Line of Evidence (LOE) for Decision ID 156774, Temperature, water
|
Region 1 |
Russian River HU, Middle Russian River HA, Mark West HSA, Windsor Creek and its tributaries |
|
|
LOE ID: |
101163 |
|
Pollutant: |
Temperature, water |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Total |
|
Beneficial Use: |
Cold Freshwater Habitat |
Aquatic Life 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 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 Temperature. Data range from 6.8 degrees C. |
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: 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 Carter (2008) the lethal temperature for spawning, incubation, and emergence life stages are 20 degrees C. The lethal temperatures for adult migration and holding, and juvenile migration and rearing is 24 degrees C. |
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(s) Windsor Creek at Mark West Station (114WC1630). |
Temporal Representation: |
The samples were collected between the dates of 2/4/2014. |
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 156774, Temperature, water
|
Region 1 |
Russian River HU, Middle Russian River HA, Mark West HSA, Windsor Creek and its tributaries |
|
|
LOE ID: |
319048 |
|
Pollutant: |
Temperature, water |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
None |
|
Beneficial Use: |
Cold Freshwater Habitat |
Aquatic Life 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 temperature data for USGS California Water Science Center and determined that 0 of 2 samples are greater than the May-November maximum of 24 degrees Celcius and 0 of 4 samples are greater than the December-April maximum of 20 degrees Celcius, so that 0 of 6 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: 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 Carter (2008) the lethal temperature for spawning, incubation, and emergence life stages are 20 degrees C. The lethal temperatures for adult migration and holding, and juvenile migration and rearing is 24 degrees C. |
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: |
These samples were collected at sampling station name: WINDSOR C A MARK WEST STATION RD NR WINDSOR CA; station code: USGS-383039122502401. |
Temporal Representation: |
These samples were collected from 4/4/2017-5/9/2017. |
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 156774, Temperature, water
|
Region 1 |
Russian River HU, Middle Russian River HA, Mark West HSA, Windsor Creek and its tributaries |
|
|
LOE ID: |
47198 |
|
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: |
This LOE is a placeholder to support a 303(d) listing decision made prior to 2006. |
Data Reference: |
Placeholder reference pre-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: |
unspecified |
QAPP Information Reference(s): |
|
Line of Evidence (LOE) for Decision ID 156774, Temperature, water
|
Region 1 |
Russian River HU, Middle Russian River HA, Mark West HSA, Windsor Creek and its tributaries |
|
|
LOE ID: |
100972 |
|
Pollutant: |
Temperature, water |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Total |
|
Beneficial Use: |
Cold Freshwater Habitat |
|
Number of Samples: |
23 |
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 23 samples exceeded the water quality standard for Temperature. Data range from 4.8 - 16.1 degrees C. |
Data Reference: |
Water Quality Assessment Data for the 2018 solicitation cycle submitted through CEDEN for 2009 5 year Permit for Russian River MS4 Program.
|
|
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: 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 Carter (2008) the lethal temperature for spawning, incubation, and emergence life stages are 20 degrees C. The lethal temperatures for adult migration and holding, and juvenile migration and rearing is 24 degrees C. |
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(s) C1 - Santa Rosa Creek down gradient of urban footprint (C1-SRC-D). |
Temporal Representation: |
The samples were collected between the dates of 12/21/2010 - 6/19/2015. |
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: |
Santa Rosa NPDES Storm Water Sampling Plan |
QAPP Information Reference(s): |
Santa Rosa NPDES Storm Water Sampling Plan |
|
Line of Evidence (LOE) for Decision ID 158587, 2,4-D (2,4-Dichlorophenoxy acetic acid)
|
Region 1 |
Russian River HU, Middle Russian River HA, Mark West HSA, Windsor Creek and its tributaries |
|
|
LOE ID: |
328296 |
|
Pollutant: |
2,4-D (2,4-Dichlorophenoxy acetic acid) |
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 USGS California Water Science Center data for Russian River HU, Middle Russian River HA, Mark West HSA, Windsor Creek and its tributaries to determine beneficial use support and results are as follows: 0 of 1 samples exceeded the water quality threshold for Dichlorophenoxyacetic Acid, 2,4-. |
Data Reference: |
WQX from the NWQMP for the 2026 Integrated Report in Region 1 |
|
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 California Maximum Contaminant Level for Dichlorophenoxyacetic Acid, 2,4- incorporated by reference in the Water Quality Control Plan, North Coast Basin is 70 mg/L (California Maximum Contaminant Levels, 2012). |
Guideline Reference: |
Maximum Contaminant Levels for organic and inorganic chemicals. CCR Title 22 |
|
Spatial Representation: |
The samples were collected at 1 monitoring site: USGS-383039122502401 (WINDSOR C A MARK WEST STATION RD NR WINDSOR CA). |
Temporal Representation: |
The samples were collected between the dates of 2017-04-11 and 2017-04-11 |
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 158587, 2,4-D (2,4-Dichlorophenoxy acetic acid)
|
Region 1 |
Russian River HU, Middle Russian River HA, Mark West HSA, Windsor Creek and its tributaries |
|
|
LOE ID: |
328294 |
|
Pollutant: |
2,4-D (2,4-Dichlorophenoxy acetic acid) |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Dissolved |
|
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 USGS California Water Science Center data for Russian River HU, Middle Russian River HA, Mark West HSA, Windsor Creek and its tributaries to determine beneficial use support and results are as follows: 0 of 1 samples exceeded the water quality threshold for Dichlorophenoxyacetic Acid, 2,4-. |
Data Reference: |
WQX from the NWQMP for the 2026 Integrated Report in Region 1 |
|
SWAMP Data: |
Non-SWAMP |
|
Water Quality Objective/Criterion: |
Waters shall not contain toxic substances in concentrations that are toxic to, or that produce detrimental physiological responses in human, plant, animal, or aquatic life. (Basin Plan, 2018) |
Objective/Criterion Reference: |
Water Quality Control Plan (Basin Plan) for the North Coast Region |
|
Evaluation Guideline: |
The USEPA recommended criterion for 2,4-D for the protection of human health from the consumption of organisms only is 1,300 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: USGS-383039122502401 (WINDSOR C A MARK WEST STATION RD NR WINDSOR CA). |
Temporal Representation: |
The samples were collected between the dates of 2017-04-11 and 2017-04-11 |
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 158587, 2,4-D (2,4-Dichlorophenoxy acetic acid)
|
Region 1 |
Russian River HU, Middle Russian River HA, Mark West HSA, Windsor Creek and its tributaries |
|
|
LOE ID: |
328297 |
|
Pollutant: |
2,4-D (2,4-Dichlorophenoxy acetic acid) |
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 USGS California Water Science Center data for Russian River HU, Middle Russian River HA, Mark West HSA, Windsor Creek and its tributaries to determine beneficial use support and results are as follows: 0 of 1 samples exceeded the water quality threshold for Dichlorophenoxyacetic Acid, 2,4-. |
Data Reference: |
WQX from the NWQMP for the 2026 Integrated Report in Region 1 |
|
SWAMP Data: |
Non-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 Dichlorophenoxyacetic Acid, 2,4- is the USEPA Aquatic Life Benchmark of 299.2 ug/L for a vascular plant (acute). |
Guideline Reference: |
OPP Aquatic Life Benchmarks |
|
Spatial Representation: |
The samples were collected at 1 monitoring site: USGS-383039122502401 (WINDSOR C A MARK WEST STATION RD NR WINDSOR CA). |
Temporal Representation: |
The samples were collected between the dates of 2017-04-11 and 2017-04-11 |
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 158587, 2,4-D (2,4-Dichlorophenoxy acetic acid)
|
Region 1 |
Russian River HU, Middle Russian River HA, Mark West HSA, Windsor Creek and its tributaries |
|
|
LOE ID: |
328292 |
|
Pollutant: |
2,4-D (2,4-Dichlorophenoxy acetic acid) |
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 USGS California Water Science Center data for Russian River HU, Middle Russian River HA, Mark West HSA, Windsor Creek and its tributaries to determine beneficial use support and results are as follows: 0 of 1 samples exceeded the water quality threshold for Dichlorophenoxyacetic Acid, 2,4-. |
Data Reference: |
WQX from the NWQMP for the 2026 Integrated Report in Region 1 |
|
SWAMP Data: |
Non-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 Dichlorophenoxyacetic Acid, 2,4- is the USEPA Aquatic Life Benchmark of 299.2 ug/L for a vascular plant (acute). |
Guideline Reference: |
OPP Aquatic Life Benchmarks |
|
Spatial Representation: |
The samples were collected at 1 monitoring site: USGS-383039122502401 (WINDSOR C A MARK WEST STATION RD NR WINDSOR CA). |
Temporal Representation: |
The samples were collected between the dates of 2017-04-11 and 2017-04-11 |
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 169830, Aldicarb
|
Region 1 |
Russian River HU, Middle Russian River HA, Mark West HSA, Windsor Creek and its tributaries |
|
|
LOE ID: |
348941 |
|
Pollutant: |
Aldicarb |
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 Russian River HU, Middle Russian River HA, Mark West HSA, Windsor Creek and its tributaries to determine beneficial use support and results are as follows: 0 of 1 samples exceeded the water quality threshold for Aldicarb. |
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 aldicarb is the USEPA Aquatic Life Benchmark of 0.46 ug/L for a fish (chronic). |
Guideline Reference: |
OPP Aquatic Life Benchmarks |
|
Spatial Representation: |
The samples were collected at 1 monitoring site: 114WC1630 (Windsor Creek at Mark West Station). |
Temporal Representation: |
The samples were collected between the dates of 2014-02-04 and 2014-02-04 |
Environmental Conditions: |
|
QAPP Information: |
Generic SWAMP QAPrP |
QAPP Information Reference(s): |
Generic SWAMP QAPrP |
|
Line of Evidence (LOE) for Decision ID 169830, Aldicarb
|
Region 1 |
Russian River HU, Middle Russian River HA, Mark West HSA, Windsor Creek and its tributaries |
|
|
LOE ID: |
348940 |
|
Pollutant: |
Aldicarb |
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 Russian River HU, Middle Russian River HA, Mark West HSA, Windsor Creek and its tributaries to determine beneficial use support and results are as follows: 0 of 1 samples exceeded the water quality threshold for Aldicarb. |
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 aldicarb is the USEPA Aquatic Life Benchmark of 0.46 ug/L for a fish (chronic). |
Guideline Reference: |
OPP Aquatic Life Benchmarks |
|
Spatial Representation: |
The samples were collected at 1 monitoring site: 114WC1630 (Windsor Creek at Mark West Station). |
Temporal Representation: |
The samples were collected between the dates of 2014-02-04 and 2014-02-04 |
Environmental Conditions: |
|
QAPP Information: |
Generic SWAMP QAPrP |
QAPP Information Reference(s): |
Generic SWAMP QAPrP |
|
Line of Evidence (LOE) for Decision ID 104119, Aminomethyl Phosphonic Acid (AMPA)
|
Region 1 |
Russian River HU, Middle Russian River HA, Mark West HSA, Windsor Creek and its tributaries |
|
|
LOE ID: |
117315 |
|
Pollutant: |
Aminomethyl Phosphonic Acid (AMPA) |
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 Russian River HU, Middle Russian River HA, Mark West HSA, Windsor Creek and its tributaries to determine beneficial use support and results are as follows: 0 of 1 samples exceeded the water quality standard for AMPA. |
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 AMPA is the USEPA Aquatic Life Benchmark of 249500 ug/L for a fish (acute). |
Guideline Reference: |
OPP Aquatic Life Benchmarks |
|
Spatial Representation: |
The samples were collected at 1 monitoring site(s) (114WC1630) |
Temporal Representation: |
The samples were collected between the dates of 2014-02-04 and 2014-02-04 |
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 104119, Aminomethyl Phosphonic Acid (AMPA)
|
Region 1 |
Russian River HU, Middle Russian River HA, Mark West HSA, Windsor Creek and its tributaries |
|
|
LOE ID: |
117313 |
|
Pollutant: |
Aminomethyl Phosphonic Acid (AMPA) |
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 Russian River HU, Middle Russian River HA, Mark West HSA, Windsor Creek and its tributaries to determine beneficial use support and results are as follows: 0 of 1 samples exceeded the water quality standard for AMPA. |
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 AMPA is the USEPA Aquatic Life Benchmark of 249500 ug/L for a fish (acute). |
Guideline Reference: |
OPP Aquatic Life Benchmarks |
|
Spatial Representation: |
The samples were collected at 1 monitoring site(s) (114WC1630) |
Temporal Representation: |
The samples were collected between the dates of 2014-02-04 and 2014-02-04 |
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 158601, Azoxystrobin
|
Region 1 |
Russian River HU, Middle Russian River HA, Mark West HSA, Windsor Creek and its tributaries |
|
|
LOE ID: |
328043 |
|
Pollutant: |
Azoxystrobin |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Dissolved |
|
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 USGS California Water Science Center data for Russian River HU, Middle Russian River HA, Mark West HSA, Windsor Creek and its tributaries to determine beneficial use support and results are as follows: 0 of 6 samples exceeded the water quality threshold for Azoxystrobin. |
Data Reference: |
WQX from the NWQMP for the 2026 Integrated Report in Region 1 |
|
SWAMP Data: |
Non-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 Azoxystrobin is the USEPA Aquatic Life Benchmark of 44 ug/L for an invertebrate (chronic). |
Guideline Reference: |
OPP Aquatic Life Benchmarks |
|
Spatial Representation: |
The samples were collected at 1 monitoring site: USGS-383039122502401 (WINDSOR C A MARK WEST STATION RD NR WINDSOR CA). |
Temporal Representation: |
The samples were collected between the dates of 2017-04-04 and 2017-05-09 |
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 158601, Azoxystrobin
|
Region 1 |
Russian River HU, Middle Russian River HA, Mark West HSA, Windsor Creek and its tributaries |
|
|
LOE ID: |
328042 |
|
Pollutant: |
Azoxystrobin |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Dissolved |
|
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 USGS California Water Science Center data for Russian River HU, Middle Russian River HA, Mark West HSA, Windsor Creek and its tributaries to determine beneficial use support and results are as follows: 0 of 6 samples exceeded the water quality threshold for Azoxystrobin. |
Data Reference: |
WQX from the NWQMP for the 2026 Integrated Report in Region 1 |
|
SWAMP Data: |
Non-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 Azoxystrobin is the USEPA Aquatic Life Benchmark of 44 ug/L for an invertebrate (chronic). |
Guideline Reference: |
OPP Aquatic Life Benchmarks |
|
Spatial Representation: |
The samples were collected at 1 monitoring site: USGS-383039122502401 (WINDSOR C A MARK WEST STATION RD NR WINDSOR CA). |
Temporal Representation: |
The samples were collected between the dates of 2017-04-04 and 2017-05-09 |
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 169827, Bifenthrin
|
Region 1 |
Russian River HU, Middle Russian River HA, Mark West HSA, Windsor Creek and its tributaries |
|
|
LOE ID: |
349046 |
|
Pollutant: |
Bifenthrin |
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 Russian River HU, Middle Russian River HA, Mark West HSA, Windsor Creek and its tributaries to determine beneficial use support, and the results are as follows: 0 of the 0 samples exceeded the evaluation guideline for Bifenthrin. 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 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: |
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 chronic criterion for bifenthrin is 0.1 ng/L (expressed as a 4-day average). If the freely dissolved concentrations of bifenthrin were reported or could be calculated then these values were used for this assessment. In the absence of freely dissolved concentrations, total concentrations were used. |
Guideline Reference: |
Water Quality Criteria Report for Bifenthrin |
|
Spatial Representation: |
The samples were collected at 1 monitoring site: 114WC1630 (Windsor Creek at Mark West Station). |
Temporal Representation: |
The samples were collected between the dates of 2014-02-04 and 2014-02-04 |
Environmental Conditions: |
|
QAPP Information: |
Generic SWAMP QAPrP |
QAPP Information Reference(s): |
Generic SWAMP QAPrP |
|
Line of Evidence (LOE) for Decision ID 169827, Bifenthrin
|
Region 1 |
Russian River HU, Middle Russian River HA, Mark West HSA, Windsor Creek and its tributaries |
|
|
LOE ID: |
349045 |
|
Pollutant: |
Bifenthrin |
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 Russian River HU, Middle Russian River HA, Mark West HSA, Windsor Creek and its tributaries to determine beneficial use support, and the results are as follows: 0 of the 0 samples exceeded the evaluation guideline for Bifenthrin. 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 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: |
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 chronic criterion for bifenthrin is 0.1 ng/L (expressed as a 4-day average). If the freely dissolved concentrations of bifenthrin were reported or could be calculated then these values were used for this assessment. In the absence of freely dissolved concentrations, total concentrations were used. |
Guideline Reference: |
Water Quality Criteria Report for Bifenthrin |
|
Spatial Representation: |
The samples were collected at 1 monitoring site: 114WC1630 (Windsor Creek at Mark West Station). |
Temporal Representation: |
The samples were collected between the dates of 2014-02-04 and 2014-02-04 |
Environmental Conditions: |
|
QAPP Information: |
Generic SWAMP QAPrP |
QAPP Information Reference(s): |
Generic SWAMP QAPrP |
|
Line of Evidence (LOE) for Decision ID 158583, Chloride
|
Region 1 |
Russian River HU, Middle Russian River HA, Mark West HSA, Windsor Creek and its tributaries |
|
|
LOE ID: |
117316 |
|
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 RWB1 Monitoring data for Russian River HU, Middle Russian River HA, Mark West HSA, Windsor Creek and its tributaries 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 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) (114WC1630) |
Temporal Representation: |
The samples were collected between the dates of 2014-02-04 and 2014-02-04 |
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 158583, Chloride
|
Region 1 |
Russian River HU, Middle Russian River HA, Mark West HSA, Windsor Creek and its tributaries |
|
|
LOE ID: |
328178 |
|
Pollutant: |
Chloride |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Dissolved |
|
Beneficial Use: |
Municipal & Domestic Supply |
|
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 USGS California Water Science Center data for Russian River HU, Middle Russian River HA, Mark West HSA, Windsor Creek and its tributaries to determine beneficial use support and results are as follows: 0 of 6 samples exceeded the water quality threshold for Chloride. |
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 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: USGS-383039122502401 (WINDSOR C A MARK WEST STATION RD NR WINDSOR CA). |
Temporal Representation: |
The samples were collected between the dates of 2017-04-04 and 2017-05-09 |
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 158583, Chloride
|
Region 1 |
Russian River HU, Middle Russian River HA, Mark West HSA, Windsor Creek and its tributaries |
|
|
LOE ID: |
328163 |
|
Pollutant: |
Chloride |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Dissolved |
|
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 USGS California Water Science Center data for Russian River HU, Middle Russian River HA, Mark West HSA, Windsor Creek and its tributaries to determine beneficial use support and results are as follows: 0 of 6 samples exceeded the water quality threshold for Chloride. |
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 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: USGS-383039122502401 (WINDSOR C A MARK WEST STATION RD NR WINDSOR CA). |
Temporal Representation: |
The samples were collected between the dates of 2017-04-04 and 2017-05-09 |
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 167715, Chlorpyrifos
|
Region 1 |
Russian River HU, Middle Russian River HA, Mark West HSA, Windsor Creek and its tributaries |
|
|
LOE ID: |
117319 |
|
Pollutant: |
Chlorpyrifos |
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 Russian River HU, Middle Russian River HA, Mark West HSA, Windsor Creek and its tributaries to determine beneficial use support and results are as follows: 0 of 1 samples exceeded the water quality standard for Chlorpyrifos. |
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. |
Objective/Criterion Reference: |
Water Quality Control Plan (Basin Plan) for the North Coast Region |
|
Evaluation Guideline: |
The USEPA drinking water health advisory for chlorpyrifos is 2 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) (114WC1630) |
Temporal Representation: |
The samples were collected between the dates of 2014-02-04 and 2014-02-04 |
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 167715, Chlorpyrifos
|
Region 1 |
Russian River HU, Middle Russian River HA, Mark West HSA, Windsor Creek and its tributaries |
|
|
LOE ID: |
113244 |
|
Pollutant: |
Chlorpyrifos |
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 Russian River HU, Middle Russian River HA, Mark West HSA, Windsor Creek and its tributaries to determine beneficial use support, and the results are as follows: 0 of the 0 samples exceeded the evaluation guideline for Chlorpyrifos. 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: |
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 freshwater criterion continuous concentration to protect aquatic organisms is 0.014 ug/L (Siepmann and Finlayson 2000). |
Guideline Reference: |
Water quality criteria for diazinon and chlorpyrifos. Administrative Report 00-3. Rancho Cordova, CA: Pesticide Investigations Unit, Office of Spills and Response. CA Department of Fish and Game |
|
Spatial Representation: |
Data was collected from 1 station(s) (Station Code(s) 114WC1630). |
Temporal Representation: |
Date for this waterbody was collected over the date range 2014-02-04 to 2014-02-04 |
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 167716, Chlorpyrifos, methyl
|
Region 1 |
Russian River HU, Middle Russian River HA, Mark West HSA, Windsor Creek and its tributaries |
|
|
LOE ID: |
117318 |
|
Pollutant: |
Chlorpyrifos, methyl |
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 Russian River HU, Middle Russian River HA, Mark West HSA, Windsor Creek and its tributaries to determine beneficial use support and results are as follows: 0 of 1 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) (114WC1630) |
Temporal Representation: |
The samples were collected between the dates of 2014-02-04 and 2014-02-04 |
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 167716, Chlorpyrifos, methyl
|
Region 1 |
Russian River HU, Middle Russian River HA, Mark West HSA, Windsor Creek and its tributaries |
|
|
LOE ID: |
117317 |
|
Pollutant: |
Chlorpyrifos, methyl |
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 Russian River HU, Middle Russian River HA, Mark West HSA, Windsor Creek and its tributaries to determine beneficial use support and results are as follows: 0 of 1 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) (114WC1630) |
Temporal Representation: |
The samples were collected between the dates of 2014-02-04 and 2014-02-04 |
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 167717, Cinerin
|
Region 1 |
Russian River HU, Middle Russian River HA, Mark West HSA, Windsor Creek and its tributaries |
|
|
LOE ID: |
349110 |
|
Pollutant: |
Cinerin |
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 Russian River HU, Middle Russian River HA, Mark West HSA, Windsor Creek and its tributaries to determine beneficial use support and results are as follows: 0 of 1 samples exceeded the water quality threshold for Cinerin. |
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 cinerin is the USEPA Aquatic Life Benchmark of 0.04 ug/L for freshwater invertebrates (chronic) and is the sum of cinerin-1 and cinerin-2. |
Guideline Reference: |
OPP Aquatic Life Benchmarks |
|
Spatial Representation: |
The samples were collected at 1 monitoring site: 114WC1630 (Windsor Creek at Mark West Station). |
Temporal Representation: |
The samples were collected between the dates of 2014-02-04 and 2014-02-04 |
Environmental Conditions: |
|
QAPP Information: |
Generic SWAMP QAPrP |
QAPP Information Reference(s): |
Generic SWAMP QAPrP |
|
Line of Evidence (LOE) for Decision ID 167717, Cinerin
|
Region 1 |
Russian River HU, Middle Russian River HA, Mark West HSA, Windsor Creek and its tributaries |
|
|
LOE ID: |
349121 |
|
Pollutant: |
Cinerin |
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 Russian River HU, Middle Russian River HA, Mark West HSA, Windsor Creek and its tributaries to determine beneficial use support and results are as follows: 0 of 1 samples exceeded the water quality threshold for Cinerin. |
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 cinerin is the USEPA Aquatic Life Benchmark of 0.04 ug/L for freshwater invertebrates (chronic) and is the sum of cinerin-1 and cinerin-2. |
Guideline Reference: |
OPP Aquatic Life Benchmarks |
|
Spatial Representation: |
The samples were collected at 1 monitoring site: 114WC1630 (Windsor Creek at Mark West Station). |
Temporal Representation: |
The samples were collected between the dates of 2014-02-04 and 2014-02-04 |
Environmental Conditions: |
|
QAPP Information: |
Generic SWAMP QAPrP |
QAPP Information Reference(s): |
Generic SWAMP QAPrP |
|
Line of Evidence (LOE) for Decision ID 167718, Coumaphos
|
Region 1 |
Russian River HU, Middle Russian River HA, Mark West HSA, Windsor Creek and its tributaries |
|
|
LOE ID: |
110312 |
|
Pollutant: |
Coumaphos |
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 Russian River HU, Middle Russian River HA, Mark West HSA, Windsor Creek and its tributaries to determine beneficial use support, and the results are as follows: 0 of the 0 samples exceeded the evaluation guideline for Coumaphos. 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: |
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 Coumaphos is the USEPA Aquatic Life Benchmark of 0.0337 ug/L for an invertebrate (chronic). |
Guideline Reference: |
OPP Aquatic Life Benchmarks |
|
Spatial Representation: |
Data was collected from 1 station(s) (Station Code(s) 114WC1630). |
Temporal Representation: |
Date for this waterbody was collected over the date range 2014-02-04 to 2014-02-04 |
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 167718, Coumaphos
|
Region 1 |
Russian River HU, Middle Russian River HA, Mark West HSA, Windsor Creek and its tributaries |
|
|
LOE ID: |
116181 |
|
Pollutant: |
Coumaphos |
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 Russian River HU, Middle Russian River HA, Mark West HSA, Windsor Creek and its tributaries to determine beneficial use support, and the results are as follows: 0 of the 0 samples exceeded the evaluation guideline for Coumaphos. 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: |
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 Coumaphos is the USEPA Aquatic Life Benchmark of 0.0337 ug/L for an invertebrate (chronic). |
Guideline Reference: |
OPP Aquatic Life Benchmarks |
|
Spatial Representation: |
Data was collected from 1 station(s) (Station Code(s) 114WC1630). |
Temporal Representation: |
Date for this waterbody was collected over the date range 2014-02-04 to 2014-02-04 |
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 169831, Cyfluthrin
|
Region 1 |
Russian River HU, Middle Russian River HA, Mark West HSA, Windsor Creek and its tributaries |
|
|
LOE ID: |
349180 |
|
Pollutant: |
Cyfluthrin |
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 Russian River HU, Middle Russian River HA, Mark West HSA, Windsor Creek and its tributaries to determine beneficial use support, and the results are as follows: 0 of the 0 samples exceeded the evaluation guideline for Cyfluthrin. 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 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: |
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 chronic criterion for cyfluthrin is 0.2 ng/L (expressed as a 4-day average). If the freely dissolved concentrations of cyfluthrin were reported or could be calculated then these values were used for this assessment. In the absence of freely dissolved concentrations, total concentrations were used. |
Guideline Reference: |
Water Quality Criteria Report for Cyfluthrin |
|
Spatial Representation: |
The samples were collected at 1 monitoring site: 114WC1630 (Windsor Creek at Mark West Station). |
Temporal Representation: |
The samples were collected between the dates of 2014-02-04 and 2014-02-04 |
Environmental Conditions: |
|
QAPP Information: |
Generic SWAMP QAPrP |
QAPP Information Reference(s): |
Generic SWAMP QAPrP |
|
Line of Evidence (LOE) for Decision ID 169831, Cyfluthrin
|
Region 1 |
Russian River HU, Middle Russian River HA, Mark West HSA, Windsor Creek and its tributaries |
|
|
LOE ID: |
349175 |
|
Pollutant: |
Cyfluthrin |
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 Russian River HU, Middle Russian River HA, Mark West HSA, Windsor Creek and its tributaries to determine beneficial use support, and the results are as follows: 0 of the 0 samples exceeded the evaluation guideline for Cyfluthrin. 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 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: |
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 chronic criterion for cyfluthrin is 0.2 ng/L (expressed as a 4-day average). If the freely dissolved concentrations of cyfluthrin were reported or could be calculated then these values were used for this assessment. In the absence of freely dissolved concentrations, total concentrations were used. |
Guideline Reference: |
Water Quality Criteria Report for Cyfluthrin |
|
Spatial Representation: |
The samples were collected at 1 monitoring site: 114WC1630 (Windsor Creek at Mark West Station). |
Temporal Representation: |
The samples were collected between the dates of 2014-02-04 and 2014-02-04 |
Environmental Conditions: |
|
QAPP Information: |
Generic SWAMP QAPrP |
QAPP Information Reference(s): |
Generic SWAMP QAPrP |
|
Line of Evidence (LOE) for Decision ID 169833, Cyhalothrin, Lambda
|
Region 1 |
Russian River HU, Middle Russian River HA, Mark West HSA, Windsor Creek and its tributaries |
|
|
LOE ID: |
349914 |
|
Pollutant: |
Cyhalothrin, Lambda |
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 Russian River HU, Middle Russian River HA, Mark West HSA, Windsor Creek and its tributaries to determine beneficial use support, and the results are as follows: 0 of the 0 samples exceeded the evaluation guideline for Lambda-cyhalothrin. 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 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: |
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 chronic criterion for lambda-cyhalothrin is 0.3 ng/L (expressed as a 4-day average). If the freely dissolved concentrations of lambda-cyhalothrin were reported or could be calculated then these values were used for this assessment. In the absence of freely dissolved concentrations, total concentrations were used. |
Guideline Reference: |
Water Quality Criteria Report for Lambda-cyhalothrin |
|
Spatial Representation: |
The samples were collected at 1 monitoring site: 114WC1630 (Windsor Creek at Mark West Station). |
Temporal Representation: |
The samples were collected between the dates of 2014-02-04 and 2014-02-04 |
Environmental Conditions: |
|
QAPP Information: |
Generic SWAMP QAPrP |
QAPP Information Reference(s): |
Generic SWAMP QAPrP |
|
Line of Evidence (LOE) for Decision ID 169833, Cyhalothrin, Lambda
|
Region 1 |
Russian River HU, Middle Russian River HA, Mark West HSA, Windsor Creek and its tributaries |
|
|
LOE ID: |
349923 |
|
Pollutant: |
Cyhalothrin, Lambda |
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 Russian River HU, Middle Russian River HA, Mark West HSA, Windsor Creek and its tributaries to determine beneficial use support, and the results are as follows: 0 of the 0 samples exceeded the evaluation guideline for Lambda-cyhalothrin. 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 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: |
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 chronic criterion for lambda-cyhalothrin is 0.3 ng/L (expressed as a 4-day average). If the freely dissolved concentrations of lambda-cyhalothrin were reported or could be calculated then these values were used for this assessment. In the absence of freely dissolved concentrations, total concentrations were used. |
Guideline Reference: |
Water Quality Criteria Report for Lambda-cyhalothrin |
|
Spatial Representation: |
The samples were collected at 1 monitoring site: 114WC1630 (Windsor Creek at Mark West Station). |
Temporal Representation: |
The samples were collected between the dates of 2014-02-04 and 2014-02-04 |
Environmental Conditions: |
|
QAPP Information: |
Generic SWAMP QAPrP |
QAPP Information Reference(s): |
Generic SWAMP QAPrP |
|
Line of Evidence (LOE) for Decision ID 169828, Cypermethrin
|
Region 1 |
Russian River HU, Middle Russian River HA, Mark West HSA, Windsor Creek and its tributaries |
|
|
LOE ID: |
349250 |
|
Pollutant: |
Cypermethrin |
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 Russian River HU, Middle Russian River HA, Mark West HSA, Windsor Creek and its tributaries to determine beneficial use support, and the results are as follows: 0 of the 0 samples exceeded the evaluation guideline for Cypermethrin. 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 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 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 chronic criterion for cypermethrin is 0.3 ng/L (expressed as a 4-day average). If the freely dissolved concentrations of cypermethrin were reported or could be calculated then these values were used for this assessment. In the absence of freely dissolved concentrations, total concentrations were used. |
Guideline Reference: |
Water Quality Criteria Report for Cypermethrin |
|
Spatial Representation: |
The samples were collected at 1 monitoring site: 114WC1630 (Windsor Creek at Mark West Station). |
Temporal Representation: |
The samples were collected between the dates of 2014-02-04 and 2014-02-04 |
Environmental Conditions: |
|
QAPP Information: |
Generic SWAMP QAPrP |
QAPP Information Reference(s): |
Generic SWAMP QAPrP |
|
Line of Evidence (LOE) for Decision ID 169828, Cypermethrin
|
Region 1 |
Russian River HU, Middle Russian River HA, Mark West HSA, Windsor Creek and its tributaries |
|
|
LOE ID: |
349240 |
|
Pollutant: |
Cypermethrin |
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 Russian River HU, Middle Russian River HA, Mark West HSA, Windsor Creek and its tributaries to determine beneficial use support, and the results are as follows: 0 of the 0 samples exceeded the evaluation guideline for Cypermethrin. 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 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 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 chronic criterion for cypermethrin is 0.3 ng/L (expressed as a 4-day average). If the freely dissolved concentrations of cypermethrin were reported or could be calculated then these values were used for this assessment. In the absence of freely dissolved concentrations, total concentrations were used. |
Guideline Reference: |
Water Quality Criteria Report for Cypermethrin |
|
Spatial Representation: |
The samples were collected at 1 monitoring site: 114WC1630 (Windsor Creek at Mark West Station). |
Temporal Representation: |
The samples were collected between the dates of 2014-02-04 and 2014-02-04 |
Environmental Conditions: |
|
QAPP Information: |
Generic SWAMP QAPrP |
QAPP Information Reference(s): |
Generic SWAMP QAPrP |
|
Line of Evidence (LOE) for Decision ID 169832, Deltamethrin
|
Region 1 |
Russian River HU, Middle Russian River HA, Mark West HSA, Windsor Creek and its tributaries |
|
|
LOE ID: |
349346 |
|
Pollutant: |
Deltamethrin |
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 Russian River HU, Middle Russian River HA, Mark West HSA, Windsor Creek and its tributaries to determine beneficial use support, and the results are as follows: 0 of the 0 samples exceeded the evaluation guideline for Deltamethrin. 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 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: |
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 evaluation guideline for deltamethrin is the USEPA Aquatic Life Benchmark of 0.000026 ug/L for an invertebrate (chronic). |
Guideline Reference: |
OPP Aquatic Life Benchmarks |
|
Spatial Representation: |
The samples were collected at 1 monitoring site: 114WC1630 (Windsor Creek at Mark West Station). |
Temporal Representation: |
The samples were collected between the dates of 2014-02-04 and 2014-02-04 |
Environmental Conditions: |
|
QAPP Information: |
Generic SWAMP QAPrP |
QAPP Information Reference(s): |
Generic SWAMP QAPrP |
|
Line of Evidence (LOE) for Decision ID 169832, Deltamethrin
|
Region 1 |
Russian River HU, Middle Russian River HA, Mark West HSA, Windsor Creek and its tributaries |
|
|
LOE ID: |
349359 |
|
Pollutant: |
Deltamethrin |
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 Russian River HU, Middle Russian River HA, Mark West HSA, Windsor Creek and its tributaries to determine beneficial use support, and the results are as follows: 0 of the 0 samples exceeded the evaluation guideline for Deltamethrin. 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 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 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 deltamethrin is the USEPA Aquatic Life Benchmark of 0.000026 ug/L for an invertebrate (chronic). |
Guideline Reference: |
OPP Aquatic Life Benchmarks |
|
Spatial Representation: |
The samples were collected at 1 monitoring site: 114WC1630 (Windsor Creek at Mark West Station). |
Temporal Representation: |
The samples were collected between the dates of 2014-02-04 and 2014-02-04 |
Environmental Conditions: |
|
QAPP Information: |
Generic SWAMP QAPrP |
QAPP Information Reference(s): |
Generic SWAMP QAPrP |
|
Line of Evidence (LOE) for Decision ID 167719, Diazinon
|
Region 1 |
Russian River HU, Middle Russian River HA, Mark West HSA, Windsor Creek and its tributaries |
|
|
LOE ID: |
117327 |
|
Pollutant: |
Diazinon |
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 Russian River HU, Middle Russian River HA, Mark West HSA, Windsor Creek and its tributaries to determine beneficial use support and results are as follows: 0 of 1 samples exceeded the water quality standard for Diazinon. |
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. |
Objective/Criterion Reference: |
Water Quality Control Plan (Basin Plan) for the North Coast Region |
|
Evaluation Guideline: |
Based on USEPA reference dose (RfD) as a drinking water level, the drinking water health advisory level for Diazinon is 1.4 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) (114WC1630) |
Temporal Representation: |
The samples were collected between the dates of 2014-02-04 and 2014-02-04 |
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 167719, Diazinon
|
Region 1 |
Russian River HU, Middle Russian River HA, Mark West HSA, Windsor Creek and its tributaries |
|
|
LOE ID: |
117323 |
|
Pollutant: |
Diazinon |
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 Russian River HU, Middle Russian River HA, Mark West HSA, Windsor Creek and its tributaries to determine beneficial use support and results are as follows: 0 of 1 samples exceeded the water quality standard for Diazinon. |
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. |
Objective/Criterion Reference: |
Water Quality Control Plan (Basin Plan) for the North Coast Region |
|
Evaluation Guideline: |
The freshwater chronic value for diazinon is 0.1 ug/L, expressed as a continuous concentration (Finlayson, 2004). |
Guideline Reference: |
Water quality for diazinon. Memorandum to J. Karkoski, Central Valley RWQCB. Rancho Cordova, CA: Pesticide Investigation Unit, CA Department of Fish and Game |
|
Spatial Representation: |
The samples were collected at 1 monitoring site(s) (114WC1630) |
Temporal Representation: |
The samples were collected between the dates of 2014-02-04 and 2014-02-04 |
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 104231, Dimethoate
|
Region 1 |
Russian River HU, Middle Russian River HA, Mark West HSA, Windsor Creek and its tributaries |
|
|
LOE ID: |
117328 |
|
Pollutant: |
Dimethoate |
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 Russian River HU, Middle Russian River HA, Mark West HSA, Windsor Creek and its tributaries to determine beneficial use support and results are as follows: 0 of 1 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) (114WC1630) |
Temporal Representation: |
The samples were collected between the dates of 2014-02-04 and 2014-02-04 |
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 104231, Dimethoate
|
Region 1 |
Russian River HU, Middle Russian River HA, Mark West HSA, Windsor Creek and its tributaries |
|
|
LOE ID: |
117329 |
|
Pollutant: |
Dimethoate |
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 Russian River HU, Middle Russian River HA, Mark West HSA, Windsor Creek and its tributaries to determine beneficial use support and results are as follows: 0 of 1 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) (114WC1630) |
Temporal Representation: |
The samples were collected between the dates of 2014-02-04 and 2014-02-04 |
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 103542, Disulfoton
|
Region 1 |
Russian River HU, Middle Russian River HA, Mark West HSA, Windsor Creek and its tributaries |
|
|
LOE ID: |
117332 |
|
Pollutant: |
Disulfoton |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Total |
|
Beneficial Use: |
Warm 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 SWAMP RWB1 Monitoring data for Russian River HU, Middle Russian River HA, Mark West HSA, Windsor Creek and its tributaries to determine beneficial use support and results are as follows: 1 of 1 samples exceeded the water quality standard for Disulfoton. |
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 Disulfoton is the USEPA Aquatic Life Benchmark of 0.01 ug/L for an invertebrate (chronic). |
Guideline Reference: |
OPP Aquatic Life Benchmarks |
|
Spatial Representation: |
The samples were collected at 1 monitoring site(s) (114WC1630) |
Temporal Representation: |
The samples were collected between the dates of 2014-02-04 and 2014-02-04 |
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 103542, Disulfoton
|
Region 1 |
Russian River HU, Middle Russian River HA, Mark West HSA, Windsor Creek and its tributaries |
|
|
LOE ID: |
117331 |
|
Pollutant: |
Disulfoton |
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 Russian River HU, Middle Russian River HA, Mark West HSA, Windsor Creek and its tributaries to determine beneficial use support and results are as follows: 0 of 1 samples exceeded the water quality standard for Disulfoton. |
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 lifetime health advisory for disulfoton is 0.7 µg/L. The Lifetime HA is based on exposure of a 70-kg adult consuming 2 liters of a water a day. |
Guideline Reference: |
2012 Edition of the Drinking Water Standards and Health Advisories |
|
Spatial Representation: |
The samples were collected at 1 monitoring site(s) (114WC1630) |
Temporal Representation: |
The samples were collected between the dates of 2014-02-04 and 2014-02-04 |
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 103542, Disulfoton
|
Region 1 |
Russian River HU, Middle Russian River HA, Mark West HSA, Windsor Creek and its tributaries |
|
|
LOE ID: |
117330 |
|
Pollutant: |
Disulfoton |
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 SWAMP RWB1 Monitoring data for Russian River HU, Middle Russian River HA, Mark West HSA, Windsor Creek and its tributaries to determine beneficial use support and results are as follows: 1 of 1 samples exceeded the water quality standard for Disulfoton. |
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 Disulfoton is the USEPA Aquatic Life Benchmark of 0.01 ug/L for an invertebrate (chronic). |
Guideline Reference: |
OPP Aquatic Life Benchmarks |
|
Spatial Representation: |
The samples were collected at 1 monitoring site(s) (114WC1630) |
Temporal Representation: |
The samples were collected between the dates of 2014-02-04 and 2014-02-04 |
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 158584, Diuron
|
Region 1 |
Russian River HU, Middle Russian River HA, Mark West HSA, Windsor Creek and its tributaries |
|
|
LOE ID: |
328304 |
|
Pollutant: |
Diuron |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Dissolved |
|
Beneficial Use: |
Warm Freshwater Habitat |
|
Number of Samples: |
2 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed USGS California Water Science Center data for Russian River HU, Middle Russian River HA, Mark West HSA, Windsor Creek and its tributaries to determine beneficial use support and results are as follows: 0 of 2 samples exceeded the water quality threshold for Diuron. |
Data Reference: |
WQX from the NWQMP for the 2026 Integrated Report in Region 1 |
|
SWAMP Data: |
Non-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: |
Aquatic life should not be affected unacceptably if the 4-day average concentration of diuron does not exceed 1.3 ug/L (UC Davis Aquatic Life Criteria). |
Guideline Reference: |
Aquatic life water quality criteria derived via the UC Davis method: III. Diuron. Reviews of Environmental Contamination and Toxicology 216:105-141. |
|
Spatial Representation: |
The samples were collected at 1 monitoring site: USGS-383039122502401 (WINDSOR C A MARK WEST STATION RD NR WINDSOR CA). |
Temporal Representation: |
The samples were collected between the dates of 2017-05-02 and 2017-05-09 |
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 158584, Diuron
|
Region 1 |
Russian River HU, Middle Russian River HA, Mark West HSA, Windsor Creek and its tributaries |
|
|
LOE ID: |
328305 |
|
Pollutant: |
Diuron |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Dissolved |
|
Beneficial Use: |
Cold Freshwater Habitat |
|
Number of Samples: |
2 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed USGS California Water Science Center data for Russian River HU, Middle Russian River HA, Mark West HSA, Windsor Creek and its tributaries to determine beneficial use support and results are as follows: 0 of 2 samples exceeded the water quality threshold for Diuron. |
Data Reference: |
WQX from the NWQMP for the 2026 Integrated Report in Region 1 |
|
SWAMP Data: |
Non-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: |
Aquatic life should not be affected unacceptably if the 4-day average concentration of diuron does not exceed 1.3 ug/L (UC Davis Aquatic Life Criteria). |
Guideline Reference: |
Aquatic life water quality criteria derived via the UC Davis method: III. Diuron. Reviews of Environmental Contamination and Toxicology 216:105-141. |
|
Spatial Representation: |
The samples were collected at 1 monitoring site: USGS-383039122502401 (WINDSOR C A MARK WEST STATION RD NR WINDSOR CA). |
Temporal Representation: |
The samples were collected between the dates of 2017-05-02 and 2017-05-09 |
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 158584, Diuron
|
Region 1 |
Russian River HU, Middle Russian River HA, Mark West HSA, Windsor Creek and its tributaries |
|
|
LOE ID: |
328307 |
|
Pollutant: |
Diuron |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Dissolved |
|
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: |
Water Board staff assessed USGS California Water Science Center data for Russian River HU, Middle Russian River HA, Mark West HSA, Windsor Creek and its tributaries to determine beneficial use support and results are as follows: 0 of 2 samples exceeded the water quality threshold for Diuron. |
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: 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 health advisory for one-in-a-million incremental cancer risk estimate calculated as a drinking water standard for diuron is 2 ug/L. |
Guideline Reference: |
2012 Edition of the Drinking Water Standards and Health Advisories |
|
Spatial Representation: |
The samples were collected at 1 monitoring site: USGS-383039122502401 (WINDSOR C A MARK WEST STATION RD NR WINDSOR CA). |
Temporal Representation: |
The samples were collected between the dates of 2017-05-02 and 2017-05-09 |
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 158584, Diuron
|
Region 1 |
Russian River HU, Middle Russian River HA, Mark West HSA, Windsor Creek and its tributaries |
|
|
LOE ID: |
349482 |
|
Pollutant: |
Diuron |
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 Russian River HU, Middle Russian River HA, Mark West HSA, Windsor Creek and its tributaries to determine beneficial use support and results are as follows: 0 of 1 samples exceeded the water quality threshold for Diuron. |
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: |
Aquatic life should not be affected unacceptably if the 4-day average concentration of diuron does not exceed 1.3 ug/L (UC Davis Aquatic Life Criteria). |
Guideline Reference: |
Aquatic life water quality criteria derived via the UC Davis method: III. Diuron. Reviews of Environmental Contamination and Toxicology 216:105-141. |
|
Spatial Representation: |
The samples were collected at 1 monitoring site: 114WC1630 (Windsor Creek at Mark West Station). |
Temporal Representation: |
The samples were collected between the dates of 2014-02-04 and 2014-02-04 |
Environmental Conditions: |
|
QAPP Information: |
Generic SWAMP QAPrP |
QAPP Information Reference(s): |
Generic SWAMP QAPrP |
|
Line of Evidence (LOE) for Decision ID 158584, Diuron
|
Region 1 |
Russian River HU, Middle Russian River HA, Mark West HSA, Windsor Creek and its tributaries |
|
|
LOE ID: |
349493 |
|
Pollutant: |
Diuron |
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 Russian River HU, Middle Russian River HA, Mark West HSA, Windsor Creek and its tributaries to determine beneficial use support and results are as follows: 0 of 1 samples exceeded the water quality threshold for Diuron. |
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: |
Aquatic life should not be affected unacceptably if the 4-day average concentration of diuron does not exceed 1.3 ug/L (UC Davis Aquatic Life Criteria). |
Guideline Reference: |
Aquatic life water quality criteria derived via the UC Davis method: III. Diuron. Reviews of Environmental Contamination and Toxicology 216:105-141. |
|
Spatial Representation: |
The samples were collected at 1 monitoring site: 114WC1630 (Windsor Creek at Mark West Station). |
Temporal Representation: |
The samples were collected between the dates of 2014-02-04 and 2014-02-04 |
Environmental Conditions: |
|
QAPP Information: |
Generic SWAMP QAPrP |
QAPP Information Reference(s): |
Generic SWAMP QAPrP |
|
Line of Evidence (LOE) for Decision ID 169835, Esfenvalerate/Fenvalerate
|
Region 1 |
Russian River HU, Middle Russian River HA, Mark West HSA, Windsor Creek and its tributaries |
|
|
LOE ID: |
349588 |
|
Pollutant: |
Esfenvalerate/Fenvalerate |
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 Russian River HU, Middle Russian River HA, Mark West HSA, Windsor Creek and its tributaries to determine beneficial use support, and the results are as follows: 0 of the 0 samples exceeded the evaluation guideline for Esfenvalerate. 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 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 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 chronic criterion for esfenvalerate is 0.3 ng/L (expressed as a 4-day average). If the freely dissolved concentrations of esfenvalerate were reported or could be calculated then these values were used for this assessment. In the absence of freely dissolved concentrations, total concentrations were used. |
Guideline Reference: |
Water Quality Criteria Report for Esfenvalerate |
|
Spatial Representation: |
The samples were collected at 1 monitoring site: 114WC1630 (Windsor Creek at Mark West Station). |
Temporal Representation: |
The samples were collected between the dates of 2014-02-04 and 2014-02-04 |
Environmental Conditions: |
|
QAPP Information: |
Generic SWAMP QAPrP |
QAPP Information Reference(s): |
Generic SWAMP QAPrP |
|
Line of Evidence (LOE) for Decision ID 169835, Esfenvalerate/Fenvalerate
|
Region 1 |
Russian River HU, Middle Russian River HA, Mark West HSA, Windsor Creek and its tributaries |
|
|
LOE ID: |
349548 |
|
Pollutant: |
Esfenvalerate/Fenvalerate |
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 Russian River HU, Middle Russian River HA, Mark West HSA, Windsor Creek and its tributaries to determine beneficial use support, and the results are as follows: 0 of the 0 samples exceeded the evaluation guideline for Esfenvalerate. 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 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 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 chronic criterion for esfenvalerate is 0.3 ng/L (expressed as a 4-day average). If the freely dissolved concentrations of esfenvalerate were reported or could be calculated then these values were used for this assessment. In the absence of freely dissolved concentrations, total concentrations were used. |
Guideline Reference: |
Water Quality Criteria Report for Esfenvalerate |
|
Spatial Representation: |
The samples were collected at 1 monitoring site: 114WC1630 (Windsor Creek at Mark West Station). |
Temporal Representation: |
The samples were collected between the dates of 2014-02-04 and 2014-02-04 |
Environmental Conditions: |
|
QAPP Information: |
Generic SWAMP QAPrP |
QAPP Information Reference(s): |
Generic SWAMP QAPrP |
|
Line of Evidence (LOE) for Decision ID 167721, Ethion
|
Region 1 |
Russian River HU, Middle Russian River HA, Mark West HSA, Windsor Creek and its tributaries |
|
|
LOE ID: |
117333 |
|
Pollutant: |
Ethion |
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 Russian River HU, Middle Russian River HA, Mark West HSA, Windsor Creek and its tributaries to determine beneficial use support and results are as follows: 0 of 1 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) (114WC1630) |
Temporal Representation: |
The samples were collected between the dates of 2014-02-04 and 2014-02-04 |
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 167721, Ethion
|
Region 1 |
Russian River HU, Middle Russian River HA, Mark West HSA, Windsor Creek and its tributaries |
|
|
LOE ID: |
349648 |
|
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 Russian River HU, Middle Russian River HA, Mark West HSA, Windsor Creek and its tributaries 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 1 samples were collected, 1 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: 114WC1630 (Windsor Creek at Mark West Station). |
Temporal Representation: |
The samples were collected between the dates of 2014-02-04 and 2014-02-04 |
Environmental Conditions: |
|
QAPP Information: |
Generic SWAMP QAPrP |
QAPP Information Reference(s): |
Generic SWAMP QAPrP |
|
Line of Evidence (LOE) for Decision ID 167721, Ethion
|
Region 1 |
Russian River HU, Middle Russian River HA, Mark West HSA, Windsor Creek and its tributaries |
|
|
LOE ID: |
349651 |
|
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 Russian River HU, Middle Russian River HA, Mark West HSA, Windsor Creek and its tributaries 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 1 samples were collected, 1 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: 114WC1630 (Windsor Creek at Mark West Station). |
Temporal Representation: |
The samples were collected between the dates of 2014-02-04 and 2014-02-04 |
Environmental Conditions: |
|
QAPP Information: |
Generic SWAMP QAPrP |
QAPP Information Reference(s): |
Generic SWAMP QAPrP |
|
Line of Evidence (LOE) for Decision ID 167722, Ethoprop
|
Region 1 |
Russian River HU, Middle Russian River HA, Mark West HSA, Windsor Creek and its tributaries |
|
|
LOE ID: |
117334 |
|
Pollutant: |
Ethoprop |
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 Russian River HU, Middle Russian River HA, Mark West HSA, Windsor Creek and its tributaries to determine beneficial use support and results are as follows: 0 of 1 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) (114WC1630) |
Temporal Representation: |
The samples were collected between the dates of 2014-02-04 and 2014-02-04 |
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 167722, Ethoprop
|
Region 1 |
Russian River HU, Middle Russian River HA, Mark West HSA, Windsor Creek and its tributaries |
|
|
LOE ID: |
117335 |
|
Pollutant: |
Ethoprop |
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 Russian River HU, Middle Russian River HA, Mark West HSA, Windsor Creek and its tributaries to determine beneficial use support and results are as follows: 0 of 1 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) (114WC1630) |
Temporal Representation: |
The samples were collected between the dates of 2014-02-04 and 2014-02-04 |
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 167723, Fenitrothion
|
Region 1 |
Russian River HU, Middle Russian River HA, Mark West HSA, Windsor Creek and its tributaries |
|
|
LOE ID: |
117338 |
|
Pollutant: |
Fenitrothion |
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 Russian River HU, Middle Russian River HA, Mark West HSA, Windsor Creek and its tributaries to determine beneficial use support and results are as follows: 0 of 1 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) (114WC1630) |
Temporal Representation: |
The samples were collected between the dates of 2014-02-04 and 2014-02-04 |
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 167723, Fenitrothion
|
Region 1 |
Russian River HU, Middle Russian River HA, Mark West HSA, Windsor Creek and its tributaries |
|
|
LOE ID: |
117337 |
|
Pollutant: |
Fenitrothion |
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 Russian River HU, Middle Russian River HA, Mark West HSA, Windsor Creek and its tributaries to determine beneficial use support and results are as follows: 0 of 1 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) (114WC1630) |
Temporal Representation: |
The samples were collected between the dates of 2014-02-04 and 2014-02-04 |
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 169834, Fenpropathrin
|
Region 1 |
Russian River HU, Middle Russian River HA, Mark West HSA, Windsor Creek and its tributaries |
|
|
LOE ID: |
349779 |
|
Pollutant: |
Fenpropathrin |
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 Russian River HU, Middle Russian River HA, Mark West HSA, Windsor Creek and its tributaries to determine beneficial use support, and the results are as follows: 0 of the 0 samples exceeded the evaluation guideline for Fenpropathrin. 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 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 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 Fenpropathrin is the USEPA Aquatic Life Benchmark of 0.0015 ug/L for an invertebrate (chronic). |
Guideline Reference: |
OPP Aquatic Life Benchmarks |
|
Spatial Representation: |
The samples were collected at 1 monitoring site: 114WC1630 (Windsor Creek at Mark West Station). |
Temporal Representation: |
The samples were collected between the dates of 2014-02-04 and 2014-02-04 |
Environmental Conditions: |
|
QAPP Information: |
Generic SWAMP QAPrP |
QAPP Information Reference(s): |
Generic SWAMP QAPrP |
|
Line of Evidence (LOE) for Decision ID 169834, Fenpropathrin
|
Region 1 |
Russian River HU, Middle Russian River HA, Mark West HSA, Windsor Creek and its tributaries |
|
|
LOE ID: |
349740 |
|
Pollutant: |
Fenpropathrin |
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 Russian River HU, Middle Russian River HA, Mark West HSA, Windsor Creek and its tributaries to determine beneficial use support, and the results are as follows: 0 of the 0 samples exceeded the evaluation guideline for Fenpropathrin. 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 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 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 Fenpropathrin is the USEPA Aquatic Life Benchmark of 0.0015 ug/L for an invertebrate (chronic). |
Guideline Reference: |
OPP Aquatic Life Benchmarks |
|
Spatial Representation: |
The samples were collected at 1 monitoring site: 114WC1630 (Windsor Creek at Mark West Station). |
Temporal Representation: |
The samples were collected between the dates of 2014-02-04 and 2014-02-04 |
Environmental Conditions: |
|
QAPP Information: |
Generic SWAMP QAPrP |
QAPP Information Reference(s): |
Generic SWAMP QAPrP |
|
Line of Evidence (LOE) for Decision ID 103383, Fenthion
|
Region 1 |
Russian River HU, Middle Russian River HA, Mark West HSA, Windsor Creek and its tributaries |
|
|
LOE ID: |
106065 |
|
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 Russian River HU, Middle Russian River HA, Mark West HSA, Windsor Creek and its tributaries 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 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: |
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) 114WC1630). |
Temporal Representation: |
Date for this waterbody was collected over the date range 2014-02-04 to 2014-02-04 |
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 103383, Fenthion
|
Region 1 |
Russian River HU, Middle Russian River HA, Mark West HSA, Windsor Creek and its tributaries |
|
|
LOE ID: |
118450 |
|
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 Russian River HU, Middle Russian River HA, Mark West HSA, Windsor Creek and its tributaries 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 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: |
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) 114WC1630). |
Temporal Representation: |
Date for this waterbody was collected over the date range 2014-02-04 to 2014-02-04 |
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 158593, Fipronil
|
Region 1 |
Russian River HU, Middle Russian River HA, Mark West HSA, Windsor Creek and its tributaries |
|
|
LOE ID: |
328325 |
|
Pollutant: |
Fipronil |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Dissolved |
|
Beneficial Use: |
Cold Freshwater Habitat |
|
Number of Samples: |
2 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed USGS California Water Science Center data for Russian River HU, Middle Russian River HA, Mark West HSA, Windsor Creek and its tributaries to determine beneficial use support and results are as follows: 0 of 2 samples exceeded the water quality threshold for Fipronil. |
Data Reference: |
WQX from the NWQMP for the 2026 Integrated Report in Region 1 |
|
SWAMP Data: |
Non-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 fipronil does not exceed 0.0032 ug/L (3.2 ng/L) in the water column more than once every three years on average (Bower, et al. 2017). |
Guideline Reference: |
Water and Sediment Quality Criteria Report for Fipronil. Phase III: Application of the pesticide water and sediment quality criteria methodologies. Department of Environmental Toxicology, University of California, Davis. |
|
Spatial Representation: |
The samples were collected at 1 monitoring site: USGS-383039122502401 (WINDSOR C A MARK WEST STATION RD NR WINDSOR CA). |
Temporal Representation: |
The samples were collected between the dates of 2017-04-11 and 2017-04-18 |
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 158593, Fipronil
|
Region 1 |
Russian River HU, Middle Russian River HA, Mark West HSA, Windsor Creek and its tributaries |
|
|
LOE ID: |
328321 |
|
Pollutant: |
Fipronil |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Dissolved |
|
Beneficial Use: |
Warm Freshwater Habitat |
|
Number of Samples: |
2 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed USGS California Water Science Center data for Russian River HU, Middle Russian River HA, Mark West HSA, Windsor Creek and its tributaries to determine beneficial use support and results are as follows: 0 of 2 samples exceeded the water quality threshold for Fipronil. |
Data Reference: |
WQX from the NWQMP for the 2026 Integrated Report in Region 1 |
|
SWAMP Data: |
Non-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 fipronil does not exceed 0.0032 ug/L (3.2 ng/L) in the water column more than once every three years on average (Bower, et al. 2017). |
Guideline Reference: |
Water and Sediment Quality Criteria Report for Fipronil. Phase III: Application of the pesticide water and sediment quality criteria methodologies. Department of Environmental Toxicology, University of California, Davis. |
|
Spatial Representation: |
The samples were collected at 1 monitoring site: USGS-383039122502401 (WINDSOR C A MARK WEST STATION RD NR WINDSOR CA). |
Temporal Representation: |
The samples were collected between the dates of 2017-04-11 and 2017-04-18 |
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 158596, Fipronil Sulfone
|
Region 1 |
Russian River HU, Middle Russian River HA, Mark West HSA, Windsor Creek and its tributaries |
|
|
LOE ID: |
328335 |
|
Pollutant: |
Fipronil Sulfone |
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 USGS California Water Science Center data for Russian River HU, Middle Russian River HA, Mark West HSA, Windsor Creek and its tributaries to determine beneficial use support and results are as follows: 0 of 1 samples exceeded the water quality threshold for Fipronil Sulfone. |
Data Reference: |
WQX from the NWQMP for the 2026 Integrated Report in Region 1 |
|
SWAMP Data: |
Non-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 Fipronil Sulfone is the USEPA Aquatic Life Benchmark of 0.037 ug/L for an invertebrate (chronic). |
Guideline Reference: |
OPP Aquatic Life Benchmarks |
|
Spatial Representation: |
The samples were collected at 1 monitoring site: USGS-383039122502401 (WINDSOR C A MARK WEST STATION RD NR WINDSOR CA). |
Temporal Representation: |
The samples were collected between the dates of 2017-04-25 and 2017-04-25 |
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 158596, Fipronil Sulfone
|
Region 1 |
Russian River HU, Middle Russian River HA, Mark West HSA, Windsor Creek and its tributaries |
|
|
LOE ID: |
328340 |
|
Pollutant: |
Fipronil Sulfone |
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 USGS California Water Science Center data for Russian River HU, Middle Russian River HA, Mark West HSA, Windsor Creek and its tributaries to determine beneficial use support and results are as follows: 0 of 1 samples exceeded the water quality threshold for Fipronil Sulfone. |
Data Reference: |
WQX from the NWQMP for the 2026 Integrated Report in Region 1 |
|
SWAMP Data: |
Non-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 Fipronil Sulfone is the USEPA Aquatic Life Benchmark of 0.037 ug/L for an invertebrate (chronic). |
Guideline Reference: |
OPP Aquatic Life Benchmarks |
|
Spatial Representation: |
The samples were collected at 1 monitoring site: USGS-383039122502401 (WINDSOR C A MARK WEST STATION RD NR WINDSOR CA). |
Temporal Representation: |
The samples were collected between the dates of 2017-04-25 and 2017-04-25 |
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 158585, Glyphosate
|
Region 1 |
Russian River HU, Middle Russian River HA, Mark West HSA, Windsor Creek and its tributaries |
|
|
LOE ID: |
328386 |
|
Pollutant: |
Glyphosate |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Dissolved |
|
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: |
Water Board staff assessed USGS California Water Science Center data for Russian River HU, Middle Russian River HA, Mark West HSA, Windsor Creek and its tributaries to determine beneficial use support and results are as follows: 0 of 2 samples exceeded the water quality threshold for Glyphosate. |
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 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: USGS-383039122502401 (WINDSOR C A MARK WEST STATION RD NR WINDSOR CA). |
Temporal Representation: |
The samples were collected between the dates of 2017-04-11 and 2017-05-09 |
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 158585, Glyphosate
|
Region 1 |
Russian River HU, Middle Russian River HA, Mark West HSA, Windsor Creek and its tributaries |
|
|
LOE ID: |
328378 |
|
Pollutant: |
Glyphosate |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Dissolved |
|
Beneficial Use: |
Cold Freshwater Habitat |
|
Number of Samples: |
2 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed USGS California Water Science Center data for Russian River HU, Middle Russian River HA, Mark West HSA, Windsor Creek and its tributaries to determine beneficial use support and results are as follows: 0 of 2 samples exceeded the water quality threshold for Glyphosate. |
Data Reference: |
WQX from the NWQMP for the 2026 Integrated Report in Region 1 |
|
SWAMP Data: |
Non-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: USGS-383039122502401 (WINDSOR C A MARK WEST STATION RD NR WINDSOR CA). |
Temporal Representation: |
The samples were collected between the dates of 2017-04-11 and 2017-05-09 |
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 158585, Glyphosate
|
Region 1 |
Russian River HU, Middle Russian River HA, Mark West HSA, Windsor Creek and its tributaries |
|
|
LOE ID: |
117340 |
|
Pollutant: |
Glyphosate |
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 Russian River HU, Middle Russian River HA, Mark West HSA, Windsor Creek and its tributaries to determine beneficial use support and results are as follows: 0 of 1 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) (114WC1630) |
Temporal Representation: |
The samples were collected between the dates of 2014-02-04 and 2014-02-04 |
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 158585, Glyphosate
|
Region 1 |
Russian River HU, Middle Russian River HA, Mark West HSA, Windsor Creek and its tributaries |
|
|
LOE ID: |
117341 |
|
Pollutant: |
Glyphosate |
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 Russian River HU, Middle Russian River HA, Mark West HSA, Windsor Creek and its tributaries to determine beneficial use support and results are as follows: 0 of 1 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) (114WC1630) |
Temporal Representation: |
The samples were collected between the dates of 2014-02-04 and 2014-02-04 |
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 158585, Glyphosate
|
Region 1 |
Russian River HU, Middle Russian River HA, Mark West HSA, Windsor Creek and its tributaries |
|
|
LOE ID: |
117342 |
|
Pollutant: |
Glyphosate |
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 Russian River HU, Middle Russian River HA, Mark West HSA, Windsor Creek and its tributaries to determine beneficial use support and results are as follows: 0 of 1 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) (114WC1630) |
Temporal Representation: |
The samples were collected between the dates of 2014-02-04 and 2014-02-04 |
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 158585, Glyphosate
|
Region 1 |
Russian River HU, Middle Russian River HA, Mark West HSA, Windsor Creek and its tributaries |
|
|
LOE ID: |
328372 |
|
Pollutant: |
Glyphosate |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Dissolved |
|
Beneficial Use: |
Warm Freshwater Habitat |
|
Number of Samples: |
2 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed USGS California Water Science Center data for Russian River HU, Middle Russian River HA, Mark West HSA, Windsor Creek and its tributaries to determine beneficial use support and results are as follows: 0 of 2 samples exceeded the water quality threshold for Glyphosate. |
Data Reference: |
WQX from the NWQMP for the 2026 Integrated Report in Region 1 |
|
SWAMP Data: |
Non-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: USGS-383039122502401 (WINDSOR C A MARK WEST STATION RD NR WINDSOR CA). |
Temporal Representation: |
The samples were collected between the dates of 2017-04-11 and 2017-05-09 |
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 158581, Hydroxyatrazine, 2-
|
Region 1 |
Russian River HU, Middle Russian River HA, Mark West HSA, Windsor Creek and its tributaries |
|
|
LOE ID: |
328404 |
|
Pollutant: |
Hydroxyatrazine, 2- |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Dissolved |
|
Beneficial Use: |
Cold Freshwater Habitat |
|
Number of Samples: |
2 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed USGS California Water Science Center data for Russian River HU, Middle Russian River HA, Mark West HSA, Windsor Creek and its tributaries to determine beneficial use support and results are as follows: 0 of 2 samples exceeded the water quality threshold for Hydroxyatrazine, 2-. |
Data Reference: |
WQX from the NWQMP for the 2026 Integrated Report in Region 1 |
|
SWAMP Data: |
Non-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 hydroxyatrazine, 2- is the USEPA Aquatic Life Benchmark of 1,500 ug/L for a fish (acute) for triazine HA degradate. |
Guideline Reference: |
OPP Aquatic Life Benchmarks |
|
Spatial Representation: |
The samples were collected at 1 monitoring site: USGS-383039122502401 (WINDSOR C A MARK WEST STATION RD NR WINDSOR CA). |
Temporal Representation: |
The samples were collected between the dates of 2017-05-02 and 2017-05-09 |
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 158581, Hydroxyatrazine, 2-
|
Region 1 |
Russian River HU, Middle Russian River HA, Mark West HSA, Windsor Creek and its tributaries |
|
|
LOE ID: |
328396 |
|
Pollutant: |
Hydroxyatrazine, 2- |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Dissolved |
|
Beneficial Use: |
Warm Freshwater Habitat |
|
Number of Samples: |
2 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed USGS California Water Science Center data for Russian River HU, Middle Russian River HA, Mark West HSA, Windsor Creek and its tributaries to determine beneficial use support and results are as follows: 0 of 2 samples exceeded the water quality threshold for Hydroxyatrazine, 2-. |
Data Reference: |
WQX from the NWQMP for the 2026 Integrated Report in Region 1 |
|
SWAMP Data: |
Non-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 hydroxyatrazine, 2- is the USEPA Aquatic Life Benchmark of 1,500 ug/L for a fish (acute) for triazine HA degradate. |
Guideline Reference: |
OPP Aquatic Life Benchmarks |
|
Spatial Representation: |
The samples were collected at 1 monitoring site: USGS-383039122502401 (WINDSOR C A MARK WEST STATION RD NR WINDSOR CA). |
Temporal Representation: |
The samples were collected between the dates of 2017-05-02 and 2017-05-09 |
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 167724, Jasmolin
|
Region 1 |
Russian River HU, Middle Russian River HA, Mark West HSA, Windsor Creek and its tributaries |
|
|
LOE ID: |
349845 |
|
Pollutant: |
Jasmolin |
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 Russian River HU, Middle Russian River HA, Mark West HSA, Windsor Creek and its tributaries to determine beneficial use support and results are as follows: 0 of 1 samples exceeded the water quality threshold for Jasmolin. |
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 jasmolin is the USEPA Aquatic Life Benchmark of 0.04 ug/L for freshwater invertebrates (chronic) and is the sum of jasmolin-1 and jasmolin-2. |
Guideline Reference: |
OPP Aquatic Life Benchmarks |
|
Spatial Representation: |
The samples were collected at 1 monitoring site: 114WC1630 (Windsor Creek at Mark West Station). |
Temporal Representation: |
The samples were collected between the dates of 2014-02-04 and 2014-02-04 |
Environmental Conditions: |
|
QAPP Information: |
Generic SWAMP QAPrP |
QAPP Information Reference(s): |
Generic SWAMP QAPrP |
|
Line of Evidence (LOE) for Decision ID 167724, Jasmolin
|
Region 1 |
Russian River HU, Middle Russian River HA, Mark West HSA, Windsor Creek and its tributaries |
|
|
LOE ID: |
349839 |
|
Pollutant: |
Jasmolin |
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 Russian River HU, Middle Russian River HA, Mark West HSA, Windsor Creek and its tributaries to determine beneficial use support and results are as follows: 0 of 1 samples exceeded the water quality threshold for Jasmolin. |
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 jasmolin is the USEPA Aquatic Life Benchmark of 0.04 ug/L for freshwater invertebrates (chronic) and is the sum of jasmolin-1 and jasmolin-2. |
Guideline Reference: |
OPP Aquatic Life Benchmarks |
|
Spatial Representation: |
The samples were collected at 1 monitoring site: 114WC1630 (Windsor Creek at Mark West Station). |
Temporal Representation: |
The samples were collected between the dates of 2014-02-04 and 2014-02-04 |
Environmental Conditions: |
|
QAPP Information: |
Generic SWAMP QAPrP |
QAPP Information Reference(s): |
Generic SWAMP QAPrP |
|
Line of Evidence (LOE) for Decision ID 158582, Kresoxim-methyl
|
Region 1 |
Russian River HU, Middle Russian River HA, Mark West HSA, Windsor Creek and its tributaries |
|
|
LOE ID: |
328455 |
|
Pollutant: |
Kresoxim-methyl |
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 USGS California Water Science Center data for Russian River HU, Middle Russian River HA, Mark West HSA, Windsor Creek and its tributaries to determine beneficial use support and results are as follows: 0 of 1 samples exceeded the water quality threshold for Kresoxim-methyl. |
Data Reference: |
WQX from the NWQMP for the 2026 Integrated Report in Region 1 |
|
SWAMP Data: |
Non-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 kresoxim-methyl is the USEPA Aquatic Life Benchmark of 30.3 ug/L for a nonvascular plant (acute). |
Guideline Reference: |
OPP Aquatic Life Benchmarks |
|
Spatial Representation: |
The samples were collected at 1 monitoring site: USGS-383039122502401 (WINDSOR C A MARK WEST STATION RD NR WINDSOR CA). |
Temporal Representation: |
The samples were collected between the dates of 2017-04-25 and 2017-04-25 |
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 158582, Kresoxim-methyl
|
Region 1 |
Russian River HU, Middle Russian River HA, Mark West HSA, Windsor Creek and its tributaries |
|
|
LOE ID: |
328456 |
|
Pollutant: |
Kresoxim-methyl |
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 USGS California Water Science Center data for Russian River HU, Middle Russian River HA, Mark West HSA, Windsor Creek and its tributaries to determine beneficial use support and results are as follows: 0 of 1 samples exceeded the water quality threshold for Kresoxim-methyl. |
Data Reference: |
WQX from the NWQMP for the 2026 Integrated Report in Region 1 |
|
SWAMP Data: |
Non-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 kresoxim-methyl is the USEPA Aquatic Life Benchmark of 30.3 ug/L for a nonvascular plant (acute). |
Guideline Reference: |
OPP Aquatic Life Benchmarks |
|
Spatial Representation: |
The samples were collected at 1 monitoring site: USGS-383039122502401 (WINDSOR C A MARK WEST STATION RD NR WINDSOR CA). |
Temporal Representation: |
The samples were collected between the dates of 2017-04-25 and 2017-04-25 |
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 167725, Malathion
|
Region 1 |
Russian River HU, Middle Russian River HA, Mark West HSA, Windsor Creek and its tributaries |
|
|
LOE ID: |
102220 |
|
Pollutant: |
Malathion |
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 Russian River HU, Middle Russian River HA, Mark West HSA, Windsor Creek and its tributaries to determine beneficial use support, and the results are as follows: 0 of the 0 samples exceeded the evaluation guideline for Malathion. 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: |
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: |
Aquatic life should not be affected unacceptably if the 4-day average concentration of Malathion, does not exceed 0.028 ug/L more than once every three years on the average (UC Davis Aquatic Life Criterion). |
Guideline Reference: |
Aquatic life water quality criteria derived via the UC Davis method: l. Organophosphate insecticides. Reviews of Environmental Contamination and Toxicology 216:1-48. |
|
Spatial Representation: |
Data was collected from 1 station(s) (Station Code(s) 114WC1630). |
Temporal Representation: |
Date for this waterbody was collected over the date range 2014-02-04 to 2014-02-04 |
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 167725, Malathion
|
Region 1 |
Russian River HU, Middle Russian River HA, Mark West HSA, Windsor Creek and its tributaries |
|
|
LOE ID: |
105949 |
|
Pollutant: |
Malathion |
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 Russian River HU, Middle Russian River HA, Mark West HSA, Windsor Creek and its tributaries to determine beneficial use support, and the results are as follows: 0 of the 0 samples exceeded the evaluation guideline for Malathion. 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: |
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: |
Aquatic life should not be affected unacceptably if the 4-day average concentration of Malathion, does not exceed 0.028 ug/L more than once every three years on the average (UC Davis Aquatic Life Criterion). |
Guideline Reference: |
Aquatic life water quality criteria derived via the UC Davis method: l. Organophosphate insecticides. Reviews of Environmental Contamination and Toxicology 216:1-48. |
|
Spatial Representation: |
Data was collected from 1 station(s) (Station Code(s) 114WC1630). |
Temporal Representation: |
Date for this waterbody was collected over the date range 2014-02-04 to 2014-02-04 |
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 161356, Mercury
|
Region 1 |
Russian River HU, Middle Russian River HA, Mark West HSA, Windsor Creek and its tributaries |
|
|
LOE ID: |
328484 |
|
Pollutant: |
Mercury |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Dissolved |
|
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 USGS California Water Science Center data for Russian River HU, Middle Russian River HA, Mark West HSA, Windsor Creek and its tributaries to determine beneficial use support and results are as follows: 0 of 3 samples exceeded the water quality threshold for Mercury. |
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 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: USGS-383039122502401 (WINDSOR C A MARK WEST STATION RD NR WINDSOR CA). |
Temporal Representation: |
The samples were collected between the dates of 2017-04-11 and 2017-05-09 |
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 161356, Mercury
|
Region 1 |
Russian River HU, Middle Russian River HA, Mark West HSA, Windsor Creek and its tributaries |
|
|
LOE ID: |
328524 |
|
Pollutant: |
Mercury |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Dissolved |
|
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 USGS California Water Science Center data for Russian River HU, Middle Russian River HA, Mark West HSA, Windsor Creek and its tributaries to determine beneficial use support and results are as follows: 0 of 3 samples exceeded the water quality threshold for Mercury. |
Data Reference: |
WQX from the NWQMP for the 2026 Integrated Report in Region 1 |
|
SWAMP Data: |
Non-SWAMP |
|
Water Quality Objective/Criterion: |
Waters shall not contain toxic substances in concentrations that are toxic to, or that produce detrimental physiological responses in human, plant, animal, or aquatic life. (Basin Plan, 2018) |
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: USGS-383039122502401 (WINDSOR C A MARK WEST STATION RD NR WINDSOR CA). |
Temporal Representation: |
The samples were collected between the dates of 2017-04-11 and 2017-05-09 |
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 161356, Mercury
|
Region 1 |
Russian River HU, Middle Russian River HA, Mark West HSA, Windsor Creek and its tributaries |
|
|
LOE ID: |
328488 |
|
Pollutant: |
Mercury |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Dissolved |
|
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 USGS California Water Science Center data for Russian River HU, Middle Russian River HA, Mark West HSA, Windsor Creek and its tributaries to determine beneficial use support and results are as follows: 0 of 3 samples exceeded the water quality threshold for Mercury. |
Data Reference: |
WQX from the NWQMP for the 2026 Integrated Report in Region 1 |
|
SWAMP Data: |
Non-SWAMP |
|
Water Quality Objective/Criterion: |
Waters shall not contain toxic substances in concentrations that are toxic to, or that produce detrimental physiological responses in human, plant, animal, or aquatic life. (Basin Plan, 2018) |
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: USGS-383039122502401 (WINDSOR C A MARK WEST STATION RD NR WINDSOR CA). |
Temporal Representation: |
The samples were collected between the dates of 2017-04-11 and 2017-05-09 |
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 161356, Mercury
|
Region 1 |
Russian River HU, Middle Russian River HA, Mark West HSA, Windsor Creek and its tributaries |
|
|
LOE ID: |
328494 |
|
Pollutant: |
Mercury |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Dissolved |
|
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 USGS California Water Science Center data for Russian River HU, Middle Russian River HA, Mark West HSA, Windsor Creek and its tributaries to determine beneficial use support and results are as follows: 0 of 3 samples exceeded the water quality threshold for Mercury. |
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 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: USGS-383039122502401 (WINDSOR C A MARK WEST STATION RD NR WINDSOR CA). |
Temporal Representation: |
The samples were collected between the dates of 2017-04-11 and 2017-05-09 |
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 169826, Methomyl
|
Region 1 |
Russian River HU, Middle Russian River HA, Mark West HSA, Windsor Creek and its tributaries |
|
|
LOE ID: |
350062 |
|
Pollutant: |
Methomyl |
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 Russian River HU, Middle Russian River HA, Mark West HSA, Windsor Creek and its tributaries to determine beneficial use support and results are as follows: 0 of 1 samples exceeded the water quality threshold for Methomyl. |
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 methomyl is the USEPA Aquatic Life Benchmark of 0.6 ug/L for an invertebrate (chronic). |
Guideline Reference: |
OPP Aquatic Life Benchmarks |
|
Spatial Representation: |
The samples were collected at 1 monitoring site: 114WC1630 (Windsor Creek at Mark West Station). |
Temporal Representation: |
The samples were collected between the dates of 2014-02-04 and 2014-02-04 |
Environmental Conditions: |
|
QAPP Information: |
Generic SWAMP QAPrP |
QAPP Information Reference(s): |
Generic SWAMP QAPrP |
|
Line of Evidence (LOE) for Decision ID 169826, Methomyl
|
Region 1 |
Russian River HU, Middle Russian River HA, Mark West HSA, Windsor Creek and its tributaries |
|
|
LOE ID: |
350037 |
|
Pollutant: |
Methomyl |
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 Russian River HU, Middle Russian River HA, Mark West HSA, Windsor Creek and its tributaries to determine beneficial use support and results are as follows: 0 of 1 samples exceeded the water quality threshold for Methomyl. |
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 methomyl is the USEPA Aquatic Life Benchmark of 0.6 ug/L for an invertebrate (chronic). |
Guideline Reference: |
OPP Aquatic Life Benchmarks |
|
Spatial Representation: |
The samples were collected at 1 monitoring site: 114WC1630 (Windsor Creek at Mark West Station). |
Temporal Representation: |
The samples were collected between the dates of 2014-02-04 and 2014-02-04 |
Environmental Conditions: |
|
QAPP Information: |
Generic SWAMP QAPrP |
QAPP Information Reference(s): |
Generic SWAMP QAPrP |
|
Line of Evidence (LOE) for Decision ID 158602, Methoxyfenozide
|
Region 1 |
Russian River HU, Middle Russian River HA, Mark West HSA, Windsor Creek and its tributaries |
|
|
LOE ID: |
328538 |
|
Pollutant: |
Methoxyfenozide |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Dissolved |
|
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 USGS California Water Science Center data for Russian River HU, Middle Russian River HA, Mark West HSA, Windsor Creek and its tributaries to determine beneficial use support and results are as follows: 0 of 6 samples exceeded the water quality threshold for Methoxyfenozide. |
Data Reference: |
WQX from the NWQMP for the 2026 Integrated Report in Region 1 |
|
SWAMP Data: |
Non-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 methoxyfenozide is the USEPA Aquatic Life Benchmark of 3.1 ug/L for an invertebrate (chronic). |
Guideline Reference: |
OPP Aquatic Life Benchmarks |
|
Spatial Representation: |
The samples were collected at 1 monitoring site: USGS-383039122502401 (WINDSOR C A MARK WEST STATION RD NR WINDSOR CA). |
Temporal Representation: |
The samples were collected between the dates of 2017-04-04 and 2017-05-09 |
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 158602, Methoxyfenozide
|
Region 1 |
Russian River HU, Middle Russian River HA, Mark West HSA, Windsor Creek and its tributaries |
|
|
LOE ID: |
328535 |
|
Pollutant: |
Methoxyfenozide |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Dissolved |
|
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 USGS California Water Science Center data for Russian River HU, Middle Russian River HA, Mark West HSA, Windsor Creek and its tributaries to determine beneficial use support and results are as follows: 0 of 6 samples exceeded the water quality threshold for Methoxyfenozide. |
Data Reference: |
WQX from the NWQMP for the 2026 Integrated Report in Region 1 |
|
SWAMP Data: |
Non-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 methoxyfenozide is the USEPA Aquatic Life Benchmark of 3.1 ug/L for an invertebrate (chronic). |
Guideline Reference: |
OPP Aquatic Life Benchmarks |
|
Spatial Representation: |
The samples were collected at 1 monitoring site: USGS-383039122502401 (WINDSOR C A MARK WEST STATION RD NR WINDSOR CA). |
Temporal Representation: |
The samples were collected between the dates of 2017-04-04 and 2017-05-09 |
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 158600, Myclobutanil
|
Region 1 |
Russian River HU, Middle Russian River HA, Mark West HSA, Windsor Creek and its tributaries |
|
|
LOE ID: |
328584 |
|
Pollutant: |
Myclobutanil |
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 USGS California Water Science Center data for Russian River HU, Middle Russian River HA, Mark West HSA, Windsor Creek and its tributaries to determine beneficial use support and results are as follows: 0 of 5 samples exceeded the water quality threshold for Myclobutanil. |
Data Reference: |
WQX from the NWQMP for the 2026 Integrated Report in Region 1 |
|
SWAMP Data: |
Non-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 myclobutanil is the USEPA Aquatic Life Benchmark of 122 ug/L for nonvascular plants. |
Guideline Reference: |
OPP Aquatic Life Benchmarks |
|
Spatial Representation: |
The samples were collected at 1 monitoring site: USGS-383039122502401 (WINDSOR C A MARK WEST STATION RD NR WINDSOR CA). |
Temporal Representation: |
The samples were collected between the dates of 2017-04-11 and 2017-05-09 |
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 158600, Myclobutanil
|
Region 1 |
Russian River HU, Middle Russian River HA, Mark West HSA, Windsor Creek and its tributaries |
|
|
LOE ID: |
328586 |
|
Pollutant: |
Myclobutanil |
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 USGS California Water Science Center data for Russian River HU, Middle Russian River HA, Mark West HSA, Windsor Creek and its tributaries to determine beneficial use support and results are as follows: 0 of 5 samples exceeded the water quality threshold for Myclobutanil. |
Data Reference: |
WQX from the NWQMP for the 2026 Integrated Report in Region 1 |
|
SWAMP Data: |
Non-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 myclobutanil is the USEPA Aquatic Life Benchmark of 122 ug/L for nonvascular plants. |
Guideline Reference: |
OPP Aquatic Life Benchmarks |
|
Spatial Representation: |
The samples were collected at 1 monitoring site: USGS-383039122502401 (WINDSOR C A MARK WEST STATION RD NR WINDSOR CA). |
Temporal Representation: |
The samples were collected between the dates of 2017-04-11 and 2017-05-09 |
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 161386, Nitrogen, Nitrate
|
Region 1 |
Russian River HU, Middle Russian River HA, Mark West HSA, Windsor Creek and its tributaries |
|
|
LOE ID: |
328718 |
|
Pollutant: |
Nitrate as Nitrate (NO3) |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Dissolved |
|
Beneficial Use: |
Municipal & Domestic Supply |
|
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 USGS California Water Science Center data for Russian River HU, Middle Russian River HA, Mark West HSA, Windsor Creek and its tributaries to determine beneficial use support and results are as follows: 0 of 6 samples exceeded the water quality threshold for Nitrate as NO3. |
Data Reference: |
WQX from the NWQMP for the 2026 Integrated Report in Region 1 |
|
SWAMP Data: |
Non-SWAMP |
|
Water Quality Objective/Criterion: |
The California Maximum Contaminant Level for nitrate (as NO3) incorporated by reference in the Water Quality Control Plan, North Coast Basin is 45.0 mg/L (Water Quality Control Plan, North Coast Basin). |
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: USGS-383039122502401 (WINDSOR C A MARK WEST STATION RD NR WINDSOR CA). |
Temporal Representation: |
The samples were collected between the dates of 2017-04-04 and 2017-05-09 |
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 161386, Nitrogen, Nitrate
|
Region 1 |
Russian River HU, Middle Russian River HA, Mark West HSA, Windsor Creek and its tributaries |
|
|
LOE ID: |
328683 |
|
Pollutant: |
Nitrogen, Nitrate |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Dissolved |
|
Beneficial Use: |
Municipal & Domestic Supply |
|
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 USGS California Water Science Center data for Russian River HU, Middle Russian River HA, Mark West HSA, Windsor Creek and its tributaries to determine beneficial use support and results are as follows: 0 of 6 samples exceeded the water quality threshold for Nitrate as N. |
Data Reference: |
WQX from the NWQMP for the 2026 Integrated Report in Region 1 |
|
SWAMP Data: |
Non-SWAMP |
|
Water Quality Objective/Criterion: |
The California Maximum Contaminant Level for nitrate (NO3 as N) incorporated by reference in the Water Quality Control Plan, North Coast Basin is 10.0 mg/L (Water Quality Control Plan, North Coast Basin). |
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: USGS-383039122502401 (WINDSOR C A MARK WEST STATION RD NR WINDSOR CA). |
Temporal Representation: |
The samples were collected between the dates of 2017-04-04 and 2017-05-09 |
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 161386, Nitrogen, Nitrate
|
Region 1 |
Russian River HU, Middle Russian River HA, Mark West HSA, Windsor Creek and its tributaries |
|
|
LOE ID: |
107817 |
|
Pollutant: |
Nitrogen, Nitrate |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Total |
|
Beneficial Use: |
Municipal & Domestic Supply |
|
Number of Samples: |
51 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed 2009 5 year Permit for Russian River MS4 Program data for Russian River HU, Middle Russian River HA, Mark West HSA, Windsor Creek and its tributaries to determine beneficial use support and results are as follows: 0 of 51 samples exceeded the water quality standard for Nitrate as N. |
Data Reference: |
Water Quality Assessment Data for the 2018 solicitation cycle submitted through CEDEN for 2009 5 year Permit for Russian River MS4 Program.
|
|
SWAMP Data: |
Non-SWAMP |
|
Water Quality Objective/Criterion: |
The California Maximum Contaminant Level for nitrate (NO3 as N) incorporated by reference in the Water Quality Control Plan, North Coast Basin is 10.0 mg/L (Water Quality Control Plan, North Coast Basin). |
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) (C1-SRC-D) |
Temporal Representation: |
The samples were collected between the dates of 2010-09-14 and 2015-06-19 |
Environmental Conditions: |
|
QAPP Information: |
Quality Assurance Project Plan for K200+ 5 Year Permit for Russian River MS4 Program |
QAPP Information Reference(s): |
Santa Rosa NPDES Storm Water Sampling Plan |
|
Line of Evidence (LOE) for Decision ID 161386, Nitrogen, Nitrate
|
Region 1 |
Russian River HU, Middle Russian River HA, Mark West HSA, Windsor Creek and its tributaries |
|
|
LOE ID: |
117345 |
|
Pollutant: |
Nitrogen, Nitrate |
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 Russian River HU, Middle Russian River HA, Mark West HSA, Windsor Creek and its tributaries to determine beneficial use support and results are as follows: 0 of 1 samples exceeded the water quality standard for Nitrate 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 California Maximum Contaminant Level for nitrate (NO3 as N) incorporated by reference in the Water Quality Control Plan, North Coast Basin is 10.0 mg/L (Water Quality Control Plan, North Coast Basin). |
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) (114WC1630) |
Temporal Representation: |
The samples were collected between the dates of 2014-02-04 and 2014-02-04 |
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 161466, Nitrogen, Nitrite
|
Region 1 |
Russian River HU, Middle Russian River HA, Mark West HSA, Windsor Creek and its tributaries |
|
|
LOE ID: |
328743 |
|
Pollutant: |
Nitrogen, Nitrite |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Dissolved |
|
Beneficial Use: |
Municipal & Domestic Supply |
|
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 USGS California Water Science Center data for Russian River HU, Middle Russian River HA, Mark West HSA, Windsor Creek and its tributaries to determine beneficial use support and results are as follows: 0 of 6 samples exceeded the water quality threshold for Nitrite as N. |
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 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 Nitrite as N 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: USGS-383039122502401 (WINDSOR C A MARK WEST STATION RD NR WINDSOR CA). |
Temporal Representation: |
The samples were collected between the dates of 2017-04-04 and 2017-05-09 |
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 161466, Nitrogen, Nitrite
|
Region 1 |
Russian River HU, Middle Russian River HA, Mark West HSA, Windsor Creek and its tributaries |
|
|
LOE ID: |
112180 |
|
Pollutant: |
Nitrogen, Nitrite |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Total |
|
Beneficial Use: |
Municipal & Domestic Supply |
|
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 2009 5 year Permit for Russian River MS4 Program data for Russian River HU, Middle Russian River HA, Mark West HSA, Windsor Creek and its tributaries to determine beneficial use support and results are as follows: 0 of 6 samples exceeded the water quality standard for Nitrite as N. |
Data Reference: |
Water Quality Assessment Data for the 2018 solicitation cycle submitted through CEDEN for 2009 5 year Permit for Russian River MS4 Program.
|
|
SWAMP Data: |
Non-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 Nitrite as N 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) (C1-SRC-D) |
Temporal Representation: |
The samples were collected between the dates of 2010-09-14 and 2011-05-19 |
Environmental Conditions: |
|
QAPP Information: |
Quality Assurance Project Plan for K200+ 5 Year Permit for Russian River MS4 Program |
QAPP Information Reference(s): |
Santa Rosa NPDES Storm Water Sampling Plan |
|
Line of Evidence (LOE) for Decision ID 161466, Nitrogen, Nitrite
|
Region 1 |
Russian River HU, Middle Russian River HA, Mark West HSA, Windsor Creek and its tributaries |
|
|
LOE ID: |
101430 |
|
Pollutant: |
Nitrogen, Nitrite |
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 RWB1 Monitoring data for Russian River HU, Middle Russian River HA, Mark West HSA, Windsor Creek and its tributaries to determine beneficial use support and results are as follows: 0 of 1 samples exceeded the water quality standard for Nitrite 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: |
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 Nitrite as N 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) (114WC1630) |
Temporal Representation: |
The samples were collected between the dates of 2014-02-04 and 2014-02-04 |
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 105060, Nitrogen, ammonia (Total Ammonia)
|
Region 1 |
Russian River HU, Middle Russian River HA, Mark West HSA, Windsor Creek and its tributaries |
|
|
LOE ID: |
117311 |
|
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 RWB1 Monitoring data for Russian River HU, Middle Russian River HA, Mark West HSA, Windsor Creek and its tributaries 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 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) (114WC1630) |
Temporal Representation: |
The samples were collected between the dates of 2014-02-04 and 2014-02-04 |
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 105060, Nitrogen, ammonia (Total Ammonia)
|
Region 1 |
Russian River HU, Middle Russian River HA, Mark West HSA, Windsor Creek and its tributaries |
|
|
LOE ID: |
117309 |
|
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 RWB1 Monitoring data for Russian River HU, Middle Russian River HA, Mark West HSA, Windsor Creek and its tributaries 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 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) (114WC1630) |
Temporal Representation: |
The samples were collected between the dates of 2014-02-04 and 2014-02-04 |
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 105060, Nitrogen, ammonia (Total Ammonia)
|
Region 1 |
Russian River HU, Middle Russian River HA, Mark West HSA, Windsor Creek and its tributaries |
|
|
LOE ID: |
117310 |
|
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 RWB1 Monitoring data for Russian River HU, Middle Russian River HA, Mark West HSA, Windsor Creek and its tributaries 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 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) (114WC1630) |
Temporal Representation: |
The samples were collected between the dates of 2014-02-04 and 2014-02-04 |
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 169824, Oxadiazon
|
Region 1 |
Russian River HU, Middle Russian River HA, Mark West HSA, Windsor Creek and its tributaries |
|
|
LOE ID: |
350259 |
|
Pollutant: |
Oxadiazon |
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 Russian River HU, Middle Russian River HA, Mark West HSA, Windsor Creek and its tributaries to determine beneficial use support and results are as follows: 0 of 1 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: 114WC1630 (Windsor Creek at Mark West Station). |
Temporal Representation: |
The samples were collected between the dates of 2014-02-04 and 2014-02-04 |
Environmental Conditions: |
|
QAPP Information: |
Generic SWAMP QAPrP |
QAPP Information Reference(s): |
Generic SWAMP QAPrP |
|
Line of Evidence (LOE) for Decision ID 169824, Oxadiazon
|
Region 1 |
Russian River HU, Middle Russian River HA, Mark West HSA, Windsor Creek and its tributaries |
|
|
LOE ID: |
350214 |
|
Pollutant: |
Oxadiazon |
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 Russian River HU, Middle Russian River HA, Mark West HSA, Windsor Creek and its tributaries to determine beneficial use support and results are as follows: 0 of 1 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: 114WC1630 (Windsor Creek at Mark West Station). |
Temporal Representation: |
The samples were collected between the dates of 2014-02-04 and 2014-02-04 |
Environmental Conditions: |
|
QAPP Information: |
Generic SWAMP QAPrP |
QAPP Information Reference(s): |
Generic SWAMP QAPrP |
|
Line of Evidence (LOE) for Decision ID 156773, Oxygen, Dissolved
|
Region 1 |
Russian River HU, Middle Russian River HA, Mark West HSA, Windsor Creek and its tributaries |
|
|
LOE ID: |
101284 |
|
Pollutant: |
Oxygen, Dissolved |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Total |
|
Beneficial Use: |
Cold Freshwater Habitat |
Aquatic Life 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 the data for this water body to determine beneficial use support and results are as follows: 1 of 1 samples exceeded the water quality standard for dissolved oxygen. Data range from 7.5 mg/L. |
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) Windsor Creek at Mark West Station (114WC1630). |
Temporal Representation: |
The samples were collected between the dates of 2/4/2014. |
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 156773, Oxygen, Dissolved
|
Region 1 |
Russian River HU, Middle Russian River HA, Mark West HSA, Windsor Creek and its tributaries |
|
|
LOE ID: |
319046 |
|
Pollutant: |
Oxygen, Dissolved |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Total |
|
Beneficial Use: |
Cold Freshwater Habitat |
Aquatic Life Use: |
Fish Spawning |
|
Number of Samples: |
6 |
Number of Exceedances: |
3 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed dissolved oxygen data for USGS California Water Science Center and determined that 0 of 2 samples are less than the May-November minimum of 6.0 mg/L and 3 of 4 samples are less than the December-April minimum of 9.0 mg/L, so that 3 of 6 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: 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 minimum average of 8.0 mg/L and dissolved oxygen concentration limits for SPWN 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: |
These samples were collected at sampling station name: WINDSOR C A MARK WEST STATION RD NR WINDSOR CA; station code: USGS-383039122502401. |
Temporal Representation: |
These samples were collected from 4/4/2017-5/9/2017. |
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 169836, Permethrin
|
Region 1 |
Russian River HU, Middle Russian River HA, Mark West HSA, Windsor Creek and its tributaries |
|
|
LOE ID: |
350322 |
|
Pollutant: |
Permethrin |
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 Russian River HU, Middle Russian River HA, Mark West HSA, Windsor Creek and its tributaries to determine beneficial use support, and the results are as follows: 0 of the 0 samples exceeded the evaluation guideline for Permethrin. 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 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 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 chronic criterion for permethrin is 1 ng/L (expressed as a 4-day average). If the freely dissolved concentrations of permethrin were reported or could be calculated then these values were used for this assessment. In the absence of freely dissolved concentrations, total concentrations were used. |
Guideline Reference: |
Water Quality Criteria Report for Permethrin |
|
Spatial Representation: |
The samples were collected at 1 monitoring site: 114WC1630 (Windsor Creek at Mark West Station). |
Temporal Representation: |
The samples were collected between the dates of 2014-02-04 and 2014-02-04 |
Environmental Conditions: |
|
QAPP Information: |
Generic SWAMP QAPrP |
QAPP Information Reference(s): |
Generic SWAMP QAPrP |
|
Line of Evidence (LOE) for Decision ID 169836, Permethrin
|
Region 1 |
Russian River HU, Middle Russian River HA, Mark West HSA, Windsor Creek and its tributaries |
|
|
LOE ID: |
350323 |
|
Pollutant: |
Permethrin |
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 Russian River HU, Middle Russian River HA, Mark West HSA, Windsor Creek and its tributaries to determine beneficial use support, and the results are as follows: 0 of the 0 samples exceeded the evaluation guideline for Permethrin. 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 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 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 chronic criterion for permethrin is 1 ng/L (expressed as a 4-day average). If the freely dissolved concentrations of permethrin were reported or could be calculated then these values were used for this assessment. In the absence of freely dissolved concentrations, total concentrations were used. |
Guideline Reference: |
Water Quality Criteria Report for Permethrin |
|
Spatial Representation: |
The samples were collected at 1 monitoring site: 114WC1630 (Windsor Creek at Mark West Station). |
Temporal Representation: |
The samples were collected between the dates of 2014-02-04 and 2014-02-04 |
Environmental Conditions: |
|
QAPP Information: |
Generic SWAMP QAPrP |
QAPP Information Reference(s): |
Generic SWAMP QAPrP |
|
Line of Evidence (LOE) for Decision ID 167727, Phorate
|
Region 1 |
Russian River HU, Middle Russian River HA, Mark West HSA, Windsor Creek and its tributaries |
|
|
LOE ID: |
101432 |
|
Pollutant: |
Phorate |
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 Russian River HU, Middle Russian River HA, Mark West HSA, Windsor Creek and its tributaries to determine beneficial use support and results are as follows: 0 of 1 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) (114WC1630) |
Temporal Representation: |
The samples were collected between the dates of 2014-02-04 and 2014-02-04 |
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 167727, Phorate
|
Region 1 |
Russian River HU, Middle Russian River HA, Mark West HSA, Windsor Creek and its tributaries |
|
|
LOE ID: |
101433 |
|
Pollutant: |
Phorate |
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 Russian River HU, Middle Russian River HA, Mark West HSA, Windsor Creek and its tributaries to determine beneficial use support and results are as follows: 0 of 1 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) (114WC1630) |
Temporal Representation: |
The samples were collected between the dates of 2014-02-04 and 2014-02-04 |
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 167728, Phosmet
|
Region 1 |
Russian River HU, Middle Russian River HA, Mark West HSA, Windsor Creek and its tributaries |
|
|
LOE ID: |
350496 |
|
Pollutant: |
Phosmet |
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 Russian River HU, Middle Russian River HA, Mark West HSA, Windsor Creek and its tributaries to determine beneficial use support and results are as follows: 0 of 1 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: 114WC1630 (Windsor Creek at Mark West Station). |
Temporal Representation: |
The samples were collected between the dates of 2014-02-04 and 2014-02-04 |
Environmental Conditions: |
|
QAPP Information: |
Generic SWAMP QAPrP |
QAPP Information Reference(s): |
Generic SWAMP QAPrP |
|
Line of Evidence (LOE) for Decision ID 167728, Phosmet
|
Region 1 |
Russian River HU, Middle Russian River HA, Mark West HSA, Windsor Creek and its tributaries |
|
|
LOE ID: |
350498 |
|
Pollutant: |
Phosmet |
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 Russian River HU, Middle Russian River HA, Mark West HSA, Windsor Creek and its tributaries to determine beneficial use support and results are as follows: 0 of 1 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: 114WC1630 (Windsor Creek at Mark West Station). |
Temporal Representation: |
The samples were collected between the dates of 2014-02-04 and 2014-02-04 |
Environmental Conditions: |
|
QAPP Information: |
Generic SWAMP QAPrP |
QAPP Information Reference(s): |
Generic SWAMP QAPrP |
|
Line of Evidence (LOE) for Decision ID 158588, Prometon (Prometone)
|
Region 1 |
Russian River HU, Middle Russian River HA, Mark West HSA, Windsor Creek and its tributaries |
|
|
LOE ID: |
328921 |
|
Pollutant: |
Prometon (Prometone) |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Dissolved |
|
Beneficial Use: |
Warm Freshwater Habitat |
|
Number of Samples: |
2 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed USGS California Water Science Center data for Russian River HU, Middle Russian River HA, Mark West HSA, Windsor Creek and its tributaries to determine beneficial use support and results are as follows: 0 of 2 samples exceeded the water quality threshold for Prometon. |
Data Reference: |
WQX from the NWQMP for the 2026 Integrated Report in Region 1 |
|
SWAMP Data: |
Non-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: USGS-383039122502401 (WINDSOR C A MARK WEST STATION RD NR WINDSOR CA). |
Temporal Representation: |
The samples were collected between the dates of 2017-04-11 and 2017-05-09 |
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 158588, Prometon (Prometone)
|
Region 1 |
Russian River HU, Middle Russian River HA, Mark West HSA, Windsor Creek and its tributaries |
|
|
LOE ID: |
328938 |
|
Pollutant: |
Prometon (Prometone) |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Dissolved |
|
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: |
Water Board staff assessed USGS California Water Science Center data for Russian River HU, Middle Russian River HA, Mark West HSA, Windsor Creek and its tributaries to determine beneficial use support and results are as follows: 0 of 2 samples exceeded the water quality threshold for Prometon. |
Data Reference: |
WQX from the NWQMP for the 2026 Integrated Report in Region 1 |
|
SWAMP Data: |
Non-SWAMP |
|
Water Quality Objective/Criterion: |
Waters shall not contain toxic substances in concentrations that are toxic to, or that produce detrimental physiological responses in human, plant, animal, or aquatic life. (Basin Plan, 2018) |
Objective/Criterion Reference: |
Water Quality Control Plan (Basin Plan) for the North Coast Region |
|
Evaluation Guideline: |
The USEPA Health Advisory for 10 day exposure of a 10 kg-Child to Prometon as a drinking water level is a concentration of 0.02 mg/L. |
Guideline Reference: |
2012 Edition of the Drinking Water Standards and Health Advisories |
|
Spatial Representation: |
The samples were collected at 1 monitoring site: USGS-383039122502401 (WINDSOR C A MARK WEST STATION RD NR WINDSOR CA). |
Temporal Representation: |
The samples were collected between the dates of 2017-04-11 and 2017-05-09 |
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 158588, Prometon (Prometone)
|
Region 1 |
Russian River HU, Middle Russian River HA, Mark West HSA, Windsor Creek and its tributaries |
|
|
LOE ID: |
328924 |
|
Pollutant: |
Prometon (Prometone) |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Dissolved |
|
Beneficial Use: |
Cold Freshwater Habitat |
|
Number of Samples: |
2 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed USGS California Water Science Center data for Russian River HU, Middle Russian River HA, Mark West HSA, Windsor Creek and its tributaries to determine beneficial use support and results are as follows: 0 of 2 samples exceeded the water quality threshold for Prometon. |
Data Reference: |
WQX from the NWQMP for the 2026 Integrated Report in Region 1 |
|
SWAMP Data: |
Non-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: USGS-383039122502401 (WINDSOR C A MARK WEST STATION RD NR WINDSOR CA). |
Temporal Representation: |
The samples were collected between the dates of 2017-04-11 and 2017-05-09 |
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 169829, Prometryn
|
Region 1 |
Russian River HU, Middle Russian River HA, Mark West HSA, Windsor Creek and its tributaries |
|
|
LOE ID: |
350685 |
|
Pollutant: |
Prometryn |
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 Russian River HU, Middle Russian River HA, Mark West HSA, Windsor Creek and its tributaries to determine beneficial use support and results are as follows: 0 of 1 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: 114WC1630 (Windsor Creek at Mark West Station). |
Temporal Representation: |
The samples were collected between the dates of 2014-02-04 and 2014-02-04 |
Environmental Conditions: |
|
QAPP Information: |
Generic SWAMP QAPrP |
QAPP Information Reference(s): |
Generic SWAMP QAPrP |
|
Line of Evidence (LOE) for Decision ID 169829, Prometryn
|
Region 1 |
Russian River HU, Middle Russian River HA, Mark West HSA, Windsor Creek and its tributaries |
|
|
LOE ID: |
350676 |
|
Pollutant: |
Prometryn |
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 Russian River HU, Middle Russian River HA, Mark West HSA, Windsor Creek and its tributaries to determine beneficial use support and results are as follows: 0 of 1 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: 114WC1630 (Windsor Creek at Mark West Station). |
Temporal Representation: |
The samples were collected between the dates of 2014-02-04 and 2014-02-04 |
Environmental Conditions: |
|
QAPP Information: |
Generic SWAMP QAPrP |
QAPP Information Reference(s): |
Generic SWAMP QAPrP |
|
Line of Evidence (LOE) for Decision ID 158597, Propiconazole
|
Region 1 |
Russian River HU, Middle Russian River HA, Mark West HSA, Windsor Creek and its tributaries |
|
|
LOE ID: |
328946 |
|
Pollutant: |
Propiconazole |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
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: |
Water Board staff assessed USGS California Water Science Center data for Russian River HU, Middle Russian River HA, Mark West HSA, Windsor Creek and its tributaries to determine beneficial use support and results are as follows: 0 of 4 samples exceeded the water quality threshold for Propiconazole. |
Data Reference: |
WQX from the NWQMP for the 2026 Integrated Report in Region 1 |
|
SWAMP Data: |
Non-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 Propiconazole is the USEPA Aquatic Life Benchmark of 15 ug/L for a fish (chronic). |
Guideline Reference: |
OPP Aquatic Life Benchmarks |
|
Spatial Representation: |
The samples were collected at 1 monitoring site: USGS-383039122502401 (WINDSOR C A MARK WEST STATION RD NR WINDSOR CA). |
Temporal Representation: |
The samples were collected between the dates of 2017-04-11 and 2017-05-09 |
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 158597, Propiconazole
|
Region 1 |
Russian River HU, Middle Russian River HA, Mark West HSA, Windsor Creek and its tributaries |
|
|
LOE ID: |
328943 |
|
Pollutant: |
Propiconazole |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Dissolved |
|
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 USGS California Water Science Center data for Russian River HU, Middle Russian River HA, Mark West HSA, Windsor Creek and its tributaries to determine beneficial use support and results are as follows: 0 of 4 samples exceeded the water quality threshold for Propiconazole. |
Data Reference: |
WQX from the NWQMP for the 2026 Integrated Report in Region 1 |
|
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 expected safe lifetime exposure limit in drinking water for Propiconazole, calculated using the IRIS Reference Dose, is 91 ug/L. This was calculated assuming 70 kg body weight, 2 liters/day water consumption, 20% relative source contribution from drinking water, and 0.013 mg/kg/day as the reference dose. |
Guideline Reference: |
IRIS Reference Summary (Various Pollutants) |
|
Spatial Representation: |
The samples were collected at 1 monitoring site: USGS-383039122502401 (WINDSOR C A MARK WEST STATION RD NR WINDSOR CA). |
Temporal Representation: |
The samples were collected between the dates of 2017-04-11 and 2017-05-09 |
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 158597, Propiconazole
|
Region 1 |
Russian River HU, Middle Russian River HA, Mark West HSA, Windsor Creek and its tributaries |
|
|
LOE ID: |
328945 |
|
Pollutant: |
Propiconazole |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Dissolved |
|
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 USGS California Water Science Center data for Russian River HU, Middle Russian River HA, Mark West HSA, Windsor Creek and its tributaries to determine beneficial use support and results are as follows: 0 of 4 samples exceeded the water quality threshold for Propiconazole. |
Data Reference: |
WQX from the NWQMP for the 2026 Integrated Report in Region 1 |
|
SWAMP Data: |
Non-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 Propiconazole is the USEPA Aquatic Life Benchmark of 15 ug/L for a fish (chronic). |
Guideline Reference: |
OPP Aquatic Life Benchmarks |
|
Spatial Representation: |
The samples were collected at 1 monitoring site: USGS-383039122502401 (WINDSOR C A MARK WEST STATION RD NR WINDSOR CA). |
Temporal Representation: |
The samples were collected between the dates of 2017-04-11 and 2017-05-09 |
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 158589, Propoxur
|
Region 1 |
Russian River HU, Middle Russian River HA, Mark West HSA, Windsor Creek and its tributaries |
|
|
LOE ID: |
328956 |
|
Pollutant: |
Propoxur |
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 USGS California Water Science Center data for Russian River HU, Middle Russian River HA, Mark West HSA, Windsor Creek and its tributaries to determine beneficial use support and results are as follows: 0 of 1 samples exceeded the water quality threshold for Propoxur. |
Data Reference: |
WQX from the NWQMP for the 2026 Integrated Report in Region 1 |
|
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 Propoxur as a drinking water level is a concentration of 0.003 mg/L. |
Guideline Reference: |
2012 Edition of the Drinking Water Standards and Health Advisories |
|
Spatial Representation: |
The samples were collected at 1 monitoring site: USGS-383039122502401 (WINDSOR C A MARK WEST STATION RD NR WINDSOR CA). |
Temporal Representation: |
The samples were collected between the dates of 2017-05-09 and 2017-05-09 |
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 158589, Propoxur
|
Region 1 |
Russian River HU, Middle Russian River HA, Mark West HSA, Windsor Creek and its tributaries |
|
|
LOE ID: |
328952 |
|
Pollutant: |
Propoxur |
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 USGS California Water Science Center data for Russian River HU, Middle Russian River HA, Mark West HSA, Windsor Creek and its tributaries to determine beneficial use support and results are as follows: 0 of 1 samples exceeded the water quality threshold for Propoxur. |
Data Reference: |
WQX from the NWQMP for the 2026 Integrated Report in Region 1 |
|
SWAMP Data: |
Non-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 propoxur is the USEPA Aquatic Life Benchmark of 5.5 ug/L for invertebrates (acute). |
Guideline Reference: |
OPP Aquatic Life Benchmarks |
|
Spatial Representation: |
The samples were collected at 1 monitoring site: USGS-383039122502401 (WINDSOR C A MARK WEST STATION RD NR WINDSOR CA). |
Temporal Representation: |
The samples were collected between the dates of 2017-05-09 and 2017-05-09 |
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 158589, Propoxur
|
Region 1 |
Russian River HU, Middle Russian River HA, Mark West HSA, Windsor Creek and its tributaries |
|
|
LOE ID: |
328961 |
|
Pollutant: |
Propoxur |
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 USGS California Water Science Center data for Russian River HU, Middle Russian River HA, Mark West HSA, Windsor Creek and its tributaries to determine beneficial use support and results are as follows: 0 of 1 samples exceeded the water quality threshold for Propoxur. |
Data Reference: |
WQX from the NWQMP for the 2026 Integrated Report in Region 1 |
|
SWAMP Data: |
Non-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 propoxur is the USEPA Aquatic Life Benchmark of 5.5 ug/L for invertebrates (acute). |
Guideline Reference: |
OPP Aquatic Life Benchmarks |
|
Spatial Representation: |
The samples were collected at 1 monitoring site: USGS-383039122502401 (WINDSOR C A MARK WEST STATION RD NR WINDSOR CA). |
Temporal Representation: |
The samples were collected between the dates of 2017-05-09 and 2017-05-09 |
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 167729, Pyrethrin
|
Region 1 |
Russian River HU, Middle Russian River HA, Mark West HSA, Windsor Creek and its tributaries |
|
|
LOE ID: |
350756 |
|
Pollutant: |
Pyrethrin |
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 Russian River HU, Middle Russian River HA, Mark West HSA, Windsor Creek and its tributaries to determine beneficial use support and results are as follows: 0 of 1 samples exceeded the water quality threshold for Pyrethrin. |
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 pyrethrin is the USEPA Aquatic Life Benchmark of 0.04 ug/L for freshwater invertebrates (chronic) and is the sum of pyrethrin-1 and pyrethrin-2. |
Guideline Reference: |
OPP Aquatic Life Benchmarks |
|
Spatial Representation: |
The samples were collected at 1 monitoring site: 114WC1630 (Windsor Creek at Mark West Station). |
Temporal Representation: |
The samples were collected between the dates of 2014-02-04 and 2014-02-04 |
Environmental Conditions: |
|
QAPP Information: |
Generic SWAMP QAPrP |
QAPP Information Reference(s): |
Generic SWAMP QAPrP |
|
Line of Evidence (LOE) for Decision ID 167729, Pyrethrin
|
Region 1 |
Russian River HU, Middle Russian River HA, Mark West HSA, Windsor Creek and its tributaries |
|
|
LOE ID: |
350781 |
|
Pollutant: |
Pyrethrin |
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 Russian River HU, Middle Russian River HA, Mark West HSA, Windsor Creek and its tributaries to determine beneficial use support and results are as follows: 0 of 1 samples exceeded the water quality threshold for Pyrethrin. |
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 pyrethrin is the USEPA Aquatic Life Benchmark of 0.04 ug/L for freshwater invertebrates (chronic) and is the sum of pyrethrin-1 and pyrethrin-2. |
Guideline Reference: |
OPP Aquatic Life Benchmarks |
|
Spatial Representation: |
The samples were collected at 1 monitoring site: 114WC1630 (Windsor Creek at Mark West Station). |
Temporal Representation: |
The samples were collected between the dates of 2014-02-04 and 2014-02-04 |
Environmental Conditions: |
|
QAPP Information: |
Generic SWAMP QAPrP |
QAPP Information Reference(s): |
Generic SWAMP QAPrP |
|
Line of Evidence (LOE) for Decision ID 169823, Pyrethrins
|
Region 1 |
Russian River HU, Middle Russian River HA, Mark West HSA, Windsor Creek and its tributaries |
|
|
LOE ID: |
350823 |
|
Pollutant: |
Pyrethrins |
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 Russian River HU, Middle Russian River HA, Mark West HSA, Windsor Creek and its tributaries to determine beneficial use support and results are as follows: 0 of 1 samples exceeded the water quality threshold for Pyrethrins. |
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 pyrethrins is the USEPA Aquatic Life Benchmark of 0.04 ug/L for an invertebrate (chronic), and is the sum of cinerin-1, cinerin-2, jasmolin-1, jasmolin-2, pyrethrin-1, and pyrethrin-2. |
Guideline Reference: |
OPP Aquatic Life Benchmarks |
|
Spatial Representation: |
The samples were collected at 1 monitoring site: 114WC1630 (Windsor Creek at Mark West Station). |
Temporal Representation: |
The samples were collected between the dates of 2014-02-04 and 2014-02-04 |
Environmental Conditions: |
|
QAPP Information: |
Generic SWAMP QAPrP |
QAPP Information Reference(s): |
Generic SWAMP QAPrP |
|
Line of Evidence (LOE) for Decision ID 169823, Pyrethrins
|
Region 1 |
Russian River HU, Middle Russian River HA, Mark West HSA, Windsor Creek and its tributaries |
|
|
LOE ID: |
350840 |
|
Pollutant: |
Pyrethrins |
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 Russian River HU, Middle Russian River HA, Mark West HSA, Windsor Creek and its tributaries to determine beneficial use support and results are as follows: 0 of 1 samples exceeded the water quality threshold for Pyrethrins. |
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 pyrethrins is the USEPA Aquatic Life Benchmark of 0.04 ug/L for an invertebrate (chronic), and is the sum of cinerin-1, cinerin-2, jasmolin-1, jasmolin-2, pyrethrin-1, and pyrethrin-2. |
Guideline Reference: |
OPP Aquatic Life Benchmarks |
|
Spatial Representation: |
The samples were collected at 1 monitoring site: 114WC1630 (Windsor Creek at Mark West Station). |
Temporal Representation: |
The samples were collected between the dates of 2014-02-04 and 2014-02-04 |
Environmental Conditions: |
|
QAPP Information: |
Generic SWAMP QAPrP |
QAPP Information Reference(s): |
Generic SWAMP QAPrP |
|
Line of Evidence (LOE) for Decision ID 169825, Pyrethroids
|
Region 1 |
Russian River HU, Middle Russian River HA, Mark West HSA, Windsor Creek and its tributaries |
|
|
LOE ID: |
350905 |
|
Pollutant: |
Pyrethroids |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Dissolved |
|
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 Russian River HU, Middle Russian River HA, Mark West HSA, Windsor Creek and its tributaries to determine beneficial use support, and the results are as follows: 0 of the 0 samples exceeded the evaluation guideline for Pyrethroids. 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 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 (Water Quality Control Plan, North Coast Basin). |
Objective/Criterion Reference: |
Water Quality Control Plan (Basin Plan) for the North Coast Region |
|
Evaluation Guideline: |
The summed ratios of the pyrethroid pesticides bifenthrin, cyfluthrin, cypermethrin, esfenvalerate, lambda-cyhalothrin, permethrin and their respective chronic concentration goals are not to exceed 1. If the freely dissolved concentrations of these pesticides were reported or could be calculated then these values were used for this assessment. In the absence of freely dissolved concentrations, total concentrations were used. |
Guideline Reference: |
Amendment to the Water Quality Control Plan for the Sacramento River and San Joaquin River Basins for the Control of Pyrethroid Pesticide Discharges |
|
Spatial Representation: |
The samples were collected at 1 monitoring site: 114WC1630 (Windsor Creek at Mark West Station). |
Temporal Representation: |
The samples were collected between the dates of 2014-02-04 and 2014-02-04 |
Environmental Conditions: |
|
QAPP Information: |
Generic SWAMP QAPrP |
QAPP Information Reference(s): |
Generic SWAMP QAPrP |
|
Line of Evidence (LOE) for Decision ID 169825, Pyrethroids
|
Region 1 |
Russian River HU, Middle Russian River HA, Mark West HSA, Windsor Creek and its tributaries |
|
|
LOE ID: |
350880 |
|
Pollutant: |
Pyrethroids |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Dissolved |
|
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 Russian River HU, Middle Russian River HA, Mark West HSA, Windsor Creek and its tributaries to determine beneficial use support, and the results are as follows: 0 of the 0 samples exceeded the evaluation guideline for Pyrethroids. 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 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 (Water Quality Control Plan, North Coast Basin). |
Objective/Criterion Reference: |
Water Quality Control Plan (Basin Plan) for the North Coast Region |
|
Evaluation Guideline: |
The summed ratios of the pyrethroid pesticides bifenthrin, cyfluthrin, cypermethrin, esfenvalerate, lambda-cyhalothrin, permethrin and their respective chronic concentration goals are not to exceed 1. If the freely dissolved concentrations of these pesticides were reported or could be calculated then these values were used for this assessment. In the absence of freely dissolved concentrations, total concentrations were used. |
Guideline Reference: |
Amendment to the Water Quality Control Plan for the Sacramento River and San Joaquin River Basins for the Control of Pyrethroid Pesticide Discharges |
|
Spatial Representation: |
The samples were collected at 1 monitoring site: 114WC1630 (Windsor Creek at Mark West Station). |
Temporal Representation: |
The samples were collected between the dates of 2014-02-04 and 2014-02-04 |
Environmental Conditions: |
|
QAPP Information: |
Generic SWAMP QAPrP |
QAPP Information Reference(s): |
Generic SWAMP QAPrP |
|
Line of Evidence (LOE) for Decision ID 158590, Simazine
|
Region 1 |
Russian River HU, Middle Russian River HA, Mark West HSA, Windsor Creek and its tributaries |
|
|
LOE ID: |
351024 |
|
Pollutant: |
Simazine |
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 Russian River HU, Middle Russian River HA, Mark West HSA, Windsor Creek and its tributaries to determine beneficial use support and results are as follows: 0 of 1 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: 114WC1630 (Windsor Creek at Mark West Station). |
Temporal Representation: |
The samples were collected between the dates of 2014-02-04 and 2014-02-04 |
Environmental Conditions: |
|
QAPP Information: |
Generic SWAMP QAPrP |
QAPP Information Reference(s): |
Generic SWAMP QAPrP |
|
Line of Evidence (LOE) for Decision ID 158590, Simazine
|
Region 1 |
Russian River HU, Middle Russian River HA, Mark West HSA, Windsor Creek and its tributaries |
|
|
LOE ID: |
329014 |
|
Pollutant: |
Simazine |
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 USGS California Water Science Center data for Russian River HU, Middle Russian River HA, Mark West HSA, Windsor Creek and its tributaries to determine beneficial use support and results are as follows: 0 of 5 samples exceeded the water quality threshold for Simazine. |
Data Reference: |
WQX from the NWQMP for the 2026 Integrated Report in Region 1 |
|
SWAMP Data: |
Non-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: USGS-383039122502401 (WINDSOR C A MARK WEST STATION RD NR WINDSOR CA). |
Temporal Representation: |
The samples were collected between the dates of 2017-04-04 and 2017-05-09 |
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 158590, Simazine
|
Region 1 |
Russian River HU, Middle Russian River HA, Mark West HSA, Windsor Creek and its tributaries |
|
|
LOE ID: |
329019 |
|
Pollutant: |
Simazine |
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 USGS California Water Science Center data for Russian River HU, Middle Russian River HA, Mark West HSA, Windsor Creek and its tributaries to determine beneficial use support and results are as follows: 0 of 5 samples exceeded the water quality threshold for Simazine. |
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 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: USGS-383039122502401 (WINDSOR C A MARK WEST STATION RD NR WINDSOR CA). |
Temporal Representation: |
The samples were collected between the dates of 2017-04-04 and 2017-05-09 |
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 158590, Simazine
|
Region 1 |
Russian River HU, Middle Russian River HA, Mark West HSA, Windsor Creek and its tributaries |
|
|
LOE ID: |
329002 |
|
Pollutant: |
Simazine |
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 USGS California Water Science Center data for Russian River HU, Middle Russian River HA, Mark West HSA, Windsor Creek and its tributaries to determine beneficial use support and results are as follows: 0 of 5 samples exceeded the water quality threshold for Simazine. |
Data Reference: |
WQX from the NWQMP for the 2026 Integrated Report in Region 1 |
|
SWAMP Data: |
Non-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: USGS-383039122502401 (WINDSOR C A MARK WEST STATION RD NR WINDSOR CA). |
Temporal Representation: |
The samples were collected between the dates of 2017-04-04 and 2017-05-09 |
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 158590, Simazine
|
Region 1 |
Russian River HU, Middle Russian River HA, Mark West HSA, Windsor Creek and its tributaries |
|
|
LOE ID: |
351088 |
|
Pollutant: |
Simazine |
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 Russian River HU, Middle Russian River HA, Mark West HSA, Windsor Creek and its tributaries to determine beneficial use support and results are as follows: 0 of 1 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: 114WC1630 (Windsor Creek at Mark West Station). |
Temporal Representation: |
The samples were collected between the dates of 2014-02-04 and 2014-02-04 |
Environmental Conditions: |
|
QAPP Information: |
Generic SWAMP QAPrP |
QAPP Information Reference(s): |
Generic SWAMP QAPrP |
|
Line of Evidence (LOE) for Decision ID 158591, Sodium
|
Region 1 |
Russian River HU, Middle Russian River HA, Mark West HSA, Windsor Creek and its tributaries |
|
|
LOE ID: |
329087 |
|
Pollutant: |
Sodium |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Dissolved |
|
Beneficial Use: |
Agricultural Supply |
|
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 USGS California Water Science Center data for Russian River HU, Middle Russian River HA, Mark West HSA, Windsor Creek and its tributaries to determine beneficial use support and results are as follows: 0 of 6 samples exceeded the water quality threshold for Sodium. |
Data Reference: |
WQX from the NWQMP for the 2026 Integrated Report in Region 1 |
|
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: |
Water Quality for Agriculture, published by the Food and Agriculture Organization of the United Nations in 1985, contains criteria protective of various agricultural uses of water, including irrigation of various types of crops and stock watering. At or below the sodium threshold of 69 mg/L, agricultural uses of water should not be limited. |
Guideline Reference: |
Water Quality for Agriculture, Food and Agriculture Organization of the United Nations - Irrigation and Drainage Paper No. 29, Rev 1, Rome (1985) |
|
Spatial Representation: |
The samples were collected at 1 monitoring site: USGS-383039122502401 (WINDSOR C A MARK WEST STATION RD NR WINDSOR CA). |
Temporal Representation: |
The samples were collected between the dates of 2017-04-04 and 2017-05-09 |
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 158591, Sodium
|
Region 1 |
Russian River HU, Middle Russian River HA, Mark West HSA, Windsor Creek and its tributaries |
|
|
LOE ID: |
329033 |
|
Pollutant: |
Sodium |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Dissolved |
|
Beneficial Use: |
Municipal & Domestic Supply |
|
Number of Samples: |
6 |
Number of Exceedances: |
4 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed USGS California Water Science Center data for Russian River HU, Middle Russian River HA, Mark West HSA, Windsor Creek and its tributaries to determine beneficial use support and results are as follows: 4 of 6 samples exceeded the water quality threshold for Sodium. |
Data Reference: |
WQX from the NWQMP for the 2026 Integrated Report in Region 1 |
|
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: |
Per the Drinking Water Standards and Health Advisories (USEPA 2012), the health advisory for sodium for individuals on a sodium-restricted diet is 20 mg/l. |
Guideline Reference: |
2012 Edition of the Drinking Water Standards and Health Advisories |
|
Spatial Representation: |
The samples were collected at 1 monitoring site: USGS-383039122502401 (WINDSOR C A MARK WEST STATION RD NR WINDSOR CA). |
Temporal Representation: |
The samples were collected between the dates of 2017-04-04 and 2017-05-09 |
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 158592, Sulfates
|
Region 1 |
Russian River HU, Middle Russian River HA, Mark West HSA, Windsor Creek and its tributaries |
|
|
LOE ID: |
329224 |
|
Pollutant: |
Sulfates |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Dissolved |
|
Beneficial Use: |
Municipal & Domestic Supply |
|
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 USGS California Water Science Center data for Russian River HU, Middle Russian River HA, Mark West HSA, Windsor Creek and its tributaries to determine beneficial use support and results are as follows: 0 of 6 samples exceeded the water quality threshold for Sulfate. |
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 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: USGS-383039122502401 (WINDSOR C A MARK WEST STATION RD NR WINDSOR CA). |
Temporal Representation: |
The samples were collected between the dates of 2017-04-04 and 2017-05-09 |
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 158592, Sulfates
|
Region 1 |
Russian River HU, Middle Russian River HA, Mark West HSA, Windsor Creek and its tributaries |
|
|
LOE ID: |
105639 |
|
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 RWB1 Monitoring data for Russian River HU, Middle Russian River HA, Mark West HSA, Windsor Creek and its tributaries 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 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) (114WC1630) |
Temporal Representation: |
The samples were collected between the dates of 2014-02-04 and 2014-02-04 |
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 158599, Tebuconazole
|
Region 1 |
Russian River HU, Middle Russian River HA, Mark West HSA, Windsor Creek and its tributaries |
|
|
LOE ID: |
329242 |
|
Pollutant: |
Tebuconazole |
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 USGS California Water Science Center data for Russian River HU, Middle Russian River HA, Mark West HSA, Windsor Creek and its tributaries to determine beneficial use support and results are as follows: 0 of 1 samples exceeded the water quality threshold for Tebuconazole. |
Data Reference: |
WQX from the NWQMP for the 2026 Integrated Report in Region 1 |
|
SWAMP Data: |
Non-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 tebuconazole is the USEPA Aquatic Life Benchmark of 11 ug/L for a fish (chronic). |
Guideline Reference: |
OPP Aquatic Life Benchmarks |
|
Spatial Representation: |
The samples were collected at 1 monitoring site: USGS-383039122502401 (WINDSOR C A MARK WEST STATION RD NR WINDSOR CA). |
Temporal Representation: |
The samples were collected between the dates of 2017-05-09 and 2017-05-09 |
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 158599, Tebuconazole
|
Region 1 |
Russian River HU, Middle Russian River HA, Mark West HSA, Windsor Creek and its tributaries |
|
|
LOE ID: |
329244 |
|
Pollutant: |
Tebuconazole |
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 USGS California Water Science Center data for Russian River HU, Middle Russian River HA, Mark West HSA, Windsor Creek and its tributaries to determine beneficial use support and results are as follows: 0 of 1 samples exceeded the water quality threshold for Tebuconazole. |
Data Reference: |
WQX from the NWQMP for the 2026 Integrated Report in Region 1 |
|
SWAMP Data: |
Non-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 tebuconazole is the USEPA Aquatic Life Benchmark of 11 ug/L for a fish (chronic). |
Guideline Reference: |
OPP Aquatic Life Benchmarks |
|
Spatial Representation: |
The samples were collected at 1 monitoring site: USGS-383039122502401 (WINDSOR C A MARK WEST STATION RD NR WINDSOR CA). |
Temporal Representation: |
The samples were collected between the dates of 2017-05-09 and 2017-05-09 |
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 167730, Terbufos
|
Region 1 |
Russian River HU, Middle Russian River HA, Mark West HSA, Windsor Creek and its tributaries |
|
|
LOE ID: |
106464 |
|
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 Russian River HU, Middle Russian River HA, Mark West HSA, Windsor Creek and its tributaries 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 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: |
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) 114WC1630). |
Temporal Representation: |
Date for this waterbody was collected over the date range 2014-02-04 to 2014-02-04 |
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 167730, Terbufos
|
Region 1 |
Russian River HU, Middle Russian River HA, Mark West HSA, Windsor Creek and its tributaries |
|
|
LOE ID: |
105640 |
|
Pollutant: |
Terbufos |
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 Russian River HU, Middle Russian River HA, Mark West HSA, Windsor Creek and its tributaries to determine beneficial use support and results are as follows: 0 of 1 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) (114WC1630) |
Temporal Representation: |
The samples were collected between the dates of 2014-02-04 and 2014-02-04 |
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 167730, Terbufos
|
Region 1 |
Russian River HU, Middle Russian River HA, Mark West HSA, Windsor Creek and its tributaries |
|
|
LOE ID: |
111082 |
|
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 Russian River HU, Middle Russian River HA, Mark West HSA, Windsor Creek and its tributaries 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 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: |
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) 114WC1630). |
Temporal Representation: |
Date for this waterbody was collected over the date range 2014-02-04 to 2014-02-04 |
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 158598, Tetraconazole
|
Region 1 |
Russian River HU, Middle Russian River HA, Mark West HSA, Windsor Creek and its tributaries |
|
|
LOE ID: |
329325 |
|
Pollutant: |
Tetraconazole |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
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: |
Water Board staff assessed USGS California Water Science Center data for Russian River HU, Middle Russian River HA, Mark West HSA, Windsor Creek and its tributaries to determine beneficial use support and results are as follows: 0 of 4 samples exceeded the water quality threshold for Tetraconazole. |
Data Reference: |
WQX from the NWQMP for the 2026 Integrated Report in Region 1 |
|
SWAMP Data: |
Non-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 Tetraconazole is the USEPA Aquatic Life Benchmark of 80 ug/L for a fish (chronic). |
Guideline Reference: |
OPP Aquatic Life Benchmarks |
|
Spatial Representation: |
The samples were collected at 1 monitoring site: USGS-383039122502401 (WINDSOR C A MARK WEST STATION RD NR WINDSOR CA). |
Temporal Representation: |
The samples were collected between the dates of 2017-04-11 and 2017-05-02 |
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 158598, Tetraconazole
|
Region 1 |
Russian River HU, Middle Russian River HA, Mark West HSA, Windsor Creek and its tributaries |
|
|
LOE ID: |
329323 |
|
Pollutant: |
Tetraconazole |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Dissolved |
|
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 USGS California Water Science Center data for Russian River HU, Middle Russian River HA, Mark West HSA, Windsor Creek and its tributaries to determine beneficial use support and results are as follows: 0 of 4 samples exceeded the water quality threshold for Tetraconazole. |
Data Reference: |
WQX from the NWQMP for the 2026 Integrated Report in Region 1 |
|
SWAMP Data: |
Non-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 Tetraconazole is the USEPA Aquatic Life Benchmark of 80 ug/L for a fish (chronic). |
Guideline Reference: |
OPP Aquatic Life Benchmarks |
|
Spatial Representation: |
The samples were collected at 1 monitoring site: USGS-383039122502401 (WINDSOR C A MARK WEST STATION RD NR WINDSOR CA). |
Temporal Representation: |
The samples were collected between the dates of 2017-04-11 and 2017-05-02 |
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 158595, Triclopyr
|
Region 1 |
Russian River HU, Middle Russian River HA, Mark West HSA, Windsor Creek and its tributaries |
|
|
LOE ID: |
329333 |
|
Pollutant: |
Triclopyr |
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 USGS California Water Science Center data for Russian River HU, Middle Russian River HA, Mark West HSA, Windsor Creek and its tributaries to determine beneficial use support and results are as follows: 0 of 1 samples exceeded the water quality threshold for Triclopyr. |
Data Reference: |
WQX from the NWQMP for the 2026 Integrated Report in Region 1 |
|
SWAMP Data: |
Non-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 triclopyr is the USEPA Aquatic Life Benchmark of 26 ug/L for a fish (chronic) for Triclopyr Butoxyethyl Ester (BEE). |
Guideline Reference: |
OPP Aquatic Life Benchmarks |
|
Spatial Representation: |
The samples were collected at 1 monitoring site: USGS-383039122502401 (WINDSOR C A MARK WEST STATION RD NR WINDSOR CA). |
Temporal Representation: |
The samples were collected between the dates of 2017-04-18 and 2017-04-18 |
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 158595, Triclopyr
|
Region 1 |
Russian River HU, Middle Russian River HA, Mark West HSA, Windsor Creek and its tributaries |
|
|
LOE ID: |
329327 |
|
Pollutant: |
Triclopyr |
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 USGS California Water Science Center data for Russian River HU, Middle Russian River HA, Mark West HSA, Windsor Creek and its tributaries to determine beneficial use support and results are as follows: 0 of 1 samples exceeded the water quality threshold for Triclopyr. |
Data Reference: |
WQX from the NWQMP for the 2026 Integrated Report in Region 1 |
|
SWAMP Data: |
Non-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 triclopyr is the USEPA Aquatic Life Benchmark of 26 ug/L for a fish (chronic) for Triclopyr Butoxyethyl Ester (BEE). |
Guideline Reference: |
OPP Aquatic Life Benchmarks |
|
Spatial Representation: |
The samples were collected at 1 monitoring site: USGS-383039122502401 (WINDSOR C A MARK WEST STATION RD NR WINDSOR CA). |
Temporal Representation: |
The samples were collected between the dates of 2017-04-18 and 2017-04-18 |
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 158594, Imidacloprid
|
Region 1 |
Russian River HU, Middle Russian River HA, Mark West HSA, Windsor Creek and its tributaries |
|
|
LOE ID: |
328409 |
|
Pollutant: |
Imidacloprid |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Dissolved |
|
Beneficial Use: |
Cold Freshwater Habitat |
|
Number of Samples: |
6 |
Number of Exceedances: |
4 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed USGS California Water Science Center data for Russian River HU, Middle Russian River HA, Mark West HSA, Windsor Creek and its tributaries to determine beneficial use support and results are as follows: 4 of 6 samples exceeded the water quality threshold for Imidacloprid. |
Data Reference: |
WQX from the NWQMP for the 2026 Integrated Report in Region 1 |
|
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 (Water Quality Control Plan, North Coast Basin). |
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 4-day average concentration of imidacloprid does not exceed 0.016 ug/L. |
Guideline Reference: |
Water Quality Criteria Report for Imidacloprid 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: USGS-383039122502401 (WINDSOR C A MARK WEST STATION RD NR WINDSOR CA). |
Temporal Representation: |
The samples were collected between the dates of 2017-04-04 and 2017-05-09 |
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 158594, Imidacloprid
|
Region 1 |
Russian River HU, Middle Russian River HA, Mark West HSA, Windsor Creek and its tributaries |
|
|
LOE ID: |
328411 |
|
Pollutant: |
Imidacloprid |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Dissolved |
|
Beneficial Use: |
Warm Freshwater Habitat |
|
Number of Samples: |
6 |
Number of Exceedances: |
4 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed USGS California Water Science Center data for Russian River HU, Middle Russian River HA, Mark West HSA, Windsor Creek and its tributaries to determine beneficial use support and results are as follows: 4 of 6 samples exceeded the water quality threshold for Imidacloprid. |
Data Reference: |
WQX from the NWQMP for the 2026 Integrated Report in Region 1 |
|
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 (Water Quality Control Plan, North Coast Basin). |
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 4-day average concentration of imidacloprid does not exceed 0.016 ug/L. |
Guideline Reference: |
Water Quality Criteria Report for Imidacloprid 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: USGS-383039122502401 (WINDSOR C A MARK WEST STATION RD NR WINDSOR CA). |
Temporal Representation: |
The samples were collected between the dates of 2017-04-04 and 2017-05-09 |
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 169147, Sediment
|
Region 1 |
Russian River HU, Middle Russian River HA, Mark West HSA, Windsor Creek and its tributaries |
|
|
LOE ID: |
328296 |
|
Pollutant: |
2,4-D (2,4-Dichlorophenoxy acetic acid) |
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 USGS California Water Science Center data for Russian River HU, Middle Russian River HA, Mark West HSA, Windsor Creek and its tributaries to determine beneficial use support and results are as follows: 0 of 1 samples exceeded the water quality threshold for Dichlorophenoxyacetic Acid, 2,4-. |
Data Reference: |
WQX from the NWQMP for the 2026 Integrated Report in Region 1 |
|
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 California Maximum Contaminant Level for Dichlorophenoxyacetic Acid, 2,4- incorporated by reference in the Water Quality Control Plan, North Coast Basin is 70 mg/L (California Maximum Contaminant Levels, 2012). |
Guideline Reference: |
Maximum Contaminant Levels for organic and inorganic chemicals. CCR Title 22 |
|
Spatial Representation: |
The samples were collected at 1 monitoring site: USGS-383039122502401 (WINDSOR C A MARK WEST STATION RD NR WINDSOR CA). |
Temporal Representation: |
The samples were collected between the dates of 2017-04-11 and 2017-04-11 |
Environmental Conditions: |
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QAPP Information: |
QAPP not required for USGS projects |
QAPP Information Reference(s): |
QAPP for USGS Data Collected during the 2026 Integrated Report Cycle |
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