans, and Standard Operating Procedures for the SWAMP program |
|
Line of Evidence (LOE) for Decision ID 168847, Phorate
|
Region 1 |
Klamath River HU, Shasta River HA |
|
|
LOE ID: |
103389 |
|
Pollutant: |
Phorate |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Total |
|
Beneficial Use: |
Warm Freshwater Habitat |
|
Number of Samples: |
3 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP RWB1 Monitoring data for Klamath River HU, Shasta River HA to determine beneficial use support and results are as follows: 0 of 3 samples exceeded the water quality standard for Phorate. |
Data Reference: |
Water Quality Assessment Data for the 2018 solicitation cycle submitted through CEDEN for SWAMP RWB1 Monitoring .
|
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
All waters shall be maintained free of toxic substances in concentrations which are toxic to, or which produce detrimental physiological responses in, human, plant, animal, or aquatic life. (Basin Plan). |
Objective/Criterion Reference: |
Water Quality Control Plan (Basin Plan) for the North Coast Region |
|
Evaluation Guideline: |
The evaluation guideline for Phorate is the USEPA Aquatic Life Benchmark of 0.21 ug/L for an invertebrate (chronic). |
Guideline Reference: |
OPP Aquatic Life Benchmarks |
|
Spatial Representation: |
The samples were collected at 1 monitoring site(s) (105SH9274) |
Temporal Representation: |
The samples were collected between the dates of 2013-03-07 and 2013-11-20 |
Environmental Conditions: |
|
QAPP Information: |
Quality Assurance Program Plan and Standard Operating Procedures for SWAMP program |
QAPP Information Reference(s): |
Quality Assurance Program Plans, Quality Assurance Project Plans, and Standard Operating Procedures for the SWAMP program |
|
Line of Evidence (LOE) for Decision ID 168847, Phorate
|
Region 1 |
Klamath River HU, Shasta River HA |
|
|
LOE ID: |
103387 |
|
Pollutant: |
Phorate |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Total |
|
Beneficial Use: |
Cold Freshwater Habitat |
|
Number of Samples: |
3 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP RWB1 Monitoring data for Klamath River HU, Shasta River HA to determine beneficial use support and results are as follows: 0 of 3 samples exceeded the water quality standard for Phorate. |
Data Reference: |
Water Quality Assessment Data for the 2018 solicitation cycle submitted through CEDEN for SWAMP RWB1 Monitoring .
|
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
All waters shall be maintained free of toxic substances in concentrations which are toxic to, or which produce detrimental physiological responses in, human, plant, animal, or aquatic life. (Basin Plan). |
Objective/Criterion Reference: |
Water Quality Control Plan (Basin Plan) for the North Coast Region |
|
Evaluation Guideline: |
The evaluation guideline for Phorate is the USEPA Aquatic Life Benchmark of 0.21 ug/L for an invertebrate (chronic). |
Guideline Reference: |
OPP Aquatic Life Benchmarks |
|
Spatial Representation: |
The samples were collected at 1 monitoring site(s) (105SH9274) |
Temporal Representation: |
The samples were collected between the dates of 2013-03-07 and 2013-11-20 |
Environmental Conditions: |
|
QAPP Information: |
Quality Assurance Program Plan and Standard Operating Procedures for SWAMP program |
QAPP Information Reference(s): |
Quality Assurance Program Plans, Quality Assurance Project Plans, and Standard Operating Procedures for the SWAMP program |
|
Line of Evidence (LOE) for Decision ID 168847, Phorate
|
Region 1 |
Klamath River HU, Shasta River HA |
|
|
LOE ID: |
123491 |
|
Pollutant: |
Phorate |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
None |
|
Beneficial Use: |
Municipal & Domestic Supply |
|
Number of Samples: |
0 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
State Water Board staff re-assessed SWAMP data for Klamath River HU, Shasta River HA to determine beneficial use support and results are as follows: 0 of 0 samples exceed the criterion for Phorate, Total. Sixteen samples were removed from assessment because an appropriate evaluation guideline for the water body-pollutant combination could not be obtained for this listing cycle. This LOE re-assesses data from LOE 29849 from the 2010 Integrated Report. Data were re-assessed in order to evaluate these data in their own LOE, instead of being evaluated in the same LOE as other pesticide data. |
Data Reference: |
Surface Water Ambient Monitoring Program (SWAMP). Summary Report for the North Coast Region (RWQCB-1) for years 2000-2006. North Coast Regional Water Quality Control Board. March 2008 |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
Per the Basin Plan (NCRWQCB 2011): No individual pesticide or combination of pesticides shall be present in concentrations that adversely affect beneficial uses. There shall be no bioaccumulation of pesticide concentrations found in bottom sediments or aquatic life. Waters designated for use as domestic or municipal supply shall not contain concentrations of pesticides in excess of the limiting concentrations set forth in California Code of Regulations, Title 22, Division 4, Chapter 15, Article 4, Section 64444, and listed in Table 3.2 of the Basin Plan. No evaluation guideline could be found to evaluate protection of the MUN beneficial use that meets the requirements of Section 6.1.3 of the Listing Policy. |
Objective/Criterion Reference: |
Water Quality Control Plan (Basin Plan) for the North Coast Region |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
Data for this line of evidence for Klamath River HU, Shasta River HA was collected at 1 monitoring site [ Shasta River at Hwy 263 - 105SH1452] |
Temporal Representation: |
Data was collected over the time period 2/27/2002-11/16/2006. |
Environmental Conditions: |
There are no known environmental conditions (e.g., seasonality, land use practices, fire events, storms, etc.) that are related to these data. |
QAPP Information: |
Quality control was conducted in accordance with the SWAMP Quality Assurance Management Plan (SWAMP 2002). |
QAPP Information Reference(s): |
Quality Assurance Management Plan for the State of California's Surface Water Ambient Monitoring Program. Sacramento, CA. State Water Resources Control Board. SWAMP. December 2002 (1st version)
|
|
Line of Evidence (LOE) for Decision ID 168847, Phorate
|
Region 1 |
Klamath River HU, Shasta River HA |
|
|
LOE ID: |
123498 |
|
Pollutant: |
Phorate |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
None |
|
Beneficial Use: |
Municipal & Domestic Supply |
|
Number of Samples: |
0 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
State Water Board staff re-assessed SWAMP data for Klamath River HU, Shasta River HA to determine beneficial use support and results are as follows: 0 of 0 samples exceed the criterion for Phorate, Total. Four samples were removed from assessment because an appropriate evaluation guideline for the water body-pollutant combination could not be obtained for this listing cycle. This LOE re-assesses data from LOE 29849 from the 2010 Integrated Report. Data were re-assessed in order to evaluate these data in their own LOE, instead of being evaluated in the same LOE as other pesticide data. |
Data Reference: |
Surface Water Ambient Monitoring Program (SWAMP). Summary Report for the North Coast Region (RWQCB-1) for years 2000-2006. North Coast Regional Water Quality Control Board. March 2008 |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
Per the Basin Plan (NCRWQCB 2011): No individual pesticide or combination of pesticides shall be present in concentrations that adversely affect beneficial uses. There shall be no bioaccumulation of pesticide concentrations found in bottom sediments or aquatic life. Waters designated for use as domestic or municipal supply shall not contain concentrations of pesticides in excess of the limiting concentrations set forth in California Code of Regulations, Title 22, Division 4, Chapter 15, Article 4, Section 64444, and listed in Table 3.2 of the Basin Plan. No evaluation guideline could be found to evaluate protection of the MUN beneficial use that meets the requirements of Section 6.1.3 of the Listing Policy. |
Objective/Criterion Reference: |
Water Quality Control Plan (Basin Plan) for the North Coast Region |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
Data for this line of evidence for Klamath River HU, Shasta River HA was collected at 1 monitoring site [ Shasta River at Montague - 105SHAMON] |
Temporal Representation: |
Data was collected over the time period 10/7/2002-6/19/2003. |
Environmental Conditions: |
There are no known environmental conditions (e.g., seasonality, land use practices, fire events, storms, etc.) that are related to these data. |
QAPP Information: |
Quality control was conducted in accordance with the SWAMP Quality Assurance Management Plan (SWAMP 2002). |
QAPP Information Reference(s): |
Quality Assurance Management Plan for the State of California's Surface Water Ambient Monitoring Program. Sacramento, CA. State Water Resources Control Board. SWAMP. December 2002 (1st version)
|
|
Line of Evidence (LOE) for Decision ID 168847, Phorate
|
Region 1 |
Klamath River HU, Shasta River HA |
|
|
LOE ID: |
103385 |
|
Pollutant: |
Phorate |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Total |
|
Beneficial Use: |
Cold Freshwater Habitat |
|
Number of Samples: |
3 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP RWB1 Monitoring data for Klamath River HU, Shasta River HA to determine beneficial use support and results are as follows: 0 of 3 samples exceeded the water quality standard for Phorate. |
Data Reference: |
Water Quality Assessment Data for the 2018 solicitation cycle submitted through CEDEN for SWAMP RWB1 Monitoring .
|
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
All waters shall be maintained free of toxic substances in concentrations which are toxic to, or which produce detrimental physiological responses in, human, plant, animal, or aquatic life. (Basin Plan). |
Objective/Criterion Reference: |
Water Quality Control Plan (Basin Plan) for the North Coast Region |
|
Evaluation Guideline: |
The evaluation guideline for Phorate is the USEPA Aquatic Life Benchmark of 0.21 ug/L for an invertebrate (chronic). |
Guideline Reference: |
OPP Aquatic Life Benchmarks |
|
Spatial Representation: |
The samples were collected at 1 monitoring site(s) (105SH1452) |
Temporal Representation: |
The samples were collected between the dates of 2013-03-06 and 2013-11-20 |
Environmental Conditions: |
|
QAPP Information: |
Quality Assurance Program Plan and Standard Operating Procedures for SWAMP program |
QAPP Information Reference(s): |
Quality Assurance Program Plans, Quality Assurance Project Plans, and Standard Operating Procedures for the SWAMP program |
|
Line of Evidence (LOE) for Decision ID 168847, Phorate
|
Region 1 |
Klamath River HU, Shasta River HA |
|
|
LOE ID: |
350342 |
|
Pollutant: |
Phorate |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Total |
|
Beneficial Use: |
Warm Freshwater Habitat |
|
Number of Samples: |
3 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed RWB1 Trend Maintenance Periods FYs 2007 2008 data for Klamath River HU, Shasta River HA to determine beneficial use support and results are as follows: 0 of 3 samples exceeded the water quality threshold for Phorate. |
Data Reference: |
RWB1 Trend Maintenance Periods FYs 2007 2008 |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
All waters shall be maintained free of toxic substances in concentrations which are toxic to, or which produce detrimental physiological responses in, human, plant, animal, or aquatic life. (Basin Plan). |
Objective/Criterion Reference: |
Water Quality Control Plan (Basin Plan) for the North Coast Region |
|
Evaluation Guideline: |
The evaluation guideline for phorate is the USEPA Aquatic Life Benchmark of 0.21 ug/L for an invertebrate (chronic). |
Guideline Reference: |
OPP Aquatic Life Benchmarks |
|
Spatial Representation: |
The samples were collected at 1 monitoring site: 105SHAEDG (Shasta River near Edgewood). |
Temporal Representation: |
The samples were collected between the dates of 2007-11-15 and 2008-07-16 |
Environmental Conditions: |
|
QAPP Information: |
Generic SWAMP QAPrP |
QAPP Information Reference(s): |
Generic SWAMP QAPrP |
|
Line of Evidence (LOE) for Decision ID 168847, Phorate
|
Region 1 |
Klamath River HU, Shasta River HA |
|
|
LOE ID: |
350347 |
|
Pollutant: |
Phorate |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Total |
|
Beneficial Use: |
Warm Freshwater Habitat |
|
Number of Samples: |
3 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed RWB1 Trend Maintenance Periods FYs 2007 2008 data for Klamath River HU, Shasta River HA to determine beneficial use support and results are as follows: 0 of 3 samples exceeded the water quality threshold for Phorate. |
Data Reference: |
RWB1 Trend Maintenance Periods FYs 2007 2008 |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
All waters shall be maintained free of toxic substances in concentrations which are toxic to, or which produce detrimental physiological responses in, human, plant, animal, or aquatic life. (Basin Plan). |
Objective/Criterion Reference: |
Water Quality Control Plan (Basin Plan) for the North Coast Region |
|
Evaluation Guideline: |
The evaluation guideline for phorate is the USEPA Aquatic Life Benchmark of 0.21 ug/L for an invertebrate (chronic). |
Guideline Reference: |
OPP Aquatic Life Benchmarks |
|
Spatial Representation: |
The samples were collected at 1 monitoring site: 105SHA263 (Shasta River at Hwy 263). |
Temporal Representation: |
The samples were collected between the dates of 2007-11-15 and 2008-07-16 |
Environmental Conditions: |
|
QAPP Information: |
Generic SWAMP QAPrP |
QAPP Information Reference(s): |
Generic SWAMP QAPrP |
|
Line of Evidence (LOE) for Decision ID 168847, Phorate
|
Region 1 |
Klamath River HU, Shasta River HA |
|
|
LOE ID: |
350351 |
|
Pollutant: |
Phorate |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Total |
|
Beneficial Use: |
Cold Freshwater Habitat |
|
Number of Samples: |
3 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed RWB1 Trend Maintenance Periods FYs 2007 2008 data for Klamath River HU, Shasta River HA to determine beneficial use support and results are as follows: 0 of 3 samples exceeded the water quality threshold for Phorate. |
Data Reference: |
RWB1 Trend Maintenance Periods FYs 2007 2008 |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
All waters shall be maintained free of toxic substances in concentrations which are toxic to, or which produce detrimental physiological responses in, human, plant, animal, or aquatic life. (Basin Plan). |
Objective/Criterion Reference: |
Water Quality Control Plan (Basin Plan) for the North Coast Region |
|
Evaluation Guideline: |
The evaluation guideline for phorate is the USEPA Aquatic Life Benchmark of 0.21 ug/L for an invertebrate (chronic). |
Guideline Reference: |
OPP Aquatic Life Benchmarks |
|
Spatial Representation: |
The samples were collected at 1 monitoring site: 105SHAEDG (Shasta River near Edgewood). |
Temporal Representation: |
The samples were collected between the dates of 2007-11-15 and 2008-07-16 |
Environmental Conditions: |
|
QAPP Information: |
Generic SWAMP QAPrP |
QAPP Information Reference(s): |
Generic SWAMP QAPrP |
|
Line of Evidence (LOE) for Decision ID 168847, Phorate
|
Region 1 |
Klamath River HU, Shasta River HA |
|
|
LOE ID: |
350353 |
|
Pollutant: |
Phorate |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Total |
|
Beneficial Use: |
Cold Freshwater Habitat |
|
Number of Samples: |
3 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed RWB1 Trend Maintenance Periods FYs 2007 2008 data for Klamath River HU, Shasta River HA to determine beneficial use support and results are as follows: 0 of 3 samples exceeded the water quality threshold for Phorate. |
Data Reference: |
RWB1 Trend Maintenance Periods FYs 2007 2008 |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
All waters shall be maintained free of toxic substances in concentrations which are toxic to, or which produce detrimental physiological responses in, human, plant, animal, or aquatic life. (Basin Plan). |
Objective/Criterion Reference: |
Water Quality Control Plan (Basin Plan) for the North Coast Region |
|
Evaluation Guideline: |
The evaluation guideline for phorate is the USEPA Aquatic Life Benchmark of 0.21 ug/L for an invertebrate (chronic). |
Guideline Reference: |
OPP Aquatic Life Benchmarks |
|
Spatial Representation: |
The samples were collected at 1 monitoring site: 105SHA263 (Shasta River at Hwy 263). |
Temporal Representation: |
The samples were collected between the dates of 2007-11-15 and 2008-07-16 |
Environmental Conditions: |
|
QAPP Information: |
Generic SWAMP QAPrP |
QAPP Information Reference(s): |
Generic SWAMP QAPrP |
|
Line of Evidence (LOE) for Decision ID 168848, Phosmet
|
Region 1 |
Klamath River HU, Shasta River HA |
|
|
LOE ID: |
350474 |
|
Pollutant: |
Phosmet |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Total |
|
Beneficial Use: |
Cold Freshwater Habitat |
|
Number of Samples: |
3 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP RWB1 Monitoring data for Klamath River HU, Shasta River HA to determine beneficial use support and results are as follows: 0 of 3 samples exceeded the water quality threshold for Phosmet. |
Data Reference: |
Water Quality Assessment Data for the 2018 solicitation cycle submitted through CEDEN for SWAMP RWB1 Monitoring .
|
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
All waters shall be maintained free of toxic substances in concentrations which are toxic to, or which produce detrimental physiological responses in, human, plant, animal, or aquatic life. (Basin Plan). |
Objective/Criterion Reference: |
Water Quality Control Plan (Basin Plan) for the North Coast Region |
|
Evaluation Guideline: |
The evaluation guideline for phosmet is the USEPA Aquatic Life Benchmark of 0.75 ug/L for an invertebrate (chronic). |
Guideline Reference: |
OPP Aquatic Life Benchmarks |
|
Spatial Representation: |
The samples were collected at 1 monitoring site: 105SH9274 (Shasta River near Edgewood). |
Temporal Representation: |
The samples were collected between the dates of 2013-03-07 and 2013-11-20 |
Environmental Conditions: |
|
QAPP Information: |
Generic SWAMP QAPrP |
QAPP Information Reference(s): |
Generic SWAMP QAPrP |
|
Line of Evidence (LOE) for Decision ID 168848, Phosmet
|
Region 1 |
Klamath River HU, Shasta River HA |
|
|
LOE ID: |
350387 |
|
Pollutant: |
Phosmet |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Total |
|
Beneficial Use: |
Cold Freshwater Habitat |
|
Number of Samples: |
3 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed RWB1 Trend Maintenance Periods FYs 2007 2008 data for Klamath River HU, Shasta River HA to determine beneficial use support and results are as follows: 0 of 3 samples exceeded the water quality threshold for Phosmet. |
Data Reference: |
RWB1 Trend Maintenance Periods FYs 2007 2008 |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
All waters shall be maintained free of toxic substances in concentrations which are toxic to, or which produce detrimental physiological responses in, human, plant, animal, or aquatic life. (Basin Plan). |
Objective/Criterion Reference: |
Water Quality Control Plan (Basin Plan) for the North Coast Region |
|
Evaluation Guideline: |
The evaluation guideline for phosmet is the USEPA Aquatic Life Benchmark of 0.75 ug/L for an invertebrate (chronic). |
Guideline Reference: |
OPP Aquatic Life Benchmarks |
|
Spatial Representation: |
The samples were collected at 1 monitoring site: 105SHAEDG (Shasta River near Edgewood). |
Temporal Representation: |
The samples were collected between the dates of 2007-11-15 and 2008-07-16 |
Environmental Conditions: |
|
QAPP Information: |
Generic SWAMP QAPrP |
QAPP Information Reference(s): |
Generic SWAMP QAPrP |
|
Line of Evidence (LOE) for Decision ID 168848, Phosmet
|
Region 1 |
Klamath River HU, Shasta River HA |
|
|
LOE ID: |
350426 |
|
Pollutant: |
Phosmet |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Total |
|
Beneficial Use: |
Cold Freshwater Habitat |
|
Number of Samples: |
3 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed RWB1 Trend Maintenance Periods FYs 2007 2008 data for Klamath River HU, Shasta River HA to determine beneficial use support and results are as follows: 0 of 3 samples exceeded the water quality threshold for Phosmet. |
Data Reference: |
RWB1 Trend Maintenance Periods FYs 2007 2008 |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
All waters shall be maintained free of toxic substances in concentrations which are toxic to, or which produce detrimental physiological responses in, human, plant, animal, or aquatic life. (Basin Plan). |
Objective/Criterion Reference: |
Water Quality Control Plan (Basin Plan) for the North Coast Region |
|
Evaluation Guideline: |
The evaluation guideline for phosmet is the USEPA Aquatic Life Benchmark of 0.75 ug/L for an invertebrate (chronic). |
Guideline Reference: |
OPP Aquatic Life Benchmarks |
|
Spatial Representation: |
The samples were collected at 1 monitoring site: 105SHA263 (Shasta River at Hwy 263). |
Temporal Representation: |
The samples were collected between the dates of 2007-11-15 and 2008-07-16 |
Environmental Conditions: |
|
QAPP Information: |
Generic SWAMP QAPrP |
QAPP Information Reference(s): |
Generic SWAMP QAPrP |
|
Line of Evidence (LOE) for Decision ID 168848, Phosmet
|
Region 1 |
Klamath River HU, Shasta River HA |
|
|
LOE ID: |
350403 |
|
Pollutant: |
Phosmet |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Total |
|
Beneficial Use: |
Warm Freshwater Habitat |
|
Number of Samples: |
3 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP RWB1 Monitoring data for Klamath River HU, Shasta River HA to determine beneficial use support and results are as follows: 0 of 3 samples exceeded the water quality threshold for Phosmet. |
Data Reference: |
Water Quality Assessment Data for the 2018 solicitation cycle submitted through CEDEN for SWAMP RWB1 Monitoring .
|
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
All waters shall be maintained free of toxic substances in concentrations which are toxic to, or which produce detrimental physiological responses in, human, plant, animal, or aquatic life. (Basin Plan). |
Objective/Criterion Reference: |
Water Quality Control Plan (Basin Plan) for the North Coast Region |
|
Evaluation Guideline: |
The evaluation guideline for phosmet is the USEPA Aquatic Life Benchmark of 0.75 ug/L for an invertebrate (chronic). |
Guideline Reference: |
OPP Aquatic Life Benchmarks |
|
Spatial Representation: |
The samples were collected at 1 monitoring site: 105SH9274 (Shasta River near Edgewood). |
Temporal Representation: |
The samples were collected between the dates of 2013-03-07 and 2013-11-20 |
Environmental Conditions: |
|
QAPP Information: |
Generic SWAMP QAPrP |
QAPP Information Reference(s): |
Generic SWAMP QAPrP |
|
Line of Evidence (LOE) for Decision ID 168848, Phosmet
|
Region 1 |
Klamath River HU, Shasta River HA |
|
|
LOE ID: |
350370 |
|
Pollutant: |
Phosmet |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Total |
|
Beneficial Use: |
Cold Freshwater Habitat |
|
Number of Samples: |
3 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP RWB1 Monitoring data for Klamath River HU, Shasta River HA to determine beneficial use support and results are as follows: 0 of 3 samples exceeded the water quality threshold for Phosmet. |
Data Reference: |
Water Quality Assessment Data for the 2018 solicitation cycle submitted through CEDEN for SWAMP RWB1 Monitoring .
|
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
All waters shall be maintained free of toxic substances in concentrations which are toxic to, or which produce detrimental physiological responses in, human, plant, animal, or aquatic life. (Basin Plan). |
Objective/Criterion Reference: |
Water Quality Control Plan (Basin Plan) for the North Coast Region |
|
Evaluation Guideline: |
The evaluation guideline for phosmet is the USEPA Aquatic Life Benchmark of 0.75 ug/L for an invertebrate (chronic). |
Guideline Reference: |
OPP Aquatic Life Benchmarks |
|
Spatial Representation: |
The samples were collected at 1 monitoring site: 105SH1452 (Shasta River at Hwy 263). |
Temporal Representation: |
The samples were collected between the dates of 2013-03-06 and 2013-11-20 |
Environmental Conditions: |
|
QAPP Information: |
Generic SWAMP QAPrP |
QAPP Information Reference(s): |
Generic SWAMP QAPrP |
|
Line of Evidence (LOE) for Decision ID 168848, Phosmet
|
Region 1 |
Klamath River HU, Shasta River HA |
|
|
LOE ID: |
350380 |
|
Pollutant: |
Phosmet |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Total |
|
Beneficial Use: |
Warm Freshwater Habitat |
|
Number of Samples: |
3 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP RWB1 Monitoring data for Klamath River HU, Shasta River HA to determine beneficial use support and results are as follows: 0 of 3 samples exceeded the water quality threshold for Phosmet. |
Data Reference: |
Water Quality Assessment Data for the 2018 solicitation cycle submitted through CEDEN for SWAMP RWB1 Monitoring .
|
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
All waters shall be maintained free of toxic substances in concentrations which are toxic to, or which produce detrimental physiological responses in, human, plant, animal, or aquatic life. (Basin Plan). |
Objective/Criterion Reference: |
Water Quality Control Plan (Basin Plan) for the North Coast Region |
|
Evaluation Guideline: |
The evaluation guideline for phosmet is the USEPA Aquatic Life Benchmark of 0.75 ug/L for an invertebrate (chronic). |
Guideline Reference: |
OPP Aquatic Life Benchmarks |
|
Spatial Representation: |
The samples were collected at 1 monitoring site: 105SH1452 (Shasta River at Hwy 263). |
Temporal Representation: |
The samples were collected between the dates of 2013-03-06 and 2013-11-20 |
Environmental Conditions: |
|
QAPP Information: |
Generic SWAMP QAPrP |
QAPP Information Reference(s): |
Generic SWAMP QAPrP |
|
Line of Evidence (LOE) for Decision ID 168848, Phosmet
|
Region 1 |
Klamath River HU, Shasta River HA |
|
|
LOE ID: |
350397 |
|
Pollutant: |
Phosmet |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Total |
|
Beneficial Use: |
Warm Freshwater Habitat |
|
Number of Samples: |
3 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed RWB1 Trend Maintenance Periods FYs 2007 2008 data for Klamath River HU, Shasta River HA to determine beneficial use support and results are as follows: 0 of 3 samples exceeded the water quality threshold for Phosmet. |
Data Reference: |
RWB1 Trend Maintenance Periods FYs 2007 2008 |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
All waters shall be maintained free of toxic substances in concentrations which are toxic to, or which produce detrimental physiological responses in, human, plant, animal, or aquatic life. (Basin Plan). |
Objective/Criterion Reference: |
Water Quality Control Plan (Basin Plan) for the North Coast Region |
|
Evaluation Guideline: |
The evaluation guideline for phosmet is the USEPA Aquatic Life Benchmark of 0.75 ug/L for an invertebrate (chronic). |
Guideline Reference: |
OPP Aquatic Life Benchmarks |
|
Spatial Representation: |
The samples were collected at 1 monitoring site: 105SHAEDG (Shasta River near Edgewood). |
Temporal Representation: |
The samples were collected between the dates of 2007-11-15 and 2008-07-16 |
Environmental Conditions: |
|
QAPP Information: |
Generic SWAMP QAPrP |
QAPP Information Reference(s): |
Generic SWAMP QAPrP |
|
Line of Evidence (LOE) for Decision ID 168848, Phosmet
|
Region 1 |
Klamath River HU, Shasta River HA |
|
|
LOE ID: |
123510 |
|
Pollutant: |
Phosmet |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
None |
|
Beneficial Use: |
Municipal & Domestic Supply |
|
Number of Samples: |
0 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
State Water Board staff re-assessed SWAMP data for Klamath River HU, Shasta River HA to determine beneficial use support and results are as follows: 0 of 0 samples exceed the criterion for Phosmet, Total. Eight sample results were not used in the assessment because the laboratory data reporting limit(s) was above the objective and therefore the results could not be quantified with the level of certainty required by the Listing Policy. Eight samples were removed from assessment because an appropriate evaluation guideline for the water body-pollutant combination could not be obtained for this listing cycle. This LOE re-assesses data from LOE 29849 from the 2010 Integrated Report. Data were re-assessed in order to evaluate these data in their own LOE, instead of being evaluated in the same LOE as other pesticide data. |
Data Reference: |
Surface Water Ambient Monitoring Program (SWAMP). Summary Report for the North Coast Region (RWQCB-1) for years 2000-2006. North Coast Regional Water Quality Control Board. March 2008 |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
Per the Basin Plan (NCRWQCB 2011): No individual pesticide or combination of pesticides shall be present in concentrations that adversely affect beneficial uses. There shall be no bioaccumulation of pesticide concentrations found in bottom sediments or aquatic life. Waters designated for use as domestic or municipal supply shall not contain concentrations of pesticides in excess of the limiting concentrations set forth in California Code of Regulations, Title 22, Division 4, Chapter 15, Article 4, Section 64444, and listed in Table 3.2 of the Basin Plan. No evaluation guideline could be found to evaluate protection of the MUN beneficial use that meets the requirements of Section 6.1.3 of the Listing Policy. |
Objective/Criterion Reference: |
Water Quality Control Plan (Basin Plan) for the North Coast Region |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
Data for this line of evidence for Klamath River HU, Shasta River HA was collected at 1 monitoring site [ Shasta River at Montague - 105SHAMON] |
Temporal Representation: |
Data was collected over the time period 10/7/2002-6/19/2003. |
Environmental Conditions: |
There are no known environmental conditions (e.g., seasonality, land use practices, fire events, storms, etc.) that are related to these data. |
QAPP Information: |
Quality control was conducted in accordance with the SWAMP Quality Assurance Management Plan (SWAMP 2002). |
QAPP Information Reference(s): |
Quality Assurance Management Plan for the State of California's Surface Water Ambient Monitoring Program. Sacramento, CA. State Water Resources Control Board. SWAMP. December 2002 (1st version)
|
|
Line of Evidence (LOE) for Decision ID 168848, Phosmet
|
Region 1 |
Klamath River HU, Shasta River HA |
|
|
LOE ID: |
123518 |
|
Pollutant: |
Phosmet |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
None |
|
Beneficial Use: |
Municipal & Domestic Supply |
|
Number of Samples: |
0 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
State Water Board staff re-assessed SWAMP data for Klamath River HU, Shasta River HA to determine beneficial use support and results are as follows: 0 of 0 samples exceed the criterion for Phosmet, Total. Sixteen sample results were not used in the assessment because the laboratory data reporting limit(s) was above the objective and therefore the results could not be quantified with the level of certainty required by the Listing Policy. Sixteen samples were removed from assessment because an appropriate evaluation guideline for the water body-pollutant combination could not be obtained for this listing cycle. This LOE re-assesses data from LOE 29849 from the 2010 Integrated Report. Data were re-assessed in order to evaluate these data in their own LOE, instead of being evaluated in the same LOE as other pesticide data. |
Data Reference: |
Surface Water Ambient Monitoring Program (SWAMP). Summary Report for the North Coast Region (RWQCB-1) for years 2000-2006. North Coast Regional Water Quality Control Board. March 2008 |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
Per the Basin Plan (NCRWQCB 2011): No individual pesticide or combination of pesticides shall be present in concentrations that adversely affect beneficial uses. There shall be no bioaccumulation of pesticide concentrations found in bottom sediments or aquatic life. Waters designated for use as domestic or municipal supply shall not contain concentrations of pesticides in excess of the limiting concentrations set forth in California Code of Regulations, Title 22, Division 4, Chapter 15, Article 4, Section 64444, and listed in Table 3.2 of the Basin Plan. No evaluation guideline could be found to evaluate protection of the MUN beneficial use that meets the requirements of Section 6.1.3 of the Listing Policy. |
Objective/Criterion Reference: |
Water Quality Control Plan (Basin Plan) for the North Coast Region |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
Data for this line of evidence for Klamath River HU, Shasta River HA was collected at 1 monitoring site [ Yreka Creek at Anderson Rd - 105YREAND] |
Temporal Representation: |
Data was collected over the time period 10/9/2002-6/20/2005. |
Environmental Conditions: |
There are no known environmental conditions (e.g., seasonality, land use practices, fire events, storms, etc.) that are related to these data. |
QAPP Information: |
Quality control was conducted in accordance with the SWAMP Quality Assurance Management Plan (SWAMP 2002). |
QAPP Information Reference(s): |
Quality Assurance Management Plan for the State of California's Surface Water Ambient Monitoring Program. Sacramento, CA. State Water Resources Control Board. SWAMP. December 2002 (1st version)
|
|
Line of Evidence (LOE) for Decision ID 168848, Phosmet
|
Region 1 |
Klamath River HU, Shasta River HA |
|
|
LOE ID: |
123517 |
|
Pollutant: |
Phosmet |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
None |
|
Beneficial Use: |
Municipal & Domestic Supply |
|
Number of Samples: |
0 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
State Water Board staff re-assessed SWAMP data for Klamath River HU, Shasta River HA to determine beneficial use support and results are as follows: 0 of 0 samples exceed the criterion for Phosmet, Total. Eight sample results were not used in the assessment because the laboratory data reporting limit(s) was above the objective and therefore the results could not be quantified with the level of certainty required by the Listing Policy. Eight samples were removed from assessment because an appropriate evaluation guideline for the water body-pollutant combination could not be obtained for this listing cycle. This LOE re-assesses data from LOE 29849 from the 2010 Integrated Report. Data were re-assessed in order to evaluate these data in their own LOE, instead of being evaluated in the same LOE as other pesticide data. |
Data Reference: |
Surface Water Ambient Monitoring Program (SWAMP). Summary Report for the North Coast Region (RWQCB-1) for years 2000-2006. North Coast Regional Water Quality Control Board. March 2008 |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
Per the Basin Plan (NCRWQCB 2011): No individual pesticide or combination of pesticides shall be present in concentrations that adversely affect beneficial uses. There shall be no bioaccumulation of pesticide concentrations found in bottom sediments or aquatic life. Waters designated for use as domestic or municipal supply shall not contain concentrations of pesticides in excess of the limiting concentrations set forth in California Code of Regulations, Title 22, Division 4, Chapter 15, Article 4, Section 64444, and listed in Table 3.2 of the Basin Plan. No evaluation guideline could be found to evaluate protection of the MUN beneficial use that meets the requirements of Section 6.1.3 of the Listing Policy. |
Objective/Criterion Reference: |
Water Quality Control Plan (Basin Plan) for the North Coast Region |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
Data for this line of evidence for Klamath River HU, Shasta River HA was collected at 1 monitoring site [ Shasta River near Edgewood - 105SH9274] |
Temporal Representation: |
Data was collected over the time period 10/7/2002-6/19/2003. |
Environmental Conditions: |
There are no known environmental conditions (e.g., seasonality, land use practices, fire events, storms, etc.) that are related to these data. |
QAPP Information: |
Quality control was conducted in accordance with the SWAMP Quality Assurance Management Plan (SWAMP 2002). |
QAPP Information Reference(s): |
Quality Assurance Management Plan for the State of California's Surface Water Ambient Monitoring Program. Sacramento, CA. State Water Resources Control Board. SWAMP. December 2002 (1st version)
|
|
Line of Evidence (LOE) for Decision ID 168848, Phosmet
|
Region 1 |
Klamath River HU, Shasta River HA |
|
|
LOE ID: |
123519 |
|
Pollutant: |
Phosmet |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
None |
|
Beneficial Use: |
Municipal & Domestic Supply |
|
Number of Samples: |
0 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
State Water Board staff re-assessed SWAMP data for Klamath River HU, Shasta River HA to determine beneficial use support and results are as follows: 0 of 0 samples exceed the criterion for Phosmet, Total. Eight sample results were not used in the assessment because the laboratory data reporting limit(s) was above the objective and therefore the results could not be quantified with the level of certainty required by the Listing Policy. Eight samples were removed from assessment because an appropriate evaluation guideline for the water body-pollutant combination could not be obtained for this listing cycle. This LOE re-assesses data from LOE 29849 from the 2010 Integrated Report. Data were re-assessed in order to evaluate these data in their own LOE, instead of being evaluated in the same LOE as other pesticide data. |
Data Reference: |
Surface Water Ambient Monitoring Program (SWAMP). Summary Report for the North Coast Region (RWQCB-1) for years 2000-2006. North Coast Regional Water Quality Control Board. March 2008 |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
Per the Basin Plan (NCRWQCB 2011): No individual pesticide or combination of pesticides shall be present in concentrations that adversely affect beneficial uses. There shall be no bioaccumulation of pesticide concentrations found in bottom sediments or aquatic life. Waters designated for use as domestic or municipal supply shall not contain concentrations of pesticides in excess of the limiting concentrations set forth in California Code of Regulations, Title 22, Division 4, Chapter 15, Article 4, Section 64444, and listed in Table 3.2 of the Basin Plan. No evaluation guideline could be found to evaluate protection of the MUN beneficial use that meets the requirements of Section 6.1.3 of the Listing Policy. |
Objective/Criterion Reference: |
Water Quality Control Plan (Basin Plan) for the North Coast Region |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
Data for this line of evidence for Klamath River HU, Shasta River HA was collected at 1 monitoring site [ Yreka Creek at Highway 3 - 105YREHW3] |
Temporal Representation: |
Data was collected over the time period 10/21/2004-6/20/2005. |
Environmental Conditions: |
There are no known environmental conditions (e.g., seasonality, land use practices, fire events, storms, etc.) that are related to these data. |
QAPP Information: |
Quality control was conducted in accordance with the SWAMP Quality Assurance Management Plan (SWAMP 2002). |
QAPP Information Reference(s): |
Quality Assurance Management Plan for the State of California's Surface Water Ambient Monitoring Program. Sacramento, CA. State Water Resources Control Board. SWAMP. December 2002 (1st version)
|
|
Line of Evidence (LOE) for Decision ID 168848, Phosmet
|
Region 1 |
Klamath River HU, Shasta River HA |
|
|
LOE ID: |
123509 |
|
Pollutant: |
Phosmet |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
None |
|
Beneficial Use: |
Municipal & Domestic Supply |
|
Number of Samples: |
0 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
State Water Board staff re-assessed SWAMP data for Klamath River HU, Shasta River HA to determine beneficial use support and results are as follows: 0 of 0 samples exceed the criterion for Phosmet, Total. Thirty-two sample results were not used in the assessment because the laboratory data reporting limit(s) was above the objective and therefore the results could not be quantified with the level of certainty required by the Listing Policy. Thirty-two samples were removed from assessment because an appropriate evaluation guideline for the water body-pollutant combination could not be obtained for this listing cycle. This LOE re-assesses data from LOE 29849 from the 2010 Integrated Report. Data were re-assessed in order to evaluate these data in their own LOE, instead of being evaluated in the same LOE as other pesticide data. |
Data Reference: |
Surface Water Ambient Monitoring Program (SWAMP). Summary Report for the North Coast Region (RWQCB-1) for years 2000-2006. North Coast Regional Water Quality Control Board. March 2008 |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
Per the Basin Plan (NCRWQCB 2011): No individual pesticide or combination of pesticides shall be present in concentrations that adversely affect beneficial uses. There shall be no bioaccumulation of pesticide concentrations found in bottom sediments or aquatic life. Waters designated for use as domestic or municipal supply shall not contain concentrations of pesticides in excess of the limiting concentrations set forth in California Code of Regulations, Title 22, Division 4, Chapter 15, Article 4, Section 64444, and listed in Table 3.2 of the Basin Plan. No evaluation guideline could be found to evaluate protection of the MUN beneficial use that meets the requirements of Section 6.1.3 of the Listing Policy. |
Objective/Criterion Reference: |
Water Quality Control Plan (Basin Plan) for the North Coast Region |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
Data for this line of evidence for Klamath River HU, Shasta River HA was collected at 1 monitoring site [ Shasta River at Hwy 263 - 105SH1452] |
Temporal Representation: |
Data was collected over the time period 2/27/2002-11/16/2006. |
Environmental Conditions: |
There are no known environmental conditions (e.g., seasonality, land use practices, fire events, storms, etc.) that are related to these data. |
QAPP Information: |
Quality control was conducted in accordance with the SWAMP Quality Assurance Management Plan (SWAMP 2002). |
QAPP Information Reference(s): |
Quality Assurance Management Plan for the State of California's Surface Water Ambient Monitoring Program. Sacramento, CA. State Water Resources Control Board. SWAMP. December 2002 (1st version)
|
|
Line of Evidence (LOE) for Decision ID 168848, Phosmet
|
Region 1 |
Klamath River HU, Shasta River HA |
|
|
LOE ID: |
350402 |
|
Pollutant: |
Phosmet |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Total |
|
Beneficial Use: |
Warm Freshwater Habitat |
|
Number of Samples: |
3 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed RWB1 Trend Maintenance Periods FYs 2007 2008 data for Klamath River HU, Shasta River HA to determine beneficial use support and results are as follows: 0 of 3 samples exceeded the water quality threshold for Phosmet. |
Data Reference: |
RWB1 Trend Maintenance Periods FYs 2007 2008 |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
All waters shall be maintained free of toxic substances in concentrations which are toxic to, or which produce detrimental physiological responses in, human, plant, animal, or aquatic life. (Basin Plan). |
Objective/Criterion Reference: |
Water Quality Control Plan (Basin Plan) for the North Coast Region |
|
Evaluation Guideline: |
The evaluation guideline for phosmet is the USEPA Aquatic Life Benchmark of 0.75 ug/L for an invertebrate (chronic). |
Guideline Reference: |
OPP Aquatic Life Benchmarks |
|
Spatial Representation: |
The samples were collected at 1 monitoring site: 105SHA263 (Shasta River at Hwy 263). |
Temporal Representation: |
The samples were collected between the dates of 2007-11-15 and 2008-07-16 |
Environmental Conditions: |
|
QAPP Information: |
Generic SWAMP QAPrP |
QAPP Information Reference(s): |
Generic SWAMP QAPrP |
|
Line of Evidence (LOE) for Decision ID 169749, Prometon (Prometone)
|
Region 1 |
Klamath River HU, Shasta River HA |
|
|
LOE ID: |
350522 |
|
Pollutant: |
Prometon (Prometone) |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Total |
|
Beneficial Use: |
Warm Freshwater Habitat |
|
Number of Samples: |
3 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed RWB1 Trend Maintenance Periods FYs 2007 2008 data for Klamath River HU, Shasta River HA to determine beneficial use support and results are as follows: 0 of 3 samples exceeded the water quality threshold for Prometon. |
Data Reference: |
RWB1 Trend Maintenance Periods FYs 2007 2008 |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
All waters shall be maintained free of toxic substances in concentrations which are toxic to, or which produce detrimental physiological responses in, human, plant, animal, or aquatic life. (Basin Plan). |
Objective/Criterion Reference: |
Water Quality Control Plan (Basin Plan) for the North Coast Region |
|
Evaluation Guideline: |
The evaluation guideline for prometon (prometone) is the USEPA Aquatic Life Benchmark of 98 ug/L for a nonvascular plant (acute). |
Guideline Reference: |
OPP Aquatic Life Benchmarks |
|
Spatial Representation: |
The samples were collected at 1 monitoring site: 105SHA263 (Shasta River at Hwy 263). |
Temporal Representation: |
The samples were collected between the dates of 2007-11-15 and 2008-07-16 |
Environmental Conditions: |
|
QAPP Information: |
Generic SWAMP QAPrP |
QAPP Information Reference(s): |
Generic SWAMP QAPrP |
|
Line of Evidence (LOE) for Decision ID 169749, Prometon (Prometone)
|
Region 1 |
Klamath River HU, Shasta River HA |
|
|
LOE ID: |
350531 |
|
Pollutant: |
Prometon (Prometone) |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Total |
|
Beneficial Use: |
Cold Freshwater Habitat |
|
Number of Samples: |
3 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed RWB1 Trend Maintenance Periods FYs 2007 2008 data for Klamath River HU, Shasta River HA to determine beneficial use support and results are as follows: 0 of 3 samples exceeded the water quality threshold for Prometon. |
Data Reference: |
RWB1 Trend Maintenance Periods FYs 2007 2008 |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
All waters shall be maintained free of toxic substances in concentrations which are toxic to, or which produce detrimental physiological responses in, human, plant, animal, or aquatic life. (Basin Plan). |
Objective/Criterion Reference: |
Water Quality Control Plan (Basin Plan) for the North Coast Region |
|
Evaluation Guideline: |
The evaluation guideline for prometon (prometone) is the USEPA Aquatic Life Benchmark of 98 ug/L for a nonvascular plant (acute). |
Guideline Reference: |
OPP Aquatic Life Benchmarks |
|
Spatial Representation: |
The samples were collected at 1 monitoring site: 105SHAEDG (Shasta River near Edgewood). |
Temporal Representation: |
The samples were collected between the dates of 2007-11-15 and 2008-07-16 |
Environmental Conditions: |
|
QAPP Information: |
Generic SWAMP QAPrP |
QAPP Information Reference(s): |
Generic SWAMP QAPrP |
|
Line of Evidence (LOE) for Decision ID 169749, Prometon (Prometone)
|
Region 1 |
Klamath River HU, Shasta River HA |
|
|
LOE ID: |
350525 |
|
Pollutant: |
Prometon (Prometone) |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Total |
|
Beneficial Use: |
Cold Freshwater Habitat |
|
Number of Samples: |
3 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed RWB1 Trend Maintenance Periods FYs 2007 2008 data for Klamath River HU, Shasta River HA to determine beneficial use support and results are as follows: 0 of 3 samples exceeded the water quality threshold for Prometon. |
Data Reference: |
RWB1 Trend Maintenance Periods FYs 2007 2008 |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
All waters shall be maintained free of toxic substances in concentrations which are toxic to, or which produce detrimental physiological responses in, human, plant, animal, or aquatic life. (Basin Plan). |
Objective/Criterion Reference: |
Water Quality Control Plan (Basin Plan) for the North Coast Region |
|
Evaluation Guideline: |
The evaluation guideline for prometon (prometone) is the USEPA Aquatic Life Benchmark of 98 ug/L for a nonvascular plant (acute). |
Guideline Reference: |
OPP Aquatic Life Benchmarks |
|
Spatial Representation: |
The samples were collected at 1 monitoring site: 105SHA263 (Shasta River at Hwy 263). |
Temporal Representation: |
The samples were collected between the dates of 2007-11-15 and 2008-07-16 |
Environmental Conditions: |
|
QAPP Information: |
Generic SWAMP QAPrP |
QAPP Information Reference(s): |
Generic SWAMP QAPrP |
|
Line of Evidence (LOE) for Decision ID 169749, Prometon (Prometone)
|
Region 1 |
Klamath River HU, Shasta River HA |
|
|
LOE ID: |
350513 |
|
Pollutant: |
Prometon (Prometone) |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Total |
|
Beneficial Use: |
Warm Freshwater Habitat |
|
Number of Samples: |
3 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed RWB1 Trend Maintenance Periods FYs 2007 2008 data for Klamath River HU, Shasta River HA to determine beneficial use support and results are as follows: 0 of 3 samples exceeded the water quality threshold for Prometon. |
Data Reference: |
RWB1 Trend Maintenance Periods FYs 2007 2008 |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
All waters shall be maintained free of toxic substances in concentrations which are toxic to, or which produce detrimental physiological responses in, human, plant, animal, or aquatic life. (Basin Plan). |
Objective/Criterion Reference: |
Water Quality Control Plan (Basin Plan) for the North Coast Region |
|
Evaluation Guideline: |
The evaluation guideline for prometon (prometone) is the USEPA Aquatic Life Benchmark of 98 ug/L for a nonvascular plant (acute). |
Guideline Reference: |
OPP Aquatic Life Benchmarks |
|
Spatial Representation: |
The samples were collected at 1 monitoring site: 105SHAEDG (Shasta River near Edgewood). |
Temporal Representation: |
The samples were collected between the dates of 2007-11-15 and 2008-07-16 |
Environmental Conditions: |
|
QAPP Information: |
Generic SWAMP QAPrP |
QAPP Information Reference(s): |
Generic SWAMP QAPrP |
|
Line of Evidence (LOE) for Decision ID 169749, Prometon (Prometone)
|
Region 1 |
Klamath River HU, Shasta River HA |
|
|
LOE ID: |
105158 |
|
Pollutant: |
Prometon (Prometone) |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Total |
|
Beneficial Use: |
Warm Freshwater Habitat |
|
Number of Samples: |
3 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP RWB1 Monitoring data for Klamath River HU, Shasta River HA to determine beneficial use support and results are as follows: 0 of 3 samples exceeded the water quality standard for Prometon. |
Data Reference: |
Water Quality Assessment Data for the 2018 solicitation cycle submitted through CEDEN for SWAMP RWB1 Monitoring .
|
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
All waters shall be maintained free of toxic substances in concentrations which are toxic to, or which produce detrimental physiological responses in, human, plant, animal, or aquatic life. (Basin Plan). |
Objective/Criterion Reference: |
Water Quality Control Plan (Basin Plan) for the North Coast Region |
|
Evaluation Guideline: |
The evaluation guideline for Prometon is the USEPA Aquatic Life Benchmark of 98 ug/L for a nonvascular plant (acute). |
Guideline Reference: |
OPP Aquatic Life Benchmarks |
|
Spatial Representation: |
The samples were collected at 1 monitoring site(s) (105SH9274) |
Temporal Representation: |
The samples were collected between the dates of 2013-03-07 and 2013-11-20 |
Environmental Conditions: |
|
QAPP Information: |
Quality Assurance Program Plan and Standard Operating Procedures for SWAMP program |
QAPP Information Reference(s): |
Quality Assurance Program Plans, Quality Assurance Project Plans, and Standard Operating Procedures for the SWAMP program |
|
Line of Evidence (LOE) for Decision ID 169749, Prometon (Prometone)
|
Region 1 |
Klamath River HU, Shasta River HA |
|
|
LOE ID: |
105156 |
|
Pollutant: |
Prometon (Prometone) |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Total |
|
Beneficial Use: |
Warm Freshwater Habitat |
|
Number of Samples: |
3 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP RWB1 Monitoring data for Klamath River HU, Shasta River HA to determine beneficial use support and results are as follows: 0 of 3 samples exceeded the water quality standard for Prometon. |
Data Reference: |
Water Quality Assessment Data for the 2018 solicitation cycle submitted through CEDEN for SWAMP RWB1 Monitoring .
|
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
All waters shall be maintained free of toxic substances in concentrations which are toxic to, or which produce detrimental physiological responses in, human, plant, animal, or aquatic life. (Basin Plan). |
Objective/Criterion Reference: |
Water Quality Control Plan (Basin Plan) for the North Coast Region |
|
Evaluation Guideline: |
The evaluation guideline for Prometon is the USEPA Aquatic Life Benchmark of 98 ug/L for a nonvascular plant (acute). |
Guideline Reference: |
OPP Aquatic Life Benchmarks |
|
Spatial Representation: |
The samples were collected at 1 monitoring site(s) (105SH1452) |
Temporal Representation: |
The samples were collected between the dates of 2013-03-06 and 2013-11-20 |
Environmental Conditions: |
|
QAPP Information: |
Quality Assurance Program Plan and Standard Operating Procedures for SWAMP program |
QAPP Information Reference(s): |
Quality Assurance Program Plans, Quality Assurance Project Plans, and Standard Operating Procedures for the SWAMP program |
|
Line of Evidence (LOE) for Decision ID 169749, Prometon (Prometone)
|
Region 1 |
Klamath River HU, Shasta River HA |
|
|
LOE ID: |
105157 |
|
Pollutant: |
Prometon (Prometone) |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Total |
|
Beneficial Use: |
Cold Freshwater Habitat |
|
Number of Samples: |
3 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP RWB1 Monitoring data for Klamath River HU, Shasta River HA to determine beneficial use support and results are as follows: 0 of 3 samples exceeded the water quality standard for Prometon. |
Data Reference: |
Water Quality Assessment Data for the 2018 solicitation cycle submitted through CEDEN for SWAMP RWB1 Monitoring .
|
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
All waters shall be maintained free of toxic substances in concentrations which are toxic to, or which produce detrimental physiological responses in, human, plant, animal, or aquatic life. (Basin Plan). |
Objective/Criterion Reference: |
Water Quality Control Plan (Basin Plan) for the North Coast Region |
|
Evaluation Guideline: |
The evaluation guideline for Prometon is the USEPA Aquatic Life Benchmark of 98 ug/L for a nonvascular plant (acute). |
Guideline Reference: |
OPP Aquatic Life Benchmarks |
|
Spatial Representation: |
The samples were collected at 1 monitoring site(s) (105SH9274) |
Temporal Representation: |
The samples were collected between the dates of 2013-03-07 and 2013-11-20 |
Environmental Conditions: |
|
QAPP Information: |
Quality Assurance Program Plan and Standard Operating Procedures for SWAMP program |
QAPP Information Reference(s): |
Quality Assurance Program Plans, Quality Assurance Project Plans, and Standard Operating Procedures for the SWAMP program |
|
Line of Evidence (LOE) for Decision ID 169749, Prometon (Prometone)
|
Region 1 |
Klamath River HU, Shasta River HA |
|
|
LOE ID: |
105155 |
|
Pollutant: |
Prometon (Prometone) |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Total |
|
Beneficial Use: |
Cold Freshwater Habitat |
|
Number of Samples: |
3 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP RWB1 Monitoring data for Klamath River HU, Shasta River HA to determine beneficial use support and results are as follows: 0 of 3 samples exceeded the water quality standard for Prometon. |
Data Reference: |
Water Quality Assessment Data for the 2018 solicitation cycle submitted through CEDEN for SWAMP RWB1 Monitoring .
|
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
All waters shall be maintained free of toxic substances in concentrations which are toxic to, or which produce detrimental physiological responses in, human, plant, animal, or aquatic life. (Basin Plan). |
Objective/Criterion Reference: |
Water Quality Control Plan (Basin Plan) for the North Coast Region |
|
Evaluation Guideline: |
The evaluation guideline for Prometon is the USEPA Aquatic Life Benchmark of 98 ug/L for a nonvascular plant (acute). |
Guideline Reference: |
OPP Aquatic Life Benchmarks |
|
Spatial Representation: |
The samples were collected at 1 monitoring site(s) (105SH1452) |
Temporal Representation: |
The samples were collected between the dates of 2013-03-06 and 2013-11-20 |
Environmental Conditions: |
|
QAPP Information: |
Quality Assurance Program Plan and Standard Operating Procedures for SWAMP program |
QAPP Information Reference(s): |
Quality Assurance Program Plans, Quality Assurance Project Plans, and Standard Operating Procedures for the SWAMP program |
|
Line of Evidence (LOE) for Decision ID 169749, Prometon (Prometone)
|
Region 1 |
Klamath River HU, Shasta River HA |
|
|
LOE ID: |
123528 |
|
Pollutant: |
Prometon (Prometone) |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
None |
|
Beneficial Use: |
Municipal & Domestic Supply |
|
Number of Samples: |
0 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
State Water Board staff re-assessed SWAMP data for Klamath River HU, Shasta River HA to determine beneficial use support and results are as follows: 0 of 0 samples exceed the criterion for Prometon, Total. Eight sample results were not used in the assessment because the laboratory data reporting limit(s) was above the objective and therefore the results could not be quantified with the level of certainty required by the Listing Policy. This LOE re-assesses data from LOE 29849 from the 2010 Integrated Report. Data were re-assessed in order to evaluate these data in their own LOE, instead of being evaluated in the same LOE as other pesticide data. |
Data Reference: |
Surface Water Ambient Monitoring Program (SWAMP). Summary Report for the North Coast Region (RWQCB-1) for years 2000-2006. North Coast Regional Water Quality Control Board. March 2008 |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
Per the Basin Plan (NCRWQCB 2011): No individual pesticide or combination of pesticides shall be present in concentrations that adversely affect beneficial uses. There shall be no bioaccumulation of pesticide concentrations found in bottom sediments or aquatic life. Waters designated for use as domestic or municipal supply shall not contain concentrations of pesticides in excess of the limiting concentrations set forth in California Code of Regulations, Title 22, Division 4, Chapter 15, Article 4, Section 64444, and listed in Table 3.2 of the Basin Plan. |
Objective/Criterion Reference: |
Water Quality Control Plan (Basin Plan) for the North Coast Region |
|
Evaluation Guideline: |
According to the 2006 USEPA Drinking Water Standards and Health Advisories, the Life-time Exposure Health Advisory for Prometon (Prometone) is 0.1 mg/L. (EPA 822-R-06-013, 2006) |
Guideline Reference: |
2006 edition of the drinking water standards and health advisories. EPA 822-R-03-013 |
|
Spatial Representation: |
Data for this line of evidence for Klamath River HU, Shasta River HA was collected at 1 monitoring site [ Shasta River at Montague - 105SHAMON] |
Temporal Representation: |
Data was collected over the time period 10/7/2002-6/19/2003. |
Environmental Conditions: |
There are no known environmental conditions (e.g., seasonality, land use practices, fire events, storms, etc.) that are related to these data. |
QAPP Information: |
Quality control was conducted in accordance with the SWAMP Quality Assurance Management Plan (SWAMP 2002). |
QAPP Information Reference(s): |
Quality Assurance Management Plan for the State of California's Surface Water Ambient Monitoring Program. Sacramento, CA. State Water Resources Control Board. SWAMP. December 2002 (1st version)
|
|
Line of Evidence (LOE) for Decision ID 169749, Prometon (Prometone)
|
Region 1 |
Klamath River HU, Shasta River HA |
|
|
LOE ID: |
123527 |
|
Pollutant: |
Prometon (Prometone) |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
None |
|
Beneficial Use: |
Municipal & Domestic Supply |
|
Number of Samples: |
13 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
State Water Board staff re-assessed SWAMP data for Klamath River HU, Shasta River HA to determine beneficial use support and results are as follows: 0 of 13 samples exceed the criterion for Prometon, Total. This LOE re-assesses data from LOE 29849 from the 2010 Integrated Report. Data were re-assessed in order to evaluate these data in their own LOE, instead of being evaluated in the same LOE as other pesticide data. |
Data Reference: |
Surface Water Ambient Monitoring Program (SWAMP). Summary Report for the North Coast Region (RWQCB-1) for years 2000-2006. North Coast Regional Water Quality Control Board. March 2008 |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
Per the Basin Plan (NCRWQCB 2011): No individual pesticide or combination of pesticides shall be present in concentrations that adversely affect beneficial uses. There shall be no bioaccumulation of pesticide concentrations found in bottom sediments or aquatic life. Waters designated for use as domestic or municipal supply shall not contain concentrations of pesticides in excess of the limiting concentrations set forth in California Code of Regulations, Title 22, Division 4, Chapter 15, Article 4, Section 64444, and listed in Table 3.2 of the Basin Plan. |
Objective/Criterion Reference: |
Water Quality Control Plan (Basin Plan) for the North Coast Region |
|
Evaluation Guideline: |
According to the 2006 USEPA Drinking Water Standards and Health Advisories, the Life-time Exposure Health Advisory for Prometon (Prometone) is 0.1 mg/L. (EPA 822-R-06-013, 2006) |
Guideline Reference: |
2006 edition of the drinking water standards and health advisories. EPA 822-R-03-013 |
|
Spatial Representation: |
Data for this line of evidence for Klamath River HU, Shasta River HA was collected at 1 monitoring site [ Shasta River at Hwy 263 - 105SH1452] |
Temporal Representation: |
Data was collected over the time period 4/24/2001-11/16/2006. |
Environmental Conditions: |
There are no known environmental conditions (e.g., seasonality, land use practices, fire events, storms, etc.) that are related to these data. |
QAPP Information: |
Quality control was conducted in accordance with the SWAMP Quality Assurance Management Plan (SWAMP 2002). |
QAPP Information Reference(s): |
Quality Assurance Management Plan for the State of California's Surface Water Ambient Monitoring Program. Sacramento, CA. State Water Resources Control Board. SWAMP. December 2002 (1st version)
|
|
Line of Evidence (LOE) for Decision ID 169749, Prometon (Prometone)
|
Region 1 |
Klamath River HU, Shasta River HA |
|
|
LOE ID: |
123529 |
|
Pollutant: |
Prometon (Prometone) |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
None |
|
Beneficial Use: |
Municipal & Domestic Supply |
|
Number of Samples: |
0 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
State Water Board staff re-assessed SWAMP data for Klamath River HU, Shasta River HA to determine beneficial use support and results are as follows: 0 of 0 samples exceed the criterion for Prometon, Total. Eight sample results were not used in the assessment because the laboratory data reporting limit(s) was above the objective and therefore the results could not be quantified with the level of certainty required by the Listing Policy. This LOE re-assesses data from LOE 29849 from the 2010 Integrated Report. Data were re-assessed in order to evaluate these data in their own LOE, instead of being evaluated in the same LOE as other pesticide data. |
Data Reference: |
Surface Water Ambient Monitoring Program (SWAMP). Summary Report for the North Coast Region (RWQCB-1) for years 2000-2006. North Coast Regional Water Quality Control Board. March 2008 |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
Per the Basin Plan (NCRWQCB 2011): No individual pesticide or combination of pesticides shall be present in concentrations that adversely affect beneficial uses. There shall be no bioaccumulation of pesticide concentrations found in bottom sediments or aquatic life. Waters designated for use as domestic or municipal supply shall not contain concentrations of pesticides in excess of the limiting concentrations set forth in California Code of Regulations, Title 22, Division 4, Chapter 15, Article 4, Section 64444, and listed in Table 3.2 of the Basin Plan. |
Objective/Criterion Reference: |
Water Quality Control Plan (Basin Plan) for the North Coast Region |
|
Evaluation Guideline: |
According to the 2006 USEPA Drinking Water Standards and Health Advisories, the Life-time Exposure Health Advisory for Prometon (Prometone) is 0.1 mg/L. (EPA 822-R-06-013, 2006) |
Guideline Reference: |
2006 edition of the drinking water standards and health advisories. EPA 822-R-03-013 |
|
Spatial Representation: |
Data for this line of evidence for Klamath River HU, Shasta River HA was collected at 1 monitoring site [ Shasta River near Edgewood - 105SH9274] |
Temporal Representation: |
Data was collected over the time period 10/7/2002-6/19/2003. |
Environmental Conditions: |
There are no known environmental conditions (e.g., seasonality, land use practices, fire events, storms, etc.) that are related to these data. |
QAPP Information: |
Quality control was conducted in accordance with the SWAMP Quality Assurance Management Plan (SWAMP 2002). |
QAPP Information Reference(s): |
Quality Assurance Management Plan for the State of California's Surface Water Ambient Monitoring Program. Sacramento, CA. State Water Resources Control Board. SWAMP. December 2002 (1st version)
|
|
Line of Evidence (LOE) for Decision ID 169749, Prometon (Prometone)
|
Region 1 |
Klamath River HU, Shasta River HA |
|
|
LOE ID: |
123373 |
|
Pollutant: |
Prometon (Prometone) |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
None |
|
Beneficial Use: |
Municipal & Domestic Supply |
|
Number of Samples: |
0 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
State Water Board staff re-assessed SWAMP data for Klamath River HU, Shasta River HA to determine beneficial use support and results are as follows: 0 of 0 samples exceed the criterion for Prometon, Total. Eight sample results were not used in the assessment because the laboratory data reporting limit(s) was above the objective and therefore the results could not be quantified with the level of certainty required by the Listing Policy. This LOE re-assesses data from LOE 29849 from the 2010 Integrated Report. Data were re-assessed in order to evaluate these data in their own LOE, instead of being evaluated in the same LOE as other pesticide data. |
Data Reference: |
Surface Water Ambient Monitoring Program (SWAMP). Summary Report for the North Coast Region (RWQCB-1) for years 2000-2006. North Coast Regional Water Quality Control Board. March 2008 |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
Per the Basin Plan (NCRWQCB 2011): No individual pesticide or combination of pesticides shall be present in concentrations that adversely affect beneficial uses. There shall be no bioaccumulation of pesticide concentrations found in bottom sediments or aquatic life. Waters designated for use as domestic or municipal supply shall not contain concentrations of pesticides in excess of the limiting concentrations set forth in California Code of Regulations, Title 22, Division 4, Chapter 15, Article 4, Section 64444, and listed in Table 3.2 of the Basin Plan. |
Objective/Criterion Reference: |
Water Quality Control Plan (Basin Plan) for the North Coast Region |
|
Evaluation Guideline: |
According to the 2006 USEPA Drinking Water Standards and Health Advisories, the Life-time Exposure Health Advisory for Prometon (Prometone) is 0.1 mg/L. (EPA 822-R-06-013, 2006) |
Guideline Reference: |
2006 edition of the drinking water standards and health advisories. EPA 822-R-03-013 |
|
Spatial Representation: |
Data for this line of evidence for Klamath River HU, Shasta River HA was collected at 1 monitoring site [ Yreka Creek at Highway 3 - 105YREHW3] |
Temporal Representation: |
Data was collected over the time period 10/21/2004-6/20/2005. |
Environmental Conditions: |
There are no known environmental conditions (e.g., seasonality, land use practices, fire events, storms, etc.) that are related to these data. |
QAPP Information: |
Quality control was conducted in accordance with the SWAMP Quality Assurance Management Plan (SWAMP 2002). |
QAPP Information Reference(s): |
Quality Assurance Management Plan for the State of California's Surface Water Ambient Monitoring Program. Sacramento, CA. State Water Resources Control Board. SWAMP. December 2002 (1st version)
|
|
Line of Evidence (LOE) for Decision ID 169749, Prometon (Prometone)
|
Region 1 |
Klamath River HU, Shasta River HA |
|
|
LOE ID: |
123372 |
|
Pollutant: |
Prometon (Prometone) |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
None |
|
Beneficial Use: |
Municipal & Domestic Supply |
|
Number of Samples: |
0 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
State Water Board staff re-assessed SWAMP data for Klamath River HU, Shasta River HA to determine beneficial use support and results are as follows: 0 of 0 samples exceed the criterion for Prometon, Total. Sixteen sample results were not used in the assessment because the laboratory data reporting limit(s) was above the objective and therefore the results could not be quantified with the level of certainty required by the Listing Policy. This LOE re-assesses data from LOE 29849 from the 2010 Integrated Report. Data were re-assessed in order to evaluate these data in their own LOE, instead of being evaluated in the same LOE as other pesticide data. |
Data Reference: |
Surface Water Ambient Monitoring Program (SWAMP). Summary Report for the North Coast Region (RWQCB-1) for years 2000-2006. North Coast Regional Water Quality Control Board. March 2008 |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
Per the Basin Plan (NCRWQCB 2011): No individual pesticide or combination of pesticides shall be present in concentrations that adversely affect beneficial uses. There shall be no bioaccumulation of pesticide concentrations found in bottom sediments or aquatic life. Waters designated for use as domestic or municipal supply shall not contain concentrations of pesticides in excess of the limiting concentrations set forth in California Code of Regulations, Title 22, Division 4, Chapter 15, Article 4, Section 64444, and listed in Table 3.2 of the Basin Plan. |
Objective/Criterion Reference: |
Water Quality Control Plan (Basin Plan) for the North Coast Region |
|
Evaluation Guideline: |
According to the 2006 USEPA Drinking Water Standards and Health Advisories, the Life-time Exposure Health Advisory for Prometon (Prometone) is 0.1 mg/L. (EPA 822-R-06-013, 2006) |
Guideline Reference: |
2006 edition of the drinking water standards and health advisories. EPA 822-R-03-013 |
|
Spatial Representation: |
Data for this line of evidence for Klamath River HU, Shasta River HA was collected at 1 monitoring site [ Yreka Creek at Anderson Rd - 105YREAND] |
Temporal Representation: |
Data was collected over the time period 10/9/2002-6/20/2005. |
Environmental Conditions: |
There are no known environmental conditions (e.g., seasonality, land use practices, fire events, storms, etc.) that are related to these data. |
QAPP Information: |
Quality control was conducted in accordance with the SWAMP Quality Assurance Management Plan (SWAMP 2002). |
QAPP Information Reference(s): |
Quality Assurance Management Plan for the State of California's Surface Water Ambient Monitoring Program. Sacramento, CA. State Water Resources Control Board. SWAMP. December 2002 (1st version)
|
|
Line of Evidence (LOE) for Decision ID 168862, Prometryn
|
Region 1 |
Klamath River HU, Shasta River HA |
|
|
LOE ID: |
105160 |
|
Pollutant: |
Prometryn |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Total |
|
Beneficial Use: |
Municipal & Domestic Supply |
|
Number of Samples: |
3 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP RWB1 Monitoring data for Klamath River HU, Shasta River HA to determine beneficial use support and results are as follows: 0 of 3 samples exceeded the water quality standard for Prometryn. |
Data Reference: |
Water Quality Assessment Data for the 2018 solicitation cycle submitted through CEDEN for SWAMP RWB1 Monitoring .
|
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
No individual pesticide or combination of pesticides shall be present in concentrations that adversely affect beneficial uses (Water Quality Control Plan, North Coast Basin). |
Objective/Criterion Reference: |
Water Quality Control Plan (Basin Plan) for the North Coast Region |
|
Evaluation Guideline: |
The USEPA expected safe lifetime exposure limit in drinking water for Prometryn, calculated using the IRIS Reference Dose, is 28 ug/L. This was calculated assuming 70 kg body weight, 2 liters/day water consumption, 20% relative source contribution from drinking water, and 0.004 mg/kg/day as the reference dose. |
Guideline Reference: |
IRIS Reference Summary (Various Pollutants) |
|
Spatial Representation: |
The samples were collected at 1 monitoring site(s) (105SH1452) |
Temporal Representation: |
The samples were collected between the dates of 2013-03-06 and 2013-11-20 |
Environmental Conditions: |
|
QAPP Information: |
Quality Assurance Program Plan and Standard Operating Procedures for SWAMP program |
QAPP Information Reference(s): |
Quality Assurance Program Plans, Quality Assurance Project Plans, and Standard Operating Procedures for the SWAMP program |
|
Line of Evidence (LOE) for Decision ID 168862, Prometryn
|
Region 1 |
Klamath River HU, Shasta River HA |
|
|
LOE ID: |
105164 |
|
Pollutant: |
Prometryn |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Total |
|
Beneficial Use: |
Municipal & Domestic Supply |
|
Number of Samples: |
3 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP RWB1 Monitoring data for Klamath River HU, Shasta River HA to determine beneficial use support and results are as follows: 0 of 3 samples exceeded the water quality standard for Prometryn. |
Data Reference: |
Water Quality Assessment Data for the 2018 solicitation cycle submitted through CEDEN for SWAMP RWB1 Monitoring .
|
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
No individual pesticide or combination of pesticides shall be present in concentrations that adversely affect beneficial uses (Water Quality Control Plan, North Coast Basin). |
Objective/Criterion Reference: |
Water Quality Control Plan (Basin Plan) for the North Coast Region |
|
Evaluation Guideline: |
The USEPA expected safe lifetime exposure limit in drinking water for Prometryn, calculated using the IRIS Reference Dose, is 28 ug/L. This was calculated assuming 70 kg body weight, 2 liters/day water consumption, 20% relative source contribution from drinking water, and 0.004 mg/kg/day as the reference dose. |
Guideline Reference: |
IRIS Reference Summary (Various Pollutants) |
|
Spatial Representation: |
The samples were collected at 1 monitoring site(s) (105SH9274) |
Temporal Representation: |
The samples were collected between the dates of 2013-03-07 and 2013-11-20 |
Environmental Conditions: |
|
QAPP Information: |
Quality Assurance Program Plan and Standard Operating Procedures for SWAMP program |
QAPP Information Reference(s): |
Quality Assurance Program Plans, Quality Assurance Project Plans, and Standard Operating Procedures for the SWAMP program |
|
Line of Evidence (LOE) for Decision ID 168862, Prometryn
|
Region 1 |
Klamath River HU, Shasta River HA |
|
|
LOE ID: |
350624 |
|
Pollutant: |
Prometryn |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Total |
|
Beneficial Use: |
Cold Freshwater Habitat |
|
Number of Samples: |
3 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed RWB1 Trend Maintenance Periods FYs 2007 2008 data for Klamath River HU, Shasta River HA to determine beneficial use support and results are as follows: 0 of 3 samples exceeded the water quality threshold for Prometryn. |
Data Reference: |
RWB1 Trend Maintenance Periods FYs 2007 2008 |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
All waters shall be maintained free of toxic substances in concentrations which are toxic to, or which produce detrimental physiological responses in, human, plant, animal, or aquatic life. (Basin Plan). |
Objective/Criterion Reference: |
Water Quality Control Plan (Basin Plan) for the North Coast Region |
|
Evaluation Guideline: |
UC Davis Aquatic Life Criteria: Aquatic life should not be affected unacceptably if the four-day average concentration of Prometryn does not exceed 0.562 ug/L in the water column more than once every three years on average (Bower, et al. 2017). |
Guideline Reference: |
Water Quality Criteria Report for Prometryn Phase III: Application of the pesticide water quality criteria methodology. Department of Environmental Toxicology. University of California, Davis. |
|
Spatial Representation: |
The samples were collected at 1 monitoring site: 105SHAEDG (Shasta River near Edgewood). |
Temporal Representation: |
The samples were collected between the dates of 2007-11-15 and 2008-07-16 |
Environmental Conditions: |
|
QAPP Information: |
Generic SWAMP QAPrP |
QAPP Information Reference(s): |
Generic SWAMP QAPrP |
|
Line of Evidence (LOE) for Decision ID 168862, Prometryn
|
Region 1 |
Klamath River HU, Shasta River HA |
|
|
LOE ID: |
350600 |
|
Pollutant: |
Prometryn |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Total |
|
Beneficial Use: |
Cold Freshwater Habitat |
|
Number of Samples: |
3 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP RWB1 Monitoring data for Klamath River HU, Shasta River HA to determine beneficial use support and results are as follows: 0 of 3 samples exceeded the water quality threshold for Prometryn. |
Data Reference: |
Water Quality Assessment Data for the 2018 solicitation cycle submitted through CEDEN for SWAMP RWB1 Monitoring .
|
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
All waters shall be maintained free of toxic substances in concentrations which are toxic to, or which produce detrimental physiological responses in, human, plant, animal, or aquatic life. (Basin Plan). |
Objective/Criterion Reference: |
Water Quality Control Plan (Basin Plan) for the North Coast Region |
|
Evaluation Guideline: |
UC Davis Aquatic Life Criteria: Aquatic life should not be affected unacceptably if the four-day average concentration of Prometryn does not exceed 0.562 ug/L in the water column more than once every three years on average (Bower, et al. 2017). |
Guideline Reference: |
Water Quality Criteria Report for Prometryn Phase III: Application of the pesticide water quality criteria methodology. Department of Environmental Toxicology. University of California, Davis. |
|
Spatial Representation: |
The samples were collected at 1 monitoring site: 105SH1452 (Shasta River at Hwy 263). |
Temporal Representation: |
The samples were collected between the dates of 2013-03-06 and 2013-11-20 |
Environmental Conditions: |
|
QAPP Information: |
Generic SWAMP QAPrP |
QAPP Information Reference(s): |
Generic SWAMP QAPrP |
|
Line of Evidence (LOE) for Decision ID 168862, Prometryn
|
Region 1 |
Klamath River HU, Shasta River HA |
|
|
LOE ID: |
350673 |
|
Pollutant: |
Prometryn |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Total |
|
Beneficial Use: |
Cold Freshwater Habitat |
|
Number of Samples: |
3 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed RWB1 Trend Maintenance Periods FYs 2007 2008 data for Klamath River HU, Shasta River HA to determine beneficial use support and results are as follows: 0 of 3 samples exceeded the water quality threshold for Prometryn. |
Data Reference: |
RWB1 Trend Maintenance Periods FYs 2007 2008 |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
All waters shall be maintained free of toxic substances in concentrations which are toxic to, or which produce detrimental physiological responses in, human, plant, animal, or aquatic life. (Basin Plan). |
Objective/Criterion Reference: |
Water Quality Control Plan (Basin Plan) for the North Coast Region |
|
Evaluation Guideline: |
UC Davis Aquatic Life Criteria: Aquatic life should not be affected unacceptably if the four-day average concentration of Prometryn does not exceed 0.562 ug/L in the water column more than once every three years on average (Bower, et al. 2017). |
Guideline Reference: |
Water Quality Criteria Report for Prometryn Phase III: Application of the pesticide water quality criteria methodology. Department of Environmental Toxicology. University of California, Davis. |
|
Spatial Representation: |
The samples were collected at 1 monitoring site: 105SHA263 (Shasta River at Hwy 263). |
Temporal Representation: |
The samples were collected between the dates of 2007-11-15 and 2008-07-16 |
Environmental Conditions: |
|
QAPP Information: |
Generic SWAMP QAPrP |
QAPP Information Reference(s): |
Generic SWAMP QAPrP |
|
Line of Evidence (LOE) for Decision ID 168862, Prometryn
|
Region 1 |
Klamath River HU, Shasta River HA |
|
|
LOE ID: |
350682 |
|
Pollutant: |
Prometryn |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Total |
|
Beneficial Use: |
Warm Freshwater Habitat |
|
Number of Samples: |
3 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed RWB1 Trend Maintenance Periods FYs 2007 2008 data for Klamath River HU, Shasta River HA to determine beneficial use support and results are as follows: 0 of 3 samples exceeded the water quality threshold for Prometryn. |
Data Reference: |
RWB1 Trend Maintenance Periods FYs 2007 2008 |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
All waters shall be maintained free of toxic substances in concentrations which are toxic to, or which produce detrimental physiological responses in, human, plant, animal, or aquatic life. (Basin Plan). |
Objective/Criterion Reference: |
Water Quality Control Plan (Basin Plan) for the North Coast Region |
|
Evaluation Guideline: |
UC Davis Aquatic Life Criteria: Aquatic life should not be affected unacceptably if the four-day average concentration of Prometryn does not exceed 0.562 ug/L in the water column more than once every three years on average (Bower, et al. 2017). |
Guideline Reference: |
Water Quality Criteria Report for Prometryn Phase III: Application of the pesticide water quality criteria methodology. Department of Environmental Toxicology. University of California, Davis. |
|
Spatial Representation: |
The samples were collected at 1 monitoring site: 105SHA263 (Shasta River at Hwy 263). |
Temporal Representation: |
The samples were collected between the dates of 2007-11-15 and 2008-07-16 |
Environmental Conditions: |
|
QAPP Information: |
Generic SWAMP QAPrP |
QAPP Information Reference(s): |
Generic SWAMP QAPrP |
|
Line of Evidence (LOE) for Decision ID 168862, Prometryn
|
Region 1 |
Klamath River HU, Shasta River HA |
|
|
LOE ID: |
350619 |
|
Pollutant: |
Prometryn |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Total |
|
Beneficial Use: |
Cold Freshwater Habitat |
|
Number of Samples: |
3 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP RWB1 Monitoring data for Klamath River HU, Shasta River HA to determine beneficial use support and results are as follows: 0 of 3 samples exceeded the water quality threshold for Prometryn. |
Data Reference: |
Water Quality Assessment Data for the 2018 solicitation cycle submitted through CEDEN for SWAMP RWB1 Monitoring .
|
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
All waters shall be maintained free of toxic substances in concentrations which are toxic to, or which produce detrimental physiological responses in, human, plant, animal, or aquatic life. (Basin Plan). |
Objective/Criterion Reference: |
Water Quality Control Plan (Basin Plan) for the North Coast Region |
|
Evaluation Guideline: |
UC Davis Aquatic Life Criteria: Aquatic life should not be affected unacceptably if the four-day average concentration of Prometryn does not exceed 0.562 ug/L in the water column more than once every three years on average (Bower, et al. 2017). |
Guideline Reference: |
Water Quality Criteria Report for Prometryn Phase III: Application of the pesticide water quality criteria methodology. Department of Environmental Toxicology. University of California, Davis. |
|
Spatial Representation: |
The samples were collected at 1 monitoring site: 105SH9274 (Shasta River near Edgewood). |
Temporal Representation: |
The samples were collected between the dates of 2013-03-07 and 2013-11-20 |
Environmental Conditions: |
|
QAPP Information: |
Generic SWAMP QAPrP |
QAPP Information Reference(s): |
Generic SWAMP QAPrP |
|
Line of Evidence (LOE) for Decision ID 168862, Prometryn
|
Region 1 |
Klamath River HU, Shasta River HA |
|
|
LOE ID: |
350643 |
|
Pollutant: |
Prometryn |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Total |
|
Beneficial Use: |
Warm Freshwater Habitat |
|
Number of Samples: |
3 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP RWB1 Monitoring data for Klamath River HU, Shasta River HA to determine beneficial use support and results are as follows: 0 of 3 samples exceeded the water quality threshold for Prometryn. |
Data Reference: |
Water Quality Assessment Data for the 2018 solicitation cycle submitted through CEDEN for SWAMP RWB1 Monitoring .
|
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
All waters shall be maintained free of toxic substances in concentrations which are toxic to, or which produce detrimental physiological responses in, human, plant, animal, or aquatic life. (Basin Plan). |
Objective/Criterion Reference: |
Water Quality Control Plan (Basin Plan) for the North Coast Region |
|
Evaluation Guideline: |
UC Davis Aquatic Life Criteria: Aquatic life should not be affected unacceptably if the four-day average concentration of Prometryn does not exceed 0.562 ug/L in the water column more than once every three years on average (Bower, et al. 2017). |
Guideline Reference: |
Water Quality Criteria Report for Prometryn Phase III: Application of the pesticide water quality criteria methodology. Department of Environmental Toxicology. University of California, Davis. |
|
Spatial Representation: |
The samples were collected at 1 monitoring site: 105SH1452 (Shasta River at Hwy 263). |
Temporal Representation: |
The samples were collected between the dates of 2013-03-06 and 2013-11-20 |
Environmental Conditions: |
|
QAPP Information: |
Generic SWAMP QAPrP |
QAPP Information Reference(s): |
Generic SWAMP QAPrP |
|
Line of Evidence (LOE) for Decision ID 168862, Prometryn
|
Region 1 |
Klamath River HU, Shasta River HA |
|
|
LOE ID: |
350694 |
|
Pollutant: |
Prometryn |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Total |
|
Beneficial Use: |
Warm Freshwater Habitat |
|
Number of Samples: |
3 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP RWB1 Monitoring data for Klamath River HU, Shasta River HA to determine beneficial use support and results are as follows: 0 of 3 samples exceeded the water quality threshold for Prometryn. |
Data Reference: |
Water Quality Assessment Data for the 2018 solicitation cycle submitted through CEDEN for SWAMP RWB1 Monitoring .
|
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
All waters shall be maintained free of toxic substances in concentrations which are toxic to, or which produce detrimental physiological responses in, human, plant, animal, or aquatic life. (Basin Plan). |
Objective/Criterion Reference: |
Water Quality Control Plan (Basin Plan) for the North Coast Region |
|
Evaluation Guideline: |
UC Davis Aquatic Life Criteria: Aquatic life should not be affected unacceptably if the four-day average concentration of Prometryn does not exceed 0.562 ug/L in the water column more than once every three years on average (Bower, et al. 2017). |
Guideline Reference: |
Water Quality Criteria Report for Prometryn Phase III: Application of the pesticide water quality criteria methodology. Department of Environmental Toxicology. University of California, Davis. |
|
Spatial Representation: |
The samples were collected at 1 monitoring site: 105SH9274 (Shasta River near Edgewood). |
Temporal Representation: |
The samples were collected between the dates of 2013-03-07 and 2013-11-20 |
Environmental Conditions: |
|
QAPP Information: |
Generic SWAMP QAPrP |
QAPP Information Reference(s): |
Generic SWAMP QAPrP |
|
Line of Evidence (LOE) for Decision ID 168862, Prometryn
|
Region 1 |
Klamath River HU, Shasta River HA |
|
|
LOE ID: |
350609 |
|
Pollutant: |
Prometryn |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Total |
|
Beneficial Use: |
Warm Freshwater Habitat |
|
Number of Samples: |
3 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed RWB1 Trend Maintenance Periods FYs 2007 2008 data for Klamath River HU, Shasta River HA to determine beneficial use support and results are as follows: 0 of 3 samples exceeded the water quality threshold for Prometryn. |
Data Reference: |
RWB1 Trend Maintenance Periods FYs 2007 2008 |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
All waters shall be maintained free of toxic substances in concentrations which are toxic to, or which produce detrimental physiological responses in, human, plant, animal, or aquatic life. (Basin Plan). |
Objective/Criterion Reference: |
Water Quality Control Plan (Basin Plan) for the North Coast Region |
|
Evaluation Guideline: |
UC Davis Aquatic Life Criteria: Aquatic life should not be affected unacceptably if the four-day average concentration of Prometryn does not exceed 0.562 ug/L in the water column more than once every three years on average (Bower, et al. 2017). |
Guideline Reference: |
Water Quality Criteria Report for Prometryn Phase III: Application of the pesticide water quality criteria methodology. Department of Environmental Toxicology. University of California, Davis. |
|
Spatial Representation: |
The samples were collected at 1 monitoring site: 105SHAEDG (Shasta River near Edgewood). |
Temporal Representation: |
The samples were collected between the dates of 2007-11-15 and 2008-07-16 |
Environmental Conditions: |
|
QAPP Information: |
Generic SWAMP QAPrP |
QAPP Information Reference(s): |
Generic SWAMP QAPrP |
|
Line of Evidence (LOE) for Decision ID 168863, Propazine
|
Region 1 |
Klamath River HU, Shasta River HA |
|
|
LOE ID: |
123390 |
|
Pollutant: |
Propazine |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
None |
|
Beneficial Use: |
Municipal & Domestic Supply |
|
Number of Samples: |
0 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
State Water Board staff re-assessed SWAMP data for Klamath River HU, Shasta River HA to determine beneficial use support and results are as follows: 0 of 0 samples exceed the criterion for Propazine, Total. Four sample results were not used in the assessment because the laboratory data reporting limit(s) was above the objective and therefore the results could not be quantified with the level of certainty required by the Listing Policy. This LOE re-assesses data from LOE 29849 from the 2010 Integrated Report. Data were re-assessed in order to evaluate these data in their own LOE, instead of being evaluated in the same LOE as other pesticide data. |
Data Reference: |
Surface Water Ambient Monitoring Program (SWAMP). Summary Report for the North Coast Region (RWQCB-1) for years 2000-2006. North Coast Regional Water Quality Control Board. March 2008 |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
Per the Basin Plan (NCRWQCB 2011): No individual pesticide or combination of pesticides shall be present in concentrations that adversely affect beneficial uses. There shall be no bioaccumulation of pesticide concentrations found in bottom sediments or aquatic life. Waters designated for use as domestic or municipal supply shall not contain concentrations of pesticides in excess of the limiting concentrations set forth in California Code of Regulations, Title 22, Division 4, Chapter 15, Article 4, Section 64444, and listed in Table 3.2 of the Basin Plan. |
Objective/Criterion Reference: |
Water Quality Control Plan (Basin Plan) for the North Coast Region |
|
Evaluation Guideline: |
According to the 2006 USEPA Drinking Water Standards and Health Advisories, the Life-time Exposure Health Advisory for Propazine is 0.1 mg/L. (EPA 822-R-06-013, 2006) |
Guideline Reference: |
2006 edition of the drinking water standards and health advisories. EPA 822-R-03-013 |
|
Spatial Representation: |
Data for this line of evidence for Klamath River HU, Shasta River HA was collected at 1 monitoring site [ Yreka Creek at Highway 3 - 105YREHW3] |
Temporal Representation: |
Data was collected over the time period 10/21/2004-6/20/2005. |
Environmental Conditions: |
There are no known environmental conditions (e.g., seasonality, land use practices, fire events, storms, etc.) that are related to these data. |
QAPP Information: |
Quality control was conducted in accordance with the SWAMP Quality Assurance Management Plan (SWAMP 2002). |
QAPP Information Reference(s): |
Quality Assurance Management Plan for the State of California's Surface Water Ambient Monitoring Program. Sacramento, CA. State Water Resources Control Board. SWAMP. December 2002 (1st version)
|
|
Line of Evidence (LOE) for Decision ID 168863, Propazine
|
Region 1 |
Klamath River HU, Shasta River HA |
|
|
LOE ID: |
350719 |
|
Pollutant: |
Propazine |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Total |
|
Beneficial Use: |
Warm Freshwater Habitat |
|
Number of Samples: |
3 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed RWB1 Trend Maintenance Periods FYs 2007 2008 data for Klamath River HU, Shasta River HA to determine beneficial use support and results are as follows: 0 of 3 samples exceeded the water quality threshold for Propazine. |
Data Reference: |
RWB1 Trend Maintenance Periods FYs 2007 2008 |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
All waters shall be maintained free of toxic substances in concentrations which are toxic to, or which produce detrimental physiological responses in, human, plant, animal, or aquatic life. (Basin Plan). |
Objective/Criterion Reference: |
Water Quality Control Plan (Basin Plan) for the North Coast Region |
|
Evaluation Guideline: |
The evaluation guideline for propazine is the USEPA Aquatic Life Benchmark of 24.8 ug/L for a nonvascular plant (acute). |
Guideline Reference: |
OPP Aquatic Life Benchmarks |
|
Spatial Representation: |
The samples were collected at 1 monitoring site: 105SHA263 (Shasta River at Hwy 263). |
Temporal Representation: |
The samples were collected between the dates of 2007-11-15 and 2008-07-16 |
Environmental Conditions: |
|
QAPP Information: |
Generic SWAMP QAPrP |
QAPP Information Reference(s): |
Generic SWAMP QAPrP |
|
Line of Evidence (LOE) for Decision ID 168863, Propazine
|
Region 1 |
Klamath River HU, Shasta River HA |
|
|
LOE ID: |
110460 |
|
Pollutant: |
Propazine |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Total |
|
Beneficial Use: |
Municipal & Domestic Supply |
|
Number of Samples: |
3 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP RWB1 Monitoring data for Klamath River HU, Shasta River HA to determine beneficial use support and results are as follows: 0 of 3 samples exceeded the water quality standard for Propazine. |
Data Reference: |
Water Quality Assessment Data for the 2018 solicitation cycle submitted through CEDEN for SWAMP RWB1 Monitoring .
|
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
Water Quality Control Plan, North Coast Region (NCRWQCB 2018): No individual pesticide or combination of pesticides shall be present in concentrations that adversely affect beneficial uses. |
Objective/Criterion Reference: |
Water Quality Control Plan (Basin Plan) for the North Coast Region |
|
Evaluation Guideline: |
The USEPA health advisory for one-in-a-million incremental cancer risk estimate calculated as a drinking water standard for propazine is 100 µg/L. |
Guideline Reference: |
2012 Edition of the Drinking Water Standards and Health Advisories |
|
Spatial Representation: |
The samples were collected at 1 monitoring site(s) (105SH9274) |
Temporal Representation: |
The samples were collected between the dates of 2013-03-07 and 2013-11-20 |
Environmental Conditions: |
|
QAPP Information: |
Quality Assurance Program Plan and Standard Operating Procedures for SWAMP program |
QAPP Information Reference(s): |
Quality Assurance Program Plans, Quality Assurance Project Plans, and Standard Operating Procedures for the SWAMP program |
|
Line of Evidence (LOE) for Decision ID 168863, Propazine
|
Region 1 |
Klamath River HU, Shasta River HA |
|
|
LOE ID: |
105167 |
|
Pollutant: |
Propazine |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Total |
|
Beneficial Use: |
Municipal & Domestic Supply |
|
Number of Samples: |
3 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP RWB1 Monitoring data for Klamath River HU, Shasta River HA to determine beneficial use support and results are as follows: 0 of 3 samples exceeded the water quality standard for Propazine. |
Data Reference: |
Water Quality Assessment Data for the 2018 solicitation cycle submitted through CEDEN for SWAMP RWB1 Monitoring .
|
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
Water Quality Control Plan, North Coast Region (NCRWQCB 2018): No individual pesticide or combination of pesticides shall be present in concentrations that adversely affect beneficial uses. |
Objective/Criterion Reference: |
Water Quality Control Plan (Basin Plan) for the North Coast Region |
|
Evaluation Guideline: |
The USEPA health advisory for one-in-a-million incremental cancer risk estimate calculated as a drinking water standard for propazine is 100 µg/L. |
Guideline Reference: |
2012 Edition of the Drinking Water Standards and Health Advisories |
|
Spatial Representation: |
The samples were collected at 1 monitoring site(s) (105SH1452) |
Temporal Representation: |
The samples were collected between the dates of 2013-03-06 and 2013-11-20 |
Environmental Conditions: |
|
QAPP Information: |
Quality Assurance Program Plan and Standard Operating Procedures for SWAMP program |
QAPP Information Reference(s): |
Quality Assurance Program Plans, Quality Assurance Project Plans, and Standard Operating Procedures for the SWAMP program |
|
Line of Evidence (LOE) for Decision ID 168863, Propazine
|
Region 1 |
Klamath River HU, Shasta River HA |
|
|
LOE ID: |
350710 |
|
Pollutant: |
Propazine |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Total |
|
Beneficial Use: |
Cold Freshwater Habitat |
|
Number of Samples: |
3 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed RWB1 Trend Maintenance Periods FYs 2007 2008 data for Klamath River HU, Shasta River HA to determine beneficial use support and results are as follows: 0 of 3 samples exceeded the water quality threshold for Propazine. |
Data Reference: |
RWB1 Trend Maintenance Periods FYs 2007 2008 |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
All waters shall be maintained free of toxic substances in concentrations which are toxic to, or which produce detrimental physiological responses in, human, plant, animal, or aquatic life. (Basin Plan). |
Objective/Criterion Reference: |
Water Quality Control Plan (Basin Plan) for the North Coast Region |
|
Evaluation Guideline: |
The evaluation guideline for propazine is the USEPA Aquatic Life Benchmark of 24.8 ug/L for a nonvascular plant (acute). |
Guideline Reference: |
OPP Aquatic Life Benchmarks |
|
Spatial Representation: |
The samples were collected at 1 monitoring site: 105SHAEDG (Shasta River near Edgewood). |
Temporal Representation: |
The samples were collected between the dates of 2007-11-15 and 2008-07-16 |
Environmental Conditions: |
|
QAPP Information: |
Generic SWAMP QAPrP |
QAPP Information Reference(s): |
Generic SWAMP QAPrP |
|
Line of Evidence (LOE) for Decision ID 168863, Propazine
|
Region 1 |
Klamath River HU, Shasta River HA |
|
|
LOE ID: |
110461 |
|
Pollutant: |
Propazine |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Total |
|
Beneficial Use: |
Warm Freshwater Habitat |
|
Number of Samples: |
3 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP RWB1 Monitoring data for Klamath River HU, Shasta River HA to determine beneficial use support and results are as follows: 0 of 3 samples exceeded the water quality standard for Propazine. |
Data Reference: |
Water Quality Assessment Data for the 2018 solicitation cycle submitted through CEDEN for SWAMP RWB1 Monitoring .
|
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
All waters shall be maintained free of toxic substances in concentrations which are toxic to, or which produce detrimental physiological responses in, human, plant, animal, or aquatic life. (Basin Plan). |
Objective/Criterion Reference: |
Water Quality Control Plan (Basin Plan) for the North Coast Region |
|
Evaluation Guideline: |
The evaluation guideline for Propazine is the USEPA Aquatic Life Benchmark of 24.8 ug/L for a nonvascular plant (acute). |
Guideline Reference: |
OPP Aquatic Life Benchmarks |
|
Spatial Representation: |
The samples were collected at 1 monitoring site(s) (105SH9274) |
Temporal Representation: |
The samples were collected between the dates of 2013-03-07 and 2013-11-20 |
Environmental Conditions: |
|
QAPP Information: |
Quality Assurance Program Plan and Standard Operating Procedures for SWAMP program |
QAPP Information Reference(s): |
Quality Assurance Program Plans, Quality Assurance Project Plans, and Standard Operating Procedures for the SWAMP program |
|
Line of Evidence (LOE) for Decision ID 168863, Propazine
|
Region 1 |
Klamath River HU, Shasta River HA |
|
|
LOE ID: |
350723 |
|
Pollutant: |
Propazine |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Total |
|
Beneficial Use: |
Cold Freshwater Habitat |
|
Number of Samples: |
3 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed RWB1 Trend Maintenance Periods FYs 2007 2008 data for Klamath River HU, Shasta River HA to determine beneficial use support and results are as follows: 0 of 3 samples exceeded the water quality threshold for Propazine. |
Data Reference: |
RWB1 Trend Maintenance Periods FYs 2007 2008 |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
All waters shall be maintained free of toxic substances in concentrations which are toxic to, or which produce detrimental physiological responses in, human, plant, animal, or aquatic life. (Basin Plan). |
Objective/Criterion Reference: |
Water Quality Control Plan (Basin Plan) for the North Coast Region |
|
Evaluation Guideline: |
The evaluation guideline for propazine is the USEPA Aquatic Life Benchmark of 24.8 ug/L for a nonvascular plant (acute). |
Guideline Reference: |
OPP Aquatic Life Benchmarks |
|
Spatial Representation: |
The samples were collected at 1 monitoring site: 105SHA263 (Shasta River at Hwy 263). |
Temporal Representation: |
The samples were collected between the dates of 2007-11-15 and 2008-07-16 |
Environmental Conditions: |
|
QAPP Information: |
Generic SWAMP QAPrP |
QAPP Information Reference(s): |
Generic SWAMP QAPrP |
|
Line of Evidence (LOE) for Decision ID 168863, Propazine
|
Region 1 |
Klamath River HU, Shasta River HA |
|
|
LOE ID: |
350702 |
|
Pollutant: |
Propazine |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Total |
|
Beneficial Use: |
Warm Freshwater Habitat |
|
Number of Samples: |
3 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed RWB1 Trend Maintenance Periods FYs 2007 2008 data for Klamath River HU, Shasta River HA to determine beneficial use support and results are as follows: 0 of 3 samples exceeded the water quality threshold for Propazine. |
Data Reference: |
RWB1 Trend Maintenance Periods FYs 2007 2008 |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
All waters shall be maintained free of toxic substances in concentrations which are toxic to, or which produce detrimental physiological responses in, human, plant, animal, or aquatic life. (Basin Plan). |
Objective/Criterion Reference: |
Water Quality Control Plan (Basin Plan) for the North Coast Region |
|
Evaluation Guideline: |
The evaluation guideline for propazine is the USEPA Aquatic Life Benchmark of 24.8 ug/L for a nonvascular plant (acute). |
Guideline Reference: |
OPP Aquatic Life Benchmarks |
|
Spatial Representation: |
The samples were collected at 1 monitoring site: 105SHAEDG (Shasta River near Edgewood). |
Temporal Representation: |
The samples were collected between the dates of 2007-11-15 and 2008-07-16 |
Environmental Conditions: |
|
QAPP Information: |
Generic SWAMP QAPrP |
QAPP Information Reference(s): |
Generic SWAMP QAPrP |
|
Line of Evidence (LOE) for Decision ID 168863, Propazine
|
Region 1 |
Klamath River HU, Shasta River HA |
|
|
LOE ID: |
123381 |
|
Pollutant: |
Propazine |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
None |
|
Beneficial Use: |
Municipal & Domestic Supply |
|
Number of Samples: |
0 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
State Water Board staff re-assessed SWAMP data for Klamath River HU, Shasta River HA to determine beneficial use support and results are as follows: 0 of 0 samples exceed the criterion for Propazine, Total. Four sample results were not used in the assessment because the laboratory data reporting limit(s) was above the objective and therefore the results could not be quantified with the level of certainty required by the Listing Policy. This LOE re-assesses data from LOE 29849 from the 2010 Integrated Report. Data were re-assessed in order to evaluate these data in their own LOE, instead of being evaluated in the same LOE as other pesticide data. |
Data Reference: |
Surface Water Ambient Monitoring Program (SWAMP). Summary Report for the North Coast Region (RWQCB-1) for years 2000-2006. North Coast Regional Water Quality Control Board. March 2008 |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
Per the Basin Plan (NCRWQCB 2011): No individual pesticide or combination of pesticides shall be present in concentrations that adversely affect beneficial uses. There shall be no bioaccumulation of pesticide concentrations found in bottom sediments or aquatic life. Waters designated for use as domestic or municipal supply shall not contain concentrations of pesticides in excess of the limiting concentrations set forth in California Code of Regulations, Title 22, Division 4, Chapter 15, Article 4, Section 64444, and listed in Table 3.2 of the Basin Plan. |
Objective/Criterion Reference: |
Water Quality Control Plan (Basin Plan) for the North Coast Region |
|
Evaluation Guideline: |
According to the 2006 USEPA Drinking Water Standards and Health Advisories, the Life-time Exposure Health Advisory for Propazine is 0.1 mg/L. (EPA 822-R-06-013, 2006) |
Guideline Reference: |
2006 edition of the drinking water standards and health advisories. EPA 822-R-03-013 |
|
Spatial Representation: |
Data for this line of evidence for Klamath River HU, Shasta River HA was collected at 1 monitoring site [ Shasta River at Montague - 105SHAMON] |
Temporal Representation: |
Data was collected over the time period 10/7/2002-6/19/2003. |
Environmental Conditions: |
There are no known environmental conditions (e.g., seasonality, land use practices, fire events, storms, etc.) that are related to these data. |
QAPP Information: |
Quality control was conducted in accordance with the SWAMP Quality Assurance Management Plan (SWAMP 2002). |
QAPP Information Reference(s): |
Quality Assurance Management Plan for the State of California's Surface Water Ambient Monitoring Program. Sacramento, CA. State Water Resources Control Board. SWAMP. December 2002 (1st version)
|
|
Line of Evidence (LOE) for Decision ID 168863, Propazine
|
Region 1 |
Klamath River HU, Shasta River HA |
|
|
LOE ID: |
123383 |
|
Pollutant: |
Propazine |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
None |
|
Beneficial Use: |
Municipal & Domestic Supply |
|
Number of Samples: |
0 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
State Water Board staff re-assessed SWAMP data for Klamath River HU, Shasta River HA to determine beneficial use support and results are as follows: 0 of 0 samples exceed the criterion for Propazine, Total. Eight sample results were not used in the assessment because the laboratory data reporting limit(s) was above the objective and therefore the results could not be quantified with the level of certainty required by the Listing Policy. This LOE re-assesses data from LOE 29849 from the 2010 Integrated Report. Data were re-assessed in order to evaluate these data in their own LOE, instead of being evaluated in the same LOE as other pesticide data. |
Data Reference: |
Surface Water Ambient Monitoring Program (SWAMP). Summary Report for the North Coast Region (RWQCB-1) for years 2000-2006. North Coast Regional Water Quality Control Board. March 2008 |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
Per the Basin Plan (NCRWQCB 2011): No individual pesticide or combination of pesticides shall be present in concentrations that adversely affect beneficial uses. There shall be no bioaccumulation of pesticide concentrations found in bottom sediments or aquatic life. Waters designated for use as domestic or municipal supply shall not contain concentrations of pesticides in excess of the limiting concentrations set forth in California Code of Regulations, Title 22, Division 4, Chapter 15, Article 4, Section 64444, and listed in Table 3.2 of the Basin Plan. |
Objective/Criterion Reference: |
Water Quality Control Plan (Basin Plan) for the North Coast Region |
|
Evaluation Guideline: |
According to the 2006 USEPA Drinking Water Standards and Health Advisories, the Life-time Exposure Health Advisory for Propazine is 0.1 mg/L. (EPA 822-R-06-013, 2006) |
Guideline Reference: |
2006 edition of the drinking water standards and health advisories. EPA 822-R-03-013 |
|
Spatial Representation: |
Data for this line of evidence for Klamath River HU, Shasta River HA was collected at 1 monitoring site [ Yreka Creek at Anderson Rd - 105YREAND] |
Temporal Representation: |
Data was collected over the time period 10/9/2002-6/20/2005. |
Environmental Conditions: |
There are no known environmental conditions (e.g., seasonality, land use practices, fire events, storms, etc.) that are related to these data. |
QAPP Information: |
Quality control was conducted in accordance with the SWAMP Quality Assurance Management Plan (SWAMP 2002). |
QAPP Information Reference(s): |
Quality Assurance Management Plan for the State of California's Surface Water Ambient Monitoring Program. Sacramento, CA. State Water Resources Control Board. SWAMP. December 2002 (1st version)
|
|
Line of Evidence (LOE) for Decision ID 168863, Propazine
|
Region 1 |
Klamath River HU, Shasta River HA |
|
|
LOE ID: |
123374 |
|
Pollutant: |
Propazine |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
None |
|
Beneficial Use: |
Municipal & Domestic Supply |
|
Number of Samples: |
0 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
State Water Board staff re-assessed SWAMP data for Klamath River HU, Shasta River HA to determine beneficial use support and results are as follows: 0 of 0 samples exceed the criterion for Propazine, Total. Thirteen sample results were not used in the assessment because the laboratory data reporting limit(s) was above the objective and therefore the results could not be quantified with the level of certainty required by the Listing Policy. This LOE re-assesses data from LOE 29849 from the 2010 Integrated Report. Data were re-assessed in order to evaluate these data in their own LOE, instead of being evaluated in the same LOE as other pesticide data. |
Data Reference: |
Surface Water Ambient Monitoring Program (SWAMP). Summary Report for the North Coast Region (RWQCB-1) for years 2000-2006. North Coast Regional Water Quality Control Board. March 2008 |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
Per the Basin Plan (NCRWQCB 2011): No individual pesticide or combination of pesticides shall be present in concentrations that adversely affect beneficial uses. There shall be no bioaccumulation of pesticide concentrations found in bottom sediments or aquatic life. Waters designated for use as domestic or municipal supply shall not contain concentrations of pesticides in excess of the limiting concentrations set forth in California Code of Regulations, Title 22, Division 4, Chapter 15, Article 4, Section 64444, and listed in Table 3.2 of the Basin Plan. |
Objective/Criterion Reference: |
Water Quality Control Plan (Basin Plan) for the North Coast Region |
|
Evaluation Guideline: |
According to the 2006 USEPA Drinking Water Standards and Health Advisories, the Life-time Exposure Health Advisory for Propazine is 0.1 mg/L. (EPA 822-R-06-013, 2006) |
Guideline Reference: |
2006 edition of the drinking water standards and health advisories. EPA 822-R-03-013 |
|
Spatial Representation: |
Data for this line of evidence for Klamath River HU, Shasta River HA was collected at 1 monitoring site [ Shasta River at Hwy 263 - 105SH1452] |
Temporal Representation: |
Data was collected over the time period 4/24/2001-11/16/2006. |
Environmental Conditions: |
There are no known environmental conditions (e.g., seasonality, land use practices, fire events, storms, etc.) that are related to these data. |
QAPP Information: |
Quality control was conducted in accordance with the SWAMP Quality Assurance Management Plan (SWAMP 2002). |
QAPP Information Reference(s): |
Quality Assurance Management Plan for the State of California's Surface Water Ambient Monitoring Program. Sacramento, CA. State Water Resources Control Board. SWAMP. December 2002 (1st version)
|
|
Line of Evidence (LOE) for Decision ID 168863, Propazine
|
Region 1 |
Klamath River HU, Shasta River HA |
|
|
LOE ID: |
110459 |
|
Pollutant: |
Propazine |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Total |
|
Beneficial Use: |
Cold Freshwater Habitat |
|
Number of Samples: |
3 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP RWB1 Monitoring data for Klamath River HU, Shasta River HA to determine beneficial use support and results are as follows: 0 of 3 samples exceeded the water quality standard for Propazine. |
Data Reference: |
Water Quality Assessment Data for the 2018 solicitation cycle submitted through CEDEN for SWAMP RWB1 Monitoring .
|
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
All waters shall be maintained free of toxic substances in concentrations which are toxic to, or which produce detrimental physiological responses in, human, plant, animal, or aquatic life. (Basin Plan). |
Objective/Criterion Reference: |
Water Quality Control Plan (Basin Plan) for the North Coast Region |
|
Evaluation Guideline: |
The evaluation guideline for Propazine is the USEPA Aquatic Life Benchmark of 24.8 ug/L for a nonvascular plant (acute). |
Guideline Reference: |
OPP Aquatic Life Benchmarks |
|
Spatial Representation: |
The samples were collected at 1 monitoring site(s) (105SH9274) |
Temporal Representation: |
The samples were collected between the dates of 2013-03-07 and 2013-11-20 |
Environmental Conditions: |
|
QAPP Information: |
Quality Assurance Program Plan and Standard Operating Procedures for SWAMP program |
QAPP Information Reference(s): |
Quality Assurance Program Plans, Quality Assurance Project Plans, and Standard Operating Procedures for the SWAMP program |
|
Line of Evidence (LOE) for Decision ID 168863, Propazine
|
Region 1 |
Klamath River HU, Shasta River HA |
|
|
LOE ID: |
123382 |
|
Pollutant: |
Propazine |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
None |
|
Beneficial Use: |
Municipal & Domestic Supply |
|
Number of Samples: |
0 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
State Water Board staff re-assessed SWAMP data for Klamath River HU, Shasta River HA to determine beneficial use support and results are as follows: 0 of 0 samples exceed the criterion for Propazine, Total. Four sample results were not used in the assessment because the laboratory data reporting limit(s) was above the objective and therefore the results could not be quantified with the level of certainty required by the Listing Policy. This LOE re-assesses data from LOE 29849 from the 2010 Integrated Report. Data were re-assessed in order to evaluate these data in their own LOE, instead of being evaluated in the same LOE as other pesticide data. |
Data Reference: |
Surface Water Ambient Monitoring Program (SWAMP). Summary Report for the North Coast Region (RWQCB-1) for years 2000-2006. North Coast Regional Water Quality Control Board. March 2008 |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
Per the Basin Plan (NCRWQCB 2011): No individual pesticide or combination of pesticides shall be present in concentrations that adversely affect beneficial uses. There shall be no bioaccumulation of pesticide concentrations found in bottom sediments or aquatic life. Waters designated for use as domestic or municipal supply shall not contain concentrations of pesticides in excess of the limiting concentrations set forth in California Code of Regulations, Title 22, Division 4, Chapter 15, Article 4, Section 64444, and listed in Table 3.2 of the Basin Plan. |
Objective/Criterion Reference: |
Water Quality Control Plan (Basin Plan) for the North Coast Region |
|
Evaluation Guideline: |
According to the 2006 USEPA Drinking Water Standards and Health Advisories, the Life-time Exposure Health Advisory for Propazine is 0.1 mg/L. (EPA 822-R-06-013, 2006) |
Guideline Reference: |
2006 edition of the drinking water standards and health advisories. EPA 822-R-03-013 |
|
Spatial Representation: |
Data for this line of evidence for Klamath River HU, Shasta River HA was collected at 1 monitoring site [ Shasta River near Edgewood - 105SH9274] |
Temporal Representation: |
Data was collected over the time period 10/7/2002-6/19/2003. |
Environmental Conditions: |
There are no known environmental conditions (e.g., seasonality, land use practices, fire events, storms, etc.) that are related to these data. |
QAPP Information: |
Quality control was conducted in accordance with the SWAMP Quality Assurance Management Plan (SWAMP 2002). |
QAPP Information Reference(s): |
Quality Assurance Management Plan for the State of California's Surface Water Ambient Monitoring Program. Sacramento, CA. State Water Resources Control Board. SWAMP. December 2002 (1st version)
|
|
Line of Evidence (LOE) for Decision ID 168863, Propazine
|
Region 1 |
Klamath River HU, Shasta River HA |
|
|
LOE ID: |
105168 |
|
Pollutant: |
Propazine |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Total |
|
Beneficial Use: |
Warm Freshwater Habitat |
|
Number of Samples: |
3 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP RWB1 Monitoring data for Klamath River HU, Shasta River HA to determine beneficial use support and results are as follows: 0 of 3 samples exceeded the water quality standard for Propazine. |
Data Reference: |
Water Quality Assessment Data for the 2018 solicitation cycle submitted through CEDEN for SWAMP RWB1 Monitoring .
|
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
All waters shall be maintained free of toxic substances in concentrations which are toxic to, or which produce detrimental physiological responses in, human, plant, animal, or aquatic life. (Basin Plan). |
Objective/Criterion Reference: |
Water Quality Control Plan (Basin Plan) for the North Coast Region |
|
Evaluation Guideline: |
The evaluation guideline for Propazine is the USEPA Aquatic Life Benchmark of 24.8 ug/L for a nonvascular plant (acute). |
Guideline Reference: |
OPP Aquatic Life Benchmarks |
|
Spatial Representation: |
The samples were collected at 1 monitoring site(s) (105SH1452) |
Temporal Representation: |
The samples were collected between the dates of 2013-03-06 and 2013-11-20 |
Environmental Conditions: |
|
QAPP Information: |
Quality Assurance Program Plan and Standard Operating Procedures for SWAMP program |
QAPP Information Reference(s): |
Quality Assurance Program Plans, Quality Assurance Project Plans, and Standard Operating Procedures for the SWAMP program |
|
Line of Evidence (LOE) for Decision ID 168863, Propazine
|
Region 1 |
Klamath River HU, Shasta River HA |
|
|
LOE ID: |
105166 |
|
Pollutant: |
Propazine |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Total |
|
Beneficial Use: |
Cold Freshwater Habitat |
|
Number of Samples: |
3 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP RWB1 Monitoring data for Klamath River HU, Shasta River HA to determine beneficial use support and results are as follows: 0 of 3 samples exceeded the water quality standard for Propazine. |
Data Reference: |
Water Quality Assessment Data for the 2018 solicitation cycle submitted through CEDEN for SWAMP RWB1 Monitoring .
|
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
All waters shall be maintained free of toxic substances in concentrations which are toxic to, or which produce detrimental physiological responses in, human, plant, animal, or aquatic life. (Basin Plan). |
Objective/Criterion Reference: |
Water Quality Control Plan (Basin Plan) for the North Coast Region |
|
Evaluation Guideline: |
The evaluation guideline for Propazine is the USEPA Aquatic Life Benchmark of 24.8 ug/L for a nonvascular plant (acute). |
Guideline Reference: |
OPP Aquatic Life Benchmarks |
|
Spatial Representation: |
The samples were collected at 1 monitoring site(s) (105SH1452) |
Temporal Representation: |
The samples were collected between the dates of 2013-03-06 and 2013-11-20 |
Environmental Conditions: |
|
QAPP Information: |
Quality Assurance Program Plan and Standard Operating Procedures for SWAMP program |
QAPP Information Reference(s): |
Quality Assurance Program Plans, Quality Assurance Project Plans, and Standard Operating Procedures for the SWAMP program |
|
Line of Evidence (LOE) for Decision ID 104948, Selenium
|
Region 1 |
Klamath River HU, Shasta River HA |
|
|
LOE ID: |
123422 |
|
Pollutant: |
Selenium |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Total |
|
Beneficial Use: |
Municipal & Domestic Supply |
|
Number of Samples: |
3 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
State Water Board staff re-assessed SWAMP data for Klamath River HU, Shasta River HA to determine beneficial use support and results are as follows: 0 of 3 samples exceed the criterion for Selenium, Total. This LOE re-assesses data from LOE 21509 from the 2010 Integrated Report. Data were re-assessed in order to (1) update the numeric objective, and (2) evaluate these data in their own LOE, instead of being evaluated in the same LOE as other metals data. |
Data Reference: |
Surface Water Ambient Monitoring Program (SWAMP). Summary Report for the North Coast Region (RWQCB-1) for years 2000-2006. North Coast Regional Water Quality Control Board. March 2008 |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
Water Quality Control Plan, North Coast Region (NCRWQCB 2011): Waters designated for use as domestic or municipal supply (MUN) shall not contain concentrations of chemical constituents in excess of the limits specified in California Code of Regulations, Title 22, Chapter 15. The maximum contaminant level listed in Table 64431-A for selenium is 0.05 mg/L. |
Objective/Criterion Reference: |
Water Quality Control Plan (Basin Plan) for the North Coast Region |
Objective/Criterion Reference: |
Maximum Contaminant Levels for organic and inorganic chemicals. CCR Title 22 |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
Data for this line of evidence for Klamath River HU, Shasta River HA was collected at 1 monitoring site [ Yreka Creek at Highway 3 - 105YREHW3] |
Temporal Representation: |
Data was collected over the time period 10/21/2004-6/20/2005. |
Environmental Conditions: |
There are no known environmental conditions (e.g., seasonality, land use practices, fire events, storms, etc.) that are related to these data. |
QAPP Information: |
Quality control was conducted in accordance with the SWAMP Quality Assurance Management Plan (SWAMP 2002). |
QAPP Information Reference(s): |
Quality Assurance Management Plan for the State of California's Surface Water Ambient Monitoring Program. Sacramento, CA. State Water Resources Control Board. SWAMP. December 2002 (1st version)
|
|
Line of Evidence (LOE) for Decision ID 104948, Selenium
|
Region 1 |
Klamath River HU, Shasta River HA |
|
|
LOE ID: |
105184 |
|
Pollutant: |
Selenium |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Total |
|
Beneficial Use: |
Municipal & Domestic Supply |
|
Number of Samples: |
5 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP RWB1 Monitoring data for Klamath River HU, Shasta River HA to determine beneficial use support and results are as follows: 0 of 5 samples exceeded the water quality standard for Selenium. |
Data Reference: |
Water Quality Assessment Data for the 2018 solicitation cycle submitted through CEDEN for SWAMP RWB1 Monitoring .
|
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
Water Quality Control Plan, North Coast Region (NCRWQCB 2018): Waters designated for use as domestic or municipal supply (MUN) shall not contain concentrations of chemical constituents in excess of the limits specified in California Code of Regulations, Title 22, Chapter 15. The maximum contaminant level listed in Table 64431-A for selenium is 0.05 mg/L. |
Objective/Criterion Reference: |
Water Quality Control Plan (Basin Plan) for the North Coast Region |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
The samples were collected at 1 monitoring site(s) (105SH9274) |
Temporal Representation: |
The samples were collected between the dates of 2013-03-07 and 2013-11-20 |
Environmental Conditions: |
|
QAPP Information: |
Quality Assurance Program Plan and Standard Operating Procedures for SWAMP program |
QAPP Information Reference(s): |
Quality Assurance Program Plans, Quality Assurance Project Plans, and Standard Operating Procedures for the SWAMP program |
|
Line of Evidence (LOE) for Decision ID 104948, Selenium
|
Region 1 |
Klamath River HU, Shasta River HA |
|
|
LOE ID: |
123410 |
|
Pollutant: |
Selenium |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Total |
|
Beneficial Use: |
Municipal & Domestic Supply |
|
Number of Samples: |
5 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
State Water Board staff re-assessed SWAMP data for Klamath River HU, Shasta River HA to determine beneficial use support and results are as follows: 0 of 5 samples exceed the criterion for Selenium, Total. This LOE re-assesses data from LOE 21509 from the 2010 Integrated Report. Data were re-assessed in order to (1) update the numeric objective, and (2) evaluate these data in their own LOE, instead of being evaluated in the same LOE as other metals data. |
Data Reference: |
Surface Water Ambient Monitoring Program (SWAMP). Summary Report for the North Coast Region (RWQCB-1) for years 2000-2006. North Coast Regional Water Quality Control Board. March 2008 |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
Water Quality Control Plan, North Coast Region (NCRWQCB 2011): Waters designated for use as domestic or municipal supply (MUN) shall not contain concentrations of chemical constituents in excess of the limits specified in California Code of Regulations, Title 22, Chapter 15. The maximum contaminant level listed in Table 64431-A for selenium is 0.05 mg/L. |
Objective/Criterion Reference: |
Water Quality Control Plan (Basin Plan) for the North Coast Region |
Objective/Criterion Reference: |
Maximum Contaminant Levels for organic and inorganic chemicals. CCR Title 22 |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
Data for this line of evidence for Klamath River HU, Shasta River HA was collected at 1 monitoring site [ Shasta River near Edgewood - 105SH9274] |
Temporal Representation: |
Data was collected over the time period 10/7/2002-6/19/2003. |
Environmental Conditions: |
There are no known environmental conditions (e.g., seasonality, land use practices, fire events, storms, etc.) that are related to these data. |
QAPP Information: |
Quality control was conducted in accordance with the SWAMP Quality Assurance Management Plan (SWAMP 2002). |
QAPP Information Reference(s): |
Quality Assurance Management Plan for the State of California's Surface Water Ambient Monitoring Program. Sacramento, CA. State Water Resources Control Board. SWAMP. December 2002 (1st version)
|
|
Line of Evidence (LOE) for Decision ID 104948, Selenium
|
Region 1 |
Klamath River HU, Shasta River HA |
|
|
LOE ID: |
123408 |
|
Pollutant: |
Selenium |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Total |
|
Beneficial Use: |
Municipal & Domestic Supply |
|
Number of Samples: |
19 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
State Water Board staff re-assessed SWAMP data for Klamath River HU, Shasta River HA to determine beneficial use support and results are as follows: 0 of 19 samples exceed the criterion for Selenium, Total. This LOE re-assesses data from LOE 21509 from the 2010 Integrated Report. Data were re-assessed in order to (1) update the numeric objective, and (2) evaluate these data in their own LOE, instead of being evaluated in the same LOE as other metals data. |
Data Reference: |
Surface Water Ambient Monitoring Program (SWAMP). Summary Report for the North Coast Region (RWQCB-1) for years 2000-2006. North Coast Regional Water Quality Control Board. March 2008 |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
Water Quality Control Plan, North Coast Region (NCRWQCB 2011): Waters designated for use as domestic or municipal supply (MUN) shall not contain concentrations of chemical constituents in excess of the limits specified in California Code of Regulations, Title 22, Chapter 15. The maximum contaminant level listed in Table 64431-A for selenium is 0.05 mg/L. |
Objective/Criterion Reference: |
Water Quality Control Plan (Basin Plan) for the North Coast Region |
Objective/Criterion Reference: |
Maximum Contaminant Levels for organic and inorganic chemicals. CCR Title 22 |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
Data for this line of evidence for Klamath River HU, Shasta River HA was collected at 1 monitoring site [ Shasta River at Hwy 263 - 105SH1452] |
Temporal Representation: |
Data was collected over the time period 2/27/2002-11/16/2006. |
Environmental Conditions: |
There are no known environmental conditions (e.g., seasonality, land use practices, fire events, storms, etc.) that are related to these data. |
QAPP Information: |
Quality control was conducted in accordance with the SWAMP Quality Assurance Management Plan (SWAMP 2002). |
QAPP Information Reference(s): |
Quality Assurance Management Plan for the State of California's Surface Water Ambient Monitoring Program. Sacramento, CA. State Water Resources Control Board. SWAMP. December 2002 (1st version)
|
|
Line of Evidence (LOE) for Decision ID 104948, Selenium
|
Region 1 |
Klamath River HU, Shasta River HA |
|
|
LOE ID: |
123409 |
|
Pollutant: |
Selenium |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Total |
|
Beneficial Use: |
Municipal & Domestic Supply |
|
Number of Samples: |
5 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
State Water Board staff re-assessed SWAMP data for Klamath River HU, Shasta River HA to determine beneficial use support and results are as follows: 0 of 5 samples exceed the criterion for Selenium, Total. This LOE re-assesses data from LOE 21509 from the 2010 Integrated Report. Data were re-assessed in order to (1) update the numeric objective, and (2) evaluate these data in their own LOE, instead of being evaluated in the same LOE as other metals data. |
Data Reference: |
Surface Water Ambient Monitoring Program (SWAMP). Summary Report for the North Coast Region (RWQCB-1) for years 2000-2006. North Coast Regional Water Quality Control Board. March 2008 |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
Water Quality Control Plan, North Coast Region (NCRWQCB 2011): Waters designated for use as domestic or municipal supply (MUN) shall not contain concentrations of chemical constituents in excess of the limits specified in California Code of Regulations, Title 22, Chapter 15. The maximum contaminant level listed in Table 64431-A for selenium is 0.05 mg/L. |
Objective/Criterion Reference: |
Water Quality Control Plan (Basin Plan) for the North Coast Region |
Objective/Criterion Reference: |
Maximum Contaminant Levels for organic and inorganic chemicals. CCR Title 22 |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
Data for this line of evidence for Klamath River HU, Shasta River HA was collected at 1 monitoring site [ Shasta River at Montague - 105SHAMON] |
Temporal Representation: |
Data was collected over the time period 10/7/2002-6/19/2003. |
Environmental Conditions: |
There are no known environmental conditions (e.g., seasonality, land use practices, fire events, storms, etc.) that are related to these data. |
QAPP Information: |
Quality control was conducted in accordance with the SWAMP Quality Assurance Management Plan (SWAMP 2002). |
QAPP Information Reference(s): |
Quality Assurance Management Plan for the State of California's Surface Water Ambient Monitoring Program. Sacramento, CA. State Water Resources Control Board. SWAMP. December 2002 (1st version)
|
|
Line of Evidence (LOE) for Decision ID 104948, Selenium
|
Region 1 |
Klamath River HU, Shasta River HA |
|
|
LOE ID: |
105182 |
|
Pollutant: |
Selenium |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Total |
|
Beneficial Use: |
Municipal & Domestic Supply |
|
Number of Samples: |
5 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP RWB1 Monitoring data for Klamath River HU, Shasta River HA to determine beneficial use support and results are as follows: 0 of 5 samples exceeded the water quality standard for Selenium. |
Data Reference: |
Water Quality Assessment Data for the 2018 solicitation cycle submitted through CEDEN for SWAMP RWB1 Monitoring .
|
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
Water Quality Control Plan, North Coast Region (NCRWQCB 2018): Waters designated for use as domestic or municipal supply (MUN) shall not contain concentrations of chemical constituents in excess of the limits specified in California Code of Regulations, Title 22, Chapter 15. The maximum contaminant level listed in Table 64431-A for selenium is 0.05 mg/L. |
Objective/Criterion Reference: |
Water Quality Control Plan (Basin Plan) for the North Coast Region |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
The samples were collected at 1 monitoring site(s) (105SH1452) |
Temporal Representation: |
The samples were collected between the dates of 2013-03-06 and 2013-11-20 |
Environmental Conditions: |
|
QAPP Information: |
Quality Assurance Program Plan and Standard Operating Procedures for SWAMP program |
QAPP Information Reference(s): |
Quality Assurance Program Plans, Quality Assurance Project Plans, and Standard Operating Procedures for the SWAMP program |
|
Line of Evidence (LOE) for Decision ID 104948, Selenium
|
Region 1 |
Klamath River HU, Shasta River HA |
|
|
LOE ID: |
43328 |
|
Pollutant: |
Selenium |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Total |
|
Beneficial Use: |
Municipal & Domestic Supply |
|
Number of Samples: |
4 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP data for Klamath River HU, Shasta River HA to determine beneficial use support and results are as follows: 0 of 4 samples exceed the criterion for Selenium. |
Data Reference: |
RWB1 Trend Maintenance Periods FYs 2007 2008 |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
Water Quality Control Plan, North Coast Region (NCRWQCB 2011): Waters designated for use as domestic or municipal supply (MUN) shall not contain concentrations of chemical constituents in excess of the limits specified in California Code of Regulations, Title 22, Chapter 15. The maximum contaminant level listed in Table 64431-A for selenium is 0.05 mg/L. |
Objective/Criterion Reference: |
Maximum Contaminant Levels for organic and inorganic chemicals. CCR Title 22 |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
Data for this line of evidence for Klamath River HU, Shasta River HA was collected at 1 monitoring site [ Shasta River near Edgewood - 105SHAEDG] |
Temporal Representation: |
Data was collected over the time period 11/15/2007-7/16/2008. |
Environmental Conditions: |
Staff is not aware of any special conditions that might affect interpretation of the data. |
QAPP Information: |
The SWAMP QAPP (2008) was followed. |
QAPP Information Reference(s): |
Surface Water Ambient Monitoring Program Quality Assurance Program Plan |
|
Line of Evidence (LOE) for Decision ID 104948, Selenium
|
Region 1 |
Klamath River HU, Shasta River HA |
|
|
LOE ID: |
123411 |
|
Pollutant: |
Selenium |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Total |
|
Beneficial Use: |
Municipal & Domestic Supply |
|
Number of Samples: |
7 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
State Water Board staff re-assessed SWAMP data for Klamath River HU, Shasta River HA to determine beneficial use support and results are as follows: 0 of 7 samples exceed the criterion for Selenium, Total. This LOE re-assesses data from LOE 21509 from the 2010 Integrated Report. Data were re-assessed in order to (1) update the numeric objective, and (2) evaluate these data in their own LOE, instead of being evaluated in the same LOE as other metals data. |
Data Reference: |
Surface Water Ambient Monitoring Program (SWAMP). Summary Report for the North Coast Region (RWQCB-1) for years 2000-2006. North Coast Regional Water Quality Control Board. March 2008 |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
Water Quality Control Plan, North Coast Region (NCRWQCB 2011): Waters designated for use as domestic or municipal supply (MUN) shall not contain concentrations of chemical constituents in excess of the limits specified in California Code of Regulations, Title 22, Chapter 15. The maximum contaminant level listed in Table 64431-A for selenium is 0.05 mg/L. |
Objective/Criterion Reference: |
Water Quality Control Plan (Basin Plan) for the North Coast Region |
Objective/Criterion Reference: |
Maximum Contaminant Levels for organic and inorganic chemicals. CCR Title 22 |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
Data for this line of evidence for Klamath River HU, Shasta River HA was collected at 1 monitoring site [ Yreka Creek at Anderson Rd - 105YREAND] |
Temporal Representation: |
Data was collected over the time period 10/9/2002-6/20/2005. |
Environmental Conditions: |
There are no known environmental conditions (e.g., seasonality, land use practices, fire events, storms, etc.) that are related to these data. |
QAPP Information: |
Quality control was conducted in accordance with the SWAMP Quality Assurance Management Plan (SWAMP 2002). |
QAPP Information Reference(s): |
Quality Assurance Management Plan for the State of California's Surface Water Ambient Monitoring Program. Sacramento, CA. State Water Resources Control Board. SWAMP. December 2002 (1st version)
|
|
Line of Evidence (LOE) for Decision ID 104948, Selenium
|
Region 1 |
Klamath River HU, Shasta River HA |
|
|
LOE ID: |
43349 |
|
Pollutant: |
Selenium |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Total |
|
Beneficial Use: |
Municipal & Domestic Supply |
|
Number of Samples: |
4 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP data for Klamath River HU, Shasta River HA to determine beneficial use support and results are as follows: 0 of 4 samples exceed the criterion for Selenium. |
Data Reference: |
RWB1 Trend Maintenance Periods FYs 2007 2008 |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
Water Quality Control Plan, North Coast Region (NCRWQCB 2011): Waters designated for use as domestic or municipal supply (MUN) shall not contain concentrations of chemical constituents in excess of the limits specified in California Code of Regulations, Title 22, Chapter 15. The maximum contaminant level listed in Table 64431-A for selenium is 0.05 mg/L. |
Objective/Criterion Reference: |
Maximum Contaminant Levels for organic and inorganic chemicals. CCR Title 22 |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
Data for this line of evidence for Klamath River HU, Shasta River HA was collected at 1 monitoring site [ Shasta River at Hwy 263 - 105SHA263] |
Temporal Representation: |
Data was collected over the time period 11/15/2007-7/16/2008. |
Environmental Conditions: |
Staff is not aware of any special conditions that might affect interpretation of the data. |
QAPP Information: |
The SWAMP QAPP (2008) was followed. |
QAPP Information Reference(s): |
Surface Water Ambient Monitoring Program Quality Assurance Program Plan |
|
Line of Evidence (LOE) for Decision ID 104948, Selenium
|
Region 1 |
Klamath River HU, Shasta River HA |
|
|
LOE ID: |
105183 |
|
Pollutant: |
Selenium |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Total |
|
Beneficial Use: |
Cold Freshwater Habitat |
|
Number of Samples: |
5 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP RWB1 Monitoring data for Klamath River HU, Shasta River HA to determine beneficial use support and results are as follows: 0 of 5 samples exceeded the water quality standard for Selenium. |
Data Reference: |
Water Quality Assessment Data for the 2018 solicitation cycle submitted through CEDEN for SWAMP RWB1 Monitoring .
|
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
Water Quality Control Plan, North Coast Region (NCRWQCB 2018): All waters shall be maintained free of toxic substances in concentrations that are toxic to, or that produce detrimental physiological responses in human, plant, animal, or aquatic life. The established numeric selenium criterion continuous concentration (expressed as a 4-day average) to protect aquatic life in freshwater is 5 ug/L (California Toxics Rule, 2000). |
Objective/Criterion Reference: |
Water Quality Standards 2000. Establishment of numeric criteria for priority toxic pollutants for the State of California: Rules and regulations. Federal Register Vol. 65, No. 97. Washington, D.C.: Environmental Protection Agency |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
The samples were collected at 1 monitoring site(s) (105SH9274) |
Temporal Representation: |
The samples were collected between the dates of 2013-03-07 and 2013-11-20 |
Environmental Conditions: |
|
QAPP Information: |
Quality Assurance Program Plan and Standard Operating Procedures for SWAMP program |
QAPP Information Reference(s): |
Quality Assurance Program Plans, Quality Assurance Project Plans, and Standard Operating Procedures for the SWAMP program |
|
Line of Evidence (LOE) for Decision ID 104948, Selenium
|
Region 1 |
Klamath River HU, Shasta River HA |
|
|
LOE ID: |
105181 |
|
Pollutant: |
Selenium |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Total |
|
Beneficial Use: |
Cold Freshwater Habitat |
|
Number of Samples: |
5 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP RWB1 Monitoring data for Klamath River HU, Shasta River HA to determine beneficial use support and results are as follows: 0 of 5 samples exceeded the water quality standard for Selenium. |
Data Reference: |
Water Quality Assessment Data for the 2018 solicitation cycle submitted through CEDEN for SWAMP RWB1 Monitoring .
|
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
Water Quality Control Plan, North Coast Region (NCRWQCB 2018): All waters shall be maintained free of toxic substances in concentrations that are toxic to, or that produce detrimental physiological responses in human, plant, animal, or aquatic life. The established numeric selenium criterion continuous concentration (expressed as a 4-day average) to protect aquatic life in freshwater is 5 ug/L (California Toxics Rule, 2000). |
Objective/Criterion Reference: |
Water Quality Standards 2000. Establishment of numeric criteria for priority toxic pollutants for the State of California: Rules and regulations. Federal Register Vol. 65, No. 97. Washington, D.C.: Environmental Protection Agency |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
The samples were collected at 1 monitoring site(s) (105SH1452) |
Temporal Representation: |
The samples were collected between the dates of 2013-03-06 and 2013-11-20 |
Environmental Conditions: |
|
QAPP Information: |
Quality Assurance Program Plan and Standard Operating Procedures for SWAMP program |
QAPP Information Reference(s): |
Quality Assurance Program Plans, Quality Assurance Project Plans, and Standard Operating Procedures for the SWAMP program |
|
Line of Evidence (LOE) for Decision ID 104948, Selenium
|
Region 1 |
Klamath River HU, Shasta River HA |
|
|
LOE ID: |
43408 |
|
Pollutant: |
Selenium |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Total |
|
Beneficial Use: |
Cold Freshwater Habitat |
|
Number of Samples: |
4 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP data for Klamath River HU, Shasta River HA to determine beneficial use support and results are as follows: 0 of 4 samples exceed the criterion for Selenium. |
Data Reference: |
RWB1 Trend Maintenance Periods FYs 2007 2008 |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
Water Quality Control Plan, North Coast Region (NCRWQCB 2011): All waters shall be maintained free of toxic substances in concentrations that are toxic to, or that produce detrimental physiological responses in human, plant, animal, or aquatic life. The established numeric selenium criterion continuous concentration (expressed as a 4-day average) to protect aquatic life in freshwater is 5 ug/L (California Toxics Rule, 2000). |
Objective/Criterion Reference: |
Code of Federal Regulations 40 part 131.38 Establishment of numeric criteria for priority toxic pollutants for the State of California. 7/1/2011 Edition |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
Data for this line of evidence for Klamath River HU, Shasta River HA was collected at 1 monitoring site [ Shasta River at Hwy 263 - 105SHA263] |
Temporal Representation: |
Data was collected over the time period 11/15/2007-7/16/2008. |
Environmental Conditions: |
Staff is not aware of any special conditions that might affect interpretation of the data. |
QAPP Information: |
The SWAMP QAPP (2008) was followed. |
QAPP Information Reference(s): |
Surface Water Ambient Monitoring Program Quality Assurance Program Plan |
|
Line of Evidence (LOE) for Decision ID 104948, Selenium
|
Region 1 |
Klamath River HU, Shasta River HA |
|
|
LOE ID: |
43405 |
|
Pollutant: |
Selenium |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Total |
|
Beneficial Use: |
Cold Freshwater Habitat |
|
Number of Samples: |
4 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP data for Klamath River HU, Shasta River HA to determine beneficial use support and results are as follows: 0 of 4 samples exceed the criterion for Selenium. |
Data Reference: |
RWB1 Trend Maintenance Periods FYs 2007 2008 |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
Water Quality Control Plan, North Coast Region (NCRWQCB 2011): All waters shall be maintained free of toxic substances in concentrations that are toxic to, or that produce detrimental physiological responses in human, plant, animal, or aquatic life. The established numeric selenium criterion continuous concentration (expressed as a 4-day average) to protect aquatic life in freshwater is 5 ug/L (California Toxics Rule, 2000). |
Objective/Criterion Reference: |
Code of Federal Regulations 40 part 131.38 Establishment of numeric criteria for priority toxic pollutants for the State of California. 7/1/2011 Edition |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
Data for this line of evidence for Klamath River HU, Shasta River HA was collected at 1 monitoring site [ Shasta River near Edgewood - 105SHAEDG] |
Temporal Representation: |
Data was collected over the time period 11/15/2007-7/16/2008. |
Environmental Conditions: |
Staff is not aware of any special conditions that might affect interpretation of the data. |
QAPP Information: |
The SWAMP QAPP (2008) was followed. |
QAPP Information Reference(s): |
Surface Water Ambient Monitoring Program Quality Assurance Program Plan |
|
Line of Evidence (LOE) for Decision ID 103855, Silver
|
Region 1 |
Klamath River HU, Shasta River HA |
|
|
LOE ID: |
110481 |
|
Pollutant: |
Silver |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Total |
|
Beneficial Use: |
Municipal & Domestic Supply |
|
Number of Samples: |
5 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP RWB1 Monitoring data for Klamath River HU, Shasta River HA to determine beneficial use support and results are as follows: 0 of 5 samples exceeded the water quality standard for Silver. |
Data Reference: |
Water Quality Assessment Data for the 2018 solicitation cycle submitted through CEDEN for SWAMP RWB1 Monitoring .
|
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
Water Quality Control Plan, North Coast Region (NCRWQCB 2018): Waters designated for use as domestic or municipal supply (MUN) shall not contain concentrations of chemical constituents in excess of the limits specified in California Code of Regulations, Title 22, Chapter 15. The secondary maximum contaminant level listed in Table 64449-A for silver is 0.1 mg/L. |
Objective/Criterion Reference: |
Water Quality Control Plan (Basin Plan) for the North Coast Region |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
The samples were collected at 1 monitoring site(s) (105SH1452) |
Temporal Representation: |
The samples were collected between the dates of 2013-03-06 and 2013-11-20 |
Environmental Conditions: |
|
QAPP Information: |
Quality Assurance Program Plan and Standard Operating Procedures for SWAMP program |
QAPP Information Reference(s): |
Quality Assurance Program Plans, Quality Assurance Project Plans, and Standard Operating Procedures for the SWAMP program |
|
Line of Evidence (LOE) for Decision ID 103855, Silver
|
Region 1 |
Klamath River HU, Shasta River HA |
|
|
LOE ID: |
105186 |
|
Pollutant: |
Silver |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Dissolved |
|
Beneficial Use: |
Cold Freshwater Habitat |
|
Number of Samples: |
5 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP RWB1 Monitoring data for Klamath River HU, Shasta River HA to determine beneficial use support and results are as follows: 0 of 5 samples exceeded the water quality standard for Silver. |
Data Reference: |
Water Quality Assessment Data for the 2018 solicitation cycle submitted through CEDEN for SWAMP RWB1 Monitoring .
|
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
California Toxics Rule (CTR) lists criterion maximum concentrations to protect aquatic life in freshwater. The criterion in freshwater is hardness dependent for each sample and varies based on the ambient hardness during sampling. Section (b)(1) in CTR contains the hardness dependent formula for the metals criterion. |
Objective/Criterion Reference: |
Water Quality Standards 2000. Establishment of numeric criteria for priority toxic pollutants for the State of California: Rules and regulations. Federal Register Vol. 65, No. 97. Washington, D.C.: Environmental Protection Agency |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
The samples were collected at 1 monitoring site(s) (105SH1452) |
Temporal Representation: |
The samples were collected between the dates of 2013-03-06 and 2013-11-20 |
Environmental Conditions: |
|
QAPP Information: |
Quality Assurance Program Plan and Standard Operating Procedures for SWAMP program |
QAPP Information Reference(s): |
Quality Assurance Program Plans, Quality Assurance Project Plans, and Standard Operating Procedures for the SWAMP program |
|
Line of Evidence (LOE) for Decision ID 103855, Silver
|
Region 1 |
Klamath River HU, Shasta River HA |
|
|
LOE ID: |
123437 |
|
Pollutant: |
Silver |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Total |
|
Beneficial Use: |
Municipal & Domestic Supply |
|
Number of Samples: |
3 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
State Water Board staff re-assessed SWAMP data for Klamath River HU, Shasta River HA to determine beneficial use support and results are as follows: 0 of 3 samples exceed the criterion for Silver, Total. This LOE re-assesses data from LOE 21509 from the 2010 Integrated Report. Data were re-assessed in order to (1) update the numeric objective, and (2) evaluate these data in their own LOE, instead of being evaluated in the same LOE as other metals data. |
Data Reference: |
Surface Water Ambient Monitoring Program (SWAMP). Summary Report for the North Coast Region (RWQCB-1) for years 2000-2006. North Coast Regional Water Quality Control Board. March 2008 |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
Water Quality Control Plan, North Coast Region (NCRWQCB 2011): Waters designated for use as domestic or municipal supply (MUN) shall not contain concentrations of chemical constituents in excess of the limits specified in California Code of Regulations, Title 22, Chapter 15. The secondary maximum contaminant level listed in Table 64449-A for silver is 0.1 mg/L. |
Objective/Criterion Reference: |
Water Quality Control Plan (Basin Plan) for the North Coast Region |
Objective/Criterion Reference: |
Secondary Maximum Contaminant Levels and Compliance. CCR Title 22 section 64449. |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
Data for this line of evidence for Klamath River HU, Shasta River HA was collected at 1 monitoring site [ Yreka Creek at Highway 3 - 105YREHW3] |
Temporal Representation: |
Data was collected over the time period 10/21/2004-6/20/2005. |
Environmental Conditions: |
There are no known environmental conditions (e.g., seasonality, land use practices, fire events, storms, etc.) that are related to these data. |
QAPP Information: |
Quality control was conducted in accordance with the SWAMP Quality Assurance Management Plan (SWAMP 2002). |
QAPP Information Reference(s): |
Letter requesting acceptance of late submittal |
|
Line of Evidence (LOE) for Decision ID 103855, Silver
|
Region 1 |
Klamath River HU, Shasta River HA |
|
|
LOE ID: |
123436 |
|
Pollutant: |
Silver |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Total |
|
Beneficial Use: |
Municipal & Domestic Supply |
|
Number of Samples: |
7 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
State Water Board staff re-assessed SWAMP data for Klamath River HU, Shasta River HA to determine beneficial use support and results are as follows: 0 of 7 samples exceed the criterion for Silver, Total. This LOE re-assesses data from LOE 21509 from the 2010 Integrated Report. Data were re-assessed in order to (1) update the numeric objective, and (2) evaluate these data in their own LOE, instead of being evaluated in the same LOE as other metals data. |
Data Reference: |
Surface Water Ambient Monitoring Program (SWAMP). Summary Report for the North Coast Region (RWQCB-1) for years 2000-2006. North Coast Regional Water Quality Control Board. March 2008 |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
Water Quality Control Plan, North Coast Region (NCRWQCB 2011): Waters designated for use as domestic or municipal supply (MUN) shall not contain concentrations of chemical constituents in excess of the limits specified in California Code of Regulations, Title 22, Chapter 15. The secondary maximum contaminant level listed in Table 64449-A for silver is 0.1 mg/L. |
Objective/Criterion Reference: |
Water Quality Control Plan (Basin Plan) for the North Coast Region |
Objective/Criterion Reference: |
Secondary Maximum Contaminant Levels and Compliance. CCR Title 22 section 64449. |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
Data for this line of evidence for Klamath River HU, Shasta River HA was collected at 1 monitoring site [ Yreka Creek at Anderson Rd - 105YREAND] |
Temporal Representation: |
Data was collected over the time period 10/9/2002-6/20/2005. |
Environmental Conditions: |
There are no known environmental conditions (e.g., seasonality, land use practices, fire events, storms, etc.) that are related to these data. |
QAPP Information: |
Quality control was conducted in accordance with the SWAMP Quality Assurance Management Plan (SWAMP 2002). |
QAPP Information Reference(s): |
Letter requesting acceptance of late submittal |
|
Line of Evidence (LOE) for Decision ID 103855, Silver
|
Region 1 |
Klamath River HU, Shasta River HA |
|
|
LOE ID: |
43357 |
|
Pollutant: |
Silver |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Total |
|
Beneficial Use: |
Municipal & Domestic Supply |
|
Number of Samples: |
4 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP data for Klamath River HU, Shasta River HA to determine beneficial use support and results are as follows: 0 of 4 samples exceed the criterion for Silver. |
Data Reference: |
RWB1 Trend Maintenance Periods FYs 2007 2008 |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
Water Quality Control Plan, North Coast Region (NCRWQCB 2011): Waters designated for use as domestic or municipal supply (MUN) shall not contain concentrations of chemical constituents in excess of the limits specified in California Code of Regulations, Title 22, Chapter 15. The secondary maximum contaminant level listed in Table 64449-A for silver is 0.1 mg/L. |
Objective/Criterion Reference: |
Secondary Maximum Contaminant Levels and Compliance. CCR Title 22 section 64449. |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
Data for this line of evidence for Klamath River HU, Shasta River HA was collected at 1 monitoring site [ Shasta River near Edgewood - 105SHAEDG] |
Temporal Representation: |
Data was collected over the time period 11/15/2007-7/16/2008. |
Environmental Conditions: |
Staff is not aware of any special conditions that might affect interpretation of the data. |
QAPP Information: |
The SWAMP QAPP (2008) was followed. |
QAPP Information Reference(s): |
Surface Water Ambient Monitoring Program Quality Assurance Program Plan |
|
Line of Evidence (LOE) for Decision ID 103855, Silver
|
Region 1 |
Klamath River HU, Shasta River HA |
|
|
LOE ID: |
43375 |
|
Pollutant: |
Silver |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Total |
|
Beneficial Use: |
Municipal & Domestic Supply |
|
Number of Samples: |
4 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP data for Klamath River HU, Shasta River HA to determine beneficial use support and results are as follows: 0 of 4 samples exceed the criterion for Silver. |
Data Reference: |
RWB1 Trend Maintenance Periods FYs 2007 2008 |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
Water Quality Control Plan, North Coast Region (NCRWQCB 2011): Waters designated for use as domestic or municipal supply (MUN) shall not contain concentrations of chemical constituents in excess of the limits specified in California Code of Regulations, Title 22, Chapter 15. The secondary maximum contaminant level listed in Table 64449-A for silver is 0.1 mg/L. |
Objective/Criterion Reference: |
Secondary Maximum Contaminant Levels and Compliance. CCR Title 22 section 64449. |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
Data for this line of evidence for Klamath River HU, Shasta River HA was collected at 1 monitoring site [ Shasta River at Hwy 263 - 105SHA263] |
Temporal Representation: |
Data was collected over the time period 11/15/2007-7/16/2008. |
Environmental Conditions: |
Staff is not aware of any special conditions that might affect interpretation of the data. |
QAPP Information: |
The SWAMP QAPP (2008) was followed. |
QAPP Information Reference(s): |
Surface Water Ambient Monitoring Program Quality Assurance Program Plan |
|
Line of Evidence (LOE) for Decision ID 103855, Silver
|
Region 1 |
Klamath River HU, Shasta River HA |
|
|
LOE ID: |
123425 |
|
Pollutant: |
Silver |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Total |
|
Beneficial Use: |
Municipal & Domestic Supply |
|
Number of Samples: |
5 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
State Water Board staff re-assessed SWAMP data for Klamath River HU, Shasta River HA to determine beneficial use support and results are as follows: 0 of 5 samples exceed the criterion for Silver, Total. This LOE re-assesses data from LOE 21509 from the 2010 Integrated Report. Data were re-assessed in order to (1) update the numeric objective, and (2) evaluate these data in their own LOE, instead of being evaluated in the same LOE as other metals data. |
Data Reference: |
Surface Water Ambient Monitoring Program (SWAMP). Summary Report for the North Coast Region (RWQCB-1) for years 2000-2006. North Coast Regional Water Quality Control Board. March 2008 |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
Water Quality Control Plan, North Coast Region (NCRWQCB 2011): Waters designated for use as domestic or municipal supply (MUN) shall not contain concentrations of chemical constituents in excess of the limits specified in California Code of Regulations, Title 22, Chapter 15. The secondary maximum contaminant level listed in Table 64449-A for silver is 0.1 mg/L. |
Objective/Criterion Reference: |
Water Quality Control Plan (Basin Plan) for the North Coast Region |
Objective/Criterion Reference: |
Secondary Maximum Contaminant Levels and Compliance. CCR Title 22 section 64449. |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
Data for this line of evidence for Klamath River HU, Shasta River HA was collected at 1 monitoring site [ Shasta River near Edgewood - 105SH9274] |
Temporal Representation: |
Data was collected over the time period 10/7/2002-6/19/2003. |
Environmental Conditions: |
There are no known environmental conditions (e.g., seasonality, land use practices, fire events, storms, etc.) that are related to these data. |
QAPP Information: |
Quality control was conducted in accordance with the SWAMP Quality Assurance Management Plan (SWAMP 2002). |
QAPP Information Reference(s): |
Letter requesting acceptance of late submittal |
|
Line of Evidence (LOE) for Decision ID 103855, Silver
|
Region 1 |
Klamath River HU, Shasta River HA |
|
|
LOE ID: |
123423 |
|
Pollutant: |
Silver |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Total |
|
Beneficial Use: |
Municipal & Domestic Supply |
|
Number of Samples: |
19 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
State Water Board staff re-assessed SWAMP data for Klamath River HU, Shasta River HA to determine beneficial use support and results are as follows: 0 of 19 samples exceed the criterion for Silver, Total. This LOE re-assesses data from LOE 21509 from the 2010 Integrated Report. Data were re-assessed in order to (1) update the numeric objective, and (2) evaluate these data in their own LOE, instead of being evaluated in the same LOE as other metals data. |
Data Reference: |
Surface Water Ambient Monitoring Program (SWAMP). Summary Report for the North Coast Region (RWQCB-1) for years 2000-2006. North Coast Regional Water Quality Control Board. March 2008 |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
Water Quality Control Plan, North Coast Region (NCRWQCB 2011): Waters designated for use as domestic or municipal supply (MUN) shall not contain concentrations of chemical constituents in excess of the limits specified in California Code of Regulations, Title 22, Chapter 15. The secondary maximum contaminant level listed in Table 64449-A for silver is 0.1 mg/L. |
Objective/Criterion Reference: |
Water Quality Control Plan (Basin Plan) for the North Coast Region |
Objective/Criterion Reference: |
Secondary Maximum Contaminant Levels and Compliance. CCR Title 22 section 64449. |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
Data for this line of evidence for Klamath River HU, Shasta River HA was collected at 1 monitoring site [ Shasta River at Hwy 263 - 105SH1452] |
Temporal Representation: |
Data was collected over the time period 2/27/2002-11/16/2006. |
Environmental Conditions: |
There are no known environmental conditions (e.g., seasonality, land use practices, fire events, storms, etc.) that are related to these data. |
QAPP Information: |
Quality control was conducted in accordance with the SWAMP Quality Assurance Management Plan (SWAMP 2002). |
QAPP Information Reference(s): |
Quality Assurance Management Plan for the State of California's Surface Water Ambient Monitoring Program. Sacramento, CA. State Water Resources Control Board. SWAMP. December 2002 (1st version)
|
|
Line of Evidence (LOE) for Decision ID 103855, Silver
|
Region 1 |
Klamath River HU, Shasta River HA |
|
|
LOE ID: |
123424 |
|
Pollutant: |
Silver |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Total |
|
Beneficial Use: |
Municipal & Domestic Supply |
|
Number of Samples: |
5 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
State Water Board staff re-assessed SWAMP data for Klamath River HU, Shasta River HA to determine beneficial use support and results are as follows: 0 of 5 samples exceed the criterion for Silver, Total. This LOE re-assesses data from LOE 21509 from the 2010 Integrated Report. Data were re-assessed in order to (1) update the numeric objective, and (2) evaluate these data in their own LOE, instead of being evaluated in the same LOE as other metals data. |
Data Reference: |
Surface Water Ambient Monitoring Program (SWAMP). Summary Report for the North Coast Region (RWQCB-1) for years 2000-2006. North Coast Regional Water Quality Control Board. March 2008 |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
Water Quality Control Plan, North Coast Region (NCRWQCB 2011): Waters designated for use as domestic or municipal supply (MUN) shall not contain concentrations of chemical constituents in excess of the limits specified in California Code of Regulations, Title 22, Chapter 15. The secondary maximum contaminant level listed in Table 64449-A for silver is 0.1 mg/L. |
Objective/Criterion Reference: |
Water Quality Control Plan (Basin Plan) for the North Coast Region |
Objective/Criterion Reference: |
Secondary Maximum Contaminant Levels and Compliance. CCR Title 22 section 64449. |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
Data for this line of evidence for Klamath River HU, Shasta River HA was collected at 1 monitoring site [ Shasta River at Montague - 105SHAMON] |
Temporal Representation: |
Data was collected over the time period 10/7/2002-6/19/2003. |
Environmental Conditions: |
There are no known environmental conditions (e.g., seasonality, land use practices, fire events, storms, etc.) that are related to these data. |
QAPP Information: |
Quality control was conducted in accordance with the SWAMP Quality Assurance Management Plan (SWAMP 2002). |
QAPP Information Reference(s): |
Quality Assurance Management Plan for the State of California's Surface Water Ambient Monitoring Program. Sacramento, CA. State Water Resources Control Board. SWAMP. December 2002 (1st version)
|
|
Line of Evidence (LOE) for Decision ID 103855, Silver
|
Region 1 |
Klamath River HU, Shasta River HA |
|
|
LOE ID: |
32578 |
|
Pollutant: |
Silver |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Total |
|
Beneficial Use: |
Cold Freshwater Habitat |
|
Number of Samples: |
4 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
None of the 4 samples exceeded the hardness based criteria calculated for silver. |
Data Reference: |
RWB1 Trend Maintenance Periods FYs 2007 2008 |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
Water Quality Control Plan, North Coast Region (NCRWQCB 2011): All waters shall be maintained free of toxic substances in concentrations that are toxic to, or that produce detrimental physiological responses in human, plant, animal, or aquatic life. California Toxics Rule (CTR) lists criterion maximum concentrations (1-hour average) to protect aquatic life in freshwater. The criterion in freshwater is hardness dependent for each sample and varies based on the ambient hardness during sampling. Section (b)(1) in CTR contains the hardness dependent formula for the metals criterion. |
Objective/Criterion Reference: |
Code of Federal Regulations 40 part 131.38 Establishment of numeric criteria for priority toxic pollutants for the State of California. 7/1/2011 Edition |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
Samples collected at station 105SHA263 (Shasta River at Hwy 263). |
Temporal Representation: |
Samples collected between 11/15/2007 and 7/16/2008. |
Environmental Conditions: |
|
QAPP Information: |
SWAMP QAPP (2008) was followed. |
QAPP Information Reference(s): |
Surface Water Ambient Monitoring Program Quality Assurance Program Plan |
|
Line of Evidence (LOE) for Decision ID 103855, Silver
|
Region 1 |
Klamath River HU, Shasta River HA |
|
|
LOE ID: |
32584 |
|
Pollutant: |
Silver |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Total |
|
Beneficial Use: |
Cold Freshwater Habitat |
|
Number of Samples: |
4 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
None of the 4 samples exceeded the hardness based criteria calculated for silver. |
Data Reference: |
RWB1 Trend Maintenance Periods FYs 2007 2008 |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
Water Quality Control Plan, North Coast Region (NCRWQCB 2011): All waters shall be maintained free of toxic substances in concentrations that are toxic to, or that produce detrimental physiological responses in human, plant, animal, or aquatic life. California Toxics Rule (CTR) lists criterion maximum concentrations (1-hour average) to protect aquatic life in freshwater. The criterion in freshwater is hardness dependent for each sample and varies based on the ambient hardness during sampling. Section (b)(1) in CTR contains the hardness dependent formula for the metals criterion. |
Objective/Criterion Reference: |
Code of Federal Regulations 40 part 131.38 Establishment of numeric criteria for priority toxic pollutants for the State of California. 7/1/2011 Edition |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
Samples collected at station 105SHAEDG (Shasta River near Edgewood). |
Temporal Representation: |
Samples collected between 11/15/2007 and 7/16/2008. |
Environmental Conditions: |
|
QAPP Information: |
SWAMP QAPP (2008) was followed. |
QAPP Information Reference(s): |
Surface Water Ambient Monitoring Program Quality Assurance Program Plan |
|
Line of Evidence (LOE) for Decision ID 103855, Silver
|
Region 1 |
Klamath River HU, Shasta River HA |
|
|
LOE ID: |
110480 |
|
Pollutant: |
Silver |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Dissolved |
|
Beneficial Use: |
Warm Freshwater Habitat |
|
Number of Samples: |
5 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP RWB1 Monitoring data for Klamath River HU, Shasta River HA to determine beneficial use support and results are as follows: 0 of 5 samples exceeded the water quality standard for Silver. |
Data Reference: |
Water Quality Assessment Data for the 2018 solicitation cycle submitted through CEDEN for SWAMP RWB1 Monitoring .
|
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
California Toxics Rule (CTR) lists criterion maximum concentrations to protect aquatic life in freshwater. The criterion in freshwater is hardness dependent for each sample and varies based on the ambient hardness during sampling. Section (b)(1) in CTR contains the hardness dependent formula for the metals criterion. |
Objective/Criterion Reference: |
Water Quality Standards 2000. Establishment of numeric criteria for priority toxic pollutants for the State of California: Rules and regulations. Federal Register Vol. 65, No. 97. Washington, D.C.: Environmental Protection Agency |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
The samples were collected at 1 monitoring site(s) (105SH9274) |
Temporal Representation: |
The samples were collected between the dates of 2013-03-07 and 2013-11-20 |
Environmental Conditions: |
|
QAPP Information: |
Quality Assurance Program Plan and Standard Operating Procedures for SWAMP program |
QAPP Information Reference(s): |
Quality Assurance Program Plans, Quality Assurance Project Plans, and Standard Operating Procedures for the SWAMP program |
|
Line of Evidence (LOE) for Decision ID 103855, Silver
|
Region 1 |
Klamath River HU, Shasta River HA |
|
|
LOE ID: |
110478 |
|
Pollutant: |
Silver |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Dissolved |
|
Beneficial Use: |
Warm Freshwater Habitat |
|
Number of Samples: |
5 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP RWB1 Monitoring data for Klamath River HU, Shasta River HA to determine beneficial use support and results are as follows: 0 of 5 samples exceeded the water quality standard for Silver. |
Data Reference: |
Water Quality Assessment Data for the 2018 solicitation cycle submitted through CEDEN for SWAMP RWB1 Monitoring .
|
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
California Toxics Rule (CTR) lists criterion maximum concentrations to protect aquatic life in freshwater. The criterion in freshwater is hardness dependent for each sample and varies based on the ambient hardness during sampling. Section (b)(1) in CTR contains the hardness dependent formula for the metals criterion. |
Objective/Criterion Reference: |
Water Quality Standards 2000. Establishment of numeric criteria for priority toxic pollutants for the State of California: Rules and regulations. Federal Register Vol. 65, No. 97. Washington, D.C.: Environmental Protection Agency |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
The samples were collected at 1 monitoring site(s) (105SH1452) |
Temporal Representation: |
The samples were collected between the dates of 2013-03-06 and 2013-11-20 |
Environmental Conditions: |
|
QAPP Information: |
Quality Assurance Program Plan and Standard Operating Procedures for SWAMP program |
QAPP Information Reference(s): |
Quality Assurance Program Plans, Quality Assurance Project Plans, and Standard Operating Procedures for the SWAMP program |
|
Line of Evidence (LOE) for Decision ID 103855, Silver
|
Region 1 |
Klamath River HU, Shasta River HA |
|
|
LOE ID: |
110479 |
|
Pollutant: |
Silver |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Dissolved |
|
Beneficial Use: |
Cold Freshwater Habitat |
|
Number of Samples: |
5 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP RWB1 Monitoring data for Klamath River HU, Shasta River HA to determine beneficial use support and results are as follows: 0 of 5 samples exceeded the water quality standard for Silver. |
Data Reference: |
Water Quality Assessment Data for the 2018 solicitation cycle submitted through CEDEN for SWAMP RWB1 Monitoring .
|
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
California Toxics Rule (CTR) lists criterion maximum concentrations to protect aquatic life in freshwater. The criterion in freshwater is hardness dependent for each sample and varies based on the ambient hardness during sampling. Section (b)(1) in CTR contains the hardness dependent formula for the metals criterion. |
Objective/Criterion Reference: |
Water Quality Standards 2000. Establishment of numeric criteria for priority toxic pollutants for the State of California: Rules and regulations. Federal Register Vol. 65, No. 97. Washington, D.C.: Environmental Protection Agency |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
The samples were collected at 1 monitoring site(s) (105SH9274) |
Temporal Representation: |
The samples were collected between the dates of 2013-03-07 and 2013-11-20 |
Environmental Conditions: |
|
QAPP Information: |
Quality Assurance Program Plan and Standard Operating Procedures for SWAMP program |
QAPP Information Reference(s): |
Quality Assurance Program Plans, Quality Assurance Project Plans, and Standard Operating Procedures for the SWAMP program |
|
Line of Evidence (LOE) for Decision ID 103855, Silver
|
Region 1 |
Klamath River HU, Shasta River HA |
|
|
LOE ID: |
110482 |
|
Pollutant: |
Silver |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Total |
|
Beneficial Use: |
Municipal & Domestic Supply |
|
Number of Samples: |
5 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP RWB1 Monitoring data for Klamath River HU, Shasta River HA to determine beneficial use support and results are as follows: 0 of 5 samples exceeded the water quality standard for Silver. |
Data Reference: |
Water Quality Assessment Data for the 2018 solicitation cycle submitted through CEDEN for SWAMP RWB1 Monitoring .
|
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
Water Quality Control Plan, North Coast Region (NCRWQCB 2018): Waters designated for use as domestic or municipal supply (MUN) shall not contain concentrations of chemical constituents in excess of the limits specified in California Code of Regulations, Title 22, Chapter 15. The secondary maximum contaminant level listed in Table 64449-A for silver is 0.1 mg/L. |
Objective/Criterion Reference: |
Water Quality Control Plan (Basin Plan) for the North Coast Region |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
The samples were collected at 1 monitoring site(s) (105SH9274) |
Temporal Representation: |
The samples were collected between the dates of 2013-03-07 and 2013-11-20 |
Environmental Conditions: |
|
QAPP Information: |
Quality Assurance Program Plan and Standard Operating Procedures for SWAMP program |
QAPP Information Reference(s): |
Quality Assurance Program Plans, Quality Assurance Project Plans, and Standard Operating Procedures for the SWAMP program |
|
Line of Evidence (LOE) for Decision ID 169750, Simazine
|
Region 1 |
Klamath River HU, Shasta River HA |
|
|
LOE ID: |
110488 |
|
Pollutant: |
Simazine |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Total |
|
Beneficial Use: |
Municipal & Domestic Supply |
|
Number of Samples: |
3 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP RWB1 Monitoring data for Klamath River HU, Shasta River HA to determine beneficial use support and results are as follows: 0 of 3 samples exceeded the water quality standard for Simazine. |
Data Reference: |
Water Quality Assessment Data for the 2018 solicitation cycle submitted through CEDEN for SWAMP RWB1 Monitoring .
|
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
Water Quality Control Plan, North Coast Region (NCRWQCB 2018): Waters designated for use as domestic or municipal supply (MUN) shall not contain concentrations of chemical constituents in excess of the limits specified in California Code of Regulations, Title 22, Chapter 15. The maximum contaminant level listed in Table 64444-A for simazine is 0.004 mg/L. |
Objective/Criterion Reference: |
Water Quality Control Plan (Basin Plan) for the North Coast Region |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
The samples were collected at 1 monitoring site(s) (105SH9274) |
Temporal Representation: |
The samples were collected between the dates of 2013-03-07 and 2013-11-20 |
Environmental Conditions: |
|
QAPP Information: |
Quality Assurance Program Plan and Standard Operating Procedures for SWAMP program |
QAPP Information Reference(s): |
Quality Assurance Program Plans, Quality Assurance Project Plans, and Standard Operating Procedures for the SWAMP program |
|
Line of Evidence (LOE) for Decision ID 169750, Simazine
|
Region 1 |
Klamath River HU, Shasta River HA |
|
|
LOE ID: |
110484 |
|
Pollutant: |
Simazine |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Total |
|
Beneficial Use: |
Municipal & Domestic Supply |
|
Number of Samples: |
3 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP RWB1 Monitoring data for Klamath River HU, Shasta River HA to determine beneficial use support and results are as follows: 0 of 3 samples exceeded the water quality standard for Simazine. |
Data Reference: |
Water Quality Assessment Data for the 2018 solicitation cycle submitted through CEDEN for SWAMP RWB1 Monitoring .
|
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
Water Quality Control Plan, North Coast Region (NCRWQCB 2018): Waters designated for use as domestic or municipal supply (MUN) shall not contain concentrations of chemical constituents in excess of the limits specified in California Code of Regulations, Title 22, Chapter 15. The maximum contaminant level listed in Table 64444-A for simazine is 0.004 mg/L. |
Objective/Criterion Reference: |
Water Quality Control Plan (Basin Plan) for the North Coast Region |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
The samples were collected at 1 monitoring site(s) (105SH1452) |
Temporal Representation: |
The samples were collected between the dates of 2013-03-06 and 2013-11-20 |
Environmental Conditions: |
|
QAPP Information: |
Quality Assurance Program Plan and Standard Operating Procedures for SWAMP program |
QAPP Information Reference(s): |
Quality Assurance Program Plans, Quality Assurance Project Plans, and Standard Operating Procedures for the SWAMP program |
|
Line of Evidence (LOE) for Decision ID 169750, Simazine
|
Region 1 |
Klamath River HU, Shasta River HA |
|
|
LOE ID: |
43336 |
|
Pollutant: |
Simazine |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Total |
|
Beneficial Use: |
Municipal & Domestic Supply |
|
Number of Samples: |
3 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP data for Klamath River HU, Shasta River HA to determine beneficial use support and results are as follows: 0 of 3 samples exceed the criterion for Simazine. |
Data Reference: |
RWB1 Trend Maintenance Periods FYs 2007 2008 |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
Water Quality Control Plan, North Coast Region (NCRWQCB 2011): Waters designated for use as domestic or municipal supply (MUN) shall not contain concentrations of chemical constituents in excess of the limits specified in California Code of Regulations, Title 22, Chapter 15. The maximum contaminant level listed in Table 64444-A for simazine is 0.004 mg/L. |
Objective/Criterion Reference: |
Maximum Contaminant Levels for organic and inorganic chemicals. CCR Title 22 |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
Data for this line of evidence for Klamath River HU, Shasta River HA was collected at 1 monitoring site [ Shasta River at Hwy 263 - 105SHA263] |
Temporal Representation: |
Data was collected over the time period 11/15/2007-7/16/2008. |
Environmental Conditions: |
Staff is not aware of any special conditions that might affect interpretation of the data. |
QAPP Information: |
The SWAMP QAPP (2008) was followed. |
QAPP Information Reference(s): |
Surface Water Ambient Monitoring Program Quality Assurance Program Plan |
|
Line of Evidence (LOE) for Decision ID 169750, Simazine
|
Region 1 |
Klamath River HU, Shasta River HA |
|
|
LOE ID: |
351031 |
|
Pollutant: |
Simazine |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Total |
|
Beneficial Use: |
Warm Freshwater Habitat |
|
Number of Samples: |
3 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed RWB1 Trend Maintenance Periods FYs 2007 2008 data for Klamath River HU, Shasta River HA to determine beneficial use support and results are as follows: 0 of 3 samples exceeded the water quality threshold for Simazine. |
Data Reference: |
RWB1 Trend Maintenance Periods FYs 2007 2008 |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
All waters shall be maintained free of toxic substances in concentrations which are toxic to, or which produce detrimental physiological responses in, human, plant, animal, or aquatic life. (Basin Plan). |
Objective/Criterion Reference: |
Water Quality Control Plan (Basin Plan) for the North Coast Region |
|
Evaluation Guideline: |
The evaluation guideline for simazine is the USEPA Aquatic Life Benchmark of 6 ug/L for a nonvascular plant (acute). |
Guideline Reference: |
OPP Aquatic Life Benchmarks |
|
Spatial Representation: |
The samples were collected at 1 monitoring site: 105SHA263 (Shasta River at Hwy 263). |
Temporal Representation: |
The samples were collected between the dates of 2007-11-15 and 2008-07-16 |
Environmental Conditions: |
|
QAPP Information: |
Generic SWAMP QAPrP |
QAPP Information Reference(s): |
Generic SWAMP QAPrP |
|
Line of Evidence (LOE) for Decision ID 169750, Simazine
|
Region 1 |
Klamath River HU, Shasta River HA |
|
|
LOE ID: |
350961 |
|
Pollutant: |
Simazine |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Total |
|
Beneficial Use: |
Warm Freshwater Habitat |
|
Number of Samples: |
3 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP RWB1 Monitoring data for Klamath River HU, Shasta River HA to determine beneficial use support and results are as follows: 0 of 3 samples exceeded the water quality threshold for Simazine. |
Data Reference: |
Water Quality Assessment Data for the 2018 solicitation cycle submitted through CEDEN for SWAMP RWB1 Monitoring .
|
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
All waters shall be maintained free of toxic substances in concentrations which are toxic to, or which produce detrimental physiological responses in, human, plant, animal, or aquatic life. (Basin Plan). |
Objective/Criterion Reference: |
Water Quality Control Plan (Basin Plan) for the North Coast Region |
|
Evaluation Guideline: |
The evaluation guideline for simazine is the USEPA Aquatic Life Benchmark of 6 ug/L for a nonvascular plant (acute). |
Guideline Reference: |
OPP Aquatic Life Benchmarks |
|
Spatial Representation: |
The samples were collected at 1 monitoring site: 105SH9274 (Shasta River near Edgewood). |
Temporal Representation: |
The samples were collected between the dates of 2013-03-07 and 2013-11-20 |
Environmental Conditions: |
|
QAPP Information: |
Generic SWAMP QAPrP |
QAPP Information Reference(s): |
Generic SWAMP QAPrP |
|
Line of Evidence (LOE) for Decision ID 169750, Simazine
|
Region 1 |
Klamath River HU, Shasta River HA |
|
|
LOE ID: |
350998 |
|
Pollutant: |
Simazine |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Total |
|
Beneficial Use: |
Cold Freshwater Habitat |
|
Number of Samples: |
3 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP RWB1 Monitoring data for Klamath River HU, Shasta River HA to determine beneficial use support and results are as follows: 0 of 3 samples exceeded the water quality threshold for Simazine. |
Data Reference: |
Water Quality Assessment Data for the 2018 solicitation cycle submitted through CEDEN for SWAMP RWB1 Monitoring .
|
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
All waters shall be maintained free of toxic substances in concentrations which are toxic to, or which produce detrimental physiological responses in, human, plant, animal, or aquatic life. (Basin Plan). |
Objective/Criterion Reference: |
Water Quality Control Plan (Basin Plan) for the North Coast Region |
|
Evaluation Guideline: |
The evaluation guideline for simazine is the USEPA Aquatic Life Benchmark of 6 ug/L for a nonvascular plant (acute). |
Guideline Reference: |
OPP Aquatic Life Benchmarks |
|
Spatial Representation: |
The samples were collected at 1 monitoring site: 105SH1452 (Shasta River at Hwy 263). |
Temporal Representation: |
The samples were collected between the dates of 2013-03-06 and 2013-11-20 |
Environmental Conditions: |
|
QAPP Information: |
Generic SWAMP QAPrP |
QAPP Information Reference(s): |
Generic SWAMP QAPrP |
|
Line of Evidence (LOE) for Decision ID 169750, Simazine
|
Region 1 |
Klamath River HU, Shasta River HA |
|
|
LOE ID: |
350968 |
|
Pollutant: |
Simazine |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Total |
|
Beneficial Use: |
Cold Freshwater Habitat |
|
Number of Samples: |
3 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP RWB1 Monitoring data for Klamath River HU, Shasta River HA to determine beneficial use support and results are as follows: 0 of 3 samples exceeded the water quality threshold for Simazine. |
Data Reference: |
Water Quality Assessment Data for the 2018 solicitation cycle submitted through CEDEN for SWAMP RWB1 Monitoring .
|
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
All waters shall be maintained free of toxic substances in concentrations which are toxic to, or which produce detrimental physiological responses in, human, plant, animal, or aquatic life. (Basin Plan). |
Objective/Criterion Reference: |
Water Quality Control Plan (Basin Plan) for the North Coast Region |
|
Evaluation Guideline: |
The evaluation guideline for simazine is the USEPA Aquatic Life Benchmark of 6 ug/L for a nonvascular plant (acute). |
Guideline Reference: |
OPP Aquatic Life Benchmarks |
|
Spatial Representation: |
The samples were collected at 1 monitoring site: 105SH9274 (Shasta River near Edgewood). |
Temporal Representation: |
The samples were collected between the dates of 2013-03-07 and 2013-11-20 |
Environmental Conditions: |
|
QAPP Information: |
Generic SWAMP QAPrP |
QAPP Information Reference(s): |
Generic SWAMP QAPrP |
|
Line of Evidence (LOE) for Decision ID 169750, Simazine
|
Region 1 |
Klamath River HU, Shasta River HA |
|
|
LOE ID: |
123452 |
|
Pollutant: |
Simazine |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
None |
|
Beneficial Use: |
Municipal & Domestic Supply |
|
Number of Samples: |
0 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
State Water Board staff re-assessed SWAMP data for Klamath River HU, Shasta River HA to determine beneficial use support and results are as follows: 0 of 0 samples exceed the criterion for Simazine, Total. Four sample results were not used in the assessment because the laboratory data reporting limit(s) was above the objective and therefore the results could not be quantified with the level of certainty required by the Listing Policy. This LOE re-assesses data from LOE 29849 from the 2010 Integrated Report. Data were re-assessed in order to evaluate these data in their own LOE, instead of being evaluated in the same LOE as other pesticide data. |
Data Reference: |
Surface Water Ambient Monitoring Program (SWAMP). Summary Report for the North Coast Region (RWQCB-1) for years 2000-2006. North Coast Regional Water Quality Control Board. March 2008 |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
Water Quality Control Plan, North Coast Region (NCRWQCB 2011): Waters designated for use as domestic or municipal supply (MUN) shall not contain concentrations of chemical constituents in excess of the limits specified in California Code of Regulations, Title 22, Chapter 15. The maximum contaminant level listed in Table 64444-A for simazine is 0.004 mg/L. |
Objective/Criterion Reference: |
Water Quality Control Plan (Basin Plan) for the North Coast Region |
Objective/Criterion Reference: |
Maximum Contaminant Levels for organic and inorganic chemicals. CCR Title 22 |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
Data for this line of evidence for Klamath River HU, Shasta River HA was collected at 1 monitoring site [ Yreka Creek at Highway 3 - 105YREHW3] |
Temporal Representation: |
Data was collected over the time period 10/21/2004-6/20/2005. |
Environmental Conditions: |
There are no known environmental conditions (e.g., seasonality, land use practices, fire events, storms, etc.) that are related to these data. |
QAPP Information: |
Quality control was conducted in accordance with the SWAMP Quality Assurance Management Plan (SWAMP 2002). |
QAPP Information Reference(s): |
Quality Assurance Management Plan for the State of California's Surface Water Ambient Monitoring Program. Sacramento, CA. State Water Resources Control Board. SWAMP. December 2002 (1st version)
|
|
Line of Evidence (LOE) for Decision ID 169750, Simazine
|
Region 1 |
Klamath River HU, Shasta River HA |
|
|
LOE ID: |
350977 |
|
Pollutant: |
Simazine |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Total |
|
Beneficial Use: |
Cold Freshwater Habitat |
|
Number of Samples: |
3 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed RWB1 Trend Maintenance Periods FYs 2007 2008 data for Klamath River HU, Shasta River HA to determine beneficial use support and results are as follows: 0 of 3 samples exceeded the water quality threshold for Simazine. |
Data Reference: |
RWB1 Trend Maintenance Periods FYs 2007 2008 |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
All waters shall be maintained free of toxic substances in concentrations which are toxic to, or which produce detrimental physiological responses in, human, plant, animal, or aquatic life. (Basin Plan). |
Objective/Criterion Reference: |
Water Quality Control Plan (Basin Plan) for the North Coast Region |
|
Evaluation Guideline: |
The evaluation guideline for simazine is the USEPA Aquatic Life Benchmark of 6 ug/L for a nonvascular plant (acute). |
Guideline Reference: |
OPP Aquatic Life Benchmarks |
|
Spatial Representation: |
The samples were collected at 1 monitoring site: 105SHAEDG (Shasta River near Edgewood). |
Temporal Representation: |
The samples were collected between the dates of 2007-11-15 and 2008-07-16 |
Environmental Conditions: |
|
QAPP Information: |
Generic SWAMP QAPrP |
QAPP Information Reference(s): |
Generic SWAMP QAPrP |
|
Line of Evidence (LOE) for Decision ID 169750, Simazine
|
Region 1 |
Klamath River HU, Shasta River HA |
|
|
LOE ID: |
351054 |
|
Pollutant: |
Simazine |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Total |
|
Beneficial Use: |
Cold Freshwater Habitat |
|
Number of Samples: |
3 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed RWB1 Trend Maintenance Periods FYs 2007 2008 data for Klamath River HU, Shasta River HA to determine beneficial use support and results are as follows: 0 of 3 samples exceeded the water quality threshold for Simazine. |
Data Reference: |
RWB1 Trend Maintenance Periods FYs 2007 2008 |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
All waters shall be maintained free of toxic substances in concentrations which are toxic to, or which produce detrimental physiological responses in, human, plant, animal, or aquatic life. (Basin Plan). |
Objective/Criterion Reference: |
Water Quality Control Plan (Basin Plan) for the North Coast Region |
|
Evaluation Guideline: |
The evaluation guideline for simazine is the USEPA Aquatic Life Benchmark of 6 ug/L for a nonvascular plant (acute). |
Guideline Reference: |
OPP Aquatic Life Benchmarks |
|
Spatial Representation: |
The samples were collected at 1 monitoring site: 105SHA263 (Shasta River at Hwy 263). |
Temporal Representation: |
The samples were collected between the dates of 2007-11-15 and 2008-07-16 |
Environmental Conditions: |
|
QAPP Information: |
Generic SWAMP QAPrP |
QAPP Information Reference(s): |
Generic SWAMP QAPrP |
|
Line of Evidence (LOE) for Decision ID 169750, Simazine
|
Region 1 |
Klamath River HU, Shasta River HA |
|
|
LOE ID: |
350945 |
|
Pollutant: |
Simazine |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Total |
|
Beneficial Use: |
Warm Freshwater Habitat |
|
Number of Samples: |
3 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed RWB1 Trend Maintenance Periods FYs 2007 2008 data for Klamath River HU, Shasta River HA to determine beneficial use support and results are as follows: 0 of 3 samples exceeded the water quality threshold for Simazine. |
Data Reference: |
RWB1 Trend Maintenance Periods FYs 2007 2008 |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
All waters shall be maintained free of toxic substances in concentrations which are toxic to, or which produce detrimental physiological responses in, human, plant, animal, or aquatic life. (Basin Plan). |
Objective/Criterion Reference: |
Water Quality Control Plan (Basin Plan) for the North Coast Region |
|
Evaluation Guideline: |
The evaluation guideline for simazine is the USEPA Aquatic Life Benchmark of 6 ug/L for a nonvascular plant (acute). |
Guideline Reference: |
OPP Aquatic Life Benchmarks |
|
Spatial Representation: |
The samples were collected at 1 monitoring site: 105SHAEDG (Shasta River near Edgewood). |
Temporal Representation: |
The samples were collected between the dates of 2007-11-15 and 2008-07-16 |
Environmental Conditions: |
|
QAPP Information: |
Generic SWAMP QAPrP |
QAPP Information Reference(s): |
Generic SWAMP QAPrP |
|
Line of Evidence (LOE) for Decision ID 169750, Simazine
|
Region 1 |
Klamath River HU, Shasta River HA |
|
|
LOE ID: |
351025 |
|
Pollutant: |
Simazine |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Total |
|
Beneficial Use: |
Warm Freshwater Habitat |
|
Number of Samples: |
3 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP RWB1 Monitoring data for Klamath River HU, Shasta River HA to determine beneficial use support and results are as follows: 0 of 3 samples exceeded the water quality threshold for Simazine. |
Data Reference: |
Water Quality Assessment Data for the 2018 solicitation cycle submitted through CEDEN for SWAMP RWB1 Monitoring .
|
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
All waters shall be maintained free of toxic substances in concentrations which are toxic to, or which produce detrimental physiological responses in, human, plant, animal, or aquatic life. (Basin Plan). |
Objective/Criterion Reference: |
Water Quality Control Plan (Basin Plan) for the North Coast Region |
|
Evaluation Guideline: |
The evaluation guideline for simazine is the USEPA Aquatic Life Benchmark of 6 ug/L for a nonvascular plant (acute). |
Guideline Reference: |
OPP Aquatic Life Benchmarks |
|
Spatial Representation: |
The samples were collected at 1 monitoring site: 105SH1452 (Shasta River at Hwy 263). |
Temporal Representation: |
The samples were collected between the dates of 2013-03-06 and 2013-11-20 |
Environmental Conditions: |
|
QAPP Information: |
Generic SWAMP QAPrP |
QAPP Information Reference(s): |
Generic SWAMP QAPrP |
|
Line of Evidence (LOE) for Decision ID 169750, Simazine
|
Region 1 |
Klamath River HU, Shasta River HA |
|
|
LOE ID: |
123451 |
|
Pollutant: |
Simazine |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
None |
|
Beneficial Use: |
Municipal & Domestic Supply |
|
Number of Samples: |
0 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
State Water Board staff re-assessed SWAMP data for Klamath River HU, Shasta River HA to determine beneficial use support and results are as follows: 0 of 0 samples exceed the criterion for Simazine, Total. Eight sample results were not used in the assessment because the laboratory data reporting limit(s) was above the objective and therefore the results could not be quantified with the level of certainty required by the Listing Policy. This LOE re-assesses data from LOE 29849 from the 2010 Integrated Report. Data were re-assessed in order to evaluate these data in their own LOE, instead of being evaluated in the same LOE as other pesticide data. |
Data Reference: |
Surface Water Ambient Monitoring Program (SWAMP). Summary Report for the North Coast Region (RWQCB-1) for years 2000-2006. North Coast Regional Water Quality Control Board. March 2008 |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
Water Quality Control Plan, North Coast Region (NCRWQCB 2011): Waters designated for use as domestic or municipal supply (MUN) shall not contain concentrations of chemical constituents in excess of the limits specified in California Code of Regulations, Title 22, Chapter 15. The maximum contaminant level listed in Table 64444-A for simazine is 0.004 mg/L. |
Objective/Criterion Reference: |
Water Quality Control Plan (Basin Plan) for the North Coast Region |
Objective/Criterion Reference: |
Maximum Contaminant Levels for organic and inorganic chemicals. CCR Title 22 |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
Data for this line of evidence for Klamath River HU, Shasta River HA was collected at 1 monitoring site [ Yreka Creek at Anderson Rd - 105YREAND] |
Temporal Representation: |
Data was collected over the time period 10/9/2002-6/20/2005. |
Environmental Conditions: |
There are no known environmental conditions (e.g., seasonality, land use practices, fire events, storms, etc.) that are related to these data. |
QAPP Information: |
Quality control was conducted in accordance with the SWAMP Quality Assurance Management Plan (SWAMP 2002). |
QAPP Information Reference(s): |
Quality Assurance Management Plan for the State of California's Surface Water Ambient Monitoring Program. Sacramento, CA. State Water Resources Control Board. SWAMP. December 2002 (1st version)
|
|
Line of Evidence (LOE) for Decision ID 169750, Simazine
|
Region 1 |
Klamath River HU, Shasta River HA |
|
|
LOE ID: |
123439 |
|
Pollutant: |
Simazine |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
None |
|
Beneficial Use: |
Municipal & Domestic Supply |
|
Number of Samples: |
0 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
State Water Board staff re-assessed SWAMP data for Klamath River HU, Shasta River HA to determine beneficial use support and results are as follows: 0 of 0 samples exceed the criterion for Simazine, Total. Four sample results were not used in the assessment because the laboratory data reporting limit(s) was above the objective and therefore the results could not be quantified with the level of certainty required by the Listing Policy. This LOE re-assesses data from LOE 29849 from the 2010 Integrated Report. Data were re-assessed in order to evaluate these data in their own LOE, instead of being evaluated in the same LOE as other pesticide data. |
Data Reference: |
Surface Water Ambient Monitoring Program (SWAMP). Summary Report for the North Coast Region (RWQCB-1) for years 2000-2006. North Coast Regional Water Quality Control Board. March 2008 |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
Water Quality Control Plan, North Coast Region (NCRWQCB 2011): Waters designated for use as domestic or municipal supply (MUN) shall not contain concentrations of chemical constituents in excess of the limits specified in California Code of Regulations, Title 22, Chapter 15. The maximum contaminant level listed in Table 64444-A for simazine is 0.004 mg/L. |
Objective/Criterion Reference: |
Water Quality Control Plan (Basin Plan) for the North Coast Region |
Objective/Criterion Reference: |
Maximum Contaminant Levels for organic and inorganic chemicals. CCR Title 22 |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
Data for this line of evidence for Klamath River HU, Shasta River HA was collected at 1 monitoring site [ Shasta River at Montague - 105SHAMON] |
Temporal Representation: |
Data was collected over the time period 10/7/2002-6/19/2003. |
Environmental Conditions: |
There are no known environmental conditions (e.g., seasonality, land use practices, fire events, storms, etc.) that are related to these data. |
QAPP Information: |
Quality control was conducted in accordance with the SWAMP Quality Assurance Management Plan (SWAMP 2002). |
QAPP Information Reference(s): |
Quality Assurance Management Plan for the State of California's Surface Water Ambient Monitoring Program. Sacramento, CA. State Water Resources Control Board. SWAMP. December 2002 (1st version)
|
|
Line of Evidence (LOE) for Decision ID 169750, Simazine
|
Region 1 |
Klamath River HU, Shasta River HA |
|
|
LOE ID: |
123450 |
|
Pollutant: |
Simazine |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
None |
|
Beneficial Use: |
Municipal & Domestic Supply |
|
Number of Samples: |
0 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
State Water Board staff re-assessed SWAMP data for Klamath River HU, Shasta River HA to determine beneficial use support and results are as follows: 0 of 0 samples exceed the criterion for Simazine, Total. Four sample results were not used in the assessment because the laboratory data reporting limit(s) was above the objective and therefore the results could not be quantified with the level of certainty required by the Listing Policy. This LOE re-assesses data from LOE 29849 from the 2010 Integrated Report. Data were re-assessed in order to evaluate these data in their own LOE, instead of being evaluated in the same LOE as other pesticide data. |
Data Reference: |
Surface Water Ambient Monitoring Program (SWAMP). Summary Report for the North Coast Region (RWQCB-1) for years 2000-2006. North Coast Regional Water Quality Control Board. March 2008 |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
Water Quality Control Plan, North Coast Region (NCRWQCB 2011): Waters designated for use as domestic or municipal supply (MUN) shall not contain concentrations of chemical constituents in excess of the limits specified in California Code of Regulations, Title 22, Chapter 15. The maximum contaminant level listed in Table 64444-A for simazine is 0.004 mg/L. |
Objective/Criterion Reference: |
Water Quality Control Plan (Basin Plan) for the North Coast Region |
Objective/Criterion Reference: |
Maximum Contaminant Levels for organic and inorganic chemicals. CCR Title 22 |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
Data for this line of evidence for Klamath River HU, Shasta River HA was collected at 1 monitoring site [ Shasta River near Edgewood - 105SH9274] |
Temporal Representation: |
Data was collected over the time period 10/7/2002-6/19/2003. |
Environmental Conditions: |
There are no known environmental conditions (e.g., seasonality, land use practices, fire events, storms, etc.) that are related to these data. |
QAPP Information: |
Quality control was conducted in accordance with the SWAMP Quality Assurance Management Plan (SWAMP 2002). |
QAPP Information Reference(s): |
Quality Assurance Management Plan for the State of California's Surface Water Ambient Monitoring Program. Sacramento, CA. State Water Resources Control Board. SWAMP. December 2002 (1st version)
|
|
Line of Evidence (LOE) for Decision ID 169750, Simazine
|
Region 1 |
Klamath River HU, Shasta River HA |
|
|
LOE ID: |
123438 |
|
Pollutant: |
Simazine |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
None |
|
Beneficial Use: |
Municipal & Domestic Supply |
|
Number of Samples: |
13 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
State Water Board staff re-assessed SWAMP data for Klamath River HU, Shasta River HA to determine beneficial use support and results are as follows: 0 of 13 samples exceed the criterion for Simazine, Total. This LOE re-assesses data from LOE 29849 from the 2010 Integrated Report. Data were re-assessed in order to evaluate these data in their own LOE, instead of being evaluated in the same LOE as other pesticide data. |
Data Reference: |
Surface Water Ambient Monitoring Program (SWAMP). Summary Report for the North Coast Region (RWQCB-1) for years 2000-2006. North Coast Regional Water Quality Control Board. March 2008 |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
Water Quality Control Plan, North Coast Region (NCRWQCB 2011): Waters designated for use as domestic or municipal supply (MUN) shall not contain concentrations of chemical constituents in excess of the limits specified in California Code of Regulations, Title 22, Chapter 15. The maximum contaminant level listed in Table 64444-A for simazine is 0.004 mg/L. |
Objective/Criterion Reference: |
Water Quality Control Plan (Basin Plan) for the North Coast Region |
Objective/Criterion Reference: |
Maximum Contaminant Levels for organic and inorganic chemicals. CCR Title 22 |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
Data for this line of evidence for Klamath River HU, Shasta River HA was collected at 1 monitoring site [ Shasta River at Hwy 263 - 105SH1452] |
Temporal Representation: |
Data was collected over the time period 4/24/2001-11/16/2006. |
Environmental Conditions: |
There are no known environmental conditions (e.g., seasonality, land use practices, fire events, storms, etc.) that are related to these data. |
QAPP Information: |
Quality control was conducted in accordance with the SWAMP Quality Assurance Management Plan (SWAMP 2002). |
QAPP Information Reference(s): |
Quality Assurance Management Plan for the State of California's Surface Water Ambient Monitoring Program. Sacramento, CA. State Water Resources Control Board. SWAMP. December 2002 (1st version)
|
|
Line of Evidence (LOE) for Decision ID 169750, Simazine
|
Region 1 |
Klamath River HU, Shasta River HA |
|
|
LOE ID: |
43335 |
|
Pollutant: |
Simazine |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Total |
|
Beneficial Use: |
Municipal & Domestic Supply |
|
Number of Samples: |
3 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP data for Klamath River HU, Shasta River HA to determine beneficial use support and results are as follows: 0 of 3 samples exceed the criterion for Simazine. |
Data Reference: |
RWB1 Trend Maintenance Periods FYs 2007 2008 |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
Water Quality Control Plan, North Coast Region (NCRWQCB 2011): Waters designated for use as domestic or municipal supply (MUN) shall not contain concentrations of chemical constituents in excess of the limits specified in California Code of Regulations, Title 22, Chapter 15. The maximum contaminant level listed in Table 64444-A for simazine is 0.004 mg/L. |
Objective/Criterion Reference: |
Maximum Contaminant Levels for organic and inorganic chemicals. CCR Title 22 |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
Data for this line of evidence for Klamath River HU, Shasta River HA was collected at 1 monitoring site [ Shasta River near Edgewood - 105SHAEDG] |
Temporal Representation: |
Data was collected over the time period 11/15/2007-7/16/2008. |
Environmental Conditions: |
Staff is not aware of any special conditions that might affect interpretation of the data. |
QAPP Information: |
The SWAMP QAPP (2008) was followed. |
QAPP Information Reference(s): |
Surface Water Ambient Monitoring Program Quality Assurance Program Plan |
|
Line of Evidence (LOE) for Decision ID 157123, Sulfates
|
Region 1 |
Klamath River HU, Shasta River HA |
|
|
LOE ID: |
105200 |
|
Pollutant: |
Sulfates |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Dissolved |
|
Beneficial Use: |
Municipal & Domestic Supply |
|
Number of Samples: |
5 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP RWB1 Monitoring data for Klamath River HU, Shasta River HA to determine beneficial use support and results are as follows: 0 of 5 samples exceeded the water quality standard for Sulfate. |
Data Reference: |
Water Quality Assessment Data for the 2018 solicitation cycle submitted through CEDEN for SWAMP RWB1 Monitoring .
|
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
Water Quality Control Plan, North Coast Region (NCRWQCB 2018): Waters designated for use as domestic or municipal supply (MUN) shall not contain concentrations of chemical constituents in excess of the limits specified in California Code of Regulations, Title 22, Chapter 15. The secondary maximum contaminant level listed in Table 64449-B for sulfate is 250 mg/L. |
Objective/Criterion Reference: |
Water Quality Control Plan (Basin Plan) for the North Coast Region |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
The samples were collected at 1 monitoring site(s) (105SH1452) |
Temporal Representation: |
The samples were collected between the dates of 2013-03-06 and 2013-11-20 |
Environmental Conditions: |
|
QAPP Information: |
Quality Assurance Program Plan and Standard Operating Procedures for SWAMP program |
QAPP Information Reference(s): |
Quality Assurance Program Plans, Quality Assurance Project Plans, and Standard Operating Procedures for the SWAMP program |
|
Line of Evidence (LOE) for Decision ID 157123, Sulfates
|
Region 1 |
Klamath River HU, Shasta River HA |
|
|
LOE ID: |
326888 |
|
Pollutant: |
Sulfates |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Dissolved |
|
Beneficial Use: |
Municipal & Domestic Supply |
|
Number of Samples: |
1 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP Perennial Stream Surveys data for Klamath River HU, Shasta River HA to determine beneficial use support and results are as follows: 0 of 1 samples exceeded the water quality threshold for Sulfate. |
Data Reference: |
Benthic, Field, Habitat, WQ from the Surface Water Ambient Monitoring Program for the 2026 Integrated Report in Region 1 |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
Water Quality Control Plan, North Coast Region (NCRWQCB 2018): Waters designated for use as domestic or municipal supply (MUN) shall not contain concentrations of chemical constituents in excess of the limits specified in California Code of Regulations, Title 22, Chapter 15. The secondary maximum contaminant level listed in Table 64449-B for sulfate is 250 mg/L. |
Objective/Criterion Reference: |
Water Quality Control Plan (Basin Plan) for the North Coast Region |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
The samples were collected at 1 monitoring site: 105PS0295 (Shasta River ~1mi above Cooley Gulch). |
Temporal Representation: |
The samples were collected between the dates of 2016-06-15 and 2016-06-15 |
Environmental Conditions: |
|
QAPP Information: |
QAPP for Surface Water Ambient Monitoring Program (SWAMP) |
QAPP Information Reference(s): |
Generic SWAMP QAPrP |
|
Line of Evidence (LOE) for Decision ID 157123, Sulfates
|
Region 1 |
Klamath River HU, Shasta River HA |
|
|
LOE ID: |
34239 |
|
Pollutant: |
Sulfates |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Not Recorded |
|
Beneficial Use: |
Municipal & Domestic Supply |
|
Number of Samples: |
4 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
None of the 4 samples exceeded the evaluation guideline. |
Data Reference: |
RWB1 Trend Maintenance Periods FYs 2007 2008 |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
Per the Basin Plan (NCRWQCB 2011): Waters shall not contain taste- or odor-producing substances in concentrations that impart undesirable tastes or odors to fish flesh or other edible products of aquatic origin, or that cause nuisance or adversely affect beneficial uses. |
Objective/Criterion Reference: |
Water Quality Control Plan (Basin Plan) for the North Coast Region |
|
Evaluation Guideline: |
Per 22 CCR 64449 (Table 64449-B): The recommended secondary maximum contaminant level for sulfate is 250 mg/L. |
Guideline Reference: |
Title 22. Division 4. Chapter 15. Sections 64400 et seq. California Code of Regulations |
|
Spatial Representation: |
Samples were collected from the Shasta River near Edgewood station (105SHAEDG). |
Temporal Representation: |
Samples were collected approximately once per quarter year from November 2007 to July 2008. |
Environmental Conditions: |
|
QAPP Information: |
SWAMP QAPP |
QAPP Information Reference(s): |
Surface Water Ambient Monitoring Program Quality Assurance Program Plan |
|
Line of Evidence (LOE) for Decision ID 157123, Sulfates
|
Region 1 |
Klamath River HU, Shasta River HA |
|
|
LOE ID: |
34238 |
|
Pollutant: |
Sulfates |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Not Recorded |
|
Beneficial Use: |
Municipal & Domestic Supply |
|
Number of Samples: |
4 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
None of the 4 samples exceeded the evaluation guideline. |
Data Reference: |
RWB1 Trend Maintenance Periods FYs 2007 2008 |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
Per the Basin Plan (NCRWQCB 2011): Waters shall not contain taste- or odor-producing substances in concentrations that impart undesirable tastes or odors to fish flesh or other edible products of aquatic origin, or that cause nuisance or adversely affect beneficial uses. |
Objective/Criterion Reference: |
Water Quality Control Plan (Basin Plan) for the North Coast Region |
|
Evaluation Guideline: |
Per 22 CCR 64449 (Table 64449-B): The recommended secondary maximum contaminant level for sulfate is 250 mg/L. |
Guideline Reference: |
Title 22. Division 4. Chapter 15. Sections 64400 et seq. California Code of Regulations |
|
Spatial Representation: |
Samples were collected from the Shasta River at Hwy 263 station (105SHA263). |
Temporal Representation: |
Samples were collected approximately once per quarter year from November 2007 to July 2008. |
Environmental Conditions: |
|
QAPP Information: |
SWAMP QAPP |
QAPP Information Reference(s): |
Surface Water Ambient Monitoring Program Quality Assurance Program Plan |
|
Line of Evidence (LOE) for Decision ID 157123, Sulfates
|
Region 1 |
Klamath River HU, Shasta River HA |
|
|
LOE ID: |
46943 |
|
Pollutant: |
Sulfates |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Not Recorded |
|
Beneficial Use: |
Municipal & Domestic Supply |
|
Number of Samples: |
32 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
None of the 32 sulfate samples collected in the Shasta River exceed the evaluation guideline. The samples were collected as part of the Surface Water Ambient Water Monitoring Program (SWAMP). The data are found in the 5-Year Monitoring Report (NCRWQCB 2008). This LOE and LOE 46944 replace LOE 25524 from the 2010 Integrated Report cycle. Data were split into two LOEs in order to separate the data from each stream into its own LOE. |
Data Reference: |
Surface Water Ambient Monitoring Program (SWAMP). Summary Report for the North Coast Region (RWQCB-1) for years 2000-2006. North Coast Regional Water Quality Control Board. March 2008 |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
Per the Basin Plan (NCRWQCB 2007, p. 3-3.00): Waters shall not contain taste- or odor-producing substances in concentrations that impart undesirable tastes or odors to fish flesh or other edible products of aquatic origin, or that cause nuisance or adversely affect beneficial uses. |
Objective/Criterion Reference: |
Water Quality Control Plan (Basin Plan) - North Coast Region (Region 1) |
|
Evaluation Guideline: |
Per 22 CCR 64449 (Table 64449-B): The recommended secondary maximum contaminant level for sulfate is 250 mg/L. |
Guideline Reference: |
Title 22. Division 4. Chapter 15. Sections 64400 et seq. California Code of Regulations |
|
Spatial Representation: |
Samples were collected in the mainstem Shasta River from 3 locations as follows: (1) near Edgewood Road (SWAMP Station ID 105SHAEDG), (2) at Montague Grenada Road (SWAMP Station ID 105SHAMON), and (3) at Highway 263 (SWAMP Station ID 105SHA263). Samples were collected in well-mixed flows in glides or riffles. |
Temporal Representation: |
The samples from Edgewood Road and Montague Grenada Road were collected as grab samples during 5 site visits at each site during the 2002 - 2003 fiscal years. Samples from Highway 263 were collected as grab samples during 22 site visits during the 2000 - 2006 fiscal years. The site visits corresponded to fall, winter, spring and early summer seasonal conditions. |
Environmental Conditions: |
There are no known environmental conditions (e.g., seasonality, land use practices, fire events, storms, etc.) that are related to these data. |
QAPP Information: |
Quality control was conducted in accordance with the SWAMP Quality Assurance Management Plan (SWAMP 2002). |
QAPP Information Reference(s): |
Quality Assurance Management Plan for the State of California's Surface Water Ambient Monitoring Program. Sacramento, CA. State Water Resources Control Board. SWAMP. December 2002 (1st version)
|
|
Line of Evidence (LOE) for Decision ID 157123, Sulfates
|
Region 1 |
Klamath River HU, Shasta River HA |
|
|
LOE ID: |
326826 |
|
Pollutant: |
Sulfates |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Dissolved |
|
Beneficial Use: |
Municipal & Domestic Supply |
|
Number of Samples: |
1 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP Reference Condition Management Plan data for Klamath River HU, Shasta River HA to determine beneficial use support and results are as follows: 0 of 1 samples exceeded the water quality threshold for Sulfate. |
Data Reference: |
Benthic, Field, Habitat, WQ from the Surface Water Ambient Monitoring Program for the 2026 Integrated Report in Region 1 |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
Water Quality Control Plan, North Coast Region (NCRWQCB 2018): Waters designated for use as domestic or municipal supply (MUN) shall not contain concentrations of chemical constituents in excess of the limits specified in California Code of Regulations, Title 22, Chapter 15. The secondary maximum contaminant level listed in Table 64449-B for sulfate is 250 mg/L. |
Objective/Criterion Reference: |
Water Quality Control Plan (Basin Plan) for the North Coast Region |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
The samples were collected at 1 monitoring site: 105WE0592 (Eddy Creek ~0.8 miles downstream from end of 4WD road.). |
Temporal Representation: |
The samples were collected between the dates of 2015-07-13 and 2015-07-13 |
Environmental Conditions: |
|
QAPP Information: |
QAPP for Surface Water Ambient Monitoring Program (SWAMP) |
QAPP Information Reference(s): |
Generic SWAMP QAPrP |
|
Line of Evidence (LOE) for Decision ID 157123, Sulfates
|
Region 1 |
Klamath River HU, Shasta River HA |
|
|
LOE ID: |
118120 |
|
Pollutant: |
Sulfates |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Dissolved |
|
Beneficial Use: |
Municipal & Domestic Supply |
|
Number of Samples: |
1 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP Perennial Stream Surveys data for Klamath River HU, Shasta River HA to determine beneficial use support and results are as follows: 0 of 1 samples exceeded the water quality standard for Sulfate. |
Data Reference: |
Water Quality Assessment Data for the 2018 solicitation cycle submitted through CEDEN for SWAMP Perennial Stream Surveys .
|
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
Water Quality Control Plan, North Coast Region (NCRWQCB 2018): Waters designated for use as domestic or municipal supply (MUN) shall not contain concentrations of chemical constituents in excess of the limits specified in California Code of Regulations, Title 22, Chapter 15. The secondary maximum contaminant level listed in Table 64449-B for sulfate is 250 mg/L. |
Objective/Criterion Reference: |
Water Quality Control Plan (Basin Plan) for the North Coast Region |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
The samples were collected at 1 monitoring site(s) (105PS0231) |
Temporal Representation: |
The samples were collected between the dates of 2013-08-29 and 2013-08-29 |
Environmental Conditions: |
|
QAPP Information: |
Quality Assurance Program Plan and Standard Operating Procedures for SWAMP program |
QAPP Information Reference(s): |
Quality Assurance Program Plans, Quality Assurance Project Plans, and Standard Operating Procedures for the SWAMP program |
|
Line of Evidence (LOE) for Decision ID 157123, Sulfates
|
Region 1 |
Klamath River HU, Shasta River HA |
|
|
LOE ID: |
105201 |
|
Pollutant: |
Sulfates |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Dissolved |
|
Beneficial Use: |
Municipal & Domestic Supply |
|
Number of Samples: |
5 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP RWB1 Monitoring data for Klamath River HU, Shasta River HA to determine beneficial use support and results are as follows: 0 of 5 samples exceeded the water quality standard for Sulfate. |
Data Reference: |
Water Quality Assessment Data for the 2018 solicitation cycle submitted through CEDEN for SWAMP RWB1 Monitoring .
|
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
Water Quality Control Plan, North Coast Region (NCRWQCB 2018): Waters designated for use as domestic or municipal supply (MUN) shall not contain concentrations of chemical constituents in excess of the limits specified in California Code of Regulations, Title 22, Chapter 15. The secondary maximum contaminant level listed in Table 64449-B for sulfate is 250 mg/L. |
Objective/Criterion Reference: |
Water Quality Control Plan (Basin Plan) for the North Coast Region |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
The samples were collected at 1 monitoring site(s) (105SH9274) |
Temporal Representation: |
The samples were collected between the dates of 2013-03-07 and 2013-11-20 |
Environmental Conditions: |
|
QAPP Information: |
Quality Assurance Program Plan and Standard Operating Procedures for SWAMP program |
QAPP Information Reference(s): |
Quality Assurance Program Plans, Quality Assurance Project Plans, and Standard Operating Procedures for the SWAMP program |
|
Line of Evidence (LOE) for Decision ID 157123, Sulfates
|
Region 1 |
Klamath River HU, Shasta River HA |
|
|
LOE ID: |
44075 |
|
Pollutant: |
Sulfates |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
None |
|
Beneficial Use: |
Municipal & Domestic Supply |
|
Number of Samples: |
1 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP data for Klamath River HU, Shasta River HA to determine beneficial use support and results are as follows: 0 of 1 samples exceed the criterion for Sulfate. |
Data Reference: |
Statewide Perennial Streams Assessment 2008 |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
Water Quality Control Plan, North Coast Region (NCRWQCB 2011): Waters designated for use as domestic or municipal supply (MUN) shall not contain concentrations of chemical constituents in excess of the limits specified in California Code of Regulations, Title 22, Chapter 15. The secondary maximum contaminant level listed in Table 64449-A for sulfate is 250 mg/L. |
Objective/Criterion Reference: |
Secondary Maximum Contaminant Levels and Compliance. CCR Title 22 section 64449. |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
Data for this line of evidence for Klamath River HU, Shasta River HA was collected at 1 monitoring site [ Evans Ditch - 105PS0188 ] |
Temporal Representation: |
Data was collected on a single day 8/26/2008. |
Environmental Conditions: |
Staff is not aware of any special conditions that might affect interpretation of the data. |
QAPP Information: |
The SWAMP QAPP (2008) was followed. |
QAPP Information Reference(s): |
Surface Water Ambient Monitoring Program Quality Assurance Program Plan |
|
Line of Evidence (LOE) for Decision ID 157123, Sulfates
|
Region 1 |
Klamath River HU, Shasta River HA |
|
|
LOE ID: |
46944 |
|
Pollutant: |
Sulfates |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Not Recorded |
|
Beneficial Use: |
Municipal & Domestic Supply |
|
Number of Samples: |
9 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
None of the 9 sulfate samples collected in Yreka Creek exceed the evaluation guideline. The samples were collected as part of the Surface Water Ambient Water Monitoring Program (SWAMP). The data are found in the 5-Year Monitoring Report (NCRWQCB 2008). This LOE and LOE 46943 replace LOE 25524 from the 2010 Integrated Report cycle. Data were split into two LOEs in order to separate the data from each stream into its own LOE. |
Data Reference: |
Surface Water Ambient Monitoring Program (SWAMP). Summary Report for the North Coast Region (RWQCB-1) for years 2000-2006. North Coast Regional Water Quality Control Board. March 2008 |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
Per the Basin Plan (NCRWQCB 2007, p. 3-3.00): Waters shall not contain taste- or odor-producing substances in concentrations that impart undesirable tastes or odors to fish flesh or other edible products of aquatic origin, or that cause nuisance or adversely affect beneficial uses. |
Objective/Criterion Reference: |
Water Quality Control Plan (Basin Plan) - North Coast Region (Region 1) |
|
Evaluation Guideline: |
Per 22 CCR 64449 (Table 64449-B): The recommended secondary maximum contaminant level for sulfate is 250 mg/L. |
Guideline Reference: |
Title 22. Division 4. Chapter 15. Sections 64400 et seq. California Code of Regulations |
|
Spatial Representation: |
Samples were collected in Yreka Creek from 2 locations as follows: (1) at Highway 3 (SWAMP Station ID 105YREHW3), and (2) at Anderson Grade Road (SWAMP Station ID 105YREAND). Samples were collected in well-mixed flows in glides or riffles. |
Temporal Representation: |
Samples in Yreka Creek were collected from October 2004 to June 2005. The site visits corresponded to fall, winter, spring and early summer seasonal conditions. |
Environmental Conditions: |
There are no known environmental conditions (e.g., seasonality, land use practices, fire events, storms, etc.) that are related to these data. |
QAPP Information: |
Quality control was conducted in accordance with the SWAMP Quality Assurance Management Plan (SWAMP 2002). |
QAPP Information Reference(s): |
Quality Assurance Management Plan for the State of California's Surface Water Ambient Monitoring Program. Sacramento, CA. State Water Resources Control Board. SWAMP. December 2002 (1st version)
|
|
Line of Evidence (LOE) for Decision ID 157123, Sulfates
|
Region 1 |
Klamath River HU, Shasta River HA |
|
|
LOE ID: |
25524 |
|
Pollutant: |
Sulfates |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Not Recorded |
|
Beneficial Use: |
Municipal & Domestic Supply |
|
Number of Samples: |
41 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
None of the 41 sulfate samples collected in the Shasta River watershed exceed the evaluation guideline. The samples were collected as part of the Surface Water Ambient Water Monitoring Program (SWAMP). The data are found in the 5-Year Monitoring Report (NCRWQCB 2008). |
Data Reference: |
Surface Water Ambient Monitoring Program (SWAMP). Summary Report for the North Coast Region (RWQCB-1) for years 2000-2006. North Coast Regional Water Quality Control Board. March 2008 |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
Per the Basin Plan (NCRWQCB 2007, p. 3-3.00): Waters shall not contain taste- or odor-producing substances in concentrations that impart undesirable tastes or odors to fish flesh or other edible products of aquatic origin, or that cause nuisance or adversely affect beneficial uses. |
Objective/Criterion Reference: |
Water Quality Control Plan (Basin Plan) - North Coast Region (Region 1) |
|
Evaluation Guideline: |
Per 22 CCR 64449 (Table 64449-B): The recommended secondary maximum contaminant level for sulfate is 250 mg/L. |
Guideline Reference: |
Title 22. Division 4. Chapter 15. Sections 64400 et seq. California Code of Regulations |
|
Spatial Representation: |
Samples were collected in the mainstem Shasta River from 3 locations as follows: (1) near Edgewood Road (SWAMP Station ID 105SHAEDG), (2) at Montague Grenada Road (SWAMP Station ID 105SHAMON), (3) at Highway 263 (SWAMP Station ID 105SHA263), (4) at Highway 3 (SWAMP Station ID 105YREHW3), and (5) at Anderson Grade Road (SWAMP Station ID 105YREAND). Samples were collected in well-mixed flows in glides or riffles. |
Temporal Representation: |
The samples from Edgewood Road and Montague Grenada Road were collected as grab samples during 5 site visits at each site during the 2002 - 2003 fiscal years. Samples from Highway 263 were collected as grab samples during 22 site visits during the 2000 - 2006 fiscal years. Samples in Yreka Creek were collected from October 2004 to June 2005. The site visits corresponded to fall, winter, spring and early summer seasonal conditions. |
Environmental Conditions: |
There are no known environmental conditions (e.g., seasonality, land use practices, fire events, storms, etc.) that are related to these data. |
QAPP Information: |
Quality control was conducted in accordance with the SWAMP Quality Assurance Management Plan (SWAMP 2002). |
QAPP Information Reference(s): |
Quality Assurance Management Plan for the State of California's Surface Water Ambient Monitoring Program. Sacramento, CA. State Water Resources Control Board. SWAMP. December 2002 (1st version)
|
|
Line of Evidence (LOE) for Decision ID 105203, Terbufos
|
Region 1 |
Klamath River HU, Shasta River HA |
|
|
LOE ID: |
123512 |
|
Pollutant: |
Terbufos |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
None |
|
Beneficial Use: |
Municipal & Domestic Supply |
|
Number of Samples: |
0 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
State Water Board staff re-assessed SWAMP data for Klamath River HU, Shasta River HA to determine beneficial use support and results are as follows: 0 of 0 samples exceed the criterion for Terbufos, Total. Twelve sample results were not used in the assessment because the laboratory data reporting limit(s) was above the objective and therefore the results could not be quantified with the level of certainty required by the Listing Policy. This LOE re-assesses data from LOE 29849 from the 2010 Integrated Report. Data were re-assessed in order to evaluate these data in their own LOE, instead of being evaluated in the same LOE as other pesticide data. |
Data Reference: |
Surface Water Ambient Monitoring Program (SWAMP). Summary Report for the North Coast Region (RWQCB-1) for years 2000-2006. North Coast Regional Water Quality Control Board. March 2008 |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
Per the Basin Plan (NCRWQCB 2011): No individual pesticide or combination of pesticides shall be present in concentrations that adversely affect beneficial uses. There shall be no bioaccumulation of pesticide concentrations found in bottom sediments or aquatic life. Waters designated for use as domestic or municipal supply shall not contain concentrations of pesticides in excess of the limiting concentrations set forth in California Code of Regulations, Title 22, Division 4, Chapter 15, Article 4, Section 64444, and listed in Table 3.2 of the Basin Plan. |
Objective/Criterion Reference: |
Water Quality Control Plan (Basin Plan) for the North Coast Region |
|
Evaluation Guideline: |
According to the 2006 USEPA Drinking Water Standards and Health Advisories, the Life-time Exposure Health Advisory for Terbufos is 0.0004 mg/L. (EPA 822-R-06-013, 2006) |
Guideline Reference: |
2006 edition of the drinking water standards and health advisories. EPA 822-R-03-013 |
|
Spatial Representation: |
Data for this line of evidence for Klamath River HU, Shasta River HA was collected at 1 monitoring site [ Shasta River at Montague - 105SHAMON] |
Temporal Representation: |
Data was collected over the time period 10/7/2002-6/19/2003. |
Environmental Conditions: |
There are no known environmental conditions (e.g., seasonality, land use practices, fire events, storms, etc.) that are related to these data. |
QAPP Information: |
Quality control was conducted in accordance with the SWAMP Quality Assurance Management Plan (SWAMP 2002). |
QAPP Information Reference(s): |
Quality Assurance Management Plan for the State of California's Surface Water Ambient Monitoring Program. Sacramento, CA. State Water Resources Control Board. SWAMP. December 2002 (1st version)
|
|
Line of Evidence (LOE) for Decision ID 105203, Terbufos
|
Region 1 |
Klamath River HU, Shasta River HA |
|
|
LOE ID: |
123513 |
|
Pollutant: |
Terbufos |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
None |
|
Beneficial Use: |
Municipal & Domestic Supply |
|
Number of Samples: |
0 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
State Water Board staff re-assessed SWAMP data for Klamath River HU, Shasta River HA to determine beneficial use support and results are as follows: 0 of 0 samples exceed the criterion for Terbufos, Total. Twelve sample results were not used in the assessment because the laboratory data reporting limit(s) was above the objective and therefore the results could not be quantified with the level of certainty required by the Listing Policy. This LOE re-assesses data from LOE 29849 from the 2010 Integrated Report. Data were re-assessed in order to evaluate these data in their own LOE, instead of being evaluated in the same LOE as other pesticide data. |
Data Reference: |
Surface Water Ambient Monitoring Program (SWAMP). Summary Report for the North Coast Region (RWQCB-1) for years 2000-2006. North Coast Regional Water Quality Control Board. March 2008 |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
Per the Basin Plan (NCRWQCB 2011): No individual pesticide or combination of pesticides shall be present in concentrations that adversely affect beneficial uses. There shall be no bioaccumulation of pesticide concentrations found in bottom sediments or aquatic life. Waters designated for use as domestic or municipal supply shall not contain concentrations of pesticides in excess of the limiting concentrations set forth in California Code of Regulations, Title 22, Division 4, Chapter 15, Article 4, Section 64444, and listed in Table 3.2 of the Basin Plan. |
Objective/Criterion Reference: |
Water Quality Control Plan (Basin Plan) for the North Coast Region |
|
Evaluation Guideline: |
According to the 2006 USEPA Drinking Water Standards and Health Advisories, the Life-time Exposure Health Advisory for Terbufos is 0.0004 mg/L. (EPA 822-R-06-013, 2006) |
Guideline Reference: |
2006 edition of the drinking water standards and health advisories. EPA 822-R-03-013 |
|
Spatial Representation: |
Data for this line of evidence for Klamath River HU, Shasta River HA was collected at 1 monitoring site [ Shasta River near Edgewood - 105SH9274] |
Temporal Representation: |
Data was collected over the time period 10/7/2002-6/19/2003. |
Environmental Conditions: |
There are no known environmental conditions (e.g., seasonality, land use practices, fire events, storms, etc.) that are related to these data. |
QAPP Information: |
Quality control was conducted in accordance with the SWAMP Quality Assurance Management Plan (SWAMP 2002). |
QAPP Information Reference(s): |
Quality Assurance Management Plan for the State of California's Surface Water Ambient Monitoring Program. Sacramento, CA. State Water Resources Control Board. SWAMP. December 2002 (1st version)
|
|
Line of Evidence (LOE) for Decision ID 105203, Terbufos
|
Region 1 |
Klamath River HU, Shasta River HA |
|
|
LOE ID: |
123511 |
|
Pollutant: |
Terbufos |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
None |
|
Beneficial Use: |
Municipal & Domestic Supply |
|
Number of Samples: |
16 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
State Water Board staff re-assessed SWAMP data for Klamath River HU, Shasta River HA to determine beneficial use support and results are as follows: 0 of 16 samples exceed the criterion for Terbufos, Total. This LOE re-assesses data from LOE 29849 from the 2010 Integrated Report. Data were re-assessed in order to evaluate these data in their own LOE, instead of being evaluated in the same LOE as other pesticide data. |
Data Reference: |
Surface Water Ambient Monitoring Program (SWAMP). Summary Report for the North Coast Region (RWQCB-1) for years 2000-2006. North Coast Regional Water Quality Control Board. March 2008 |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
Per the Basin Plan (NCRWQCB 2011): No individual pesticide or combination of pesticides shall be present in concentrations that adversely affect beneficial uses. There shall be no bioaccumulation of pesticide concentrations found in bottom sediments or aquatic life. Waters designated for use as domestic or municipal supply shall not contain concentrations of pesticides in excess of the limiting concentrations set forth in California Code of Regulations, Title 22, Division 4, Chapter 15, Article 4, Section 64444, and listed in Table 3.2 of the Basin Plan. |
Objective/Criterion Reference: |
Water Quality Control Plan (Basin Plan) for the North Coast Region |
|
Evaluation Guideline: |
According to the 2006 USEPA Drinking Water Standards and Health Advisories, the Life-time Exposure Health Advisory for Terbufos is 0.0004 mg/L. (EPA 822-R-06-013, 2006) |
Guideline Reference: |
2006 edition of the drinking water standards and health advisories. EPA 822-R-03-013 |
|
Spatial Representation: |
Data for this line of evidence for Klamath River HU, Shasta River HA was collected at 1 monitoring site [ Shasta River at Hwy 263 - 105SH1452] |
Temporal Representation: |
Data was collected over the time period 4/24/2001-11/16/2006. |
Environmental Conditions: |
There are no known environmental conditions (e.g., seasonality, land use practices, fire events, storms, etc.) that are related to these data. |
QAPP Information: |
Quality control was conducted in accordance with the SWAMP Quality Assurance Management Plan (SWAMP 2002). |
QAPP Information Reference(s): |
Quality Assurance Management Plan for the State of California's Surface Water Ambient Monitoring Program. Sacramento, CA. State Water Resources Control Board. SWAMP. December 2002 (1st version)
|
|
Line of Evidence (LOE) for Decision ID 105203, Terbufos
|
Region 1 |
Klamath River HU, Shasta River HA |
|
|
LOE ID: |
123521 |
|
Pollutant: |
Terbufos |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
None |
|
Beneficial Use: |
Municipal & Domestic Supply |
|
Number of Samples: |
0 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
State Water Board staff re-assessed SWAMP data for Klamath River HU, Shasta River HA to determine beneficial use support and results are as follows: 0 of 0 samples exceed the criterion for Terbufos, Total. Twelve sample results were not used in the assessment because the laboratory data reporting limit(s) was above the objective and therefore the results could not be quantified with the level of certainty required by the Listing Policy. This LOE re-assesses data from LOE 29849 from the 2010 Integrated Report. Data were re-assessed in order to evaluate these data in their own LOE, instead of being evaluated in the same LOE as other pesticide data. |
Data Reference: |
Surface Water Ambient Monitoring Program (SWAMP). Summary Report for the North Coast Region (RWQCB-1) for years 2000-2006. North Coast Regional Water Quality Control Board. March 2008 |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
Per the Basin Plan (NCRWQCB 2011): No individual pesticide or combination of pesticides shall be present in concentrations that adversely affect beneficial uses. There shall be no bioaccumulation of pesticide concentrations found in bottom sediments or aquatic life. Waters designated for use as domestic or municipal supply shall not contain concentrations of pesticides in excess of the limiting concentrations set forth in California Code of Regulations, Title 22, Division 4, Chapter 15, Article 4, Section 64444, and listed in Table 3.2 of the Basin Plan. |
Objective/Criterion Reference: |
Water Quality Control Plan (Basin Plan) for the North Coast Region |
|
Evaluation Guideline: |
According to the 2006 USEPA Drinking Water Standards and Health Advisories, the Life-time Exposure Health Advisory for Terbufos is 0.0004 mg/L. (EPA 822-R-06-013, 2006) |
Guideline Reference: |
2006 edition of the drinking water standards and health advisories. EPA 822-R-03-013 |
|
Spatial Representation: |
Data for this line of evidence for Klamath River HU, Shasta River HA was collected at 1 monitoring site [ Yreka Creek at Highway 3 - 105YREHW3] |
Temporal Representation: |
Data was collected over the time period 10/21/2004-6/20/2005. |
Environmental Conditions: |
There are no known environmental conditions (e.g., seasonality, land use practices, fire events, storms, etc.) that are related to these data. |
QAPP Information: |
Quality control was conducted in accordance with the SWAMP Quality Assurance Management Plan (SWAMP 2002). |
QAPP Information Reference(s): |
Quality Assurance Management Plan for the State of California's Surface Water Ambient Monitoring Program. Sacramento, CA. State Water Resources Control Board. SWAMP. December 2002 (1st version)
|
|
Line of Evidence (LOE) for Decision ID 105203, Terbufos
|
Region 1 |
Klamath River HU, Shasta River HA |
|
|
LOE ID: |
123520 |
|
Pollutant: |
Terbufos |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
None |
|
Beneficial Use: |
Municipal & Domestic Supply |
|
Number of Samples: |
0 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
State Water Board staff re-assessed SWAMP data for Klamath River HU, Shasta River HA to determine beneficial use support and results are as follows: 0 of 0 samples exceed the criterion for Terbufos, Total. Twenty-four sample results were not used in the assessment because the laboratory data reporting limit(s) was above the objective and therefore the results could not be quantified with the level of certainty required by the Listing Policy. This LOE re-assesses data from LOE 29849 from the 2010 Integrated Report. Data were re-assessed in order to evaluate these data in their own LOE, instead of being evaluated in the same LOE as other pesticide data. |
Data Reference: |
Surface Water Ambient Monitoring Program (SWAMP). Summary Report for the North Coast Region (RWQCB-1) for years 2000-2006. North Coast Regional Water Quality Control Board. March 2008 |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
Per the Basin Plan (NCRWQCB 2011): No individual pesticide or combination of pesticides shall be present in concentrations that adversely affect beneficial uses. There shall be no bioaccumulation of pesticide concentrations found in bottom sediments or aquatic life. Waters designated for use as domestic or municipal supply shall not contain concentrations of pesticides in excess of the limiting concentrations set forth in California Code of Regulations, Title 22, Division 4, Chapter 15, Article 4, Section 64444, and listed in Table 3.2 of the Basin Plan. |
Objective/Criterion Reference: |
Water Quality Control Plan (Basin Plan) for the North Coast Region |
|
Evaluation Guideline: |
According to the 2006 USEPA Drinking Water Standards and Health Advisories, the Life-time Exposure Health Advisory for Terbufos is 0.0004 mg/L. (EPA 822-R-06-013, 2006) |
Guideline Reference: |
2006 edition of the drinking water standards and health advisories. EPA 822-R-03-013 |
|
Spatial Representation: |
Data for this line of evidence for Klamath River HU, Shasta River HA was collected at 1 monitoring site [ Yreka Creek at Anderson Rd - 105YREAND] |
Temporal Representation: |
Data was collected over the time period 10/9/2002-6/20/2005. |
Environmental Conditions: |
There are no known environmental conditions (e.g., seasonality, land use practices, fire events, storms, etc.) that are related to these data. |
QAPP Information: |
Quality control was conducted in accordance with the SWAMP Quality Assurance Management Plan (SWAMP 2002). |
QAPP Information Reference(s): |
Quality Assurance Management Plan for the State of California's Surface Water Ambient Monitoring Program. Sacramento, CA. State Water Resources Control Board. SWAMP. December 2002 (1st version)
|
|
Line of Evidence (LOE) for Decision ID 105203, Terbufos
|
Region 1 |
Klamath River HU, Shasta River HA |
|
|
LOE ID: |
111154 |
|
Pollutant: |
Terbufos |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Total |
|
Beneficial Use: |
Cold Freshwater Habitat |
|
Number of Samples: |
0 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP RWB1 Monitoring data for Klamath River HU, Shasta River HA to determine beneficial use support, and the results are as follows: 0 of the 0 samples exceeded the evaluation guideline for Terbufos. Although a total of 3 samples were collected, 3 of these samples were not included in the assessment because the laboratory data reporting limit(s) was above the objective and therefore the results could not be quantified with the level of certainty required by the Listing Policy Section 6.1.5.5. |
Data Reference: |
Water Quality Assessment Data for the 2018 solicitation cycle submitted through CEDEN for SWAMP RWB1 Monitoring .
|
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
All waters shall be maintained free of toxic substances in concentrations which are toxic to, or which produce detrimental physiological responses in, human, plant, animal, or aquatic life. (Basin Plan). |
Objective/Criterion Reference: |
Water Quality Control Plan (Basin Plan) for the North Coast Region |
|
Evaluation Guideline: |
The evaluation guideline for Terbufos is the USEPA Aquatic Life Benchmark of 0.03 ug/L for an invertebrate (chronic). |
Guideline Reference: |
OPP Aquatic Life Benchmarks |
|
Spatial Representation: |
Data was collected from 1 station(s) (Station Code(s) 105SH1452). |
Temporal Representation: |
Date for this waterbody was collected over the date range 2013-03-06 to 2013-11-20 |
Environmental Conditions: |
|
QAPP Information: |
Quality Assurance Program Plan and Standard Operating Procedures for SWAMP program |
QAPP Information Reference(s): |
Quality Assurance Program Plans, Quality Assurance Project Plans, and Standard Operating Procedures for the SWAMP program |
|
Line of Evidence (LOE) for Decision ID 105203, Terbufos
|
Region 1 |
Klamath River HU, Shasta River HA |
|
|
LOE ID: |
119096 |
|
Pollutant: |
Terbufos |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Total |
|
Beneficial Use: |
Cold Freshwater Habitat |
|
Number of Samples: |
0 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP RWB1 Monitoring data for Klamath River HU, Shasta River HA to determine beneficial use support, and the results are as follows: 0 of the 0 samples exceeded the evaluation guideline for Terbufos. Although a total of 3 samples were collected, 3 of these samples were not included in the assessment because the laboratory data reporting limit(s) was above the objective and therefore the results could not be quantified with the level of certainty required by the Listing Policy Section 6.1.5.5. |
Data Reference: |
Water Quality Assessment Data for the 2018 solicitation cycle submitted through CEDEN for SWAMP RWB1 Monitoring .
|
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
All waters shall be maintained free of toxic substances in concentrations which are toxic to, or which produce detrimental physiological responses in, human, plant, animal, or aquatic life. (Basin Plan). |
Objective/Criterion Reference: |
Water Quality Control Plan (Basin Plan) for the North Coast Region |
|
Evaluation Guideline: |
The evaluation guideline for Terbufos is the USEPA Aquatic Life Benchmark of 0.03 ug/L for an invertebrate (chronic). |
Guideline Reference: |
OPP Aquatic Life Benchmarks |
|
Spatial Representation: |
Data was collected from 1 station(s) (Station Code(s) 105SH9274). |
Temporal Representation: |
Date for this waterbody was collected over the date range 2013-03-07 to 2013-11-20 |
Environmental Conditions: |
|
QAPP Information: |
Quality Assurance Program Plan and Standard Operating Procedures for SWAMP program |
QAPP Information Reference(s): |
Quality Assurance Program Plans, Quality Assurance Project Plans, and Standard Operating Procedures for the SWAMP program |
|
Line of Evidence (LOE) for Decision ID 105203, Terbufos
|
Region 1 |
Klamath River HU, Shasta River HA |
|
|
LOE ID: |
105203 |
|
Pollutant: |
Terbufos |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Total |
|
Beneficial Use: |
Municipal & Domestic Supply |
|
Number of Samples: |
3 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP RWB1 Monitoring data for Klamath River HU, Shasta River HA to determine beneficial use support and results are as follows: 0 of 3 samples exceeded the water quality standard for Terbufos. |
Data Reference: |
Water Quality Assessment Data for the 2018 solicitation cycle submitted through CEDEN for SWAMP RWB1 Monitoring .
|
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
Water Quality Control Plan, North Coast Basin: All waters shall be maintained free of toxic substances in concentrations that are toxic to, or that produce detrimental physiological responses in human, plant, animal, or aquatic life. |
Objective/Criterion Reference: |
Water Quality Control Plan (Basin Plan) for the North Coast Region |
|
Evaluation Guideline: |
The USEPA drinking water health advisory for terbufos is 0.4 µg/L. |
Guideline Reference: |
2012 Edition of the Drinking Water Standards and Health Advisories |
|
Spatial Representation: |
The samples were collected at 1 monitoring site(s) (105SH9274) |
Temporal Representation: |
The samples were collected between the dates of 2013-03-07 and 2013-11-20 |
Environmental Conditions: |
|
QAPP Information: |
Quality Assurance Program Plan and Standard Operating Procedures for SWAMP program |
QAPP Information Reference(s): |
Quality Assurance Program Plans, Quality Assurance Project Plans, and Standard Operating Procedures for the SWAMP program |
|
Line of Evidence (LOE) for Decision ID 105203, Terbufos
|
Region 1 |
Klamath River HU, Shasta River HA |
|
|
LOE ID: |
105202 |
|
Pollutant: |
Terbufos |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Total |
|
Beneficial Use: |
Municipal & Domestic Supply |
|
Number of Samples: |
3 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP RWB1 Monitoring data for Klamath River HU, Shasta River HA to determine beneficial use support and results are as follows: 0 of 3 samples exceeded the water quality standard for Terbufos. |
Data Reference: |
Water Quality Assessment Data for the 2018 solicitation cycle submitted through CEDEN for SWAMP RWB1 Monitoring .
|
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
Water Quality Control Plan, North Coast Basin: All waters shall be maintained free of toxic substances in concentrations that are toxic to, or that produce detrimental physiological responses in human, plant, animal, or aquatic life. |
Objective/Criterion Reference: |
Water Quality Control Plan (Basin Plan) for the North Coast Region |
|
Evaluation Guideline: |
The USEPA drinking water health advisory for terbufos is 0.4 µg/L. |
Guideline Reference: |
2012 Edition of the Drinking Water Standards and Health Advisories |
|
Spatial Representation: |
The samples were collected at 1 monitoring site(s) (105SH1452) |
Temporal Representation: |
The samples were collected between the dates of 2013-03-06 and 2013-11-20 |
Environmental Conditions: |
|
QAPP Information: |
Quality Assurance Program Plan and Standard Operating Procedures for SWAMP program |
QAPP Information Reference(s): |
Quality Assurance Program Plans, Quality Assurance Project Plans, and Standard Operating Procedures for the SWAMP program |
|
Line of Evidence (LOE) for Decision ID 105203, Terbufos
|
Region 1 |
Klamath River HU, Shasta River HA |
|
|
LOE ID: |
113157 |
|
Pollutant: |
Terbufos |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Total |
|
Beneficial Use: |
Warm Freshwater Habitat |
|
Number of Samples: |
0 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP RWB1 Monitoring data for Klamath River HU, Shasta River HA to determine beneficial use support, and the results are as follows: 0 of the 0 samples exceeded the evaluation guideline for Terbufos. Although a total of 3 samples were collected, 3 of these samples were not included in the assessment because the laboratory data reporting limit(s) was above the objective and therefore the results could not be quantified with the level of certainty required by the Listing Policy Section 6.1.5.5. |
Data Reference: |
Water Quality Assessment Data for the 2018 solicitation cycle submitted through CEDEN for SWAMP RWB1 Monitoring .
|
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
All waters shall be maintained free of toxic substances in concentrations which are toxic to, or which produce detrimental physiological responses in, human, plant, animal, or aquatic life. (Basin Plan). |
Objective/Criterion Reference: |
Water Quality Control Plan (Basin Plan) for the North Coast Region |
|
Evaluation Guideline: |
The evaluation guideline for Terbufos is the USEPA Aquatic Life Benchmark of 0.03 ug/L for an invertebrate (chronic). |
Guideline Reference: |
OPP Aquatic Life Benchmarks |
|
Spatial Representation: |
Data was collected from 1 station(s) (Station Code(s) 105SH9274). |
Temporal Representation: |
Date for this waterbody was collected over the date range 2013-03-07 to 2013-11-20 |
Environmental Conditions: |
|
QAPP Information: |
Quality Assurance Program Plan and Standard Operating Procedures for SWAMP program |
QAPP Information Reference(s): |
Quality Assurance Program Plans, Quality Assurance Project Plans, and Standard Operating Procedures for the SWAMP program |
|
Line of Evidence (LOE) for Decision ID 105203, Terbufos
|
Region 1 |
Klamath River HU, Shasta River HA |
|
|
LOE ID: |
106450 |
|
Pollutant: |
Terbufos |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Total |
|
Beneficial Use: |
Warm Freshwater Habitat |
|
Number of Samples: |
0 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP RWB1 Monitoring data for Klamath River HU, Shasta River HA to determine beneficial use support, and the results are as follows: 0 of the 0 samples exceeded the evaluation guideline for Terbufos. Although a total of 3 samples were collected, 3 of these samples were not included in the assessment because the laboratory data reporting limit(s) was above the objective and therefore the results could not be quantified with the level of certainty required by the Listing Policy Section 6.1.5.5. |
Data Reference: |
Water Quality Assessment Data for the 2018 solicitation cycle submitted through CEDEN for SWAMP RWB1 Monitoring .
|
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
All waters shall be maintained free of toxic substances in concentrations which are toxic to, or which produce detrimental physiological responses in, human, plant, animal, or aquatic life. (Basin Plan). |
Objective/Criterion Reference: |
Water Quality Control Plan (Basin Plan) for the North Coast Region |
|
Evaluation Guideline: |
The evaluation guideline for Terbufos is the USEPA Aquatic Life Benchmark of 0.03 ug/L for an invertebrate (chronic). |
Guideline Reference: |
OPP Aquatic Life Benchmarks |
|
Spatial Representation: |
Data was collected from 1 station(s) (Station Code(s) 105SH1452). |
Temporal Representation: |
Date for this waterbody was collected over the date range 2013-03-06 to 2013-11-20 |
Environmental Conditions: |
|
QAPP Information: |
Quality Assurance Program Plan and Standard Operating Procedures for SWAMP program |
QAPP Information Reference(s): |
Quality Assurance Program Plans, Quality Assurance Project Plans, and Standard Operating Procedures for the SWAMP program |
|
Line of Evidence (LOE) for Decision ID 169485, Thiobencarb
|
Region 1 |
Klamath River HU, Shasta River HA |
|
|
LOE ID: |
105216 |
|
Pollutant: |
Thiobencarb |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Total |
|
Beneficial Use: |
Cold Freshwater Habitat |
|
Number of Samples: |
3 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP RWB1 Monitoring data for Klamath River HU, Shasta River HA to determine beneficial use support and results are as follows: 0 of 3 samples exceeded the water quality standard for Thiobencarb. |
Data Reference: |
Water Quality Assessment Data for the 2018 solicitation cycle submitted through CEDEN for SWAMP RWB1 Monitoring .
|
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
All waters shall be maintained free of toxic substances in concentrations which are toxic to, or which produce detrimental physiological responses in, human, plant, animal, or aquatic life. (Basin Plan). |
Objective/Criterion Reference: |
Water Quality Control Plan (Basin Plan) for the North Coast Region |
|
Evaluation Guideline: |
The evaluation guideline for Thiobencarb is the USEPA Aquatic Life Benchmark of 1 ug/L for an invertebrate (chronic). |
Guideline Reference: |
OPP Aquatic Life Benchmarks |
|
Spatial Representation: |
The samples were collected at 1 monitoring site(s) (105SH9274) |
Temporal Representation: |
The samples were collected between the dates of 2013-03-07 and 2013-11-20 |
Environmental Conditions: |
|
QAPP Information: |
Quality Assurance Program Plan and Standard Operating Procedures for SWAMP program |
QAPP Information Reference(s): |
Quality Assurance Program Plans, Quality Assurance Project Plans, and Standard Operating Procedures for the SWAMP program |
|
Line of Evidence (LOE) for Decision ID 169485, Thiobencarb
|
Region 1 |
Klamath River HU, Shasta River HA |
|
|
LOE ID: |
105217 |
|
Pollutant: |
Thiobencarb |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Total |
|
Beneficial Use: |
Municipal & Domestic Supply |
|
Number of Samples: |
3 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP RWB1 Monitoring data for Klamath River HU, Shasta River HA to determine beneficial use support and results are as follows: 0 of 3 samples exceeded the water quality standard for Thiobencarb. |
Data Reference: |
Water Quality Assessment Data for the 2018 solicitation cycle submitted through CEDEN for SWAMP RWB1 Monitoring .
|
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
Water Quality Control Plan, North Coast Region (NCRWQCB 2018): Waters designated for use as domestic or municipal supply (MUN) shall not contain concentrations of chemical constituents in excess of the limits specified in California Code of Regulations, Title 22, Chapter 15. The secondary maximum contaminant level listed in Table 64449-A for thiobencarb is 0.001 mg/L |
Objective/Criterion Reference: |
Water Quality Control Plan (Basin Plan) for the North Coast Region |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
The samples were collected at 1 monitoring site(s) (105SH9274) |
Temporal Representation: |
The samples were collected between the dates of 2013-03-07 and 2013-11-20 |
Environmental Conditions: |
|
QAPP Information: |
Quality Assurance Program Plan and Standard Operating Procedures for SWAMP program |
QAPP Information Reference(s): |
Quality Assurance Program Plans, Quality Assurance Project Plans, and Standard Operating Procedures for the SWAMP program |
|
Line of Evidence (LOE) for Decision ID 169485, Thiobencarb
|
Region 1 |
Klamath River HU, Shasta River HA |
|
|
LOE ID: |
351114 |
|
Pollutant: |
Thiobencarb |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Total |
|
Beneficial Use: |
Cold Freshwater Habitat |
|
Number of Samples: |
3 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed RWB1 Trend Maintenance Periods FYs 2007 2008 data for Klamath River HU, Shasta River HA to determine beneficial use support and results are as follows: 0 of 3 samples exceeded the water quality threshold for Thiobencarb. |
Data Reference: |
RWB1 Trend Maintenance Periods FYs 2007 2008 |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
All waters shall be maintained free of toxic substances in concentrations which are toxic to, or which produce detrimental physiological responses in, human, plant, animal, or aquatic life. (Basin Plan). |
Objective/Criterion Reference: |
Water Quality Control Plan (Basin Plan) for the North Coast Region |
|
Evaluation Guideline: |
The evaluation guideline for thiobencarb is the USEPA Aquatic Life Benchmark of 1 ug/L for an invertebrate (chronic). |
Guideline Reference: |
OPP Aquatic Life Benchmarks |
|
Spatial Representation: |
The samples were collected at 1 monitoring site: 105SHAEDG (Shasta River near Edgewood). |
Temporal Representation: |
The samples were collected between the dates of 2007-11-15 and 2008-07-16 |
Environmental Conditions: |
|
QAPP Information: |
Generic SWAMP QAPrP |
QAPP Information Reference(s): |
Generic SWAMP QAPrP |
|
Line of Evidence (LOE) for Decision ID 169485, Thiobencarb
|
Region 1 |
Klamath River HU, Shasta River HA |
|
|
LOE ID: |
351097 |
|
Pollutant: |
Thiobencarb |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Total |
|
Beneficial Use: |
Warm Freshwater Habitat |
|
Number of Samples: |
3 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed RWB1 Trend Maintenance Periods FYs 2007 2008 data for Klamath River HU, Shasta River HA to determine beneficial use support and results are as follows: 0 of 3 samples exceeded the water quality threshold for Thiobencarb. |
Data Reference: |
RWB1 Trend Maintenance Periods FYs 2007 2008 |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
All waters shall be maintained free of toxic substances in concentrations which are toxic to, or which produce detrimental physiological responses in, human, plant, animal, or aquatic life. (Basin Plan). |
Objective/Criterion Reference: |
Water Quality Control Plan (Basin Plan) for the North Coast Region |
|
Evaluation Guideline: |
The evaluation guideline for thiobencarb is the USEPA Aquatic Life Benchmark of 1 ug/L for an invertebrate (chronic). |
Guideline Reference: |
OPP Aquatic Life Benchmarks |
|
Spatial Representation: |
The samples were collected at 1 monitoring site: 105SHAEDG (Shasta River near Edgewood). |
Temporal Representation: |
The samples were collected between the dates of 2007-11-15 and 2008-07-16 |
Environmental Conditions: |
|
QAPP Information: |
Generic SWAMP QAPrP |
QAPP Information Reference(s): |
Generic SWAMP QAPrP |
|
Line of Evidence (LOE) for Decision ID 169485, Thiobencarb
|
Region 1 |
Klamath River HU, Shasta River HA |
|
|
LOE ID: |
123385 |
|
Pollutant: |
Thiobencarb/Bolero |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
None |
|
Beneficial Use: |
Municipal & Domestic Supply |
|
Number of Samples: |
0 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
State Water Board staff re-assessed SWAMP data for Klamath River HU, Shasta River HA to determine beneficial use support and results are as follows: 0 of 0 samples exceed the criterion for Thiobencarb, Total. Thirty-two sample results were not used in the assessment because the laboratory data reporting limit(s) was above the objective and therefore the results could not be quantified with the level of certainty required by the Listing Policy. This LOE re-assesses data from LOE 29849 from the 2010 Integrated Report. Data were re-assessed in order to (1) update the numeric objective, and (2) evaluate these data in their own LOE, instead of being evaluated in the same LOE as other pesticide data. |
Data Reference: |
Surface Water Ambient Monitoring Program (SWAMP). Summary Report for the North Coast Region (RWQCB-1) for years 2000-2006. North Coast Regional Water Quality Control Board. March 2008 |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
Water Quality Control Plan, North Coast Region (NCRWQCB 2011): Waters designated for use as domestic or municipal supply (MUN) shall not contain concentrations of chemical constituents in excess of the limits specified in California Code of Regulations, Title 22, Chapter 15. The secondary maximum contaminant level listed in Table 64449-A for thiobencarb is 0.001 mg/L. |
Objective/Criterion Reference: |
Water Quality Control Plan (Basin Plan) for the North Coast Region |
Objective/Criterion Reference: |
Secondary Maximum Contaminant Levels and Compliance. CCR Title 22 section 64449. |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
Data for this line of evidence for Klamath River HU, Shasta River HA was collected at 1 monitoring site [ Shasta River at Hwy 263 - 105SH1452] |
Temporal Representation: |
Data was collected over the time period 2/27/2002-11/16/2006. |
Environmental Conditions: |
There are no known environmental conditions (e.g., seasonality, land use practices, fire events, storms, etc.) that are related to these data. |
QAPP Information: |
Quality control was conducted in accordance with the SWAMP Quality Assurance Management Plan (SWAMP 2002). |
QAPP Information Reference(s): |
Quality Assurance Management Plan for the State of California's Surface Water Ambient Monitoring Program. Sacramento, CA. State Water Resources Control Board. SWAMP. December 2002 (1st version)
|
|
Line of Evidence (LOE) for Decision ID 169485, Thiobencarb
|
Region 1 |
Klamath River HU, Shasta River HA |
|
|
LOE ID: |
123386 |
|
Pollutant: |
Thiobencarb/Bolero |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
None |
|
Beneficial Use: |
Municipal & Domestic Supply |
|
Number of Samples: |
0 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
State Water Board staff re-assessed SWAMP data for Klamath River HU, Shasta River HA to determine beneficial use support and results are as follows: 0 of 0 samples exceed the criterion for Thiobencarb, Total. Eight sample results were not used in the assessment because the laboratory data reporting limit(s) was above the objective and therefore the results could not be quantified with the level of certainty required by the Listing Policy. This LOE re-assesses data from LOE 29849 from the 2010 Integrated Report. Data were re-assessed in order to (1) update the numeric objective, and (2) evaluate these data in their own LOE, instead of being evaluated in the same LOE as other pesticide data. |
Data Reference: |
Surface Water Ambient Monitoring Program (SWAMP). Summary Report for the North Coast Region (RWQCB-1) for years 2000-2006. North Coast Regional Water Quality Control Board. March 2008 |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
Water Quality Control Plan, North Coast Region (NCRWQCB 2011): Waters designated for use as domestic or municipal supply (MUN) shall not contain concentrations of chemical constituents in excess of the limits specified in California Code of Regulations, Title 22, Chapter 15. The secondary maximum contaminant level listed in Table 64449-A for thiobencarb is 0.001 mg/L. |
Objective/Criterion Reference: |
Water Quality Control Plan (Basin Plan) for the North Coast Region |
Objective/Criterion Reference: |
Secondary Maximum Contaminant Levels and Compliance. CCR Title 22 section 64449. |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
Data for this line of evidence for Klamath River HU, Shasta River HA was collected at 1 monitoring site [ Shasta River at Montague - 105SHAMON] |
Temporal Representation: |
Data was collected over the time period 10/7/2002-6/19/2003. |
Environmental Conditions: |
There are no known environmental conditions (e.g., seasonality, land use practices, fire events, storms, etc.) that are related to these data. |
QAPP Information: |
Quality control was conducted in accordance with the SWAMP Quality Assurance Management Plan (SWAMP 2002). |
QAPP Information Reference(s): |
Quality Assurance Management Plan for the State of California's Surface Water Ambient Monitoring Program. Sacramento, CA. State Water Resources Control Board. SWAMP. December 2002 (1st version)
|
|
Line of Evidence (LOE) for Decision ID 169485, Thiobencarb
|
Region 1 |
Klamath River HU, Shasta River HA |
|
|
LOE ID: |
43194 |
|
Pollutant: |
Thiobencarb/Bolero |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Total |
|
Beneficial Use: |
Municipal & Domestic Supply |
|
Number of Samples: |
3 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP data for Klamath River HU, Shasta River HA to determine beneficial use support and results are as follows: 0 of 3 samples exceed the criterion for Thiobencarb. |
Data Reference: |
RWB1 Trend Maintenance Periods FYs 2007 2008 |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
Water Quality Control Plan, North Coast Region (NCRWQCB 2011): Waters designated for use as domestic or municipal supply (MUN) shall not contain concentrations of chemical constituents in excess of the limits specified in California Code of Regulations, Title 22, Chapter 15. The secondary maximum contaminant level listed in Table 64449-A for thiobencarb is 0.001 mg/L |
Objective/Criterion Reference: |
Secondary Maximum Contaminant Levels and Compliance. CCR Title 22 section 64449. |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
Data for this line of evidence for Klamath River HU, Shasta River HA was collected at 1 monitoring site [ Shasta River near Edgewood - 105SHAEDG] |
Temporal Representation: |
Data was collected over the time period 11/15/2007-7/16/2008. |
Environmental Conditions: |
Staff is not aware of any special conditions that might affect interpretation of the data. |
QAPP Information: |
The SWAMP QAPP (2008) was followed. |
QAPP Information Reference(s): |
Surface Water Ambient Monitoring Program Quality Assurance Program Plan |
|
Line of Evidence (LOE) for Decision ID 169485, Thiobencarb
|
Region 1 |
Klamath River HU, Shasta River HA |
|
|
LOE ID: |
105213 |
|
Pollutant: |
Thiobencarb |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Total |
|
Beneficial Use: |
Cold Freshwater Habitat |
|
Number of Samples: |
3 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP RWB1 Monitoring data for Klamath River HU, Shasta River HA to determine beneficial use support and results are as follows: 0 of 3 samples exceeded the water quality standard for Thiobencarb. |
Data Reference: |
Water Quality Assessment Data for the 2018 solicitation cycle submitted through CEDEN for SWAMP RWB1 Monitoring .
|
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
All waters shall be maintained free of toxic substances in concentrations which are toxic to, or which produce detrimental physiological responses in, human, plant, animal, or aquatic life. (Basin Plan). |
Objective/Criterion Reference: |
Water Quality Control Plan (Basin Plan) for the North Coast Region |
|
Evaluation Guideline: |
The evaluation guideline for Thiobencarb is the USEPA Aquatic Life Benchmark of 1 ug/L for an invertebrate (chronic). |
Guideline Reference: |
OPP Aquatic Life Benchmarks |
|
Spatial Representation: |
The samples were collected at 1 monitoring site(s) (105SH1452) |
Temporal Representation: |
The samples were collected between the dates of 2013-03-06 and 2013-11-20 |
Environmental Conditions: |
|
QAPP Information: |
Quality Assurance Program Plan and Standard Operating Procedures for SWAMP program |
QAPP Information Reference(s): |
Quality Assurance Program Plans, Quality Assurance Project Plans, and Standard Operating Procedures for the SWAMP program |
|
Line of Evidence (LOE) for Decision ID 169485, Thiobencarb
|
Region 1 |
Klamath River HU, Shasta River HA |
|
|
LOE ID: |
105214 |
|
Pollutant: |
Thiobencarb |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Total |
|
Beneficial Use: |
Municipal & Domestic Supply |
|
Number of Samples: |
3 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP RWB1 Monitoring data for Klamath River HU, Shasta River HA to determine beneficial use support and results are as follows: 0 of 3 samples exceeded the water quality standard for Thiobencarb. |
Data Reference: |
Water Quality Assessment Data for the 2018 solicitation cycle submitted through CEDEN for SWAMP RWB1 Monitoring .
|
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
Water Quality Control Plan, North Coast Region (NCRWQCB 2018): Waters designated for use as domestic or municipal supply (MUN) shall not contain concentrations of chemical constituents in excess of the limits specified in California Code of Regulations, Title 22, Chapter 15. The secondary maximum contaminant level listed in Table 64449-A for thiobencarb is 0.001 mg/L |
Objective/Criterion Reference: |
Water Quality Control Plan (Basin Plan) for the North Coast Region |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
The samples were collected at 1 monitoring site(s) (105SH1452) |
Temporal Representation: |
The samples were collected between the dates of 2013-03-06 and 2013-11-20 |
Environmental Conditions: |
|
QAPP Information: |
Quality Assurance Program Plan and Standard Operating Procedures for SWAMP program |
QAPP Information Reference(s): |
Quality Assurance Program Plans, Quality Assurance Project Plans, and Standard Operating Procedures for the SWAMP program |
|
Line of Evidence (LOE) for Decision ID 169485, Thiobencarb
|
Region 1 |
Klamath River HU, Shasta River HA |
|
|
LOE ID: |
105215 |
|
Pollutant: |
Thiobencarb |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Total |
|
Beneficial Use: |
Warm Freshwater Habitat |
|
Number of Samples: |
3 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP RWB1 Monitoring data for Klamath River HU, Shasta River HA to determine beneficial use support and results are as follows: 0 of 3 samples exceeded the water quality standard for Thiobencarb. |
Data Reference: |
Water Quality Assessment Data for the 2018 solicitation cycle submitted through CEDEN for SWAMP RWB1 Monitoring .
|
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
All waters shall be maintained free of toxic substances in concentrations which are toxic to, or which produce detrimental physiological responses in, human, plant, animal, or aquatic life. (Basin Plan). |
Objective/Criterion Reference: |
Water Quality Control Plan (Basin Plan) for the North Coast Region |
|
Evaluation Guideline: |
The evaluation guideline for Thiobencarb is the USEPA Aquatic Life Benchmark of 1 ug/L for an invertebrate (chronic). |
Guideline Reference: |
OPP Aquatic Life Benchmarks |
|
Spatial Representation: |
The samples were collected at 1 monitoring site(s) (105SH1452) |
Temporal Representation: |
The samples were collected between the dates of 2013-03-06 and 2013-11-20 |
Environmental Conditions: |
|
QAPP Information: |
Quality Assurance Program Plan and Standard Operating Procedures for SWAMP program |
QAPP Information Reference(s): |
Quality Assurance Program Plans, Quality Assurance Project Plans, and Standard Operating Procedures for the SWAMP program |
|
Line of Evidence (LOE) for Decision ID 169485, Thiobencarb
|
Region 1 |
Klamath River HU, Shasta River HA |
|
|
LOE ID: |
123395 |
|
Pollutant: |
Thiobencarb/Bolero |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
None |
|
Beneficial Use: |
Municipal & Domestic Supply |
|
Number of Samples: |
0 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
State Water Board staff re-assessed SWAMP data for Klamath River HU, Shasta River HA to determine beneficial use support and results are as follows: 0 of 0 samples exceed the criterion for Thiobencarb, Total. Eight sample results were not used in the assessment because the laboratory data reporting limit(s) was above the objective and therefore the results could not be quantified with the level of certainty required by the Listing Policy. This LOE re-assesses data from LOE 29849 from the 2010 Integrated Report. Data were re-assessed in order to (1) update the numeric objective, and (2) evaluate these data in their own LOE, instead of being evaluated in the same LOE as other pesticide data. |
Data Reference: |
Surface Water Ambient Monitoring Program (SWAMP). Summary Report for the North Coast Region (RWQCB-1) for years 2000-2006. North Coast Regional Water Quality Control Board. March 2008 |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
Water Quality Control Plan, North Coast Region (NCRWQCB 2011): Waters designated for use as domestic or municipal supply (MUN) shall not contain concentrations of chemical constituents in excess of the limits specified in California Code of Regulations, Title 22, Chapter 15. The secondary maximum contaminant level listed in Table 64449-A for thiobencarb is 0.001 mg/L. |
Objective/Criterion Reference: |
Water Quality Control Plan (Basin Plan) for the North Coast Region |
Objective/Criterion Reference: |
Secondary Maximum Contaminant Levels and Compliance. CCR Title 22 section 64449. |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
Data for this line of evidence for Klamath River HU, Shasta River HA was collected at 1 monitoring site [ Yreka Creek at Highway 3 - 105YREHW3] |
Temporal Representation: |
Data was collected over the time period 10/21/2004-6/20/2005. |
Environmental Conditions: |
There are no known environmental conditions (e.g., seasonality, land use practices, fire events, storms, etc.) that are related to these data. |
QAPP Information: |
Quality control was conducted in accordance with the SWAMP Quality Assurance Management Plan (SWAMP 2002). |
QAPP Information Reference(s): |
Quality Assurance Management Plan for the State of California's Surface Water Ambient Monitoring Program. Sacramento, CA. State Water Resources Control Board. SWAMP. December 2002 (1st version)
|
|
Line of Evidence (LOE) for Decision ID 169485, Thiobencarb
|
Region 1 |
Klamath River HU, Shasta River HA |
|
|
LOE ID: |
43195 |
|
Pollutant: |
Thiobencarb/Bolero |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Total |
|
Beneficial Use: |
Municipal & Domestic Supply |
|
Number of Samples: |
3 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP data for Klamath River HU, Shasta River HA to determine beneficial use support and results are as follows: 0 of 3 samples exceed the criterion for Thiobencarb. |
Data Reference: |
RWB1 Trend Maintenance Periods FYs 2007 2008 |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
Water Quality Control Plan, North Coast Region (NCRWQCB 2011): Waters designated for use as domestic or municipal supply (MUN) shall not contain concentrations of chemical constituents in excess of the limits specified in California Code of Regulations, Title 22, Chapter 15. The secondary maximum contaminant level listed in Table 64449-A for thiobencarb is 0.001 mg/L |
Objective/Criterion Reference: |
Secondary Maximum Contaminant Levels and Compliance. CCR Title 22 section 64449. |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
Data for this line of evidence for Klamath River HU, Shasta River HA was collected at 1 monitoring site [ Shasta River at Hwy 263 - 105SHA263] |
Temporal Representation: |
Data was collected over the time period 11/15/2007-7/16/2008. |
Environmental Conditions: |
Staff is not aware of any special conditions that might affect interpretation of the data. |
QAPP Information: |
The SWAMP QAPP (2008) was followed. |
QAPP Information Reference(s): |
Surface Water Ambient Monitoring Program Quality Assurance Program Plan |
|
Line of Evidence (LOE) for Decision ID 169485, Thiobencarb
|
Region 1 |
Klamath River HU, Shasta River HA |
|
|
LOE ID: |
351101 |
|
Pollutant: |
Thiobencarb |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Total |
|
Beneficial Use: |
Cold Freshwater Habitat |
|
Number of Samples: |
3 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed RWB1 Trend Maintenance Periods FYs 2007 2008 data for Klamath River HU, Shasta River HA to determine beneficial use support and results are as follows: 0 of 3 samples exceeded the water quality threshold for Thiobencarb. |
Data Reference: |
RWB1 Trend Maintenance Periods FYs 2007 2008 |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
All waters shall be maintained free of toxic substances in concentrations which are toxic to, or which produce detrimental physiological responses in, human, plant, animal, or aquatic life. (Basin Plan). |
Objective/Criterion Reference: |
Water Quality Control Plan (Basin Plan) for the North Coast Region |
|
Evaluation Guideline: |
The evaluation guideline for thiobencarb is the USEPA Aquatic Life Benchmark of 1 ug/L for an invertebrate (chronic). |
Guideline Reference: |
OPP Aquatic Life Benchmarks |
|
Spatial Representation: |
The samples were collected at 1 monitoring site: 105SHA263 (Shasta River at Hwy 263). |
Temporal Representation: |
The samples were collected between the dates of 2007-11-15 and 2008-07-16 |
Environmental Conditions: |
|
QAPP Information: |
Generic SWAMP QAPrP |
QAPP Information Reference(s): |
Generic SWAMP QAPrP |
|
Line of Evidence (LOE) for Decision ID 169485, Thiobencarb
|
Region 1 |
Klamath River HU, Shasta River HA |
|
|
LOE ID: |
351103 |
|
Pollutant: |
Thiobencarb |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Total |
|
Beneficial Use: |
Warm Freshwater Habitat |
|
Number of Samples: |
3 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed RWB1 Trend Maintenance Periods FYs 2007 2008 data for Klamath River HU, Shasta River HA to determine beneficial use support and results are as follows: 0 of 3 samples exceeded the water quality threshold for Thiobencarb. |
Data Reference: |
RWB1 Trend Maintenance Periods FYs 2007 2008 |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
All waters shall be maintained free of toxic substances in concentrations which are toxic to, or which produce detrimental physiological responses in, human, plant, animal, or aquatic life. (Basin Plan). |
Objective/Criterion Reference: |
Water Quality Control Plan (Basin Plan) for the North Coast Region |
|
Evaluation Guideline: |
The evaluation guideline for thiobencarb is the USEPA Aquatic Life Benchmark of 1 ug/L for an invertebrate (chronic). |
Guideline Reference: |
OPP Aquatic Life Benchmarks |
|
Spatial Representation: |
The samples were collected at 1 monitoring site: 105SHA263 (Shasta River at Hwy 263). |
Temporal Representation: |
The samples were collected between the dates of 2007-11-15 and 2008-07-16 |
Environmental Conditions: |
|
QAPP Information: |
Generic SWAMP QAPrP |
QAPP Information Reference(s): |
Generic SWAMP QAPrP |
|
Line of Evidence (LOE) for Decision ID 169485, Thiobencarb
|
Region 1 |
Klamath River HU, Shasta River HA |
|
|
LOE ID: |
105219 |
|
Pollutant: |
Thiobencarb |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Total |
|
Beneficial Use: |
Warm Freshwater Habitat |
|
Number of Samples: |
3 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP RWB1 Monitoring data for Klamath River HU, Shasta River HA to determine beneficial use support and results are as follows: 0 of 3 samples exceeded the water quality standard for Thiobencarb. |
Data Reference: |
Water Quality Assessment Data for the 2018 solicitation cycle submitted through CEDEN for SWAMP RWB1 Monitoring .
|
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
All waters shall be maintained free of toxic substances in concentrations which are toxic to, or which produce detrimental physiological responses in, human, plant, animal, or aquatic life. (Basin Plan). |
Objective/Criterion Reference: |
Water Quality Control Plan (Basin Plan) for the North Coast Region |
|
Evaluation Guideline: |
The evaluation guideline for Thiobencarb is the USEPA Aquatic Life Benchmark of 1 ug/L for an invertebrate (chronic). |
Guideline Reference: |
OPP Aquatic Life Benchmarks |
|
Spatial Representation: |
The samples were collected at 1 monitoring site(s) (105SH9274) |
Temporal Representation: |
The samples were collected between the dates of 2013-03-07 and 2013-11-20 |
Environmental Conditions: |
|
QAPP Information: |
Quality Assurance Program Plan and Standard Operating Procedures for SWAMP program |
QAPP Information Reference(s): |
Quality Assurance Program Plans, Quality Assurance Project Plans, and Standard Operating Procedures for the SWAMP program |
|
Line of Evidence (LOE) for Decision ID 169485, Thiobencarb
|
Region 1 |
Klamath River HU, Shasta River HA |
|
|
LOE ID: |
123394 |
|
Pollutant: |
Thiobencarb/Bolero |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
None |
|
Beneficial Use: |
Municipal & Domestic Supply |
|
Number of Samples: |
0 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
State Water Board staff re-assessed SWAMP data for Klamath River HU, Shasta River HA to determine beneficial use support and results are as follows: 0 of 0 samples exceed the criterion for Thiobencarb, Total. Sixteen sample results were not used in the assessment because the laboratory data reporting limit(s) was above the objective and therefore the results could not be quantified with the level of certainty required by the Listing Policy. This LOE re-assesses data from LOE 29849 from the 2010 Integrated Report. Data were re-assessed in order to (1) update the numeric objective, and (2) evaluate these data in their own LOE, instead of being evaluated in the same LOE as other pesticide data. |
Data Reference: |
Surface Water Ambient Monitoring Program (SWAMP). Summary Report for the North Coast Region (RWQCB-1) for years 2000-2006. North Coast Regional Water Quality Control Board. March 2008 |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
Water Quality Control Plan, North Coast Region (NCRWQCB 2011): Waters designated for use as domestic or municipal supply (MUN) shall not contain concentrations of chemical constituents in excess of the limits specified in California Code of Regulations, Title 22, Chapter 15. The secondary maximum contaminant level listed in Table 64449-A for thiobencarb is 0.001 mg/L. |
Objective/Criterion Reference: |
Water Quality Control Plan (Basin Plan) for the North Coast Region |
Objective/Criterion Reference: |
Secondary Maximum Contaminant Levels and Compliance. CCR Title 22 section 64449. |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
Data for this line of evidence for Klamath River HU, Shasta River HA was collected at 1 monitoring site [ Yreka Creek at Anderson Rd - 105YREAND] |
Temporal Representation: |
Data was collected over the time period 10/9/2002-6/20/2005. |
Environmental Conditions: |
There are no known environmental conditions (e.g., seasonality, land use practices, fire events, storms, etc.) that are related to these data. |
QAPP Information: |
Quality control was conducted in accordance with the SWAMP Quality Assurance Management Plan (SWAMP 2002). |
QAPP Information Reference(s): |
Quality Assurance Management Plan for the State of California's Surface Water Ambient Monitoring Program. Sacramento, CA. State Water Resources Control Board. SWAMP. December 2002 (1st version)
|
|
Line of Evidence (LOE) for Decision ID 169485, Thiobencarb
|
Region 1 |
Klamath River HU, Shasta River HA |
|
|
LOE ID: |
123393 |
|
Pollutant: |
Thiobencarb/Bolero |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
None |
|
Beneficial Use: |
Municipal & Domestic Supply |
|
Number of Samples: |
0 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
State Water Board staff re-assessed SWAMP data for Klamath River HU, Shasta River HA to determine beneficial use support and results are as follows: 0 of 0 samples exceed the criterion for Thiobencarb, Total. Eight sample results were not used in the assessment because the laboratory data reporting limit(s) was above the objective and therefore the results could not be quantified with the level of certainty required by the Listing Policy. This LOE re-assesses data from LOE 29849 from the 2010 Integrated Report. Data were re-assessed in order to (1) update the numeric objective, and (2) evaluate these data in their own LOE, instead of being evaluated in the same LOE as other pesticide data. |
Data Reference: |
Surface Water Ambient Monitoring Program (SWAMP). Summary Report for the North Coast Region (RWQCB-1) for years 2000-2006. North Coast Regional Water Quality Control Board. March 2008 |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
Water Quality Control Plan, North Coast Region (NCRWQCB 2011): Waters designated for use as domestic or municipal supply (MUN) shall not contain concentrations of chemical constituents in excess of the limits specified in California Code of Regulations, Title 22, Chapter 15. The secondary maximum contaminant level listed in Table 64449-A for thiobencarb is 0.001 mg/L. |
Objective/Criterion Reference: |
Water Quality Control Plan (Basin Plan) for the North Coast Region |
Objective/Criterion Reference: |
Secondary Maximum Contaminant Levels and Compliance. CCR Title 22 section 64449. |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
Data for this line of evidence for Klamath River HU, Shasta River HA was collected at 1 monitoring site [ Shasta River near Edgewood - 105SH9274] |
Temporal Representation: |
Data was collected over the time period 10/7/2002-6/19/2003. |
Environmental Conditions: |
There are no known environmental conditions (e.g., seasonality, land use practices, fire events, storms, etc.) that are related to these data. |
QAPP Information: |
Quality control was conducted in accordance with the SWAMP Quality Assurance Management Plan (SWAMP 2002). |
QAPP Information Reference(s): |
Quality Assurance Management Plan for the State of California's Surface Water Ambient Monitoring Program. Sacramento, CA. State Water Resources Control Board. SWAMP. December 2002 (1st version)
|
|
Line of Evidence (LOE) for Decision ID 100722, Zinc
|
Region 1 |
Klamath River HU, Shasta River HA |
|
|
LOE ID: |
105228 |
|
Pollutant: |
Zinc |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Dissolved |
|
Beneficial Use: |
Cold Freshwater Habitat |
|
Number of Samples: |
5 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP RWB1 Monitoring data for Klamath River HU, Shasta River HA to determine beneficial use support and results are as follows: 0 of 5 samples exceeded the water quality standard for Zinc. |
Data Reference: |
Water Quality Assessment Data for the 2018 solicitation cycle submitted through CEDEN for SWAMP RWB1 Monitoring .
|
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
California Toxics Rule (CTR) lists criterion continuous concentrations to protect aquatic life in freshwater. The criterion in freshwater is hardness dependent for each sample and varies based on the ambient hardness during sampling. Section (b)(1) in CTR contains the hardness dependent formula for the metals criterion. |
Objective/Criterion Reference: |
Water Quality Standards 2000. Establishment of numeric criteria for priority toxic pollutants for the State of California: Rules and regulations. Federal Register Vol. 65, No. 97. Washington, D.C.: Environmental Protection Agency |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
The samples were collected at 1 monitoring site(s) (105SH9274) |
Temporal Representation: |
The samples were collected between the dates of 2013-03-07 and 2013-11-20 |
Environmental Conditions: |
|
QAPP Information: |
Quality Assurance Program Plan and Standard Operating Procedures for SWAMP program |
QAPP Information Reference(s): |
Quality Assurance Program Plans, Quality Assurance Project Plans, and Standard Operating Procedures for the SWAMP program |
|
Line of Evidence (LOE) for Decision ID 100722, Zinc
|
Region 1 |
Klamath River HU, Shasta River HA |
|
|
LOE ID: |
43284 |
|
Pollutant: |
Zinc |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Total |
|
Beneficial Use: |
Municipal & Domestic Supply |
|
Number of Samples: |
4 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP data for Klamath River HU, Shasta River HA to determine beneficial use support and results are as follows: 0 of 4 samples exceed the criterion for Zinc. |
Data Reference: |
RWB1 Trend Maintenance Periods FYs 2007 2008 |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
Water Quality Control Plan, North Coast Region (NCRWQCB 2011): Waters designated for use as domestic or municipal supply (MUN) shall not contain concentrations of chemical constituents in excess of the limits specified in California Code of Regulations, Title 22, Chapter 15. The secondary maximum contaminant level listed in Table 64449-A for Zinc is 5 mg/L. |
Objective/Criterion Reference: |
Secondary Maximum Contaminant Levels and Compliance. CCR Title 22 section 64449. |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
Data for this line of evidence for Klamath River HU, Shasta River HA was collected at 1 monitoring site [ Shasta River at Hwy 263 - 105SHA263] |
Temporal Representation: |
Data was collected over the time period 11/15/2007-7/16/2008. |
Environmental Conditions: |
Staff is not aware of any special conditions that might affect interpretation of the data. |
QAPP Information: |
The SWAMP QAPP (2008) was followed. |
QAPP Information Reference(s): |
Surface Water Ambient Monitoring Program Quality Assurance Program Plan |
|
Line of Evidence (LOE) for Decision ID 100722, Zinc
|
Region 1 |
Klamath River HU, Shasta River HA |
|
|
LOE ID: |
105230 |
|
Pollutant: |
Zinc |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Dissolved |
|
Beneficial Use: |
Warm Freshwater Habitat |
|
Number of Samples: |
5 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP RWB1 Monitoring data for Klamath River HU, Shasta River HA to determine beneficial use support and results are as follows: 0 of 5 samples exceeded the water quality standard for Zinc. |
Data Reference: |
Water Quality Assessment Data for the 2018 solicitation cycle submitted through CEDEN for SWAMP RWB1 Monitoring .
|
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
California Toxics Rule (CTR) lists criterion continuous concentrations to protect aquatic life in freshwater. The criterion in freshwater is hardness dependent for each sample and varies based on the ambient hardness during sampling. Section (b)(1) in CTR contains the hardness dependent formula for the metals criterion. |
Objective/Criterion Reference: |
Water Quality Standards 2000. Establishment of numeric criteria for priority toxic pollutants for the State of California: Rules and regulations. Federal Register Vol. 65, No. 97. Washington, D.C.: Environmental Protection Agency |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
The samples were collected at 1 monitoring site(s) (105SH9274) |
Temporal Representation: |
The samples were collected between the dates of 2013-03-07 and 2013-11-20 |
Environmental Conditions: |
|
QAPP Information: |
Quality Assurance Program Plan and Standard Operating Procedures for SWAMP program |
QAPP Information Reference(s): |
Quality Assurance Program Plans, Quality Assurance Project Plans, and Standard Operating Procedures for the SWAMP program |
|
Line of Evidence (LOE) for Decision ID 100722, Zinc
|
Region 1 |
Klamath River HU, Shasta River HA |
|
|
LOE ID: |
105227 |
|
Pollutant: |
Zinc |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Dissolved |
|
Beneficial Use: |
Warm Freshwater Habitat |
|
Number of Samples: |
5 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP RWB1 Monitoring data for Klamath River HU, Shasta River HA to determine beneficial use support and results are as follows: 0 of 5 samples exceeded the water quality standard for Zinc. |
Data Reference: |
Water Quality Assessment Data for the 2018 solicitation cycle submitted through CEDEN for SWAMP RWB1 Monitoring .
|
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
California Toxics Rule (CTR) lists criterion continuous concentrations to protect aquatic life in freshwater. The criterion in freshwater is hardness dependent for each sample and varies based on the ambient hardness during sampling. Section (b)(1) in CTR contains the hardness dependent formula for the metals criterion. |
Objective/Criterion Reference: |
Water Quality Standards 2000. Establishment of numeric criteria for priority toxic pollutants for the State of California: Rules and regulations. Federal Register Vol. 65, No. 97. Washington, D.C.: Environmental Protection Agency |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
The samples were collected at 1 monitoring site(s) (105SH1452) |
Temporal Representation: |
The samples were collected between the dates of 2013-03-06 and 2013-11-20 |
Environmental Conditions: |
|
QAPP Information: |
Quality Assurance Program Plan and Standard Operating Procedures for SWAMP program |
QAPP Information Reference(s): |
Quality Assurance Program Plans, Quality Assurance Project Plans, and Standard Operating Procedures for the SWAMP program |
|
Line of Evidence (LOE) for Decision ID 100722, Zinc
|
Region 1 |
Klamath River HU, Shasta River HA |
|
|
LOE ID: |
32579 |
|
Pollutant: |
Zinc |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Total |
|
Beneficial Use: |
Cold Freshwater Habitat |
|
Number of Samples: |
4 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
None of the 4 samples exceeded the hardness based criteria calculated for zinc. |
Data Reference: |
RWB1 Trend Maintenance Periods FYs 2007 2008 |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
Water Quality Control Plan, North Coast Region (NCRWQCB 2011): All waters shall be maintained free of toxic substances in concentrations that are toxic to, or that produce detrimental physiological responses in human, plant, animal, or aquatic life. California Toxics Rule (CTR) lists criterion continuous concentrations (4-day average) to protect aquatic life in freshwater. The criterion in freshwater is hardness dependent for each sample and varies based on the ambient hardness during sampling. Section (b)(1) in CTR contains the hardness dependent formula for the metals criterion. |
Objective/Criterion Reference: |
Code of Federal Regulations 40 part 131.38 Establishment of numeric criteria for priority toxic pollutants for the State of California. 7/1/2011 Edition |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
Samples collected at station 105SHA263 (Shasta River at Hwy 263). |
Temporal Representation: |
Samples collected between 11/15/2007 and 7/16/2008. |
Environmental Conditions: |
|
QAPP Information: |
SWAMP QAPP (2008) was followed. |
QAPP Information Reference(s): |
Surface Water Ambient Monitoring Program Quality Assurance Program Plan |
|
Line of Evidence (LOE) for Decision ID 100722, Zinc
|
Region 1 |
Klamath River HU, Shasta River HA |
|
|
LOE ID: |
32585 |
|
Pollutant: |
Zinc |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Total |
|
Beneficial Use: |
Cold Freshwater Habitat |
|
Number of Samples: |
4 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
None of the 4 samples exceeded the hardness based criteria calculated for zinc. |
Data Reference: |
RWB1 Trend Maintenance Periods FYs 2007 2008 |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
Water Quality Control Plan, North Coast Region (NCRWQCB 2011): All waters shall be maintained free of toxic substances in concentrations that are toxic to, or that produce detrimental physiological responses in human, plant, animal, or aquatic life. California Toxics Rule (CTR) lists criterion continuous concentrations (4-day average) to protect aquatic life in freshwater. The criterion in freshwater is hardness dependent for each sample and varies based on the ambient hardness during sampling. Section (b)(1) in CTR contains the hardness dependent formula for the metals criterion. |
Objective/Criterion Reference: |
Code of Federal Regulations 40 part 131.38 Establishment of numeric criteria for priority toxic pollutants for the State of California. 7/1/2011 Edition |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
Samples collected at station 105SHAEDG (Shasta River near Edgewood). |
Temporal Representation: |
Samples collected between 11/15/2007 and 7/16/2008. |
Environmental Conditions: |
|
QAPP Information: |
SWAMP QAPP (2008) was followed. |
QAPP Information Reference(s): |
Surface Water Ambient Monitoring Program Quality Assurance Program Plan |
|
Line of Evidence (LOE) for Decision ID 100722, Zinc
|
Region 1 |
Klamath River HU, Shasta River HA |
|
|
LOE ID: |
123443 |
|
Pollutant: |
Zinc |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Total |
|
Beneficial Use: |
Municipal & Domestic Supply |
|
Number of Samples: |
5 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
State Water Board staff re-assessed SWAMP data for Klamath River HU, Shasta River HA to determine beneficial use support and results are as follows: 0 of 5 samples exceed the criterion for Zinc, Total. This LOE re-assesses data from LOE 21509 from the 2010 Integrated Report. Data were re-assessed in order to evaluate these data in their own LOE, instead of being evaluated in the same LOE as other metals data. |
Data Reference: |
Surface Water Ambient Monitoring Program (SWAMP). Summary Report for the North Coast Region (RWQCB-1) for years 2000-2006. North Coast Regional Water Quality Control Board. March 2008 |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
Water Quality Control Plan, North Coast Region (NCRWQCB 2011): Waters designated for use as domestic or municipal supply (MUN) shall not contain concentrations of chemical constituents in excess of the limits specified in California Code of Regulations, Title 22, Chapter 15. The secondary maximum contaminant level listed in Table 64449-A for Zinc is 5 mg/L. |
Objective/Criterion Reference: |
Water Quality Control Plan (Basin Plan) for the North Coast Region |
Objective/Criterion Reference: |
Secondary Maximum Contaminant Levels and Compliance. CCR Title 22 section 64449. |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
Data for this line of evidence for Klamath River HU, Shasta River HA was collected at 1 monitoring site [ Shasta River near Edgewood - 105SH9274] |
Temporal Representation: |
Data was collected over the time period 10/7/2002-6/19/2003. |
Environmental Conditions: |
There are no known environmental conditions (e.g., seasonality, land use practices, fire events, storms, etc.) that are related to these data. |
QAPP Information: |
Quality control was conducted in accordance with the SWAMP Quality Assurance Management Plan (SWAMP 2002). |
QAPP Information Reference(s): |
Quality Assurance Management Plan for the State of California's Surface Water Ambient Monitoring Program. Sacramento, CA. State Water Resources Control Board. SWAMP. December 2002 (1st version)
|
|
Line of Evidence (LOE) for Decision ID 100722, Zinc
|
Region 1 |
Klamath River HU, Shasta River HA |
|
|
LOE ID: |
123454 |
|
Pollutant: |
Zinc |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Total |
|
Beneficial Use: |
Municipal & Domestic Supply |
|
Number of Samples: |
3 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
State Water Board staff re-assessed SWAMP data for Klamath River HU, Shasta River HA to determine beneficial use support and results are as follows: 0 of 3 samples exceed the criterion for Zinc, Total. This LOE re-assesses data from LOE 21509 from the 2010 Integrated Report. Data were re-assessed in order to evaluate these data in their own LOE, instead of being evaluated in the same LOE as other metals data. |
Data Reference: |
Surface Water Ambient Monitoring Program (SWAMP). Summary Report for the North Coast Region (RWQCB-1) for years 2000-2006. North Coast Regional Water Quality Control Board. March 2008 |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
Water Quality Control Plan, North Coast Region (NCRWQCB 2011): Waters designated for use as domestic or municipal supply (MUN) shall not contain concentrations of chemical constituents in excess of the limits specified in California Code of Regulations, Title 22, Chapter 15. The secondary maximum contaminant level listed in Table 64449-A for Zinc is 5 mg/L. |
Objective/Criterion Reference: |
Water Quality Control Plan (Basin Plan) for the North Coast Region |
Objective/Criterion Reference: |
Secondary Maximum Contaminant Levels and Compliance. CCR Title 22 section 64449. |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
Data for this line of evidence for Klamath River HU, Shasta River HA was collected at 1 monitoring site [ Yreka Creek at Highway 3 - 105YREHW3] |
Temporal Representation: |
Data was collected over the time period 10/21/2004-6/20/2005. |
Environmental Conditions: |
There are no known environmental conditions (e.g., seasonality, land use practices, fire events, storms, etc.) that are related to these data. |
QAPP Information: |
Quality control was conducted in accordance with the SWAMP Quality Assurance Management Plan (SWAMP 2002). |
QAPP Information Reference(s): |
Quality Assurance Management Plan for the State of California's Surface Water Ambient Monitoring Program. Sacramento, CA. State Water Resources Control Board. SWAMP. December 2002 (1st version)
|
|
Line of Evidence (LOE) for Decision ID 100722, Zinc
|
Region 1 |
Klamath River HU, Shasta River HA |
|
|
LOE ID: |
105231 |
|
Pollutant: |
Zinc |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Total |
|
Beneficial Use: |
Municipal & Domestic Supply |
|
Number of Samples: |
5 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP RWB1 Monitoring data for Klamath River HU, Shasta River HA to determine beneficial use support and results are as follows: 0 of 5 samples exceeded the water quality standard for Zinc. |
Data Reference: |
Water Quality Assessment Data for the 2018 solicitation cycle submitted through CEDEN for SWAMP RWB1 Monitoring .
|
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
Water Quality Control Plan, North Coast Region (NCRWQCB 2018): Waters designated for use as domestic or municipal supply (MUN) shall not contain concentrations of chemical constituents in excess of the limits specified in California Code of Regulations, Title 22, Chapter 15. The secondary maximum contaminant level listed in Table 64449-A for Zinc is 5 mg/L. |
Objective/Criterion Reference: |
Water Quality Control Plan (Basin Plan) for the North Coast Region |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
The samples were collected at 1 monitoring site(s) (105SH1452) |
Temporal Representation: |
The samples were collected between the dates of 2013-03-06 and 2013-11-20 |
Environmental Conditions: |
|
QAPP Information: |
Quality Assurance Program Plan and Standard Operating Procedures for SWAMP program |
QAPP Information Reference(s): |
Quality Assurance Program Plans, Quality Assurance Project Plans, and Standard Operating Procedures for the SWAMP program |
|
Line of Evidence (LOE) for Decision ID 100722, Zinc
|
Region 1 |
Klamath River HU, Shasta River HA |
|
|
LOE ID: |
43272 |
|
Pollutant: |
Zinc |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Total |
|
Beneficial Use: |
Municipal & Domestic Supply |
|
Number of Samples: |
4 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP data for Klamath River HU, Shasta River HA to determine beneficial use support and results are as follows: 0 of 4 samples exceed the criterion for Zinc. |
Data Reference: |
RWB1 Trend Maintenance Periods FYs 2007 2008 |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
Water Quality Control Plan, North Coast Region (NCRWQCB 2011): Waters designated for use as domestic or municipal supply (MUN) shall not contain concentrations of chemical constituents in excess of the limits specified in California Code of Regulations, Title 22, Chapter 15. The secondary maximum contaminant level listed in Table 64449-A for Zinc is 5 mg/L. |
Objective/Criterion Reference: |
Secondary Maximum Contaminant Levels and Compliance. CCR Title 22 section 64449. |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
Data for this line of evidence for Klamath River HU, Shasta River HA was collected at 1 monitoring site [ Shasta River near Edgewood - 105SHAEDG] |
Temporal Representation: |
Data was collected over the time period 11/15/2007-7/16/2008. |
Environmental Conditions: |
Staff is not aware of any special conditions that might affect interpretation of the data. |
QAPP Information: |
The SWAMP QAPP (2008) was followed. |
QAPP Information Reference(s): |
Surface Water Ambient Monitoring Program Quality Assurance Program Plan |
|
Line of Evidence (LOE) for Decision ID 100722, Zinc
|
Region 1 |
Klamath River HU, Shasta River HA |
|
|
LOE ID: |
123442 |
|
Pollutant: |
Zinc |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Total |
|
Beneficial Use: |
Municipal & Domestic Supply |
|
Number of Samples: |
22 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
State Water Board staff re-assessed SWAMP data for Klamath River HU, Shasta River HA to determine beneficial use support and results are as follows: 0 of 22 samples exceed the criterion for Zinc, Total. This LOE re-assesses data from LOE 21509 from the 2010 Integrated Report. Data were re-assessed in order to evaluate these data in their own LOE, instead of being evaluated in the same LOE as other metals data. |
Data Reference: |
Surface Water Ambient Monitoring Program (SWAMP). Summary Report for the North Coast Region (RWQCB-1) for years 2000-2006. North Coast Regional Water Quality Control Board. March 2008 |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
Water Quality Control Plan, North Coast Region (NCRWQCB 2011): Waters designated for use as domestic or municipal supply (MUN) shall not contain concentrations of chemical constituents in excess of the limits specified in California Code of Regulations, Title 22, Chapter 15. The secondary maximum contaminant level listed in Table 64449-A for Zinc is 5 mg/L. |
Objective/Criterion Reference: |
Water Quality Control Plan (Basin Plan) for the North Coast Region |
Objective/Criterion Reference: |
Secondary Maximum Contaminant Levels and Compliance. CCR Title 22 section 64449. |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
Data for this line of evidence for Klamath River HU, Shasta River HA was collected at 1 monitoring site [ Shasta River at Hwy 263 - 105SH1452] |
Temporal Representation: |
Data was collected over the time period 3/20/2001-11/16/2006. |
Environmental Conditions: |
There are no known environmental conditions (e.g., seasonality, land use practices, fire events, storms, etc.) that are related to these data. |
QAPP Information: |
Quality control was conducted in accordance with the SWAMP Quality Assurance Management Plan (SWAMP 2002). |
QAPP Information Reference(s): |
Quality Assurance Management Plan for the State of California's Surface Water Ambient Monitoring Program. Sacramento, CA. State Water Resources Control Board. SWAMP. December 2002 (1st version)
|
|
Line of Evidence (LOE) for Decision ID 100722, Zinc
|
Region 1 |
Klamath River HU, Shasta River HA |
|
|
LOE ID: |
123455 |
|
Pollutant: |
Zinc |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Total |
|
Beneficial Use: |
Municipal & Domestic Supply |
|
Number of Samples: |
5 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
State Water Board staff re-assessed SWAMP data for Klamath River HU, Shasta River HA to determine beneficial use support and results are as follows: 0 of 5 samples exceed the criterion for Zinc, Total. This LOE re-assesses data from LOE 21509 from the 2010 Integrated Report. Data were re-assessed in order to evaluate these data in their own LOE, instead of being evaluated in the same LOE as other metals data. |
Data Reference: |
Surface Water Ambient Monitoring Program (SWAMP). Summary Report for the North Coast Region (RWQCB-1) for years 2000-2006. North Coast Regional Water Quality Control Board. March 2008 |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
Water Quality Control Plan, North Coast Region (NCRWQCB 2011): Waters designated for use as domestic or municipal supply (MUN) shall not contain concentrations of chemical constituents in excess of the limits specified in California Code of Regulations, Title 22, Chapter 15. The secondary maximum contaminant level listed in Table 64449-A for Zinc is 5 mg/L. |
Objective/Criterion Reference: |
Water Quality Control Plan (Basin Plan) for the North Coast Region |
Objective/Criterion Reference: |
Secondary Maximum Contaminant Levels and Compliance. CCR Title 22 section 64449. |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
Data for this line of evidence for Klamath River HU, Shasta River HA was collected at 1 monitoring site [ Shasta River at Montague - 105SHAMON] |
Temporal Representation: |
Data was collected over the time period 10/7/2002-6/19/2003. |
Environmental Conditions: |
There are no known environmental conditions (e.g., seasonality, land use practices, fire events, storms, etc.) that are related to these data. |
QAPP Information: |
Quality control was conducted in accordance with the SWAMP Quality Assurance Management Plan (SWAMP 2002). |
QAPP Information Reference(s): |
Quality Assurance Management Plan for the State of California's Surface Water Ambient Monitoring Program. Sacramento, CA. State Water Resources Control Board. SWAMP. December 2002 (1st version)
|
|
Line of Evidence (LOE) for Decision ID 100722, Zinc
|
Region 1 |
Klamath River HU, Shasta River HA |
|
|
LOE ID: |
105232 |
|
Pollutant: |
Zinc |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Total |
|
Beneficial Use: |
Municipal & Domestic Supply |
|
Number of Samples: |
5 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP RWB1 Monitoring data for Klamath River HU, Shasta River HA to determine beneficial use support and results are as follows: 0 of 5 samples exceeded the water quality standard for Zinc. |
Data Reference: |
Water Quality Assessment Data for the 2018 solicitation cycle submitted through CEDEN for SWAMP RWB1 Monitoring .
|
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
Water Quality Control Plan, North Coast Region (NCRWQCB 2018): Waters designated for use as domestic or municipal supply (MUN) shall not contain concentrations of chemical constituents in excess of the limits specified in California Code of Regulations, Title 22, Chapter 15. The secondary maximum contaminant level listed in Table 64449-A for Zinc is 5 mg/L. |
Objective/Criterion Reference: |
Water Quality Control Plan (Basin Plan) for the North Coast Region |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
The samples were collected at 1 monitoring site(s) (105SH9274) |
Temporal Representation: |
The samples were collected between the dates of 2013-03-07 and 2013-11-20 |
Environmental Conditions: |
|
QAPP Information: |
Quality Assurance Program Plan and Standard Operating Procedures for SWAMP program |
QAPP Information Reference(s): |
Quality Assurance Program Plans, Quality Assurance Project Plans, and Standard Operating Procedures for the SWAMP program |
|
Line of Evidence (LOE) for Decision ID 100722, Zinc
|
Region 1 |
Klamath River HU, Shasta River HA |
|
|
LOE ID: |
123453 |
|
Pollutant: |
Zinc |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Total |
|
Beneficial Use: |
Municipal & Domestic Supply |
|
Number of Samples: |
7 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
State Water Board staff re-assessed SWAMP data for Klamath River HU, Shasta River HA to determine beneficial use support and results are as follows: 0 of 7 samples exceed the criterion for Zinc, Total. This LOE re-assesses data from LOE 21509 from the 2010 Integrated Report. Data were re-assessed in order to evaluate these data in their own LOE, instead of being evaluated in the same LOE as other metals data. |
Data Reference: |
Surface Water Ambient Monitoring Program (SWAMP). Summary Report for the North Coast Region (RWQCB-1) for years 2000-2006. North Coast Regional Water Quality Control Board. March 2008 |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
Water Quality Control Plan, North Coast Region (NCRWQCB 2011): Waters designated for use as domestic or municipal supply (MUN) shall not contain concentrations of chemical constituents in excess of the limits specified in California Code of Regulations, Title 22, Chapter 15. The secondary maximum contaminant level listed in Table 64449-A for Zinc is 5 mg/L. |
Objective/Criterion Reference: |
Water Quality Control Plan (Basin Plan) for the North Coast Region |
Objective/Criterion Reference: |
Secondary Maximum Contaminant Levels and Compliance. CCR Title 22 section 64449. |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
Data for this line of evidence for Klamath River HU, Shasta River HA was collected at 1 monitoring site [ Yreka Creek at Anderson Rd - 105YREAND] |
Temporal Representation: |
Data was collected over the time period 10/9/2002-6/20/2005. |
Environmental Conditions: |
There are no known environmental conditions (e.g., seasonality, land use practices, fire events, storms, etc.) that are related to these data. |
QAPP Information: |
Quality control was conducted in accordance with the SWAMP Quality Assurance Management Plan (SWAMP 2002). |
QAPP Information Reference(s): |
Quality Assurance Management Plan for the State of California's Surface Water Ambient Monitoring Program. Sacramento, CA. State Water Resources Control Board. SWAMP. December 2002 (1st version)
|
|
Line of Evidence (LOE) for Decision ID 100722, Zinc
|
Region 1 |
Klamath River HU, Shasta River HA |
|
|
LOE ID: |
105226 |
|
Pollutant: |
Zinc |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Dissolved |
|
Beneficial Use: |
Cold Freshwater Habitat |
|
Number of Samples: |
5 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP RWB1 Monitoring data for Klamath River HU, Shasta River HA to determine beneficial use support and results are as follows: 0 of 5 samples exceeded the water quality standard for Zinc. |
Data Reference: |
Water Quality Assessment Data for the 2018 solicitation cycle submitted through CEDEN for SWAMP RWB1 Monitoring .
|
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
California Toxics Rule (CTR) lists criterion continuous concentrations to protect aquatic life in freshwater. The criterion in freshwater is hardness dependent for each sample and varies based on the ambient hardness during sampling. Section (b)(1) in CTR contains the hardness dependent formula for the metals criterion. |
Objective/Criterion Reference: |
Water Quality Standards 2000. Establishment of numeric criteria for priority toxic pollutants for the State of California: Rules and regulations. Federal Register Vol. 65, No. 97. Washington, D.C.: Environmental Protection Agency |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
The samples were collected at 1 monitoring site(s) (105SH1452) |
Temporal Representation: |
The samples were collected between the dates of 2013-03-06 and 2013-11-20 |
Environmental Conditions: |
|
QAPP Information: |
Quality Assurance Program Plan and Standard Operating Procedures for SWAMP program |
QAPP Information Reference(s): |
Quality Assurance Program Plans, Quality Assurance Project Plans, and Standard Operating Procedures for the SWAMP program |
|
Line of Evidence (LOE) for Decision ID 168775, alpha-Endosulfan (Endosulfan 1)
|
Region 1 |
Klamath River HU, Shasta River HA |
|
|
LOE ID: |
41539 |
|
Pollutant: |
alpha-Endosulfan (Endosulfan 1) |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Total |
|
Beneficial Use: |
Warm Freshwater Habitat |
|
Number of Samples: |
3 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP data for Klamath River HU, Shasta River HA to determine beneficial use support and results are as follows: 0 of 3 samples exceed the criterion for Endosulfan I. |
Data Reference: |
RWB1 Trend Maintenance Periods FYs 2007 2008 |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
Water Quality Control Plan, North Coast Region (NCRWQCB 2011): All waters shall be maintained free of toxic substances in concentrations that are toxic to, or that produce detrimental physiological responses in human, plant, animal, or aquatic life. The established numeric criteria for alpha-endosulfan to protect aquatic life in freshwater as criterion continuous concentration (expressed as a 4-day average) is 0.056 ug/L (California Toxics Rule, 2000). |
Objective/Criterion Reference: |
Code of Federal Regulations 40 part 131.38 Establishment of numeric criteria for priority toxic pollutants for the State of California. 7/1/2011 Edition |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
Data for this line of evidence for Klamath River HU, Shasta River HA was collected at 1 monitoring site [ Shasta River at Hwy 263 - 105SHA263] |
Temporal Representation: |
Data was collected over the time period 11/15/2007-7/16/2008. |
Environmental Conditions: |
Staff is not aware of any special conditions that might affect interpretation of the data. |
QAPP Information: |
The SWAMP QAPP (2008) was followed. |
QAPP Information Reference(s): |
Surface Water Ambient Monitoring Program Quality Assurance Program Plan |
|
Line of Evidence (LOE) for Decision ID 168775, alpha-Endosulfan (Endosulfan 1)
|
Region 1 |
Klamath River HU, Shasta River HA |
|
|
LOE ID: |
109491 |
|
Pollutant: |
alpha-Endosulfan (Endosulfan 1) |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Total |
|
Beneficial Use: |
Commercial or recreational collection of fish, shellfish, or organisms |
|
Number of Samples: |
1 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP RWB1 Monitoring data for Klamath River HU, Shasta River HA to determine beneficial use support and results are as follows: 0 of 1 samples exceeded the water quality standard for Endosulfan I. |
Data Reference: |
Water Quality Assessment Data for the 2018 solicitation cycle submitted through CEDEN for SWAMP RWB1 Monitoring .
|
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
The established numeric criteria for alpha-endosulfan to protection of human health from consumption of organisms only is 240 ug/L (California Toxics Rule, 2000). |
Objective/Criterion Reference: |
Water Quality Standards 2000. Establishment of numeric criteria for priority toxic pollutants for the State of California: Rules and regulations. Federal Register Vol. 65, No. 97. Washington, D.C.: Environmental Protection Agency |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
The samples were collected at 1 monitoring site(s) (105SH1452) |
Temporal Representation: |
The samples were collected between the dates of 2013-04-29 and 2013-04-29 |
Environmental Conditions: |
|
QAPP Information: |
Quality Assurance Program Plan and Standard Operating Procedures for SWAMP program |
QAPP Information Reference(s): |
Quality Assurance Program Plans, Quality Assurance Project Plans, and Standard Operating Procedures for the SWAMP program |
|
Line of Evidence (LOE) for Decision ID 168775, alpha-Endosulfan (Endosulfan 1)
|
Region 1 |
Klamath River HU, Shasta River HA |
|
|
LOE ID: |
109495 |
|
Pollutant: |
alpha-Endosulfan (Endosulfan 1) |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Total |
|
Beneficial Use: |
Cold Freshwater Habitat |
|
Number of Samples: |
1 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP RWB1 Monitoring data for Klamath River HU, Shasta River HA to determine beneficial use support and results are as follows: 0 of 1 samples exceeded the water quality standard for Endosulfan I. |
Data Reference: |
Water Quality Assessment Data for the 2018 solicitation cycle submitted through CEDEN for SWAMP RWB1 Monitoring .
|
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
The established numeric criteria for alpha-endosulfan to protect aquatic life in freshwater as criterion continuous concentration (expressed as a 4-day average) is 0.056 ug/L (California Toxics Rule, 2000). |
Objective/Criterion Reference: |
Water Quality Standards 2000. Establishment of numeric criteria for priority toxic pollutants for the State of California: Rules and regulations. Federal Register Vol. 65, No. 97. Washington, D.C.: Environmental Protection Agency |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
The samples were collected at 1 monitoring site(s) (105SH9274) |
Temporal Representation: |
The samples were collected between the dates of 2013-04-29 and 2013-04-29 |
Environmental Conditions: |
|
QAPP Information: |
Quality Assurance Program Plan and Standard Operating Procedures for SWAMP program |
QAPP Information Reference(s): |
Quality Assurance Program Plans, Quality Assurance Project Plans, and Standard Operating Procedures for the SWAMP program |
|
Line of Evidence (LOE) for Decision ID 168775, alpha-Endosulfan (Endosulfan 1)
|
Region 1 |
Klamath River HU, Shasta River HA |
|
|
LOE ID: |
41522 |
|
Pollutant: |
alpha-Endosulfan (Endosulfan 1) |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Total |
|
Beneficial Use: |
Municipal & Domestic Supply |
|
Number of Samples: |
3 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP data for Klamath River HU, Shasta River HA to determine beneficial use support and results are as follows: 0 of 3 samples exceed the criterion for Endosulfan I. |
Data Reference: |
RWB1 Trend Maintenance Periods FYs 2007 2008 |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
Water Quality Control Plan, North Coast Region (NCRWQCB 2011): All waters shall be maintained free of toxic substances in concentrations that are toxic to, or that produce detrimental physiological responses in human, plant, animal, or aquatic life. The established numeric criteria for alpha-endosulfan to protect of human health from the consumption of water and organisms is 110 ug/L (California Toxics Rule, 2000). |
Objective/Criterion Reference: |
Code of Federal Regulations 40 part 131.38 Establishment of numeric criteria for priority toxic pollutants for the State of California. 7/1/2011 Edition |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
Data for this line of evidence for Klamath River HU, Shasta River HA was collected at 1 monitoring site [ Shasta River at Hwy 263 - 105SHA263] |
Temporal Representation: |
Data was collected over the time period 11/15/2007-7/16/2008. |
Environmental Conditions: |
Staff is not aware of any special conditions that might affect interpretation of the data. |
QAPP Information: |
The SWAMP QAPP (2008) was followed. |
QAPP Information Reference(s): |
Surface Water Ambient Monitoring Program Quality Assurance Program Plan |
|
Line of Evidence (LOE) for Decision ID 168775, alpha-Endosulfan (Endosulfan 1)
|
Region 1 |
Klamath River HU, Shasta River HA |
|
|
LOE ID: |
109493 |
|
Pollutant: |
alpha-Endosulfan (Endosulfan 1) |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Total |
|
Beneficial Use: |
Municipal & Domestic Supply |
|
Number of Samples: |
1 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP RWB1 Monitoring data for Klamath River HU, Shasta River HA to determine beneficial use support and results are as follows: 0 of 1 samples exceeded the water quality standard for Endosulfan I. |
Data Reference: |
Water Quality Assessment Data for the 2018 solicitation cycle submitted through CEDEN for SWAMP RWB1 Monitoring .
|
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
The established numeric criteria for alpha-endosulfan to protect of human health from the consumption of water and organisms is 110 ug/L (California Toxics Rule, 2000). |
Objective/Criterion Reference: |
Water Quality Standards 2000. Establishment of numeric criteria for priority toxic pollutants for the State of California: Rules and regulations. Federal Register Vol. 65, No. 97. Washington, D.C.: Environmental Protection Agency |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
The samples were collected at 1 monitoring site(s) (105SH1452) |
Temporal Representation: |
The samples were collected between the dates of 2013-04-29 and 2013-04-29 |
Environmental Conditions: |
|
QAPP Information: |
Quality Assurance Program Plan and Standard Operating Procedures for SWAMP program |
QAPP Information Reference(s): |
Quality Assurance Program Plans, Quality Assurance Project Plans, and Standard Operating Procedures for the SWAMP program |
|
Line of Evidence (LOE) for Decision ID 168775, alpha-Endosulfan (Endosulfan 1)
|
Region 1 |
Klamath River HU, Shasta River HA |
|
|
LOE ID: |
41663 |
|
Pollutant: |
alpha-Endosulfan (Endosulfan 1) |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Total |
|
Beneficial Use: |
Commercial or recreational collection of fish, shellfish, or organisms |
|
Number of Samples: |
3 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP data for Klamath River HU, Shasta River HA to determine beneficial use support and results are as follows: 0 of 3 samples exceed the criterion for Endosulfan I. |
Data Reference: |
RWB1 Trend Maintenance Periods FYs 2007 2008 |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
Water Quality Control Plan, North Coast Region (NCRWQCB 2011): All waters shall be maintained free of toxic substances in concentrations that are toxic to, or that produce detrimental physiological responses in human, plant, animal, or aquatic life. The established numeric criteria for alpha-endosulfan to protection of human health from consumption of organisms only is 240 ug/L (California Toxics Rule, 2000). |
Objective/Criterion Reference: |
Code of Federal Regulations 40 part 131.38 Establishment of numeric criteria for priority toxic pollutants for the State of California. 7/1/2011 Edition |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
Data for this line of evidence for Klamath River HU, Shasta River HA was collected at 1 monitoring site [ Shasta River at Hwy 263 - 105SHA263] |
Temporal Representation: |
Data was collected over the time period 11/15/2007-7/16/2008. |
Environmental Conditions: |
Staff is not aware of any special conditions that might affect interpretation of the data. |
QAPP Information: |
The SWAMP QAPP (2008) was followed. |
QAPP Information Reference(s): |
Surface Water Ambient Monitoring Program Quality Assurance Program Plan |
|
Line of Evidence (LOE) for Decision ID 168775, alpha-Endosulfan (Endosulfan 1)
|
Region 1 |
Klamath River HU, Shasta River HA |
|
|
LOE ID: |
41538 |
|
Pollutant: |
alpha-Endosulfan (Endosulfan 1) |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Total |
|
Beneficial Use: |
Warm Freshwater Habitat |
|
Number of Samples: |
3 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP data for Klamath River HU, Shasta River HA to determine beneficial use support and results are as follows: 0 of 3 samples exceed the criterion for Endosulfan I. |
Data Reference: |
RWB1 Trend Maintenance Periods FYs 2007 2008 |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
Water Quality Control Plan, North Coast Region (NCRWQCB 2011): All waters shall be maintained free of toxic substances in concentrations that are toxic to, or that produce detrimental physiological responses in human, plant, animal, or aquatic life. The established numeric criteria for alpha-endosulfan to protect aquatic life in freshwater as criterion continuous concentration (expressed as a 4-day average) is 0.056 ug/L (California Toxics Rule, 2000). |
Objective/Criterion Reference: |
Code of Federal Regulations 40 part 131.38 Establishment of numeric criteria for priority toxic pollutants for the State of California. 7/1/2011 Edition |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
Data for this line of evidence for Klamath River HU, Shasta River HA was collected at 1 monitoring site [ Shasta River near Edgewood - 105SHAEDG] |
Temporal Representation: |
Data was collected over the time period 11/15/2007-7/16/2008. |
Environmental Conditions: |
Staff is not aware of any special conditions that might affect interpretation of the data. |
QAPP Information: |
The SWAMP QAPP (2008) was followed. |
QAPP Information Reference(s): |
Surface Water Ambient Monitoring Program Quality Assurance Program Plan |
|
Line of Evidence (LOE) for Decision ID 168775, alpha-Endosulfan (Endosulfan 1)
|
Region 1 |
Klamath River HU, Shasta River HA |
|
|
LOE ID: |
41521 |
|
Pollutant: |
alpha-Endosulfan (Endosulfan 1) |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Total |
|
Beneficial Use: |
Municipal & Domestic Supply |
|
Number of Samples: |
3 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP data for Klamath River HU, Shasta River HA to determine beneficial use support and results are as follows: 0 of 3 samples exceed the criterion for Endosulfan I. |
Data Reference: |
RWB1 Trend Maintenance Periods FYs 2007 2008 |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
Water Quality Control Plan, North Coast Region (NCRWQCB 2011): All waters shall be maintained free of toxic substances in concentrations that are toxic to, or that produce detrimental physiological responses in human, plant, animal, or aquatic life. The established numeric criteria for alpha-endosulfan to protect of human health from the consumption of water and organisms is 110 ug/L (California Toxics Rule, 2000). |
Objective/Criterion Reference: |
Code of Federal Regulations 40 part 131.38 Establishment of numeric criteria for priority toxic pollutants for the State of California. 7/1/2011 Edition |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
Data for this line of evidence for Klamath River HU, Shasta River HA was collected at 1 monitoring site [ Shasta River near Edgewood - 105SHAEDG] |
Temporal Representation: |
Data was collected over the time period 11/15/2007-7/16/2008. |
Environmental Conditions: |
Staff is not aware of any special conditions that might affect interpretation of the data. |
QAPP Information: |
The SWAMP QAPP (2008) was followed. |
QAPP Information Reference(s): |
Surface Water Ambient Monitoring Program Quality Assurance Program Plan |
|
Line of Evidence (LOE) for Decision ID 168775, alpha-Endosulfan (Endosulfan 1)
|
Region 1 |
Klamath River HU, Shasta River HA |
|
|
LOE ID: |
109496 |
|
Pollutant: |
alpha-Endosulfan (Endosulfan 1) |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Total |
|
Beneficial Use: |
Municipal & Domestic Supply |
|
Number of Samples: |
1 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP RWB1 Monitoring data for Klamath River HU, Shasta River HA to determine beneficial use support and results are as follows: 0 of 1 samples exceeded the water quality standard for Endosulfan I. |
Data Reference: |
Water Quality Assessment Data for the 2018 solicitation cycle submitted through CEDEN for SWAMP RWB1 Monitoring .
|
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
The established numeric criteria for alpha-endosulfan to protect of human health from the consumption of water and organisms is 110 ug/L (California Toxics Rule, 2000). |
Objective/Criterion Reference: |
Water Quality Standards 2000. Establishment of numeric criteria for priority toxic pollutants for the State of California: Rules and regulations. Federal Register Vol. 65, No. 97. Washington, D.C.: Environmental Protection Agency |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
The samples were collected at 1 monitoring site(s) (105SH9274) |
Temporal Representation: |
The samples were collected between the dates of 2013-04-29 and 2013-04-29 |
Environmental Conditions: |
|
QAPP Information: |
Quality Assurance Program Plan and Standard Operating Procedures for SWAMP program |
QAPP Information Reference(s): |
Quality Assurance Program Plans, Quality Assurance Project Plans, and Standard Operating Procedures for the SWAMP program |
|
Line of Evidence (LOE) for Decision ID 168775, alpha-Endosulfan (Endosulfan 1)
|
Region 1 |
Klamath River HU, Shasta River HA |
|
|
LOE ID: |
41731 |
|
Pollutant: |
alpha-Endosulfan (Endosulfan 1) |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Total |
|
Beneficial Use: |
Cold Freshwater Habitat |
|
Number of Samples: |
3 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP data for Klamath River HU, Shasta River HA to determine beneficial use support and results are as follows: 0 of 3 samples exceed the criterion for Endosulfan I. |
Data Reference: |
RWB1 Trend Maintenance Periods FYs 2007 2008 |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
Water Quality Control Plan, North Coast Region (NCRWQCB 2011): All waters shall be maintained free of toxic substances in concentrations that are toxic to, or that produce detrimental physiological responses in human, plant, animal, or aquatic life. The established numeric criteria for alpha-endosulfan to protect aquatic life in freshwater as criterion continuous concentration (expressed as a 4-day average) is 0.056 ug/L (California Toxics Rule, 2000). |
Objective/Criterion Reference: |
Code of Federal Regulations 40 part 131.38 Establishment of numeric criteria for priority toxic pollutants for the State of California. 7/1/2011 Edition |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
Data for this line of evidence for Klamath River HU, Shasta River HA was collected at 1 monitoring site [ Shasta River at Hwy 263 - 105SHA263] |
Temporal Representation: |
Data was collected over the time period 11/15/2007-7/16/2008. |
Environmental Conditions: |
Staff is not aware of any special conditions that might affect interpretation of the data. |
QAPP Information: |
The SWAMP QAPP (2008) was followed. |
QAPP Information Reference(s): |
Surface Water Ambient Monitoring Program Quality Assurance Program Plan |
|
Line of Evidence (LOE) for Decision ID 168775, alpha-Endosulfan (Endosulfan 1)
|
Region 1 |
Klamath River HU, Shasta River HA |
|
|
LOE ID: |
109492 |
|
Pollutant: |
alpha-Endosulfan (Endosulfan 1) |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Total |
|
Beneficial Use: |
Cold Freshwater Habitat |
|
Number of Samples: |
1 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP RWB1 Monitoring data for Klamath River HU, Shasta River HA to determine beneficial use support and results are as follows: 0 of 1 samples exceeded the water quality standard for Endosulfan I. |
Data Reference: |
Water Quality Assessment Data for the 2018 solicitation cycle submitted through CEDEN for SWAMP RWB1 Monitoring .
|
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
The established numeric criteria for alpha-endosulfan to protect aquatic life in freshwater as criterion continuous concentration (expressed as a 4-day average) is 0.056 ug/L (California Toxics Rule, 2000). |
Objective/Criterion Reference: |
Water Quality Standards 2000. Establishment of numeric criteria for priority toxic pollutants for the State of California: Rules and regulations. Federal Register Vol. 65, No. 97. Washington, D.C.: Environmental Protection Agency |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
The samples were collected at 1 monitoring site(s) (105SH1452) |
Temporal Representation: |
The samples were collected between the dates of 2013-04-29 and 2013-04-29 |
Environmental Conditions: |
|
QAPP Information: |
Quality Assurance Program Plan and Standard Operating Procedures for SWAMP program |
QAPP Information Reference(s): |
Quality Assurance Program Plans, Quality Assurance Project Plans, and Standard Operating Procedures for the SWAMP program |
|
Line of Evidence (LOE) for Decision ID 168775, alpha-Endosulfan (Endosulfan 1)
|
Region 1 |
Klamath River HU, Shasta River HA |
|
|
LOE ID: |
41506 |
|
Pollutant: |
alpha-Endosulfan (Endosulfan 1) |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Total |
|
Beneficial Use: |
Commercial or recreational collection of fish, shellfish, or organisms |
|
Number of Samples: |
3 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP data for Klamath River HU, Shasta River HA to determine beneficial use support and results are as follows: 0 of 3 samples exceed the criterion for Endosulfan I. |
Data Reference: |
RWB1 Trend Maintenance Periods FYs 2007 2008 |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
Water Quality Control Plan, North Coast Region (NCRWQCB 2011): All waters shall be maintained free of toxic substances in concentrations that are toxic to, or that produce detrimental physiological responses in human, plant, animal, or aquatic life. The established numeric criteria for alpha-endosulfan to protection of human health from consumption of organisms only is 240 ug/L (California Toxics Rule, 2000). |
Objective/Criterion Reference: |
Code of Federal Regulations 40 part 131.38 Establishment of numeric criteria for priority toxic pollutants for the State of California. 7/1/2011 Edition |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
Data for this line of evidence for Klamath River HU, Shasta River HA was collected at 1 monitoring site [ Shasta River near Edgewood - 105SHAEDG] |
Temporal Representation: |
Data was collected over the time period 11/15/2007-7/16/2008. |
Environmental Conditions: |
Staff is not aware of any special conditions that might affect interpretation of the data. |
QAPP Information: |
The SWAMP QAPP (2008) was followed. |
QAPP Information Reference(s): |
Surface Water Ambient Monitoring Program Quality Assurance Program Plan |
|
Line of Evidence (LOE) for Decision ID 168775, alpha-Endosulfan (Endosulfan 1)
|
Region 1 |
Klamath River HU, Shasta River HA |
|
|
LOE ID: |
41730 |
|
Pollutant: |
alpha-Endosulfan (Endosulfan 1) |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Total |
|
Beneficial Use: |
Cold Freshwater Habitat |
|
Number of Samples: |
3 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP data for Klamath River HU, Shasta River HA to determine beneficial use support and results are as follows: 0 of 3 samples exceed the criterion for Endosulfan I. |
Data Reference: |
RWB1 Trend Maintenance Periods FYs 2007 2008 |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
Water Quality Control Plan, North Coast Region (NCRWQCB 2011): All waters shall be maintained free of toxic substances in concentrations that are toxic to, or that produce detrimental physiological responses in human, plant, animal, or aquatic life. The established numeric criteria for alpha-endosulfan to protect aquatic life in freshwater as criterion continuous concentration (expressed as a 4-day average) is 0.056 ug/L (California Toxics Rule, 2000). |
Objective/Criterion Reference: |
Code of Federal Regulations 40 part 131.38 Establishment of numeric criteria for priority toxic pollutants for the State of California. 7/1/2011 Edition |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
Data for this line of evidence for Klamath River HU, Shasta River HA was collected at 1 monitoring site [ Shasta River near Edgewood - 105SHAEDG] |
Temporal Representation: |
Data was collected over the time period 11/15/2007-7/16/2008. |
Environmental Conditions: |
Staff is not aware of any special conditions that might affect interpretation of the data. |
QAPP Information: |
The SWAMP QAPP (2008) was followed. |
QAPP Information Reference(s): |
Surface Water Ambient Monitoring Program Quality Assurance Program Plan |
|
Line of Evidence (LOE) for Decision ID 168775, alpha-Endosulfan (Endosulfan 1)
|
Region 1 |
Klamath River HU, Shasta River HA |
|
|
LOE ID: |
109494 |
|
Pollutant: |
alpha-Endosulfan (Endosulfan 1) |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Total |
|
Beneficial Use: |
Commercial or recreational collection of fish, shellfish, or organisms |
|
Number of Samples: |
1 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP RWB1 Monitoring data for Klamath River HU, Shasta River HA to determine beneficial use support and results are as follows: 0 of 1 samples exceeded the water quality standard for Endosulfan I. |
Data Reference: |
Water Quality Assessment Data for the 2018 solicitation cycle submitted through CEDEN for SWAMP RWB1 Monitoring .
|
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
The established numeric criteria for alpha-endosulfan to protection of human health from consumption of organisms only is 240 ug/L (California Toxics Rule, 2000). |
Objective/Criterion Reference: |
Water Quality Standards 2000. Establishment of numeric criteria for priority toxic pollutants for the State of California: Rules and regulations. Federal Register Vol. 65, No. 97. Washington, D.C.: Environmental Protection Agency |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
The samples were collected at 1 monitoring site(s) (105SH9274) |
Temporal Representation: |
The samples were collected between the dates of 2013-04-29 and 2013-04-29 |
Environmental Conditions: |
|
QAPP Information: |
Quality Assurance Program Plan and Standard Operating Procedures for SWAMP program |
QAPP Information Reference(s): |
Quality Assurance Program Plans, Quality Assurance Project Plans, and Standard Operating Procedures for the SWAMP program |
|
Line of Evidence (LOE) for Decision ID 168781, beta-Endosulfan (Endosulfan 2)
|
Region 1 |
Klamath River HU, Shasta River HA |
|
|
LOE ID: |
109498 |
|
Pollutant: |
beta-Endosulfan (Endosulfan 2) |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Total |
|
Beneficial Use: |
Commercial or recreational collection of fish, shellfish, or organisms |
|
Number of Samples: |
1 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP RWB1 Monitoring data for Klamath River HU, Shasta River HA to determine beneficial use support and results are as follows: 0 of 1 samples exceeded the water quality standard for Endosulfan II. |
Data Reference: |
Water Quality Assessment Data for the 2018 solicitation cycle submitted through CEDEN for SWAMP RWB1 Monitoring .
|
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
The established numeric criteria for beta-endosulfan to protection of human health from consumption of organisms only is 240 ug/L (California Toxics Rule, 2000). |
Objective/Criterion Reference: |
Water Quality Standards 2000. Establishment of numeric criteria for priority toxic pollutants for the State of California: Rules and regulations. Federal Register Vol. 65, No. 97. Washington, D.C.: Environmental Protection Agency |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
The samples were collected at 1 monitoring site(s) (105SH1452) |
Temporal Representation: |
The samples were collected between the dates of 2013-04-29 and 2013-04-29 |
Environmental Conditions: |
|
QAPP Information: |
Quality Assurance Program Plan and Standard Operating Procedures for SWAMP program |
QAPP Information Reference(s): |
Quality Assurance Program Plans, Quality Assurance Project Plans, and Standard Operating Procedures for the SWAMP program |
|
Line of Evidence (LOE) for Decision ID 168781, beta-Endosulfan (Endosulfan 2)
|
Region 1 |
Klamath River HU, Shasta River HA |
|
|
LOE ID: |
41608 |
|
Pollutant: |
beta-Endosulfan (Endosulfan 2) |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Total |
|
Beneficial Use: |
Municipal & Domestic Supply |
|
Number of Samples: |
3 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP data for Klamath River HU, Shasta River HA to determine beneficial use support and results are as follows: 0 of 3 samples exceed the criterion for Endosulfan II. |
Data Reference: |
RWB1 Trend Maintenance Periods FYs 2007 2008 |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
Water Quality Control Plan, North Coast Region (NCRWQCB 2011): All waters shall be maintained free of toxic substances in concentrations that are toxic to, or that produce detrimental physiological responses in human, plant, animal, or aquatic life. The established numeric criteria for beta-endosulfan to protect of human health from the consumption of water and organisms is 110 ug/L (California Toxics Rule, 2000). |
Objective/Criterion Reference: |
Code of Federal Regulations 40 part 131.38 Establishment of numeric criteria for priority toxic pollutants for the State of California. 7/1/2011 Edition |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
Data for this line of evidence for Klamath River HU, Shasta River HA was collected at 1 monitoring site [ Shasta River near Edgewood - 105SHAEDG] |
Temporal Representation: |
Data was collected over the time period 11/15/2007-7/16/2008. |
Environmental Conditions: |
Staff is not aware of any special conditions that might affect interpretation of the data. |
QAPP Information: |
The SWAMP QAPP (2008) was followed. |
QAPP Information Reference(s): |
Surface Water Ambient Monitoring Program Quality Assurance Program Plan |
|
Line of Evidence (LOE) for Decision ID 168781, beta-Endosulfan (Endosulfan 2)
|
Region 1 |
Klamath River HU, Shasta River HA |
|
|
LOE ID: |
41602 |
|
Pollutant: |
beta-Endosulfan (Endosulfan 2) |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Total |
|
Beneficial Use: |
Cold Freshwater Habitat |
|
Number of Samples: |
3 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP data for Klamath River HU, Shasta River HA to determine beneficial use support and results are as follows: 0 of 3 samples exceed the criterion for Endosulfan II. |
Data Reference: |
RWB1 Trend Maintenance Periods FYs 2007 2008 |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
Water Quality Control Plan, North Coast Region (NCRWQCB 2011): All waters shall be maintained free of toxic substances in concentrations that are toxic to, or that produce detrimental physiological responses in human, plant, animal, or aquatic life. The established numeric criteria for beta-endosulfan to protect aquatic life in freshwater as criterion continuous concentration (expressed as a 4-day average) is 0.056 ug/L (California Toxics Rule, 2000). |
Objective/Criterion Reference: |
Code of Federal Regulations 40 part 131.38 Establishment of numeric criteria for priority toxic pollutants for the State of California. 7/1/2011 Edition |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
Data for this line of evidence for Klamath River HU, Shasta River HA was collected at 1 monitoring site [ Shasta River near Edgewood - 105SHAEDG] |
Temporal Representation: |
Data was collected over the time period 11/15/2007-7/16/2008. |
Environmental Conditions: |
Staff is not aware of any special conditions that might affect interpretation of the data. |
QAPP Information: |
The SWAMP QAPP (2008) was followed. |
QAPP Information Reference(s): |
Surface Water Ambient Monitoring Program Quality Assurance Program Plan |
|
Line of Evidence (LOE) for Decision ID 168781, beta-Endosulfan (Endosulfan 2)
|
Region 1 |
Klamath River HU, Shasta River HA |
|
|
LOE ID: |
41603 |
|
Pollutant: |
beta-Endosulfan (Endosulfan 2) |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Total |
|
Beneficial Use: |
Cold Freshwater Habitat |
|
Number of Samples: |
3 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP data for Klamath River HU, Shasta River HA to determine beneficial use support and results are as follows: 0 of 3 samples exceed the criterion for Endosulfan II. |
Data Reference: |
RWB1 Trend Maintenance Periods FYs 2007 2008 |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
Water Quality Control Plan, North Coast Region (NCRWQCB 2011): All waters shall be maintained free of toxic substances in concentrations that are toxic to, or that produce detrimental physiological responses in human, plant, animal, or aquatic life. The established numeric criteria for beta-endosulfan to protect aquatic life in freshwater as criterion continuous concentration (expressed as a 4-day average) is 0.056 ug/L (California Toxics Rule, 2000). |
Objective/Criterion Reference: |
Code of Federal Regulations 40 part 131.38 Establishment of numeric criteria for priority toxic pollutants for the State of California. 7/1/2011 Edition |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
Data for this line of evidence for Klamath River HU, Shasta River HA was collected at 1 monitoring site [ Shasta River at Hwy 263 - 105SHA263] |
Temporal Representation: |
Data was collected over the time period 11/15/2007-7/16/2008. |
Environmental Conditions: |
Staff is not aware of any special conditions that might affect interpretation of the data. |
QAPP Information: |
The SWAMP QAPP (2008) was followed. |
QAPP Information Reference(s): |
Surface Water Ambient Monitoring Program Quality Assurance Program Plan |
|
Line of Evidence (LOE) for Decision ID 168781, beta-Endosulfan (Endosulfan 2)
|
Region 1 |
Klamath River HU, Shasta River HA |
|
|
LOE ID: |
109500 |
|
Pollutant: |
beta-Endosulfan (Endosulfan 2) |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Total |
|
Beneficial Use: |
Municipal & Domestic Supply |
|
Number of Samples: |
1 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP RWB1 Monitoring data for Klamath River HU, Shasta River HA to determine beneficial use support and results are as follows: 0 of 1 samples exceeded the water quality standard for Endosulfan II. |
Data Reference: |
Water Quality Assessment Data for the 2018 solicitation cycle submitted through CEDEN for SWAMP RWB1 Monitoring .
|
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
The established numeric criteria for beta-endosulfan to protect of human health from the consumption of water and organisms is 110 ug/L (California Toxics Rule, 2000). |
Objective/Criterion Reference: |
Water Quality Standards 2000. Establishment of numeric criteria for priority toxic pollutants for the State of California: Rules and regulations. Federal Register Vol. 65, No. 97. Washington, D.C.: Environmental Protection Agency |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
The samples were collected at 1 monitoring site(s) (105SH1452) |
Temporal Representation: |
The samples were collected between the dates of 2013-04-29 and 2013-04-29 |
Environmental Conditions: |
|
QAPP Information: |
Quality Assurance Program Plan and Standard Operating Procedures for SWAMP program |
QAPP Information Reference(s): |
Quality Assurance Program Plans, Quality Assurance Project Plans, and Standard Operating Procedures for the SWAMP program |
|
Line of Evidence (LOE) for Decision ID 168781, beta-Endosulfan (Endosulfan 2)
|
Region 1 |
Klamath River HU, Shasta River HA |
|
|
LOE ID: |
41570 |
|
Pollutant: |
beta-Endosulfan (Endosulfan 2) |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Total |
|
Beneficial Use: |
Warm Freshwater Habitat |
|
Number of Samples: |
3 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP data for Klamath River HU, Shasta River HA to determine beneficial use support and results are as follows: 0 of 3 samples exceed the criterion for Endosulfan II. |
Data Reference: |
RWB1 Trend Maintenance Periods FYs 2007 2008 |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
Water Quality Control Plan, North Coast Region (NCRWQCB 2011): All waters shall be maintained free of toxic substances in concentrations that are toxic to, or that produce detrimental physiological responses in human, plant, animal, or aquatic life. The established numeric criteria for beta-endosulfan to protect aquatic life in freshwater as criterion continuous concentration (expressed as a 4-day average) is 0.056 ug/L (California Toxics Rule, 2000). |
Objective/Criterion Reference: |
Code of Federal Regulations 40 part 131.38 Establishment of numeric criteria for priority toxic pollutants for the State of California. 7/1/2011 Edition |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
Data for this line of evidence for Klamath River HU, Shasta River HA was collected at 1 monitoring site [ Shasta River near Edgewood - 105SHAEDG] |
Temporal Representation: |
Data was collected over the time period 11/15/2007-7/16/2008. |
Environmental Conditions: |
Staff is not aware of any special conditions that might affect interpretation of the data. |
QAPP Information: |
The SWAMP QAPP (2008) was followed. |
QAPP Information Reference(s): |
Surface Water Ambient Monitoring Program Quality Assurance Program Plan |
|
Line of Evidence (LOE) for Decision ID 168781, beta-Endosulfan (Endosulfan 2)
|
Region 1 |
Klamath River HU, Shasta River HA |
|
|
LOE ID: |
41571 |
|
Pollutant: |
beta-Endosulfan (Endosulfan 2) |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Total |
|
Beneficial Use: |
Warm Freshwater Habitat |
|
Number of Samples: |
3 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP data for Klamath River HU, Shasta River HA to determine beneficial use support and results are as follows: 0 of 3 samples exceed the criterion for Endosulfan II. |
Data Reference: |
RWB1 Trend Maintenance Periods FYs 2007 2008 |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
Water Quality Control Plan, North Coast Region (NCRWQCB 2011): All waters shall be maintained free of toxic substances in concentrations that are toxic to, or that produce detrimental physiological responses in human, plant, animal, or aquatic life. The established numeric criteria for beta-endosulfan to protect aquatic life in freshwater as criterion continuous concentration (expressed as a 4-day average) is 0.056 ug/L (California Toxics Rule, 2000). |
Objective/Criterion Reference: |
Code of Federal Regulations 40 part 131.38 Establishment of numeric criteria for priority toxic pollutants for the State of California. 7/1/2011 Edition |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
Data for this line of evidence for Klamath River HU, Shasta River HA was collected at 1 monitoring site [ Shasta River at Hwy 263 - 105SHA263] |
Temporal Representation: |
Data was collected over the time period 11/15/2007-7/16/2008. |
Environmental Conditions: |
Staff is not aware of any special conditions that might affect interpretation of the data. |
QAPP Information: |
The SWAMP QAPP (2008) was followed. |
QAPP Information Reference(s): |
Surface Water Ambient Monitoring Program Quality Assurance Program Plan |
|
Line of Evidence (LOE) for Decision ID 168781, beta-Endosulfan (Endosulfan 2)
|
Region 1 |
Klamath River HU, Shasta River HA |
|
|
LOE ID: |
41553 |
|
Pollutant: |
beta-Endosulfan (Endosulfan 2) |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Total |
|
Beneficial Use: |
Commercial or recreational collection of fish, shellfish, or organisms |
|
Number of Samples: |
3 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP data for Klamath River HU, Shasta River HA to determine beneficial use support and results are as follows: 0 of 3 samples exceed the criterion for Endosulfan II. |
Data Reference: |
RWB1 Trend Maintenance Periods FYs 2007 2008 |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
Water Quality Control Plan, North Coast Region (NCRWQCB 2011): All waters shall be maintained free of toxic substances in concentrations that are toxic to, or that produce detrimental physiological responses in human, plant, animal, or aquatic life. The established numeric criteria for beta-endosulfan to protection of human health from consumption of organisms only is 240 ug/L (California Toxics Rule, 2000). |
Objective/Criterion Reference: |
Code of Federal Regulations 40 part 131.38 Establishment of numeric criteria for priority toxic pollutants for the State of California. 7/1/2011 Edition |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
Data for this line of evidence for Klamath River HU, Shasta River HA was collected at 1 monitoring site [ Shasta River near Edgewood - 105SHAEDG] |
Temporal Representation: |
Data was collected over the time period 11/15/2007-7/16/2008. |
Environmental Conditions: |
Staff is not aware of any special conditions that might affect interpretation of the data. |
QAPP Information: |
The SWAMP QAPP (2008) was followed. |
QAPP Information Reference(s): |
Surface Water Ambient Monitoring Program Quality Assurance Program Plan |
|
Line of Evidence (LOE) for Decision ID 168781, beta-Endosulfan (Endosulfan 2)
|
Region 1 |
Klamath River HU, Shasta River HA |
|
|
LOE ID: |
41554 |
|
Pollutant: |
beta-Endosulfan (Endosulfan 2) |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Total |
|
Beneficial Use: |
Commercial or recreational collection of fish, shellfish, or organisms |
|
Number of Samples: |
3 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP data for Klamath River HU, Shasta River HA to determine beneficial use support and results are as follows: 0 of 3 samples exceed the criterion for Endosulfan II. |
Data Reference: |
RWB1 Trend Maintenance Periods FYs 2007 2008 |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
Water Quality Control Plan, North Coast Region (NCRWQCB 2011): All waters shall be maintained free of toxic substances in concentrations that are toxic to, or that produce detrimental physiological responses in human, plant, animal, or aquatic life. The established numeric criteria for beta-endosulfan to protection of human health from consumption of organisms only is 240 ug/L (California Toxics Rule, 2000). |
Objective/Criterion Reference: |
Code of Federal Regulations 40 part 131.38 Establishment of numeric criteria for priority toxic pollutants for the State of California. 7/1/2011 Edition |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
Data for this line of evidence for Klamath River HU, Shasta River HA was collected at 1 monitoring site [ Shasta River at Hwy 263 - 105SHA263] |
Temporal Representation: |
Data was collected over the time period 11/15/2007-7/16/2008. |
Environmental Conditions: |
Staff is not aware of any special conditions that might affect interpretation of the data. |
QAPP Information: |
The SWAMP QAPP (2008) was followed. |
QAPP Information Reference(s): |
Surface Water Ambient Monitoring Program Quality Assurance Program Plan |
|
Line of Evidence (LOE) for Decision ID 168781, beta-Endosulfan (Endosulfan 2)
|
Region 1 |
Klamath River HU, Shasta River HA |
|
|
LOE ID: |
109502 |
|
Pollutant: |
beta-Endosulfan (Endosulfan 2) |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Total |
|
Beneficial Use: |
Cold Freshwater Habitat |
|
Number of Samples: |
1 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP RWB1 Monitoring data for Klamath River HU, Shasta River HA to determine beneficial use support and results are as follows: 0 of 1 samples exceeded the water quality standard for Endosulfan II. |
Data Reference: |
Water Quality Assessment Data for the 2018 solicitation cycle submitted through CEDEN for SWAMP RWB1 Monitoring .
|
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
The established numeric criteria for beta-endosulfan to protect aquatic life in freshwater as criterion continuous concentration (expressed as a 4-day average) is 0.056 ug/L (California Toxics Rule, 2000). |
Objective/Criterion Reference: |
Water Quality Standards 2000. Establishment of numeric criteria for priority toxic pollutants for the State of California: Rules and regulations. Federal Register Vol. 65, No. 97. Washington, D.C.: Environmental Protection Agency |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
The samples were collected at 1 monitoring site(s) (105SH9274) |
Temporal Representation: |
The samples were collected between the dates of 2013-04-29 and 2013-04-29 |
Environmental Conditions: |
|
QAPP Information: |
Quality Assurance Program Plan and Standard Operating Procedures for SWAMP program |
QAPP Information Reference(s): |
Quality Assurance Program Plans, Quality Assurance Project Plans, and Standard Operating Procedures for the SWAMP program |
|
Line of Evidence (LOE) for Decision ID 168781, beta-Endosulfan (Endosulfan 2)
|
Region 1 |
Klamath River HU, Shasta River HA |
|
|
LOE ID: |
109503 |
|
Pollutant: |
beta-Endosulfan (Endosulfan 2) |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Total |
|
Beneficial Use: |
Municipal & Domestic Supply |
|
Number of Samples: |
1 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP RWB1 Monitoring data for Klamath River HU, Shasta River HA to determine beneficial use support and results are as follows: 0 of 1 samples exceeded the water quality standard for Endosulfan II. |
Data Reference: |
Water Quality Assessment Data for the 2018 solicitation cycle submitted through CEDEN for SWAMP RWB1 Monitoring .
|
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
The established numeric criteria for beta-endosulfan to protect of human health from the consumption of water and organisms is 110 ug/L (California Toxics Rule, 2000). |
Objective/Criterion Reference: |
Water Quality Standards 2000. Establishment of numeric criteria for priority toxic pollutants for the State of California: Rules and regulations. Federal Register Vol. 65, No. 97. Washington, D.C.: Environmental Protection Agency |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
The samples were collected at 1 monitoring site(s) (105SH9274) |
Temporal Representation: |
The samples were collected between the dates of 2013-04-29 and 2013-04-29 |
Environmental Conditions: |
|
QAPP Information: |
Quality Assurance Program Plan and Standard Operating Procedures for SWAMP program |
QAPP Information Reference(s): |
Quality Assurance Program Plans, Quality Assurance Project Plans, and Standard Operating Procedures for the SWAMP program |
|
Line of Evidence (LOE) for Decision ID 168781, beta-Endosulfan (Endosulfan 2)
|
Region 1 |
Klamath River HU, Shasta River HA |
|
|
LOE ID: |
109499 |
|
Pollutant: |
beta-Endosulfan (Endosulfan 2) |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Total |
|
Beneficial Use: |
Cold Freshwater Habitat |
|
Number of Samples: |
1 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP RWB1 Monitoring data for Klamath River HU, Shasta River HA to determine beneficial use support and results are as follows: 0 of 1 samples exceeded the water quality standard for Endosulfan II. |
Data Reference: |
Water Quality Assessment Data for the 2018 solicitation cycle submitted through CEDEN for SWAMP RWB1 Monitoring .
|
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
The established numeric criteria for beta-endosulfan to protect aquatic life in freshwater as criterion continuous concentration (expressed as a 4-day average) is 0.056 ug/L (California Toxics Rule, 2000). |
Objective/Criterion Reference: |
Water Quality Standards 2000. Establishment of numeric criteria for priority toxic pollutants for the State of California: Rules and regulations. Federal Register Vol. 65, No. 97. Washington, D.C.: Environmental Protection Agency |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
The samples were collected at 1 monitoring site(s) (105SH1452) |
Temporal Representation: |
The samples were collected between the dates of 2013-04-29 and 2013-04-29 |
Environmental Conditions: |
|
QAPP Information: |
Quality Assurance Program Plan and Standard Operating Procedures for SWAMP program |
QAPP Information Reference(s): |
Quality Assurance Program Plans, Quality Assurance Project Plans, and Standard Operating Procedures for the SWAMP program |
|
Line of Evidence (LOE) for Decision ID 168781, beta-Endosulfan (Endosulfan 2)
|
Region 1 |
Klamath River HU, Shasta River HA |
|
|
LOE ID: |
109501 |
|
Pollutant: |
beta-Endosulfan (Endosulfan 2) |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Total |
|
Beneficial Use: |
Commercial or recreational collection of fish, shellfish, or organisms |
|
Number of Samples: |
1 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP RWB1 Monitoring data for Klamath River HU, Shasta River HA to determine beneficial use support and results are as follows: 0 of 1 samples exceeded the water quality standard for Endosulfan II. |
Data Reference: |
Water Quality Assessment Data for the 2018 solicitation cycle submitted through CEDEN for SWAMP RWB1 Monitoring .
|
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
The established numeric criteria for beta-endosulfan to protection of human health from consumption of organisms only is 240 ug/L (California Toxics Rule, 2000). |
Objective/Criterion Reference: |
Water Quality Standards 2000. Establishment of numeric criteria for priority toxic pollutants for the State of California: Rules and regulations. Federal Register Vol. 65, No. 97. Washington, D.C.: Environmental Protection Agency |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
The samples were collected at 1 monitoring site(s) (105SH9274) |
Temporal Representation: |
The samples were collected between the dates of 2013-04-29 and 2013-04-29 |
Environmental Conditions: |
|
QAPP Information: |
Quality Assurance Program Plan and Standard Operating Procedures for SWAMP program |
QAPP Information Reference(s): |
Quality Assurance Program Plans, Quality Assurance Project Plans, and Standard Operating Procedures for the SWAMP program |
|
Line of Evidence (LOE) for Decision ID 168781, beta-Endosulfan (Endosulfan 2)
|
Region 1 |
Klamath River HU, Shasta River HA |
|
|
LOE ID: |
41609 |
|
Pollutant: |
beta-Endosulfan (Endosulfan 2) |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Total |
|
Beneficial Use: |
Municipal & Domestic Supply |
|
Number of Samples: |
3 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP data for Klamath River HU, Shasta River HA to determine beneficial use support and results are as follows: 0 of 3 samples exceed the criterion for Endosulfan II. |
Data Reference: |
RWB1 Trend Maintenance Periods FYs 2007 2008 |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
Water Quality Control Plan, North Coast Region (NCRWQCB 2011): All waters shall be maintained free of toxic substances in concentrations that are toxic to, or that produce detrimental physiological responses in human, plant, animal, or aquatic life. The established numeric criteria for beta-endosulfan to protect of human health from the consumption of water and organisms is 110 ug/L (California Toxics Rule, 2000). |
Objective/Criterion Reference: |
Code of Federal Regulations 40 part 131.38 Establishment of numeric criteria for priority toxic pollutants for the State of California. 7/1/2011 Edition |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
Data for this line of evidence for Klamath River HU, Shasta River HA was collected at 1 monitoring site [ Shasta River at Hwy 263 - 105SHA263] |
Temporal Representation: |
Data was collected over the time period 11/15/2007-7/16/2008. |
Environmental Conditions: |
Staff is not aware of any special conditions that might affect interpretation of the data. |
QAPP Information: |
The SWAMP QAPP (2008) was followed. |
QAPP Information Reference(s): |
Surface Water Ambient Monitoring Program Quality Assurance Program Plan |
|
Line of Evidence (LOE) for Decision ID 169301, Benthic Community Effects
|
Region 1 |
Klamath River HU, Shasta River HA |
|
|
LOE ID: |
96309 |
|
Pollutant: |
Benthic-Macroinvertebrate Bioassessments |
LOE Subgroup: |
Population/Community Degradation |
Matrix: |
Water |
Fraction: |
None |
|
Beneficial Use: |
Cold Freshwater Habitat |
Aquatic Life Use: |
Cold Freshwater Habitat |
|
Number of Samples: |
1 |
Number of Exceedances: |
1 |
|
Data and Information Type: |
Benthic macroinvertebrate surveys |
Data Used to Assess Water Quality: |
The site had a CSCI score(s) of 0.660446062. Therefore, this site is exceeding the water quality objective for the aquatic life beneficial use. |
Data Reference: |
Water Quality Assessment Data for the 2018 solicitation cycle submitted through CEDEN for SWAMP Perennial Stream Surveys .
|
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
From the Water Quality Control Plan, North Coast Region: All waters shall be maintained free of toxic substances in concentrations that are toxic to, or that produce detrimental physiological responses in human, plant, animal, or aquatic life. |
Objective/Criterion Reference: |
Water Quality Control Plan (Basin Plan) for the North Coast Region |
|
Evaluation Guideline: |
The California Stream Condition Index (CSCI) is a biological scoring tool that helps aquatic resource managers translate complex data about benthic macroinvertebrates found living in a stream into an overall measure of stream health. The CSCI score is calculated by comparing the expected condition with actual (observed) results (Rhen, A.C. et al., 2015). CSCI scores range from 0 (highly degraded) to greater than 1 (equivalent to reference). CSCI scoring of biological condition are as follows (per the scientific paper supporting the development of the CSCI scoring tool): greater than or equal to 0.92 = likely intact condition, 0.91 to 0.80 = possibly altered condition, 0.79 to 0.63 = likely altered condition, less than or equal to 0.62 = very likely altered condition. Sites with scores below 0.79 are considered to have exceeded the water quality objective for the aquatic life beneficial use. |
Guideline Reference: |
Bioassessment in complex environments: designing an
index for consistent meaning in different settings
|
|
Spatial Representation: |
These samples were collected at the following station: 105PS0231 |
Temporal Representation: |
These samples were collected on: 8/29/2013 |
Environmental Conditions: |
|
QAPP Information: |
Data collected following SWAMP QA protocols. QAPP for SWAMP Perennial Stream Surveys. |
QAPP Information Reference(s): |
Quality Assurance Program Plans, Quality Assurance Project Plans, and Standard Operating Procedures for the SWAMP program |
|
Line of Evidence (LOE) for Decision ID 169301, Benthic Community Effects
|
Region 1 |
Klamath River HU, Shasta River HA |
|
|
LOE ID: |
96332 |
|
Pollutant: |
Benthic-Macroinvertebrate Bioassessments |
LOE Subgroup: |
Population/Community Degradation |
Matrix: |
Water |
Fraction: |
None |
|
Beneficial Use: |
Cold Freshwater Habitat |
Aquatic Life Use: |
Cold Freshwater Habitat |
|
Number of Samples: |
1 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
Benthic macroinvertebrate surveys |
Data Used to Assess Water Quality: |
The site had a CSCI score(s) of 1.107362949. Therefore, this site is not exceeding the water quality objective for the aquatic life beneficial use. |
Data Reference: |
Water Quality Assessment Data for the 2018 solicitation cycle submitted through CEDEN for SWAMP Reference Condition Management Plan .
|
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
From the Water Quality Control Plan, North Coast Region: All waters shall be maintained free of toxic substances in concentrations that are toxic to, or that produce detrimental physiological responses in human, plant, animal, or aquatic life. |
Objective/Criterion Reference: |
Water Quality Control Plan (Basin Plan) for the North Coast Region |
|
Evaluation Guideline: |
The California Stream Condition Index (CSCI) is a biological scoring tool that helps aquatic resource managers translate complex data about benthic macroinvertebrates found living in a stream into an overall measure of stream health. The CSCI score is calculated by comparing the expected condition with actual (observed) results (Rhen, A.C. et al., 2015). CSCI scores range from 0 (highly degraded) to greater than 1 (equivalent to reference). CSCI scoring of biological condition are as follows (per the scientific paper supporting the development of the CSCI scoring tool): greater than or equal to 0.92 = likely intact condition, 0.91 to 0.80 = possibly altered condition, 0.79 to 0.63 = likely altered condition, less than or equal to 0.62 = very likely altered condition. Sites with scores below 0.79 are considered to have exceeded the water quality objective for the aquatic life beneficial use. |
Guideline Reference: |
Bioassessment in complex environments: designing an
index for consistent meaning in different settings
|
|
Spatial Representation: |
These samples were collected at the following station: 105WE0592 |
Temporal Representation: |
These samples were collected on: 7/13/2015 |
Environmental Conditions: |
|
QAPP Information: |
Data collected following SWAMP QA protocols. QAPP for SWAMP Reference Condition Management Plan. |
QAPP Information Reference(s): |
Quality Assurance Program Plans, Quality Assurance Project Plans, and Standard Operating Procedures for the SWAMP program |
|
Line of Evidence (LOE) for Decision ID 169301, Benthic Community Effects
|
Region 1 |
Klamath River HU, Shasta River HA |
|
|
LOE ID: |
132752 |
|
Pollutant: |
Habitat Assessment (Streams) |
LOE Subgroup: |
Ancillary Line of Evidence |
Matrix: |
-N/A |
Fraction: |
None |
|
Beneficial Use: |
Cold Freshwater Habitat |
Aquatic Life Use: |
Cold Freshwater Habitat |
|
Number of Samples: |
1 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
HABITAT ASSESSMENT |
Data Used to Assess Water Quality: |
The site had an IPI score of 1.09 which indicates the habitat is Likely Intact. |
Data Reference: |
Water Quality Assessment Data for the 2018 solicitation cycle submitted through CEDEN for SWAMP Reference Condition Management Plan .
|
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
From the Water Quality Control Plan, North Coast Region: All waters shall be maintained free of toxic substances in concentrations that are toxic to, or that produce detrimental physiological responses in human, plant, animal, or aquatic life. |
Objective/Criterion Reference: |
Water Quality Control Plan (Basin Plan) for the North Coast Region |
|
Evaluation Guideline: |
Physical characteristics of a site vary due to both natural factors and human disturbance. Statistical models based on a large statewide reference data set can help distinguish natural variability from anthropogenic stress. These models work across the diverse stream types found in California. The Index of Physical Habitat Integrity (IPI) is a multimetric Index developed based on these models to characterize physical habitat condition for streams in California. Index scores near 1 indicate physical habitat conditions similar to reference, whereas lower scores indicate degradation. For the purposes of making statewide assessments, three thresholds (analogous to those used for the CSCI) were established based on the 30th; 10th; and 1st percentiles of IPI scores at reference sites. These three thresholds divide the IPI scoring range into 4 categories of physical condition as follows: greater than or equal to 0.94 = likely intact condition; 0.93 to 0.84 = possibly altered condition; 0.83 to 0.71 = likely altered condition; less than or equal to 0.70 = very likely altered condition. Scores of 0.83 or lower indicate that the physical habitat has been altered and low CSCI scores from this site may be due to impacts to the physical habitat. beneficial use. |
Guideline Reference: |
An Index to Measure the Quality of Physical Habitat in California Wadeable Streams |
|
Spatial Representation: |
These samples were collected at the following station: 105WE0592 |
Temporal Representation: |
These samples were collected on: 7/13/2015 |
Environmental Conditions: |
|
QAPP Information: |
Data collected following SWAMP QA protocols. QAPP for SWAMP Reference Condition Management Plan. |
QAPP Information Reference(s): |
Quality Assurance Program Plans, Quality Assurance Project Plans, and Standard Operating Procedures for the SWAMP program |
|
Line of Evidence (LOE) for Decision ID 169301, Benthic Community Effects
|
Region 1 |
Klamath River HU, Shasta River HA |
|
|
LOE ID: |
34159 |
|
Pollutant: |
pH |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
None |
|
Beneficial Use: |
Cold Freshwater Habitat |
|
Number of Samples: |
4 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
None of the 4 samples exceeded the objective. |
Data Reference: |
RWB1 Trend Maintenance Periods FYs 2007 2008 |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
Water Quality Control Plan, North Coast Region (NCRWQCB 2011): Table 3-1 states that the lower limit pH for this water body is 7.0, and the upper limit pH for this water body is 8.5. |
Objective/Criterion Reference: |
Water Quality Control Plan (Basin Plan) for the North Coast Region |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
Samples were collected from the Shasta River at Hwy 263 station (105SHA263). |
Temporal Representation: |
Samples were collected approximately once per quarter year from November 2007 to July 2008. |
Environmental Conditions: |
|
QAPP Information: |
SWAMP QAPP |
QAPP Information Reference(s): |
Surface Water Ambient Monitoring Program Quality Assurance Program Plan |
|
Line of Evidence (LOE) for Decision ID 169301, Benthic Community Effects
|
Region 1 |
Klamath River HU, Shasta River HA |
|
|
LOE ID: |
318405 |
|
Pollutant: |
pH |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
None |
|
Beneficial Use: |
Cold Freshwater Habitat |
|
Number of Samples: |
33 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed pH data for SWAMP RWB1 Monitoring and determined that 0 samples are less than pH 6.5 and 0 samples are greater than pH 8.5, so that 0 of 33 samples exceed the water quality objective. |
Data Reference: |
Benthic, Field, Habitat, Tissue, Toxicity, WQ from the Surface Water Ambient Monitoring Program for the 2026 Integrated Report in Region 1 |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
Water Quality Control Plan, North Coast Basin, Chapter III, General Objectives for all Inland Surface Waters, Enclosed Bays and Estuaries states the following: The pH shall conform to the values listed in Table 3-1 which states that the water quality objective for pH shall not be depressed below 7.0 or raised above 8.5. |
Objective/Criterion Reference: |
Water Quality Control Plan (Basin Plan) for the North Coast Region |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
These samples were collected at sampling station name: Parks Creek at Shasta River; station code: 105PC0001. |
Temporal Representation: |
These samples were collected from 4/8/2021-10/28/2021. |
Environmental Conditions: |
|
QAPP Information: |
QAPP for SWAMP RWB1 Monitoring |
QAPP Information Reference(s): |
Generic SWAMP QAPrP |
|
Line of Evidence (LOE) for Decision ID 169301, Benthic Community Effects
|
Region 1 |
Klamath River HU, Shasta River HA |
|
|
LOE ID: |
100704 |
|
Pollutant: |
pH |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
None |
|
Beneficial Use: |
Cold Freshwater Habitat |
|
Number of Samples: |
4 |
Number of Exceedances: |
2 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP RWB1 Monitoring data for Klamath River HU, Shasta River HA to determine beneficial use support and results are as follows: 2 of 4 samples exceeded the water quality standard for pH. |
Data Reference: |
Water Quality Assessment Data for the 2018 solicitation cycle submitted through CEDEN for SWAMP RWB1 Monitoring .
|
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
Water Quality Control Plan, North Coast Basin, Chapter III, General Objectives for all Inland Surface Waters, Enclosed Bays and Estuaries states the following: The pH shall conform to the values listed in Table 3-1 which states that the water quality objective for pH for water bodies in the Shasta River shall not be depressed below 7.0 or raised above 8.5. |
Objective/Criterion Reference: |
Water Quality Control Plan (Basin Plan) for the North Coast Region |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
The samples were collected at 1 monitoring site(s) Shasta River at Hwy 263
(105SH1452) |
Temporal Representation: |
The samples were collected between the dates of 2013-03-06 to 2013-11-20. |
Environmental Conditions: |
There are no known environmental conditions (e.g., seasonality, land use practices, fire events, storms, etc.) that are related to these data. |
QAPP Information: |
Quality Assurance Program Plan and Standard Operating Procedures for SWAMP program  |
QAPP Information Reference(s): |
Water Quality Assessment Data for the 2018 solicitation cycle submitted through CEDEN for SWAMP Reference Condition Management Plan .
|
QAPP Information Reference(s): |
Quality Assurance Program Plans, Quality Assurance Project Plans, and Standard Operating Procedures for the SWAMP program |
|
Line of Evidence (LOE) for Decision ID 169301, Benthic Community Effects
|
Region 1 |
Klamath River HU, Shasta River HA |
|
|
LOE ID: |
317912 |
|
Pollutant: |
Specific Conductivity |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Total |
|
Beneficial Use: |
Cold Freshwater Habitat |
|
Number of Samples: |
1 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed data from the parent project SWAMP RWB1 Monitoring and determined that calendar year 2021 does not exceed the 90% or 50% upper limit, so that 0 of 1 sample exceeds the water quality objective. |
Data Reference: |
Benthic, Field, Habitat, Tissue, Toxicity, WQ from the Surface Water Ambient Monitoring Program for the 2026 Integrated Report in Region 1 |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
Per the Basin Plan (NCRWQCB 2007): The 90% upper limit specific conductance objective at 77 F is 700 micromhos (or mS/cm2). The 50% upper limit specific conductance objective at 77 F is 400 micromhos (or mS/cm2). The 90% and 50% upper limits represent the 90/50 percentile values for a calendar year. 90% or 50% or more of the values must be less than or equal to the upper limit. |
Objective/Criterion Reference: |
Water Quality Control Plan (Basin Plan) for the North Coast Region |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
These samples were collected at sampling station name: Big Springs Creek at Old Water Wheel; station code: 105BS7150. |
Temporal Representation: |
These samples were collected from 4/15/2021-10/28/2021. |
Environmental Conditions: |
|
QAPP Information: |
QAPP for SWAMP RWB1 Monitoring |
QAPP Information Reference(s): |
Generic SWAMP QAPrP |
|
Line of Evidence (LOE) for Decision ID 169301, Benthic Community Effects
|
Region 1 |
Klamath River HU, Shasta River HA |
|
|
LOE ID: |
318621 |
|
Pollutant: |
Specific Conductivity |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Total |
|
Beneficial Use: |
Cold Freshwater Habitat |
|
Number of Samples: |
6 |
Number of Exceedances: |
6 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed specific conductivity data for Klamath Hydroelectric Settlement Monitoring and determined that calendar years 2010, 2011, 2012, 2013, 2014, and 2015 exceed the 50% upper limit, so that 6 of 6 samples exceed the water quality objective. |
Data Reference: |
Field, WQ from the Klamath Basin Monitoring Program for the 2026 Integrated Report in Region 1 |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
Per the Basin Plan (NCRWQCB 2007): The 90% upper limit specific conductance objective at 77 F is 700 micromhos (or mS/cm2). The 50% upper limit specific conductance objective at 77 F is 400 micromhos (or mS/cm2). The 90% and 50% upper limits represent the 90/50 percentile values for a calendar year. 90% or 50% or more of the values must be less than or equal to the upper limit. |
Objective/Criterion Reference: |
Water Quality Control Plan (Basin Plan) for the North Coast Region |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
These samples were collected at sampling station name: Shasta River near mouth (Baseline); station code: SH00000_KHSA. |
Temporal Representation: |
These samples were collected from 9/8/2010-12/14/2016. |
Environmental Conditions: |
|
QAPP Information: |
QAPP for Klamath Hydroelectric Settlement Monitoring |
QAPP Information Reference(s): |
San Francisco Estuary Institute - QA doc_cyano SOP (2009) - Klamath Hydroelectric Settlement Monitoring - 402674 |
|
Line of Evidence (LOE) for Decision ID 169301, Benthic Community Effects
|
Region 1 |
Klamath River HU, Shasta River HA |
|
|
LOE ID: |
318012 |
|
Pollutant: |
Specific Conductivity |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Total |
|
Beneficial Use: |
Cold Freshwater Habitat |
|
Number of Samples: |
1 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed data for parent project SWAMP Reference Condition Management Plan and determined that calendar year 2015 did not exceed either the 90% or the 50% upper limit, so that 0 of 1 sample exceeds the water quality objective for specific conductivity. |
Data Reference: |
Benthic, Field, Habitat, WQ from the Surface Water Ambient Monitoring Program for the 2026 Integrated Report in Region 1 |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
Per the Basin Plan (NCRWQCB 2007): The 90% upper limit specific conductance objective at 77 F is 700 micromhos (or mS/cm2). The 50% upper limit specific conductance objective at 77 F is 400 micromhos (or mS/cm2). The 90% and 50% upper limits represent the 90/50 percentile values for a calendar year. 90% or 50% or more of the values must be less than or equal to the upper limit. |
Objective/Criterion Reference: |
Water Quality Control Plan (Basin Plan) for the North Coast Region |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
This sample was collected at sampling station name: Eddy Creek ~0.8 miles downstream from end of 4WD road.; station code: 105WE0592. |
Temporal Representation: |
This sample was collected on 7/13/2015. |
Environmental Conditions: |
|
QAPP Information: |
QAPP for SWAMP Reference Condition Management Plan |
QAPP Information Reference(s): |
Generic SWAMP QAPrP |
|
Line of Evidence (LOE) for Decision ID 169301, Benthic Community Effects
|
Region 1 |
Klamath River HU, Shasta River HA |
|
|
LOE ID: |
318617 |
|
Pollutant: |
Specific Conductivity |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Total |
|
Beneficial Use: |
Cold Freshwater Habitat |
|
Number of Samples: |
1 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed specific conductivity data for SWAMP Perennial Stream Surveys and determined that calendar year 2016 does not exceed the 90% or 50% upper limit, so that 0 of 1 sample exceeds the water quality objective. |
Data Reference: |
Benthic, Field, Habitat, WQ from the Surface Water Ambient Monitoring Program for the 2026 Integrated Report in Region 1 |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
Per the Basin Plan (NCRWQCB 2007): The 90% upper limit specific conductance objective at 77 F is 800 micromhos (or mS/cm2). The 50% upper limit specific conductance objective at 77 F is 600 micromhos (or mS/cm2). The 90% and 50% upper limits represent the 90/50 percentile values for a calendar year. 90% or 50% or more of the values must be less than or equal to the upper limit. |
Objective/Criterion Reference: |
Water Quality Control Plan (Basin Plan) for the North Coast Region |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
This sample was collected at sampling station name: Shasta River ~1mi above Cooley Gulch; station code: 105PS0295. |
Temporal Representation: |
This sample was collected on 6/15/2016. |
Environmental Conditions: |
|
QAPP Information: |
QAPP for SWAMP Perennial Stream Surveys |
QAPP Information Reference(s): |
Generic SWAMP QAPrP |
|
Line of Evidence (LOE) for Decision ID 169301, Benthic Community Effects
|
Region 1 |
Klamath River HU, Shasta River HA |
|
|
LOE ID: |
319005 |
|
Pollutant: |
Specific Conductivity |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Total |
|
Beneficial Use: |
Cold Freshwater Habitat |
|
Number of Samples: |
1 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed specific conductivity data for USGS California Water Science Center and determined that calendar year 2015 does not exceed either the 90% or 50% upper limit, so that 0 of 1 sample exceeds the water quality objective. |
Data Reference: |
WQX from the NWQMP for the 2026 Integrated Report in Region 1 |
|
SWAMP Data: |
Non-SWAMP |
|
Water Quality Objective/Criterion: |
Per the Basin Plan (NCRWQCB 2007): The 90% upper limit specific conductance objective at 77 F is 800 micromhos (or mS/cm2). The 50% upper limit specific conductance objective at 77 F is 600 micromhos (or mS/cm2). The 90% and 50% upper limits represent the 90/50 percentile values for a calendar year. 90% or 50% or more of the values must be less than or equal to the upper limit. |
Objective/Criterion Reference: |
Water Quality Control Plan (Basin Plan) for the North Coast Region |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
This sample was collected at sampling station name: SHASTA R NR EDGEWOOD CA; station code: USGS-11516750. |
Temporal Representation: |
This sample was collected on 8/27/2015. |
Environmental Conditions: |
|
QAPP Information: |
QAPP for USGS California Water Science Center |
QAPP Information Reference(s): |
QAPP for USGS Data Collected during the 2026 Integrated Report Cycle |
|
Line of Evidence (LOE) for Decision ID 169301, Benthic Community Effects
|
Region 1 |
Klamath River HU, Shasta River HA |
|
|
LOE ID: |
318406 |
|
Pollutant: |
Specific Conductivity |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Total |
|
Beneficial Use: |
Cold Freshwater Habitat |
|
Number of Samples: |
1 |
Number of Exceedances: |
1 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed specific conductivity data for SWAMP RWB1 Monitoring and determined that calendar year 2021 did not exceed the 90% upper limit of 700 micromhos and did exceed the 50% upper limit of 400 micromhos, so that 1 of 1 sample exceeds the water quality objective. |
Data Reference: |
Benthic, Field, Habitat, Tissue, Toxicity, WQ from the Surface Water Ambient Monitoring Program for the 2026 Integrated Report in Region 1 |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
Per the Basin Plan (NCRWQCB 2007): The 90% upper limit specific conductance objective at 77 F is 700 micromhos (or mS/cm2). The 50% upper limit specific conductance objective at 77 F is 400 micromhos (or mS/cm2). The 90% and 50% upper limits represent the 90/50 percentile values for a calendar year. 90% or 50% or more of the values must be less than or equal to the upper limit. |
Objective/Criterion Reference: |
Water Quality Control Plan (Basin Plan) for the North Coast Region |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
These samples were collected at sampling station name: Parks Creek at Shasta River; station code: 105PC0001. |
Temporal Representation: |
These samples were collected from 4/8/2021-10/28/2021. |
Environmental Conditions: |
|
QAPP Information: |
QAPP for SWAMP RWB1 Monitoring |
QAPP Information Reference(s): |
Generic SWAMP QAPrP |
|
Line of Evidence (LOE) for Decision ID 169301, Benthic Community Effects
|
Region 1 |
Klamath River HU, Shasta River HA |
|
|
LOE ID: |
318619 |
|
Pollutant: |
Specific Conductivity |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Total |
|
Beneficial Use: |
Cold Freshwater Habitat |
|
Number of Samples: |
1 |
Number of Exceedances: |
1 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed specific conductivity data for SWAMP RWB1 Monitoring and determined that calendar year 2021 exceeds the 50% upper limit, so that 1 of 1 sample exceeds the water quality objective. |
Data Reference: |
Benthic, Field, Habitat, Tissue, Toxicity, WQ from the Surface Water Ambient Monitoring Program for the 2026 Integrated Report in Region 1 |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
Per the Basin Plan (NCRWQCB 2007): The 90% upper limit specific conductance objective at 77 F is 700 micromhos (or mS/cm2). The 50% upper limit specific conductance objective at 77 F is 400 micromhos (or mS/cm2). The 90% and 50% upper limits represent the 90/50 percentile values for a calendar year. 90% or 50% or more of the values must be less than or equal to the upper limit. |
Objective/Criterion Reference: |
Water Quality Control Plan (Basin Plan) for the North Coast Region |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
These samples were collected at sampling station name: Shasta River downstream Parks Creek; station code: 105SH6389. |
Temporal Representation: |
These samples were collected from 4/8/2021-10/28/2021. |
Environmental Conditions: |
|
QAPP Information: |
QAPP for SWAMP RWB1 Monitoring |
QAPP Information Reference(s): |
Generic SWAMP QAPrP |
|
Line of Evidence (LOE) for Decision ID 169301, Benthic Community Effects
|
Region 1 |
Klamath River HU, Shasta River HA |
|
|
LOE ID: |
318408 |
|
Pollutant: |
Specific Conductivity |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Total |
|
Beneficial Use: |
Cold Freshwater Habitat |
|
Number of Samples: |
1 |
Number of Exceedances: |
1 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed specific conductivity data for SWAMP RWB1 Monitoring and determined that calendar year 2021 exceeded both the 90% upper limit of 700 micromhos 50% upper limit of 400 micromhos, so that 1 of 1 sample exceeds the water quality objective. |
Data Reference: |
Benthic, Field, Habitat, Tissue, Toxicity, WQ from the Surface Water Ambient Monitoring Program for the 2026 Integrated Report in Region 1 |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
Per the Basin Plan (NCRWQCB 2007): The 90% upper limit specific conductance objective at 77 F is 700 micromhos (or mS/cm2). The 50% upper limit specific conductance objective at 77 F is 400 micromhos (or mS/cm2). The 90% and 50% upper limits represent the 90/50 percentile values for a calendar year. 90% or 50% or more of the values must be less than or equal to the upper limit. |
Objective/Criterion Reference: |
Water Quality Control Plan (Basin Plan) for the North Coast Region |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
These samples were collected at sampling station name: Parks Creek Overflow at Big Springs Road Crossing; station code: 105PO0001. |
Temporal Representation: |
These samples were collected from 4/8/2021-10/28/2021. |
Environmental Conditions: |
|
QAPP Information: |
QAPP for SWAMP RWB1 Monitoring |
QAPP Information Reference(s): |
Generic SWAMP QAPrP |
|
Line of Evidence (LOE) for Decision ID 169301, Benthic Community Effects
|
Region 1 |
Klamath River HU, Shasta River HA |
|
|
LOE ID: |
318250 |
|
Pollutant: |
Specific Conductivity |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Total |
|
Beneficial Use: |
Cold Freshwater Habitat |
|
Number of Samples: |
1 |
Number of Exceedances: |
1 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed specific conductivity data for SWAMP RWB1 Monitoring and determined that 1 of 1 sample exceeds the water quality objective for calendar year 2021. |
Data Reference: |
Benthic, Field, Habitat, Tissue, Toxicity, WQ from the Surface Water Ambient Monitoring Program for the 2026 Integrated Report in Region 1 |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
Per the Basin Plan (NCRWQCB 2007): The 90% upper limit specific conductance objective at 77 F is 700 micromhos (or mS/cm2). The 50% upper limit specific conductance objective at 77 F is 400 micromhos (or mS/cm2). The 90% and 50% upper limits represent the 90/50 percentile values for a calendar year. 90% or 50% or more of the values must be less than or equal to the upper limit. |
Objective/Criterion Reference: |
Water Quality Control Plan (Basin Plan) for the North Coast Region |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
These samples were collected at sampling station name: Little Springs Creek at Outlet Works; station code: 105LS9900. |
Temporal Representation: |
These samples were collected from 6/3/2021-10/28/2021. |
Environmental Conditions: |
|
QAPP Information: |
QAPP for SWAMP RWB1 Monitoring |
QAPP Information Reference(s): |
Generic SWAMP QAPrP |
|
Line of Evidence (LOE) for Decision ID 169301, Benthic Community Effects
|
Region 1 |
Klamath River HU, Shasta River HA |
|
|
LOE ID: |
318252 |
|
Pollutant: |
Specific Conductivity |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Total |
|
Beneficial Use: |
Cold Freshwater Habitat |
|
Number of Samples: |
1 |
Number of Exceedances: |
1 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed specific conductivity data for SWAMP RWB1 Monitoring and determined that 1 of 1 sample exceeds the water quality objective for calendar year 2021. |
Data Reference: |
Benthic, Field, Habitat, Tissue, Toxicity, WQ from the Surface Water Ambient Monitoring Program for the 2026 Integrated Report in Region 1 |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
Per the Basin Plan (NCRWQCB 2007): The 90% upper limit specific conductance objective at 77 F is 700 micromhos (or mS/cm2). The 50% upper limit specific conductance objective at 77 F is 400 micromhos (or mS/cm2). The 90% and 50% upper limits represent the 90/50 percentile values for a calendar year. 90% or 50% or more of the values must be less than or equal to the upper limit. |
Objective/Criterion Reference: |
Water Quality Control Plan (Basin Plan) for the North Coast Region |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
These samples were collected at sampling station name: Little Springs Creek at Spring Head; station code: 105LS9999. |
Temporal Representation: |
These samples were collected from 4/8/2021-5/27/2021. |
Environmental Conditions: |
|
QAPP Information: |
QAPP for SWAMP RWB1 Monitoring |
QAPP Information Reference(s): |
Generic SWAMP QAPrP |
|
Line of Evidence (LOE) for Decision ID 169301, Benthic Community Effects
|
Region 1 |
Klamath River HU, Shasta River HA |
|
|
LOE ID: |
318623 |
|
Pollutant: |
Specific Conductivity |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Total |
|
Beneficial Use: |
Cold Freshwater Habitat |
|
Number of Samples: |
1 |
Number of Exceedances: |
1 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed specific conductivity data for SWAMP RWB1 Monitoring and determined that calendar year 2021 exceeds the 50% upper limit, so that 1 of 1 sample exceeds the water quality objective. |
Data Reference: |
Benthic, Field, Habitat, Tissue, Toxicity, WQ from the Surface Water Ambient Monitoring Program for the 2026 Integrated Report in Region 1 |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
Per the Basin Plan (NCRWQCB 2007): The 90% upper limit specific conductance objective at 77 F is 700 micromhos (or mS/cm2). The 50% upper limit specific conductance objective at 77 F is 400 micromhos (or mS/cm2). The 90% and 50% upper limits represent the 90/50 percentile values for a calendar year. 90% or 50% or more of the values must be less than or equal to the upper limit. |
Objective/Criterion Reference: |
Water Quality Control Plan (Basin Plan) for the North Coast Region |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
These samples were collected at sampling station name: Shasta River upstream Parks Creek; station code: 105SH6418. |
Temporal Representation: |
These samples were collected from 4/8/2021-10/28/2021. |
Environmental Conditions: |
|
QAPP Information: |
QAPP for SWAMP RWB1 Monitoring |
QAPP Information Reference(s): |
Generic SWAMP QAPrP |
|
Line of Evidence (LOE) for Decision ID 169301, Benthic Community Effects
|
Region 1 |
Klamath River HU, Shasta River HA |
|
|
LOE ID: |
100711 |
|
Pollutant: |
pH |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
None |
|
Beneficial Use: |
Cold Freshwater Habitat |
|
Number of Samples: |
1 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP Perennial Stream Surveys data for Klamath River HU, Shasta River HA to determine beneficial use support and results are as follows: 0 of 1 samples exceeded the water quality standard for pH. |
Data Reference: |
Water Quality Assessment Data for the 2018 solicitation cycle submitted through CEDEN for SWAMP Perennial Stream Surveys .
|
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
Water Quality Control Plan, North Coast Basin, Chapter III, General Objectives for all Inland Surface Waters, Enclosed Bays and Estuaries states the following: The pH shall conform to the values listed in Table 3-1 which states that the water quality objective for pH for water bodies in Shasta River shall not be depressed below 7.0 or raised above 8.5. |
Objective/Criterion Reference: |
Water Quality Control Plan (Basin Plan) for the North Coast Region |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
The samples were collected at 1 monitoring site(s) Shasta River ~2.2mi below E. Louie Rd.
(105PS0231) |
Temporal Representation: |
The samples were collected between the date 08/29/2013. |
Environmental Conditions: |
There are no known environmental conditions (e.g., seasonality, land use practices, fire events, storms, etc.) that are related to these data. |
QAPP Information: |
Quality Assurance Program Plan and Standard Operating Procedures for SWAMP program  |
QAPP Information Reference(s): |
Quality Assurance Program Plans, Quality Assurance Project Plans, and Standard Operating Procedures for the SWAMP program |
|
Line of Evidence (LOE) for Decision ID 169301, Benthic Community Effects
|
Region 1 |
Klamath River HU, Shasta River HA |
|
|
LOE ID: |
318620 |
|
Pollutant: |
pH |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
None |
|
Beneficial Use: |
Cold Freshwater Habitat |
|
Number of Samples: |
79 |
Number of Exceedances: |
67 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed pH data for Klamath Hydroelectric Settlement Monitoring and determined that 0 samples are less than pH 7.0 and 67 samples are greater than pH 8.5, so that 67 of 79 samples exceed the water quality objective. |
Data Reference: |
Field, WQ from the Klamath Basin Monitoring Program for the 2026 Integrated Report in Region 1 |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
Water Quality Control Plan, North Coast Basin, Chapter III, General Objectives for all Inland Surface Waters, Enclosed Bays and Estuaries states the following: The pH shall conform to the values listed in Table 3-1 which states that the water quality objective for pH shall not be depressed below 7.0 or raised above 8.5. |
Objective/Criterion Reference: |
Water Quality Control Plan (Basin Plan) for the North Coast Region |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
These samples were collected at sampling station name: Shasta River near mouth (Baseline); station code: SH00000_KHSA. |
Temporal Representation: |
These samples were collected from 9/8/2010-12/14/2016. |
Environmental Conditions: |
|
QAPP Information: |
QAPP for Klamath Hydroelectric Settlement Monitoring |
QAPP Information Reference(s): |
San Francisco Estuary Institute - QA doc_cyano SOP (2009) - Klamath Hydroelectric Settlement Monitoring - 402674 |
|
Line of Evidence (LOE) for Decision ID 169301, Benthic Community Effects
|
Region 1 |
Klamath River HU, Shasta River HA |
|
|
LOE ID: |
318407 |
|
Pollutant: |
pH |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
None |
|
Beneficial Use: |
Cold Freshwater Habitat |
|
Number of Samples: |
40 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed pH data for SWAMP RWB1 Monitoring and determined that 0 samples are less than pH 6.5 and 0 samples are greater than pH 8.5, so that 0 of 40 samples exceed the water quality objective. |
Data Reference: |
Benthic, Field, Habitat, Tissue, Toxicity, WQ from the Surface Water Ambient Monitoring Program for the 2026 Integrated Report in Region 1 |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
Water Quality Control Plan, North Coast Basin, Chapter III, General Objectives for all Inland Surface Waters, Enclosed Bays and Estuaries states the following: The pH shall conform to the values listed in Table 3-1 which states that the water quality objective for pH shall not be depressed below 7.0 or raised above 8.5. |
Objective/Criterion Reference: |
Water Quality Control Plan (Basin Plan) for the North Coast Region |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
These samples were collected at sampling station name: Parks Creek Overflow at Big Springs Road Crossing; station code: 105PO0001. |
Temporal Representation: |
These samples were collected from 4/8/2021-10/28/2021. |
Environmental Conditions: |
|
QAPP Information: |
QAPP for SWAMP RWB1 Monitoring |
QAPP Information Reference(s): |
Generic SWAMP QAPrP |
|
Line of Evidence (LOE) for Decision ID 169301, Benthic Community Effects
|
Region 1 |
Klamath River HU, Shasta River HA |
|
|
LOE ID: |
100703 |
|
Pollutant: |
pH |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
None |
|
Beneficial Use: |
Cold Freshwater Habitat |
|
Number of Samples: |
4 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP RWB1 Monitoring data for Klamath River HU, Shasta River HA to determine beneficial use support and results are as follows: 0 of 4 samples exceeded the water quality standard for pH. |
Data Reference: |
Water Quality Assessment Data for the 2018 solicitation cycle submitted through CEDEN for SWAMP RWB1 Monitoring .
|
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
Water Quality Control Plan, North Coast Basin, Chapter III, General Objectives for all Inland Surface Waters, Enclosed Bays and Estuaries states the following: The pH shall conform to the values listed in Table 3-1 which states that the water quality objective for pH for water bodies in the Shasta River shall not be depressed below 7.0 or raised above 8.5. |
Objective/Criterion Reference: |
Water Quality Control Plan (Basin Plan) for the North Coast Region |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
The samples were collected at 1 monitoring site(s) Shasta River near Edgewood
(105SH9274). |
Temporal Representation: |
The samples were collected between the dates of 2013-04-29 to 2013-11-20. |
Environmental Conditions: |
There are no known environmental conditions (e.g., seasonality, land use practices, fire events, storms, etc.) that are related to these data. |
QAPP Information: |
Quality Assurance Program Plan and Standard Operating Procedures for SWAMP program  |
QAPP Information Reference(s): |
Quality Assurance Program Plans, Quality Assurance Project Plans, and Standard Operating Procedures for the SWAMP program |
|
Line of Evidence (LOE) for Decision ID 169301, Benthic Community Effects
|
Region 1 |
Klamath River HU, Shasta River HA |
|
|
LOE ID: |
318622 |
|
Pollutant: |
pH |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
None |
|
Beneficial Use: |
Cold Freshwater Habitat |
|
Number of Samples: |
34 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed pH data for SWAMP RWB1 Monitoring and determined that 0 samples are less than pH 7.0 and 0 samples are less than pH 8.5, so that 0 of 34 samples exceed the water quality objective. |
Data Reference: |
Benthic, Field, Habitat, Tissue, Toxicity, WQ from the Surface Water Ambient Monitoring Program for the 2026 Integrated Report in Region 1 |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
Water Quality Control Plan, North Coast Basin, Chapter III, General Objectives for all Inland Surface Waters, Enclosed Bays and Estuaries states the following: The pH shall conform to the values listed in Table 3-1 which states that the water quality objective for pH shall not be depressed below 7.0 or raised above 8.5. |
Objective/Criterion Reference: |
Water Quality Control Plan (Basin Plan) for the North Coast Region |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
These samples were collected at sampling station name: Shasta River upstream Parks Creek; station code: 105SH6418. |
Temporal Representation: |
These samples were collected from 4/8/2021-10/28/2021. |
Environmental Conditions: |
|
QAPP Information: |
QAPP for SWAMP RWB1 Monitoring |
QAPP Information Reference(s): |
Generic SWAMP QAPrP |
|
Line of Evidence (LOE) for Decision ID 169301, Benthic Community Effects
|
Region 1 |
Klamath River HU, Shasta River HA |
|
|
LOE ID: |
318251 |
|
Pollutant: |
pH |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
None |
|
Beneficial Use: |
Cold Freshwater Habitat |
|
Number of Samples: |
12 |
Number of Exceedances: |
1 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed pH data for SWAMP RWB1 Monitoring and determined that 1 sample is less than pH 7.0 and 0 samples are greater than pH 8.5, so that 1 of 12 samples exceeds the water quality objective. |
Data Reference: |
Benthic, Field, Habitat, Tissue, Toxicity, WQ from the Surface Water Ambient Monitoring Program for the 2026 Integrated Report in Region 1 |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
Water Quality Control Plan, North Coast Basin, Chapter III, General Objectives for all Inland Surface Waters, Enclosed Bays and Estuaries states the following: The pH shall conform to the values listed in Table 3-1 which states that the water quality objective for pH shall not be depressed below 7.0 or raised above 8.5. |
Objective/Criterion Reference: |
Water Quality Control Plan (Basin Plan) for the North Coast Region |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
These samples were collected at sampling station name: Little Springs Creek at Spring Head; station code: 105LS9999. |
Temporal Representation: |
These samples were collected from 4/8/2021-5/27/2021. |
Environmental Conditions: |
|
QAPP Information: |
QAPP for SWAMP RWB1 Monitoring |
QAPP Information Reference(s): |
Generic SWAMP QAPrP |
|
Line of Evidence (LOE) for Decision ID 169301, Benthic Community Effects
|
Region 1 |
Klamath River HU, Shasta River HA |
|
|
LOE ID: |
318011 |
|
Pollutant: |
pH |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
None |
|
Beneficial Use: |
Cold Freshwater Habitat |
|
Number of Samples: |
1 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed data for parent project SWAMP Reference Condition Management Plan and determined that 0 samples were less than pH 7 or greater than pH 8.5, so that 0 of 1 sample exceeds the water quality objective for pH. |
Data Reference: |
Benthic, Field, Habitat, WQ from the Surface Water Ambient Monitoring Program for the 2026 Integrated Report in Region 1 |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
Water Quality Control Plan, North Coast Basin, Chapter III, General Objectives for all Inland Surface Waters, Enclosed Bays and Estuaries states the following: The pH shall conform to the values listed in Table 3-1 which states that the water quality objective for pH shall not be depressed below 7.0 or raised above 8.5. |
Objective/Criterion Reference: |
Water Quality Control Plan (Basin Plan) for the North Coast Region |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
This sample was collected at sampling station name: Eddy Creek ~0.8 miles downstream from end of 4WD road.; station code: 105WE0592. |
Temporal Representation: |
This sample was collected on 7/13/2015. |
Environmental Conditions: |
|
QAPP Information: |
QAPP for SWAMP Reference Condition Management Plan |
QAPP Information Reference(s): |
Generic SWAMP QAPrP |
|
Line of Evidence (LOE) for Decision ID 169301, Benthic Community Effects
|
Region 1 |
Klamath River HU, Shasta River HA |
|
|
LOE ID: |
318616 |
|
Pollutant: |
pH |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
None |
|
Beneficial Use: |
Cold Freshwater Habitat |
|
Number of Samples: |
1 |
Number of Exceedances: |
1 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed pH data for SWAMP Perennial Stream Surveys and determined that 0 samples are less than pH 7.0 and 1 sample is greater than pH 8.5, so that 1 of 1 sample exceeds the water quality objective. |
Data Reference: |
Benthic, Field, Habitat, WQ from the Surface Water Ambient Monitoring Program for the 2026 Integrated Report in Region 1 |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
Water Quality Control Plan, North Coast Basin, Chapter III, General Objectives for all Inland Surface Waters, Enclosed Bays and Estuaries states the following: The pH shall conform to the values listed in Table 3-1 which states that the water quality objective for pH shall not be depressed below 7.0 or raised above 8.5. |
Objective/Criterion Reference: |
Water Quality Control Plan (Basin Plan) for the North Coast Region |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
This sample was collected at sampling station name: Shasta River ~1mi above Cooley Gulch; station code: 105PS0295. |
Temporal Representation: |
This sample was collected on 6/15/2016. |
Environmental Conditions: |
|
QAPP Information: |
QAPP for SWAMP Perennial Stream Surveys |
QAPP Information Reference(s): |
Generic SWAMP QAPrP |
|
Line of Evidence (LOE) for Decision ID 169301, Benthic Community Effects
|
Region 1 |
Klamath River HU, Shasta River HA |
|
|
LOE ID: |
318618 |
|
Pollutant: |
pH |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
None |
|
Beneficial Use: |
Cold Freshwater Habitat |
|
Number of Samples: |
39 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed pH data for SWAMP RWB1 Monitoring and determined that 0 samples are less than pH 7.0 and 0 samples are greater than pH 8.5, so that 0 of 39 samples exceed the water quality objective. |
Data Reference: |
Benthic, Field, Habitat, Tissue, Toxicity, WQ from the Surface Water Ambient Monitoring Program for the 2026 Integrated Report in Region 1 |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
Water Quality Control Plan, North Coast Basin, Chapter III, General Objectives for all Inland Surface Waters, Enclosed Bays and Estuaries states the following: The pH shall conform to the values listed in Table 3-1 which states that the water quality objective for pH shall not be depressed below 7.0 or raised above 8.5. |
Objective/Criterion Reference: |
Water Quality Control Plan (Basin Plan) for the North Coast Region |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
These samples were collected at sampling station name: Shasta River downstream Parks Creek; station code: 105SH6389. |
Temporal Representation: |
These samples were collected from 4/8/2021-10/28/2021. |
Environmental Conditions: |
|
QAPP Information: |
QAPP for SWAMP RWB1 Monitoring |
QAPP Information Reference(s): |
Generic SWAMP QAPrP |
|
Line of Evidence (LOE) for Decision ID 169301, Benthic Community Effects
|
Region 1 |
Klamath River HU, Shasta River HA |
|
|
LOE ID: |
317911 |
|
Pollutant: |
pH |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
None |
|
Beneficial Use: |
Cold Freshwater Habitat |
|
Number of Samples: |
23 |
Number of Exceedances: |
21 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed data from the parent project SWAMP RWB1 Monitoring and determined that 21 samples were less than pH 7 and 0 samples were greater than pH 8.5, so that 21 of 23 samples exceed the water quality objective for pH. |
Data Reference: |
Benthic, Field, Habitat, Tissue, Toxicity, WQ from the Surface Water Ambient Monitoring Program for the 2026 Integrated Report in Region 1 |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
Water Quality Control Plan, North Coast Basin, Chapter III, General Objectives for all Inland Surface Waters, Enclosed Bays and Estuaries states the following: The pH shall conform to the values listed in Table 3-1 which states that the water quality objective for pH shall not be depressed below 6.5 or raised above 8.5. |
Objective/Criterion Reference: |
Water Quality Control Plan (Basin Plan) for the North Coast Region |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
These samples were collected at sampling station name: Big Springs Creek at Old Water Wheel; station code: 105BS7150. |
Temporal Representation: |
These samples were collected from 4/15/2021-10/28/2021. |
Environmental Conditions: |
|
QAPP Information: |
QAPP for SWAMP RWB1 Monitoring |
QAPP Information Reference(s): |
Generic SWAMP QAPrP |
|
Line of Evidence (LOE) for Decision ID 169301, Benthic Community Effects
|
Region 1 |
Klamath River HU, Shasta River HA |
|
|
LOE ID: |
33910 |
|
Pollutant: |
pH |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
None |
|
Beneficial Use: |
Cold Freshwater Habitat |
|
Number of Samples: |
1 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
The sample collected did not exceed the objective |
Data Reference: |
Statewide Perennial Streams Assessment 2008 |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
Water Quality Control Plan, North Coast Region (NCRWQCB 2011): Table 3-1 states that the lower limit pH for surface water bodies for this water body is 7.0, and the upper limit pH is 8.5. |
Objective/Criterion Reference: |
Water Quality Control Plan (Basin Plan) for the North Coast Region |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
One sample was collected from the Evans Ditch station (105PS0188). |
Temporal Representation: |
One sample was collected in August 2008. |
Environmental Conditions: |
|
QAPP Information: |
SWAMP QAPP |
QAPP Information Reference(s): |
Surface Water Ambient Monitoring Program Quality Assurance Program Plan |
|
Line of Evidence (LOE) for Decision ID 169301, Benthic Community Effects
|
Region 1 |
Klamath River HU, Shasta River HA |
|
|
LOE ID: |
34160 |
|
Pollutant: |
pH |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
None |
|
Beneficial Use: |
Cold Freshwater Habitat |
|
Number of Samples: |
4 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
None of the 4 samples exceeded the objective. |
Data Reference: |
RWB1 Trend Maintenance Periods FYs 2007 2008 |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
Water Quality Control Plan, North Coast Region (NCRWQCB 2011): Table 3-1 states that the lower limit pH for this water body is 7.0, and the upper limit pH for this water body is 8.5. |
Objective/Criterion Reference: |
Water Quality Control Plan (Basin Plan) for the North Coast Region |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
Samples were collected from the Shasta River near Edgewood station (105SHAEDG). |
Temporal Representation: |
Samples were collected approximately once per quarter year from November 2007 to July 2008. |
Environmental Conditions: |
|
QAPP Information: |
SWAMP QAPP |
QAPP Information Reference(s): |
Surface Water Ambient Monitoring Program Quality Assurance Program Plan |
|
Line of Evidence (LOE) for Decision ID 169301, Benthic Community Effects
|
Region 1 |
Klamath River HU, Shasta River HA |
|
|
LOE ID: |
318249 |
|
Pollutant: |
pH |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
None |
|
Beneficial Use: |
Cold Freshwater Habitat |
|
Number of Samples: |
23 |
Number of Exceedances: |
1 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed pH data for SWAMP RWB1 Monitoring and determined that 6 samples are less than pH 7.0 and 0 samples are greater than pH 8.5, so that 6 of 23 samples exceed the water quality objective. |
Data Reference: |
Benthic, Field, Habitat, Tissue, Toxicity, WQ from the Surface Water Ambient Monitoring Program for the 2026 Integrated Report in Region 1 |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
Water Quality Control Plan, North Coast Basin, Chapter III, General Objectives for all Inland Surface Waters, Enclosed Bays and Estuaries states the following: The pH shall conform to the values listed in Table 3-1 which states that the water quality objective for pH shall not be depressed below 7.0 or raised above 8.5. |
Objective/Criterion Reference: |
Water Quality Control Plan (Basin Plan) for the North Coast Region |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
These samples were collected at sampling station name: Little Springs Creek at Outlet Works; station code: 105LS9900. |
Temporal Representation: |
These samples were collected from 6/3/2021-10/28/2021. |
Environmental Conditions: |
|
QAPP Information: |
QAPP for SWAMP RWB1 Monitoring |
QAPP Information Reference(s): |
Generic SWAMP QAPrP |
|
Line of Evidence (LOE) for Decision ID 169301, Benthic Community Effects
|
Region 1 |
Klamath River HU, Shasta River HA |
|
|
LOE ID: |
319006 |
|
Pollutant: |
pH |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
None |
|
Beneficial Use: |
Cold Freshwater Habitat |
|
Number of Samples: |
26 |
Number of Exceedances: |
24 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed pH data for Karuk Tribe (Tribal) and determined that 0 samples are less than pH 7.0 and 24 samples are greater than pH 8.5, so that 24 of 26 samples exceed the water quality objective. |
Data Reference: |
WQX from the NWQMP for the 2026 Integrated Report in Region 1 |
|
SWAMP Data: |
Non-SWAMP |
|
Water Quality Objective/Criterion: |
Water Quality Control Plan, North Coast Basin, Chapter III, General Objectives for all Inland Surface Waters, Enclosed Bays and Estuaries states the following: The pH shall conform to the values listed in Table 3-1 which states that the water quality objective for pH shall not be depressed below 7.0 or raised above 8.5. |
Objective/Criterion Reference: |
Water Quality Control Plan (Basin Plan) for the North Coast Region |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
These samples were collected at sampling station name: Shasta River; station code: KARUKDNR_WQX-SH. |
Temporal Representation: |
These samples were collected from 4/28/2011-9/28/2022. |
Environmental Conditions: |
|
QAPP Information: |
QAPP for Karuk Tribe (Tribal) |
QAPP Information Reference(s): |
Data collected by a California Tribe QAPP Approved by U.S. EPA
QAPP Reference
|
|
Line of Evidence (LOE) for Decision ID 169301, Benthic Community Effects
|
Region 1 |
Klamath River HU, Shasta River HA |
|
|
LOE ID: |
352528 |
|
Pollutant: |
Benthic-Macroinvertebrate Bioassessments |
LOE Subgroup: |
Population/Community Degradation |
Matrix: |
Water |
Fraction: |
None |
|
Beneficial Use: |
Cold Freshwater Habitat |
|
Number of Samples: |
1 |
Number of Exceedances: |
1 |
|
Data and Information Type: |
Benthic macroinvertebrate surveys |
Data Used to Assess Water Quality: |
Water Board staff assessed data for 105PS0295 to determine beneficial use support and the results are as follows: 1 of 1 samples exceeded the water quality standard. CSCI scores were from 0.741181173 to 0.741181173 . |
Data Reference: |
Benthic, Field, Habitat, WQ from the Surface Water Ambient Monitoring Program for the 2026 Integrated Report in Region 1 |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
All waters shall be maintained free of toxic substances in concentrations that are toxic to, or that produce detrimental physiological responses in human, plant, animal, or aquatic life. Compliance with this objective will be determined by use of indicator organisms, analyses of species diversity, population density, growth anomalies, bioassays of appropriate duration, or other appropriate methods as specified by the Regional Water Board (NCRWQCB 2018). |
Objective/Criterion Reference: |
Water Quality Control Plan (Basin Plan) for the North Coast Region |
|
Evaluation Guideline: |
The California Stream Condition Index (CSCI) is a biological scoring tool that helps aquatic resource managers translate complex data about benthic macroinvertebrates found living in a stream into an overall measure of stream health. The CSCI score is calculated by comparing the expected condition with actual (observed) results (Rhen, A.C. et al., 2015). CSCI scores range from 0 (highly degraded) to greater than 1 (equivalent to reference). CSCI scoring of biological condition are as follows (per the scientific paper supporting the development of the CSCI scoring tool): greater than or equal to 0.92 = likely intact condition, 0.91 to 0.80 = possibly altered condition, 0.79 to 0.63 = likely altered condition, less than or equal to 0.62 = very likely altered condition. Sites with scores below 0.79 are considered to have exceeded the water quality objective for the aquatic life beneficial use.) |
Guideline Reference: |
Bioassessment in complex environments: designing an
index for consistent meaning in different settings
|
|
Spatial Representation: |
The samples were collected at 1 monitoring site: 105PS0295 (Shasta River ~1mi above Cooley Gulch). |
Temporal Representation: |
Samples were collected from 2016-06-15 to 2016-06-15. |
Environmental Conditions: |
|
QAPP Information: |
QAPP for Surface Water Ambient Monitoring Program (SWAMP) |
QAPP Information Reference(s): |
Generic SWAMP QAPrP |
|
Line of Evidence (LOE) for Decision ID 169301, Benthic Community Effects
|
Region 1 |
Klamath River HU, Shasta River HA |
|
|
LOE ID: |
1656 |
|
Pollutant: |
Organic Enrichment/Low Dissolved Oxygen |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Not Specified |
Fraction: |
None |
|
Beneficial Use: |
Cold Freshwater Habitat |
|
Number of Samples: |
0 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
Not Specified |
Data Used to Assess Water Quality: |
Unspecified¿This LOE is a placeholder to support a 303(d) listing decision made prior to 2006. |
Data Reference: |
Placeholder reference 2006 303(d) |
|
SWAMP Data: |
Non-SWAMP |
|
Water Quality Objective/Criterion: |
|
Objective/Criterion Reference: |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
|
Temporal Representation: |
|
Environmental Conditions: |
|
QAPP Information: |
QA Info Missing |
QAPP Information Reference(s): |
|
Line of Evidence (LOE) for Decision ID 169301, Benthic Community Effects
|
Region 1 |
Klamath River HU, Shasta River HA |
|
|
LOE ID: |
33156 |
|
Pollutant: |
Oxygen, Dissolved |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Total Dissolved |
|
Beneficial Use: |
Cold Freshwater Habitat |
|
Number of Samples: |
672 |
Number of Exceedances: |
448 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Four hundred and forty-eight of the six hundred and seventy-two daily minimum DO values were below the 7.0 mg/L objective. Additionally, more than 50% of the daily minimum DO values at all sites in 2008 and 2009 were below 9.0 mg/L. |
Data Reference: |
Data for Various Pollutants in the Shasta Valley Resource Convservation District, 2008-2009. |
|
SWAMP Data: |
Non-SWAMP |
|
Water Quality Objective/Criterion: |
Water Quality Control Plan, North Coast Region (NCRWQCB 2011): The minimum dissolved oxygen objective is 7.0 mg/L. The 50% lower limit dissolved oxygen objective is 9.0 mg/L. The 50% lower limits represent the 50 percentile values for a calendar year. 50% or more of the values must be greater than or equal to the lower limit. |
Objective/Criterion Reference: |
Water Quality Control Plan (Basin Plan) for the North Coast Region |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
Samples were collected at the following locations: Site 105SRS1DO-downstream of the old dam, site 105SRS2DO-upstream of the old dam, site 105SRSA3DO-Shasta River at bend, and site 105SRS4DO-Shasta River at the small bridge. |
Temporal Representation: |
Samples were collected between 03/22/08 and 9/2/2009. |
Environmental Conditions: |
|
QAPP Information: |
Quality Assurance Project Plan for the 'Shasta Water Association Dam Demobilization and Water Quality Improvements Project' Prepared by: Amy Hansen Shasta Valley Resource Conservation District May 21, 2007 Version Number 1.0 |
QAPP Information Reference(s): |
Quality Assurance Project Plan for the Shasta Water Association Dam Demobilization and Water Quality Improvements Project, Version Number 1.0 and for the Araujo Diversion Removal Project, Version Number 1.0. |
|
Line of Evidence (LOE) for Decision ID 169301, Benthic Community Effects
|
Region 1 |
Klamath River HU, Shasta River HA |
|
|
LOE ID: |
32815 |
|
Pollutant: |
Temperature, water |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
None |
|
Beneficial Use: |
Cold Freshwater Habitat |
|
Number of Samples: |
2 |
Number of Exceedances: |
2 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Two of two annual maximum temperatures in the Shasta River exceeded the evaluation guideline. The annual maximum temperature in 2008 was 25.1 degrees C, and in 2009 was 26.0 degrees C. |
Data Reference: |
Data for Various Pollutants in the Shasta Valley Resource Convservation District, 2008-2009. |
|
SWAMP Data: |
Non-SWAMP |
|
Water Quality Objective/Criterion: |
Water Quality Control Plan, North Coast Region (NCRWQCB 2011): Natural receiving water temperature of intrastate waters shall not be altered unless it can be demonstrated to the satisfaction of the Regional Water Board that such alteration in temperature does not adversely affect beneficial uses. At no time or place shall the temperature of any COLD water be increased more than 5 degrees Fahrenheit (F) above natural receiving water temperature. |
Objective/Criterion Reference: |
Water Quality Control Plan (Basin Plan) for the North Coast Region |
|
Evaluation Guideline: |
According to the Shasta River TMDL, at River Mile (RM) 18.4 an annual maximum water temperature of 18.3 degrees C in the mainstem Shasta River is consistent with the "Water Quality Compliance Scenario", which includes 1) site potential riparian shade conditions on a river-reach scale, 2) modified temperature regime of tailwater return flows such that the return flows do not cause heating of the receiving water, 3) Big Springs Creek temperatures reduced by 4 degrees C from baseline, 4) Parks Creek temperatures reduced by 2 degrees C from baseline, and 5) 50% increase in Shasta River flows downstream of the Big Springs Creek confluence (an increase of 45 cfs). The maximum temperature value for RM 18.4 of the Shasta River is an estimate extrapolated from the Shasta River temperature TMDL model's water quality compliance scenario (Figure 6.3 in the Staff Report for the Action Plan for the Shasta River Watershed Dissolved Oxygen and Temperature TMDLs) (NCRWQCB 2006)." |
Guideline Reference: |
Staff Report for the Action Plan for the Shasta River Watershed Temperature and Dissolved Oxygen Total Maximum Daily Loads |
|
Spatial Representation: |
Continuous data were collected at one location on the Shasta River at site 105SRS3DO. |
Temporal Representation: |
Data were collected hourly from March - September in 2008 and 2009. |
Environmental Conditions: |
|
QAPP Information: |
Quality Assurance Project Plan for the 'Shasta Water Association Dam Demobilization and Water Quality Improvements Project' Prepared by: Amy Hansen Shasta Valley Resource Conservation District May 21, 2007 Version Number 1.0 |
QAPP Information Reference(s): |
Quality Assurance Project Plan for the Shasta Water Association Dam Demobilization and Water Quality Improvements Project, Version Number 1.0 and for the Araujo Diversion Removal Project, Version Number 1.0. |
|
Line of Evidence (LOE) for Decision ID 169301, Benthic Community Effects
|
Region 1 |
Klamath River HU, Shasta River HA |
|
|
LOE ID: |
31721 |
|
Pollutant: |
Temperature, water |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
None |
|
Beneficial Use: |
Cold Freshwater Habitat |
|
Number of Samples: |
2 |
Number of Exceedances: |
2 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Two of two annual maximum temperatures in the Shasta River exceeded the evaluation guideline. The annual maximum temperature in 2009 at site 105SRS1DO (RM 17.9) was 26.1 degrees C, and at site 105SRS2DO (RM 18.2) was 26.0 degrees C. Annual maximum temperatures at these two sites in 2008 could not be determined, as the data did not include late July/early August when the highest annual temperatures generally occur. |
Data Reference: |
Data for Various Pollutants in the Shasta Valley Resource Convservation District, 2008-2009. |
|
SWAMP Data: |
Non-SWAMP |
|
Water Quality Objective/Criterion: |
Water Quality Control Plan, North Coast Region (NCRWQCB 2011): Natural receiving water temperature of intrastate waters shall not be altered unless it can be demonstrated to the satisfaction of the Regional Water Board that such alteration in temperature does not adversely affect beneficial uses. At no time or place shall the temperature of any COLD water be increased more than 5 degrees Fahrenheit (F) above natural receiving water temperature. |
Objective/Criterion Reference: |
Water Quality Control Plan (Basin Plan) for the North Coast Region |
|
Evaluation Guideline: |
According to the Shasta River TMDL, at River Mile (RM) 17.9 and 18.1 an annual maximum water temperature of 18.2 degrees C in the mainstem Shasta River is consistent with the "Water Quality Compliance Scenario", which includes 1) site potential riparian shade conditions on a river-reach scale, 2) modified temperature regime of tailwater return flows such that the return flows do not cause heating of the receiving water, 3) Big Springs Creek temperatures reduced by 4 degrees C from baseline, 4) Parks Creek temperatures reduced by 2 degrees C from baseline, and 5) 50% increase in Shasta River flows downstream of the Big Springs Creek confluence (an increase of 45 cfs). The maximum temperature value for RM 17.9 & 18.1 of the Shasta River is an estimate extrapolated from the Shasta River temperature TMDL model's water quality compliance scenario (Figure 6.3 in the Staff Report for the Action Plan for the Shasta River Watershed Dissolved Oxygen and Temperature TMDLs) (NCRWQCB 2006)." |
Guideline Reference: |
Staff Report for the Action Plan for the Shasta River Watershed Temperature and Dissolved Oxygen Total Maximum Daily Loads |
|
Spatial Representation: |
Continuous data were collected at two locations on the Shasta River: 1) downstream dam site (105SRS1DO) and 2) upstream dam site (105SRS2DO). |
Temporal Representation: |
Data were collected hourly from March 2009 - September 2009. |
Environmental Conditions: |
|
QAPP Information: |
Quality Assurance Project Plan for the 'Shasta Water Association Dam Demobilization and Water Quality Improvements Project' Prepared by: Amy Hansen Shasta Valley Resource Conservation District May 21, 2007 Version Number 1.0 |
QAPP Information Reference(s): |
Quality Assurance Project Plan for the Shasta Water Association Dam Demobilization and Water Quality Improvements Project, Version Number 1.0 and for the Araujo Diversion Removal Project, Version Number 1.0. |
|
Line of Evidence (LOE) for Decision ID 169301, Benthic Community Effects
|
Region 1 |
Klamath River HU, Shasta River HA |
|
|
LOE ID: |
32839 |
|
Pollutant: |
Temperature, water |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
None |
|
Beneficial Use: |
Cold Freshwater Habitat |
|
Number of Samples: |
2 |
Number of Exceedances: |
2 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Two of two annual maximum temperature in the Shasta River exceeded the evaluation guideline. The annual maximum temperature in 2008 was 28.8 degrees C and in 2009 was 29.6 degrees C. |
Data Reference: |
Data for Various Pollutants in the Shasta Valley Resource Convservation District, 2008-2009. |
|
SWAMP Data: |
Non-SWAMP |
|
Water Quality Objective/Criterion: |
Water Quality Control Plan, North Coast Region (NCRWQCB 2011): Natural receiving water temperature of intrastate waters shall not be altered unless it can be demonstrated to the satisfaction of the Regional Water Board that such alteration in temperature does not adversely affect beneficial uses. At no time or place shall the temperature of any COLD water be increased more than 5 degrees Fahrenheit (F) above natural receiving water temperature. |
Objective/Criterion Reference: |
Water Quality Control Plan (Basin Plan) for the North Coast Region |
|
Evaluation Guideline: |
According to the Shasta River TMDL, at River Mile (RM) 11.9 an annual maximum water temperature of 17.4 degrees C in the mainstem Shasta River is consistent with the "Water Quality Compliance Scenario", which includes 1) site potential riparian shade conditions on a river-reach scale, 2) modified temperature regime of tailwater return flows such that the return flows do not cause heating of the receiving water, 3) Big Springs Creek temperatures reduced by 4 degrees C from baseline, 4) Parks Creek temperatures reduced by 2 degrees C from baseline, and 5) 50% increase in Shasta River flows downstream of the Big Springs Creek confluence (an increase of 45 cfs). The maximum temperature value for RM 11.9 of the Shasta River is an estimate extrapolated from the Shasta River temperature TMDL model's water quality compliance scenario (Figure 6.3 in the Staff Report for the Action Plan for the Shasta River Watershed Dissolved Oxygen and Temperature TMDLs) (NCRWQCB 2006)." |
Guideline Reference: |
Staff Report for the Action Plan for the Shasta River Watershed Temperature and Dissolved Oxygen Total Maximum Daily Loads |
|
Spatial Representation: |
Continuous data were collected at one location on the Shasta River at site 105SRA02T. |
Temporal Representation: |
Data were collected hourly from April - September in 2008 & March - September in 2009. |
Environmental Conditions: |
|
QAPP Information: |
Quality Assurance Project Plan for the 'Araujo Diversion Removal Project' Prepared by: Amy Hansen Shasta Valley Resource Conservation District July 30, 2007. |
QAPP Information Reference(s): |
Quality Assurance Project Plan for the Shasta Water Association Dam Demobilization and Water Quality Improvements Project, Version Number 1.0 and for the Araujo Diversion Removal Project, Version Number 1.0. |
|
Line of Evidence (LOE) for Decision ID 169301, Benthic Community Effects
|
Region 1 |
Klamath River HU, Shasta River HA |
|
|
LOE ID: |
329312 |
|
Pollutant: |
Temperature, water |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
None |
|
Beneficial Use: |
Cold Freshwater Habitat |
|
Number of Samples: |
1 |
Number of Exceedances: |
1 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed USGS California Water Science Center data for Klamath River HU, Shasta River HA to determine beneficial use support and results are as follows: 1 of 1 samples exceeded the water quality threshold for Temperature. |
Data Reference: |
WQX from the NWQMP for the 2026 Integrated Report in Region 1 |
|
SWAMP Data: |
Non-SWAMP |
|
Water Quality Objective/Criterion: |
Natural receiving water temperature of intrastate waters shall not be altered unless it can be demonstrated to the satisfaction of the Regional Water Board that such alteration in temperature does not adversely affect beneficial uses. At no time or place shall the temperature of any COLD water be increased more than 5 degrees Fahrenheit (F) above natural receiving water temperature (Basin Plan, North Coast Region). |
Objective/Criterion Reference: |
Water Quality Control Plan (Basin Plan) for the North Coast Region |
|
Evaluation Guideline: |
According to Carter (2008) the lethal temperature evaluation guideline for salmonid spawning, egg incubation & fry emergence is 20C. |
Guideline Reference: |
Effects of Temperature, Dissolved Oxygen/Total Dissolved Gas, Ammonia, and pH on Salmonids. Implications for California's North Coast TMDLs. California Regional Water Quality Control Board, North Coast Region |
|
Spatial Representation: |
The samples were collected at 1 monitoring site: USGS-11516750 (SHASTA R NR EDGEWOOD CA). |
Temporal Representation: |
The samples were collected between the dates of 2015-08-27 and 2015-08-27 |
Environmental Conditions: |
|
QAPP Information: |
QAPP not required for USGS projects |
QAPP Information Reference(s): |
QAPP for USGS Data Collected during the 2026 Integrated Report Cycle |
|
Line of Evidence (LOE) for Decision ID 169301, Benthic Community Effects
|
Region 1 |
Klamath River HU, Shasta River HA |
|
|
LOE ID: |
329256 |
|
Pollutant: |
Temperature, water |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
None |
|
Beneficial Use: |
Cold Freshwater Habitat |
|
Number of Samples: |
25 |
Number of Exceedances: |
11 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed Karuk Tribe (Tribal) data for Klamath River HU, Shasta River HA to determine beneficial use support and results are as follows: 11 of 25 samples exceeded the water quality threshold for Temperature. |
Data Reference: |
WQX from the NWQMP for the 2026 Integrated Report in Region 1 |
|
SWAMP Data: |
Non-SWAMP |
|
Water Quality Objective/Criterion: |
Natural receiving water temperature of intrastate waters shall not be altered unless it can be demonstrated to the satisfaction of the Regional Water Board that such alteration in temperature does not adversely affect beneficial uses. At no time or place shall the temperature of any COLD water be increased more than 5 degrees Fahrenheit (F) above natural receiving water temperature (Basin Plan, North Coast Region). |
Objective/Criterion Reference: |
Water Quality Control Plan (Basin Plan) for the North Coast Region |
|
Evaluation Guideline: |
According to Carter (2008) the lethal temperature evaluation guideline for salmonid spawning, egg incubation & fry emergence is 20C. |
Guideline Reference: |
Effects of Temperature, Dissolved Oxygen/Total Dissolved Gas, Ammonia, and pH on Salmonids. Implications for California's North Coast TMDLs. California Regional Water Quality Control Board, North Coast Region |
|
Spatial Representation: |
The samples were collected at 1 monitoring site: KARUKDNR_WQX-SH (Shasta River). |
Temporal Representation: |
The samples were collected between the dates of 2011-04-28 and 2022-09-28 |
Environmental Conditions: |
|
QAPP Information: |
Karuk Tribe QA |
QAPP Information Reference(s): |
Data collected by a California Tribe QAPP Approved by U.S. EPA
QAPP Reference
|
|
Line of Evidence (LOE) for Decision ID 169301, Benthic Community Effects
|
Region 1 |
Klamath River HU, Shasta River HA |
|
|
LOE ID: |
32858 |
|
Pollutant: |
Temperature, water |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
None |
|
Beneficial Use: |
Cold Freshwater Habitat |
|
Number of Samples: |
1 |
Number of Exceedances: |
1 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
One of one annual maximum temperature in the Shasta River exceeded the evaluation guideline. The annual maximum temperature in 2008 was 28.2 degrees C. The annual maximum temperature in 2009 at this site could not be determined, as the data did not include late July/early August when the highest annual temperatures generally occur. |
Data Reference: |
Data for Various Pollutants in the Shasta Valley Resource Convservation District, 2008-2009. |
|
SWAMP Data: |
Non-SWAMP |
|
Water Quality Objective/Criterion: |
Water Quality Control Plan, North Coast Region (NCRWQCB 2011): Natural receiving water temperature of intrastate waters shall not be altered unless it can be demonstrated to the satisfaction of the Regional Water Board that such alteration in temperature does not adversely affect beneficial uses. At no time or place shall the temperature of any COLD water be increased more than 5 degrees Fahrenheit (F) above natural receiving water temperature. |
Objective/Criterion Reference: |
Water Quality Control Plan (Basin Plan) for the North Coast Region |
|
Evaluation Guideline: |
According to the Shasta River TMDL, at River Mile (RM) 10.9 an annual maximum water temperature of 17.3 degrees C in the mainstem Shasta River is consistent with the "Water Quality Compliance Scenario", which includes 1) site potential riparian shade conditions on a river-reach scale, 2) modified temperature regime of tailwater return flows such that the return flows do not cause heating of the receiving water, 3) Big Springs Creek temperatures reduced by 4 degrees C from baseline, 4) Parks Creek temperatures reduced by 2 degrees C from baseline, and 5) 50% increase in Shasta River flows downstream of the Big Springs Creek confluence (an increase of 45 cfs). The maximum temperature value for RM 10.9 of the Shasta River is an estimate extrapolated from the Shasta River temperature TMDL model's water quality compliance scenario (Figure 6.3 in the Staff Report for the Action Plan for the Shasta River Watershed Dissolved Oxygen and Temperature TMDLs) (NCRWQCB 2006)." |
Guideline Reference: |
Staff Report for the Action Plan for the Shasta River Watershed Temperature and Dissolved Oxygen Total Maximum Daily Loads |
|
Spatial Representation: |
Continuous data were collected at one location on the Shasta River at site 105SRA01T. |
Temporal Representation: |
Data were collected hourly from April - September 2008. |
Environmental Conditions: |
|
QAPP Information: |
Quality Assurance Project Plan for the 'Araujo Diversion Removal Project' Prepared by: Amy Hansen Shasta Valley Resource Conservation District July 30, 2007. |
QAPP Information Reference(s): |
Quality Assurance Project Plan for the Shasta Water Association Dam Demobilization and Water Quality Improvements Project, Version Number 1.0 and for the Araujo Diversion Removal Project, Version Number 1.0. |
|
Line of Evidence (LOE) for Decision ID 169301, Benthic Community Effects
|
Region 1 |
Klamath River HU, Shasta River HA |
|
|
LOE ID: |
326936 |
|
Pollutant: |
Temperature, water |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
None |
|
Beneficial Use: |
Cold Freshwater Habitat |
|
Number of Samples: |
25 |
Number of Exceedances: |
2 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP RWB1 Monitoring data for Klamath River HU, Shasta River HA to determine beneficial use support and results are as follows: 2 of 25 samples exceeded the water quality threshold for Temperature. |
Data Reference: |
Benthic, Field, Habitat, Tissue, Toxicity, WQ from the Surface Water Ambient Monitoring Program for the 2026 Integrated Report in Region 1 |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
Natural receiving water temperature of intrastate waters shall not be altered unless it can be demonstrated to the satisfaction of the Regional Water Board that such alteration in temperature does not adversely affect beneficial uses. At no time or place shall the temperature of any COLD water be increased more than 5 degrees Fahrenheit (F) above natural receiving water temperature (Basin Plan, North Coast Region). |
Objective/Criterion Reference: |
Water Quality Control Plan (Basin Plan) for the North Coast Region |
|
Evaluation Guideline: |
According to Carter (2008) the lethal temperature evaluation guideline for salmonid spawning, egg incubation & fry emergence is 20C. |
Guideline Reference: |
Effects of Temperature, Dissolved Oxygen/Total Dissolved Gas, Ammonia, and pH on Salmonids. Implications for California's North Coast TMDLs. California Regional Water Quality Control Board, North Coast Region |
|
Spatial Representation: |
The samples were collected at 1 monitoring site: 105PO0001 (Parks Creek Overflow at Big Springs Road Crossing). |
Temporal Representation: |
The samples were collected between the dates of 2021-04-08 and 2021-10-28 |
Environmental Conditions: |
|
QAPP Information: |
QAPP for Surface Water Ambient Monitoring Program (SWAMP) |
QAPP Information Reference(s): |
Generic SWAMP QAPrP |
|
Line of Evidence (LOE) for Decision ID 169301, Benthic Community Effects
|
Region 1 |
Klamath River HU, Shasta River HA |
|
|
LOE ID: |
31698 |
|
Pollutant: |
Temperature, water |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
None |
|
Beneficial Use: |
Cold Freshwater Habitat |
|
Number of Samples: |
6 |
Number of Exceedances: |
6 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Six of six annual maximum temperatures in the Shasta River exceeded the evaluation guideline. The annual maximum temperature in 2008 & 2009 at sites 105SRA1DO (RM 13.6), site 105SRA2DO (RM 13.6), and site 105SRA3DO (RM 13.5) ranged from 27.1 to 28.7 degrees C. |
Data Reference: |
Data for Various Pollutants in the Shasta Valley Resource Convservation District, 2008-2009. |
|
SWAMP Data: |
Non-SWAMP |
|
Water Quality Objective/Criterion: |
Water Quality Control Plan, North Coast Region (NCRWQCB 2011): Natural receiving water temperature of intrastate waters shall not be altered unless it can be demonstrated to the satisfaction of the Regional Water Board that such alteration in temperature does not adversely affect beneficial uses. At no time or place shall the temperature of any COLD water be increased more than 5 degrees Fahrenheit (F) above natural receiving water temperature. |
Objective/Criterion Reference: |
Water Quality Control Plan (Basin Plan) for the North Coast Region |
|
Evaluation Guideline: |
According to the Shasta River TMDL, at River Mile (RM) 13.6 and 13.5 an annual maximum water temperature of 17.9 degrees C in the mainstem Shasta River is consistent with the "Water Quality Compliance Scenario", which includes 1) site potential riparian shade conditions on a river-reach scale, 2) modified temperature regime of tailwater return flows such that the return flows do not cause heating of the receiving water, 3) Big Springs Creek temperatures reduced by 4 degrees C from baseline, 4) Parks Creek temperatures reduced by 2 degrees C from baseline, and 5) 50% increase in Shasta River flows downstream of the Big Springs Creek confluence (an increase of 45 cfs). The maximum temperature value for RM 13.6 & 13.5 of the Shasta River is an estimate extrapolated from the Shasta River temperature TMDL model's water quality compliance scenario (Figure 6.3 in the Staff Report for the Action Plan for the Shasta River Watershed Dissolved Oxygen and Temperature TMDLs) (NCRWQCB 2006)." |
Guideline Reference: |
Staff Report for the Action Plan for the Shasta River Watershed Temperature and Dissolved Oxygen Total Maximum Daily Loads |
|
Spatial Representation: |
Continuous data were collected at three locations on the Shasta River: 1) downstream dam site (105SRA1DO) , 2) upstream dam site (105SRA2DO), and upstream pump/screen (105SRA3DO). |
Temporal Representation: |
Data were collected hourly from March - September in 2008 & 2009. |
Environmental Conditions: |
|
QAPP Information: |
Quality Assurance Project Plan for the 'Araujo Diversion Removal Project' Prepared by: Amy Hansen Shasta Valley Resource Conservation District July 30, 2007. |
QAPP Information Reference(s): |
Quality Assurance Project Plan for the Shasta Water Association Dam Demobilization and Water Quality Improvements Project, Version Number 1.0 and for the Araujo Diversion Removal Project, Version Number 1.0. |
|
Line of Evidence (LOE) for Decision ID 169301, Benthic Community Effects
|
Region 1 |
Klamath River HU, Shasta River HA |
|
|
LOE ID: |
32837 |
|
Pollutant: |
Temperature, water |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
None |
|
Beneficial Use: |
Cold Freshwater Habitat |
|
Number of Samples: |
2 |
Number of Exceedances: |
2 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Two of two annual maximum temperatures in the Shasta River exceeded the evaluation guideline. The annual maximum temperature in 2008 was 25.2 degrees C, and in 2009 was 25.5 degrees C. |
Data Reference: |
Data for Various Pollutants in the Shasta Valley Resource Convservation District, 2008-2009. |
|
SWAMP Data: |
Non-SWAMP |
|
Water Quality Objective/Criterion: |
Water Quality Control Plan, North Coast Region (NCRWQCB 2011): Natural receiving water temperature of intrastate waters shall not be altered unless it can be demonstrated to the satisfaction of the Regional Water Board that such alteration in temperature does not adversely affect beneficial uses. At no time or place shall the temperature of any COLD water be increased more than 5 degrees Fahrenheit (F) above natural receiving water temperature. |
Objective/Criterion Reference: |
Water Quality Control Plan (Basin Plan) for the North Coast Region |
|
Evaluation Guideline: |
According to the Shasta River TMDL, at River Mile (RM) 23.6 an annual maximum water temperature of 17.7 degrees C in the mainstem Shasta River is consistent with the "Water Quality Compliance Scenario", which includes 1) site potential riparian shade conditions on a river-reach scale, 2) modified temperature regime of tailwater return flows such that the return flows do not cause heating of the receiving water, 3) Big Springs Creek temperatures reduced by 4 degrees C from baseline, 4) Parks Creek temperatures reduced by 2 degrees C from baseline, and 5) 50% increase in Shasta River flows downstream of the Big Springs Creek confluence (an increase of 45 cfs). The maximum temperature value for RM 23.2 of the Shasta River is an estimate extrapolated from the Shasta River temperature TMDL model's water quality compliance scenario (Figure 6.3 in the Staff Report for the Action Plan for the Shasta River Watershed Dissolved Oxygen and Temperature TMDLs) (NCRWQCB 2006)." |
Guideline Reference: |
Staff Report for the Action Plan for the Shasta River Watershed Temperature and Dissolved Oxygen Total Maximum Daily Loads |
|
Spatial Representation: |
Continuous data were collected at one location on the Shasta River at site 105SRS02T. |
Temporal Representation: |
Data were collected hourly from April - September 2008 and March - September 2009. |
Environmental Conditions: |
|
QAPP Information: |
Quality Assurance Project Plan for the 'Shasta Water Association Dam Demobilization and Water Quality Improvements Project' Prepared by: Amy Hansen Shasta Valley Resource Conservation District May 21, 2007 Version Number 1.0 |
QAPP Information Reference(s): |
Quality Assurance Project Plan for the Shasta Water Association Dam Demobilization and Water Quality Improvements Project, Version Number 1.0 and for the Araujo Diversion Removal Project, Version Number 1.0. |
|
Line of Evidence (LOE) for Decision ID 169301, Benthic Community Effects
|
Region 1 |
Klamath River HU, Shasta River HA |
|
|
LOE ID: |
32816 |
|
Pollutant: |
Temperature, water |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
None |
|
Beneficial Use: |
Cold Freshwater Habitat |
|
Number of Samples: |
1 |
Number of Exceedances: |
1 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
One of one annual maximum temperature in the Shasta River exceeded the evaluation guideline. The annual maximum temperature in 2009 was 25.6 degrees C. The annual maximum temperature in 2008 at this site could not be determined, as the data did not include late July/early August when the highest annual temperatures generally occur. |
Data Reference: |
Data for Various Pollutants in the Shasta Valley Resource Convservation District, 2008-2009. |
|
SWAMP Data: |
Non-SWAMP |
|
Water Quality Objective/Criterion: |
Water Quality Control Plan, North Coast Region (NCRWQCB 2011): Natural receiving water temperature of intrastate waters shall not be altered unless it can be demonstrated to the satisfaction of the Regional Water Board that such alteration in temperature does not adversely affect beneficial uses. At no time or place shall the temperature of any COLD water be increased more than 5 degrees Fahrenheit (F) above natural receiving water temperature. |
Objective/Criterion Reference: |
Water Quality Control Plan (Basin Plan) for the North Coast Region |
|
Evaluation Guideline: |
According to the Shasta River TMDL, at River Mile (RM) 18.7 an annual maximum water temperature of 18.4 degrees C in the mainstem Shasta River is consistent with the "Water Quality Compliance Scenario", which includes 1) site potential riparian shade conditions on a river-reach scale, 2) modified temperature regime of tailwater return flows such that the return flows do not cause heating of the receiving water, 3) Big Springs Creek temperatures reduced by 4 degrees C from baseline, 4) Parks Creek temperatures reduced by 2 degrees C from baseline, and 5) 50% increase in Shasta River flows downstream of the Big Springs Creek confluence (an increase of 45 cfs). The maximum temperature value for RM 18.7 of the Shasta River is an estimate extrapolated from the Shasta River temperature TMDL model's water quality compliance scenario (Figure 6.3 in the Staff Report for the Action Plan for the Shasta River Watershed Dissolved Oxygen and Temperature TMDLs) (NCRWQCB 2006)." |
Guideline Reference: |
Staff Report for the Action Plan for the Shasta River Watershed Temperature and Dissolved Oxygen Total Maximum Daily Loads |
|
Spatial Representation: |
Continuous data were collected at one location on the Shasta River at site 105SRS4DO. |
Temporal Representation: |
Data were collected hourly from March - September 2009. |
Environmental Conditions: |
|
QAPP Information: |
Quality Assurance Project Plan for the 'Shasta Water Association Dam Demobilization and Water Quality Improvements Project' Prepared by: Amy Hansen Shasta Valley Resource Conservation District May 21, 2007 Version Number 1.0 |
QAPP Information Reference(s): |
Quality Assurance Project Plan for the Shasta Water Association Dam Demobilization and Water Quality Improvements Project, Version Number 1.0 and for the Araujo Diversion Removal Project, Version Number 1.0. |
|
Line of Evidence (LOE) for Decision ID 169301, Benthic Community Effects
|
Region 1 |
Klamath River HU, Shasta River HA |
|
|
LOE ID: |
32817 |
|
Pollutant: |
Temperature, water |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
None |
|
Beneficial Use: |
Cold Freshwater Habitat |
|
Number of Samples: |
2 |
Number of Exceedances: |
2 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Two of two annual maximum temperatures in the Shasta River exceeded the evaluation guideline. The annual maximum temperature in 2008 was 25.0 degrees C, and in 2009 was 24.5 degrees C. |
Data Reference: |
Data for Various Pollutants in the Shasta Valley Resource Convservation District, 2008-2009. |
|
SWAMP Data: |
Non-SWAMP |
|
Water Quality Objective/Criterion: |
Water Quality Control Plan, North Coast Region (NCRWQCB 2011): Natural receiving water temperature of intrastate waters shall not be altered unless it can be demonstrated to the satisfaction of the Regional Water Board that such alteration in temperature does not adversely affect beneficial uses. At no time or place shall the temperature of any COLD water be increased more than 5 degrees Fahrenheit (F) above natural receiving water temperature. |
Objective/Criterion Reference: |
Water Quality Control Plan (Basin Plan) for the North Coast Region |
|
Evaluation Guideline: |
According to the Shasta River TMDL, at River Mile (RM) 21.2 an annual maximum water temperature of 17.9 degrees C in the mainstem Shasta River is consistent with the "Water Quality Compliance Scenario", which includes 1) site potential riparian shade conditions on a river-reach scale, 2) modified temperature regime of tailwater return flows such that the return flows do not cause heating of the receiving water, 3) Big Springs Creek temperatures reduced by 4 degrees C from baseline, 4) Parks Creek temperatures reduced by 2 degrees C from baseline, and 5) 50% increase in Shasta River flows downstream of the Big Springs Creek confluence (an increase of 45 cfs). The maximum temperature value for RM 21.2 of the Shasta River is an estimate extrapolated from the Shasta River temperature TMDL model's water quality compliance scenario (Figure 6.3 in the Staff Report for the Action Plan for the Shasta River Watershed Dissolved Oxygen and Temperature TMDLs) (NCRWQCB 2006)." |
Guideline Reference: |
Staff Report for the Action Plan for the Shasta River Watershed Temperature and Dissolved Oxygen Total Maximum Daily Loads |
|
Spatial Representation: |
Continuous data were collected at one location on the Shasta River at site 105SRS01T. |
Temporal Representation: |
Data were collected hourly from April - September 2008 and March - September 2009. |
Environmental Conditions: |
|
QAPP Information: |
Quality Assurance Project Plan for the 'Shasta Water Association Dam Demobilization and Water Quality Improvements Project' Prepared by: Amy Hansen Shasta Valley Resource Conservation District May 21, 2007 Version Number 1.0 |
QAPP Information Reference(s): |
Quality Assurance Project Plan for the Shasta Water Association Dam Demobilization and Water Quality Improvements Project, Version Number 1.0 and for the Araujo Diversion Removal Project, Version Number 1.0. |
|
Line of Evidence (LOE) for Decision ID 169301, Benthic Community Effects
|
Region 1 |
Klamath River HU, Shasta River HA |
|
|
LOE ID: |
43240 |
|
Pollutant: |
Temperature, water |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
None |
|
Beneficial Use: |
Cold Freshwater Habitat |
|
Number of Samples: |
2 |
Number of Exceedances: |
1 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP data for Klamath River HU, Shasta River HA to determine beneficial use support and results are as follows: 1 of 2 annual maximum temperatures in the Shasta River near Edgewood exceed the evaluation guideline for Water Temperature. A total of 4 grab samples were collected and annual maximum temperatures were calculated for each calendar year. |
Data Reference: |
RWB1 Trend Maintenance Periods FYs 2007 2008 |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
Water Quality Control Plan, North Coast Region (NCRWQCB 2011): Natural receiving water temperature of intrastate waters shall not be altered unless it can be demonstrated to the satisfaction of the Regional Water Board that such alteration in temperature does not adversely affect beneficial uses. At no time or place shall the temperature of any COLD water be increased more than 5 degrees Fahrenheit (F) above natural receiving water temperature. |
Objective/Criterion Reference: |
Water Quality Control Plan (Basin Plan) for the North Coast Region |
|
Evaluation Guideline: |
Per "Effects of Temperature, Dissolved Oxygen/Total Dissolved Gas, Ammonia, and pH on Salmonids" (Carter 2008): The lethal temperature evaluation guideline for both steelhead adult migration & holding and juvenile growth & rearing of 24°C applies in the Shasta River above Lake Shastina July - September 15th. The lethal temperature evaluation guideline for salmonid spawning, egg incubation & fry emergence is 20C and applies September 16th - June. See LOE ID 31510 for more information on natural temperature alterations and salmonid presence and periodicity in this water body. |
Guideline Reference: |
Effects of Temperature, Dissolved Oxygen/Total Dissolved Gas, Ammonia, and pH on Salmonids. Implications for California's North Coast TMDLs. California Regional Water Quality Control Board, North Coast Region |
|
Spatial Representation: |
Data for this line of evidence for Klamath River HU, Shasta River HA was collected at 1 monitoring site [ Shasta River near Edgewood - 105SHAEDG] |
Temporal Representation: |
Data was collected over the time period 11/15/2007-7/16/2008. |
Environmental Conditions: |
Staff is not aware of any special conditions that might affect interpretation of the data. |
QAPP Information: |
The SWAMP QAPP (2008) was followed. |
QAPP Information Reference(s): |
Surface Water Ambient Monitoring Program Quality Assurance Program Plan |
|
Line of Evidence (LOE) for Decision ID 169301, Benthic Community Effects
|
Region 1 |
Klamath River HU, Shasta River HA |
|
|
LOE ID: |
32838 |
|
Pollutant: |
Temperature, water |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
None |
|
Beneficial Use: |
Cold Freshwater Habitat |
|
Number of Samples: |
2 |
Number of Exceedances: |
2 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Two of two annual maximum temperature in the Shasta River exceeded the evaluation guideline. The annual maximum temperature in 2008 was 27.5 degrees C and in 2009 was 28.7 degrees C. |
Data Reference: |
Data for Various Pollutants in the Shasta Valley Resource Convservation District, 2008-2009. |
|
SWAMP Data: |
Non-SWAMP |
|
Water Quality Objective/Criterion: |
Water Quality Control Plan, North Coast Region (NCRWQCB 2011): Natural receiving water temperature of intrastate waters shall not be altered unless it can be demonstrated to the satisfaction of the Regional Water Board that such alteration in temperature does not adversely affect beneficial uses. At no time or place shall the temperature of any COLD water be increased more than 5 degrees Fahrenheit (F) above natural receiving water temperature. |
Objective/Criterion Reference: |
Water Quality Control Plan (Basin Plan) for the North Coast Region |
|
Evaluation Guideline: |
According to the Shasta River TMDL, at River Mile (RM) 13.2 an annual maximum water temperature of 17.6 degrees C in the mainstem Shasta River is consistent with the "Water Quality Compliance Scenario", which includes 1) site potential riparian shade conditions on a river-reach scale, 2) modified temperature regime of tailwater return flows such that the return flows do not cause heating of the receiving water, 3) Big Springs Creek temperatures reduced by 4 degrees C from baseline, 4) Parks Creek temperatures reduced by 2 degrees C from baseline, and 5) 50% increase in Shasta River flows downstream of the Big Springs Creek confluence (an increase of 45 cfs). The maximum temperature value for RM 13.2 of the Shasta River is an estimate extrapolated from the Shasta River temperature TMDL model's water quality compliance scenario (Figure 6.3 in the Staff Report for the Action Plan for the Shasta River Watershed Dissolved Oxygen and Temperature TMDLs) (NCRWQCB 2006)." |
Guideline Reference: |
Staff Report for the Action Plan for the Shasta River Watershed Temperature and Dissolved Oxygen Total Maximum Daily Loads |
|
Spatial Representation: |
Continuous data were collected at one location on the Shasta River at site 105SRA4DO. |
Temporal Representation: |
Data were collected hourly from March - September 2008 & 2009. |
Environmental Conditions: |
|
QAPP Information: |
Quality Assurance Project Plan for the 'Araujo Diversion Removal Project' Prepared by: Amy Hansen Shasta Valley Resource Conservation District July 30, 2007. |
QAPP Information Reference(s): |
Quality Assurance Project Plan for the Shasta Water Association Dam Demobilization and Water Quality Improvements Project, Version Number 1.0 and for the Araujo Diversion Removal Project, Version Number 1.0. |
|
Line of Evidence (LOE) for Decision ID 157122, Oxygen, Dissolved
|
Region 1 |
Klamath River HU, Shasta River HA |
|
|
LOE ID: |
326204 |
|
Pollutant: |
Oxygen, Dissolved |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
None |
|
Beneficial Use: |
Fish Spawning |
|
Number of Samples: |
24 |
Number of Exceedances: |
12 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP RWB1 Monitoring data for Klamath River HU, Shasta River HA to determine beneficial use support and results are as follows: 12 of 24 samples exceeded the water quality threshold for Oxygen, Dissolved. |
Data Reference: |
Benthic, Field, Habitat, Tissue, Toxicity, WQ from the Surface Water Ambient Monitoring Program for the 2026 Integrated Report in Region 1 |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
Water Quality Control Plan, North Coast Basin, Chapter III, General Objectives for all Inland Surface Waters, Enclosed Bays and Estuaries states: Dissolved oxygen concentrations shall conform to those limits listed in Section 3.3.5. Section 3.3.5 lists dissolved oxygen concentration limits for SPAWN beneficial use waters to be a daily minimum of 9.0 mg/L and a 7-day moving average of 11.0 mg/L. |
Objective/Criterion Reference: |
Water Quality Control Plan (Basin Plan) for the North Coast Region |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
The samples were collected at 1 monitoring site: 105SH6418 (Shasta River upstream Parks Creek). |
Temporal Representation: |
The samples were collected between the dates of 2021-04-08 and 2021-10-28 |
Environmental Conditions: |
|
QAPP Information: |
QAPP for Surface Water Ambient Monitoring Program (SWAMP) |
QAPP Information Reference(s): |
Generic SWAMP QAPrP |
|
Line of Evidence (LOE) for Decision ID 157122, Oxygen, Dissolved
|
Region 1 |
Klamath River HU, Shasta River HA |
|
|
LOE ID: |
326207 |
|
Pollutant: |
Oxygen, Dissolved |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
None |
|
Beneficial Use: |
Fish Spawning |
|
Number of Samples: |
1 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP Perennial Stream Surveys data for Klamath River HU, Shasta River HA to determine beneficial use support and results are as follows: 0 of 1 samples exceeded the water quality threshold for Oxygen, Dissolved. |
Data Reference: |
Benthic, Field, Habitat, WQ from the Surface Water Ambient Monitoring Program for the 2026 Integrated Report in Region 1 |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
Water Quality Control Plan, North Coast Basin, Chapter III, General Objectives for all Inland Surface Waters, Enclosed Bays and Estuaries states: Dissolved oxygen concentrations shall conform to those limits listed in Section 3.3.5. Section 3.3.5 lists dissolved oxygen concentration limits for SPAWN beneficial use waters to be a daily minimum of 9.0 mg/L and a 7-day moving average of 11.0 mg/L. |
Objective/Criterion Reference: |
Water Quality Control Plan (Basin Plan) for the North Coast Region |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
The samples were collected at 1 monitoring site: 105PS0295 (Shasta River ~1mi above Cooley Gulch). |
Temporal Representation: |
The samples were collected between the dates of 2016-06-15 and 2016-06-15 |
Environmental Conditions: |
|
QAPP Information: |
QAPP for Surface Water Ambient Monitoring Program (SWAMP) |
QAPP Information Reference(s): |
Generic SWAMP QAPrP |
|
Line of Evidence (LOE) for Decision ID 157122, Oxygen, Dissolved
|
Region 1 |
Klamath River HU, Shasta River HA |
|
|
LOE ID: |
326217 |
|
Pollutant: |
Oxygen, Dissolved |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
None |
|
Beneficial Use: |
Fish Spawning |
|
Number of Samples: |
6 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP RWB1 Monitoring data for Klamath River HU, Shasta River HA to determine beneficial use support and results are as follows: 0 of 6 samples exceeded the water quality threshold for Oxygen, Dissolved. |
Data Reference: |
Benthic, Field, Habitat, Tissue, Toxicity, WQ from the Surface Water Ambient Monitoring Program for the 2026 Integrated Report in Region 1 |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
Water Quality Control Plan, North Coast Basin, Chapter III, General Objectives for all Inland Surface Waters, Enclosed Bays and Estuaries states: Dissolved oxygen concentrations shall conform to those limits listed in Section 3.3.5. Section 3.3.5 lists dissolved oxygen concentration limits for SPAWN beneficial use waters to be a daily minimum of 9.0 mg/L and a 7-day moving average of 11.0 mg/L. |
Objective/Criterion Reference: |
Water Quality Control Plan (Basin Plan) for the North Coast Region |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
The samples were collected at 1 monitoring site: 105LS9999 (Little Springs Creek at Spring Head). |
Temporal Representation: |
The samples were collected between the dates of 2021-04-15 and 2021-05-20 |
Environmental Conditions: |
|
QAPP Information: |
QAPP for Surface Water Ambient Monitoring Program (SWAMP) |
QAPP Information Reference(s): |
Generic SWAMP QAPrP |
|
Line of Evidence (LOE) for Decision ID 157122, Oxygen, Dissolved
|
Region 1 |
Klamath River HU, Shasta River HA |
|
|
LOE ID: |
326228 |
|
Pollutant: |
Oxygen, Dissolved |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
None |
|
Beneficial Use: |
Fish Spawning |
|
Number of Samples: |
22 |
Number of Exceedances: |
10 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP RWB1 Monitoring data for Klamath River HU, Shasta River HA to determine beneficial use support and results are as follows: 10 of 22 samples exceeded the water quality threshold for Oxygen, Dissolved. |
Data Reference: |
Benthic, Field, Habitat, Tissue, Toxicity, WQ from the Surface Water Ambient Monitoring Program for the 2026 Integrated Report in Region 1 |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
Water Quality Control Plan, North Coast Basin, Chapter III, General Objectives for all Inland Surface Waters, Enclosed Bays and Estuaries states: Dissolved oxygen concentrations shall conform to those limits listed in Section 3.3.5. Section 3.3.5 lists dissolved oxygen concentration limits for SPAWN beneficial use waters to be a daily minimum of 9.0 mg/L and a 7-day moving average of 11.0 mg/L. |
Objective/Criterion Reference: |
Water Quality Control Plan (Basin Plan) for the North Coast Region |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
The samples were collected at 1 monitoring site: 105SH6389 (Shasta River downstream Parks Creek). |
Temporal Representation: |
The samples were collected between the dates of 2021-04-08 and 2021-10-21 |
Environmental Conditions: |
|
QAPP Information: |
QAPP for Surface Water Ambient Monitoring Program (SWAMP) |
QAPP Information Reference(s): |
Generic SWAMP QAPrP |
|
Line of Evidence (LOE) for Decision ID 157122, Oxygen, Dissolved
|
Region 1 |
Klamath River HU, Shasta River HA |
|
|
LOE ID: |
326249 |
|
Pollutant: |
Oxygen, Dissolved |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
None |
|
Beneficial Use: |
Fish Spawning |
|
Number of Samples: |
25 |
Number of Exceedances: |
17 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP RWB1 Monitoring data for Klamath River HU, Shasta River HA to determine beneficial use support and results are as follows: 17 of 25 samples exceeded the water quality threshold for Oxygen, Dissolved. |
Data Reference: |
Benthic, Field, Habitat, Tissue, Toxicity, WQ from the Surface Water Ambient Monitoring Program for the 2026 Integrated Report in Region 1 |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
Water Quality Control Plan, North Coast Basin, Chapter III, General Objectives for all Inland Surface Waters, Enclosed Bays and Estuaries states: Dissolved oxygen concentrations shall conform to those limits listed in Section 3.3.5. Section 3.3.5 lists dissolved oxygen concentration limits for SPAWN beneficial use waters to be a daily minimum of 9.0 mg/L and a 7-day moving average of 11.0 mg/L. |
Objective/Criterion Reference: |
Water Quality Control Plan (Basin Plan) for the North Coast Region |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
The samples were collected at 1 monitoring site: 105PO0001 (Parks Creek Overflow at Big Springs Road Crossing). |
Temporal Representation: |
The samples were collected between the dates of 2021-04-08 and 2021-10-28 |
Environmental Conditions: |
|
QAPP Information: |
QAPP for Surface Water Ambient Monitoring Program (SWAMP) |
QAPP Information Reference(s): |
Generic SWAMP QAPrP |
|
Line of Evidence (LOE) for Decision ID 157122, Oxygen, Dissolved
|
Region 1 |
Klamath River HU, Shasta River HA |
|
|
LOE ID: |
326254 |
|
Pollutant: |
Oxygen, Dissolved |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
None |
|
Beneficial Use: |
Fish Spawning |
|
Number of Samples: |
17 |
Number of Exceedances: |
2 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP RWB1 Monitoring data for Klamath River HU, Shasta River HA to determine beneficial use support and results are as follows: 2 of 17 samples exceeded the water quality threshold for Oxygen, Dissolved. |
Data Reference: |
Benthic, Field, Habitat, Tissue, Toxicity, WQ from the Surface Water Ambient Monitoring Program for the 2026 Integrated Report in Region 1 |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
Water Quality Control Plan, North Coast Basin, Chapter III, General Objectives for all Inland Surface Waters, Enclosed Bays and Estuaries states: Dissolved oxygen concentrations shall conform to those limits listed in Section 3.3.5. Section 3.3.5 lists dissolved oxygen concentration limits for SPAWN beneficial use waters to be a daily minimum of 9.0 mg/L and a 7-day moving average of 11.0 mg/L. |
Objective/Criterion Reference: |
Water Quality Control Plan (Basin Plan) for the North Coast Region |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
The samples were collected at 1 monitoring site: 105LS9900 (Little Springs Creek at Outlet Works). |
Temporal Representation: |
The samples were collected between the dates of 2021-06-03 and 2021-10-28 |
Environmental Conditions: |
|
QAPP Information: |
QAPP for Surface Water Ambient Monitoring Program (SWAMP) |
QAPP Information Reference(s): |
Generic SWAMP QAPrP |
|
Line of Evidence (LOE) for Decision ID 157122, Oxygen, Dissolved
|
Region 1 |
Klamath River HU, Shasta River HA |
|
|
LOE ID: |
326173 |
|
Pollutant: |
Oxygen, Dissolved |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
None |
|
Beneficial Use: |
Warm Freshwater Habitat |
|
Number of Samples: |
17 |
Number of Exceedances: |
1 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP RWB1 Monitoring data for Klamath River HU, Shasta River HA to determine beneficial use support and results are as follows: 1 of 17 samples exceeded the water quality threshold for Oxygen, Dissolved. |
Data Reference: |
Benthic, Field, Habitat, Tissue, Toxicity, WQ from the Surface Water Ambient Monitoring Program for the 2026 Integrated Report in Region 1 |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
Water Quality Control Plan, North Coast Basin, Chapter III, General Objectives for all Inland Surface Waters, Enclosed Bays and Estuaries states: Dissolved oxygen concentrations shall conform to those limits listed in Section 3.3.5. Section 3.3.5 lists dissolved oxygen concentration limits for WARM beneficial use waters to be a daily minimum of 5.0 mg/L and a 7-day moving average of 6.0 mg/L. |
Objective/Criterion Reference: |
Water Quality Control Plan (Basin Plan) for the North Coast Region |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
The samples were collected at 1 monitoring site: 105LS9900 (Little Springs Creek at Outlet Works). |
Temporal Representation: |
The samples were collected between the dates of 2021-06-03 and 2021-10-28 |
Environmental Conditions: |
|
QAPP Information: |
QAPP for Surface Water Ambient Monitoring Program (SWAMP) |
QAPP Information Reference(s): |
Generic SWAMP QAPrP |
|
Line of Evidence (LOE) for Decision ID 157122, Oxygen, Dissolved
|
Region 1 |
Klamath River HU, Shasta River HA |
|
|
LOE ID: |
326092 |
|
Pollutant: |
Oxygen, Dissolved |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
None |
|
Beneficial Use: |
Warm Freshwater Habitat |
|
Number of Samples: |
24 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP RWB1 Monitoring data for Klamath River HU, Shasta River HA to determine beneficial use support and results are as follows: 0 of 24 samples exceeded the water quality threshold for Oxygen, Dissolved. |
Data Reference: |
Benthic, Field, Habitat, Tissue, Toxicity, WQ from the Surface Water Ambient Monitoring Program for the 2026 Integrated Report in Region 1 |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
Water Quality Control Plan, North Coast Basin, Chapter III, General Objectives for all Inland Surface Waters, Enclosed Bays and Estuaries states: Dissolved oxygen concentrations shall conform to those limits listed in Section 3.3.5. Section 3.3.5 lists dissolved oxygen concentration limits for WARM beneficial use waters to be a daily minimum of 5.0 mg/L and a 7-day moving average of 6.0 mg/L. |
Objective/Criterion Reference: |
Water Quality Control Plan (Basin Plan) for the North Coast Region |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
The samples were collected at 1 monitoring site: 105PC0001 (Parks Creek at Shasta River). |
Temporal Representation: |
The samples were collected between the dates of 2021-04-08 and 2021-10-28 |
Environmental Conditions: |
|
QAPP Information: |
QAPP for Surface Water Ambient Monitoring Program (SWAMP) |
QAPP Information Reference(s): |
Generic SWAMP QAPrP |
|
Line of Evidence (LOE) for Decision ID 157122, Oxygen, Dissolved
|
Region 1 |
Klamath River HU, Shasta River HA |
|
|
LOE ID: |
326102 |
|
Pollutant: |
Oxygen, Dissolved |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
None |
|
Beneficial Use: |
Warm Freshwater Habitat |
|
Number of Samples: |
1 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP Reference Condition Management Plan data for Klamath River HU, Shasta River HA to determine beneficial use support and results are as follows: 0 of 1 samples exceeded the water quality threshold for Oxygen, Dissolved. |
Data Reference: |
Benthic, Field, Habitat, WQ from the Surface Water Ambient Monitoring Program for the 2026 Integrated Report in Region 1 |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
Water Quality Control Plan, North Coast Basin, Chapter III, General Objectives for all Inland Surface Waters, Enclosed Bays and Estuaries states: Dissolved oxygen concentrations shall conform to those limits listed in Section 3.3.5. Section 3.3.5 lists dissolved oxygen concentration limits for WARM beneficial use waters to be a daily minimum of 5.0 mg/L and a 7-day moving average of 6.0 mg/L. |
Objective/Criterion Reference: |
Water Quality Control Plan (Basin Plan) for the North Coast Region |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
The samples were collected at 1 monitoring site: 105WE0592 (Eddy Creek ~0.8 miles downstream from end of 4WD road.). |
Temporal Representation: |
The samples were collected between the dates of 2015-07-13 and 2015-07-13 |
Environmental Conditions: |
|
QAPP Information: |
QAPP for Surface Water Ambient Monitoring Program (SWAMP) |
QAPP Information Reference(s): |
Generic SWAMP QAPrP |
|
Line of Evidence (LOE) for Decision ID 157122, Oxygen, Dissolved
|
Region 1 |
Klamath River HU, Shasta River HA |
|
|
LOE ID: |
326137 |
|
Pollutant: |
Oxygen, Dissolved |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
None |
|
Beneficial Use: |
Warm Freshwater Habitat |
|
Number of Samples: |
6 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP RWB1 Monitoring data for Klamath River HU, Shasta River HA to determine beneficial use support and results are as follows: 0 of 6 samples exceeded the water quality threshold for Oxygen, Dissolved. |
Data Reference: |
Benthic, Field, Habitat, Tissue, Toxicity, WQ from the Surface Water Ambient Monitoring Program for the 2026 Integrated Report in Region 1 |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
Water Quality Control Plan, North Coast Basin, Chapter III, General Objectives for all Inland Surface Waters, Enclosed Bays and Estuaries states: Dissolved oxygen concentrations shall conform to those limits listed in Section 3.3.5. Section 3.3.5 lists dissolved oxygen concentration limits for WARM beneficial use waters to be a daily minimum of 5.0 mg/L and a 7-day moving average of 6.0 mg/L. |
Objective/Criterion Reference: |
Water Quality Control Plan (Basin Plan) for the North Coast Region |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
The samples were collected at 1 monitoring site: 105LS9999 (Little Springs Creek at Spring Head). |
Temporal Representation: |
The samples were collected between the dates of 2021-04-15 and 2021-05-20 |
Environmental Conditions: |
|
QAPP Information: |
QAPP for Surface Water Ambient Monitoring Program (SWAMP) |
QAPP Information Reference(s): |
Generic SWAMP QAPrP |
|
Line of Evidence (LOE) for Decision ID 157122, Oxygen, Dissolved
|
Region 1 |
Klamath River HU, Shasta River HA |
|
|
LOE ID: |
328802 |
|
Pollutant: |
Oxygen, Dissolved |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
None |
|
Beneficial Use: |
Fish Spawning |
|
Number of Samples: |
26 |
Number of Exceedances: |
4 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed Karuk Tribe (Tribal) data for Klamath River HU, Shasta River HA to determine beneficial use support and results are as follows: 4 of 26 samples exceeded the water quality threshold for Oxygen, Dissolved. |
Data Reference: |
WQX from the NWQMP for the 2026 Integrated Report in Region 1 |
|
SWAMP Data: |
Non-SWAMP |
|
Water Quality Objective/Criterion: |
Water Quality Control Plan, North Coast Basin, Chapter III, General Objectives for all Inland Surface Waters, Enclosed Bays and Estuaries states: Dissolved oxygen concentrations shall conform to those limits listed in Section 3.3.5. Section 3.3.5 lists dissolved oxygen concentration limits for SPAWN beneficial use waters to be a daily minimum of 9.0 mg/L and a 7-day moving average of 11.0 mg/L. |
Objective/Criterion Reference: |
Water Quality Control Plan (Basin Plan) for the North Coast Region |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
The samples were collected at 1 monitoring site: KARUKDNR_WQX-SH (Shasta River). |
Temporal Representation: |
The samples were collected between the dates of 2011-04-28 and 2022-09-28 |
Environmental Conditions: |
|
QAPP Information: |
Karuk Tribe QA |
QAPP Information Reference(s): |
Data collected by a California Tribe QAPP Approved by U.S. EPA
QAPP Reference
|
|
Line of Evidence (LOE) for Decision ID 157122, Oxygen, Dissolved
|
Region 1 |
Klamath River HU, Shasta River HA |
|
|
LOE ID: |
328848 |
|
Pollutant: |
Oxygen, Dissolved |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
None |
|
Beneficial Use: |
Warm Freshwater Habitat |
|
Number of Samples: |
26 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed Karuk Tribe (Tribal) data for Klamath River HU, Shasta River HA to determine beneficial use support and results are as follows: 0 of 26 samples exceeded the water quality threshold for Oxygen, Dissolved. |
Data Reference: |
WQX from the NWQMP for the 2026 Integrated Report in Region 1 |
|
SWAMP Data: |
Non-SWAMP |
|
Water Quality Objective/Criterion: |
Water Quality Control Plan, North Coast Basin, Chapter III, General Objectives for all Inland Surface Waters, Enclosed Bays and Estuaries states: Dissolved oxygen concentrations shall conform to those limits listed in Section 3.3.5. Section 3.3.5 lists dissolved oxygen concentration limits for WARM beneficial use waters to be a daily minimum of 5.0 mg/L and a 7-day moving average of 6.0 mg/L. |
Objective/Criterion Reference: |
Water Quality Control Plan (Basin Plan) for the North Coast Region |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
The samples were collected at 1 monitoring site: KARUKDNR_WQX-SH (Shasta River). |
Temporal Representation: |
The samples were collected between the dates of 2011-04-28 and 2022-09-28 |
Environmental Conditions: |
|
QAPP Information: |
Karuk Tribe QA |
QAPP Information Reference(s): |
Data collected by a California Tribe QAPP Approved by U.S. EPA
QAPP Reference
|
|
Line of Evidence (LOE) for Decision ID 157122, Oxygen, Dissolved
|
Region 1 |
Klamath River HU, Shasta River HA |
|
|
LOE ID: |
328782 |
|
Pollutant: |
Oxygen, Dissolved |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
None |
|
Beneficial Use: |
Cold Freshwater Habitat |
|
Number of Samples: |
26 |
Number of Exceedances: |
1 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed Karuk Tribe (Tribal) data for Klamath River HU, Shasta River HA to determine beneficial use support and results are as follows: 1 of 26 samples exceeded the water quality threshold for Oxygen, Dissolved. |
Data Reference: |
WQX from the NWQMP for the 2026 Integrated Report in Region 1 |
|
SWAMP Data: |
Non-SWAMP |
|
Water Quality Objective/Criterion: |
Water Quality Control Plan, North Coast Basin, Chapter III, General Objectives for all Inland Surface Waters, Enclosed Bays and Estuaries states: Dissolved oxygen concentrations shall conform to those limits listed in Section 3.3.5. Section 3.3.5 lists dissolved oxygen concentration limits for COLD beneficial use waters to be a daily minimum of 6.0 mg/L and a 7-day moving average of 8.0 mg/L. |
Objective/Criterion Reference: |
Water Quality Control Plan (Basin Plan) for the North Coast Region |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
The samples were collected at 1 monitoring site: KARUKDNR_WQX-SH (Shasta River). |
Temporal Representation: |
The samples were collected between the dates of 2011-04-28 and 2022-09-28 |
Environmental Conditions: |
|
QAPP Information: |
Karuk Tribe QA |
QAPP Information Reference(s): |
Data collected by a California Tribe QAPP Approved by U.S. EPA
QAPP Reference
|
|
Line of Evidence (LOE) for Decision ID 157122, Oxygen, Dissolved
|
Region 1 |
Klamath River HU, Shasta River HA |
|
|
LOE ID: |
326202 |
|
Pollutant: |
Oxygen, Dissolved |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
None |
|
Beneficial Use: |
Cold Freshwater Habitat |
|
Number of Samples: |
24 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP RWB1 Monitoring data for Klamath River HU, Shasta River HA to determine beneficial use support and results are as follows: 0 of 24 samples exceeded the water quality threshold for Oxygen, Dissolved. |
Data Reference: |
Benthic, Field, Habitat, Tissue, Toxicity, WQ from the Surface Water Ambient Monitoring Program for the 2026 Integrated Report in Region 1 |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
Water Quality Control Plan, North Coast Basin, Chapter III, General Objectives for all Inland Surface Waters, Enclosed Bays and Estuaries states: Dissolved oxygen concentrations shall conform to those limits listed in Section 3.3.5. Section 3.3.5 lists dissolved oxygen concentration limits for COLD beneficial use waters to be a daily minimum of 6.0 mg/L and a 7-day moving average of 8.0 mg/L. |
Objective/Criterion Reference: |
Water Quality Control Plan (Basin Plan) for the North Coast Region |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
The samples were collected at 1 monitoring site: 105PC0001 (Parks Creek at Shasta River). |
Temporal Representation: |
The samples were collected between the dates of 2021-04-08 and 2021-10-28 |
Environmental Conditions: |
|
QAPP Information: |
QAPP for Surface Water Ambient Monitoring Program (SWAMP) |
QAPP Information Reference(s): |
Generic SWAMP QAPrP |
|
Line of Evidence (LOE) for Decision ID 157122, Oxygen, Dissolved
|
Region 1 |
Klamath River HU, Shasta River HA |
|
|
LOE ID: |
326226 |
|
Pollutant: |
Oxygen, Dissolved |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
None |
|
Beneficial Use: |
Cold Freshwater Habitat |
|
Number of Samples: |
6 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP RWB1 Monitoring data for Klamath River HU, Shasta River HA to determine beneficial use support and results are as follows: 0 of 6 samples exceeded the water quality threshold for Oxygen, Dissolved. |
Data Reference: |
Benthic, Field, Habitat, Tissue, Toxicity, WQ from the Surface Water Ambient Monitoring Program for the 2026 Integrated Report in Region 1 |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
Water Quality Control Plan, North Coast Basin, Chapter III, General Objectives for all Inland Surface Waters, Enclosed Bays and Estuaries states: Dissolved oxygen concentrations shall conform to those limits listed in Section 3.3.5. Section 3.3.5 lists dissolved oxygen concentration limits for COLD beneficial use waters to be a daily minimum of 6.0 mg/L and a 7-day moving average of 8.0 mg/L. |
Objective/Criterion Reference: |
Water Quality Control Plan (Basin Plan) for the North Coast Region |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
The samples were collected at 1 monitoring site: 105LS9999 (Little Springs Creek at Spring Head). |
Temporal Representation: |
The samples were collected between the dates of 2021-04-15 and 2021-05-20 |
Environmental Conditions: |
|
QAPP Information: |
QAPP for Surface Water Ambient Monitoring Program (SWAMP) |
QAPP Information Reference(s): |
Generic SWAMP QAPrP |
|
Line of Evidence (LOE) for Decision ID 157122, Oxygen, Dissolved
|
Region 1 |
Klamath River HU, Shasta River HA |
|
|
LOE ID: |
326199 |
|
Pollutant: |
Oxygen, Dissolved |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
None |
|
Beneficial Use: |
Cold Freshwater Habitat |
|
Number of Samples: |
25 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP RWB1 Monitoring data for Klamath River HU, Shasta River HA to determine beneficial use support and results are as follows: 0 of 25 samples exceeded the water quality threshold for Oxygen, Dissolved. |
Data Reference: |
Benthic, Field, Habitat, Tissue, Toxicity, WQ from the Surface Water Ambient Monitoring Program for the 2026 Integrated Report in Region 1 |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
Water Quality Control Plan, North Coast Basin, Chapter III, General Objectives for all Inland Surface Waters, Enclosed Bays and Estuaries states: Dissolved oxygen concentrations shall conform to those limits listed in Section 3.3.5. Section 3.3.5 lists dissolved oxygen concentration limits for COLD beneficial use waters to be a daily minimum of 6.0 mg/L and a 7-day moving average of 8.0 mg/L. |
Objective/Criterion Reference: |
Water Quality Control Plan (Basin Plan) for the North Coast Region |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
The samples were collected at 1 monitoring site: 105BS7150 (Big Springs Creek at Old Water Wheel). |
Temporal Representation: |
The samples were collected between the dates of 2021-04-08 and 2021-10-28 |
Environmental Conditions: |
|
QAPP Information: |
QAPP for Surface Water Ambient Monitoring Program (SWAMP) |
QAPP Information Reference(s): |
Generic SWAMP QAPrP |
|
Line of Evidence (LOE) for Decision ID 157122, Oxygen, Dissolved
|
Region 1 |
Klamath River HU, Shasta River HA |
|
|
LOE ID: |
326251 |
|
Pollutant: |
Oxygen, Dissolved |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
None |
|
Beneficial Use: |
Cold Freshwater Habitat |
|
Number of Samples: |
25 |
Number of Exceedances: |
6 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP RWB1 Monitoring data for Klamath River HU, Shasta River HA to determine beneficial use support and results are as follows: 6 of 25 samples exceeded the water quality threshold for Oxygen, Dissolved. |
Data Reference: |
Benthic, Field, Habitat, Tissue, Toxicity, WQ from the Surface Water Ambient Monitoring Program for the 2026 Integrated Report in Region 1 |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
Water Quality Control Plan, North Coast Basin, Chapter III, General Objectives for all Inland Surface Waters, Enclosed Bays and Estuaries states: Dissolved oxygen concentrations shall conform to those limits listed in Section 3.3.5. Section 3.3.5 lists dissolved oxygen concentration limits for COLD beneficial use waters to be a daily minimum of 6.0 mg/L and a 7-day moving average of 8.0 mg/L. |
Objective/Criterion Reference: |
Water Quality Control Plan (Basin Plan) for the North Coast Region |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
The samples were collected at 1 monitoring site: 105PO0001 (Parks Creek Overflow at Big Springs Road Crossing). |
Temporal Representation: |
The samples were collected between the dates of 2021-04-08 and 2021-10-28 |
Environmental Conditions: |
|
QAPP Information: |
QAPP for Surface Water Ambient Monitoring Program (SWAMP) |
QAPP Information Reference(s): |
Generic SWAMP QAPrP |
|
Line of Evidence (LOE) for Decision ID 157122, Oxygen, Dissolved
|
Region 1 |
Klamath River HU, Shasta River HA |
|
|
LOE ID: |
326231 |
|
Pollutant: |
Oxygen, Dissolved |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
None |
|
Beneficial Use: |
Cold Freshwater Habitat |
|
Number of Samples: |
22 |
Number of Exceedances: |
1 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP RWB1 Monitoring data for Klamath River HU, Shasta River HA to determine beneficial use support and results are as follows: 1 of 22 samples exceeded the water quality threshold for Oxygen, Dissolved. |
Data Reference: |
Benthic, Field, Habitat, Tissue, Toxicity, WQ from the Surface Water Ambient Monitoring Program for the 2026 Integrated Report in Region 1 |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
Water Quality Control Plan, North Coast Basin, Chapter III, General Objectives for all Inland Surface Waters, Enclosed Bays and Estuaries states: Dissolved oxygen concentrations shall conform to those limits listed in Section 3.3.5. Section 3.3.5 lists dissolved oxygen concentration limits for COLD beneficial use waters to be a daily minimum of 6.0 mg/L and a 7-day moving average of 8.0 mg/L. |
Objective/Criterion Reference: |
Water Quality Control Plan (Basin Plan) for the North Coast Region |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
The samples were collected at 1 monitoring site: 105SH6389 (Shasta River downstream Parks Creek). |
Temporal Representation: |
The samples were collected between the dates of 2021-04-08 and 2021-10-21 |
Environmental Conditions: |
|
QAPP Information: |
QAPP for Surface Water Ambient Monitoring Program (SWAMP) |
QAPP Information Reference(s): |
Generic SWAMP QAPrP |
|
Line of Evidence (LOE) for Decision ID 157122, Oxygen, Dissolved
|
Region 1 |
Klamath River HU, Shasta River HA |
|
|
LOE ID: |
326186 |
|
Pollutant: |
Oxygen, Dissolved |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
None |
|
Beneficial Use: |
Cold Freshwater Habitat |
|
Number of Samples: |
24 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP RWB1 Monitoring data for Klamath River HU, Shasta River HA to determine beneficial use support and results are as follows: 0 of 24 samples exceeded the water quality threshold for Oxygen, Dissolved. |
Data Reference: |
Benthic, Field, Habitat, Tissue, Toxicity, WQ from the Surface Water Ambient Monitoring Program for the 2026 Integrated Report in Region 1 |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
Water Quality Control Plan, North Coast Basin, Chapter III, General Objectives for all Inland Surface Waters, Enclosed Bays and Estuaries states: Dissolved oxygen concentrations shall conform to those limits listed in Section 3.3.5. Section 3.3.5 lists dissolved oxygen concentration limits for COLD beneficial use waters to be a daily minimum of 6.0 mg/L and a 7-day moving average of 8.0 mg/L. |
Objective/Criterion Reference: |
Water Quality Control Plan (Basin Plan) for the North Coast Region |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
The samples were collected at 1 monitoring site: 105SH6418 (Shasta River upstream Parks Creek). |
Temporal Representation: |
The samples were collected between the dates of 2021-04-08 and 2021-10-28 |
Environmental Conditions: |
|
QAPP Information: |
QAPP for Surface Water Ambient Monitoring Program (SWAMP) |
QAPP Information Reference(s): |
Generic SWAMP QAPrP |
|
Line of Evidence (LOE) for Decision ID 157122, Oxygen, Dissolved
|
Region 1 |
Klamath River HU, Shasta River HA |
|
|
LOE ID: |
326164 |
|
Pollutant: |
Oxygen, Dissolved |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
None |
|
Beneficial Use: |
Cold Freshwater Habitat |
|
Number of Samples: |
1 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP Perennial Stream Surveys data for Klamath River HU, Shasta River HA to determine beneficial use support and results are as follows: 0 of 1 samples exceeded the water quality threshold for Oxygen, Dissolved. |
Data Reference: |
Benthic, Field, Habitat, WQ from the Surface Water Ambient Monitoring Program for the 2026 Integrated Report in Region 1 |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
Water Quality Control Plan, North Coast Basin, Chapter III, General Objectives for all Inland Surface Waters, Enclosed Bays and Estuaries states: Dissolved oxygen concentrations shall conform to those limits listed in Section 3.3.5. Section 3.3.5 lists dissolved oxygen concentration limits for COLD beneficial use waters to be a daily minimum of 6.0 mg/L and a 7-day moving average of 8.0 mg/L. |
Objective/Criterion Reference: |
Water Quality Control Plan (Basin Plan) for the North Coast Region |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
The samples were collected at 1 monitoring site: 105PS0295 (Shasta River ~1mi above Cooley Gulch). |
Temporal Representation: |
The samples were collected between the dates of 2016-06-15 and 2016-06-15 |
Environmental Conditions: |
|
QAPP Information: |
QAPP for Surface Water Ambient Monitoring Program (SWAMP) |
QAPP Information Reference(s): |
Generic SWAMP QAPrP |
|
Line of Evidence (LOE) for Decision ID 157122, Oxygen, Dissolved
|
Region 1 |
Klamath River HU, Shasta River HA |
|
|
LOE ID: |
326162 |
|
Pollutant: |
Oxygen, Dissolved |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
None |
|
Beneficial Use: |
Cold Freshwater Habitat |
|
Number of Samples: |
1 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP Reference Condition Management Plan data for Klamath River HU, Shasta River HA to determine beneficial use support and results are as follows: 0 of 1 samples exceeded the water quality threshold for Oxygen, Dissolved. |
Data Reference: |
Benthic, Field, Habitat, WQ from the Surface Water Ambient Monitoring Program for the 2026 Integrated Report in Region 1 |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
Water Quality Control Plan, North Coast Basin, Chapter III, General Objectives for all Inland Surface Waters, Enclosed Bays and Estuaries states: Dissolved oxygen concentrations shall conform to those limits listed in Section 3.3.5. Section 3.3.5 lists dissolved oxygen concentration limits for COLD beneficial use waters to be a daily minimum of 6.0 mg/L and a 7-day moving average of 8.0 mg/L. |
Objective/Criterion Reference: |
Water Quality Control Plan (Basin Plan) for the North Coast Region |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
The samples were collected at 1 monitoring site: 105WE0592 (Eddy Creek ~0.8 miles downstream from end of 4WD road.). |
Temporal Representation: |
The samples were collected between the dates of 2015-07-13 and 2015-07-13 |
Environmental Conditions: |
|
QAPP Information: |
QAPP for Surface Water Ambient Monitoring Program (SWAMP) |
QAPP Information Reference(s): |
Generic SWAMP QAPrP |
|
Line of Evidence (LOE) for Decision ID 157122, Oxygen, Dissolved
|
Region 1 |
Klamath River HU, Shasta River HA |
|
|
LOE ID: |
326154 |
|
Pollutant: |
Oxygen, Dissolved |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
None |
|
Beneficial Use: |
Cold Freshwater Habitat |
|
Number of Samples: |
17 |
Number of Exceedances: |
1 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP RWB1 Monitoring data for Klamath River HU, Shasta River HA to determine beneficial use support and results are as follows: 1 of 17 samples exceeded the water quality threshold for Oxygen, Dissolved. |
Data Reference: |
Benthic, Field, Habitat, Tissue, Toxicity, WQ from the Surface Water Ambient Monitoring Program for the 2026 Integrated Report in Region 1 |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
Water Quality Control Plan, North Coast Basin, Chapter III, General Objectives for all Inland Surface Waters, Enclosed Bays and Estuaries states: Dissolved oxygen concentrations shall conform to those limits listed in Section 3.3.5. Section 3.3.5 lists dissolved oxygen concentration limits for COLD beneficial use waters to be a daily minimum of 6.0 mg/L and a 7-day moving average of 8.0 mg/L. |
Objective/Criterion Reference: |
Water Quality Control Plan (Basin Plan) for the North Coast Region |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
The samples were collected at 1 monitoring site: 105LS9900 (Little Springs Creek at Outlet Works). |
Temporal Representation: |
The samples were collected between the dates of 2021-06-03 and 2021-10-28 |
Environmental Conditions: |
|
QAPP Information: |
QAPP for Surface Water Ambient Monitoring Program (SWAMP) |
QAPP Information Reference(s): |
Generic SWAMP QAPrP |
|
Line of Evidence (LOE) for Decision ID 157122, Oxygen, Dissolved
|
Region 1 |
Klamath River HU, Shasta River HA |
|
|
LOE ID: |
326133 |
|
Pollutant: |
Oxygen, Dissolved |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
None |
|
Beneficial Use: |
Cold Freshwater Habitat |
|
Number of Samples: |
79 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed Klamath Hydroelectric Settlement Monitoring data for Klamath River HU, Shasta River HA to determine beneficial use support and results are as follows: 0 of 79 samples exceeded the water quality threshold for Oxygen, Dissolved. |
Data Reference: |
Field, WQ from the Klamath Basin Monitoring Program for the 2026 Integrated Report in Region 1 |
|
SWAMP Data: |
Non-SWAMP |
|
Water Quality Objective/Criterion: |
Water Quality Control Plan, North Coast Basin, Chapter III, General Objectives for all Inland Surface Waters, Enclosed Bays and Estuaries states: Dissolved oxygen concentrations shall conform to those limits listed in Section 3.3.5. Section 3.3.5 lists dissolved oxygen concentration limits for COLD beneficial use waters to be a daily minimum of 6.0 mg/L and a 7-day moving average of 8.0 mg/L. |
Objective/Criterion Reference: |
Water Quality Control Plan (Basin Plan) for the North Coast Region |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
The samples were collected at 1 monitoring site: SH00000_KHSA (Shasta River near mouth (Baseline)). |
Temporal Representation: |
The samples were collected between the dates of 2010-09-08 and 2016-12-14 |
Environmental Conditions: |
|
QAPP Information: |
Klamath Hydroelectric Settlement Monitoring QAPP |
QAPP Information Reference(s): |
San Francisco Estuary Institute - QA doc_cyano SOP (2009) - Klamath Hydroelectric Settlement Monitoring - 402674 |
|
Line of Evidence (LOE) for Decision ID 157122, Oxygen, Dissolved
|
Region 1 |
Klamath River HU, Shasta River HA |
|
|
LOE ID: |
326245 |
|
Pollutant: |
Oxygen, Dissolved |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
None |
|
Beneficial Use: |
Warm Freshwater Habitat |
|
Number of Samples: |
79 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed Klamath Hydroelectric Settlement Monitoring data for Klamath River HU, Shasta River HA to determine beneficial use support and results are as follows: 0 of 79 samples exceeded the water quality threshold for Oxygen, Dissolved. |
Data Reference: |
Field, WQ from the Klamath Basin Monitoring Program for the 2026 Integrated Report in Region 1 |
|
SWAMP Data: |
Non-SWAMP |
|
Water Quality Objective/Criterion: |
Water Quality Control Plan, North Coast Basin, Chapter III, General Objectives for all Inland Surface Waters, Enclosed Bays and Estuaries states: Dissolved oxygen concentrations shall conform to those limits listed in Section 3.3.5. Section 3.3.5 lists dissolved oxygen concentration limits for WARM beneficial use waters to be a daily minimum of 5.0 mg/L and a 7-day moving average of 6.0 mg/L. |
Objective/Criterion Reference: |
Water Quality Control Plan (Basin Plan) for the North Coast Region |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
The samples were collected at 1 monitoring site: SH00000_KHSA (Shasta River near mouth (Baseline)). |
Temporal Representation: |
The samples were collected between the dates of 2010-09-08 and 2016-12-14 |
Environmental Conditions: |
|
QAPP Information: |
Klamath Hydroelectric Settlement Monitoring QAPP |
QAPP Information Reference(s): |
San Francisco Estuary Institute - QA doc_cyano SOP (2009) - Klamath Hydroelectric Settlement Monitoring - 402674 |
|
Line of Evidence (LOE) for Decision ID 157122, Oxygen, Dissolved
|
Region 1 |
Klamath River HU, Shasta River HA |
|
|
LOE ID: |
326241 |
|
Pollutant: |
Oxygen, Dissolved |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
None |
|
Beneficial Use: |
Warm Freshwater Habitat |
|
Number of Samples: |
22 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP RWB1 Monitoring data for Klamath River HU, Shasta River HA to determine beneficial use support and results are as follows: 0 of 22 samples exceeded the water quality threshold for Oxygen, Dissolved. |
Data Reference: |
Benthic, Field, Habitat, Tissue, Toxicity, WQ from the Surface Water Ambient Monitoring Program for the 2026 Integrated Report in Region 1 |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
Water Quality Control Plan, North Coast Basin, Chapter III, General Objectives for all Inland Surface Waters, Enclosed Bays and Estuaries states: Dissolved oxygen concentrations shall conform to those limits listed in Section 3.3.5. Section 3.3.5 lists dissolved oxygen concentration limits for WARM beneficial use waters to be a daily minimum of 5.0 mg/L and a 7-day moving average of 6.0 mg/L. |
Objective/Criterion Reference: |
Water Quality Control Plan (Basin Plan) for the North Coast Region |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
The samples were collected at 1 monitoring site: 105SH6389 (Shasta River downstream Parks Creek). |
Temporal Representation: |
The samples were collected between the dates of 2021-04-08 and 2021-10-21 |
Environmental Conditions: |
|
QAPP Information: |
QAPP for Surface Water Ambient Monitoring Program (SWAMP) |
QAPP Information Reference(s): |
Generic SWAMP QAPrP |
|
Line of Evidence (LOE) for Decision ID 157122, Oxygen, Dissolved
|
Region 1 |
Klamath River HU, Shasta River HA |
|
|
LOE ID: |
326208 |
|
Pollutant: |
Oxygen, Dissolved |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
None |
|
Beneficial Use: |
Warm Freshwater Habitat |
|
Number of Samples: |
25 |
Number of Exceedances: |
3 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP RWB1 Monitoring data for Klamath River HU, Shasta River HA to determine beneficial use support and results are as follows: 3 of 25 samples exceeded the water quality threshold for Oxygen, Dissolved. |
Data Reference: |
Benthic, Field, Habitat, Tissue, Toxicity, WQ from the Surface Water Ambient Monitoring Program for the 2026 Integrated Report in Region 1 |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
Water Quality Control Plan, North Coast Basin, Chapter III, General Objectives for all Inland Surface Waters, Enclosed Bays and Estuaries states: Dissolved oxygen concentrations shall conform to those limits listed in Section 3.3.5. Section 3.3.5 lists dissolved oxygen concentration limits for WARM beneficial use waters to be a daily minimum of 5.0 mg/L and a 7-day moving average of 6.0 mg/L. |
Objective/Criterion Reference: |
Water Quality Control Plan (Basin Plan) for the North Coast Region |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
The samples were collected at 1 monitoring site: 105PO0001 (Parks Creek Overflow at Big Springs Road Crossing). |
Temporal Representation: |
The samples were collected between the dates of 2021-04-08 and 2021-10-28 |
Environmental Conditions: |
|
QAPP Information: |
QAPP for Surface Water Ambient Monitoring Program (SWAMP) |
QAPP Information Reference(s): |
Generic SWAMP QAPrP |
|
Line of Evidence (LOE) for Decision ID 157122, Oxygen, Dissolved
|
Region 1 |
Klamath River HU, Shasta River HA |
|
|
LOE ID: |
326205 |
|
Pollutant: |
Oxygen, Dissolved |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
None |
|
Beneficial Use: |
Warm Freshwater Habitat |
|
Number of Samples: |
24 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP RWB1 Monitoring data for Klamath River HU, Shasta River HA to determine beneficial use support and results are as follows: 0 of 24 samples exceeded the water quality threshold for Oxygen, Dissolved. |
Data Reference: |
Benthic, Field, Habitat, Tissue, Toxicity, WQ from the Surface Water Ambient Monitoring Program for the 2026 Integrated Report in Region 1 |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
Water Quality Control Plan, North Coast Basin, Chapter III, General Objectives for all Inland Surface Waters, Enclosed Bays and Estuaries states: Dissolved oxygen concentrations shall conform to those limits listed in Section 3.3.5. Section 3.3.5 lists dissolved oxygen concentration limits for WARM beneficial use waters to be a daily minimum of 5.0 mg/L and a 7-day moving average of 6.0 mg/L. |
Objective/Criterion Reference: |
Water Quality Control Plan (Basin Plan) for the North Coast Region |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
The samples were collected at 1 monitoring site: 105SH6418 (Shasta River upstream Parks Creek). |
Temporal Representation: |
The samples were collected between the dates of 2021-04-08 and 2021-10-28 |
Environmental Conditions: |
|
QAPP Information: |
QAPP for Surface Water Ambient Monitoring Program (SWAMP) |
QAPP Information Reference(s): |
Generic SWAMP QAPrP |
|
Line of Evidence (LOE) for Decision ID 157122, Oxygen, Dissolved
|
Region 1 |
Klamath River HU, Shasta River HA |
|
|
LOE ID: |
326266 |
|
Pollutant: |
Oxygen, Dissolved |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
None |
|
Beneficial Use: |
Warm Freshwater Habitat |
|
Number of Samples: |
1 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP Perennial Stream Surveys data for Klamath River HU, Shasta River HA to determine beneficial use support and results are as follows: 0 of 1 samples exceeded the water quality threshold for Oxygen, Dissolved. |
Data Reference: |
Benthic, Field, Habitat, WQ from the Surface Water Ambient Monitoring Program for the 2026 Integrated Report in Region 1 |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
Water Quality Control Plan, North Coast Basin, Chapter III, General Objectives for all Inland Surface Waters, Enclosed Bays and Estuaries states: Dissolved oxygen concentrations shall conform to those limits listed in Section 3.3.5. Section 3.3.5 lists dissolved oxygen concentration limits for WARM beneficial use waters to be a daily minimum of 5.0 mg/L and a 7-day moving average of 6.0 mg/L. |
Objective/Criterion Reference: |
Water Quality Control Plan (Basin Plan) for the North Coast Region |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
The samples were collected at 1 monitoring site: 105PS0295 (Shasta River ~1mi above Cooley Gulch). |
Temporal Representation: |
The samples were collected between the dates of 2016-06-15 and 2016-06-15 |
Environmental Conditions: |
|
QAPP Information: |
QAPP for Surface Water Ambient Monitoring Program (SWAMP) |
QAPP Information Reference(s): |
Generic SWAMP QAPrP |
|
Line of Evidence (LOE) for Decision ID 157122, Oxygen, Dissolved
|
Region 1 |
Klamath River HU, Shasta River HA |
|
|
LOE ID: |
326157 |
|
Pollutant: |
Oxygen, Dissolved |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
None |
|
Beneficial Use: |
Warm Freshwater Habitat |
|
Number of Samples: |
25 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP RWB1 Monitoring data for Klamath River HU, Shasta River HA to determine beneficial use support and results are as follows: 0 of 25 samples exceeded the water quality threshold for Oxygen, Dissolved. |
Data Reference: |
Benthic, Field, Habitat, Tissue, Toxicity, WQ from the Surface Water Ambient Monitoring Program for the 2026 Integrated Report in Region 1 |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
Water Quality Control Plan, North Coast Basin, Chapter III, General Objectives for all Inland Surface Waters, Enclosed Bays and Estuaries states: Dissolved oxygen concentrations shall conform to those limits listed in Section 3.3.5. Section 3.3.5 lists dissolved oxygen concentration limits for WARM beneficial use waters to be a daily minimum of 5.0 mg/L and a 7-day moving average of 6.0 mg/L. |
Objective/Criterion Reference: |
Water Quality Control Plan (Basin Plan) for the North Coast Region |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
The samples were collected at 1 monitoring site: 105BS7150 (Big Springs Creek at Old Water Wheel). |
Temporal Representation: |
The samples were collected between the dates of 2021-04-08 and 2021-10-28 |
Environmental Conditions: |
|
QAPP Information: |
QAPP for Surface Water Ambient Monitoring Program (SWAMP) |
QAPP Information Reference(s): |
Generic SWAMP QAPrP |
|
Line of Evidence (LOE) for Decision ID 157122, Oxygen, Dissolved
|
Region 1 |
Klamath River HU, Shasta River HA |
|
|
LOE ID: |
326108 |
|
Pollutant: |
Oxygen, Dissolved |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
None |
|
Beneficial Use: |
Fish Spawning |
|
Number of Samples: |
24 |
Number of Exceedances: |
5 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP RWB1 Monitoring data for Klamath River HU, Shasta River HA to determine beneficial use support and results are as follows: 5 of 24 samples exceeded the water quality threshold for Oxygen, Dissolved. |
Data Reference: |
Benthic, Field, Habitat, Tissue, Toxicity, WQ from the Surface Water Ambient Monitoring Program for the 2026 Integrated Report in Region 1 |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
Water Quality Control Plan, North Coast Basin, Chapter III, General Objectives for all Inland Surface Waters, Enclosed Bays and Estuaries states: Dissolved oxygen concentrations shall conform to those limits listed in Section 3.3.5. Section 3.3.5 lists dissolved oxygen concentration limits for SPAWN beneficial use waters to be a daily minimum of 9.0 mg/L and a 7-day moving average of 11.0 mg/L. |
Objective/Criterion Reference: |
Water Quality Control Plan (Basin Plan) for the North Coast Region |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
The samples were collected at 1 monitoring site: 105PC0001 (Parks Creek at Shasta River). |
Temporal Representation: |
The samples were collected between the dates of 2021-04-08 and 2021-10-28 |
Environmental Conditions: |
|
QAPP Information: |
QAPP for Surface Water Ambient Monitoring Program (SWAMP) |
QAPP Information Reference(s): |
Generic SWAMP QAPrP |
|
Line of Evidence (LOE) for Decision ID 157122, Oxygen, Dissolved
|
Region 1 |
Klamath River HU, Shasta River HA |
|
|
LOE ID: |
326120 |
|
Pollutant: |
Oxygen, Dissolved |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
None |
|
Beneficial Use: |
Fish Spawning |
|
Number of Samples: |
1 |
Number of Exceedances: |
1 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP Reference Condition Management Plan data for Klamath River HU, Shasta River HA to determine beneficial use support and results are as follows: 1 of 1 samples exceeded the water quality threshold for Oxygen, Dissolved. |
Data Reference: |
Benthic, Field, Habitat, WQ from the Surface Water Ambient Monitoring Program for the 2026 Integrated Report in Region 1 |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
Water Quality Control Plan, North Coast Basin, Chapter III, General Objectives for all Inland Surface Waters, Enclosed Bays and Estuaries states: Dissolved oxygen concentrations shall conform to those limits listed in Section 3.3.5. Section 3.3.5 lists dissolved oxygen concentration limits for SPAWN beneficial use waters to be a daily minimum of 9.0 mg/L and a 7-day moving average of 11.0 mg/L. |
Objective/Criterion Reference: |
Water Quality Control Plan (Basin Plan) for the North Coast Region |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
The samples were collected at 1 monitoring site: 105WE0592 (Eddy Creek ~0.8 miles downstream from end of 4WD road.). |
Temporal Representation: |
The samples were collected between the dates of 2015-07-13 and 2015-07-13 |
Environmental Conditions: |
|
QAPP Information: |
QAPP for Surface Water Ambient Monitoring Program (SWAMP) |
QAPP Information Reference(s): |
Generic SWAMP QAPrP |
|
Line of Evidence (LOE) for Decision ID 157122, Oxygen, Dissolved
|
Region 1 |
Klamath River HU, Shasta River HA |
|
|
LOE ID: |
326178 |
|
Pollutant: |
Oxygen, Dissolved |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
None |
|
Beneficial Use: |
Fish Spawning |
|
Number of Samples: |
79 |
Number of Exceedances: |
6 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed Klamath Hydroelectric Settlement Monitoring data for Klamath River HU, Shasta River HA to determine beneficial use support and results are as follows: 6 of 79 samples exceeded the water quality threshold for Oxygen, Dissolved. |
Data Reference: |
Field, WQ from the Klamath Basin Monitoring Program for the 2026 Integrated Report in Region 1 |
|
SWAMP Data: |
Non-SWAMP |
|
Water Quality Objective/Criterion: |
Water Quality Control Plan, North Coast Basin, Chapter III, General Objectives for all Inland Surface Waters, Enclosed Bays and Estuaries states: Dissolved oxygen concentrations shall conform to those limits listed in Section 3.3.5. Section 3.3.5 lists dissolved oxygen concentration limits for SPAWN beneficial use waters to be a daily minimum of 9.0 mg/L and a 7-day moving average of 11.0 mg/L. |
Objective/Criterion Reference: |
Water Quality Control Plan (Basin Plan) for the North Coast Region |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
The samples were collected at 1 monitoring site: SH00000_KHSA (Shasta River near mouth (Baseline)). |
Temporal Representation: |
The samples were collected between the dates of 2010-09-08 and 2016-12-14 |
Environmental Conditions: |
|
QAPP Information: |
Klamath Hydroelectric Settlement Monitoring QAPP |
QAPP Information Reference(s): |
San Francisco Estuary Institute - QA doc_cyano SOP (2009) - Klamath Hydroelectric Settlement Monitoring - 402674 |
|
Line of Evidence (LOE) for Decision ID 157122, Oxygen, Dissolved
|
Region 1 |
Klamath River HU, Shasta River HA |
|
|
LOE ID: |
326198 |
|
Pollutant: |
Oxygen, Dissolved |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
None |
|
Beneficial Use: |
Fish Spawning |
|
Number of Samples: |
25 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP RWB1 Monitoring data for Klamath River HU, Shasta River HA to determine beneficial use support and results are as follows: 0 of 25 samples exceeded the water quality threshold for Oxygen, Dissolved. |
Data Reference: |
Benthic, Field, Habitat, Tissue, Toxicity, WQ from the Surface Water Ambient Monitoring Program for the 2026 Integrated Report in Region 1 |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
Water Quality Control Plan, North Coast Basin, Chapter III, General Objectives for all Inland Surface Waters, Enclosed Bays and Estuaries states: Dissolved oxygen concentrations shall conform to those limits listed in Section 3.3.5. Section 3.3.5 lists dissolved oxygen concentration limits for SPAWN beneficial use waters to be a daily minimum of 9.0 mg/L and a 7-day moving average of 11.0 mg/L. |
Objective/Criterion Reference: |
Water Quality Control Plan (Basin Plan) for the North Coast Region |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
The samples were collected at 1 monitoring site: 105BS7150 (Big Springs Creek at Old Water Wheel). |
Temporal Representation: |
The samples were collected between the dates of 2021-04-08 and 2021-10-28 |
Environmental Conditions: |
|
QAPP Information: |
QAPP for Surface Water Ambient Monitoring Program (SWAMP) |
QAPP Information Reference(s): |
Generic SWAMP QAPrP |
|
Line of Evidence (LOE) for Decision ID 163032, Specific Conductivity
|
Region 1 |
Klamath River HU, Shasta River HA |
|
|
LOE ID: |
318406 |
|
Pollutant: |
Specific Conductivity |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Total |
|
Beneficial Use: |
Cold Freshwater Habitat |
|
Number of Samples: |
1 |
Number of Exceedances: |
1 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed specific conductivity data for SWAMP RWB1 Monitoring and determined that calendar year 2021 did not exceed the 90% upper limit of 700 micromhos and did exceed the 50% upper limit of 400 micromhos, so that 1 of 1 sample exceeds the water quality objective. |
Data Reference: |
Benthic, Field, Habitat, Tissue, Toxicity, WQ from the Surface Water Ambient Monitoring Program for the 2026 Integrated Report in Region 1 |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
Per the Basin Plan (NCRWQCB 2007): The 90% upper limit specific conductance objective at 77 F is 700 micromhos (or mS/cm2). The 50% upper limit specific conductance objective at 77 F is 400 micromhos (or mS/cm2). The 90% and 50% upper limits represent the 90/50 percentile values for a calendar year. 90% or 50% or more of the values must be less than or equal to the upper limit. |
Objective/Criterion Reference: |
Water Quality Control Plan (Basin Plan) for the North Coast Region |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
These samples were collected at sampling station name: Parks Creek at Shasta River; station code: 105PC0001. |
Temporal Representation: |
These samples were collected from 4/8/2021-10/28/2021. |
Environmental Conditions: |
|
QAPP Information: |
QAPP for SWAMP RWB1 Monitoring |
QAPP Information Reference(s): |
Generic SWAMP QAPrP |
|
Line of Evidence (LOE) for Decision ID 163032, Specific Conductivity
|
Region 1 |
Klamath River HU, Shasta River HA |
|
|
LOE ID: |
21223 |
|
Pollutant: |
Specific Conductivity |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
None |
|
Beneficial Use: |
Municipal & Domestic Supply |
|
Number of Samples: |
13 |
Number of Exceedances: |
3 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Three of the 13 specific conductivity samples collected from Yreka Creek exceed the objective. The samples were collected as part of the Surface Water Ambient Water Monitoring Program (SWAMP). The data are found in the SWAMP Summary Report for the North Coast Region for Years 2000-2006 (NCRWQCB 2008). |
Data Reference: |
Surface Water Ambient Monitoring Program (SWAMP). Summary Report for the North Coast Region (RWQCB-1) for years 2000-2006. North Coast Regional Water Quality Control Board. March 2008 |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
Per the Basin Plan (NCRWQCB 2007): The 90% upper limit specific conductance objective at 77 F is 700 micromhos (or mS/cm2). The 50% upper limit specific conductance objective at 77 F is 400 micromhos (or mS/cm2). The 90% and 50% upper limits represent the 90/50 percentile values for a calendar year. 90% or 50% or more of the values must be less than or equal to the upper limit. |
Objective/Criterion Reference: |
Water Quality Control Plan (Basin Plan) - North Coast Region (Region 1) |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
Samples were collected from Yreka Creek from two locations as follows: (1) at Highway 3 (SWAMP Station ID YREHW3), and (2) at Anderson Grade Road (SWAMP Station ID YREAND). Samples were collected from well-mixed flows in glides or riffles. |
Temporal Representation: |
Samples were collected from October 2004 to June 2005. The site visits corresponded to fall, winter, spring and early summer seasonal conditions. |
Environmental Conditions: |
There are no known environmental conditions (e.g., seasonality, land use practices, fire events, storms, etc.) that are related to these data. |
QAPP Information: |
Quality control was conducted in accordance with the SWAMP Quality Assurance Management Plan (Puckett 2002). |
QAPP Information Reference(s): |
Quality Assurance Management Plan for the State of California's Surface Water Ambient Monitoring Program. Sacramento, CA. State Water Resources Control Board. SWAMP. December 2002 (1st version)
|
|
Line of Evidence (LOE) for Decision ID 163032, Specific Conductivity
|
Region 1 |
Klamath River HU, Shasta River HA |
|
|
LOE ID: |
319005 |
|
Pollutant: |
Specific Conductivity |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Total |
|
Beneficial Use: |
Cold Freshwater Habitat |
|
Number of Samples: |
1 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed specific conductivity data for USGS California Water Science Center and determined that calendar year 2015 does not exceed either the 90% or 50% upper limit, so that 0 of 1 sample exceeds the water quality objective. |
Data Reference: |
WQX from the NWQMP for the 2026 Integrated Report in Region 1 |
|
SWAMP Data: |
Non-SWAMP |
|
Water Quality Objective/Criterion: |
Per the Basin Plan (NCRWQCB 2007): The 90% upper limit specific conductance objective at 77 F is 800 micromhos (or mS/cm2). The 50% upper limit specific conductance objective at 77 F is 600 micromhos (or mS/cm2). The 90% and 50% upper limits represent the 90/50 percentile values for a calendar year. 90% or 50% or more of the values must be less than or equal to the upper limit. |
Objective/Criterion Reference: |
Water Quality Control Plan (Basin Plan) for the North Coast Region |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
This sample was collected at sampling station name: SHASTA R NR EDGEWOOD CA; station code: USGS-11516750. |
Temporal Representation: |
This sample was collected on 8/27/2015. |
Environmental Conditions: |
|
QAPP Information: |
QAPP for USGS California Water Science Center |
QAPP Information Reference(s): |
QAPP for USGS Data Collected during the 2026 Integrated Report Cycle |
|
Line of Evidence (LOE) for Decision ID 163032, Specific Conductivity
|
Region 1 |
Klamath River HU, Shasta River HA |
|
|
LOE ID: |
318621 |
|
Pollutant: |
Specific Conductivity |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Total |
|
Beneficial Use: |
Cold Freshwater Habitat |
|
Number of Samples: |
6 |
Number of Exceedances: |
6 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed specific conductivity data for Klamath Hydroelectric Settlement Monitoring and determined that calendar years 2010, 2011, 2012, 2013, 2014, and 2015 exceed the 50% upper limit, so that 6 of 6 samples exceed the water quality objective. |
Data Reference: |
Field, WQ from the Klamath Basin Monitoring Program for the 2026 Integrated Report in Region 1 |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
Per the Basin Plan (NCRWQCB 2007): The 90% upper limit specific conductance objective at 77 F is 700 micromhos (or mS/cm2). The 50% upper limit specific conductance objective at 77 F is 400 micromhos (or mS/cm2). The 90% and 50% upper limits represent the 90/50 percentile values for a calendar year. 90% or 50% or more of the values must be less than or equal to the upper limit. |
Objective/Criterion Reference: |
Water Quality Control Plan (Basin Plan) for the North Coast Region |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
These samples were collected at sampling station name: Shasta River near mouth (Baseline); station code: SH00000_KHSA. |
Temporal Representation: |
These samples were collected from 9/8/2010-12/14/2016. |
Environmental Conditions: |
|
QAPP Information: |
QAPP for Klamath Hydroelectric Settlement Monitoring |
QAPP Information Reference(s): |
San Francisco Estuary Institute - QA doc_cyano SOP (2009) - Klamath Hydroelectric Settlement Monitoring - 402674 |
|
Line of Evidence (LOE) for Decision ID 163032, Specific Conductivity
|
Region 1 |
Klamath River HU, Shasta River HA |
|
|
LOE ID: |
318619 |
|
Pollutant: |
Specific Conductivity |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Total |
|
Beneficial Use: |
Cold Freshwater Habitat |
|
Number of Samples: |
1 |
Number of Exceedances: |
1 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed specific conductivity data for SWAMP RWB1 Monitoring and determined that calendar year 2021 exceeds the 50% upper limit, so that 1 of 1 sample exceeds the water quality objective. |
Data Reference: |
Benthic, Field, Habitat, Tissue, Toxicity, WQ from the Surface Water Ambient Monitoring Program for the 2026 Integrated Report in Region 1 |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
Per the Basin Plan (NCRWQCB 2007): The 90% upper limit specific conductance objective at 77 F is 700 micromhos (or mS/cm2). The 50% upper limit specific conductance objective at 77 F is 400 micromhos (or mS/cm2). The 90% and 50% upper limits represent the 90/50 percentile values for a calendar year. 90% or 50% or more of the values must be less than or equal to the upper limit. |
Objective/Criterion Reference: |
Water Quality Control Plan (Basin Plan) for the North Coast Region |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
These samples were collected at sampling station name: Shasta River downstream Parks Creek; station code: 105SH6389. |
Temporal Representation: |
These samples were collected from 4/8/2021-10/28/2021. |
Environmental Conditions: |
|
QAPP Information: |
QAPP for SWAMP RWB1 Monitoring |
QAPP Information Reference(s): |
Generic SWAMP QAPrP |
|
Line of Evidence (LOE) for Decision ID 163032, Specific Conductivity
|
Region 1 |
Klamath River HU, Shasta River HA |
|
|
LOE ID: |
318617 |
|
Pollutant: |
Specific Conductivity |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Total |
|
Beneficial Use: |
Cold Freshwater Habitat |
|
Number of Samples: |
1 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed specific conductivity data for SWAMP Perennial Stream Surveys and determined that calendar year 2016 does not exceed the 90% or 50% upper limit, so that 0 of 1 sample exceeds the water quality objective. |
Data Reference: |
Benthic, Field, Habitat, WQ from the Surface Water Ambient Monitoring Program for the 2026 Integrated Report in Region 1 |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
Per the Basin Plan (NCRWQCB 2007): The 90% upper limit specific conductance objective at 77 F is 800 micromhos (or mS/cm2). The 50% upper limit specific conductance objective at 77 F is 600 micromhos (or mS/cm2). The 90% and 50% upper limits represent the 90/50 percentile values for a calendar year. 90% or 50% or more of the values must be less than or equal to the upper limit. |
Objective/Criterion Reference: |
Water Quality Control Plan (Basin Plan) for the North Coast Region |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
This sample was collected at sampling station name: Shasta River ~1mi above Cooley Gulch; station code: 105PS0295. |
Temporal Representation: |
This sample was collected on 6/15/2016. |
Environmental Conditions: |
|
QAPP Information: |
QAPP for SWAMP Perennial Stream Surveys |
QAPP Information Reference(s): |
Generic SWAMP QAPrP |
|
Line of Evidence (LOE) for Decision ID 163032, Specific Conductivity
|
Region 1 |
Klamath River HU, Shasta River HA |
|
|
LOE ID: |
318250 |
|
Pollutant: |
Specific Conductivity |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Total |
|
Beneficial Use: |
Cold Freshwater Habitat |
|
Number of Samples: |
1 |
Number of Exceedances: |
1 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed specific conductivity data for SWAMP RWB1 Monitoring and determined that 1 of 1 sample exceeds the water quality objective for calendar year 2021. |
Data Reference: |
Benthic, Field, Habitat, Tissue, Toxicity, WQ from the Surface Water Ambient Monitoring Program for the 2026 Integrated Report in Region 1 |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
Per the Basin Plan (NCRWQCB 2007): The 90% upper limit specific conductance objective at 77 F is 700 micromhos (or mS/cm2). The 50% upper limit specific conductance objective at 77 F is 400 micromhos (or mS/cm2). The 90% and 50% upper limits represent the 90/50 percentile values for a calendar year. 90% or 50% or more of the values must be less than or equal to the upper limit. |
Objective/Criterion Reference: |
Water Quality Control Plan (Basin Plan) for the North Coast Region |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
These samples were collected at sampling station name: Little Springs Creek at Outlet Works; station code: 105LS9900. |
Temporal Representation: |
These samples were collected from 6/3/2021-10/28/2021. |
Environmental Conditions: |
|
QAPP Information: |
QAPP for SWAMP RWB1 Monitoring |
QAPP Information Reference(s): |
Generic SWAMP QAPrP |
|
Line of Evidence (LOE) for Decision ID 163032, Specific Conductivity
|
Region 1 |
Klamath River HU, Shasta River HA |
|
|
LOE ID: |
318252 |
|
Pollutant: |
Specific Conductivity |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Total |
|
Beneficial Use: |
Cold Freshwater Habitat |
|
Number of Samples: |
1 |
Number of Exceedances: |
1 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed specific conductivity data for SWAMP RWB1 Monitoring and determined that 1 of 1 sample exceeds the water quality objective for calendar year 2021. |
Data Reference: |
Benthic, Field, Habitat, Tissue, Toxicity, WQ from the Surface Water Ambient Monitoring Program for the 2026 Integrated Report in Region 1 |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
Per the Basin Plan (NCRWQCB 2007): The 90% upper limit specific conductance objective at 77 F is 700 micromhos (or mS/cm2). The 50% upper limit specific conductance objective at 77 F is 400 micromhos (or mS/cm2). The 90% and 50% upper limits represent the 90/50 percentile values for a calendar year. 90% or 50% or more of the values must be less than or equal to the upper limit. |
Objective/Criterion Reference: |
Water Quality Control Plan (Basin Plan) for the North Coast Region |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
These samples were collected at sampling station name: Little Springs Creek at Spring Head; station code: 105LS9999. |
Temporal Representation: |
These samples were collected from 4/8/2021-5/27/2021. |
Environmental Conditions: |
|
QAPP Information: |
QAPP for SWAMP RWB1 Monitoring |
QAPP Information Reference(s): |
Generic SWAMP QAPrP |
|
Line of Evidence (LOE) for Decision ID 163032, Specific Conductivity
|
Region 1 |
Klamath River HU, Shasta River HA |
|
|
LOE ID: |
317912 |
|
Pollutant: |
Specific Conductivity |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Total |
|
Beneficial Use: |
Cold Freshwater Habitat |
|
Number of Samples: |
1 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed data from the parent project SWAMP RWB1 Monitoring and determined that calendar year 2021 does not exceed the 90% or 50% upper limit, so that 0 of 1 sample exceeds the water quality objective. |
Data Reference: |
Benthic, Field, Habitat, Tissue, Toxicity, WQ from the Surface Water Ambient Monitoring Program for the 2026 Integrated Report in Region 1 |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
Per the Basin Plan (NCRWQCB 2007): The 90% upper limit specific conductance objective at 77 F is 700 micromhos (or mS/cm2). The 50% upper limit specific conductance objective at 77 F is 400 micromhos (or mS/cm2). The 90% and 50% upper limits represent the 90/50 percentile values for a calendar year. 90% or 50% or more of the values must be less than or equal to the upper limit. |
Objective/Criterion Reference: |
Water Quality Control Plan (Basin Plan) for the North Coast Region |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
These samples were collected at sampling station name: Big Springs Creek at Old Water Wheel; station code: 105BS7150. |
Temporal Representation: |
These samples were collected from 4/15/2021-10/28/2021. |
Environmental Conditions: |
|
QAPP Information: |
QAPP for SWAMP RWB1 Monitoring |
QAPP Information Reference(s): |
Generic SWAMP QAPrP |
|
Line of Evidence (LOE) for Decision ID 163032, Specific Conductivity
|
Region 1 |
Klamath River HU, Shasta River HA |
|
|
LOE ID: |
318012 |
|
Pollutant: |
Specific Conductivity |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Total |
|
Beneficial Use: |
Cold Freshwater Habitat |
|
Number of Samples: |
1 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed data for parent project SWAMP Reference Condition Management Plan and determined that calendar year 2015 did not exceed either the 90% or the 50% upper limit, so that 0 of 1 sample exceeds the water quality objective for specific conductivity. |
Data Reference: |
Benthic, Field, Habitat, WQ from the Surface Water Ambient Monitoring Program for the 2026 Integrated Report in Region 1 |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
Per the Basin Plan (NCRWQCB 2007): The 90% upper limit specific conductance objective at 77 F is 700 micromhos (or mS/cm2). The 50% upper limit specific conductance objective at 77 F is 400 micromhos (or mS/cm2). The 90% and 50% upper limits represent the 90/50 percentile values for a calendar year. 90% or 50% or more of the values must be less than or equal to the upper limit. |
Objective/Criterion Reference: |
Water Quality Control Plan (Basin Plan) for the North Coast Region |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
This sample was collected at sampling station name: Eddy Creek ~0.8 miles downstream from end of 4WD road.; station code: 105WE0592. |
Temporal Representation: |
This sample was collected on 7/13/2015. |
Environmental Conditions: |
|
QAPP Information: |
QAPP for SWAMP Reference Condition Management Plan |
QAPP Information Reference(s): |
Generic SWAMP QAPrP |
|
Line of Evidence (LOE) for Decision ID 163032, Specific Conductivity
|
Region 1 |
Klamath River HU, Shasta River HA |
|
|
LOE ID: |
21220 |
|
Pollutant: |
Specific Conductivity |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
None |
|
Beneficial Use: |
Municipal & Domestic Supply |
|
Number of Samples: |
32 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
None of the 32 specific conductivity samples collected from the mainstem Shasta River exceed the objective. The samples were collected as part of the Surface Water Ambient Water Monitoring Program (SWAMP). The data are found in the SWAMP Summary Report for the North Coast Region for Years 2000-2006 (NCRWQCB 2008). |
Data Reference: |
Surface Water Ambient Monitoring Program (SWAMP). Summary Report for the North Coast Region (RWQCB-1) for years 2000-2006. North Coast Regional Water Quality Control Board. March 2008 |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
Per the Basin Plan (NCRWQCB 2007): The 90% upper limit specific conductance objective at 77 F is 800 micromhos (or mS/cm2). The 50% upper limit specific conductance objective at 77 F is 600 micromhos (or mS/cm2). The 90% and 50% upper limits represent the 90/50 percentile values for a calendar year. 90% or 50% or more of the values must be less than or equal to the upper limit. |
Objective/Criterion Reference: |
Water Quality Control Plan (Basin Plan) - North Coast Region (Region 1) |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
Samples were collected in the mainstem Shasta River from 3 locations as follows: (1) near Edgewood Road (SWAMP Station ID SHAEDG), (2) at Montague Grenada Road (SWAMP Station ID SHAMON), and (3) at Highway 263 (SWAMP Station ID SHA263). Samples were collected in well-mixed flows in glides or riffles. |
Temporal Representation: |
The samples from Edgewood Road and Montague Grenada Road were collected as grab samples during 5 site visits at each site during the 2002 - 2003 fiscal years. Samples from Highway 263 were collected as grab samples during 22 site visits during the 2000 - 2006 fiscal years. The site visits corresponded to fall, winter, spring and early summer seasonal conditions. |
Environmental Conditions: |
There are no known environmental conditions (e.g., seasonality, land use practices, fire events, storms, etc.) that are related to these data. |
QAPP Information: |
Quality control was conducted in accordance with the SWAMP Quality Assurance Management Plan (Puckett 2002). |
QAPP Information Reference(s): |
Quality Assurance Management Plan for the State of California's Surface Water Ambient Monitoring Program. Sacramento, CA. State Water Resources Control Board. SWAMP. December 2002 (1st version)
|
|
Line of Evidence (LOE) for Decision ID 163032, Specific Conductivity
|
Region 1 |
Klamath River HU, Shasta River HA |
|
|
LOE ID: |
34422 |
|
Pollutant: |
Specific Conductivity |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
None |
|
Beneficial Use: |
Municipal & Domestic Supply |
|
Number of Samples: |
2 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Zero of the 2 samples exceeded the objective. |
Data Reference: |
RWB1 Trend Maintenance Periods FYs 2007 2008 |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
Water Quality Control Plan, North Coast Region (NCRWQCB 2011): The site specific objective for the mainstem Shasta River is a 90% upper limit of 800 uS. Therefore, 90% of the values in a calendar year must be lower than this limit. In addition the site specific objective of 50% upper limit of 600 uS which represents the 50 percentile values of the monthly means for a calendar year applies to this water body. Therefore, 50% or more of the monthly means in a calendar year must be less than or equal to an upper limit. |
Objective/Criterion Reference: |
Water Quality Control Plan (Basin Plan) for the North Coast Region |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
Samples were collected from the Shasta River at Hwy 263 station (105SHA263). |
Temporal Representation: |
Samples were collected on the following dates: 11/15/2007 2/27/2008 4/9/2008 7/16/2008 |
Environmental Conditions: |
|
QAPP Information: |
SWAMP QAPP (2008). |
QAPP Information Reference(s): |
Surface Water Ambient Monitoring Program Quality Assurance Program Plan |
|
Line of Evidence (LOE) for Decision ID 163032, Specific Conductivity
|
Region 1 |
Klamath River HU, Shasta River HA |
|
|
LOE ID: |
34376 |
|
Pollutant: |
Specific Conductivity |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
None |
|
Beneficial Use: |
Municipal & Domestic Supply |
|
Number of Samples: |
2 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Zero of the 2 samples exceeded the objective. |
Data Reference: |
RWB1 Trend Maintenance Periods FYs 2007 2008 |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
Water Quality Control Plan, North Coast Region (NCRWQCB 2011): The site specific objective for the mainstem Shasta River is a 90% upper limit of 800 uS. Therefore, 90% of the values in a calendar year must be lower than this limit. In addition the site specific objective of 50% upper limit of 600 uS which represents the 50 percentile values of the monthly means for a calendar year applies to this water body. Therefore, 50% or more of the monthly means in a calendar year must be less than or equal to an upper limit. |
Objective/Criterion Reference: |
Water Quality Control Plan (Basin Plan) for the North Coast Region |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
Samples were collected from the Shasta River near Edgewood station (105SHAEDG). |
Temporal Representation: |
Samples were collected on the following dates: 11/15/2007 2/27/2008 4/10/2008 7/16/2008 |
Environmental Conditions: |
|
QAPP Information: |
SWAMP QAPP (2008). |
QAPP Information Reference(s): |
Surface Water Ambient Monitoring Program Quality Assurance Program Plan |
|
Line of Evidence (LOE) for Decision ID 163032, Specific Conductivity
|
Region 1 |
Klamath River HU, Shasta River HA |
|
|
LOE ID: |
100742 |
|
Pollutant: |
Specific Conductivity |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
None |
|
Beneficial Use: |
Municipal & Domestic Supply |
|
Number of Samples: |
4 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed the data for this water body to determine beneficial use support and results are as follows: 0 of 4 samples exceeded the water quality standard for specific conductance. Data range from 194 - 230. |
Data Reference: |
Water Quality Assessment Data for the 2018 solicitation cycle submitted through CEDEN for SWAMP RWB1 Monitoring .
|
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
Water Quality Control Plan, North Coast Basin, Chapter III, General Objectives for all Inland Surface Waters, Enclosed Bays and Estuaries states the following: Specific conductivity shall conform to Table 3-1 which states that water quality objective for specific conductivity has an 90% upper limit of 800 micromhos and a 50% upper limit of 600 micromhos. |
Objective/Criterion Reference: |
Water Quality Control Plan (Basin Plan) for the North Coast Region |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
The samples were collected at 1 monitoring site(s) (105SH9274) |
Temporal Representation: |
The samples were collected between the dates 03/07/2013 - 11/20/2013. |
Environmental Conditions: |
There are no known environmental conditions (e.g., seasonality, land use practices, fire events, storms, etc.) that are related to these data. |
QAPP Information: |
Quality Assurance Program Plan and Standard Operating Procedures for SWAMP program  |
QAPP Information Reference(s): |
Quality Assurance Program Plans, Quality Assurance Project Plans, and Standard Operating Procedures for the SWAMP program |
|
Line of Evidence (LOE) for Decision ID 163032, Specific Conductivity
|
Region 1 |
Klamath River HU, Shasta River HA |
|
|
LOE ID: |
100743 |
|
Pollutant: |
Specific Conductivity |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
None |
|
Beneficial Use: |
Municipal & Domestic Supply |
|
Number of Samples: |
4 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed the data for this water body to determine beneficial use support and results are as follows: 0 of 4 samples exceeded the water quality standard for specific conductance. Data range from 432 - 587. |
Data Reference: |
Water Quality Assessment Data for the 2018 solicitation cycle submitted through CEDEN for SWAMP RWB1 Monitoring .
|
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
Water Quality Control Plan, North Coast Basin, Chapter III, General Objectives for all Inland Surface Waters, Enclosed Bays and Estuaries states the following: Specific conductivity shall conform to Table 3-1 which states that water quality objective for specific conductivity has an 90% upper limit of 800 micromhos and a 50% upper limit of 600 micromhos. |
Objective/Criterion Reference: |
Water Quality Control Plan (Basin Plan) for the North Coast Region |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
The samples were collected at 1 monitoring site(s) Shasta River at Hwy 263 (105SH1452) |
Temporal Representation: |
The samples were collected between the dates 03/06/2013 - 11/20/2013. |
Environmental Conditions: |
There are no known environmental conditions (e.g., seasonality, land use practices, fire events, storms, etc.) that are related to these data. |
QAPP Information: |
Quality Assurance Program Plan and Standard Operating Procedures for SWAMP program  |
QAPP Information Reference(s): |
Quality Assurance Program Plans, Quality Assurance Project Plans, and Standard Operating Procedures for the SWAMP program |
|
Line of Evidence (LOE) for Decision ID 163032, Specific Conductivity
|
Region 1 |
Klamath River HU, Shasta River HA |
|
|
LOE ID: |
100751 |
|
Pollutant: |
Specific Conductivity |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
None |
|
Beneficial Use: |
Municipal & Domestic Supply |
|
Number of Samples: |
1 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed the data for this water body to determine beneficial use support and results are as follows: 0 of 1 samples exceeded the water quality standard for specific conductance. Data range from 424 micromhos. |
Data Reference: |
Water Quality Assessment Data for the 2018 solicitation cycle submitted through CEDEN for SWAMP Perennial Stream Surveys .
|
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
Water Quality Control Plan, North Coast Basin, Chapter III, General Objectives for all Inland Surface Waters, Enclosed Bays and Estuaries states the following: Specific conductivity shall conform to Table 3-1 which states that water quality objective for specific conductivity has an 90% upper limit of 800 micromhos and a 50% upper limit of 600 micromhos. |
Objective/Criterion Reference: |
Water Quality Control Plan (Basin Plan) for the North Coast Region |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
The samples were collected at 1 monitoring site(s) Shasta River ~2.2mi below E. Louie Rd.
(105PS0231) |
Temporal Representation: |
The samples were collected between the dates 08/29/2013. |
Environmental Conditions: |
There are no known environmental conditions (e.g., seasonality, land use practices, fire events, storms, etc.) that are related to these data. |
QAPP Information: |
Quality Assurance Program Plan and Standard Operating Procedures for SWAMP program  |
QAPP Information Reference(s): |
Quality Assurance Program Plans, Quality Assurance Project Plans, and Standard Operating Procedures for the SWAMP program |
|
Line of Evidence (LOE) for Decision ID 163032, Specific Conductivity
|
Region 1 |
Klamath River HU, Shasta River HA |
|
|
LOE ID: |
318408 |
|
Pollutant: |
Specific Conductivity |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Total |
|
Beneficial Use: |
Cold Freshwater Habitat |
|
Number of Samples: |
1 |
Number of Exceedances: |
1 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed specific conductivity data for SWAMP RWB1 Monitoring and determined that calendar year 2021 exceeded both the 90% upper limit of 700 micromhos 50% upper limit of 400 micromhos, so that 1 of 1 sample exceeds the water quality objective. |
Data Reference: |
Benthic, Field, Habitat, Tissue, Toxicity, WQ from the Surface Water Ambient Monitoring Program for the 2026 Integrated Report in Region 1 |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
Per the Basin Plan (NCRWQCB 2007): The 90% upper limit specific conductance objective at 77 F is 700 micromhos (or mS/cm2). The 50% upper limit specific conductance objective at 77 F is 400 micromhos (or mS/cm2). The 90% and 50% upper limits represent the 90/50 percentile values for a calendar year. 90% or 50% or more of the values must be less than or equal to the upper limit. |
Objective/Criterion Reference: |
Water Quality Control Plan (Basin Plan) for the North Coast Region |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
These samples were collected at sampling station name: Parks Creek Overflow at Big Springs Road Crossing; station code: 105PO0001. |
Temporal Representation: |
These samples were collected from 4/8/2021-10/28/2021. |
Environmental Conditions: |
|
QAPP Information: |
QAPP for SWAMP RWB1 Monitoring |
QAPP Information Reference(s): |
Generic SWAMP QAPrP |
|
Line of Evidence (LOE) for Decision ID 163032, Specific Conductivity
|
Region 1 |
Klamath River HU, Shasta River HA |
|
|
LOE ID: |
44472 |
|
Pollutant: |
Specific Conductivity |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
None |
|
Beneficial Use: |
Municipal & Domestic Supply |
|
Number of Samples: |
1 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP data for Evans Ditch to determine beneficial use support and results are as follows: 0 of 1 samples exceed the criterion for Specific Conductivity. |
Data Reference: |
Statewide Perennial Streams Assessment 2008 |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
Water Quality Control Plan, North Coast Region (NCRWQCB 2011): The site specific objective for Evans Ditch is a 90% upper limit of 700 uS. Therefore, 90% of the values in a calendar year must be lower than this limit. In addition the site specific objective of 50% upper limit of 400 uS which represents the 50 percentile values of the monthly means for a calendar year applies to this water body. Therefore, 50% or more of the monthly means in a calendar year must be less than or equal to an upper limit. |
Objective/Criterion Reference: |
Water Quality Control Plan (Basin Plan) for the North Coast Region |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
Data for this line of evidence for Klamath River HU, Shasta River HA was collected at 1 monitoring site [ Evans Ditch - 105PS0188] |
Temporal Representation: |
Data was collected on a single day 8/26/2008. |
Environmental Conditions: |
Staff is not aware of any special conditions that might affect interpretation of the data. |
QAPP Information: |
The SWAMP QAPP (2008) was followed. |
QAPP Information Reference(s): |
Surface Water Ambient Monitoring Program Quality Assurance Program Plan |
|
Line of Evidence (LOE) for Decision ID 163032, Specific Conductivity
|
Region 1 |
Klamath River HU, Shasta River HA |
|
|
LOE ID: |
318623 |
|
Pollutant: |
Specific Conductivity |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Total |
|
Beneficial Use: |
Cold Freshwater Habitat |
|
Number of Samples: |
1 |
Number of Exceedances: |
1 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed specific conductivity data for SWAMP RWB1 Monitoring and determined that calendar year 2021 exceeds the 50% upper limit, so that 1 of 1 sample exceeds the water quality objective. |
Data Reference: |
Benthic, Field, Habitat, Tissue, Toxicity, WQ from the Surface Water Ambient Monitoring Program for the 2026 Integrated Report in Region 1 |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
Per the Basin Plan (NCRWQCB 2007): The 90% upper limit specific conductance objective at 77 F is 700 micromhos (or mS/cm2). The 50% upper limit specific conductance objective at 77 F is 400 micromhos (or mS/cm2). The 90% and 50% upper limits represent the 90/50 percentile values for a calendar year. 90% or 50% or more of the values must be less than or equal to the upper limit. |
Objective/Criterion Reference: |
Water Quality Control Plan (Basin Plan) for the North Coast Region |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
These samples were collected at sampling station name: Shasta River upstream Parks Creek; station code: 105SH6418. |
Temporal Representation: |
These samples were collected from 4/8/2021-10/28/2021. |
Environmental Conditions: |
|
QAPP Information: |
QAPP for SWAMP RWB1 Monitoring |
QAPP Information Reference(s): |
Generic SWAMP QAPrP |
|
Line of Evidence (LOE) for Decision ID 155237, pH
|
Region 1 |
Klamath River HU, Shasta River HA |
|
|
LOE ID: |
318618 |
|
Pollutant: |
pH |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
None |
|
Beneficial Use: |
Cold Freshwater Habitat |
|
Number of Samples: |
39 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed pH data for SWAMP RWB1 Monitoring and determined that 0 samples are less than pH 7.0 and 0 samples are greater than pH 8.5, so that 0 of 39 samples exceed the water quality objective. |
Data Reference: |
Benthic, Field, Habitat, Tissue, Toxicity, WQ from the Surface Water Ambient Monitoring Program for the 2026 Integrated Report in Region 1 |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
Water Quality Control Plan, North Coast Basin, Chapter III, General Objectives for all Inland Surface Waters, Enclosed Bays and Estuaries states the following: The pH shall conform to the values listed in Table 3-1 which states that the water quality objective for pH shall not be depressed below 7.0 or raised above 8.5. |
Objective/Criterion Reference: |
Water Quality Control Plan (Basin Plan) for the North Coast Region |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
These samples were collected at sampling station name: Shasta River downstream Parks Creek; station code: 105SH6389. |
Temporal Representation: |
These samples were collected from 4/8/2021-10/28/2021. |
Environmental Conditions: |
|
QAPP Information: |
QAPP for SWAMP RWB1 Monitoring |
QAPP Information Reference(s): |
Generic SWAMP QAPrP |
|
Line of Evidence (LOE) for Decision ID 155237, pH
|
Region 1 |
Klamath River HU, Shasta River HA |
|
|
LOE ID: |
100711 |
|
Pollutant: |
pH |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
None |
|
Beneficial Use: |
Cold Freshwater Habitat |
|
Number of Samples: |
1 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP Perennial Stream Surveys data for Klamath River HU, Shasta River HA to determine beneficial use support and results are as follows: 0 of 1 samples exceeded the water quality standard for pH. |
Data Reference: |
Water Quality Assessment Data for the 2018 solicitation cycle submitted through CEDEN for SWAMP Perennial Stream Surveys .
|
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
Water Quality Control Plan, North Coast Basin, Chapter III, General Objectives for all Inland Surface Waters, Enclosed Bays and Estuaries states the following: The pH shall conform to the values listed in Table 3-1 which states that the water quality objective for pH for water bodies in Shasta River shall not be depressed below 7.0 or raised above 8.5. |
Objective/Criterion Reference: |
Water Quality Control Plan (Basin Plan) for the North Coast Region |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
The samples were collected at 1 monitoring site(s) Shasta River ~2.2mi below E. Louie Rd.
(105PS0231) |
Temporal Representation: |
The samples were collected between the date 08/29/2013. |
Environmental Conditions: |
There are no known environmental conditions (e.g., seasonality, land use practices, fire events, storms, etc.) that are related to these data. |
QAPP Information: |
Quality Assurance Program Plan and Standard Operating Procedures for SWAMP program  |
QAPP Information Reference(s): |
Quality Assurance Program Plans, Quality Assurance Project Plans, and Standard Operating Procedures for the SWAMP program |
|
Line of Evidence (LOE) for Decision ID 155237, pH
|
Region 1 |
Klamath River HU, Shasta River HA |
|
|
LOE ID: |
100704 |
|
Pollutant: |
pH |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
None |
|
Beneficial Use: |
Cold Freshwater Habitat |
|
Number of Samples: |
4 |
Number of Exceedances: |
2 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP RWB1 Monitoring data for Klamath River HU, Shasta River HA to determine beneficial use support and results are as follows: 2 of 4 samples exceeded the water quality standard for pH. |
Data Reference: |
Water Quality Assessment Data for the 2018 solicitation cycle submitted through CEDEN for SWAMP RWB1 Monitoring .
|
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
Water Quality Control Plan, North Coast Basin, Chapter III, General Objectives for all Inland Surface Waters, Enclosed Bays and Estuaries states the following: The pH shall conform to the values listed in Table 3-1 which states that the water quality objective for pH for water bodies in the Shasta River shall not be depressed below 7.0 or raised above 8.5. |
Objective/Criterion Reference: |
Water Quality Control Plan (Basin Plan) for the North Coast Region |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
The samples were collected at 1 monitoring site(s) Shasta River at Hwy 263
(105SH1452) |
Temporal Representation: |
The samples were collected between the dates of 2013-03-06 to 2013-11-20. |
Environmental Conditions: |
There are no known environmental conditions (e.g., seasonality, land use practices, fire events, storms, etc.) that are related to these data. |
QAPP Information: |
Quality Assurance Program Plan and Standard Operating Procedures for SWAMP program  |
QAPP Information Reference(s): |
Water Quality Assessment Data for the 2018 solicitation cycle submitted through CEDEN for SWAMP Reference Condition Management Plan .
|
QAPP Information Reference(s): |
Quality Assurance Program Plans, Quality Assurance Project Plans, and Standard Operating Procedures for the SWAMP program |
|
Line of Evidence (LOE) for Decision ID 155237, pH
|
Region 1 |
Klamath River HU, Shasta River HA |
|
|
LOE ID: |
34160 |
|
Pollutant: |
pH |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
None |
|
Beneficial Use: |
Cold Freshwater Habitat |
|
Number of Samples: |
4 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
None of the 4 samples exceeded the objective. |
Data Reference: |
RWB1 Trend Maintenance Periods FYs 2007 2008 |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
Water Quality Control Plan, North Coast Region (NCRWQCB 2011): Table 3-1 states that the lower limit pH for this water body is 7.0, and the upper limit pH for this water body is 8.5. |
Objective/Criterion Reference: |
Water Quality Control Plan (Basin Plan) for the North Coast Region |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
Samples were collected from the Shasta River near Edgewood station (105SHAEDG). |
Temporal Representation: |
Samples were collected approximately once per quarter year from November 2007 to July 2008. |
Environmental Conditions: |
|
QAPP Information: |
SWAMP QAPP |
QAPP Information Reference(s): |
Surface Water Ambient Monitoring Program Quality Assurance Program Plan |
|
Line of Evidence (LOE) for Decision ID 155237, pH
|
Region 1 |
Klamath River HU, Shasta River HA |
|
|
LOE ID: |
34159 |
|
Pollutant: |
pH |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
None |
|
Beneficial Use: |
Cold Freshwater Habitat |
|
Number of Samples: |
4 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
None of the 4 samples exceeded the objective. |
Data Reference: |
RWB1 Trend Maintenance Periods FYs 2007 2008 |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
Water Quality Control Plan, North Coast Region (NCRWQCB 2011): Table 3-1 states that the lower limit pH for this water body is 7.0, and the upper limit pH for this water body is 8.5. |
Objective/Criterion Reference: |
Water Quality Control Plan (Basin Plan) for the North Coast Region |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
Samples were collected from the Shasta River at Hwy 263 station (105SHA263). |
Temporal Representation: |
Samples were collected approximately once per quarter year from November 2007 to July 2008. |
Environmental Conditions: |
|
QAPP Information: |
SWAMP QAPP |
QAPP Information Reference(s): |
Surface Water Ambient Monitoring Program Quality Assurance Program Plan |
|
Line of Evidence (LOE) for Decision ID 155237, pH
|
Region 1 |
Klamath River HU, Shasta River HA |
|
|
LOE ID: |
100703 |
|
Pollutant: |
pH |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
None |
|
Beneficial Use: |
Cold Freshwater Habitat |
|
Number of Samples: |
4 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP RWB1 Monitoring data for Klamath River HU, Shasta River HA to determine beneficial use support and results are as follows: 0 of 4 samples exceeded the water quality standard for pH. |
Data Reference: |
Water Quality Assessment Data for the 2018 solicitation cycle submitted through CEDEN for SWAMP RWB1 Monitoring .
|
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
Water Quality Control Plan, North Coast Basin, Chapter III, General Objectives for all Inland Surface Waters, Enclosed Bays and Estuaries states the following: The pH shall conform to the values listed in Table 3-1 which states that the water quality objective for pH for water bodies in the Shasta River shall not be depressed below 7.0 or raised above 8.5. |
Objective/Criterion Reference: |
Water Quality Control Plan (Basin Plan) for the North Coast Region |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
The samples were collected at 1 monitoring site(s) Shasta River near Edgewood
(105SH9274). |
Temporal Representation: |
The samples were collected between the dates of 2013-04-29 to 2013-11-20. |
Environmental Conditions: |
There are no known environmental conditions (e.g., seasonality, land use practices, fire events, storms, etc.) that are related to these data. |
QAPP Information: |
Quality Assurance Program Plan and Standard Operating Procedures for SWAMP program  |
QAPP Information Reference(s): |
Quality Assurance Program Plans, Quality Assurance Project Plans, and Standard Operating Procedures for the SWAMP program |
|
Line of Evidence (LOE) for Decision ID 155237, pH
|
Region 1 |
Klamath River HU, Shasta River HA |
|
|
LOE ID: |
33910 |
|
Pollutant: |
pH |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
None |
|
Beneficial Use: |
Cold Freshwater Habitat |
|
Number of Samples: |
1 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
The sample collected did not exceed the objective |
Data Reference: |
Statewide Perennial Streams Assessment 2008 |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
Water Quality Control Plan, North Coast Region (NCRWQCB 2011): Table 3-1 states that the lower limit pH for surface water bodies for this water body is 7.0, and the upper limit pH is 8.5. |
Objective/Criterion Reference: |
Water Quality Control Plan (Basin Plan) for the North Coast Region |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
One sample was collected from the Evans Ditch station (105PS0188). |
Temporal Representation: |
One sample was collected in August 2008. |
Environmental Conditions: |
|
QAPP Information: |
SWAMP QAPP |
QAPP Information Reference(s): |
Surface Water Ambient Monitoring Program Quality Assurance Program Plan |
|
Line of Evidence (LOE) for Decision ID 155237, pH
|
Region 1 |
Klamath River HU, Shasta River HA |
|
|
LOE ID: |
318407 |
|
Pollutant: |
pH |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
None |
|
Beneficial Use: |
Cold Freshwater Habitat |
|
Number of Samples: |
40 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed pH data for SWAMP RWB1 Monitoring and determined that 0 samples are less than pH 6.5 and 0 samples are greater than pH 8.5, so that 0 of 40 samples exceed the water quality objective. |
Data Reference: |
Benthic, Field, Habitat, Tissue, Toxicity, WQ from the Surface Water Ambient Monitoring Program for the 2026 Integrated Report in Region 1 |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
Water Quality Control Plan, North Coast Basin, Chapter III, General Objectives for all Inland Surface Waters, Enclosed Bays and Estuaries states the following: The pH shall conform to the values listed in Table 3-1 which states that the water quality objective for pH shall not be depressed below 7.0 or raised above 8.5. |
Objective/Criterion Reference: |
Water Quality Control Plan (Basin Plan) for the North Coast Region |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
These samples were collected at sampling station name: Parks Creek Overflow at Big Springs Road Crossing; station code: 105PO0001. |
Temporal Representation: |
These samples were collected from 4/8/2021-10/28/2021. |
Environmental Conditions: |
|
QAPP Information: |
QAPP for SWAMP RWB1 Monitoring |
QAPP Information Reference(s): |
Generic SWAMP QAPrP |
|
Line of Evidence (LOE) for Decision ID 155237, pH
|
Region 1 |
Klamath River HU, Shasta River HA |
|
|
LOE ID: |
318405 |
|
Pollutant: |
pH |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
None |
|
Beneficial Use: |
Cold Freshwater Habitat |
|
Number of Samples: |
33 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed pH data for SWAMP RWB1 Monitoring and determined that 0 samples are less than pH 6.5 and 0 samples are greater than pH 8.5, so that 0 of 33 samples exceed the water quality objective. |
Data Reference: |
Benthic, Field, Habitat, Tissue, Toxicity, WQ from the Surface Water Ambient Monitoring Program for the 2026 Integrated Report in Region 1 |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
Water Quality Control Plan, North Coast Basin, Chapter III, General Objectives for all Inland Surface Waters, Enclosed Bays and Estuaries states the following: The pH shall conform to the values listed in Table 3-1 which states that the water quality objective for pH shall not be depressed below 7.0 or raised above 8.5. |
Objective/Criterion Reference: |
Water Quality Control Plan (Basin Plan) for the North Coast Region |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
These samples were collected at sampling station name: Parks Creek at Shasta River; station code: 105PC0001. |
Temporal Representation: |
These samples were collected from 4/8/2021-10/28/2021. |
Environmental Conditions: |
|
QAPP Information: |
QAPP for SWAMP RWB1 Monitoring |
QAPP Information Reference(s): |
Generic SWAMP QAPrP |
|
Line of Evidence (LOE) for Decision ID 155237, pH
|
Region 1 |
Klamath River HU, Shasta River HA |
|
|
LOE ID: |
318622 |
|
Pollutant: |
pH |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
None |
|
Beneficial Use: |
Cold Freshwater Habitat |
|
Number of Samples: |
34 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed pH data for SWAMP RWB1 Monitoring and determined that 0 samples are less than pH 7.0 and 0 samples are less than pH 8.5, so that 0 of 34 samples exceed the water quality objective. |
Data Reference: |
Benthic, Field, Habitat, Tissue, Toxicity, WQ from the Surface Water Ambient Monitoring Program for the 2026 Integrated Report in Region 1 |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
Water Quality Control Plan, North Coast Basin, Chapter III, General Objectives for all Inland Surface Waters, Enclosed Bays and Estuaries states the following: The pH shall conform to the values listed in Table 3-1 which states that the water quality objective for pH shall not be depressed below 7.0 or raised above 8.5. |
Objective/Criterion Reference: |
Water Quality Control Plan (Basin Plan) for the North Coast Region |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
These samples were collected at sampling station name: Shasta River upstream Parks Creek; station code: 105SH6418. |
Temporal Representation: |
These samples were collected from 4/8/2021-10/28/2021. |
Environmental Conditions: |
|
QAPP Information: |
QAPP for SWAMP RWB1 Monitoring |
QAPP Information Reference(s): |
Generic SWAMP QAPrP |
|
Line of Evidence (LOE) for Decision ID 155237, pH
|
Region 1 |
Klamath River HU, Shasta River HA |
|
|
LOE ID: |
318620 |
|
Pollutant: |
pH |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
None |
|
Beneficial Use: |
Cold Freshwater Habitat |
|
Number of Samples: |
79 |
Number of Exceedances: |
67 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed pH data for Klamath Hydroelectric Settlement Monitoring and determined that 0 samples are less than pH 7.0 and 67 samples are greater than pH 8.5, so that 67 of 79 samples exceed the water quality objective. |
Data Reference: |
Field, WQ from the Klamath Basin Monitoring Program for the 2026 Integrated Report in Region 1 |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
Water Quality Control Plan, North Coast Basin, Chapter III, General Objectives for all Inland Surface Waters, Enclosed Bays and Estuaries states the following: The pH shall conform to the values listed in Table 3-1 which states that the water quality objective for pH shall not be depressed below 7.0 or raised above 8.5. |
Objective/Criterion Reference: |
Water Quality Control Plan (Basin Plan) for the North Coast Region |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
These samples were collected at sampling station name: Shasta River near mouth (Baseline); station code: SH00000_KHSA. |
Temporal Representation: |
These samples were collected from 9/8/2010-12/14/2016. |
Environmental Conditions: |
|
QAPP Information: |
QAPP for Klamath Hydroelectric Settlement Monitoring |
QAPP Information Reference(s): |
San Francisco Estuary Institute - QA doc_cyano SOP (2009) - Klamath Hydroelectric Settlement Monitoring - 402674 |
|
Line of Evidence (LOE) for Decision ID 155237, pH
|
Region 1 |
Klamath River HU, Shasta River HA |
|
|
LOE ID: |
319006 |
|
Pollutant: |
pH |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
None |
|
Beneficial Use: |
Cold Freshwater Habitat |
|
Number of Samples: |
26 |
Number of Exceedances: |
24 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed pH data for Karuk Tribe (Tribal) and determined that 0 samples are less than pH 7.0 and 24 samples are greater than pH 8.5, so that 24 of 26 samples exceed the water quality objective. |
Data Reference: |
WQX from the NWQMP for the 2026 Integrated Report in Region 1 |
|
SWAMP Data: |
Non-SWAMP |
|
Water Quality Objective/Criterion: |
Water Quality Control Plan, North Coast Basin, Chapter III, General Objectives for all Inland Surface Waters, Enclosed Bays and Estuaries states the following: The pH shall conform to the values listed in Table 3-1 which states that the water quality objective for pH shall not be depressed below 7.0 or raised above 8.5. |
Objective/Criterion Reference: |
Water Quality Control Plan (Basin Plan) for the North Coast Region |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
These samples were collected at sampling station name: Shasta River; station code: KARUKDNR_WQX-SH. |
Temporal Representation: |
These samples were collected from 4/28/2011-9/28/2022. |
Environmental Conditions: |
|
QAPP Information: |
QAPP for Karuk Tribe (Tribal) |
QAPP Information Reference(s): |
Data collected by a California Tribe QAPP Approved by U.S. EPA
QAPP Reference
|
|
Line of Evidence (LOE) for Decision ID 155237, pH
|
Region 1 |
Klamath River HU, Shasta River HA |
|
|
LOE ID: |
318249 |
|
Pollutant: |
pH |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
None |
|
Beneficial Use: |
Cold Freshwater Habitat |
|
Number of Samples: |
23 |
Number of Exceedances: |
1 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed pH data for SWAMP RWB1 Monitoring and determined that 6 samples are less than pH 7.0 and 0 samples are greater than pH 8.5, so that 6 of 23 samples exceed the water quality objective. |
Data Reference: |
Benthic, Field, Habitat, Tissue, Toxicity, WQ from the Surface Water Ambient Monitoring Program for the 2026 Integrated Report in Region 1 |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
Water Quality Control Plan, North Coast Basin, Chapter III, General Objectives for all Inland Surface Waters, Enclosed Bays and Estuaries states the following: The pH shall conform to the values listed in Table 3-1 which states that the water quality objective for pH shall not be depressed below 7.0 or raised above 8.5. |
Objective/Criterion Reference: |
Water Quality Control Plan (Basin Plan) for the North Coast Region |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
These samples were collected at sampling station name: Little Springs Creek at Outlet Works; station code: 105LS9900. |
Temporal Representation: |
These samples were collected from 6/3/2021-10/28/2021. |
Environmental Conditions: |
|
QAPP Information: |
QAPP for SWAMP RWB1 Monitoring |
QAPP Information Reference(s): |
Generic SWAMP QAPrP |
|
Line of Evidence (LOE) for Decision ID 155237, pH
|
Region 1 |
Klamath River HU, Shasta River HA |
|
|
LOE ID: |
318251 |
|
Pollutant: |
pH |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
None |
|
Beneficial Use: |
Cold Freshwater Habitat |
|
Number of Samples: |
12 |
Number of Exceedances: |
1 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed pH data for SWAMP RWB1 Monitoring and determined that 1 sample is less than pH 7.0 and 0 samples are greater than pH 8.5, so that 1 of 12 samples exceeds the water quality objective. |
Data Reference: |
Benthic, Field, Habitat, Tissue, Toxicity, WQ from the Surface Water Ambient Monitoring Program for the 2026 Integrated Report in Region 1 |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
Water Quality Control Plan, North Coast Basin, Chapter III, General Objectives for all Inland Surface Waters, Enclosed Bays and Estuaries states the following: The pH shall conform to the values listed in Table 3-1 which states that the water quality objective for pH shall not be depressed below 7.0 or raised above 8.5. |
Objective/Criterion Reference: |
Water Quality Control Plan (Basin Plan) for the North Coast Region |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
These samples were collected at sampling station name: Little Springs Creek at Spring Head; station code: 105LS9999. |
Temporal Representation: |
These samples were collected from 4/8/2021-5/27/2021. |
Environmental Conditions: |
|
QAPP Information: |
QAPP for SWAMP RWB1 Monitoring |
QAPP Information Reference(s): |
Generic SWAMP QAPrP |
|
Line of Evidence (LOE) for Decision ID 155237, pH
|
Region 1 |
Klamath River HU, Shasta River HA |
|
|
LOE ID: |
318616 |
|
Pollutant: |
pH |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
None |
|
Beneficial Use: |
Cold Freshwater Habitat |
|
Number of Samples: |
1 |
Number of Exceedances: |
1 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed pH data for SWAMP Perennial Stream Surveys and determined that 0 samples are less than pH 7.0 and 1 sample is greater than pH 8.5, so that 1 of 1 sample exceeds the water quality objective. |
Data Reference: |
Benthic, Field, Habitat, WQ from the Surface Water Ambient Monitoring Program for the 2026 Integrated Report in Region 1 |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
Water Quality Control Plan, North Coast Basin, Chapter III, General Objectives for all Inland Surface Waters, Enclosed Bays and Estuaries states the following: The pH shall conform to the values listed in Table 3-1 which states that the water quality objective for pH shall not be depressed below 7.0 or raised above 8.5. |
Objective/Criterion Reference: |
Water Quality Control Plan (Basin Plan) for the North Coast Region |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
This sample was collected at sampling station name: Shasta River ~1mi above Cooley Gulch; station code: 105PS0295. |
Temporal Representation: |
This sample was collected on 6/15/2016. |
Environmental Conditions: |
|
QAPP Information: |
QAPP for SWAMP Perennial Stream Surveys |
QAPP Information Reference(s): |
Generic SWAMP QAPrP |
|
Line of Evidence (LOE) for Decision ID 155237, pH
|
Region 1 |
Klamath River HU, Shasta River HA |
|
|
LOE ID: |
318011 |
|
Pollutant: |
pH |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
None |
|
Beneficial Use: |
Cold Freshwater Habitat |
|
Number of Samples: |
1 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed data for parent project SWAMP Reference Condition Management Plan and determined that 0 samples were less than pH 7 or greater than pH 8.5, so that 0 of 1 sample exceeds the water quality objective for pH. |
Data Reference: |
Benthic, Field, Habitat, WQ from the Surface Water Ambient Monitoring Program for the 2026 Integrated Report in Region 1 |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
Water Quality Control Plan, North Coast Basin, Chapter III, General Objectives for all Inland Surface Waters, Enclosed Bays and Estuaries states the following: The pH shall conform to the values listed in Table 3-1 which states that the water quality objective for pH shall not be depressed below 7.0 or raised above 8.5. |
Objective/Criterion Reference: |
Water Quality Control Plan (Basin Plan) for the North Coast Region |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
This sample was collected at sampling station name: Eddy Creek ~0.8 miles downstream from end of 4WD road.; station code: 105WE0592. |
Temporal Representation: |
This sample was collected on 7/13/2015. |
Environmental Conditions: |
|
QAPP Information: |
QAPP for SWAMP Reference Condition Management Plan |
QAPP Information Reference(s): |
Generic SWAMP QAPrP |
|
Line of Evidence (LOE) for Decision ID 155237, pH
|
Region 1 |
Klamath River HU, Shasta River HA |
|
|
LOE ID: |
317911 |
|
Pollutant: |
pH |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
None |
|
Beneficial Use: |
Cold Freshwater Habitat |
|
Number of Samples: |
23 |
Number of Exceedances: |
21 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed data from the parent project SWAMP RWB1 Monitoring and determined that 21 samples were less than pH 7 and 0 samples were greater than pH 8.5, so that 21 of 23 samples exceed the water quality objective for pH. |
Data Reference: |
Benthic, Field, Habitat, Tissue, Toxicity, WQ from the Surface Water Ambient Monitoring Program for the 2026 Integrated Report in Region 1 |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
Water Quality Control Plan, North Coast Basin, Chapter III, General Objectives for all Inland Surface Waters, Enclosed Bays and Estuaries states the following: The pH shall conform to the values listed in Table 3-1 which states that the water quality objective for pH shall not be depressed below 6.5 or raised above 8.5. |
Objective/Criterion Reference: |
Water Quality Control Plan (Basin Plan) for the North Coast Region |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
These samples were collected at sampling station name: Big Springs Creek at Old Water Wheel; station code: 105BS7150. |
Temporal Representation: |
These samples were collected from 4/15/2021-10/28/2021. |
Environmental Conditions: |
|
QAPP Information: |
QAPP for SWAMP RWB1 Monitoring |
QAPP Information Reference(s): |
Generic SWAMP QAPrP |
|
Line of Evidence (LOE) for Decision ID 77895, DDE (Dichlorodiphenyldichloroethylene)
|
Region 1 |
Klamath River HU, Shasta River HA |
|
|
LOE ID: |
25611 |
|
Pollutant: |
DDE (Dichlorodiphenyldichloroethylene) |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
None |
|
Beneficial Use: |
Municipal & Domestic Supply |
|
Number of Samples: |
1 |
Number of Exceedances: |
1 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
One DDE sample collected in Yreka Creek had a detectable level of DDE and the sample exceed the evaluation guideline. The sample concentration was reported as detected not quantifiable (DNQ), with an estimated value of .0015 ug/l (method detection limit of 0.001 ug/l, reporting limit of .002 ug/l). There were also an additional 11 samples from Yreka Creek, which were non-detect. However, these non-detect data could not be utilized in this assessment because the detection limit for DDE is above the evaluation guideline. Per the listing policy, when a sample value is less than the quantitation limit, and the quantitation limit is greater than the evaluation guideline, the result shall not be used in the analysis. The samples were collected as part of the Surface Water Ambient Water Monitoring Program (SWAMP) (NCRWQCB 2008). |
Data Reference: |
Surface Water Ambient Monitoring Program (SWAMP). DDT, DDE, and DDD data from SWAMP Sampling for Years 2001-2006. North Coast Regional Water Quality Control Board. |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
Per the Basin Plan (NCRWQCB 2007): No individual pesticide or combination of pesticides shall be present in concentrations that adversely affect beneficial uses. There shall be no bioaccumulation of pesticide concentrations found in bottom sediments or aquatic life. Waters designated for use as domestic or municipal supply shall not contain concentrations of pesticides in excess of the limiting concentrations set forth in California Code of Regulations, Title 22, Division 4, Chapter 15, Article 4, Section 64444, and listed in Table 3.2 of the Basin Plan. |
Objective/Criterion Reference: |
Water Quality Control Plan (Basin Plan) - North Coast Region (Region 1) |
|
Evaluation Guideline: |
Per the National Recommended Water Quality Criteria (USEPA 2006): The recommended criterion for DDE for the protection of source waters for human health consumption of water and organisms is 0.00022 ug/l. |
Guideline Reference: |
National Recommended Water Quality Criteria. United States Environmental Protection Agency. Office of Water. Office of Science and Technology |
|
Spatial Representation: |
Samples were collected in Yreka Creek from 2 locations as follows: (1) Yreka Creek at Highway 3 (SWAMP Station ID 105YREHW3) and (2) in Yreka Creek at Anderson Grade Road (SWAMP Station ID 105YREAND). Samples were collected in well-mixed flows in glides or runs. |
Temporal Representation: |
Samples in Yreka Creek were collected from October 2002 to June 2005. The site visits corresponded to fall, winter, spring and early summer seasonal conditions. |
Environmental Conditions: |
There are no known environmental conditions (e.g., seasonality, land use practices, fire events, storms, etc.) that are related to these data. |
QAPP Information: |
Quality control was conducted in accordance with the SWAMP Quality Assurance Management Plan (SWAMP 2002). |
QAPP Information Reference(s): |
Quality Assurance Management Plan for the State of California's Surface Water Ambient Monitoring Program. Sacramento, CA. State Water Resources Control Board. SWAMP. December 2002 (1st version)
|
|
Line of Evidence (LOE) for Decision ID 77895, DDE (Dichlorodiphenyldichloroethylene)
|
Region 1 |
Klamath River HU, Shasta River HA |
|
|
LOE ID: |
123357 |
|
Pollutant: |
DDE (Dichlorodiphenyldichloroethylene) |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
None |
|
Beneficial Use: |
Municipal & Domestic Supply |
|
Number of Samples: |
0 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
State Water Board staff re-assessed SWAMP data for Klamath River HU, Shasta River HA to determine beneficial use support and results are as follows: 0 of 0 samples exceed the criterion for DDE(o,p'), Total. Eight samples were removed from assessment because an appropriate evaluation guideline for the water body-pollutant combination could not be obtained for this listing cycle. This LOE re-assesses data from LOE 29849 from the 2010 Integrated Report. Data were re-assessed in order to evaluate these data in their own LOE, instead of being evaluated in the same LOE as other pesticide data. |
Data Reference: |
Surface Water Ambient Monitoring Program (SWAMP). Summary Report for the North Coast Region (RWQCB-1) for years 2000-2006. North Coast Regional Water Quality Control Board. March 2008 |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
Per the Basin Plan (NCRWQCB 2011): No individual pesticide or combination of pesticides shall be present in concentrations that adversely affect beneficial uses. There shall be no bioaccumulation of pesticide concentrations found in bottom sediments or aquatic life. Waters designated for use as domestic or municipal supply shall not contain concentrations of pesticides in excess of the limiting concentrations set forth in California Code of Regulations, Title 22, Division 4, Chapter 15, Article 4, Section 64444, and listed in Table 3.2 of the Basin Plan. No evaluation guideline could be found to evaluate protection of the MUN beneficial use that meets the requirements of Section 6.1.3 of the Listing Policy. |
Objective/Criterion Reference: |
Water Quality Control Plan (Basin Plan) for the North Coast Region |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
Data for this line of evidence for Klamath River HU, Shasta River HA was collected at 1 monitoring site [ Shasta River at Montague - 105SHAMON] |
Temporal Representation: |
Data was collected over the time period 10/7/2002-6/19/2003. |
Environmental Conditions: |
There are no known environmental conditions (e.g., seasonality, land use practices, fire events, storms, etc.) that are related to these data. |
QAPP Information: |
Quality control was conducted in accordance with the SWAMP Quality Assurance Management Plan (SWAMP 2002). |
QAPP Information Reference(s): |
Quality Assurance Management Plan for the State of California's Surface Water Ambient Monitoring Program. Sacramento, CA. State Water Resources Control Board. SWAMP. December 2002 (1st version)
|
|
Line of Evidence (LOE) for Decision ID 77895, DDE (Dichlorodiphenyldichloroethylene)
|
Region 1 |
Klamath River HU, Shasta River HA |
|
|
LOE ID: |
115655 |
|
Pollutant: |
DDE (Dichlorodiphenyldichloroethylene) |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Total |
|
Beneficial Use: |
Municipal & Domestic Supply |
|
Number of Samples: |
0 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP RWB1 Monitoring data for Klamath River HU, Shasta River HA to determine beneficial use support, and the results are as follows: 0 of the 0 samples exceeded the evaluation guideline for DDE(p,p'). Although a total of 1 samples were collected, 1 of these samples were not included in the assessment because the laboratory data reporting limit(s) was above the objective and therefore the results could not be quantified with the level of certainty required by the Listing Policy Section 6.1.5.5. |
Data Reference: |
Water Quality Assessment Data for the 2018 solicitation cycle submitted through CEDEN for SWAMP RWB1 Monitoring .
|
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
The 4,4'-DDE criterion for the protection of human health from the consumption of water and organisms is 0.00059 ug/L (California Toxics Rule, 2000). |
Objective/Criterion Reference: |
Water Quality Standards 2000. Establishment of numeric criteria for priority toxic pollutants for the State of California: Rules and regulations. Federal Register Vol. 65, No. 97. Washington, D.C.: Environmental Protection Agency |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
Data was collected from 1 station(s) (Station Code(s) 105SH9274). |
Temporal Representation: |
Date for this waterbody was collected over the date range 2013-04-29 to 2013-04-29 |
Environmental Conditions: |
|
QAPP Information: |
Quality Assurance Program Plan and Standard Operating Procedures for SWAMP program |
QAPP Information Reference(s): |
Quality Assurance Program Plans, Quality Assurance Project Plans, and Standard Operating Procedures for the SWAMP program |
|
Line of Evidence (LOE) for Decision ID 77895, DDE (Dichlorodiphenyldichloroethylene)
|
Region 1 |
Klamath River HU, Shasta River HA |
|
|
LOE ID: |
34539 |
|
Pollutant: |
DDE (Dichlorodiphenyldichloroethylene) |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Total |
|
Beneficial Use: |
Municipal & Domestic Supply |
|
Number of Samples: |
0 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
The method detection limit for all 3 of the non-detect samples was greater than the criteria: thus the data was not used in this assessment. |
Data Reference: |
RWB1 Trend Maintenance Periods FYs 2007 2008 |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
Per the Basin Plan (NCRWQCB 2011): All waters shall be maintained free of toxic substances in concentrations that are toxic to, or that produce detrimental physiological responses in human, plant, animal, or aquatic life. The 4,4'-DDE criterion for the protection of human health from the consumption of water and organisms is 0.00022 ug/L (USEPA Nationally Recommended Criteria, 2006). |
Objective/Criterion Reference: |
National Recommended Water Quality Criteria. United States Environmental Protection Agency. Office of Water. Office of Science and Technology |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
Samples collected at station 105SHA263 (Shasta River at Hwy 263). |
Temporal Representation: |
Samples were collected on 11/15/2007, 4/9/2008, and 7/16/2008. |
Environmental Conditions: |
|
QAPP Information: |
SWAMP QAPP (2008) was followed. |
QAPP Information Reference(s): |
Surface Water Ambient Monitoring Program Quality Assurance Program Plan |
|
Line of Evidence (LOE) for Decision ID 77895, DDE (Dichlorodiphenyldichloroethylene)
|
Region 1 |
Klamath River HU, Shasta River HA |
|
|
LOE ID: |
115653 |
|
Pollutant: |
DDE (Dichlorodiphenyldichloroethylene) |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Total |
|
Beneficial Use: |
Municipal & Domestic Supply |
|
Number of Samples: |
0 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP RWB1 Monitoring data for Klamath River HU, Shasta River HA to determine beneficial use support, and the results are as follows: 0 of the 0 samples exceeded the evaluation guideline for DDE(p,p'). Although a total of 1 samples were collected, 1 of these samples were not included in the assessment because the laboratory data reporting limit(s) was above the objective and therefore the results could not be quantified with the level of certainty required by the Listing Policy Section 6.1.5.5. |
Data Reference: |
Water Quality Assessment Data for the 2018 solicitation cycle submitted through CEDEN for SWAMP RWB1 Monitoring .
|
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
The 4,4'-DDE criterion for the protection of human health from the consumption of water and organisms is 0.00059 ug/L (California Toxics Rule, 2000). |
Objective/Criterion Reference: |
Water Quality Standards 2000. Establishment of numeric criteria for priority toxic pollutants for the State of California: Rules and regulations. Federal Register Vol. 65, No. 97. Washington, D.C.: Environmental Protection Agency |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
Data was collected from 1 station(s) (Station Code(s) 105SH1452). |
Temporal Representation: |
Date for this waterbody was collected over the date range 2013-04-29 to 2013-04-29 |
Environmental Conditions: |
|
QAPP Information: |
Quality Assurance Program Plan and Standard Operating Procedures for SWAMP program |
QAPP Information Reference(s): |
Quality Assurance Program Plans, Quality Assurance Project Plans, and Standard Operating Procedures for the SWAMP program |
|
Line of Evidence (LOE) for Decision ID 77895, DDE (Dichlorodiphenyldichloroethylene)
|
Region 1 |
Klamath River HU, Shasta River HA |
|
|
LOE ID: |
123358 |
|
Pollutant: |
DDE (Dichlorodiphenyldichloroethylene) |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
None |
|
Beneficial Use: |
Municipal & Domestic Supply |
|
Number of Samples: |
0 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
State Water Board staff re-assessed SWAMP data for Klamath River HU, Shasta River HA to determine beneficial use support and results are as follows: 0 of 0 samples exceed the criterion for DDE(o,p'), Total. Eight samples were removed from assessment because an appropriate evaluation guideline for the water body-pollutant combination could not be obtained for this listing cycle. This LOE re-assesses data from LOE 29849 from the 2010 Integrated Report. Data were re-assessed in order to evaluate these data in their own LOE, instead of being evaluated in the same LOE as other pesticide data. |
Data Reference: |
Surface Water Ambient Monitoring Program (SWAMP). Summary Report for the North Coast Region (RWQCB-1) for years 2000-2006. North Coast Regional Water Quality Control Board. March 2008 |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
Per the Basin Plan (NCRWQCB 2011): No individual pesticide or combination of pesticides shall be present in concentrations that adversely affect beneficial uses. There shall be no bioaccumulation of pesticide concentrations found in bottom sediments or aquatic life. Waters designated for use as domestic or municipal supply shall not contain concentrations of pesticides in excess of the limiting concentrations set forth in California Code of Regulations, Title 22, Division 4, Chapter 15, Article 4, Section 64444, and listed in Table 3.2 of the Basin Plan. No evaluation guideline could be found to evaluate protection of the MUN beneficial use that meets the requirements of Section 6.1.3 of the Listing Policy. |
Objective/Criterion Reference: |
Water Quality Control Plan (Basin Plan) for the North Coast Region |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
Data for this line of evidence for Klamath River HU, Shasta River HA was collected at 1 monitoring site [ Shasta River near Edgewood - 105SH9274] |
Temporal Representation: |
Data was collected over the time period 10/7/2002-6/19/2003. |
Environmental Conditions: |
There are no known environmental conditions (e.g., seasonality, land use practices, fire events, storms, etc.) that are related to these data. |
QAPP Information: |
Quality control was conducted in accordance with the SWAMP Quality Assurance Management Plan (SWAMP 2002). |
QAPP Information Reference(s): |
Quality Assurance Management Plan for the State of California's Surface Water Ambient Monitoring Program. Sacramento, CA. State Water Resources Control Board. SWAMP. December 2002 (1st version)
|
|
Line of Evidence (LOE) for Decision ID 77895, DDE (Dichlorodiphenyldichloroethylene)
|
Region 1 |
Klamath River HU, Shasta River HA |
|
|
LOE ID: |
123163 |
|
Pollutant: |
DDE (Dichlorodiphenyldichloroethylene) |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
None |
|
Beneficial Use: |
Municipal & Domestic Supply |
|
Number of Samples: |
0 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
State Water Board staff re-assessed SWAMP data for Klamath River HU, Shasta River HA to determine beneficial use support and results are as follows: 0 of 0 samples exceed the criterion for DDE(o,p'), Total. Eight samples were removed from assessment because an appropriate evaluation guideline for the water body-pollutant combination could not be obtained for this listing cycle. This LOE re-assesses data from LOE 29849 from the 2010 Integrated Report. Data were re-assessed in order to evaluate these data in their own LOE, instead of being evaluated in the same LOE as other pesticide data. |
Data Reference: |
Surface Water Ambient Monitoring Program (SWAMP). Summary Report for the North Coast Region (RWQCB-1) for years 2000-2006. North Coast Regional Water Quality Control Board. March 2008 |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
Per the Basin Plan (NCRWQCB 2011): No individual pesticide or combination of pesticides shall be present in concentrations that adversely affect beneficial uses. There shall be no bioaccumulation of pesticide concentrations found in bottom sediments or aquatic life. Waters designated for use as domestic or municipal supply shall not contain concentrations of pesticides in excess of the limiting concentrations set forth in California Code of Regulations, Title 22, Division 4, Chapter 15, Article 4, Section 64444, and listed in Table 3.2 of the Basin Plan. No evaluation guideline could be found to evaluate protection of the MUN beneficial use that meets the requirements of Section 6.1.3 of the Listing Policy. |
Objective/Criterion Reference: |
Water Quality Control Plan (Basin Plan) for the North Coast Region |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
Data for this line of evidence for Klamath River HU, Shasta River HA was collected at 1 monitoring site [ Yreka Creek at Highway 3 - 105YREHW3] |
Temporal Representation: |
Data was collected over the time period 10/21/2004-6/20/2005. |
Environmental Conditions: |
There are no known environmental conditions (e.g., seasonality, land use practices, fire events, storms, etc.) that are related to these data. |
QAPP Information: |
Quality control was conducted in accordance with the SWAMP Quality Assurance Management Plan (SWAMP 2002). |
QAPP Information Reference(s): |
Quality Assurance Management Plan for the State of California's Surface Water Ambient Monitoring Program. Sacramento, CA. State Water Resources Control Board. SWAMP. December 2002 (1st version)
|
|
Line of Evidence (LOE) for Decision ID 77895, DDE (Dichlorodiphenyldichloroethylene)
|
Region 1 |
Klamath River HU, Shasta River HA |
|
|
LOE ID: |
123346 |
|
Pollutant: |
DDE (Dichlorodiphenyldichloroethylene) |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
None |
|
Beneficial Use: |
Municipal & Domestic Supply |
|
Number of Samples: |
0 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
State Water Board staff re-assessed SWAMP data for Klamath River HU, Shasta River HA to determine beneficial use support and results are as follows: 0 of 0 samples exceed the criterion for DDE(o,p'), Total. Thirty-three samples were removed from assessment because an appropriate evaluation guideline for the water body-pollutant combination could not be obtained for this listing cycle. This LOE re-assesses data from LOE 29849 from the 2010 Integrated Report. Data were re-assessed in order to evaluate these data in their own LOE, instead of being evaluated in the same LOE as other pesticide data. |
Data Reference: |
Surface Water Ambient Monitoring Program (SWAMP). Summary Report for the North Coast Region (RWQCB-1) for years 2000-2006. North Coast Regional Water Quality Control Board. March 2008 |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
Per the Basin Plan (NCRWQCB 2011): No individual pesticide or combination of pesticides shall be present in concentrations that adversely affect beneficial uses. There shall be no bioaccumulation of pesticide concentrations found in bottom sediments or aquatic life. Waters designated for use as domestic or municipal supply shall not contain concentrations of pesticides in excess of the limiting concentrations set forth in California Code of Regulations, Title 22, Division 4, Chapter 15, Article 4, Section 64444, and listed in Table 3.2 of the Basin Plan. No evaluation guideline could be found to evaluate protection of the MUN beneficial use that meets the requirements of Section 6.1.3 of the Listing Policy. |
Objective/Criterion Reference: |
Water Quality Control Plan (Basin Plan) for the North Coast Region |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
Data for this line of evidence for Klamath River HU, Shasta River HA was collected at 1 monitoring site [ Shasta River at Hwy 263 - 105SH1452] |
Temporal Representation: |
Data was collected over the time period 4/24/2001-11/16/2006. |
Environmental Conditions: |
There are no known environmental conditions (e.g., seasonality, land use practices, fire events, storms, etc.) that are related to these data. |
QAPP Information: |
Quality control was conducted in accordance with the SWAMP Quality Assurance Management Plan (SWAMP 2002). |
QAPP Information Reference(s): |
Quality Assurance Management Plan for the State of California's Surface Water Ambient Monitoring Program. Sacramento, CA. State Water Resources Control Board. SWAMP. December 2002 (1st version)
|
|
Line of Evidence (LOE) for Decision ID 77895, DDE (Dichlorodiphenyldichloroethylene)
|
Region 1 |
Klamath River HU, Shasta River HA |
|
|
LOE ID: |
123359 |
|
Pollutant: |
DDE (Dichlorodiphenyldichloroethylene) |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
None |
|
Beneficial Use: |
Municipal & Domestic Supply |
|
Number of Samples: |
0 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
State Water Board staff re-assessed SWAMP data for Klamath River HU, Shasta River HA to determine beneficial use support and results are as follows: 0 of 0 samples exceed the criterion for DDE(o,p'), Total. Sixteen samples were removed from assessment because an appropriate evaluation guideline for the water body-pollutant combination could not be obtained for this listing cycle. This LOE re-assesses data from LOE 29849 from the 2010 Integrated Report. Data were re-assessed in order to evaluate these data in their own LOE, instead of being evaluated in the same LOE as other pesticide data. |
Data Reference: |
Surface Water Ambient Monitoring Program (SWAMP). Summary Report for the North Coast Region (RWQCB-1) for years 2000-2006. North Coast Regional Water Quality Control Board. March 2008 |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
Per the Basin Plan (NCRWQCB 2011): No individual pesticide or combination of pesticides shall be present in concentrations that adversely affect beneficial uses. There shall be no bioaccumulation of pesticide concentrations found in bottom sediments or aquatic life. Waters designated for use as domestic or municipal supply shall not contain concentrations of pesticides in excess of the limiting concentrations set forth in California Code of Regulations, Title 22, Division 4, Chapter 15, Article 4, Section 64444, and listed in Table 3.2 of the Basin Plan. No evaluation guideline could be found to evaluate protection of the MUN beneficial use that meets the requirements of Section 6.1.3 of the Listing Policy. |
Objective/Criterion Reference: |
Water Quality Control Plan (Basin Plan) for the North Coast Region |
|
Evaluation Guideline: |
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Guideline Reference: |
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Spatial Representation: |
Data for this line of evidence for Klamath River HU, Shasta River HA was collected at 1 monitoring site [ Yreka Creek at Anderson Rd - 105YREAND] |
Temporal Representation: |
Data was collected over the time period 10/9/2002-6/20/2005. |
Environmental Conditions: |
There are no known environmental conditions (e.g., seasonality, land use practices, fire events, storms, etc.) that are related to these data. |
QAPP Information: |
Quality control was conducted in accordance with the SWAMP Quality Assurance Management Plan (SWAMP 2002). |
QAPP Information Reference(s): |
Quality Assurance Management Plan for the State of California's Surface Water Ambient Monitoring Program. Sacramento, CA. State Water Resources Control Board. SWAMP. December 2002 (1st version)
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Line of Evidence (LOE) for Decision ID 77895, DDE (Dichlorodiphenyldichloroethylene)
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Region 1 |
Klamath River HU, Shasta River HA |
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LOE ID: |
115652 |
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Pollutant: |
DDE (Dichlorodiphenyldichloroethylene) |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Total |
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Beneficial Use: |
Commercial or recreational collection of fish, shellfish, or organisms |
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Number of Samples: |
0 |
Number of Exceedances: |
0 |
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Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP RWB1 Monitoring data for Klamath River HU, Shasta River HA to determine beneficial use support, and the results are as follows: 0 of the 0 samples exceeded the evaluation guideline for DDE(p,p'). Although a total of 1 samples were collected, 1 of these samples were not included in the assessment because the laboratory data reporting limit(s) was above the objective and therefore the results could not be quantified with the level of certainty required by the Listing Policy Section 6.1.5.5. |
Data Reference: |
Water Quality Assessment Data for the 2018 solicitation cycle submitted through CEDEN for SWAMP RWB1 Monitoring .
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SWAMP Data: |
SWAMP |
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Water Quality Objective/Criterion: |
The 4,4'-DDE criterion for the protection of human health from consumption of organisms only is 0.00059 ug/L (California Toxics Rule, 2000). |
Objective/Criterion Reference: |
Water Quality Standards 2000. Establishment of numeric criteria for priority toxic pollutants for the State of California: Rules and regulations. Federal Register Vol. 65, No. 97. Washington, D.C.: Environmental Protection Agency |
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Evaluation Guideline: |
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Guideline Reference: |
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Spatial Representation: |
Data was collected from 1 station(s) (Station Code(s) 105SH1452). |
Temporal Representation: |
Date for this waterbody was collected over the date range 2013-04-29 to 2013-04-29 |
Environmental Conditions: |
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QAPP Information: |
Quality Assurance Program Plan and Standard Operating Procedures for SWAMP program |
QAPP Information Reference(s): |
Quality Assurance Program Plans, Quality Assurance Project Plans, and Standard Operating Procedures for the SWAMP program |
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Line of Evidence (LOE) for Decision ID 77895, DDE (Dichlorodiphenyldichloroethylene)
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Region 1 |
Klamath River HU, Shasta River HA |
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LOE ID: |
102361 |
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Pollutant: |
DDE (Dichlorodiphenyldichloroethylene) |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Total |
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Beneficial Use: |
Commercial or recreational collection of fish, shellfish, or organisms |
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Number of Samples: |
0 |
Number of Exceedances: |
0 |
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Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP RWB1 Monitoring data for Klamath River HU, Shasta River HA to determine beneficial use support, and the results are as follows: 0 of the 0 samples exceeded the evaluation guideline for DDE(p,p'). Although a total of 1 samples were collected, 1 of these samples were not included in the assessment because the laboratory data reporting limit(s) was above the objective and therefore the results could not be quantified with the level of certainty required by the Listing Policy Section 6.1.5.5. |
Data Reference: |
Water Quality Assessment Data for the 2018 solicitation cycle submitted through CEDEN for SWAMP RWB1 Monitoring .
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SWAMP Data: |
SWAMP |
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Water Quality Objective/Criterion: |
The 4,4'-DDE criterion for the protection of human health from consumption of organisms only is 0.00059 ug/L (California Toxics Rule, 2000). |
Objective/Criterion Reference: |
Water Quality Standards 2000. Establishment of numeric criteria for priority toxic pollutants for the State of California: Rules and regulations. Federal Register Vol. 65, No. 97. Washington, D.C.: Environmental Protection Agency |
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Evaluation Guideline: |
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Guideline Reference: |
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Spatial Representation: |
Data was collected from 1 station(s) (Station Code(s) 105SH9274). |
Temporal Representation: |
Date for this waterbody was collected over the date range 2013-04-29 to 2013-04-29 |
Environmental Conditions: |
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QAPP Information: |
Quality Assurance Program Plan and Standard Operating Procedures for SWAMP program |
QAPP Information Reference(s): |
Quality Assurance Program Plans, Quality Assurance Project Plans, and Standard Operating Procedures for the SWAMP program |
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