Line of Evidence (LOE) for Decision ID 25430, Anthracene
|
Region 3 |
San Antonio Creek (San Antonio Watershed, Rancho del las Flores Bridge at Hwy 135 to downstream at Railroad Bridge) |
|
|
LOE ID: |
15835 |
|
Pollutant: |
Anthracene |
LOE Subgroup: |
Pollutant-Sediment |
Matrix: |
Sediment |
Fraction: |
None |
|
Beneficial Use: |
Cold Freshwater Habitat |
Aquatic Life 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: |
Central Coast Regional Board Staff assessed CCAMP_SWAMP Monitoring (00SW3001) data for San Antonio Creek (313) to determine beneficial use support and results are as follows: 0 of 2 samples exceed the criterion for Anthracene. |
Data Reference: |
Final Data File used for assessment: SWAMP Toxicity Data 2001-06 |
|
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. (Water Quality Control Plan, Central Coast Basin, General Objective Chapter III, Section II.A.2 Objectives for all Inland Surface Waters, Enclosed Bays and Estuaries). |
Objective/Criterion Reference: |
Water Quality Control Plan (Basin Plan) - Central Coast Region (Region 3) |
|
Evaluation Guideline: |
In fresh water sediments the probable effects level (predictive of sediment toxicity) for anthracene is 845 ug/Kg dry weight (MacDonald et al. 2000). |
Guideline Reference: |
Development and evaluation of consensus-based sediment effect concentrations for polychlorinated biphenyls. Environmental Toxicology and Chemistry. 19(5): 1403-1413 |
|
Spatial Representation: |
Data for this line of evidence for San Antonio Creek (313) was collected at 2 monitoring sites [ 313SAC-San Antonio Creek at Rail Road Bridge, u/s lagoon , 313SAI-San Antonio Creek at San Antonio Road West] |
Temporal Representation: |
Data was collected on a single day 3/28/2002. SWAMP toxicity monitoring includes both water samples (collected in both winter and summer) and sediment samples (collected in spring). |
Environmental Conditions: |
Staff is not aware of any special conditions that might effect interpretation of the data. |
QAPP Information: |
All data was collected following the Standard Operating Procedures and Data Quality Objectives outlined in the SWAMP QAMP, (Puckett, 2002). QA data are included in submission. All data are flagged as appropriate. |
QAPP Information Reference(s): |
|
Line of Evidence (LOE) for Decision ID 25430, Anthracene
|
Region 3 |
San Antonio Creek (San Antonio Watershed, Rancho del las Flores Bridge at Hwy 135 to downstream at Railroad Bridge) |
|
|
LOE ID: |
15608 |
|
Pollutant: |
Anthracene |
LOE Subgroup: |
Pollutant-Sediment |
Matrix: |
Sediment |
Fraction: |
None |
|
Beneficial Use: |
Cold Freshwater Habitat |
Aquatic Life Use: |
Cold Freshwater Habitat |
|
Number of Samples: |
1 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Central Coast Regional Board Staff assessed CCAMP_SWAMP Monitoring (03SW3001) data for San Antonio Creek (313) to determine beneficial use support and results are as follows: 0 of 1 samples exceed the criterion for Anthracene. |
Data Reference: |
Final Data File used for assessment: SWAMP Toxicity Data 2001-06 |
|
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. (Water Quality Control Plan, Central Coast Basin, General Objective Chapter III, Section II.A.2 Objectives for all Inland Surface Waters, Enclosed Bays and Estuaries). |
Objective/Criterion Reference: |
Water Quality Control Plan (Basin Plan) - Central Coast Region (Region 3) |
|
Evaluation Guideline: |
In fresh water sediments the probable effects level (predictive of sediment toxicity) for anthracene is 845 ug/Kg dry weight (MacDonald et al. 2000). |
Guideline Reference: |
Development and evaluation of consensus-based sediment effect concentrations for polychlorinated biphenyls. Environmental Toxicology and Chemistry. 19(5): 1403-1413 |
|
Spatial Representation: |
Data for this line of evidence for San Antonio Creek (313) was collected at 1 monitoring site [ 313SAI-San Antonio Creek at San Antonio Road West] |
Temporal Representation: |
Data was collected on a single day 3/31/2004. SWAMP toxicity monitoring includes both water samples (collected in both winter and summer) and sediment samples (collected in spring). |
Environmental Conditions: |
Staff is not aware of any special conditions that might effect interpretation of the data. |
QAPP Information: |
All data was collected following the Standard Operating Procedures and Data Quality Objectives outlined in the SWAMP QAMP, (Puckett, 2002). QA data are included in submission. All data are flagged as appropriate. |
QAPP Information Reference(s): |
|
Line of Evidence (LOE) for Decision ID 25430, Anthracene
|
Region 3 |
San Antonio Creek (San Antonio Watershed, Rancho del las Flores Bridge at Hwy 135 to downstream at Railroad Bridge) |
|
|
LOE ID: |
15609 |
|
Pollutant: |
Anthracene |
LOE Subgroup: |
Pollutant-Sediment |
Matrix: |
Sediment |
Fraction: |
None |
|
Beneficial Use: |
Warm Freshwater Habitat |
Aquatic Life 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: |
Central Coast Regional Board Staff assessed CCAMP_SWAMP Monitoring (03SW3001) data for San Antonio Creek (313) to determine beneficial use support and results are as follows: 0 of 1 samples exceed the criterion for Anthracene. |
Data Reference: |
Final Data File used for assessment: SWAMP Toxicity Data 2001-06 |
|
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. (Water Quality Control Plan, Central Coast Basin, General Objective Chapter III, Section II.A.2 Objectives for all Inland Surface Waters, Enclosed Bays and Estuaries). |
Objective/Criterion Reference: |
Water Quality Control Plan (Basin Plan) - Central Coast Region (Region 3) |
|
Evaluation Guideline: |
In fresh water sediments the probable effects level (predictive of sediment toxicity) for anthracene is 845 ug/Kg dry weight (MacDonald et al. 2000). |
Guideline Reference: |
Development and evaluation of consensus-based sediment effect concentrations for polychlorinated biphenyls. Environmental Toxicology and Chemistry. 19(5): 1403-1413 |
|
Spatial Representation: |
Data for this line of evidence for San Antonio Creek (313) was collected at 1 monitoring site [ 313SAI-San Antonio Creek at San Antonio Road West] |
Temporal Representation: |
Data was collected on a single day 3/31/2004. SWAMP toxicity monitoring includes both water samples (collected in both winter and summer) and sediment samples (collected in spring). |
Environmental Conditions: |
Staff is not aware of any special conditions that might effect interpretation of the data. |
QAPP Information: |
All data was collected following the Standard Operating Procedures and Data Quality Objectives outlined in the SWAMP QAMP, (Puckett, 2002). QA data are included in submission. All data are flagged as appropriate. |
QAPP Information Reference(s): |
|
Line of Evidence (LOE) for Decision ID 25430, Anthracene
|
Region 3 |
San Antonio Creek (San Antonio Watershed, Rancho del las Flores Bridge at Hwy 135 to downstream at Railroad Bridge) |
|
|
LOE ID: |
15848 |
|
Pollutant: |
Anthracene |
LOE Subgroup: |
Pollutant-Sediment |
Matrix: |
Sediment |
Fraction: |
None |
|
Beneficial Use: |
Warm Freshwater Habitat |
Aquatic Life 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: |
Central Coast Regional Board Staff assessed CCAMP_SWAMP Monitoring (00SW3001) data for San Antonio Creek (313) to determine beneficial use support and results are as follows: 0 of 2 samples exceed the criterion for Anthracene. |
Data Reference: |
Final Data File used for assessment: SWAMP Toxicity Data 2001-06 |
|
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. (Water Quality Control Plan, Central Coast Basin, General Objective Chapter III, Section II.A.2 Objectives for all Inland Surface Waters, Enclosed Bays and Estuaries). |
Objective/Criterion Reference: |
Water Quality Control Plan (Basin Plan) - Central Coast Region (Region 3) |
|
Evaluation Guideline: |
In fresh water sediments the probable effects level (predictive of sediment toxicity) for anthracene is 845 ug/Kg dry weight (MacDonald et al. 2000). |
Guideline Reference: |
Development and evaluation of consensus-based sediment effect concentrations for polychlorinated biphenyls. Environmental Toxicology and Chemistry. 19(5): 1403-1413 |
|
Spatial Representation: |
Data for this line of evidence for San Antonio Creek (313) was collected at 2 monitoring sites [ 313SAC-San Antonio Creek at Rail Road Bridge, u/s lagoon , 313SAI-San Antonio Creek at San Antonio Road West] |
Temporal Representation: |
Data was collected on a single day 3/28/2002. SWAMP toxicity monitoring includes both water samples (collected in both winter and summer) and sediment samples (collected in spring). |
Environmental Conditions: |
Staff is not aware of any special conditions that might effect interpretation of the data. |
QAPP Information: |
All data was collected following the Standard Operating Procedures and Data Quality Objectives outlined in the SWAMP QAMP, (Puckett, 2002). QA data are included in submission. All data are flagged as appropriate. |
QAPP Information Reference(s): |
|
Line of Evidence (LOE) for Decision ID 25431, Arsenic
|
Region 3 |
San Antonio Creek (San Antonio Watershed, Rancho del las Flores Bridge at Hwy 135 to downstream at Railroad Bridge) |
|
|
LOE ID: |
15675 |
|
Pollutant: |
Arsenic |
LOE Subgroup: |
Pollutant-Sediment |
Matrix: |
Sediment |
Fraction: |
None |
|
Beneficial Use: |
Cold Freshwater Habitat |
Aquatic Life Use: |
Cold Freshwater Habitat |
|
Number of Samples: |
1 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Central Coast Regional Board Staff assessed CCAMP_SWAMP Monitoring (03SW3001) data for San Antonio Creek (313) to determine beneficial use support and results are as follows: 0 of 1 samples exceed the criterion for Arsenic. |
Data Reference: |
Final Data File used for assessment: SWAMP Toxicity Data 2001-06 |
|
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. (Water Quality Control Plan, Central Coast Basin, General Objective Chapter III, Section II.A.2 Objectives for all Inland Surface Waters, Enclosed Bays and Estuaries). |
Objective/Criterion Reference: |
Water Quality Control Plan (Basin Plan) - Central Coast Region (Region 3) |
|
Evaluation Guideline: |
In fresh water sediments the probable effects level (predictive of sediment toxicity) for arsenic is 33 mg/Kg dry weight (MacDonald et al. 2000). |
Guideline Reference: |
Development and evaluation of consensus-based sediment effect concentrations for polychlorinated biphenyls. Environmental Toxicology and Chemistry. 19(5): 1403-1413 |
|
Spatial Representation: |
Data for this line of evidence for San Antonio Creek (313) was collected at 1 monitoring site [ 313SAI-San Antonio Creek at San Antonio Road West] |
Temporal Representation: |
Data was collected on a single day 3/31/2004. SWAMP toxicity monitoring includes both water samples (collected in both winter and summer) and sediment samples (collected in spring). |
Environmental Conditions: |
Staff is not aware of any special conditions that might effect interpretation of the data. |
QAPP Information: |
All data was collected following the Standard Operating Procedures and Data Quality Objectives outlined in the SWAMP QAMP, (Puckett, 2002). QA data are included in submission. All data are flagged as appropriate. |
QAPP Information Reference(s): |
|
Line of Evidence (LOE) for Decision ID 25431, Arsenic
|
Region 3 |
San Antonio Creek (San Antonio Watershed, Rancho del las Flores Bridge at Hwy 135 to downstream at Railroad Bridge) |
|
|
LOE ID: |
15645 |
|
Pollutant: |
Arsenic |
LOE Subgroup: |
Pollutant-Sediment |
Matrix: |
Sediment |
Fraction: |
None |
|
Beneficial Use: |
Cold Freshwater Habitat |
Aquatic Life 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: |
Central Coast Regional Board Staff assessed CCAMP_SWAMP Monitoring (00SW3001) data for San Antonio Creek (313) to determine beneficial use support and results are as follows: 0 of 2 samples exceed the criterion for Arsenic. |
Data Reference: |
Final Data File used for assessment: SWAMP Toxicity Data 2001-06 |
|
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. (Water Quality Control Plan, Central Coast Basin, General Objective Chapter III, Section II.A.2 Objectives for all Inland Surface Waters, Enclosed Bays and Estuaries). |
Objective/Criterion Reference: |
Water Quality Control Plan (Basin Plan) - Central Coast Region (Region 3) |
|
Evaluation Guideline: |
In fresh water sediments the probable effects level (predictive of sediment toxicity) for arsenic is 33 mg/Kg dry weight (MacDonald et al. 2000). |
Guideline Reference: |
Development and evaluation of consensus-based sediment effect concentrations for polychlorinated biphenyls. Environmental Toxicology and Chemistry. 19(5): 1403-1413 |
|
Spatial Representation: |
Data for this line of evidence for San Antonio Creek (313) was collected at 2 monitoring sites [ 313SAC-San Antonio Creek at Rail Road Bridge, u/s lagoon , 313SAI-San Antonio Creek at San Antonio Road West] |
Temporal Representation: |
Data was collected on a single day 3/28/2002. SWAMP toxicity monitoring includes both water samples (collected in both winter and summer) and sediment samples (collected in spring). |
Environmental Conditions: |
Staff is not aware of any special conditions that might effect interpretation of the data. |
QAPP Information: |
All data was collected following the Standard Operating Procedures and Data Quality Objectives outlined in the SWAMP QAMP, (Puckett, 2002). QA data are included in submission. All data are flagged as appropriate. |
QAPP Information Reference(s): |
|
Line of Evidence (LOE) for Decision ID 25431, Arsenic
|
Region 3 |
San Antonio Creek (San Antonio Watershed, Rancho del las Flores Bridge at Hwy 135 to downstream at Railroad Bridge) |
|
|
LOE ID: |
15676 |
|
Pollutant: |
Arsenic |
LOE Subgroup: |
Pollutant-Sediment |
Matrix: |
Sediment |
Fraction: |
None |
|
Beneficial Use: |
Warm Freshwater Habitat |
Aquatic Life 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: |
Central Coast Regional Board Staff assessed CCAMP_SWAMP Monitoring (03SW3001) data for San Antonio Creek (313) to determine beneficial use support and results are as follows: 0 of 1 samples exceed the criterion for Arsenic. |
Data Reference: |
Final Data File used for assessment: SWAMP Toxicity Data 2001-06 |
|
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. (Water Quality Control Plan, Central Coast Basin, General Objective Chapter III, Section II.A.2 Objectives for all Inland Surface Waters, Enclosed Bays and Estuaries). |
Objective/Criterion Reference: |
Water Quality Control Plan (Basin Plan) - Central Coast Region (Region 3) |
|
Evaluation Guideline: |
In fresh water sediments the probable effects level (predictive of sediment toxicity) for arsenic is 33 mg/Kg dry weight (MacDonald et al. 2000). |
Guideline Reference: |
Development and evaluation of consensus-based sediment effect concentrations for polychlorinated biphenyls. Environmental Toxicology and Chemistry. 19(5): 1403-1413 |
|
Spatial Representation: |
Data for this line of evidence for San Antonio Creek (313) was collected at 1 monitoring site [ 313SAI-San Antonio Creek at San Antonio Road West] |
Temporal Representation: |
Data was collected on a single day 3/31/2004. SWAMP toxicity monitoring includes both water samples (collected in both winter and summer) and sediment samples (collected in spring). |
Environmental Conditions: |
Staff is not aware of any special conditions that might effect interpretation of the data. |
QAPP Information: |
All data was collected following the Standard Operating Procedures and Data Quality Objectives outlined in the SWAMP QAMP, (Puckett, 2002). QA data are included in submission. All data are flagged as appropriate. |
QAPP Information Reference(s): |
|
Line of Evidence (LOE) for Decision ID 25431, Arsenic
|
Region 3 |
San Antonio Creek (San Antonio Watershed, Rancho del las Flores Bridge at Hwy 135 to downstream at Railroad Bridge) |
|
|
LOE ID: |
15646 |
|
Pollutant: |
Arsenic |
LOE Subgroup: |
Pollutant-Sediment |
Matrix: |
Sediment |
Fraction: |
None |
|
Beneficial Use: |
Warm Freshwater Habitat |
Aquatic Life 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: |
Central Coast Regional Board Staff assessed CCAMP_SWAMP Monitoring (00SW3001) data for San Antonio Creek (313) to determine beneficial use support and results are as follows: 0 of 2 samples exceed the criterion for Arsenic. |
Data Reference: |
Final Data File used for assessment: SWAMP Toxicity Data 2001-06 |
|
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. (Water Quality Control Plan, Central Coast Basin, General Objective Chapter III, Section II.A.2 Objectives for all Inland Surface Waters, Enclosed Bays and Estuaries). |
Objective/Criterion Reference: |
Water Quality Control Plan (Basin Plan) - Central Coast Region (Region 3) |
|
Evaluation Guideline: |
In fresh water sediments the probable effects level (predictive of sediment toxicity) for arsenic is 33 mg/Kg dry weight (MacDonald et al. 2000). |
Guideline Reference: |
Development and evaluation of consensus-based sediment effect concentrations for polychlorinated biphenyls. Environmental Toxicology and Chemistry. 19(5): 1403-1413 |
|
Spatial Representation: |
Data for this line of evidence for San Antonio Creek (313) was collected at 2 monitoring sites [ 313SAC-San Antonio Creek at Rail Road Bridge, u/s lagoon , 313SAI-San Antonio Creek at San Antonio Road West] |
Temporal Representation: |
Data was collected on a single day 3/28/2002. SWAMP toxicity monitoring includes both water samples (collected in both winter and summer) and sediment samples (collected in spring). |
Environmental Conditions: |
Staff is not aware of any special conditions that might effect interpretation of the data. |
QAPP Information: |
All data was collected following the Standard Operating Procedures and Data Quality Objectives outlined in the SWAMP QAMP, (Puckett, 2002). QA data are included in submission. All data are flagged as appropriate. |
QAPP Information Reference(s): |
|
Line of Evidence (LOE) for Decision ID 25482, Benzo(a)anthracene
|
Region 3 |
San Antonio Creek (San Antonio Watershed, Rancho del las Flores Bridge at Hwy 135 to downstream at Railroad Bridge) |
|
|
LOE ID: |
15545 |
|
Pollutant: |
Benzo(a)anthracene |
LOE Subgroup: |
Pollutant-Sediment |
Matrix: |
Sediment |
Fraction: |
None |
|
Beneficial Use: |
Warm Freshwater Habitat |
Aquatic Life 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: |
Central Coast Regional Board Staff assessed CCAMP_SWAMP Monitoring (03SW3001) data for San Antonio Creek (313) to determine beneficial use support and results are as follows: 0 of 1 samples exceed the criterion for Benzo(a)anthracene. |
Data Reference: |
Final Data File used for assessment: SWAMP Toxicity Data 2001-06 |
|
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. (Water Quality Control Plan, Central Coast Basin, General Objective Chapter III, Section II.A.2 Objectives for all Inland Surface Waters, Enclosed Bays and Estuaries). |
Objective/Criterion Reference: |
Water Quality Control Plan (Basin Plan) - Central Coast Region (Region 3) |
|
Evaluation Guideline: |
In fresh water sediments the probable effects level (predictive of sediment toxicity) for Benzo(a)anthracene is 1050 ug/Kg dry weight (MacDonald et al. 2000). |
Guideline Reference: |
Development and evaluation of consensus-based sediment effect concentrations for polychlorinated biphenyls. Environmental Toxicology and Chemistry. 19(5): 1403-1413 |
|
Spatial Representation: |
Data for this line of evidence for San Antonio Creek (313) was collected at 1 monitoring site [ 313SAI-San Antonio Creek at San Antonio Road West] |
Temporal Representation: |
Data was collected on a single day 3/31/2004. SWAMP toxicity monitoring includes both water samples (collected in both winter and summer) and sediment samples (collected in spring). |
Environmental Conditions: |
Staff is not aware of any special conditions that might effect interpretation of the data. |
QAPP Information: |
All data was collected following the Standard Operating Procedures and Data Quality Objectives outlined in the SWAMP QAMP, (Puckett, 2002). QA data are included in submission. All data are flagged as appropriate. |
QAPP Information Reference(s): |
|
Line of Evidence (LOE) for Decision ID 25482, Benzo(a)anthracene
|
Region 3 |
San Antonio Creek (San Antonio Watershed, Rancho del las Flores Bridge at Hwy 135 to downstream at Railroad Bridge) |
|
|
LOE ID: |
15527 |
|
Pollutant: |
Benzo(a)anthracene |
LOE Subgroup: |
Pollutant-Sediment |
Matrix: |
Sediment |
Fraction: |
None |
|
Beneficial Use: |
Warm Freshwater Habitat |
Aquatic Life 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: |
Central Coast Regional Board Staff assessed CCAMP_SWAMP Monitoring (00SW3001) data for San Antonio Creek (313) to determine beneficial use support and results are as follows: 0 of 2 samples exceed the criterion for Benzo(a)anthracene. |
Data Reference: |
Final Data File used for assessment: SWAMP Toxicity Data 2001-06 |
|
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. (Water Quality Control Plan, Central Coast Basin, General Objective Chapter III, Section II.A.2 Objectives for all Inland Surface Waters, Enclosed Bays and Estuaries). |
Objective/Criterion Reference: |
Water Quality Control Plan (Basin Plan) - Central Coast Region (Region 3) |
|
Evaluation Guideline: |
In fresh water sediments the probable effects level (predictive of sediment toxicity) for Benzo(a)anthracene is 1050 ug/Kg dry weight (MacDonald et al. 2000). |
Guideline Reference: |
Development and evaluation of consensus-based sediment effect concentrations for polychlorinated biphenyls. Environmental Toxicology and Chemistry. 19(5): 1403-1413 |
|
Spatial Representation: |
Data for this line of evidence for San Antonio Creek (313) was collected at 2 monitoring sites [ 313SAC-San Antonio Creek at Rail Road Bridge, u/s lagoon , 313SAI-San Antonio Creek at San Antonio Road West] |
Temporal Representation: |
Data was collected on a single day 3/28/2002. SWAMP toxicity monitoring includes both water samples (collected in both winter and summer) and sediment samples (collected in spring). |
Environmental Conditions: |
Staff is not aware of any special conditions that might effect interpretation of the data. |
QAPP Information: |
All data was collected following the Standard Operating Procedures and Data Quality Objectives outlined in the SWAMP QAMP, (Puckett, 2002). QA data are included in submission. All data are flagged as appropriate. |
QAPP Information Reference(s): |
|
Line of Evidence (LOE) for Decision ID 25482, Benzo(a)anthracene
|
Region 3 |
San Antonio Creek (San Antonio Watershed, Rancho del las Flores Bridge at Hwy 135 to downstream at Railroad Bridge) |
|
|
LOE ID: |
15544 |
|
Pollutant: |
Benzo(a)anthracene |
LOE Subgroup: |
Pollutant-Sediment |
Matrix: |
Sediment |
Fraction: |
None |
|
Beneficial Use: |
Cold Freshwater Habitat |
Aquatic Life Use: |
Cold Freshwater Habitat |
|
Number of Samples: |
1 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Central Coast Regional Board Staff assessed CCAMP_SWAMP Monitoring (03SW3001) data for San Antonio Creek (313) to determine beneficial use support and results are as follows: 0 of 1 samples exceed the criterion for Benzo(a)anthracene. |
Data Reference: |
Final Data File used for assessment: SWAMP Toxicity Data 2001-06 |
|
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. (Water Quality Control Plan, Central Coast Basin, General Objective Chapter III, Section II.A.2 Objectives for all Inland Surface Waters, Enclosed Bays and Estuaries). |
Objective/Criterion Reference: |
Water Quality Control Plan (Basin Plan) - Central Coast Region (Region 3) |
|
Evaluation Guideline: |
In fresh water sediments the probable effects level (predictive of sediment toxicity) for Benzo(a)anthracene is 1050 ug/Kg dry weight (MacDonald et al. 2000). |
Guideline Reference: |
Development and evaluation of consensus-based sediment effect concentrations for polychlorinated biphenyls. Environmental Toxicology and Chemistry. 19(5): 1403-1413 |
|
Spatial Representation: |
Data for this line of evidence for San Antonio Creek (313) was collected at 1 monitoring site [ 313SAI-San Antonio Creek at San Antonio Road West] |
Temporal Representation: |
Data was collected on a single day 3/31/2004. SWAMP toxicity monitoring includes both water samples (collected in both winter and summer) and sediment samples (collected in spring). |
Environmental Conditions: |
Staff is not aware of any special conditions that might effect interpretation of the data. |
QAPP Information: |
All data was collected following the Standard Operating Procedures and Data Quality Objectives outlined in the SWAMP QAMP, (Puckett, 2002). QA data are included in submission. All data are flagged as appropriate. |
QAPP Information Reference(s): |
|
Line of Evidence (LOE) for Decision ID 25482, Benzo(a)anthracene
|
Region 3 |
San Antonio Creek (San Antonio Watershed, Rancho del las Flores Bridge at Hwy 135 to downstream at Railroad Bridge) |
|
|
LOE ID: |
15514 |
|
Pollutant: |
Benzo(a)anthracene |
LOE Subgroup: |
Pollutant-Sediment |
Matrix: |
Sediment |
Fraction: |
None |
|
Beneficial Use: |
Cold Freshwater Habitat |
Aquatic Life 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: |
Central Coast Regional Board Staff assessed CCAMP_SWAMP Monitoring (00SW3001) data for San Antonio Creek (313) to determine beneficial use support and results are as follows: 0 of 2 samples exceed the criterion for Benzo(a)anthracene. |
Data Reference: |
Final Data File used for assessment: SWAMP Toxicity Data 2001-06 |
|
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. (Water Quality Control Plan, Central Coast Basin, General Objective Chapter III, Section II.A.2 Objectives for all Inland Surface Waters, Enclosed Bays and Estuaries). |
Objective/Criterion Reference: |
Water Quality Control Plan (Basin Plan) - Central Coast Region (Region 3) |
|
Evaluation Guideline: |
In fresh water sediments the probable effects level (predictive of sediment toxicity) for Benzo(a)anthracene is 1050 ug/Kg dry weight (MacDonald et al. 2000). |
Guideline Reference: |
Development and evaluation of consensus-based sediment effect concentrations for polychlorinated biphenyls. Environmental Toxicology and Chemistry. 19(5): 1403-1413 |
|
Spatial Representation: |
Data for this line of evidence for San Antonio Creek (313) was collected at 2 monitoring sites [ 313SAC-San Antonio Creek at Rail Road Bridge, u/s lagoon , 313SAI-San Antonio Creek at San Antonio Road West] |
Temporal Representation: |
Data was collected on a single day 3/28/2002. SWAMP toxicity monitoring includes both water samples (collected in both winter and summer) and sediment samples (collected in spring). |
Environmental Conditions: |
Staff is not aware of any special conditions that might effect interpretation of the data. |
QAPP Information: |
All data was collected following the Standard Operating Procedures and Data Quality Objectives outlined in the SWAMP QAMP, (Puckett, 2002). QA data are included in submission. All data are flagged as appropriate. |
QAPP Information Reference(s): |
|
Line of Evidence (LOE) for Decision ID 25481, Benzo(a)pyrene (3,4-Benzopyrene -7-d)
|
Region 3 |
San Antonio Creek (San Antonio Watershed, Rancho del las Flores Bridge at Hwy 135 to downstream at Railroad Bridge) |
|
|
LOE ID: |
15394 |
|
Pollutant: |
Benzo(a)pyrene (3,4-Benzopyrene -7-d) |
LOE Subgroup: |
Pollutant-Sediment |
Matrix: |
Sediment |
Fraction: |
None |
|
Beneficial Use: |
Warm Freshwater Habitat |
Aquatic Life 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: |
Central Coast Regional Board Staff assessed CCAMP_SWAMP Monitoring (03SW3001) data for San Antonio Creek (313) to determine beneficial use support and results are as follows: 0 of 1 samples exceed the criterion for Benzo(a)pyrene. |
Data Reference: |
Final Data File used for assessment: SWAMP Toxicity Data 2001-06 |
|
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. (Water Quality Control Plan, Central Coast Basin, General Objective Chapter III, Section II.A.2 Objectives for all Inland Surface Waters, Enclosed Bays and Estuaries). |
Objective/Criterion Reference: |
Water Quality Control Plan (Basin Plan) - Central Coast Region (Region 3) |
|
Evaluation Guideline: |
In fresh water sediments the probable effects level (predictive of sediment toxicity) for Benzo(a)Pyrene is 1450 ug/Kg dry weight (Macdonald et al. 2000) |
Guideline Reference: |
Development and evaluation of consensus-based sediment effect concentrations for polychlorinated biphenyls. Environmental Toxicology and Chemistry. 19(5): 1403-1413 |
|
Spatial Representation: |
Data for this line of evidence for San Antonio Creek (313) was collected at 1 monitoring site [ 313SAI-San Antonio Creek at San Antonio Road West] |
Temporal Representation: |
Data was collected on a single day 3/31/2004. SWAMP toxicity monitoring includes both water samples (collected in both winter and summer) and sediment samples (collected in spring). |
Environmental Conditions: |
Staff is not aware of any special conditions that might effect interpretation of the data. |
QAPP Information: |
All data was collected following the Standard Operating Procedures and Data Quality Objectives outlined in the SWAMP QAMP, (Puckett, 2002). QA data are included in submission. All data are flagged as appropriate. |
QAPP Information Reference(s): |
|
Line of Evidence (LOE) for Decision ID 25481, Benzo(a)pyrene (3,4-Benzopyrene -7-d)
|
Region 3 |
San Antonio Creek (San Antonio Watershed, Rancho del las Flores Bridge at Hwy 135 to downstream at Railroad Bridge) |
|
|
LOE ID: |
15375 |
|
Pollutant: |
Benzo(a)pyrene (3,4-Benzopyrene -7-d) |
LOE Subgroup: |
Pollutant-Sediment |
Matrix: |
Sediment |
Fraction: |
None |
|
Beneficial Use: |
Cold Freshwater Habitat |
Aquatic Life 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: |
Central Coast Regional Board Staff assessed CCAMP_SWAMP Monitoring (00SW3001) data for San Antonio Creek (313) to determine beneficial use support and results are as follows: 0 of 2 samples exceed the criterion for Benzo(a)pyrene. |
Data Reference: |
Final Data File used for assessment: SWAMP Toxicity Data 2001-06 |
|
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. (Water Quality Control Plan, Central Coast Basin, General Objective Chapter III, Section II.A.2 Objectives for all Inland Surface Waters, Enclosed Bays and Estuaries). |
Objective/Criterion Reference: |
Water Quality Control Plan (Basin Plan) - Central Coast Region (Region 3) |
|
Evaluation Guideline: |
In fresh water sediments the probable effects level (predictive of sediment toxicity) for Benzo(a)Pyrene is 1450 ug/Kg dry weight (Macdonald et al. 2000) |
Guideline Reference: |
Development and evaluation of consensus-based sediment effect concentrations for polychlorinated biphenyls. Environmental Toxicology and Chemistry. 19(5): 1403-1413 |
|
Spatial Representation: |
Data for this line of evidence for San Antonio Creek (313) was collected at 2 monitoring sites [ 313SAC-San Antonio Creek at Rail Road Bridge, u/s lagoon , 313SAI-San Antonio Creek at San Antonio Road West] |
Temporal Representation: |
Data was collected on a single day 3/28/2002. SWAMP toxicity monitoring includes both water samples (collected in both winter and summer) and sediment samples (collected in spring). |
Environmental Conditions: |
Staff is not aware of any special conditions that might effect interpretation of the data. |
QAPP Information: |
All data was collected following the Standard Operating Procedures and Data Quality Objectives outlined in the SWAMP QAMP, (Puckett, 2002). QA data are included in submission. All data are flagged as appropriate. |
QAPP Information Reference(s): |
|
Line of Evidence (LOE) for Decision ID 25481, Benzo(a)pyrene (3,4-Benzopyrene -7-d)
|
Region 3 |
San Antonio Creek (San Antonio Watershed, Rancho del las Flores Bridge at Hwy 135 to downstream at Railroad Bridge) |
|
|
LOE ID: |
15393 |
|
Pollutant: |
Benzo(a)pyrene (3,4-Benzopyrene -7-d) |
LOE Subgroup: |
Pollutant-Sediment |
Matrix: |
Sediment |
Fraction: |
None |
|
Beneficial Use: |
Cold Freshwater Habitat |
Aquatic Life Use: |
Cold Freshwater Habitat |
|
Number of Samples: |
1 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Central Coast Regional Board Staff assessed CCAMP_SWAMP Monitoring (03SW3001) data for San Antonio Creek (313) to determine beneficial use support and results are as follows: 0 of 1 samples exceed the criterion for Benzo(a)pyrene. |
Data Reference: |
Final Data File used for assessment: SWAMP Toxicity Data 2001-06 |
|
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. (Water Quality Control Plan, Central Coast Basin, General Objective Chapter III, Section II.A.2 Objectives for all Inland Surface Waters, Enclosed Bays and Estuaries). |
Objective/Criterion Reference: |
Water Quality Control Plan (Basin Plan) - Central Coast Region (Region 3) |
|
Evaluation Guideline: |
In fresh water sediments the probable effects level (predictive of sediment toxicity) for Benzo(a)Pyrene is 1450 ug/Kg dry weight (Macdonald et al. 2000) |
Guideline Reference: |
Development and evaluation of consensus-based sediment effect concentrations for polychlorinated biphenyls. Environmental Toxicology and Chemistry. 19(5): 1403-1413 |
|
Spatial Representation: |
Data for this line of evidence for San Antonio Creek (313) was collected at 1 monitoring site [ 313SAI-San Antonio Creek at San Antonio Road West] |
Temporal Representation: |
Data was collected on a single day 3/31/2004. SWAMP toxicity monitoring includes both water samples (collected in both winter and summer) and sediment samples (collected in spring). |
Environmental Conditions: |
Staff is not aware of any special conditions that might effect interpretation of the data. |
QAPP Information: |
All data was collected following the Standard Operating Procedures and Data Quality Objectives outlined in the SWAMP QAMP, (Puckett, 2002). QA data are included in submission. All data are flagged as appropriate. |
QAPP Information Reference(s): |
|
Line of Evidence (LOE) for Decision ID 25481, Benzo(a)pyrene (3,4-Benzopyrene -7-d)
|
Region 3 |
San Antonio Creek (San Antonio Watershed, Rancho del las Flores Bridge at Hwy 135 to downstream at Railroad Bridge) |
|
|
LOE ID: |
15376 |
|
Pollutant: |
Benzo(a)pyrene (3,4-Benzopyrene -7-d) |
LOE Subgroup: |
Pollutant-Sediment |
Matrix: |
Sediment |
Fraction: |
None |
|
Beneficial Use: |
Warm Freshwater Habitat |
Aquatic Life 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: |
Central Coast Regional Board Staff assessed CCAMP_SWAMP Monitoring (00SW3001) data for San Antonio Creek (313) to determine beneficial use support and results are as follows: 0 of 2 samples exceed the criterion for Benzo(a)pyrene. |
Data Reference: |
Final Data File used for assessment: SWAMP Toxicity Data 2001-06 |
|
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. (Water Quality Control Plan, Central Coast Basin, General Objective Chapter III, Section II.A.2 Objectives for all Inland Surface Waters, Enclosed Bays and Estuaries). |
Objective/Criterion Reference: |
Water Quality Control Plan (Basin Plan) - Central Coast Region (Region 3) |
|
Evaluation Guideline: |
In fresh water sediments the probable effects level (predictive of sediment toxicity) for Benzo(a)Pyrene is 1450 ug/Kg dry weight (Macdonald et al. 2000) |
Guideline Reference: |
Development and evaluation of consensus-based sediment effect concentrations for polychlorinated biphenyls. Environmental Toxicology and Chemistry. 19(5): 1403-1413 |
|
Spatial Representation: |
Data for this line of evidence for San Antonio Creek (313) was collected at 2 monitoring sites [ 313SAC-San Antonio Creek at Rail Road Bridge, u/s lagoon , 313SAI-San Antonio Creek at San Antonio Road West] |
Temporal Representation: |
Data was collected on a single day 3/28/2002. SWAMP toxicity monitoring includes both water samples (collected in both winter and summer) and sediment samples (collected in spring). |
Environmental Conditions: |
Staff is not aware of any special conditions that might effect interpretation of the data. |
QAPP Information: |
All data was collected following the Standard Operating Procedures and Data Quality Objectives outlined in the SWAMP QAMP, (Puckett, 2002). QA data are included in submission. All data are flagged as appropriate. |
QAPP Information Reference(s): |
|
Line of Evidence (LOE) for Decision ID 25495, Cadmium
|
Region 3 |
San Antonio Creek (San Antonio Watershed, Rancho del las Flores Bridge at Hwy 135 to downstream at Railroad Bridge) |
|
|
LOE ID: |
15460 |
|
Pollutant: |
Cadmium |
LOE Subgroup: |
Pollutant-Sediment |
Matrix: |
Sediment |
Fraction: |
None |
|
Beneficial Use: |
Cold Freshwater Habitat |
Aquatic Life 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: |
Central Coast Regional Board Staff assessed CCAMP_SWAMP Monitoring (00SW3001) data for San Antonio Creek (313) to determine beneficial use support and results are as follows: 0 of 2 samples exceed the criterion for Cadmium. |
Data Reference: |
Final Data File used for assessment: SWAMP Toxicity Data 2001-06 |
|
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. (Water Quality Control Plan, Central Coast Basin, General Objective Chapter III, Section II.A.2 Objectives for all Inland Surface Waters, Enclosed Bays and Estuaries). |
Objective/Criterion Reference: |
Water Quality Control Plan (Basin Plan) - Central Coast Region (Region 3) |
|
Evaluation Guideline: |
In fresh water sediments the probable effects level (predictive of sediment toxicity) for cadmium is 4.98 mg/Kg dry weight (MacDonald et al. 2000). |
Guideline Reference: |
Development and evaluation of consensus-based sediment effect concentrations for polychlorinated biphenyls. Environmental Toxicology and Chemistry. 19(5): 1403-1413 |
|
Spatial Representation: |
Data for this line of evidence for San Antonio Creek (313) was collected at 2 monitoring sites [ 313SAC-San Antonio Creek at Rail Road Bridge, u/s lagoon , 313SAI-San Antonio Creek at San Antonio Road West] |
Temporal Representation: |
Data was collected on a single day 3/28/2002. SWAMP toxicity monitoring includes both water samples (collected in both winter and summer) and sediment samples (collected in spring). |
Environmental Conditions: |
Staff is not aware of any special conditions that might effect interpretation of the data. |
QAPP Information: |
All data was collected following the Standard Operating Procedures and Data Quality Objectives outlined in the SWAMP QAMP, (Puckett, 2002). QA data are included in submission. All data are flagged as appropriate. |
QAPP Information Reference(s): |
|
Line of Evidence (LOE) for Decision ID 25495, Cadmium
|
Region 3 |
San Antonio Creek (San Antonio Watershed, Rancho del las Flores Bridge at Hwy 135 to downstream at Railroad Bridge) |
|
|
LOE ID: |
15491 |
|
Pollutant: |
Cadmium |
LOE Subgroup: |
Pollutant-Sediment |
Matrix: |
Sediment |
Fraction: |
None |
|
Beneficial Use: |
Warm Freshwater Habitat |
Aquatic Life 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: |
Central Coast Regional Board Staff assessed CCAMP_SWAMP Monitoring (03SW3001) data for San Antonio Creek (313) to determine beneficial use support and results are as follows: 0 of 1 samples exceed the criterion for Cadmium. |
Data Reference: |
Final Data File used for assessment: SWAMP Toxicity Data 2001-06 |
|
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. (Water Quality Control Plan, Central Coast Basin, General Objective Chapter III, Section II.A.2 Objectives for all Inland Surface Waters, Enclosed Bays and Estuaries). |
Objective/Criterion Reference: |
Water Quality Control Plan (Basin Plan) - Central Coast Region (Region 3) |
|
Evaluation Guideline: |
In fresh water sediments the probable effects level (predictive of sediment toxicity) for cadmium is 4.98 mg/Kg dry weight (MacDonald et al. 2000). |
Guideline Reference: |
Development and evaluation of consensus-based sediment effect concentrations for polychlorinated biphenyls. Environmental Toxicology and Chemistry. 19(5): 1403-1413 |
|
Spatial Representation: |
Data for this line of evidence for San Antonio Creek (313) was collected at 1 monitoring site [ 313SAI-San Antonio Creek at San Antonio Road West] |
Temporal Representation: |
Data was collected on a single day 3/31/2004. SWAMP toxicity monitoring includes both water samples (collected in both winter and summer) and sediment samples (collected in spring). |
Environmental Conditions: |
Staff is not aware of any special conditions that might effect interpretation of the data. |
QAPP Information: |
All data was collected following the Standard Operating Procedures and Data Quality Objectives outlined in the SWAMP QAMP, (Puckett, 2002). QA data are included in submission. All data are flagged as appropriate. |
QAPP Information Reference(s): |
|
Line of Evidence (LOE) for Decision ID 25495, Cadmium
|
Region 3 |
San Antonio Creek (San Antonio Watershed, Rancho del las Flores Bridge at Hwy 135 to downstream at Railroad Bridge) |
|
|
LOE ID: |
15478 |
|
Pollutant: |
Cadmium |
LOE Subgroup: |
Pollutant-Sediment |
Matrix: |
Sediment |
Fraction: |
None |
|
Beneficial Use: |
Cold Freshwater Habitat |
Aquatic Life Use: |
Cold Freshwater Habitat |
|
Number of Samples: |
1 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Central Coast Regional Board Staff assessed CCAMP_SWAMP Monitoring (03SW3001) data for San Antonio Creek (313) to determine beneficial use support and results are as follows: 0 of 1 samples exceed the criterion for Cadmium. |
Data Reference: |
Final Data File used for assessment: SWAMP Toxicity Data 2001-06 |
|
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. (Water Quality Control Plan, Central Coast Basin, General Objective Chapter III, Section II.A.2 Objectives for all Inland Surface Waters, Enclosed Bays and Estuaries). |
Objective/Criterion Reference: |
Water Quality Control Plan (Basin Plan) - Central Coast Region (Region 3) |
|
Evaluation Guideline: |
In fresh water sediments the probable effects level (predictive of sediment toxicity) for cadmium is 4.98 mg/Kg dry weight (MacDonald et al. 2000). |
Guideline Reference: |
Development and evaluation of consensus-based sediment effect concentrations for polychlorinated biphenyls. Environmental Toxicology and Chemistry. 19(5): 1403-1413 |
|
Spatial Representation: |
Data for this line of evidence for San Antonio Creek (313) was collected at 1 monitoring site [ 313SAI-San Antonio Creek at San Antonio Road West] |
Temporal Representation: |
Data was collected on a single day 3/31/2004. SWAMP toxicity monitoring includes both water samples (collected in both winter and summer) and sediment samples (collected in spring). |
Environmental Conditions: |
Staff is not aware of any special conditions that might effect interpretation of the data. |
QAPP Information: |
All data was collected following the Standard Operating Procedures and Data Quality Objectives outlined in the SWAMP QAMP, (Puckett, 2002). QA data are included in submission. All data are flagged as appropriate. |
QAPP Information Reference(s): |
|
Line of Evidence (LOE) for Decision ID 25495, Cadmium
|
Region 3 |
San Antonio Creek (San Antonio Watershed, Rancho del las Flores Bridge at Hwy 135 to downstream at Railroad Bridge) |
|
|
LOE ID: |
15461 |
|
Pollutant: |
Cadmium |
LOE Subgroup: |
Pollutant-Sediment |
Matrix: |
Sediment |
Fraction: |
None |
|
Beneficial Use: |
Warm Freshwater Habitat |
Aquatic Life 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: |
Central Coast Regional Board Staff assessed CCAMP_SWAMP Monitoring (00SW3001) data for San Antonio Creek (313) to determine beneficial use support and results are as follows: 0 of 2 samples exceed the criterion for Cadmium. |
Data Reference: |
Final Data File used for assessment: SWAMP Toxicity Data 2001-06 |
|
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. (Water Quality Control Plan, Central Coast Basin, General Objective Chapter III, Section II.A.2 Objectives for all Inland Surface Waters, Enclosed Bays and Estuaries). |
Objective/Criterion Reference: |
Water Quality Control Plan (Basin Plan) - Central Coast Region (Region 3) |
|
Evaluation Guideline: |
In fresh water sediments the probable effects level (predictive of sediment toxicity) for cadmium is 4.98 mg/Kg dry weight (MacDonald et al. 2000). |
Guideline Reference: |
Development and evaluation of consensus-based sediment effect concentrations for polychlorinated biphenyls. Environmental Toxicology and Chemistry. 19(5): 1403-1413 |
|
Spatial Representation: |
Data for this line of evidence for San Antonio Creek (313) was collected at 2 monitoring sites [ 313SAC-San Antonio Creek at Rail Road Bridge, u/s lagoon , 313SAI-San Antonio Creek at San Antonio Road West] |
Temporal Representation: |
Data was collected on a single day 3/28/2002. SWAMP toxicity monitoring includes both water samples (collected in both winter and summer) and sediment samples (collected in spring). |
Environmental Conditions: |
Staff is not aware of any special conditions that might effect interpretation of the data. |
QAPP Information: |
All data was collected following the Standard Operating Procedures and Data Quality Objectives outlined in the SWAMP QAMP, (Puckett, 2002). QA data are included in submission. All data are flagged as appropriate. |
QAPP Information Reference(s): |
|
Line of Evidence (LOE) for Decision ID 25344, Chlorophyll-a
|
Region 3 |
San Antonio Creek (San Antonio Watershed, Rancho del las Flores Bridge at Hwy 135 to downstream at Railroad Bridge) |
|
|
LOE ID: |
9678 |
|
Pollutant: |
Chlorophyll-a |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
None |
|
Beneficial Use: |
Cold Freshwater Habitat |
Aquatic Life Use: |
Cold Freshwater Habitat |
|
Number of Samples: |
28 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Central Coast Regional Board Staff assessed CCAMP Santa Barbara (SantaBarb) data for San Antonio Creek (313) to determine beneficial use support and results are as follows: 0 of 28 samples exceed the criterion for Chlorophyll a. |
Data Reference: |
Final Data File used for assessment: CCAMP Water Quality Data_file1 |
|
Final Data File used for assessment: CCAMP Water Quality Data_file2 |
|
Final Data File used for assessment: CCAMP Water Quality Data_file3 |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
Waters shall not contain biostimulatory substances in concentrations that promote aquatic growths to the extent that such growths cause nuisance or adversely affect beneficial uses (general objective for biostimulatory substances, Water Quality Control Plan, Central Coast Basin, Chapter III, Section II). |
Objective/Criterion Reference: |
Water Quality Control Plan (Basin Plan) - Central Coast Region (Region 3) |
|
North Carolina standards, criteria, or toxic concentrations. Adopted per title 15A North Carolina Administrative Code subchapter 2B - Surface water and wetland standards |
|
Water quality standards table |
|
Evaluation Guideline: |
North Carolina Administrative code (NCAC), Title 15A - Environmental and Natural Resources, Subchapter 2B-Surface water and wetland standards, Rule 0211-Fresh surface water quality standards for class C waters (Class C is defined as freshwaters protected for secondary recreation, fishing, aquatic life including propagation and survival, and wildlife). Section 3(a) of Rule 0211 applies to all fresh surface waters and states that chlorophyll a is not to exceed 40 ug/L. |
Guideline Reference: |
North Carolina standards, criteria, or toxic concentrations. Adopted per title 15A North Carolina Administrative Code subchapter 2B - Surface water and wetland standards |
|
North Carolina standards, criteria, or toxic concentrations. Adopted per title 15A North Carolina Administrative Code subchapter 2B - Surface water and wetland standards |
|
Spatial Representation: |
Data for this line of evidence for San Antonio Creek (313) was collected at 3 monitoring sites [ 313SAB-San Antonio Creek at Rancho de las Flores Bridge and Highway 135, 313SAE-San Antonio Creek at San Antonio Road East, 313SAI-San Antonio Creek at San Antonio Road West] |
Temporal Representation: |
Data was collected over the time period 1/18/2001-3/17/2002. Santa Barbara Coast is one of five annual rotation areas that are monitored for conventional pollutants by CCAMP staff monthly for one year. Toxicity monitoring is conducted twice during the rotation year (winter and summer) at a subset of sites. |
Environmental Conditions: |
Staff is not aware of any special conditions that might effect interpretation of the data. |
QAPP Information: |
All data was collected following the Standard Operating Procedures and Data Quality Objectives outlined in the SWAMP QAMP, (Puckett, 2002). QA data are included in submission. All data are flagged as appropriate. |
QAPP Information Reference(s): |
|
Line of Evidence (LOE) for Decision ID 25344, Chlorophyll-a
|
Region 3 |
San Antonio Creek (San Antonio Watershed, Rancho del las Flores Bridge at Hwy 135 to downstream at Railroad Bridge) |
|
|
LOE ID: |
9709 |
|
Pollutant: |
Chlorophyll-a |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
None |
|
Beneficial Use: |
Cold Freshwater Habitat |
Aquatic Life Use: |
Cold Freshwater Habitat |
|
Number of Samples: |
60 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Central Coast Regional Board Staff assessed CCAMP Coastal Confluences (CC) data for San Antonio Creek (313) to determine beneficial use support and results are as follows: 0 of 60 samples exceed the criterion for Chlorophyll a. |
Data Reference: |
Final Data File used for assessment: CCAMP Water Quality Data_file1 |
|
Final Data File used for assessment: CCAMP Water Quality Data_file2 |
|
Final Data File used for assessment: CCAMP Water Quality Data_file3 |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
Waters shall not contain biostimulatory substances in concentrations that promote aquatic growths to the extent that such growths cause nuisance or adversely affect beneficial uses (general objective for biostimulatory substances, Water Quality Control Plan, Central Coast Basin, Chapter III, Section II). |
Objective/Criterion Reference: |
Water Quality Control Plan (Basin Plan) - Central Coast Region (Region 3) |
|
North Carolina standards, criteria, or toxic concentrations. Adopted per title 15A North Carolina Administrative Code subchapter 2B - Surface water and wetland standards |
|
Water quality standards table |
|
Evaluation Guideline: |
North Carolina Administrative code (NCAC), Title 15A - Environmental and Natural Resources, Subchapter 2B-Surface water and wetland standards, Rule 0211-Fresh surface water quality standards for class C waters (Class C is defined as freshwaters protected for secondary recreation, fishing, aquatic life including propagation and survival, and wildlife). Section 3(a) of Rule 0211 applies to all fresh surface waters and states that chlorophyll a is not to exceed 40 ug/L. |
Guideline Reference: |
North Carolina standards, criteria, or toxic concentrations. Adopted per title 15A North Carolina Administrative Code subchapter 2B - Surface water and wetland standards |
|
North Carolina standards, criteria, or toxic concentrations. Adopted per title 15A North Carolina Administrative Code subchapter 2B - Surface water and wetland standards |
|
Spatial Representation: |
Data for this line of evidence for San Antonio Creek (313) was collected at 2 monitoring sites [ 313SAC-San Antonio Creek at Rail Road Bridge, u/s lagoon , 313SAI-San Antonio Creek at San Antonio Road West] |
Temporal Representation: |
Data was collected over the time period 1/18/2001-12/6/2006. CCAMP Coastal confluence monitoring is conducted monthly (with the exception of April 2003 - December 2003) and is ongoing. |
Environmental Conditions: |
Staff is not aware of any special conditions that might effect interpretation of the data. |
QAPP Information: |
All data was collected following the Standard Operating Procedures and Data Quality Objectives outlined in the SWAMP QAMP, (Puckett, 2002). QA data are included in submission. All data are flagged as appropriate. |
QAPP Information Reference(s): |
|
Line of Evidence (LOE) for Decision ID 25344, Chlorophyll-a
|
Region 3 |
San Antonio Creek (San Antonio Watershed, Rancho del las Flores Bridge at Hwy 135 to downstream at Railroad Bridge) |
|
|
LOE ID: |
9810 |
|
Pollutant: |
Chlorophyll-a |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
None |
|
Beneficial Use: |
Warm Freshwater Habitat |
Aquatic Life Use: |
Warm Freshwater Habitat |
|
Number of Samples: |
60 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Central Coast Regional Board Staff assessed CCAMP Coastal Confluences (CC) data for San Antonio Creek (313) to determine beneficial use support and results are as follows: 0 of 60 samples exceed the criterion for Chlorophyll a. |
Data Reference: |
Final Data File used for assessment: CCAMP Water Quality Data_file1 |
|
Final Data File used for assessment: CCAMP Water Quality Data_file2 |
|
Final Data File used for assessment: CCAMP Water Quality Data_file3 |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
Waters shall not contain biostimulatory substances in concentrations that promote aquatic growths to the extent that such growths cause nuisance or adversely affect beneficial uses (general objective for biostimulatory substances, Water Quality Control Plan, Central Coast Basin, Chapter III, Section II). |
Objective/Criterion Reference: |
Water Quality Control Plan (Basin Plan) - Central Coast Region (Region 3) |
|
North Carolina standards, criteria, or toxic concentrations. Adopted per title 15A North Carolina Administrative Code subchapter 2B - Surface water and wetland standards |
|
Water quality standards table |
|
Evaluation Guideline: |
North Carolina Administrative code (NCAC), Title 15A - Environmental and Natural Resources, Subchapter 2B-Surface water and wetland standards, Rule 0211-Fresh surface water quality standards for class C waters (Class C is defined as freshwaters protected for secondary recreation, fishing, aquatic life including propagation and survival, and wildlife). Section 3(a) of Rule 0211 applies to all fresh surface waters and states that chlorophyll a is not to exceed 40 ug/L. |
Guideline Reference: |
North Carolina standards, criteria, or toxic concentrations. Adopted per title 15A North Carolina Administrative Code subchapter 2B - Surface water and wetland standards |
|
Spatial Representation: |
Data for this line of evidence for San Antonio Creek (313) was collected at 2 monitoring sites [ 313SAC-San Antonio Creek at Rail Road Bridge, u/s lagoon , 313SAI-San Antonio Creek at San Antonio Road West] |
Temporal Representation: |
Data was collected over the time period 1/18/2001-12/6/2006. CCAMP Coastal confluence monitoring is conducted monthly (with the exception of April 2003 - December 2003) and is ongoing. |
Environmental Conditions: |
Staff is not aware of any special conditions that might effect interpretation of the data. |
QAPP Information: |
All data was collected following the Standard Operating Procedures and Data Quality Objectives outlined in the SWAMP QAMP, (Puckett, 2002). QA data are included in submission. All data are flagged as appropriate. |
QAPP Information Reference(s): |
|
Line of Evidence (LOE) for Decision ID 25344, Chlorophyll-a
|
Region 3 |
San Antonio Creek (San Antonio Watershed, Rancho del las Flores Bridge at Hwy 135 to downstream at Railroad Bridge) |
|
|
LOE ID: |
9691 |
|
Pollutant: |
Chlorophyll-a |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
None |
|
Beneficial Use: |
Warm Freshwater Habitat |
Aquatic Life Use: |
Warm Freshwater Habitat |
|
Number of Samples: |
28 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Central Coast Regional Board Staff assessed CCAMP Santa Barbara (SantaBarb) data for San Antonio Creek (313) to determine beneficial use support and results are as follows: 0 of 28 samples exceed the criterion for Chlorophyll a. |
Data Reference: |
Final Data File used for assessment: CCAMP Water Quality Data_file1 |
|
Final Data File used for assessment: CCAMP Water Quality Data_file2 |
|
Final Data File used for assessment: CCAMP Water Quality Data_file3 |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
Waters shall not contain biostimulatory substances in concentrations that promote aquatic growths to the extent that such growths cause nuisance or adversely affect beneficial uses (general objective for biostimulatory substances, Water Quality Control Plan, Central Coast Basin, Chapter III, Section II). |
Objective/Criterion Reference: |
Water Quality Control Plan (Basin Plan) - Central Coast Region (Region 3) |
|
North Carolina standards, criteria, or toxic concentrations. Adopted per title 15A North Carolina Administrative Code subchapter 2B - Surface water and wetland standards |
|
Water quality standards table |
|
Evaluation Guideline: |
North Carolina Administrative code (NCAC), Title 15A - Environmental and Natural Resources, Subchapter 2B-Surface water and wetland standards, Rule 0211-Fresh surface water quality standards for class C waters (Class C is defined as freshwaters protected for secondary recreation, fishing, aquatic life including propagation and survival, and wildlife). Section 3(a) of Rule 0211 applies to all fresh surface waters and states that chlorophyll a is not to exceed 40 ug/L. |
Guideline Reference: |
North Carolina standards, criteria, or toxic concentrations. Adopted per title 15A North Carolina Administrative Code subchapter 2B - Surface water and wetland standards |
|
North Carolina standards, criteria, or toxic concentrations. Adopted per title 15A North Carolina Administrative Code subchapter 2B - Surface water and wetland standards |
|
Spatial Representation: |
Data for this line of evidence for San Antonio Creek (313) was collected at 3 monitoring sites [ 313SAB-San Antonio Creek at Rancho de las Flores Bridge and Highway 135, 313SAE-San Antonio Creek at San Antonio Road East, 313SAI-San Antonio Creek at San Antonio Road West] |
Temporal Representation: |
Data was collected over the time period 1/18/2001-3/17/2002. Santa Barbara Coast is one of five annual rotation areas that are monitored for conventional pollutants by CCAMP staff monthly for one year. Toxicity monitoring is conducted twice during the rotation year (winter and summer) at a subset of sites. |
Environmental Conditions: |
Staff is not aware of any special conditions that might effect interpretation of the data. |
QAPP Information: |
All data was collected following the Standard Operating Procedures and Data Quality Objectives outlined in the SWAMP QAMP, (Puckett, 2002). QA data are included in submission. All data are flagged as appropriate. |
QAPP Information Reference(s): |
|
Line of Evidence (LOE) for Decision ID 25343, Chromium (total)
|
Region 3 |
San Antonio Creek (San Antonio Watershed, Rancho del las Flores Bridge at Hwy 135 to downstream at Railroad Bridge) |
|
|
LOE ID: |
15932 |
|
Pollutant: |
Chromium (total) |
LOE Subgroup: |
Pollutant-Sediment |
Matrix: |
Sediment |
Fraction: |
None |
|
Beneficial Use: |
Cold Freshwater Habitat |
Aquatic Life Use: |
Cold Freshwater Habitat |
|
Number of Samples: |
1 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Central Coast Regional Board Staff assessed CCAMP_SWAMP Monitoring (03SW3001) data for San Antonio Creek (313) to determine beneficial use support and results are as follows: 0 of 1 samples exceed the criterion for Chromium. |
Data Reference: |
Final Data File used for assessment: SWAMP Toxicity Data 2001-06 |
|
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. (Water Quality Control Plan, Central Coast Basin, General Objective Chapter III, Section II.A.2 Objectives for all Inland Surface Waters, Enclosed Bays and Estuaries). |
Objective/Criterion Reference: |
Water Quality Control Plan (Basin Plan) - Central Coast Region (Region 3) |
|
Evaluation Guideline: |
In fresh water sediments the probable effects level (predictive of sediment toxicity) for chromium is 111 mg/Kg dry weight (MacDonald et al. 2000). |
Guideline Reference: |
Development and evaluation of consensus-based sediment effect concentrations for polychlorinated biphenyls. Environmental Toxicology and Chemistry. 19(5): 1403-1413 |
|
Spatial Representation: |
Data for this line of evidence for San Antonio Creek (313) was collected at 1 monitoring site [ 313SAI-San Antonio Creek at San Antonio Road West] |
Temporal Representation: |
Data was collected on a single day 3/31/2004. SWAMP toxicity monitoring includes both water samples (collected in both winter and summer) and sediment samples (collected in spring). |
Environmental Conditions: |
Staff is not aware of any special conditions that might effect interpretation of the data. |
QAPP Information: |
All data was collected following the Standard Operating Procedures and Data Quality Objectives outlined in the SWAMP QAMP, (Puckett, 2002). QA data are included in submission. All data are flagged as appropriate. |
QAPP Information Reference(s): |
|
Line of Evidence (LOE) for Decision ID 25343, Chromium (total)
|
Region 3 |
San Antonio Creek (San Antonio Watershed, Rancho del las Flores Bridge at Hwy 135 to downstream at Railroad Bridge) |
|
|
LOE ID: |
15933 |
|
Pollutant: |
Chromium (total) |
LOE Subgroup: |
Pollutant-Sediment |
Matrix: |
Sediment |
Fraction: |
None |
|
Beneficial Use: |
Warm Freshwater Habitat |
Aquatic Life 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: |
Central Coast Regional Board Staff assessed CCAMP_SWAMP Monitoring (03SW3001) data for San Antonio Creek (313) to determine beneficial use support and results are as follows: 0 of 1 samples exceed the criterion for Chromium. |
Data Reference: |
Final Data File used for assessment: SWAMP Toxicity Data 2001-06 |
|
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. (Water Quality Control Plan, Central Coast Basin, General Objective Chapter III, Section II.A.2 Objectives for all Inland Surface Waters, Enclosed Bays and Estuaries). |
Objective/Criterion Reference: |
Water Quality Control Plan (Basin Plan) - Central Coast Region (Region 3) |
|
Evaluation Guideline: |
In fresh water sediments the probable effects level (predictive of sediment toxicity) for chromium is 111 mg/Kg dry weight (MacDonald et al. 2000). |
Guideline Reference: |
Development and evaluation of consensus-based sediment effect concentrations for polychlorinated biphenyls. Environmental Toxicology and Chemistry. 19(5): 1403-1413 |
|
Spatial Representation: |
Data for this line of evidence for San Antonio Creek (313) was collected at 1 monitoring site [ 313SAI-San Antonio Creek at San Antonio Road West] |
Temporal Representation: |
Data was collected on a single day 3/31/2004. SWAMP toxicity monitoring includes both water samples (collected in both winter and summer) and sediment samples (collected in spring). |
Environmental Conditions: |
Staff is not aware of any special conditions that might effect interpretation of the data. |
QAPP Information: |
All data was collected following the Standard Operating Procedures and Data Quality Objectives outlined in the SWAMP QAMP, (Puckett, 2002). QA data are included in submission. All data are flagged as appropriate. |
QAPP Information Reference(s): |
|
Line of Evidence (LOE) for Decision ID 25343, Chromium (total)
|
Region 3 |
San Antonio Creek (San Antonio Watershed, Rancho del las Flores Bridge at Hwy 135 to downstream at Railroad Bridge) |
|
|
LOE ID: |
16100 |
|
Pollutant: |
Chromium (total) |
LOE Subgroup: |
Pollutant-Sediment |
Matrix: |
Sediment |
Fraction: |
None |
|
Beneficial Use: |
Cold Freshwater Habitat |
Aquatic Life 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: |
Central Coast Regional Board Staff assessed CCAMP_SWAMP Monitoring (00SW3001) data for San Antonio Creek (313) to determine beneficial use support and results are as follows: 0 of 2 samples exceed the criterion for Chromium. |
Data Reference: |
Final Data File used for assessment: SWAMP Toxicity Data 2001-06 |
|
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. (Water Quality Control Plan, Central Coast Basin, General Objective Chapter III, Section II.A.2 Objectives for all Inland Surface Waters, Enclosed Bays and Estuaries). |
Objective/Criterion Reference: |
Water Quality Control Plan (Basin Plan) - Central Coast Region (Region 3) |
|
Evaluation Guideline: |
In fresh water sediments the probable effects level (predictive of sediment toxicity) for chromium is 111 mg/Kg dry weight (MacDonald et al. 2000). |
Guideline Reference: |
Development and evaluation of consensus-based sediment effect concentrations for polychlorinated biphenyls. Environmental Toxicology and Chemistry. 19(5): 1403-1413 |
|
Spatial Representation: |
Data for this line of evidence for San Antonio Creek (313) was collected at 2 monitoring sites [ 313SAC-San Antonio Creek at Rail Road Bridge, u/s lagoon , 313SAI-San Antonio Creek at San Antonio Road West] |
Temporal Representation: |
Data was collected on a single day 3/28/2002. SWAMP toxicity monitoring includes both water samples (collected in both winter and summer) and sediment samples (collected in spring). |
Environmental Conditions: |
Staff is not aware of any special conditions that might effect interpretation of the data. |
QAPP Information: |
All data was collected following the Standard Operating Procedures and Data Quality Objectives outlined in the SWAMP QAMP, (Puckett, 2002). QA data are included in submission. All data are flagged as appropriate. |
QAPP Information Reference(s): |
|
Line of Evidence (LOE) for Decision ID 25343, Chromium (total)
|
Region 3 |
San Antonio Creek (San Antonio Watershed, Rancho del las Flores Bridge at Hwy 135 to downstream at Railroad Bridge) |
|
|
LOE ID: |
16101 |
|
Pollutant: |
Chromium (total) |
LOE Subgroup: |
Pollutant-Sediment |
Matrix: |
Sediment |
Fraction: |
None |
|
Beneficial Use: |
Warm Freshwater Habitat |
Aquatic Life 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: |
Central Coast Regional Board Staff assessed CCAMP_SWAMP Monitoring (00SW3001) data for San Antonio Creek (313) to determine beneficial use support and results are as follows: 0 of 2 samples exceed the criterion for Chromium. |
Data Reference: |
Final Data File used for assessment: SWAMP Toxicity Data 2001-06 |
|
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. (Water Quality Control Plan, Central Coast Basin, General Objective Chapter III, Section II.A.2 Objectives for all Inland Surface Waters, Enclosed Bays and Estuaries). |
Objective/Criterion Reference: |
Water Quality Control Plan (Basin Plan) - Central Coast Region (Region 3) |
|
Evaluation Guideline: |
In fresh water sediments the probable effects level (predictive of sediment toxicity) for chromium is 111 mg/Kg dry weight (MacDonald et al. 2000). |
Guideline Reference: |
Development and evaluation of consensus-based sediment effect concentrations for polychlorinated biphenyls. Environmental Toxicology and Chemistry. 19(5): 1403-1413 |
|
Spatial Representation: |
Data for this line of evidence for San Antonio Creek (313) was collected at 2 monitoring sites [ 313SAC-San Antonio Creek at Rail Road Bridge, u/s lagoon , 313SAI-San Antonio Creek at San Antonio Road West] |
Temporal Representation: |
Data was collected on a single day 3/28/2002. SWAMP toxicity monitoring includes both water samples (collected in both winter and summer) and sediment samples (collected in spring). |
Environmental Conditions: |
Staff is not aware of any special conditions that might effect interpretation of the data. |
QAPP Information: |
All data was collected following the Standard Operating Procedures and Data Quality Objectives outlined in the SWAMP QAMP, (Puckett, 2002). QA data are included in submission. All data are flagged as appropriate. |
QAPP Information Reference(s): |
|
Line of Evidence (LOE) for Decision ID 25450, Chrysene (C1-C4)
|
Region 3 |
San Antonio Creek (San Antonio Watershed, Rancho del las Flores Bridge at Hwy 135 to downstream at Railroad Bridge) |
|
|
LOE ID: |
15986 |
|
Pollutant: |
Chrysene (C1-C4) |
LOE Subgroup: |
Pollutant-Sediment |
Matrix: |
Sediment |
Fraction: |
None |
|
Beneficial Use: |
Warm Freshwater Habitat |
Aquatic Life 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: |
Central Coast Regional Board Staff assessed CCAMP_SWAMP Monitoring (00SW3001) data for San Antonio Creek (313) to determine beneficial use support and results are as follows: 0 of 2 samples exceed the criterion for Chrysene. |
Data Reference: |
Final Data File used for assessment: SWAMP Toxicity Data 2001-06 |
|
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. (Water Quality Control Plan, Central Coast Basin, General Objective Chapter III, Section II.A.2 Objectives for all Inland Surface Waters, Enclosed Bays and Estuaries). |
Objective/Criterion Reference: |
Water Quality Control Plan (Basin Plan) - Central Coast Region (Region 3) |
|
Evaluation Guideline: |
In fresh water sediments the probable effects level (predictive of sediment toxicity) for Chrysene is 1290 ug/Kg dry weight (Macdonald et al. 2000) |
Guideline Reference: |
Development and evaluation of consensus-based sediment effect concentrations for polychlorinated biphenyls. Environmental Toxicology and Chemistry. 19(5): 1403-1413 |
|
Spatial Representation: |
Data for this line of evidence for San Antonio Creek (313) was collected at 2 monitoring sites [ 313SAC-San Antonio Creek at Rail Road Bridge, u/s lagoon , 313SAI-San Antonio Creek at San Antonio Road West] |
Temporal Representation: |
Data was collected on a single day 3/28/2002. SWAMP toxicity monitoring includes both water samples (collected in both winter and summer) and sediment samples (collected in spring). |
Environmental Conditions: |
Staff is not aware of any special conditions that might effect interpretation of the data. |
QAPP Information: |
All data was collected following the Standard Operating Procedures and Data Quality Objectives outlined in the SWAMP QAMP, (Puckett, 2002). QA data are included in submission. All data are flagged as appropriate. |
QAPP Information Reference(s): |
|
Line of Evidence (LOE) for Decision ID 25450, Chrysene (C1-C4)
|
Region 3 |
San Antonio Creek (San Antonio Watershed, Rancho del las Flores Bridge at Hwy 135 to downstream at Railroad Bridge) |
|
|
LOE ID: |
15985 |
|
Pollutant: |
Chrysene (C1-C4) |
LOE Subgroup: |
Pollutant-Sediment |
Matrix: |
Sediment |
Fraction: |
None |
|
Beneficial Use: |
Cold Freshwater Habitat |
Aquatic Life 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: |
Central Coast Regional Board Staff assessed CCAMP_SWAMP Monitoring (00SW3001) data for San Antonio Creek (313) to determine beneficial use support and results are as follows: 0 of 2 samples exceed the criterion for Chrysene. |
Data Reference: |
Final Data File used for assessment: SWAMP Toxicity Data 2001-06 |
|
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. (Water Quality Control Plan, Central Coast Basin, General Objective Chapter III, Section II.A.2 Objectives for all Inland Surface Waters, Enclosed Bays and Estuaries). |
Objective/Criterion Reference: |
Water Quality Control Plan (Basin Plan) - Central Coast Region (Region 3) |
|
Evaluation Guideline: |
In fresh water sediments the probable effects level (predictive of sediment toxicity) for Chrysene is 1290 ug/Kg dry weight (Macdonald et al. 2000) |
Guideline Reference: |
Development and evaluation of consensus-based sediment effect concentrations for polychlorinated biphenyls. Environmental Toxicology and Chemistry. 19(5): 1403-1413 |
|
Spatial Representation: |
Data for this line of evidence for San Antonio Creek (313) was collected at 2 monitoring sites [ 313SAC-San Antonio Creek at Rail Road Bridge, u/s lagoon , 313SAI-San Antonio Creek at San Antonio Road West] |
Temporal Representation: |
Data was collected on a single day 3/28/2002. SWAMP toxicity monitoring includes both water samples (collected in both winter and summer) and sediment samples (collected in spring). |
Environmental Conditions: |
Staff is not aware of any special conditions that might effect interpretation of the data. |
QAPP Information: |
All data was collected following the Standard Operating Procedures and Data Quality Objectives outlined in the SWAMP QAMP, (Puckett, 2002). QA data are included in submission. All data are flagged as appropriate. |
QAPP Information Reference(s): |
|
Line of Evidence (LOE) for Decision ID 25450, Chrysene (C1-C4)
|
Region 3 |
San Antonio Creek (San Antonio Watershed, Rancho del las Flores Bridge at Hwy 135 to downstream at Railroad Bridge) |
|
|
LOE ID: |
16003 |
|
Pollutant: |
Chrysene (C1-C4) |
LOE Subgroup: |
Pollutant-Sediment |
Matrix: |
Sediment |
Fraction: |
None |
|
Beneficial Use: |
Cold Freshwater Habitat |
Aquatic Life Use: |
Cold Freshwater Habitat |
|
Number of Samples: |
1 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Central Coast Regional Board Staff assessed CCAMP_SWAMP Monitoring (03SW3001) data for San Antonio Creek (313) to determine beneficial use support and results are as follows: 0 of 1 samples exceed the criterion for Chrysene. |
Data Reference: |
Final Data File used for assessment: SWAMP Toxicity Data 2001-06 |
|
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. (Water Quality Control Plan, Central Coast Basin, General Objective Chapter III, Section II.A.2 Objectives for all Inland Surface Waters, Enclosed Bays and Estuaries). |
Objective/Criterion Reference: |
Water Quality Control Plan (Basin Plan) - Central Coast Region (Region 3) |
|
Evaluation Guideline: |
In fresh water sediments the probable effects level (predictive of sediment toxicity) for Chrysene is 1290 ug/Kg dry weight (Macdonald et al. 2000) |
Guideline Reference: |
Development and evaluation of consensus-based sediment effect concentrations for polychlorinated biphenyls. Environmental Toxicology and Chemistry. 19(5): 1403-1413 |
|
Spatial Representation: |
Data for this line of evidence for San Antonio Creek (313) was collected at 1 monitoring site [ 313SAI-San Antonio Creek at San Antonio Road West] |
Temporal Representation: |
Data was collected on a single day 3/31/2004. SWAMP toxicity monitoring includes both water samples (collected in both winter and summer) and sediment samples (collected in spring). |
Environmental Conditions: |
Staff is not aware of any special conditions that might effect interpretation of the data. |
QAPP Information: |
All data was collected following the Standard Operating Procedures and Data Quality Objectives outlined in the SWAMP QAMP, (Puckett, 2002). QA data are included in submission. All data are flagged as appropriate. |
QAPP Information Reference(s): |
|
Line of Evidence (LOE) for Decision ID 25450, Chrysene (C1-C4)
|
Region 3 |
San Antonio Creek (San Antonio Watershed, Rancho del las Flores Bridge at Hwy 135 to downstream at Railroad Bridge) |
|
|
LOE ID: |
16016 |
|
Pollutant: |
Chrysene (C1-C4) |
LOE Subgroup: |
Pollutant-Sediment |
Matrix: |
Sediment |
Fraction: |
None |
|
Beneficial Use: |
Warm Freshwater Habitat |
Aquatic Life 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: |
Central Coast Regional Board Staff assessed CCAMP_SWAMP Monitoring (03SW3001) data for San Antonio Creek (313) to determine beneficial use support and results are as follows: 0 of 1 samples exceed the criterion for Chrysene. |
Data Reference: |
Final Data File used for assessment: SWAMP Toxicity Data 2001-06 |
|
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. (Water Quality Control Plan, Central Coast Basin, General Objective Chapter III, Section II.A.2 Objectives for all Inland Surface Waters, Enclosed Bays and Estuaries). |
Objective/Criterion Reference: |
Water Quality Control Plan (Basin Plan) - Central Coast Region (Region 3) |
|
Evaluation Guideline: |
In fresh water sediments the probable effects level (predictive of sediment toxicity) for Chrysene is 1290 ug/Kg dry weight (Macdonald et al. 2000) |
Guideline Reference: |
Development and evaluation of consensus-based sediment effect concentrations for polychlorinated biphenyls. Environmental Toxicology and Chemistry. 19(5): 1403-1413 |
|
Spatial Representation: |
Data for this line of evidence for San Antonio Creek (313) was collected at 1 monitoring site [ 313SAI-San Antonio Creek at San Antonio Road West] |
Temporal Representation: |
Data was collected on a single day 3/31/2004. SWAMP toxicity monitoring includes both water samples (collected in both winter and summer) and sediment samples (collected in spring). |
Environmental Conditions: |
Staff is not aware of any special conditions that might effect interpretation of the data. |
QAPP Information: |
All data was collected following the Standard Operating Procedures and Data Quality Objectives outlined in the SWAMP QAMP, (Puckett, 2002). QA data are included in submission. All data are flagged as appropriate. |
QAPP Information Reference(s): |
|
Line of Evidence (LOE) for Decision ID 25460, Copper
|
Region 3 |
San Antonio Creek (San Antonio Watershed, Rancho del las Flores Bridge at Hwy 135 to downstream at Railroad Bridge) |
|
|
LOE ID: |
16846 |
|
Pollutant: |
Copper |
LOE Subgroup: |
Pollutant-Sediment |
Matrix: |
Sediment |
Fraction: |
None |
|
Beneficial Use: |
Warm Freshwater Habitat |
Aquatic Life 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: |
Central Coast Regional Board Staff assessed CCAMP_SWAMP Monitoring (03SW3001) data for San Antonio Creek (313) to determine beneficial use support and results are as follows: 0 of 1 samples exceed the criterion for Copper. |
Data Reference: |
Final Data File used for assessment: SWAMP Toxicity Data 2001-06 |
|
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. (Water Quality Control Plan, Central Coast Basin, General Objective Chapter III, Section II.A.2 Objectives for all Inland Surface Waters, Enclosed Bays and Estuaries). |
Objective/Criterion Reference: |
Water Quality Control Plan (Basin Plan) - Central Coast Region (Region 3) |
|
Evaluation Guideline: |
In fresh water sediments the probable effects level (predictive of sediment toxicity) for cooper is 149 mg/Kg dry weight (MacDonald et al. 2000). |
Guideline Reference: |
Development and evaluation of consensus-based sediment effect concentrations for polychlorinated biphenyls. Environmental Toxicology and Chemistry. 19(5): 1403-1413 |
|
Spatial Representation: |
Data for this line of evidence for San Antonio Creek (313) was collected at 1 monitoring site [ 313SAI-San Antonio Creek at San Antonio Road West] |
Temporal Representation: |
Data was collected on a single day 3/31/2004. SWAMP toxicity monitoring includes both water samples (collected in both winter and summer) and sediment samples (collected in spring). |
Environmental Conditions: |
Staff is not aware of any special conditions that might effect interpretation of the data. |
QAPP Information: |
All data was collected following the Standard Operating Procedures and Data Quality Objectives outlined in the SWAMP QAMP, (Puckett, 2002). QA data are included in submission. All data are flagged as appropriate. |
QAPP Information Reference(s): |
|
Line of Evidence (LOE) for Decision ID 25460, Copper
|
Region 3 |
San Antonio Creek (San Antonio Watershed, Rancho del las Flores Bridge at Hwy 135 to downstream at Railroad Bridge) |
|
|
LOE ID: |
16812 |
|
Pollutant: |
Copper |
LOE Subgroup: |
Pollutant-Sediment |
Matrix: |
Sediment |
Fraction: |
None |
|
Beneficial Use: |
Cold Freshwater Habitat |
Aquatic Life 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: |
Central Coast Regional Board Staff assessed CCAMP_SWAMP Monitoring (00SW3001) data for San Antonio Creek (313) to determine beneficial use support and results are as follows: 0 of 2 samples exceed the criterion for Copper. |
Data Reference: |
Final Data File used for assessment: SWAMP Toxicity Data 2001-06 |
|
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. (Water Quality Control Plan, Central Coast Basin, General Objective Chapter III, Section II.A.2 Objectives for all Inland Surface Waters, Enclosed Bays and Estuaries). |
Objective/Criterion Reference: |
Water Quality Control Plan (Basin Plan) - Central Coast Region (Region 3) |
|
Evaluation Guideline: |
In fresh water sediments the probable effects level (predictive of sediment toxicity) for cooper is 149 mg/Kg dry weight (MacDonald et al. 2000). |
Guideline Reference: |
Development and evaluation of consensus-based sediment effect concentrations for polychlorinated biphenyls. Environmental Toxicology and Chemistry. 19(5): 1403-1413 |
|
Spatial Representation: |
Data for this line of evidence for San Antonio Creek (313) was collected at 2 monitoring sites [ 313SAC-San Antonio Creek at Rail Road Bridge, u/s lagoon , 313SAI-San Antonio Creek at San Antonio Road West] |
Temporal Representation: |
Data was collected on a single day 3/28/2002. SWAMP toxicity monitoring includes both water samples (collected in both winter and summer) and sediment samples (collected in spring). |
Environmental Conditions: |
Staff is not aware of any special conditions that might effect interpretation of the data. |
QAPP Information: |
All data was collected following the Standard Operating Procedures and Data Quality Objectives outlined in the SWAMP QAMP, (Puckett, 2002). QA data are included in submission. All data are flagged as appropriate. |
QAPP Information Reference(s): |
|
Line of Evidence (LOE) for Decision ID 25460, Copper
|
Region 3 |
San Antonio Creek (San Antonio Watershed, Rancho del las Flores Bridge at Hwy 135 to downstream at Railroad Bridge) |
|
|
LOE ID: |
16845 |
|
Pollutant: |
Copper |
LOE Subgroup: |
Pollutant-Sediment |
Matrix: |
Sediment |
Fraction: |
None |
|
Beneficial Use: |
Cold Freshwater Habitat |
Aquatic Life Use: |
Cold Freshwater Habitat |
|
Number of Samples: |
1 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Central Coast Regional Board Staff assessed CCAMP_SWAMP Monitoring (03SW3001) data for San Antonio Creek (313) to determine beneficial use support and results are as follows: 0 of 1 samples exceed the criterion for Copper. |
Data Reference: |
Final Data File used for assessment: SWAMP Toxicity Data 2001-06 |
|
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. (Water Quality Control Plan, Central Coast Basin, General Objective Chapter III, Section II.A.2 Objectives for all Inland Surface Waters, Enclosed Bays and Estuaries). |
Objective/Criterion Reference: |
Water Quality Control Plan (Basin Plan) - Central Coast Region (Region 3) |
|
Evaluation Guideline: |
In fresh water sediments the probable effects level (predictive of sediment toxicity) for cooper is 149 mg/Kg dry weight (MacDonald et al. 2000). |
Guideline Reference: |
Development and evaluation of consensus-based sediment effect concentrations for polychlorinated biphenyls. Environmental Toxicology and Chemistry. 19(5): 1403-1413 |
|
Spatial Representation: |
Data for this line of evidence for San Antonio Creek (313) was collected at 1 monitoring site [ 313SAI-San Antonio Creek at San Antonio Road West] |
Temporal Representation: |
Data was collected on a single day 3/31/2004. SWAMP toxicity monitoring includes both water samples (collected in both winter and summer) and sediment samples (collected in spring). |
Environmental Conditions: |
Staff is not aware of any special conditions that might effect interpretation of the data. |
QAPP Information: |
All data was collected following the Standard Operating Procedures and Data Quality Objectives outlined in the SWAMP QAMP, (Puckett, 2002). QA data are included in submission. All data are flagged as appropriate. |
QAPP Information Reference(s): |
|
Line of Evidence (LOE) for Decision ID 25460, Copper
|
Region 3 |
San Antonio Creek (San Antonio Watershed, Rancho del las Flores Bridge at Hwy 135 to downstream at Railroad Bridge) |
|
|
LOE ID: |
16813 |
|
Pollutant: |
Copper |
LOE Subgroup: |
Pollutant-Sediment |
Matrix: |
Sediment |
Fraction: |
None |
|
Beneficial Use: |
Warm Freshwater Habitat |
Aquatic Life 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: |
Central Coast Regional Board Staff assessed CCAMP_SWAMP Monitoring (00SW3001) data for San Antonio Creek (313) to determine beneficial use support and results are as follows: 0 of 2 samples exceed the criterion for Copper. |
Data Reference: |
Final Data File used for assessment: SWAMP Toxicity Data 2001-06 |
|
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. (Water Quality Control Plan, Central Coast Basin, General Objective Chapter III, Section II.A.2 Objectives for all Inland Surface Waters, Enclosed Bays and Estuaries). |
Objective/Criterion Reference: |
Water Quality Control Plan (Basin Plan) - Central Coast Region (Region 3) |
|
Evaluation Guideline: |
In fresh water sediments the probable effects level (predictive of sediment toxicity) for cooper is 149 mg/Kg dry weight (MacDonald et al. 2000). |
Guideline Reference: |
Development and evaluation of consensus-based sediment effect concentrations for polychlorinated biphenyls. Environmental Toxicology and Chemistry. 19(5): 1403-1413 |
|
Spatial Representation: |
Data for this line of evidence for San Antonio Creek (313) was collected at 2 monitoring sites [ 313SAC-San Antonio Creek at Rail Road Bridge, u/s lagoon , 313SAI-San Antonio Creek at San Antonio Road West] |
Temporal Representation: |
Data was collected on a single day 3/28/2002. SWAMP toxicity monitoring includes both water samples (collected in both winter and summer) and sediment samples (collected in spring). |
Environmental Conditions: |
Staff is not aware of any special conditions that might effect interpretation of the data. |
QAPP Information: |
All data was collected following the Standard Operating Procedures and Data Quality Objectives outlined in the SWAMP QAMP, (Puckett, 2002). QA data are included in submission. All data are flagged as appropriate. |
QAPP Information Reference(s): |
|
Line of Evidence (LOE) for Decision ID 25219, Diazinon
|
Region 3 |
San Antonio Creek (San Antonio Watershed, Rancho del las Flores Bridge at Hwy 135 to downstream at Railroad Bridge) |
|
|
LOE ID: |
16691 |
|
Pollutant: |
Diazinon |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
None |
|
Beneficial Use: |
Cold Freshwater Habitat |
Aquatic Life Use: |
Cold Freshwater Habitat |
|
Number of Samples: |
1 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Central Coast Regional Board Staff assessed CCAMP_SWAMP Monitoring (03SW3001) data for San Antonio Creek (313) to determine beneficial use support and results are as follows: 0 of 1 samples exceed the criterion for Diazinon. |
Data Reference: |
Final Data File used for assessment: SWAMP Toxicity Data 2001-06 |
|
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. (Water Quality Control Plan, Central Coast Basin, Chapter III, Section II.A.2 Objectives for all Inland Surface Waters, Enclosed Bays and Estuaries). |
Objective/Criterion 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 |
|
Water Quality Control Plan (Basin Plan) - Central Coast Region (Region 3) |
|
Evaluation Guideline: |
One hour average maximum concentration 0.16 ug/L as stated in Sipmann 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 for this line of evidence for San Antonio Creek (313) was collected at 1 monitoring site [ 313SAI-San Antonio Creek at San Antonio Road West] |
Temporal Representation: |
Data was collected on a single day 3/31/2004. SWAMP toxicity monitoring includes both water samples (collected in both winter and summer) and sediment samples (collected in spring). |
Environmental Conditions: |
Staff is not aware of any special conditions that might effect interpretation of the data. |
QAPP Information: |
All data was collected following the Standard Operating Procedures and Data Quality Objectives outlined in the SWAMP QAMP, (Puckett, 2002). QA data are included in submission. All data are flagged as appropriate. |
QAPP Information Reference(s): |
|
Line of Evidence (LOE) for Decision ID 25219, Diazinon
|
Region 3 |
San Antonio Creek (San Antonio Watershed, Rancho del las Flores Bridge at Hwy 135 to downstream at Railroad Bridge) |
|
|
LOE ID: |
16651 |
|
Pollutant: |
Diazinon |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
None |
|
Beneficial Use: |
Warm Freshwater Habitat |
Aquatic Life Use: |
Warm Freshwater Habitat |
|
Number of Samples: |
8 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Central Coast Regional Board Staff assessed CCAMP_SWAMP Monitoring (00SW3001) data for San Antonio Creek (313) to determine beneficial use support and results are as follows: 0 of 8 samples exceed the criterion for Diazinon. |
Data Reference: |
Final Data File used for assessment: SWAMP Toxicity Data 2001-06 |
|
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. (Water Quality Control Plan, Central Coast Basin, Chapter III, Section II.A.2 Objectives for all Inland Surface Waters, Enclosed Bays and Estuaries). |
Objective/Criterion 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 |
|
Water Quality Control Plan (Basin Plan) - Central Coast Region (Region 3) |
|
Evaluation Guideline: |
One hour average maximum concentration 0.16 ug/L as stated in Sipmann 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 for this line of evidence for San Antonio Creek (313) was collected at 3 monitoring sites [ 313SAB-San Antonio Creek at Rancho de las Flores Bridge and Highway 135, 313SAC-San Antonio Creek at Rail Road Bridge, u/s lagoon , 313SAI-San Antonio Creek at San Antonio Road West] |
Temporal Representation: |
Data was collected over the time period 12/10/2001-3/17/2002. SWAMP toxicity monitoring includes both water samples (collected in both winter and summer) and sediment samples (collected in spring). |
Environmental Conditions: |
Staff is not aware of any special conditions that might effect interpretation of the data. |
QAPP Information: |
All data was collected following the Standard Operating Procedures and Data Quality Objectives outlined in the SWAMP QAMP, (Puckett, 2002). QA data are included in submission. All data are flagged as appropriate. |
QAPP Information Reference(s): |
|
Line of Evidence (LOE) for Decision ID 25219, Diazinon
|
Region 3 |
San Antonio Creek (San Antonio Watershed, Rancho del las Flores Bridge at Hwy 135 to downstream at Railroad Bridge) |
|
|
LOE ID: |
16692 |
|
Pollutant: |
Diazinon |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
None |
|
Beneficial Use: |
Warm Freshwater Habitat |
Aquatic Life 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: |
Central Coast Regional Board Staff assessed CCAMP_SWAMP Monitoring (03SW3001) data for San Antonio Creek (313) to determine beneficial use support and results are as follows: 0 of 1 samples exceed the criterion for Diazinon. |
Data Reference: |
Final Data File used for assessment: SWAMP Toxicity Data 2001-06 |
|
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. (Water Quality Control Plan, Central Coast Basin, Chapter III, Section II.A.2 Objectives for all Inland Surface Waters, Enclosed Bays and Estuaries). |
Objective/Criterion 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 |
|
Water Quality Control Plan (Basin Plan) - Central Coast Region (Region 3) |
|
Evaluation Guideline: |
One hour average maximum concentration 0.16 ug/L as stated in Sipmann 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 for this line of evidence for San Antonio Creek (313) was collected at 1 monitoring site [ 313SAI-San Antonio Creek at San Antonio Road West] |
Temporal Representation: |
Data was collected on a single day 3/31/2004. SWAMP toxicity monitoring includes both water samples (collected in both winter and summer) and sediment samples (collected in spring). |
Environmental Conditions: |
Staff is not aware of any special conditions that might effect interpretation of the data. |
QAPP Information: |
All data was collected following the Standard Operating Procedures and Data Quality Objectives outlined in the SWAMP QAMP, (Puckett, 2002). QA data are included in submission. All data are flagged as appropriate. |
QAPP Information Reference(s): |
|
Line of Evidence (LOE) for Decision ID 25219, Diazinon
|
Region 3 |
San Antonio Creek (San Antonio Watershed, Rancho del las Flores Bridge at Hwy 135 to downstream at Railroad Bridge) |
|
|
LOE ID: |
16650 |
|
Pollutant: |
Diazinon |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
None |
|
Beneficial Use: |
Cold Freshwater Habitat |
Aquatic Life Use: |
Cold Freshwater Habitat |
|
Number of Samples: |
8 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Central Coast Regional Board Staff assessed CCAMP_SWAMP Monitoring (00SW3001) data for San Antonio Creek (313) to determine beneficial use support and results are as follows: 0 of 8 samples exceed the criterion for Diazinon. |
Data Reference: |
Final Data File used for assessment: SWAMP Toxicity Data 2001-06 |
|
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. (Water Quality Control Plan, Central Coast Basin, Chapter III, Section II.A.2 Objectives for all Inland Surface Waters, Enclosed Bays and Estuaries). |
Objective/Criterion 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 |
|
Water Quality Control Plan (Basin Plan) - Central Coast Region (Region 3) |
|
Evaluation Guideline: |
One hour average maximum concentration 0.16 ug/L as stated in Sipmann 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 for this line of evidence for San Antonio Creek (313) was collected at 3 monitoring sites [ 313SAB-San Antonio Creek at Rancho de las Flores Bridge and Highway 135, 313SAC-San Antonio Creek at Rail Road Bridge, u/s lagoon , 313SAI-San Antonio Creek at San Antonio Road West] |
Temporal Representation: |
Data was collected over the time period 12/10/2001-3/17/2002. SWAMP toxicity monitoring includes both water samples (collected in both winter and summer) and sediment samples (collected in spring). |
Environmental Conditions: |
Staff is not aware of any special conditions that might effect interpretation of the data. |
QAPP Information: |
All data was collected following the Standard Operating Procedures and Data Quality Objectives outlined in the SWAMP QAMP, (Puckett, 2002). QA data are included in submission. All data are flagged as appropriate. |
QAPP Information Reference(s): |
|
Line of Evidence (LOE) for Decision ID 25461, Dieldrin
|
Region 3 |
San Antonio Creek (San Antonio Watershed, Rancho del las Flores Bridge at Hwy 135 to downstream at Railroad Bridge) |
|
|
LOE ID: |
16512 |
|
Pollutant: |
Dieldrin |
LOE Subgroup: |
Pollutant-Sediment |
Matrix: |
Sediment |
Fraction: |
None |
|
Beneficial Use: |
Warm Freshwater Habitat |
Aquatic Life 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: |
Central Coast Regional Board Staff assessed CCAMP_SWAMP Monitoring (00SW3001) data for San Antonio Creek (313) to determine beneficial use support and results are as follows: 0 of 2 samples exceed the criterion for Dieldrin. |
Data Reference: |
Final Data File used for assessment: SWAMP Toxicity Data 2001-06 |
|
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. (Water Quality Control Plan, Central Coast Basin, General Objective Chapter III, Section II.A.2 Objectives for all Inland Surface Waters, Enclosed Bays and Estuaries). |
Objective/Criterion Reference: |
Water Quality Control Plan (Basin Plan) - Central Coast Region (Region 3) |
|
Evaluation Guideline: |
In fresh water sediments the probable effects level (predictive of sediment toxicity) for dieldrin is 61.8 ug/Kg dry weight (MacDonald et al. 2000). |
Guideline Reference: |
Development and evaluation of consensus-based sediment effect concentrations for polychlorinated biphenyls. Environmental Toxicology and Chemistry. 19(5): 1403-1413 |
|
Spatial Representation: |
Data for this line of evidence for San Antonio Creek (313) was collected at 2 monitoring sites [ 313SAC-San Antonio Creek at Rail Road Bridge, u/s lagoon , 313SAI-San Antonio Creek at San Antonio Road West] |
Temporal Representation: |
Data was collected on a single day 3/28/2002. SWAMP toxicity monitoring includes both water samples (collected in both winter and summer) and sediment samples (collected in spring). |
Environmental Conditions: |
Staff is not aware of any special conditions that might effect interpretation of the data. |
QAPP Information: |
All data was collected following the Standard Operating Procedures and Data Quality Objectives outlined in the SWAMP QAMP, (Puckett, 2002). QA data are included in submission. All data are flagged as appropriate. |
QAPP Information Reference(s): |
|
Line of Evidence (LOE) for Decision ID 25461, Dieldrin
|
Region 3 |
San Antonio Creek (San Antonio Watershed, Rancho del las Flores Bridge at Hwy 135 to downstream at Railroad Bridge) |
|
|
LOE ID: |
16541 |
|
Pollutant: |
Dieldrin |
LOE Subgroup: |
Pollutant-Sediment |
Matrix: |
Sediment |
Fraction: |
None |
|
Beneficial Use: |
Cold Freshwater Habitat |
Aquatic Life Use: |
Cold Freshwater Habitat |
|
Number of Samples: |
1 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Central Coast Regional Board Staff assessed CCAMP_SWAMP Monitoring (03SW3001) data for San Antonio Creek (313) to determine beneficial use support and results are as follows: 0 of 1 samples exceed the criterion for Dieldrin. |
Data Reference: |
Final Data File used for assessment: SWAMP Toxicity Data 2001-06 |
|
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. (Water Quality Control Plan, Central Coast Basin, General Objective Chapter III, Section II.A.2 Objectives for all Inland Surface Waters, Enclosed Bays and Estuaries). |
Objective/Criterion Reference: |
Water Quality Control Plan (Basin Plan) - Central Coast Region (Region 3) |
|
Evaluation Guideline: |
In fresh water sediments the probable effects level (predictive of sediment toxicity) for dieldrin is 61.8 ug/Kg dry weight (MacDonald et al. 2000). |
Guideline Reference: |
Development and evaluation of consensus-based sediment effect concentrations for polychlorinated biphenyls. Environmental Toxicology and Chemistry. 19(5): 1403-1413 |
|
Spatial Representation: |
Data for this line of evidence for San Antonio Creek (313) was collected at 1 monitoring site [ 313SAI-San Antonio Creek at San Antonio Road West] |
Temporal Representation: |
Data was collected on a single day 3/31/2004. SWAMP toxicity monitoring includes both water samples (collected in both winter and summer) and sediment samples (collected in spring). |
Environmental Conditions: |
Staff is not aware of any special conditions that might effect interpretation of the data. |
QAPP Information: |
All data was collected following the Standard Operating Procedures and Data Quality Objectives outlined in the SWAMP QAMP, (Puckett, 2002). QA data are included in submission. All data are flagged as appropriate. |
QAPP Information Reference(s): |
|
Line of Evidence (LOE) for Decision ID 25461, Dieldrin
|
Region 3 |
San Antonio Creek (San Antonio Watershed, Rancho del las Flores Bridge at Hwy 135 to downstream at Railroad Bridge) |
|
|
LOE ID: |
16511 |
|
Pollutant: |
Dieldrin |
LOE Subgroup: |
Pollutant-Sediment |
Matrix: |
Sediment |
Fraction: |
None |
|
Beneficial Use: |
Cold Freshwater Habitat |
Aquatic Life 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: |
Central Coast Regional Board Staff assessed CCAMP_SWAMP Monitoring (00SW3001) data for San Antonio Creek (313) to determine beneficial use support and results are as follows: 0 of 2 samples exceed the criterion for Dieldrin. |
Data Reference: |
Final Data File used for assessment: SWAMP Toxicity Data 2001-06 |
|
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. (Water Quality Control Plan, Central Coast Basin, General Objective Chapter III, Section II.A.2 Objectives for all Inland Surface Waters, Enclosed Bays and Estuaries). |
Objective/Criterion Reference: |
Water Quality Control Plan (Basin Plan) - Central Coast Region (Region 3) |
|
Evaluation Guideline: |
In fresh water sediments the probable effects level (predictive of sediment toxicity) for dieldrin is 61.8 ug/Kg dry weight (MacDonald et al. 2000). |
Guideline Reference: |
Development and evaluation of consensus-based sediment effect concentrations for polychlorinated biphenyls. Environmental Toxicology and Chemistry. 19(5): 1403-1413 |
|
Spatial Representation: |
Data for this line of evidence for San Antonio Creek (313) was collected at 2 monitoring sites [ 313SAC-San Antonio Creek at Rail Road Bridge, u/s lagoon , 313SAI-San Antonio Creek at San Antonio Road West] |
Temporal Representation: |
Data was collected on a single day 3/28/2002. SWAMP toxicity monitoring includes both water samples (collected in both winter and summer) and sediment samples (collected in spring). |
Environmental Conditions: |
Staff is not aware of any special conditions that might effect interpretation of the data. |
QAPP Information: |
All data was collected following the Standard Operating Procedures and Data Quality Objectives outlined in the SWAMP QAMP, (Puckett, 2002). QA data are included in submission. All data are flagged as appropriate. |
QAPP Information Reference(s): |
|
Line of Evidence (LOE) for Decision ID 25461, Dieldrin
|
Region 3 |
San Antonio Creek (San Antonio Watershed, Rancho del las Flores Bridge at Hwy 135 to downstream at Railroad Bridge) |
|
|
LOE ID: |
16542 |
|
Pollutant: |
Dieldrin |
LOE Subgroup: |
Pollutant-Sediment |
Matrix: |
Sediment |
Fraction: |
None |
|
Beneficial Use: |
Warm Freshwater Habitat |
Aquatic Life 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: |
Central Coast Regional Board Staff assessed CCAMP_SWAMP Monitoring (03SW3001) data for San Antonio Creek (313) to determine beneficial use support and results are as follows: 0 of 1 samples exceed the criterion for Dieldrin. |
Data Reference: |
Final Data File used for assessment: SWAMP Toxicity Data 2001-06 |
|
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. (Water Quality Control Plan, Central Coast Basin, General Objective Chapter III, Section II.A.2 Objectives for all Inland Surface Waters, Enclosed Bays and Estuaries). |
Objective/Criterion Reference: |
Water Quality Control Plan (Basin Plan) - Central Coast Region (Region 3) |
|
Evaluation Guideline: |
In fresh water sediments the probable effects level (predictive of sediment toxicity) for dieldrin is 61.8 ug/Kg dry weight (MacDonald et al. 2000). |
Guideline Reference: |
Development and evaluation of consensus-based sediment effect concentrations for polychlorinated biphenyls. Environmental Toxicology and Chemistry. 19(5): 1403-1413 |
|
Spatial Representation: |
Data for this line of evidence for San Antonio Creek (313) was collected at 1 monitoring site [ 313SAI-San Antonio Creek at San Antonio Road West] |
Temporal Representation: |
Data was collected on a single day 3/31/2004. SWAMP toxicity monitoring includes both water samples (collected in both winter and summer) and sediment samples (collected in spring). |
Environmental Conditions: |
Staff is not aware of any special conditions that might effect interpretation of the data. |
QAPP Information: |
All data was collected following the Standard Operating Procedures and Data Quality Objectives outlined in the SWAMP QAMP, (Puckett, 2002). QA data are included in submission. All data are flagged as appropriate. |
QAPP Information Reference(s): |
|
Line of Evidence (LOE) for Decision ID 25515, Endrin
|
Region 3 |
San Antonio Creek (San Antonio Watershed, Rancho del las Flores Bridge at Hwy 135 to downstream at Railroad Bridge) |
|
|
LOE ID: |
16389 |
|
Pollutant: |
Endrin |
LOE Subgroup: |
Pollutant-Sediment |
Matrix: |
Sediment |
Fraction: |
None |
|
Beneficial Use: |
Warm Freshwater Habitat |
Aquatic Life 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: |
Central Coast Regional Board Staff assessed CCAMP_SWAMP Monitoring (03SW3001) data for San Antonio Creek (313) to determine beneficial use support and results are as follows: 0 of 1 samples exceed the criterion for Endrin. |
Data Reference: |
Final Data File used for assessment: SWAMP Toxicity Data 2001-06 |
|
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. (Water Quality Control Plan, Central Coast Basin, General Objective Chapter III, Section II.A.2 Objectives for all Inland Surface Waters, Enclosed Bays and Estuaries). |
Objective/Criterion Reference: |
Water Quality Control Plan (Basin Plan) - Central Coast Region (Region 3) |
|
Evaluation Guideline: |
In fresh water sediments the probable effects level (predictive of sediment toxicity) for endrin is 207 ug/Kg dry weight (MacDonald et al. 2000). |
Guideline Reference: |
Development and evaluation of consensus-based sediment effect concentrations for polychlorinated biphenyls. Environmental Toxicology and Chemistry. 19(5): 1403-1413 |
|
Spatial Representation: |
Data for this line of evidence for San Antonio Creek (313) was collected at 1 monitoring site [ 313SAI-San Antonio Creek at San Antonio Road West] |
Temporal Representation: |
Data was collected on a single day 3/31/2004. SWAMP toxicity monitoring includes both water samples (collected in both winter and summer) and sediment samples (collected in spring). |
Environmental Conditions: |
Staff is not aware of any special conditions that might effect interpretation of the data. |
QAPP Information: |
All data was collected following the Standard Operating Procedures and Data Quality Objectives outlined in the SWAMP QAMP, (Puckett, 2002). QA data are included in submission. All data are flagged as appropriate. |
QAPP Information Reference(s): |
|
Line of Evidence (LOE) for Decision ID 25515, Endrin
|
Region 3 |
San Antonio Creek (San Antonio Watershed, Rancho del las Flores Bridge at Hwy 135 to downstream at Railroad Bridge) |
|
|
LOE ID: |
16594 |
|
Pollutant: |
Endrin |
LOE Subgroup: |
Pollutant-Sediment |
Matrix: |
Sediment |
Fraction: |
None |
|
Beneficial Use: |
Cold Freshwater Habitat |
Aquatic Life 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: |
Central Coast Regional Board Staff assessed CCAMP_SWAMP Monitoring (00SW3001) data for San Antonio Creek (313) to determine beneficial use support and results are as follows: 0 of 2 samples exceed the criterion for Endrin. |
Data Reference: |
Final Data File used for assessment: SWAMP Toxicity Data 2001-06 |
|
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. (Water Quality Control Plan, Central Coast Basin, General Objective Chapter III, Section II.A.2 Objectives for all Inland Surface Waters, Enclosed Bays and Estuaries). |
Objective/Criterion Reference: |
Water Quality Control Plan (Basin Plan) - Central Coast Region (Region 3) |
|
Evaluation Guideline: |
In fresh water sediments the probable effects level (predictive of sediment toxicity) for endrin is 207 ug/Kg dry weight (MacDonald et al. 2000). |
Guideline Reference: |
Development and evaluation of consensus-based sediment effect concentrations for polychlorinated biphenyls. Environmental Toxicology and Chemistry. 19(5): 1403-1413 |
|
Spatial Representation: |
Data for this line of evidence for San Antonio Creek (313) was collected at 2 monitoring sites [ 313SAC-San Antonio Creek at Rail Road Bridge, u/s lagoon , 313SAI-San Antonio Creek at San Antonio Road West] |
Temporal Representation: |
Data was collected on a single day 3/28/2002. SWAMP toxicity monitoring includes both water samples (collected in both winter and summer) and sediment samples (collected in spring). |
Environmental Conditions: |
Staff is not aware of any special conditions that might effect interpretation of the data. |
QAPP Information: |
All data was collected following the Standard Operating Procedures and Data Quality Objectives outlined in the SWAMP QAMP, (Puckett, 2002). QA data are included in submission. All data are flagged as appropriate. |
QAPP Information Reference(s): |
|
Line of Evidence (LOE) for Decision ID 25515, Endrin
|
Region 3 |
San Antonio Creek (San Antonio Watershed, Rancho del las Flores Bridge at Hwy 135 to downstream at Railroad Bridge) |
|
|
LOE ID: |
16376 |
|
Pollutant: |
Endrin |
LOE Subgroup: |
Pollutant-Sediment |
Matrix: |
Sediment |
Fraction: |
None |
|
Beneficial Use: |
Cold Freshwater Habitat |
Aquatic Life Use: |
Cold Freshwater Habitat |
|
Number of Samples: |
1 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Central Coast Regional Board Staff assessed CCAMP_SWAMP Monitoring (03SW3001) data for San Antonio Creek (313) to determine beneficial use support and results are as follows: 0 of 1 samples exceed the criterion for Endrin. |
Data Reference: |
Final Data File used for assessment: SWAMP Toxicity Data 2001-06 |
|
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. (Water Quality Control Plan, Central Coast Basin, General Objective Chapter III, Section II.A.2 Objectives for all Inland Surface Waters, Enclosed Bays and Estuaries). |
Objective/Criterion Reference: |
Water Quality Control Plan (Basin Plan) - Central Coast Region (Region 3) |
|
Evaluation Guideline: |
In fresh water sediments the probable effects level (predictive of sediment toxicity) for endrin is 207 ug/Kg dry weight (MacDonald et al. 2000). |
Guideline Reference: |
Development and evaluation of consensus-based sediment effect concentrations for polychlorinated biphenyls. Environmental Toxicology and Chemistry. 19(5): 1403-1413 |
|
Spatial Representation: |
Data for this line of evidence for San Antonio Creek (313) was collected at 1 monitoring site [ 313SAI-San Antonio Creek at San Antonio Road West] |
Temporal Representation: |
Data was collected on a single day 3/31/2004. SWAMP toxicity monitoring includes both water samples (collected in both winter and summer) and sediment samples (collected in spring). |
Environmental Conditions: |
Staff is not aware of any special conditions that might effect interpretation of the data. |
QAPP Information: |
All data was collected following the Standard Operating Procedures and Data Quality Objectives outlined in the SWAMP QAMP, (Puckett, 2002). QA data are included in submission. All data are flagged as appropriate. |
QAPP Information Reference(s): |
|
Line of Evidence (LOE) for Decision ID 25515, Endrin
|
Region 3 |
San Antonio Creek (San Antonio Watershed, Rancho del las Flores Bridge at Hwy 135 to downstream at Railroad Bridge) |
|
|
LOE ID: |
16595 |
|
Pollutant: |
Endrin |
LOE Subgroup: |
Pollutant-Sediment |
Matrix: |
Sediment |
Fraction: |
None |
|
Beneficial Use: |
Warm Freshwater Habitat |
Aquatic Life 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: |
Central Coast Regional Board Staff assessed CCAMP_SWAMP Monitoring (00SW3001) data for San Antonio Creek (313) to determine beneficial use support and results are as follows: 0 of 2 samples exceed the criterion for Endrin. |
Data Reference: |
Final Data File used for assessment: SWAMP Toxicity Data 2001-06 |
|
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. (Water Quality Control Plan, Central Coast Basin, General Objective Chapter III, Section II.A.2 Objectives for all Inland Surface Waters, Enclosed Bays and Estuaries). |
Objective/Criterion Reference: |
Water Quality Control Plan (Basin Plan) - Central Coast Region (Region 3) |
|
Evaluation Guideline: |
In fresh water sediments the probable effects level (predictive of sediment toxicity) for endrin is 207 ug/Kg dry weight (MacDonald et al. 2000). |
Guideline Reference: |
Development and evaluation of consensus-based sediment effect concentrations for polychlorinated biphenyls. Environmental Toxicology and Chemistry. 19(5): 1403-1413 |
|
Spatial Representation: |
Data for this line of evidence for San Antonio Creek (313) was collected at 2 monitoring sites [ 313SAC-San Antonio Creek at Rail Road Bridge, u/s lagoon , 313SAI-San Antonio Creek at San Antonio Road West] |
Temporal Representation: |
Data was collected on a single day 3/28/2002. SWAMP toxicity monitoring includes both water samples (collected in both winter and summer) and sediment samples (collected in spring). |
Environmental Conditions: |
Staff is not aware of any special conditions that might effect interpretation of the data. |
QAPP Information: |
All data was collected following the Standard Operating Procedures and Data Quality Objectives outlined in the SWAMP QAMP, (Puckett, 2002). QA data are included in submission. All data are flagged as appropriate. |
QAPP Information Reference(s): |
|
Line of Evidence (LOE) for Decision ID 25527, Fluoranthene
|
Region 3 |
San Antonio Creek (San Antonio Watershed, Rancho del las Flores Bridge at Hwy 135 to downstream at Railroad Bridge) |
|
|
LOE ID: |
16427 |
|
Pollutant: |
Fluoranthene |
LOE Subgroup: |
Pollutant-Sediment |
Matrix: |
Sediment |
Fraction: |
None |
|
Beneficial Use: |
Cold Freshwater Habitat |
Aquatic Life 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: |
Central Coast Regional Board Staff assessed CCAMP_SWAMP Monitoring (00SW3001) data for San Antonio Creek (313) to determine beneficial use support and results are as follows: 0 of 2 samples exceed the criterion for Fluoranthene. |
Data Reference: |
Final Data File used for assessment: SWAMP Toxicity Data 2001-06 |
|
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. (Water Quality Control Plan, Central Coast Basin, General Objective Chapter III, Section II.A.2 Objectives for all Inland Surface Waters, Enclosed Bays and Estuaries). |
Objective/Criterion Reference: |
Water Quality Control Plan (Basin Plan) - Central Coast Region (Region 3) |
|
Evaluation Guideline: |
In fresh water sediments the probable effects level (predictive of sediment toxicity) for Fluoranthene is 2,230 ug/Kg dry weight (Macdonald et al. 2000) |
Guideline Reference: |
Development and evaluation of consensus-based sediment effect concentrations for polychlorinated biphenyls. Environmental Toxicology and Chemistry. 19(5): 1403-1413 |
|
Spatial Representation: |
Data for this line of evidence for San Antonio Creek (313) was collected at 2 monitoring sites [ 313SAC-San Antonio Creek at Rail Road Bridge, u/s lagoon , 313SAI-San Antonio Creek at San Antonio Road West] |
Temporal Representation: |
Data was collected on a single day 3/28/2002. SWAMP toxicity monitoring includes both water samples (collected in both winter and summer) and sediment samples (collected in spring). |
Environmental Conditions: |
Staff is not aware of any special conditions that might effect interpretation of the data. |
QAPP Information: |
All data was collected following the Standard Operating Procedures and Data Quality Objectives outlined in the SWAMP QAMP, (Puckett, 2002). QA data are included in submission. All data are flagged as appropriate. |
QAPP Information Reference(s): |
|
Line of Evidence (LOE) for Decision ID 25527, Fluoranthene
|
Region 3 |
San Antonio Creek (San Antonio Watershed, Rancho del las Flores Bridge at Hwy 135 to downstream at Railroad Bridge) |
|
|
LOE ID: |
16428 |
|
Pollutant: |
Fluoranthene |
LOE Subgroup: |
Pollutant-Sediment |
Matrix: |
Sediment |
Fraction: |
None |
|
Beneficial Use: |
Warm Freshwater Habitat |
Aquatic Life 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: |
Central Coast Regional Board Staff assessed CCAMP_SWAMP Monitoring (00SW3001) data for San Antonio Creek (313) to determine beneficial use support and results are as follows: 0 of 2 samples exceed the criterion for Fluoranthene. |
Data Reference: |
Final Data File used for assessment: SWAMP Toxicity Data 2001-06 |
|
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. (Water Quality Control Plan, Central Coast Basin, General Objective Chapter III, Section II.A.2 Objectives for all Inland Surface Waters, Enclosed Bays and Estuaries). |
Objective/Criterion Reference: |
Water Quality Control Plan (Basin Plan) - Central Coast Region (Region 3) |
|
Evaluation Guideline: |
In fresh water sediments the probable effects level (predictive of sediment toxicity) for Fluoranthene is 2,230 ug/Kg dry weight (Macdonald et al. 2000) |
Guideline Reference: |
Development and evaluation of consensus-based sediment effect concentrations for polychlorinated biphenyls. Environmental Toxicology and Chemistry. 19(5): 1403-1413 |
|
Spatial Representation: |
Data for this line of evidence for San Antonio Creek (313) was collected at 2 monitoring sites [ 313SAC-San Antonio Creek at Rail Road Bridge, u/s lagoon , 313SAI-San Antonio Creek at San Antonio Road West] |
Temporal Representation: |
Data was collected on a single day 3/28/2002. SWAMP toxicity monitoring includes both water samples (collected in both winter and summer) and sediment samples (collected in spring). |
Environmental Conditions: |
Staff is not aware of any special conditions that might effect interpretation of the data. |
QAPP Information: |
All data was collected following the Standard Operating Procedures and Data Quality Objectives outlined in the SWAMP QAMP, (Puckett, 2002). QA data are included in submission. All data are flagged as appropriate. |
QAPP Information Reference(s): |
|
Line of Evidence (LOE) for Decision ID 25527, Fluoranthene
|
Region 3 |
San Antonio Creek (San Antonio Watershed, Rancho del las Flores Bridge at Hwy 135 to downstream at Railroad Bridge) |
|
|
LOE ID: |
16458 |
|
Pollutant: |
Fluoranthene |
LOE Subgroup: |
Pollutant-Sediment |
Matrix: |
Sediment |
Fraction: |
None |
|
Beneficial Use: |
Warm Freshwater Habitat |
Aquatic Life 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: |
Central Coast Regional Board Staff assessed CCAMP_SWAMP Monitoring (03SW3001) data for San Antonio Creek (313) to determine beneficial use support and results are as follows: 0 of 1 samples exceed the criterion for Fluoranthene. |
Data Reference: |
Final Data File used for assessment: SWAMP Toxicity Data 2001-06 |
|
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. (Water Quality Control Plan, Central Coast Basin, General Objective Chapter III, Section II.A.2 Objectives for all Inland Surface Waters, Enclosed Bays and Estuaries). |
Objective/Criterion Reference: |
Water Quality Control Plan (Basin Plan) - Central Coast Region (Region 3) |
|
Evaluation Guideline: |
In fresh water sediments the probable effects level (predictive of sediment toxicity) for Fluoranthene is 2,230 ug/Kg dry weight (Macdonald et al. 2000) |
Guideline Reference: |
Development and evaluation of consensus-based sediment effect concentrations for polychlorinated biphenyls. Environmental Toxicology and Chemistry. 19(5): 1403-1413 |
|
Spatial Representation: |
Data for this line of evidence for San Antonio Creek (313) was collected at 1 monitoring site [ 313SAI-San Antonio Creek at San Antonio Road West] |
Temporal Representation: |
Data was collected on a single day 3/31/2004. SWAMP toxicity monitoring includes both water samples (collected in both winter and summer) and sediment samples (collected in spring). |
Environmental Conditions: |
Staff is not aware of any special conditions that might effect interpretation of the data. |
QAPP Information: |
All data was collected following the Standard Operating Procedures and Data Quality Objectives outlined in the SWAMP QAMP, (Puckett, 2002). QA data are included in submission. All data are flagged as appropriate. |
QAPP Information Reference(s): |
|
Line of Evidence (LOE) for Decision ID 25527, Fluoranthene
|
Region 3 |
San Antonio Creek (San Antonio Watershed, Rancho del las Flores Bridge at Hwy 135 to downstream at Railroad Bridge) |
|
|
LOE ID: |
16457 |
|
Pollutant: |
Fluoranthene |
LOE Subgroup: |
Pollutant-Sediment |
Matrix: |
Sediment |
Fraction: |
None |
|
Beneficial Use: |
Cold Freshwater Habitat |
Aquatic Life Use: |
Cold Freshwater Habitat |
|
Number of Samples: |
1 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Central Coast Regional Board Staff assessed CCAMP_SWAMP Monitoring (03SW3001) data for San Antonio Creek (313) to determine beneficial use support and results are as follows: 0 of 1 samples exceed the criterion for Fluoranthene. |
Data Reference: |
Final Data File used for assessment: SWAMP Toxicity Data 2001-06 |
|
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. (Water Quality Control Plan, Central Coast Basin, General Objective Chapter III, Section II.A.2 Objectives for all Inland Surface Waters, Enclosed Bays and Estuaries). |
Objective/Criterion Reference: |
Water Quality Control Plan (Basin Plan) - Central Coast Region (Region 3) |
|
Evaluation Guideline: |
In fresh water sediments the probable effects level (predictive of sediment toxicity) for Fluoranthene is 2,230 ug/Kg dry weight (Macdonald et al. 2000) |
Guideline Reference: |
Development and evaluation of consensus-based sediment effect concentrations for polychlorinated biphenyls. Environmental Toxicology and Chemistry. 19(5): 1403-1413 |
|
Spatial Representation: |
Data for this line of evidence for San Antonio Creek (313) was collected at 1 monitoring site [ 313SAI-San Antonio Creek at San Antonio Road West] |
Temporal Representation: |
Data was collected on a single day 3/31/2004. SWAMP toxicity monitoring includes both water samples (collected in both winter and summer) and sediment samples (collected in spring). |
Environmental Conditions: |
Staff is not aware of any special conditions that might effect interpretation of the data. |
QAPP Information: |
All data was collected following the Standard Operating Procedures and Data Quality Objectives outlined in the SWAMP QAMP, (Puckett, 2002). QA data are included in submission. All data are flagged as appropriate. |
QAPP Information Reference(s): |
|
Line of Evidence (LOE) for Decision ID 25528, Fluorene
|
Region 3 |
San Antonio Creek (San Antonio Watershed, Rancho del las Flores Bridge at Hwy 135 to downstream at Railroad Bridge) |
|
|
LOE ID: |
17308 |
|
Pollutant: |
Fluorene |
LOE Subgroup: |
Pollutant-Sediment |
Matrix: |
Sediment |
Fraction: |
None |
|
Beneficial Use: |
Cold Freshwater Habitat |
Aquatic Life 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: |
Central Coast Regional Board Staff assessed CCAMP_SWAMP Monitoring (00SW3001) data for San Antonio Creek (313) to determine beneficial use support and results are as follows: 0 of 2 samples exceed the criterion for Fluorene. |
Data Reference: |
Final Data File used for assessment: SWAMP Toxicity Data 2001-06 |
|
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. (Water Quality Control Plan, Central Coast Basin, General Objective Chapter III, Section II.A.2 Objectives for all Inland Surface Waters, Enclosed Bays and Estuaries). |
Objective/Criterion Reference: |
Water Quality Control Plan (Basin Plan) - Central Coast Region (Region 3) |
|
Evaluation Guideline: |
In fresh water sediments the probable effects level (predictive of sediment toxicity) for fluorene is 536 ug/Kg dry weight (MacDonald et al. 2000). |
Guideline Reference: |
Development and evaluation of consensus-based sediment effect concentrations for polychlorinated biphenyls. Environmental Toxicology and Chemistry. 19(5): 1403-1413 |
|
Spatial Representation: |
Data for this line of evidence for San Antonio Creek (313) was collected at 2 monitoring sites [ 313SAC-San Antonio Creek at Rail Road Bridge, u/s lagoon , 313SAI-San Antonio Creek at San Antonio Road West] |
Temporal Representation: |
Data was collected on a single day 3/28/2002. SWAMP toxicity monitoring includes both water samples (collected in both winter and summer) and sediment samples (collected in spring). |
Environmental Conditions: |
Staff is not aware of any special conditions that might effect interpretation of the data. |
QAPP Information: |
All data was collected following the Standard Operating Procedures and Data Quality Objectives outlined in the SWAMP QAMP, (Puckett, 2002). QA data are included in submission. All data are flagged as appropriate. |
QAPP Information Reference(s): |
|
Line of Evidence (LOE) for Decision ID 25528, Fluorene
|
Region 3 |
San Antonio Creek (San Antonio Watershed, Rancho del las Flores Bridge at Hwy 135 to downstream at Railroad Bridge) |
|
|
LOE ID: |
17309 |
|
Pollutant: |
Fluorene |
LOE Subgroup: |
Pollutant-Sediment |
Matrix: |
Sediment |
Fraction: |
None |
|
Beneficial Use: |
Warm Freshwater Habitat |
Aquatic Life 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: |
Central Coast Regional Board Staff assessed CCAMP_SWAMP Monitoring (00SW3001) data for San Antonio Creek (313) to determine beneficial use support and results are as follows: 0 of 2 samples exceed the criterion for Fluorene. |
Data Reference: |
Final Data File used for assessment: SWAMP Toxicity Data 2001-06 |
|
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. (Water Quality Control Plan, Central Coast Basin, General Objective Chapter III, Section II.A.2 Objectives for all Inland Surface Waters, Enclosed Bays and Estuaries). |
Objective/Criterion Reference: |
Water Quality Control Plan (Basin Plan) - Central Coast Region (Region 3) |
|
Evaluation Guideline: |
In fresh water sediments the probable effects level (predictive of sediment toxicity) for fluorene is 536 ug/Kg dry weight (MacDonald et al. 2000). |
Guideline Reference: |
Development and evaluation of consensus-based sediment effect concentrations for polychlorinated biphenyls. Environmental Toxicology and Chemistry. 19(5): 1403-1413 |
|
Spatial Representation: |
Data for this line of evidence for San Antonio Creek (313) was collected at 2 monitoring sites [ 313SAC-San Antonio Creek at Rail Road Bridge, u/s lagoon , 313SAI-San Antonio Creek at San Antonio Road West] |
Temporal Representation: |
Data was collected on a single day 3/28/2002. SWAMP toxicity monitoring includes both water samples (collected in both winter and summer) and sediment samples (collected in spring). |
Environmental Conditions: |
Staff is not aware of any special conditions that might effect interpretation of the data. |
QAPP Information: |
All data was collected following the Standard Operating Procedures and Data Quality Objectives outlined in the SWAMP QAMP, (Puckett, 2002). QA data are included in submission. All data are flagged as appropriate. |
QAPP Information Reference(s): |
|
Line of Evidence (LOE) for Decision ID 25528, Fluorene
|
Region 3 |
San Antonio Creek (San Antonio Watershed, Rancho del las Flores Bridge at Hwy 135 to downstream at Railroad Bridge) |
|
|
LOE ID: |
17338 |
|
Pollutant: |
Fluorene |
LOE Subgroup: |
Pollutant-Sediment |
Matrix: |
Sediment |
Fraction: |
None |
|
Beneficial Use: |
Cold Freshwater Habitat |
Aquatic Life Use: |
Cold Freshwater Habitat |
|
Number of Samples: |
1 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Central Coast Regional Board Staff assessed CCAMP_SWAMP Monitoring (03SW3001) data for San Antonio Creek (313) to determine beneficial use support and results are as follows: 0 of 1 samples exceed the criterion for Fluorene. |
Data Reference: |
Final Data File used for assessment: SWAMP Toxicity Data 2001-06 |
|
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. (Water Quality Control Plan, Central Coast Basin, General Objective Chapter III, Section II.A.2 Objectives for all Inland Surface Waters, Enclosed Bays and Estuaries). |
Objective/Criterion Reference: |
Water Quality Control Plan (Basin Plan) - Central Coast Region (Region 3) |
|
Evaluation Guideline: |
In fresh water sediments the probable effects level (predictive of sediment toxicity) for fluorene is 536 ug/Kg dry weight (MacDonald et al. 2000). |
Guideline Reference: |
Development and evaluation of consensus-based sediment effect concentrations for polychlorinated biphenyls. Environmental Toxicology and Chemistry. 19(5): 1403-1413 |
|
Spatial Representation: |
Data for this line of evidence for San Antonio Creek (313) was collected at 1 monitoring site [ 313SAI-San Antonio Creek at San Antonio Road West] |
Temporal Representation: |
Data was collected on a single day 3/31/2004. SWAMP toxicity monitoring includes both water samples (collected in both winter and summer) and sediment samples (collected in spring). |
Environmental Conditions: |
Staff is not aware of any special conditions that might effect interpretation of the data. |
QAPP Information: |
All data was collected following the Standard Operating Procedures and Data Quality Objectives outlined in the SWAMP QAMP, (Puckett, 2002). QA data are included in submission. All data are flagged as appropriate. |
QAPP Information Reference(s): |
|
Line of Evidence (LOE) for Decision ID 25528, Fluorene
|
Region 3 |
San Antonio Creek (San Antonio Watershed, Rancho del las Flores Bridge at Hwy 135 to downstream at Railroad Bridge) |
|
|
LOE ID: |
17339 |
|
Pollutant: |
Fluorene |
LOE Subgroup: |
Pollutant-Sediment |
Matrix: |
Sediment |
Fraction: |
None |
|
Beneficial Use: |
Warm Freshwater Habitat |
Aquatic Life 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: |
Central Coast Regional Board Staff assessed CCAMP_SWAMP Monitoring (03SW3001) data for San Antonio Creek (313) to determine beneficial use support and results are as follows: 0 of 1 samples exceed the criterion for Fluorene. |
Data Reference: |
Final Data File used for assessment: SWAMP Toxicity Data 2001-06 |
|
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. (Water Quality Control Plan, Central Coast Basin, General Objective Chapter III, Section II.A.2 Objectives for all Inland Surface Waters, Enclosed Bays and Estuaries). |
Objective/Criterion Reference: |
Water Quality Control Plan (Basin Plan) - Central Coast Region (Region 3) |
|
Evaluation Guideline: |
In fresh water sediments the probable effects level (predictive of sediment toxicity) for fluorene is 536 ug/Kg dry weight (MacDonald et al. 2000). |
Guideline Reference: |
Development and evaluation of consensus-based sediment effect concentrations for polychlorinated biphenyls. Environmental Toxicology and Chemistry. 19(5): 1403-1413 |
|
Spatial Representation: |
Data for this line of evidence for San Antonio Creek (313) was collected at 1 monitoring site [ 313SAI-San Antonio Creek at San Antonio Road West] |
Temporal Representation: |
Data was collected on a single day 3/31/2004. SWAMP toxicity monitoring includes both water samples (collected in both winter and summer) and sediment samples (collected in spring). |
Environmental Conditions: |
Staff is not aware of any special conditions that might effect interpretation of the data. |
QAPP Information: |
All data was collected following the Standard Operating Procedures and Data Quality Objectives outlined in the SWAMP QAMP, (Puckett, 2002). QA data are included in submission. All data are flagged as appropriate. |
QAPP Information Reference(s): |
|
Line of Evidence (LOE) for Decision ID 25576, Lead
|
Region 3 |
San Antonio Creek (San Antonio Watershed, Rancho del las Flores Bridge at Hwy 135 to downstream at Railroad Bridge) |
|
|
LOE ID: |
17172 |
|
Pollutant: |
Lead |
LOE Subgroup: |
Pollutant-Sediment |
Matrix: |
Sediment |
Fraction: |
None |
|
Beneficial Use: |
Warm Freshwater Habitat |
Aquatic Life 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: |
Central Coast Regional Board Staff assessed CCAMP_SWAMP Monitoring (03SW3001) data for San Antonio Creek (313) to determine beneficial use support and results are as follows: 0 of 1 samples exceed the criterion for Lead. |
Data Reference: |
Final Data File used for assessment: SWAMP Toxicity Data 2001-06 |
|
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. (Water Quality Control Plan, Central Coast Basin, General Objective Chapter III, Section II.A.2 Objectives for all Inland Surface Waters, Enclosed Bays and Estuaries). |
Objective/Criterion Reference: |
Water Quality Control Plan (Basin Plan) - Central Coast Region (Region 3) |
|
Evaluation Guideline: |
In fresh water sediments the probable effects level (predictive of sediment toxicity) for lead is 128 mg/Kg dry weight (MacDonald et al. 2000). |
Guideline Reference: |
Development and evaluation of consensus-based sediment effect concentrations for polychlorinated biphenyls. Environmental Toxicology and Chemistry. 19(5): 1403-1413 |
|
Spatial Representation: |
Data for this line of evidence for San Antonio Creek (313) was collected at 1 monitoring site [ 313SAI-San Antonio Creek at San Antonio Road West] |
Temporal Representation: |
Data was collected on a single day 3/31/2004. SWAMP toxicity monitoring includes both water samples (collected in both winter and summer) and sediment samples (collected in spring). |
Environmental Conditions: |
Staff is not aware of any special conditions that might effect interpretation of the data. |
QAPP Information: |
All data was collected following the Standard Operating Procedures and Data Quality Objectives outlined in the SWAMP QAMP, (Puckett, 2002). QA data are included in submission. All data are flagged as appropriate. |
QAPP Information Reference(s): |
|
Line of Evidence (LOE) for Decision ID 25576, Lead
|
Region 3 |
San Antonio Creek (San Antonio Watershed, Rancho del las Flores Bridge at Hwy 135 to downstream at Railroad Bridge) |
|
|
LOE ID: |
17154 |
|
Pollutant: |
Lead |
LOE Subgroup: |
Pollutant-Sediment |
Matrix: |
Sediment |
Fraction: |
None |
|
Beneficial Use: |
Warm Freshwater Habitat |
Aquatic Life 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: |
Central Coast Regional Board Staff assessed CCAMP_SWAMP Monitoring (00SW3001) data for San Antonio Creek (313) to determine beneficial use support and results are as follows: 0 of 2 samples exceed the criterion for Lead. |
Data Reference: |
Final Data File used for assessment: SWAMP Toxicity Data 2001-06 |
|
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. (Water Quality Control Plan, Central Coast Basin, General Objective Chapter III, Section II.A.2 Objectives for all Inland Surface Waters, Enclosed Bays and Estuaries). |
Objective/Criterion Reference: |
Water Quality Control Plan (Basin Plan) - Central Coast Region (Region 3) |
|
Evaluation Guideline: |
In fresh water sediments the probable effects level (predictive of sediment toxicity) for lead is 128 mg/Kg dry weight (MacDonald et al. 2000). |
Guideline Reference: |
Development and evaluation of consensus-based sediment effect concentrations for polychlorinated biphenyls. Environmental Toxicology and Chemistry. 19(5): 1403-1413 |
|
Spatial Representation: |
Data for this line of evidence for San Antonio Creek (313) was collected at 2 monitoring sites [ 313SAC-San Antonio Creek at Rail Road Bridge, u/s lagoon , 313SAI-San Antonio Creek at San Antonio Road West] |
Temporal Representation: |
Data was collected on a single day 3/28/2002. SWAMP toxicity monitoring includes both water samples (collected in both winter and summer) and sediment samples (collected in spring). |
Environmental Conditions: |
Staff is not aware of any special conditions that might effect interpretation of the data. |
QAPP Information: |
All data was collected following the Standard Operating Procedures and Data Quality Objectives outlined in the SWAMP QAMP, (Puckett, 2002). QA data are included in submission. All data are flagged as appropriate. |
QAPP Information Reference(s): |
|
Line of Evidence (LOE) for Decision ID 25576, Lead
|
Region 3 |
San Antonio Creek (San Antonio Watershed, Rancho del las Flores Bridge at Hwy 135 to downstream at Railroad Bridge) |
|
|
LOE ID: |
17171 |
|
Pollutant: |
Lead |
LOE Subgroup: |
Pollutant-Sediment |
Matrix: |
Sediment |
Fraction: |
None |
|
Beneficial Use: |
Cold Freshwater Habitat |
Aquatic Life Use: |
Cold Freshwater Habitat |
|
Number of Samples: |
1 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Central Coast Regional Board Staff assessed CCAMP_SWAMP Monitoring (03SW3001) data for San Antonio Creek (313) to determine beneficial use support and results are as follows: 0 of 1 samples exceed the criterion for Lead. |
Data Reference: |
Final Data File used for assessment: SWAMP Toxicity Data 2001-06 |
|
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. (Water Quality Control Plan, Central Coast Basin, General Objective Chapter III, Section II.A.2 Objectives for all Inland Surface Waters, Enclosed Bays and Estuaries). |
Objective/Criterion Reference: |
Water Quality Control Plan (Basin Plan) - Central Coast Region (Region 3) |
|
Evaluation Guideline: |
In fresh water sediments the probable effects level (predictive of sediment toxicity) for lead is 128 mg/Kg dry weight (MacDonald et al. 2000). |
Guideline Reference: |
Development and evaluation of consensus-based sediment effect concentrations for polychlorinated biphenyls. Environmental Toxicology and Chemistry. 19(5): 1403-1413 |
|
Spatial Representation: |
Data for this line of evidence for San Antonio Creek (313) was collected at 1 monitoring site [ 313SAI-San Antonio Creek at San Antonio Road West] |
Temporal Representation: |
Data was collected on a single day 3/31/2004. SWAMP toxicity monitoring includes both water samples (collected in both winter and summer) and sediment samples (collected in spring). |
Environmental Conditions: |
Staff is not aware of any special conditions that might effect interpretation of the data. |
QAPP Information: |
All data was collected following the Standard Operating Procedures and Data Quality Objectives outlined in the SWAMP QAMP, (Puckett, 2002). QA data are included in submission. All data are flagged as appropriate. |
QAPP Information Reference(s): |
|
Line of Evidence (LOE) for Decision ID 25576, Lead
|
Region 3 |
San Antonio Creek (San Antonio Watershed, Rancho del las Flores Bridge at Hwy 135 to downstream at Railroad Bridge) |
|
|
LOE ID: |
17141 |
|
Pollutant: |
Lead |
LOE Subgroup: |
Pollutant-Sediment |
Matrix: |
Sediment |
Fraction: |
None |
|
Beneficial Use: |
Cold Freshwater Habitat |
Aquatic Life 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: |
Central Coast Regional Board Staff assessed CCAMP_SWAMP Monitoring (00SW3001) data for San Antonio Creek (313) to determine beneficial use support and results are as follows: 0 of 2 samples exceed the criterion for Lead. |
Data Reference: |
Final Data File used for assessment: SWAMP Toxicity Data 2001-06 |
|
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. (Water Quality Control Plan, Central Coast Basin, General Objective Chapter III, Section II.A.2 Objectives for all Inland Surface Waters, Enclosed Bays and Estuaries). |
Objective/Criterion Reference: |
Water Quality Control Plan (Basin Plan) - Central Coast Region (Region 3) |
|
Evaluation Guideline: |
In fresh water sediments the probable effects level (predictive of sediment toxicity) for lead is 128 mg/Kg dry weight (MacDonald et al. 2000). |
Guideline Reference: |
Development and evaluation of consensus-based sediment effect concentrations for polychlorinated biphenyls. Environmental Toxicology and Chemistry. 19(5): 1403-1413 |
|
Spatial Representation: |
Data for this line of evidence for San Antonio Creek (313) was collected at 2 monitoring sites [ 313SAC-San Antonio Creek at Rail Road Bridge, u/s lagoon , 313SAI-San Antonio Creek at San Antonio Road West] |
Temporal Representation: |
Data was collected on a single day 3/28/2002. SWAMP toxicity monitoring includes both water samples (collected in both winter and summer) and sediment samples (collected in spring). |
Environmental Conditions: |
Staff is not aware of any special conditions that might effect interpretation of the data. |
QAPP Information: |
All data was collected following the Standard Operating Procedures and Data Quality Objectives outlined in the SWAMP QAMP, (Puckett, 2002). QA data are included in submission. All data are flagged as appropriate. |
QAPP Information Reference(s): |
|
Line of Evidence (LOE) for Decision ID 25577, Mercury
|
Region 3 |
San Antonio Creek (San Antonio Watershed, Rancho del las Flores Bridge at Hwy 135 to downstream at Railroad Bridge) |
|
|
LOE ID: |
17225 |
|
Pollutant: |
Mercury |
LOE Subgroup: |
Pollutant-Sediment |
Matrix: |
Sediment |
Fraction: |
None |
|
Beneficial Use: |
Cold Freshwater Habitat |
Aquatic Life Use: |
Cold Freshwater Habitat |
|
Number of Samples: |
1 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Central Coast Regional Board Staff assessed CCAMP_SWAMP Monitoring (03SW3001) data for San Antonio Creek (313) to determine beneficial use support and results are as follows: 0 of 1 samples exceed the criterion for Mercury. |
Data Reference: |
Final Data File used for assessment: SWAMP Toxicity Data 2001-06 |
|
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. (Water Quality Control Plan, Central Coast Basin, General Objective Chapter III, Section II.A.2 Objectives for all Inland Surface Waters, Enclosed Bays and Estuaries). |
Objective/Criterion Reference: |
Water Quality Control Plan (Basin Plan) - Central Coast Region (Region 3) |
|
Evaluation Guideline: |
In fresh water sediments the probable effects level (predictive of sediment toxicity) for mercury is 1.06 mg/Kg dry weight (MacDonald et al. 2000). |
Guideline Reference: |
Development and evaluation of consensus-based sediment effect concentrations for polychlorinated biphenyls. Environmental Toxicology and Chemistry. 19(5): 1403-1413 |
|
Spatial Representation: |
Data for this line of evidence for San Antonio Creek (313) was collected at 1 monitoring site [ 313SAI-San Antonio Creek at San Antonio Road West] |
Temporal Representation: |
Data was collected on a single day 3/31/2004. SWAMP toxicity monitoring includes both water samples (collected in both winter and summer) and sediment samples (collected in spring). |
Environmental Conditions: |
Staff is not aware of any special conditions that might effect interpretation of the data. |
QAPP Information: |
All data was collected following the Standard Operating Procedures and Data Quality Objectives outlined in the SWAMP QAMP, (Puckett, 2002). QA data are included in submission. All data are flagged as appropriate. |
QAPP Information Reference(s): |
|
Line of Evidence (LOE) for Decision ID 25577, Mercury
|
Region 3 |
San Antonio Creek (San Antonio Watershed, Rancho del las Flores Bridge at Hwy 135 to downstream at Railroad Bridge) |
|
|
LOE ID: |
17207 |
|
Pollutant: |
Mercury |
LOE Subgroup: |
Pollutant-Sediment |
Matrix: |
Sediment |
Fraction: |
None |
|
Beneficial Use: |
Cold Freshwater Habitat |
Aquatic Life 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: |
Central Coast Regional Board Staff assessed CCAMP_SWAMP Monitoring (00SW3001) data for San Antonio Creek (313) to determine beneficial use support and results are as follows: 1 of 2 samples exceed the criterion for Mercury. |
Data Reference: |
Final Data File used for assessment: SWAMP Toxicity Data 2001-06 |
|
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. (Water Quality Control Plan, Central Coast Basin, General Objective Chapter III, Section II.A.2 Objectives for all Inland Surface Waters, Enclosed Bays and Estuaries). |
Objective/Criterion Reference: |
Water Quality Control Plan (Basin Plan) - Central Coast Region (Region 3) |
|
Evaluation Guideline: |
In fresh water sediments the probable effects level (predictive of sediment toxicity) for mercury is 1.06 mg/Kg dry weight (MacDonald et al. 2000). |
Guideline Reference: |
Development and evaluation of consensus-based sediment effect concentrations for polychlorinated biphenyls. Environmental Toxicology and Chemistry. 19(5): 1403-1413 |
|
Spatial Representation: |
Data for this line of evidence for San Antonio Creek (313) was collected at 2 monitoring sites [ 313SAC-San Antonio Creek at Rail Road Bridge, u/s lagoon , 313SAI-San Antonio Creek at San Antonio Road West] |
Temporal Representation: |
Data was collected on a single day 3/28/2002. SWAMP toxicity monitoring includes both water samples (collected in both winter and summer) and sediment samples (collected in spring). |
Environmental Conditions: |
Staff is not aware of any special conditions that might effect interpretation of the data. |
QAPP Information: |
All data was collected following the Standard Operating Procedures and Data Quality Objectives outlined in the SWAMP QAMP, (Puckett, 2002). QA data are included in submission. All data are flagged as appropriate. |
QAPP Information Reference(s): |
|
Line of Evidence (LOE) for Decision ID 25577, Mercury
|
Region 3 |
San Antonio Creek (San Antonio Watershed, Rancho del las Flores Bridge at Hwy 135 to downstream at Railroad Bridge) |
|
|
LOE ID: |
17208 |
|
Pollutant: |
Mercury |
LOE Subgroup: |
Pollutant-Sediment |
Matrix: |
Sediment |
Fraction: |
None |
|
Beneficial Use: |
Warm Freshwater Habitat |
Aquatic Life 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: |
Central Coast Regional Board Staff assessed CCAMP_SWAMP Monitoring (00SW3001) data for San Antonio Creek (313) to determine beneficial use support and results are as follows: 1 of 2 samples exceed the criterion for Mercury. |
Data Reference: |
Final Data File used for assessment: SWAMP Toxicity Data 2001-06 |
|
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. (Water Quality Control Plan, Central Coast Basin, General Objective Chapter III, Section II.A.2 Objectives for all Inland Surface Waters, Enclosed Bays and Estuaries). |
Objective/Criterion Reference: |
Water Quality Control Plan (Basin Plan) - Central Coast Region (Region 3) |
|
Evaluation Guideline: |
In fresh water sediments the probable effects level (predictive of sediment toxicity) for mercury is 1.06 mg/Kg dry weight (MacDonald et al. 2000). |
Guideline Reference: |
Development and evaluation of consensus-based sediment effect concentrations for polychlorinated biphenyls. Environmental Toxicology and Chemistry. 19(5): 1403-1413 |
|
Spatial Representation: |
Data for this line of evidence for San Antonio Creek (313) was collected at 2 monitoring sites [ 313SAC-San Antonio Creek at Rail Road Bridge, u/s lagoon , 313SAI-San Antonio Creek at San Antonio Road West] |
Temporal Representation: |
Data was collected on a single day 3/28/2002. SWAMP toxicity monitoring includes both water samples (collected in both winter and summer) and sediment samples (collected in spring). |
Environmental Conditions: |
Staff is not aware of any special conditions that might effect interpretation of the data. |
QAPP Information: |
All data was collected following the Standard Operating Procedures and Data Quality Objectives outlined in the SWAMP QAMP, (Puckett, 2002). QA data are included in submission. All data are flagged as appropriate. |
QAPP Information Reference(s): |
|
Line of Evidence (LOE) for Decision ID 25577, Mercury
|
Region 3 |
San Antonio Creek (San Antonio Watershed, Rancho del las Flores Bridge at Hwy 135 to downstream at Railroad Bridge) |
|
|
LOE ID: |
17238 |
|
Pollutant: |
Mercury |
LOE Subgroup: |
Pollutant-Sediment |
Matrix: |
Sediment |
Fraction: |
None |
|
Beneficial Use: |
Warm Freshwater Habitat |
Aquatic Life 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: |
Central Coast Regional Board Staff assessed CCAMP_SWAMP Monitoring (03SW3001) data for San Antonio Creek (313) to determine beneficial use support and results are as follows: 0 of 1 samples exceed the criterion for Mercury. |
Data Reference: |
Final Data File used for assessment: SWAMP Toxicity Data 2001-06 |
|
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. (Water Quality Control Plan, Central Coast Basin, General Objective Chapter III, Section II.A.2 Objectives for all Inland Surface Waters, Enclosed Bays and Estuaries). |
Objective/Criterion Reference: |
Water Quality Control Plan (Basin Plan) - Central Coast Region (Region 3) |
|
Evaluation Guideline: |
In fresh water sediments the probable effects level (predictive of sediment toxicity) for mercury is 1.06 mg/Kg dry weight (MacDonald et al. 2000). |
Guideline Reference: |
Development and evaluation of consensus-based sediment effect concentrations for polychlorinated biphenyls. Environmental Toxicology and Chemistry. 19(5): 1403-1413 |
|
Spatial Representation: |
Data for this line of evidence for San Antonio Creek (313) was collected at 1 monitoring site [ 313SAI-San Antonio Creek at San Antonio Road West] |
Temporal Representation: |
Data was collected on a single day 3/31/2004. SWAMP toxicity monitoring includes both water samples (collected in both winter and summer) and sediment samples (collected in spring). |
Environmental Conditions: |
Staff is not aware of any special conditions that might effect interpretation of the data. |
QAPP Information: |
All data was collected following the Standard Operating Procedures and Data Quality Objectives outlined in the SWAMP QAMP, (Puckett, 2002). QA data are included in submission. All data are flagged as appropriate. |
QAPP Information Reference(s): |
|
Line of Evidence (LOE) for Decision ID 25632, Naphthalene
|
Region 3 |
San Antonio Creek (San Antonio Watershed, Rancho del las Flores Bridge at Hwy 135 to downstream at Railroad Bridge) |
|
|
LOE ID: |
17061 |
|
Pollutant: |
Naphthalene |
LOE Subgroup: |
Pollutant-Sediment |
Matrix: |
Sediment |
Fraction: |
None |
|
Beneficial Use: |
Warm Freshwater Habitat |
Aquatic Life 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: |
Central Coast Regional Board Staff assessed CCAMP_SWAMP Monitoring (03SW3001) data for San Antonio Creek (313) to determine beneficial use support and results are as follows: 0 of 1 samples exceed the criterion for Naphthalene. |
Data Reference: |
Final Data File used for assessment: SWAMP Toxicity Data 2001-06 |
|
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. (Water Quality Control Plan, Central Coast Basin, General Objective Chapter III, Section II.A.2 Objectives for all Inland Surface Waters, Enclosed Bays and Estuaries). |
Objective/Criterion Reference: |
Water Quality Control Plan (Basin Plan) - Central Coast Region (Region 3) |
|
Evaluation Guideline: |
In fresh water sediments the probable effects level (predictive of sediment toxicity) for naphthalene is 561 ug/Kg dry weight (MacDonald et al. 2000). |
Guideline Reference: |
Development and evaluation of consensus-based sediment effect concentrations for polychlorinated biphenyls. Environmental Toxicology and Chemistry. 19(5): 1403-1413 |
|
Spatial Representation: |
Data for this line of evidence for San Antonio Creek (313) was collected at 1 monitoring site [ 313SAI-San Antonio Creek at San Antonio Road West] |
Temporal Representation: |
Data was collected on a single day 3/31/2004. SWAMP toxicity monitoring includes both water samples (collected in both winter and summer) and sediment samples (collected in spring). |
Environmental Conditions: |
Staff is not aware of any special conditions that might effect interpretation of the data. |
QAPP Information: |
All data was collected following the Standard Operating Procedures and Data Quality Objectives outlined in the SWAMP QAMP, (Puckett, 2002). QA data are included in submission. All data are flagged as appropriate. |
QAPP Information Reference(s): |
|
Line of Evidence (LOE) for Decision ID 25632, Naphthalene
|
Region 3 |
San Antonio Creek (San Antonio Watershed, Rancho del las Flores Bridge at Hwy 135 to downstream at Railroad Bridge) |
|
|
LOE ID: |
17043 |
|
Pollutant: |
Naphthalene |
LOE Subgroup: |
Pollutant-Sediment |
Matrix: |
Sediment |
Fraction: |
None |
|
Beneficial Use: |
Warm Freshwater Habitat |
Aquatic Life 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: |
Central Coast Regional Board Staff assessed CCAMP_SWAMP Monitoring (00SW3001) data for San Antonio Creek (313) to determine beneficial use support and results are as follows: 0 of 2 samples exceed the criterion for Naphthalene. |
Data Reference: |
Final Data File used for assessment: SWAMP Toxicity Data 2001-06 |
|
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. (Water Quality Control Plan, Central Coast Basin, General Objective Chapter III, Section II.A.2 Objectives for all Inland Surface Waters, Enclosed Bays and Estuaries). |
Objective/Criterion Reference: |
Water Quality Control Plan (Basin Plan) - Central Coast Region (Region 3) |
|
Evaluation Guideline: |
In fresh water sediments the probable effects level (predictive of sediment toxicity) for naphthalene is 561 ug/Kg dry weight (MacDonald et al. 2000). |
Guideline Reference: |
Development and evaluation of consensus-based sediment effect concentrations for polychlorinated biphenyls. Environmental Toxicology and Chemistry. 19(5): 1403-1413 |
|
Spatial Representation: |
Data for this line of evidence for San Antonio Creek (313) was collected at 2 monitoring sites [ 313SAC-San Antonio Creek at Rail Road Bridge, u/s lagoon , 313SAI-San Antonio Creek at San Antonio Road West] |
Temporal Representation: |
Data was collected on a single day 3/28/2002. SWAMP toxicity monitoring includes both water samples (collected in both winter and summer) and sediment samples (collected in spring). |
Environmental Conditions: |
Staff is not aware of any special conditions that might effect interpretation of the data. |
QAPP Information: |
All data was collected following the Standard Operating Procedures and Data Quality Objectives outlined in the SWAMP QAMP, (Puckett, 2002). QA data are included in submission. All data are flagged as appropriate. |
QAPP Information Reference(s): |
|
Line of Evidence (LOE) for Decision ID 25632, Naphthalene
|
Region 3 |
San Antonio Creek (San Antonio Watershed, Rancho del las Flores Bridge at Hwy 135 to downstream at Railroad Bridge) |
|
|
LOE ID: |
17042 |
|
Pollutant: |
Naphthalene |
LOE Subgroup: |
Pollutant-Sediment |
Matrix: |
Sediment |
Fraction: |
None |
|
Beneficial Use: |
Cold Freshwater Habitat |
Aquatic Life 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: |
Central Coast Regional Board Staff assessed CCAMP_SWAMP Monitoring (00SW3001) data for San Antonio Creek (313) to determine beneficial use support and results are as follows: 0 of 2 samples exceed the criterion for Naphthalene. |
Data Reference: |
Final Data File used for assessment: SWAMP Toxicity Data 2001-06 |
|
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. (Water Quality Control Plan, Central Coast Basin, General Objective Chapter III, Section II.A.2 Objectives for all Inland Surface Waters, Enclosed Bays and Estuaries). |
Objective/Criterion Reference: |
Water Quality Control Plan (Basin Plan) - Central Coast Region (Region 3) |
|
Evaluation Guideline: |
In fresh water sediments the probable effects level (predictive of sediment toxicity) for naphthalene is 561 ug/Kg dry weight (MacDonald et al. 2000). |
Guideline Reference: |
Development and evaluation of consensus-based sediment effect concentrations for polychlorinated biphenyls. Environmental Toxicology and Chemistry. 19(5): 1403-1413 |
|
Spatial Representation: |
Data for this line of evidence for San Antonio Creek (313) was collected at 2 monitoring sites [ 313SAC-San Antonio Creek at Rail Road Bridge, u/s lagoon , 313SAI-San Antonio Creek at San Antonio Road West] |
Temporal Representation: |
Data was collected on a single day 3/28/2002. SWAMP toxicity monitoring includes both water samples (collected in both winter and summer) and sediment samples (collected in spring). |
Environmental Conditions: |
Staff is not aware of any special conditions that might effect interpretation of the data. |
QAPP Information: |
All data was collected following the Standard Operating Procedures and Data Quality Objectives outlined in the SWAMP QAMP, (Puckett, 2002). QA data are included in submission. All data are flagged as appropriate. |
QAPP Information Reference(s): |
|
Line of Evidence (LOE) for Decision ID 25632, Naphthalene
|
Region 3 |
San Antonio Creek (San Antonio Watershed, Rancho del las Flores Bridge at Hwy 135 to downstream at Railroad Bridge) |
|
|
LOE ID: |
17060 |
|
Pollutant: |
Naphthalene |
LOE Subgroup: |
Pollutant-Sediment |
Matrix: |
Sediment |
Fraction: |
None |
|
Beneficial Use: |
Cold Freshwater Habitat |
Aquatic Life Use: |
Cold Freshwater Habitat |
|
Number of Samples: |
1 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Central Coast Regional Board Staff assessed CCAMP_SWAMP Monitoring (03SW3001) data for San Antonio Creek (313) to determine beneficial use support and results are as follows: 0 of 1 samples exceed the criterion for Naphthalene. |
Data Reference: |
Final Data File used for assessment: SWAMP Toxicity Data 2001-06 |
|
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. (Water Quality Control Plan, Central Coast Basin, General Objective Chapter III, Section II.A.2 Objectives for all Inland Surface Waters, Enclosed Bays and Estuaries). |
Objective/Criterion Reference: |
Water Quality Control Plan (Basin Plan) - Central Coast Region (Region 3) |
|
Evaluation Guideline: |
In fresh water sediments the probable effects level (predictive of sediment toxicity) for naphthalene is 561 ug/Kg dry weight (MacDonald et al. 2000). |
Guideline Reference: |
Development and evaluation of consensus-based sediment effect concentrations for polychlorinated biphenyls. Environmental Toxicology and Chemistry. 19(5): 1403-1413 |
|
Spatial Representation: |
Data for this line of evidence for San Antonio Creek (313) was collected at 1 monitoring site [ 313SAI-San Antonio Creek at San Antonio Road West] |
Temporal Representation: |
Data was collected on a single day 3/31/2004. SWAMP toxicity monitoring includes both water samples (collected in both winter and summer) and sediment samples (collected in spring). |
Environmental Conditions: |
Staff is not aware of any special conditions that might effect interpretation of the data. |
QAPP Information: |
All data was collected following the Standard Operating Procedures and Data Quality Objectives outlined in the SWAMP QAMP, (Puckett, 2002). QA data are included in submission. All data are flagged as appropriate. |
QAPP Information Reference(s): |
|
Line of Evidence (LOE) for Decision ID 25578, Nickel
|
Region 3 |
San Antonio Creek (San Antonio Watershed, Rancho del las Flores Bridge at Hwy 135 to downstream at Railroad Bridge) |
|
|
LOE ID: |
17112 |
|
Pollutant: |
Nickel |
LOE Subgroup: |
Pollutant-Sediment |
Matrix: |
Sediment |
Fraction: |
None |
|
Beneficial Use: |
Warm Freshwater Habitat |
Aquatic Life 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: |
Central Coast Regional Board Staff assessed CCAMP_SWAMP Monitoring (00SW3001) data for San Antonio Creek (313) to determine beneficial use support and results are as follows: 0 of 2 samples exceed the criterion for Nickel. |
Data Reference: |
Final Data File used for assessment: SWAMP Toxicity Data 2001-06 |
|
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. (Water Quality Control Plan, Central Coast Basin, General Objective Chapter III, Section II.A.2 Objectives for all Inland Surface Waters, Enclosed Bays and Estuaries). |
Objective/Criterion Reference: |
Water Quality Control Plan (Basin Plan) - Central Coast Region (Region 3) |
|
Evaluation Guideline: |
In fresh water sediments the probable effects level (predictive of sediment toxicity) for nickel is 48.6 mg/Kg dry weight (MacDonald et al. 2000). |
Guideline Reference: |
Development and evaluation of consensus-based sediment effect concentrations for polychlorinated biphenyls. Environmental Toxicology and Chemistry. 19(5): 1403-1413 |
|
Spatial Representation: |
Data for this line of evidence for San Antonio Creek (313) was collected at 2 monitoring sites [ 313SAC-San Antonio Creek at Rail Road Bridge, u/s lagoon , 313SAI-San Antonio Creek at San Antonio Road West] |
Temporal Representation: |
Data was collected on a single day 3/28/2002. SWAMP toxicity monitoring includes both water samples (collected in both winter and summer) and sediment samples (collected in spring). |
Environmental Conditions: |
Staff is not aware of any special conditions that might effect interpretation of the data. |
QAPP Information: |
All data was collected following the Standard Operating Procedures and Data Quality Objectives outlined in the SWAMP QAMP, (Puckett, 2002). QA data are included in submission. All data are flagged as appropriate. |
QAPP Information Reference(s): |
|
Line of Evidence (LOE) for Decision ID 25578, Nickel
|
Region 3 |
San Antonio Creek (San Antonio Watershed, Rancho del las Flores Bridge at Hwy 135 to downstream at Railroad Bridge) |
|
|
LOE ID: |
16904 |
|
Pollutant: |
Nickel |
LOE Subgroup: |
Pollutant-Sediment |
Matrix: |
Sediment |
Fraction: |
None |
|
Beneficial Use: |
Warm Freshwater Habitat |
Aquatic Life 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: |
Central Coast Regional Board Staff assessed CCAMP_SWAMP Monitoring (03SW3001) data for San Antonio Creek (313) to determine beneficial use support and results are as follows: 0 of 1 samples exceed the criterion for Nickel. |
Data Reference: |
Final Data File used for assessment: SWAMP Toxicity Data 2001-06 |
|
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. (Water Quality Control Plan, Central Coast Basin, General Objective Chapter III, Section II.A.2 Objectives for all Inland Surface Waters, Enclosed Bays and Estuaries). |
Objective/Criterion Reference: |
Water Quality Control Plan (Basin Plan) - Central Coast Region (Region 3) |
|
Evaluation Guideline: |
In fresh water sediments the probable effects level (predictive of sediment toxicity) for nickel is 48.6 mg/Kg dry weight (MacDonald et al. 2000). |
Guideline Reference: |
Development and evaluation of consensus-based sediment effect concentrations for polychlorinated biphenyls. Environmental Toxicology and Chemistry. 19(5): 1403-1413 |
|
Spatial Representation: |
Data for this line of evidence for San Antonio Creek (313) was collected at 1 monitoring site [ 313SAI-San Antonio Creek at San Antonio Road West] |
Temporal Representation: |
Data was collected on a single day 3/31/2004. SWAMP toxicity monitoring includes both water samples (collected in both winter and summer) and sediment samples (collected in spring). |
Environmental Conditions: |
Staff is not aware of any special conditions that might effect interpretation of the data. |
QAPP Information: |
All data was collected following the Standard Operating Procedures and Data Quality Objectives outlined in the SWAMP QAMP, (Puckett, 2002). QA data are included in submission. All data are flagged as appropriate. |
QAPP Information Reference(s): |
|
Line of Evidence (LOE) for Decision ID 25578, Nickel
|
Region 3 |
San Antonio Creek (San Antonio Watershed, Rancho del las Flores Bridge at Hwy 135 to downstream at Railroad Bridge) |
|
|
LOE ID: |
16891 |
|
Pollutant: |
Nickel |
LOE Subgroup: |
Pollutant-Sediment |
Matrix: |
Sediment |
Fraction: |
None |
|
Beneficial Use: |
Cold Freshwater Habitat |
Aquatic Life Use: |
Cold Freshwater Habitat |
|
Number of Samples: |
1 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Central Coast Regional Board Staff assessed CCAMP_SWAMP Monitoring (03SW3001) data for San Antonio Creek (313) to determine beneficial use support and results are as follows: 0 of 1 samples exceed the criterion for Nickel. |
Data Reference: |
Final Data File used for assessment: SWAMP Toxicity Data 2001-06 |
|
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. (Water Quality Control Plan, Central Coast Basin, General Objective Chapter III, Section II.A.2 Objectives for all Inland Surface Waters, Enclosed Bays and Estuaries). |
Objective/Criterion Reference: |
Water Quality Control Plan (Basin Plan) - Central Coast Region (Region 3) |
|
Evaluation Guideline: |
In fresh water sediments the probable effects level (predictive of sediment toxicity) for nickel is 48.6 mg/Kg dry weight (MacDonald et al. 2000). |
Guideline Reference: |
Development and evaluation of consensus-based sediment effect concentrations for polychlorinated biphenyls. Environmental Toxicology and Chemistry. 19(5): 1403-1413 |
|
Spatial Representation: |
Data for this line of evidence for San Antonio Creek (313) was collected at 1 monitoring site [ 313SAI-San Antonio Creek at San Antonio Road West] |
Temporal Representation: |
Data was collected on a single day 3/31/2004. SWAMP toxicity monitoring includes both water samples (collected in both winter and summer) and sediment samples (collected in spring). |
Environmental Conditions: |
Staff is not aware of any special conditions that might effect interpretation of the data. |
QAPP Information: |
All data was collected following the Standard Operating Procedures and Data Quality Objectives outlined in the SWAMP QAMP, (Puckett, 2002). QA data are included in submission. All data are flagged as appropriate. |
QAPP Information Reference(s): |
|
Line of Evidence (LOE) for Decision ID 25578, Nickel
|
Region 3 |
San Antonio Creek (San Antonio Watershed, Rancho del las Flores Bridge at Hwy 135 to downstream at Railroad Bridge) |
|
|
LOE ID: |
17111 |
|
Pollutant: |
Nickel |
LOE Subgroup: |
Pollutant-Sediment |
Matrix: |
Sediment |
Fraction: |
None |
|
Beneficial Use: |
Cold Freshwater Habitat |
Aquatic Life 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: |
Central Coast Regional Board Staff assessed CCAMP_SWAMP Monitoring (00SW3001) data for San Antonio Creek (313) to determine beneficial use support and results are as follows: 0 of 2 samples exceed the criterion for Nickel. |
Data Reference: |
Final Data File used for assessment: SWAMP Toxicity Data 2001-06 |
|
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. (Water Quality Control Plan, Central Coast Basin, General Objective Chapter III, Section II.A.2 Objectives for all Inland Surface Waters, Enclosed Bays and Estuaries). |
Objective/Criterion Reference: |
Water Quality Control Plan (Basin Plan) - Central Coast Region (Region 3) |
|
Evaluation Guideline: |
In fresh water sediments the probable effects level (predictive of sediment toxicity) for nickel is 48.6 mg/Kg dry weight (MacDonald et al. 2000). |
Guideline Reference: |
Development and evaluation of consensus-based sediment effect concentrations for polychlorinated biphenyls. Environmental Toxicology and Chemistry. 19(5): 1403-1413 |
|
Spatial Representation: |
Data for this line of evidence for San Antonio Creek (313) was collected at 2 monitoring sites [ 313SAC-San Antonio Creek at Rail Road Bridge, u/s lagoon , 313SAI-San Antonio Creek at San Antonio Road West] |
Temporal Representation: |
Data was collected on a single day 3/28/2002. SWAMP toxicity monitoring includes both water samples (collected in both winter and summer) and sediment samples (collected in spring). |
Environmental Conditions: |
Staff is not aware of any special conditions that might effect interpretation of the data. |
QAPP Information: |
All data was collected following the Standard Operating Procedures and Data Quality Objectives outlined in the SWAMP QAMP, (Puckett, 2002). QA data are included in submission. All data are flagged as appropriate. |
QAPP Information Reference(s): |
|
Line of Evidence (LOE) for Decision ID 25709, Nitrate
|
Region 3 |
San Antonio Creek (San Antonio Watershed, Rancho del las Flores Bridge at Hwy 135 to downstream at Railroad Bridge) |
|
|
LOE ID: |
9663 |
|
Pollutant: |
Nitrate |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
None |
|
Beneficial Use: |
Agricultural Supply |
|
Number of Samples: |
30 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Central Coast Regional Board Staff assessed CCAMP Santa Barbara (SantaBarb) data for San Antonio Creek (313) to determine beneficial use support and results are as follows: 0 of 30 samples exceed the criterion for Nitrate as N. |
Data Reference: |
Final Data File used for assessment: CCAMP Water Quality Data_file1 |
|
Final Data File used for assessment: CCAMP Water Quality Data_file2 |
|
Final Data File used for assessment: CCAMP Water Quality Data_file3 |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
Waters shall not contain concentrations of chemical constituents in amounts which adversely affect the agricultural beneficial use. Interpretation of adverse effect shall be as derived from the University of California Agricultural Extension Service guidelines provided in Table 3-3 (Central Coast Waterboard Basin Plan, Chapter III, Section II.A.2 Objectives for all Inland and Surface Waters, Enclosed Bays and Estuaries). In Table 3-3 of the Basin Plan (page III-8), water quality guidelines state that severe problems may occur when nitrate exceeds 30 mg/L NO3 as N in irrigation supply water. |
Objective/Criterion Reference: |
Water Quality Control Plan (Basin Plan) - Central Coast Region (Region 3) |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
Data for this line of evidence for San Antonio Creek (313) was collected at 3 monitoring sites [ 313SAB-San Antonio Creek at Rancho de las Flores Bridge and Highway 135, 313SAE-San Antonio Creek at San Antonio Road East, 313SAI-San Antonio Creek at San Antonio Road West] |
Temporal Representation: |
Data was collected over the time period 1/18/2001-3/17/2002. Santa Barbara Coast is one of five annual rotation areas that are monitored for conventional pollutants by CCAMP staff monthly for one year. Toxicity monitoring is conducted twice during the rotation year (winter and summer) at a subset of sites. |
Environmental Conditions: |
Staff is not aware of any special conditions that might effect interpretation of the data. |
QAPP Information: |
All data was collected following the Standard Operating Procedures and Data Quality Objectives outlined in the SWAMP QAMP, (Puckett, 2002). QA data are included in submission. All data are flagged as appropriate. |
QAPP Information Reference(s): |
|
Line of Evidence (LOE) for Decision ID 25709, Nitrate
|
Region 3 |
San Antonio Creek (San Antonio Watershed, Rancho del las Flores Bridge at Hwy 135 to downstream at Railroad Bridge) |
|
|
LOE ID: |
9811 |
|
Pollutant: |
Nitrate |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
None |
|
Beneficial Use: |
Agricultural Supply |
|
Number of Samples: |
56 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Central Coast Regional Board Staff assessed CCAMP Coastal Confluences (CC) data for San Antonio Creek (313) to determine beneficial use support and results are as follows: 0 of 56 samples exceed the criterion for Nitrate as N. |
Data Reference: |
Final Data File used for assessment: CCAMP Water Quality Data_file1 |
|
Final Data File used for assessment: CCAMP Water Quality Data_file2 |
|
Final Data File used for assessment: CCAMP Water Quality Data_file3 |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
Waters shall not contain concentrations of chemical constituents in amounts which adversely affect the agricultural beneficial use. Interpretation of adverse effect shall be as derived from the University of California Agricultural Extension Service guidelines provided in Table 3-3 (Central Coast Waterboard Basin Plan, Chapter III, Section II.A.2 Objectives for all Inland and Surface Waters, Enclosed Bays and Estuaries). In Table 3-3 of the Basin Plan (page III-8), water quality guidelines state that severe problems may occur when nitrate exceeds 30 mg/L NO3 as N in irrigation supply water. |
Objective/Criterion Reference: |
Water Quality Control Plan (Basin Plan) - Central Coast Region (Region 3) |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
Data for this line of evidence for San Antonio Creek (313) was collected at 2 monitoring sites [ 313SAC-San Antonio Creek at Rail Road Bridge, u/s lagoon , 313SAI-San Antonio Creek at San Antonio Road West] |
Temporal Representation: |
Data was collected over the time period 1/18/2001-12/6/2006. CCAMP Coastal confluence monitoring is conducted monthly (with the exception of April 2003 - December 2003) and is ongoing. |
Environmental Conditions: |
Staff is not aware of any special conditions that might effect interpretation of the data. |
QAPP Information: |
All data was collected following the Standard Operating Procedures and Data Quality Objectives outlined in the SWAMP QAMP, (Puckett, 2002). QA data are included in submission. All data are flagged as appropriate. |
QAPP Information Reference(s): |
|
Line of Evidence (LOE) for Decision ID 25709, Nitrate
|
Region 3 |
San Antonio Creek (San Antonio Watershed, Rancho del las Flores Bridge at Hwy 135 to downstream at Railroad Bridge) |
|
|
LOE ID: |
9676 |
|
Pollutant: |
Nitrate |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
None |
|
Beneficial Use: |
Municipal & Domestic Supply |
|
Number of Samples: |
30 |
Number of Exceedances: |
1 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Central Coast Regional Board Staff assessed CCAMP Santa Barbara (SantaBarb) data for San Antonio Creek (313) to determine beneficial use support and results are as follows: 1 of 30 samples exceed the criterion for Nitrate as N. |
Data Reference: |
Final Data File used for assessment: CCAMP Water Quality Data_file1 |
|
Final Data File used for assessment: CCAMP Water Quality Data_file2 |
|
Final Data File used for assessment: CCAMP Water Quality Data_file3 |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
The Water Quality Control Plan, Central Coast Basin Objective for municipal and domestic supply uses of inland surface waters (Section II.A.2) states the following: waters shall not contain concentrations of chemical constituents in excess of the limits specified in California Code of Regulations, Title 22, Article 4, Chapter 15, Section 64435, Tables 2 and 3 as listed in Table 3-2. The maximum contaminant level listed in Table 3-2 (inorganic and fluoride concentrations not to be exceeded in domestic or municipal supply) for nitrate is 10.0 mg/L (NO3 as N). |
Objective/Criterion Reference: |
Title 22, Division 4, Ch. 15, Article 4, Section 64431, Table 64431-A |
|
Water Quality Control Plan (Basin Plan) - Central Coast Region (Region 3) |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
Data for this line of evidence for San Antonio Creek (313) was collected at 3 monitoring sites [ 313SAB-San Antonio Creek at Rancho de las Flores Bridge and Highway 135, 313SAE-San Antonio Creek at San Antonio Road East, 313SAI-San Antonio Creek at San Antonio Road West] |
Temporal Representation: |
Data was collected over the time period 1/18/2001-3/17/2002. Santa Barbara Coast is one of five annual rotation areas that are monitored for conventional pollutants by CCAMP staff monthly for one year. Toxicity monitoring is conducted twice during the rotation year (winter and summer) at a subset of sites. |
Environmental Conditions: |
Staff is not aware of any special conditions that might effect interpretation of the data. |
QAPP Information: |
All data was collected following the Standard Operating Procedures and Data Quality Objectives outlined in the SWAMP QAMP, (Puckett, 2002). QA data are included in submission. All data are flagged as appropriate. |
QAPP Information Reference(s): |
|
Line of Evidence (LOE) for Decision ID 25709, Nitrate
|
Region 3 |
San Antonio Creek (San Antonio Watershed, Rancho del las Flores Bridge at Hwy 135 to downstream at Railroad Bridge) |
|
|
LOE ID: |
9710 |
|
Pollutant: |
Nitrate |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
None |
|
Beneficial Use: |
Municipal & Domestic Supply |
|
Number of Samples: |
56 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Central Coast Regional Board Staff assessed CCAMP Coastal Confluences (CC) data for San Antonio Creek (313) to determine beneficial use support and results are as follows: 0 of 56 samples exceed the criterion for Nitrate as N. |
Data Reference: |
Final Data File used for assessment: CCAMP Water Quality Data_file1 |
|
Final Data File used for assessment: CCAMP Water Quality Data_file2 |
|
Final Data File used for assessment: CCAMP Water Quality Data_file3 |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
The Water Quality Control Plan, Central Coast Basin Objective for municipal and domestic supply uses of inland surface waters (Section II.A.2) states the following: waters shall not contain concentrations of chemical constituents in excess of the limits specified in California Code of Regulations, Title 22, Article 4, Chapter 15, Section 64435, Tables 2 and 3 as listed in Table 3-2. The maximum contaminant level listed in Table 3-2 (inorganic and fluoride concentrations not to be exceeded in domestic or municipal supply) for nitrate is 10.0 mg/L (NO3 as N). |
Objective/Criterion Reference: |
Title 22, Division 4, Ch. 15, Article 4, Section 64431, Table 64431-A |
|
Water Quality Control Plan (Basin Plan) - Central Coast Region (Region 3) |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
Data for this line of evidence for San Antonio Creek (313) was collected at 2 monitoring sites [ 313SAC-San Antonio Creek at Rail Road Bridge, u/s lagoon , 313SAI-San Antonio Creek at San Antonio Road West] |
Temporal Representation: |
Data was collected over the time period 1/18/2001-12/6/2006. CCAMP Coastal confluence monitoring is conducted monthly (with the exception of April 2003 - December 2003) and is ongoing. |
Environmental Conditions: |
Staff is not aware of any special conditions that might effect interpretation of the data. |
QAPP Information: |
All data was collected following the Standard Operating Procedures and Data Quality Objectives outlined in the SWAMP QAMP, (Puckett, 2002). QA data are included in submission. All data are flagged as appropriate. |
QAPP Information Reference(s): |
|
Line of Evidence (LOE) for Decision ID 25426, Phenanthrene
|
Region 3 |
San Antonio Creek (San Antonio Watershed, Rancho del las Flores Bridge at Hwy 135 to downstream at Railroad Bridge) |
|
|
LOE ID: |
17038 |
|
Pollutant: |
Phenanthrene |
LOE Subgroup: |
Pollutant-Sediment |
Matrix: |
Sediment |
Fraction: |
None |
|
Beneficial Use: |
Warm Freshwater Habitat |
Aquatic Life 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: |
Central Coast Regional Board Staff assessed CCAMP_SWAMP Monitoring (03SW3001) data for San Antonio Creek (313) to determine beneficial use support and results are as follows: 0 of 1 samples exceed the criterion for Phenanthrene. |
Data Reference: |
Final Data File used for assessment: SWAMP Toxicity Data 2001-06 |
|
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. (Water Quality Control Plan, Central Coast Basin, General Objective Chapter III, Section II.A.2 Objectives for all Inland Surface Waters, Enclosed Bays and Estuaries). |
Objective/Criterion Reference: |
Water Quality Control Plan (Basin Plan) - Central Coast Region (Region 3) |
|
Evaluation Guideline: |
In fresh water sediments the probable effects level (predictive of sediment toxicity) for Phenanthrene is 1170 ug/Kg dry weight (Macdonald et al. 2000) |
Guideline Reference: |
Development and evaluation of consensus-based sediment effect concentrations for polychlorinated biphenyls. Environmental Toxicology and Chemistry. 19(5): 1403-1413 |
|
Spatial Representation: |
Data for this line of evidence for San Antonio Creek (313) was collected at 1 monitoring site [ 313SAI-San Antonio Creek at San Antonio Road West] |
Temporal Representation: |
Data was collected on a single day 3/31/2004. SWAMP toxicity monitoring includes both water samples (collected in both winter and summer) and sediment samples (collected in spring). |
Environmental Conditions: |
Staff is not aware of any special conditions that might effect interpretation of the data. |
QAPP Information: |
All data was collected following the Standard Operating Procedures and Data Quality Objectives outlined in the SWAMP QAMP, (Puckett, 2002). QA data are included in submission. All data are flagged as appropriate. |
QAPP Information Reference(s): |
|
Line of Evidence (LOE) for Decision ID 25426, Phenanthrene
|
Region 3 |
San Antonio Creek (San Antonio Watershed, Rancho del las Flores Bridge at Hwy 135 to downstream at Railroad Bridge) |
|
|
LOE ID: |
17007 |
|
Pollutant: |
Phenanthrene |
LOE Subgroup: |
Pollutant-Sediment |
Matrix: |
Sediment |
Fraction: |
None |
|
Beneficial Use: |
Cold Freshwater Habitat |
Aquatic Life 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: |
Central Coast Regional Board Staff assessed CCAMP_SWAMP Monitoring (00SW3001) data for San Antonio Creek (313) to determine beneficial use support and results are as follows: 0 of 2 samples exceed the criterion for Phenanthrene. |
Data Reference: |
Final Data File used for assessment: SWAMP Toxicity Data 2001-06 |
|
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. (Water Quality Control Plan, Central Coast Basin, General Objective Chapter III, Section II.A.2 Objectives for all Inland Surface Waters, Enclosed Bays and Estuaries). |
Objective/Criterion Reference: |
Water Quality Control Plan (Basin Plan) - Central Coast Region (Region 3) |
|
Evaluation Guideline: |
In fresh water sediments the probable effects level (predictive of sediment toxicity) for Phenanthrene is 1170 ug/Kg dry weight (Macdonald et al. 2000) |
Guideline Reference: |
Development and evaluation of consensus-based sediment effect concentrations for polychlorinated biphenyls. Environmental Toxicology and Chemistry. 19(5): 1403-1413 |
|
Spatial Representation: |
Data for this line of evidence for San Antonio Creek (313) was collected at 2 monitoring sites [ 313SAC-San Antonio Creek at Rail Road Bridge, u/s lagoon , 313SAI-San Antonio Creek at San Antonio Road West] |
Temporal Representation: |
Data was collected on a single day 3/28/2002. SWAMP toxicity monitoring includes both water samples (collected in both winter and summer) and sediment samples (collected in spring). |
Environmental Conditions: |
Staff is not aware of any special conditions that might effect interpretation of the data. |
QAPP Information: |
All data was collected following the Standard Operating Procedures and Data Quality Objectives outlined in the SWAMP QAMP, (Puckett, 2002). QA data are included in submission. All data are flagged as appropriate. |
QAPP Information Reference(s): |
|
Line of Evidence (LOE) for Decision ID 25426, Phenanthrene
|
Region 3 |
San Antonio Creek (San Antonio Watershed, Rancho del las Flores Bridge at Hwy 135 to downstream at Railroad Bridge) |
|
|
LOE ID: |
17025 |
|
Pollutant: |
Phenanthrene |
LOE Subgroup: |
Pollutant-Sediment |
Matrix: |
Sediment |
Fraction: |
None |
|
Beneficial Use: |
Cold Freshwater Habitat |
Aquatic Life Use: |
Cold Freshwater Habitat |
|
Number of Samples: |
1 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Central Coast Regional Board Staff assessed CCAMP_SWAMP Monitoring (03SW3001) data for San Antonio Creek (313) to determine beneficial use support and results are as follows: 0 of 1 samples exceed the criterion for Phenanthrene. |
Data Reference: |
Final Data File used for assessment: SWAMP Toxicity Data 2001-06 |
|
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. (Water Quality Control Plan, Central Coast Basin, General Objective Chapter III, Section II.A.2 Objectives for all Inland Surface Waters, Enclosed Bays and Estuaries). |
Objective/Criterion Reference: |
Water Quality Control Plan (Basin Plan) - Central Coast Region (Region 3) |
|
Evaluation Guideline: |
In fresh water sediments the probable effects level (predictive of sediment toxicity) for Phenanthrene is 1170 ug/Kg dry weight (Macdonald et al. 2000) |
Guideline Reference: |
Development and evaluation of consensus-based sediment effect concentrations for polychlorinated biphenyls. Environmental Toxicology and Chemistry. 19(5): 1403-1413 |
|
Spatial Representation: |
Data for this line of evidence for San Antonio Creek (313) was collected at 1 monitoring site [ 313SAI-San Antonio Creek at San Antonio Road West] |
Temporal Representation: |
Data was collected on a single day 3/31/2004. SWAMP toxicity monitoring includes both water samples (collected in both winter and summer) and sediment samples (collected in spring). |
Environmental Conditions: |
Staff is not aware of any special conditions that might effect interpretation of the data. |
QAPP Information: |
All data was collected following the Standard Operating Procedures and Data Quality Objectives outlined in the SWAMP QAMP, (Puckett, 2002). QA data are included in submission. All data are flagged as appropriate. |
QAPP Information Reference(s): |
|
Line of Evidence (LOE) for Decision ID 25426, Phenanthrene
|
Region 3 |
San Antonio Creek (San Antonio Watershed, Rancho del las Flores Bridge at Hwy 135 to downstream at Railroad Bridge) |
|
|
LOE ID: |
17008 |
|
Pollutant: |
Phenanthrene |
LOE Subgroup: |
Pollutant-Sediment |
Matrix: |
Sediment |
Fraction: |
None |
|
Beneficial Use: |
Warm Freshwater Habitat |
Aquatic Life 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: |
Central Coast Regional Board Staff assessed CCAMP_SWAMP Monitoring (00SW3001) data for San Antonio Creek (313) to determine beneficial use support and results are as follows: 0 of 2 samples exceed the criterion for Phenanthrene. |
Data Reference: |
Final Data File used for assessment: SWAMP Toxicity Data 2001-06 |
|
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. (Water Quality Control Plan, Central Coast Basin, General Objective Chapter III, Section II.A.2 Objectives for all Inland Surface Waters, Enclosed Bays and Estuaries). |
Objective/Criterion Reference: |
Water Quality Control Plan (Basin Plan) - Central Coast Region (Region 3) |
|
Evaluation Guideline: |
In fresh water sediments the probable effects level (predictive of sediment toxicity) for Phenanthrene is 1170 ug/Kg dry weight (Macdonald et al. 2000) |
Guideline Reference: |
Development and evaluation of consensus-based sediment effect concentrations for polychlorinated biphenyls. Environmental Toxicology and Chemistry. 19(5): 1403-1413 |
|
Spatial Representation: |
Data for this line of evidence for San Antonio Creek (313) was collected at 2 monitoring sites [ 313SAC-San Antonio Creek at Rail Road Bridge, u/s lagoon , 313SAI-San Antonio Creek at San Antonio Road West] |
Temporal Representation: |
Data was collected on a single day 3/28/2002. SWAMP toxicity monitoring includes both water samples (collected in both winter and summer) and sediment samples (collected in spring). |
Environmental Conditions: |
Staff is not aware of any special conditions that might effect interpretation of the data. |
QAPP Information: |
All data was collected following the Standard Operating Procedures and Data Quality Objectives outlined in the SWAMP QAMP, (Puckett, 2002). QA data are included in submission. All data are flagged as appropriate. |
QAPP Information Reference(s): |
|
Line of Evidence (LOE) for Decision ID 25427, Pyrene
|
Region 3 |
San Antonio Creek (San Antonio Watershed, Rancho del las Flores Bridge at Hwy 135 to downstream at Railroad Bridge) |
|
|
LOE ID: |
17933 |
|
Pollutant: |
Pyrene |
LOE Subgroup: |
Pollutant-Sediment |
Matrix: |
Sediment |
Fraction: |
None |
|
Beneficial Use: |
Warm Freshwater Habitat |
Aquatic Life 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: |
Central Coast Regional Board Staff assessed CCAMP_SWAMP Monitoring (03SW3001) data for San Antonio Creek (313) to determine beneficial use support and results are as follows: 0 of 1 samples exceed the criterion for Pyrene. |
Data Reference: |
Final Data File used for assessment: SWAMP Toxicity Data 2001-06 |
|
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. (Water Quality Control Plan, Central Coast Basin, General Objective Chapter III, Section II.A.2 Objectives for all Inland Surface Waters, Enclosed Bays and Estuaries). |
Objective/Criterion Reference: |
Water Quality Control Plan (Basin Plan) - Central Coast Region (Region 3) |
|
Evaluation Guideline: |
In fresh water sediments the probable effects level (predictive of sediment toxicity) for Pyrene is 1520 ug/Kg dry weight (Macdonald et al. 2000) |
Guideline Reference: |
Development and evaluation of consensus-based sediment effect concentrations for polychlorinated biphenyls. Environmental Toxicology and Chemistry. 19(5): 1403-1413 |
|
Spatial Representation: |
Data for this line of evidence for San Antonio Creek (313) was collected at 1 monitoring site [ 313SAI-San Antonio Creek at San Antonio Road West] |
Temporal Representation: |
Data was collected on a single day 3/31/2004. SWAMP toxicity monitoring includes both water samples (collected in both winter and summer) and sediment samples (collected in spring). |
Environmental Conditions: |
Staff is not aware of any special conditions that might effect interpretation of the data. |
QAPP Information: |
All data was collected following the Standard Operating Procedures and Data Quality Objectives outlined in the SWAMP QAMP, (Puckett, 2002). QA data are included in submission. All data are flagged as appropriate. |
QAPP Information Reference(s): |
|
Line of Evidence (LOE) for Decision ID 25427, Pyrene
|
Region 3 |
San Antonio Creek (San Antonio Watershed, Rancho del las Flores Bridge at Hwy 135 to downstream at Railroad Bridge) |
|
|
LOE ID: |
17914 |
|
Pollutant: |
Pyrene |
LOE Subgroup: |
Pollutant-Sediment |
Matrix: |
Sediment |
Fraction: |
None |
|
Beneficial Use: |
Warm Freshwater Habitat |
Aquatic Life 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: |
Central Coast Regional Board Staff assessed CCAMP_SWAMP Monitoring (00SW3001) data for San Antonio Creek (313) to determine beneficial use support and results are as follows: 0 of 2 samples exceed the criterion for Pyrene. |
Data Reference: |
Final Data File used for assessment: SWAMP Toxicity Data 2001-06 |
|
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. (Water Quality Control Plan, Central Coast Basin, General Objective Chapter III, Section II.A.2 Objectives for all Inland Surface Waters, Enclosed Bays and Estuaries). |
Objective/Criterion Reference: |
Water Quality Control Plan (Basin Plan) - Central Coast Region (Region 3) |
|
Evaluation Guideline: |
In fresh water sediments the probable effects level (predictive of sediment toxicity) for Pyrene is 1520 ug/Kg dry weight (Macdonald et al. 2000) |
Guideline Reference: |
Development and evaluation of consensus-based sediment effect concentrations for polychlorinated biphenyls. Environmental Toxicology and Chemistry. 19(5): 1403-1413 |
|
Spatial Representation: |
Data for this line of evidence for San Antonio Creek (313) was collected at 2 monitoring sites [ 313SAC-San Antonio Creek at Rail Road Bridge, u/s lagoon , 313SAI-San Antonio Creek at San Antonio Road West] |
Temporal Representation: |
Data was collected on a single day 3/28/2002. SWAMP toxicity monitoring includes both water samples (collected in both winter and summer) and sediment samples (collected in spring). |
Environmental Conditions: |
Staff is not aware of any special conditions that might effect interpretation of the data. |
QAPP Information: |
All data was collected following the Standard Operating Procedures and Data Quality Objectives outlined in the SWAMP QAMP, (Puckett, 2002). QA data are included in submission. All data are flagged as appropriate. |
QAPP Information Reference(s): |
|
Line of Evidence (LOE) for Decision ID 25427, Pyrene
|
Region 3 |
San Antonio Creek (San Antonio Watershed, Rancho del las Flores Bridge at Hwy 135 to downstream at Railroad Bridge) |
|
|
LOE ID: |
17899 |
|
Pollutant: |
Pyrene |
LOE Subgroup: |
Pollutant-Sediment |
Matrix: |
Sediment |
Fraction: |
None |
|
Beneficial Use: |
Cold Freshwater Habitat |
Aquatic Life 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: |
Central Coast Regional Board Staff assessed CCAMP_SWAMP Monitoring (00SW3001) data for San Antonio Creek (313) to determine beneficial use support and results are as follows: 0 of 2 samples exceed the criterion for Pyrene. |
Data Reference: |
Final Data File used for assessment: SWAMP Toxicity Data 2001-06 |
|
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. (Water Quality Control Plan, Central Coast Basin, General Objective Chapter III, Section II.A.2 Objectives for all Inland Surface Waters, Enclosed Bays and Estuaries). |
Objective/Criterion Reference: |
Water Quality Control Plan (Basin Plan) - Central Coast Region (Region 3) |
|
Evaluation Guideline: |
In fresh water sediments the probable effects level (predictive of sediment toxicity) for Pyrene is 1520 ug/Kg dry weight (Macdonald et al. 2000) |
Guideline Reference: |
Development and evaluation of consensus-based sediment effect concentrations for polychlorinated biphenyls. Environmental Toxicology and Chemistry. 19(5): 1403-1413 |
|
Spatial Representation: |
Data for this line of evidence for San Antonio Creek (313) was collected at 2 monitoring sites [ 313SAC-San Antonio Creek at Rail Road Bridge, u/s lagoon , 313SAI-San Antonio Creek at San Antonio Road West] |
Temporal Representation: |
Data was collected on a single day 3/28/2002. SWAMP toxicity monitoring includes both water samples (collected in both winter and summer) and sediment samples (collected in spring). |
Environmental Conditions: |
Staff is not aware of any special conditions that might effect interpretation of the data. |
QAPP Information: |
All data was collected following the Standard Operating Procedures and Data Quality Objectives outlined in the SWAMP QAMP, (Puckett, 2002). QA data are included in submission. All data are flagged as appropriate. |
QAPP Information Reference(s): |
|
Line of Evidence (LOE) for Decision ID 25427, Pyrene
|
Region 3 |
San Antonio Creek (San Antonio Watershed, Rancho del las Flores Bridge at Hwy 135 to downstream at Railroad Bridge) |
|
|
LOE ID: |
17932 |
|
Pollutant: |
Pyrene |
LOE Subgroup: |
Pollutant-Sediment |
Matrix: |
Sediment |
Fraction: |
None |
|
Beneficial Use: |
Cold Freshwater Habitat |
Aquatic Life Use: |
Cold Freshwater Habitat |
|
Number of Samples: |
1 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Central Coast Regional Board Staff assessed CCAMP_SWAMP Monitoring (03SW3001) data for San Antonio Creek (313) to determine beneficial use support and results are as follows: 0 of 1 samples exceed the criterion for Pyrene. |
Data Reference: |
Final Data File used for assessment: SWAMP Toxicity Data 2001-06 |
|
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. (Water Quality Control Plan, Central Coast Basin, General Objective Chapter III, Section II.A.2 Objectives for all Inland Surface Waters, Enclosed Bays and Estuaries). |
Objective/Criterion Reference: |
Water Quality Control Plan (Basin Plan) - Central Coast Region (Region 3) |
|
Evaluation Guideline: |
In fresh water sediments the probable effects level (predictive of sediment toxicity) for Pyrene is 1520 ug/Kg dry weight (Macdonald et al. 2000) |
Guideline Reference: |
Development and evaluation of consensus-based sediment effect concentrations for polychlorinated biphenyls. Environmental Toxicology and Chemistry. 19(5): 1403-1413 |
|
Spatial Representation: |
Data for this line of evidence for San Antonio Creek (313) was collected at 1 monitoring site [ 313SAI-San Antonio Creek at San Antonio Road West] |
Temporal Representation: |
Data was collected on a single day 3/31/2004. SWAMP toxicity monitoring includes both water samples (collected in both winter and summer) and sediment samples (collected in spring). |
Environmental Conditions: |
Staff is not aware of any special conditions that might effect interpretation of the data. |
QAPP Information: |
All data was collected following the Standard Operating Procedures and Data Quality Objectives outlined in the SWAMP QAMP, (Puckett, 2002). QA data are included in submission. All data are flagged as appropriate. |
QAPP Information Reference(s): |
|
Line of Evidence (LOE) for Decision ID 25242, Turbidity
|
Region 3 |
San Antonio Creek (San Antonio Watershed, Rancho del las Flores Bridge at Hwy 135 to downstream at Railroad Bridge) |
|
|
LOE ID: |
13311 |
|
Pollutant: |
Turbidity |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
None |
|
Beneficial Use: |
Cold Freshwater Habitat |
Aquatic Life Use: |
Cold Freshwater Habitat |
|
Number of Samples: |
49 |
Number of Exceedances: |
10 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Central Coast Regional Board Staff assessed CCAMP Coastal Confluences (CC) data for San Antonio Creek (313) to determine beneficial use support and results are as follows: 10 of 49 samples exceed the criterion for Turbidity(NTU). |
Data Reference: |
Final Data File used for assessment: CCAMP Water Quality Data_file1 |
|
Final Data File used for assessment: CCAMP Water Quality Data_file2 |
|
Final Data File used for assessment: CCAMP Water Quality Data_file3 |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
Waters shall be free of changes in turbidity that cause nuisance or adversely affect beneficial uses. Water Quality Control Plan, Central Coast Basin, Chapter III, Section II.A.2 Objectives for all Inland Surface Waters, Enclosed Bays and Estuaries. |
Objective/Criterion Reference: |
Water Quality Control Plan (Basin Plan) - Central Coast Region (Region 3) |
|
Evaluation Guideline: |
Sigler et al. (1984) states that turbidities of 25 NTU's or greater caused reduction in juvenile salmonid growth due to interference with their ability to find food. |
Guideline Reference: |
Effects of chronic turbidity on density and growth of steelheads and coho salmon. Transactions of the American Fisheries Society 113:142-150 |
|
Spatial Representation: |
Data for this line of evidence for San Antonio Creek (313) was collected at 2 monitoring sites [ 313SAC-San Antonio Creek at Rail Road Bridge, u/s lagoon , 313SAI-San Antonio Creek at San Antonio Road West] |
Temporal Representation: |
Data was collected over the time period 1/18/2001-12/6/2006. CCAMP Coastal confluence monitoring is conducted monthly (with the exception of April 2003 - December 2003) and is ongoing. |
Environmental Conditions: |
Staff is not aware of any special conditions that might effect interpretation of the data. |
QAPP Information: |
All data was collected following the Standard Operating Procedures and Data Quality Objectives outlined in the SWAMP QAMP, (Puckett, 2002). QA data are included in submission. All data are flagged as appropriate. |
QAPP Information Reference(s): |
|
Line of Evidence (LOE) for Decision ID 25242, Turbidity
|
Region 3 |
San Antonio Creek (San Antonio Watershed, Rancho del las Flores Bridge at Hwy 135 to downstream at Railroad Bridge) |
|
|
LOE ID: |
13275 |
|
Pollutant: |
Turbidity |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
None |
|
Beneficial Use: |
Warm Freshwater Habitat |
Aquatic Life 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: |
Central Coast Regional Board Staff assessed CCAMP Diurnal Dissolved Oxygen Sampling (DO) data for San Antonio Creek (313) to determine beneficial use support and results are as follows: 0 of 2 samples exceed the criterion for Turbidity(NTU). |
Data Reference: |
Final Data File used for assessment: CCAMP Water Quality Data_file1 |
|
Final Data File used for assessment: CCAMP Water Quality Data_file2 |
|
Final Data File used for assessment: CCAMP Water Quality Data_file3 |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
Waters shall be free of changes in turbidity that cause nuisance or adversely affect beneficial uses. Water Quality Control Plan, Central Coast Basin, Chapter III, Section II.A.2 Objectives for all Inland Surface Waters, Enclosed Bays and Estuaries. |
Objective/Criterion Reference: |
Water Quality Control Plan (Basin Plan) - Central Coast Region (Region 3) |
|
Evaluation Guideline: |
Sigler et al. (1984) states that turbidities of 25 NTU's or greater caused reduction in juvenile salmonid growth due to interference with their ability to find food. |
Guideline Reference: |
Effects of chronic turbidity on density and growth of steelheads and coho salmon. Transactions of the American Fisheries Society 113:142-150 |
|
Spatial Representation: |
Data for this line of evidence for San Antonio Creek (313) was collected at 2 monitoring sites [ 313SAB-San Antonio Creek at Rancho de las Flores Bridge and Highway 135, 313SAI-San Antonio Creek at San Antonio Road West] |
Temporal Representation: |
Data was collected on a single day 7/18/2001. Diurnal monitoring conducted in summer months at all CCAMP monitoring sites. |
Environmental Conditions: |
Staff is not aware of any special conditions that might effect interpretation of the data. |
QAPP Information: |
All data was collected following the Standard Operating Procedures and Data Quality Objectives outlined in the SWAMP QAMP, (Puckett, 2002). QA data are included in submission. All data are flagged as appropriate. |
QAPP Information Reference(s): |
|
Line of Evidence (LOE) for Decision ID 25242, Turbidity
|
Region 3 |
San Antonio Creek (San Antonio Watershed, Rancho del las Flores Bridge at Hwy 135 to downstream at Railroad Bridge) |
|
|
LOE ID: |
13274 |
|
Pollutant: |
Turbidity |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
None |
|
Beneficial Use: |
Cold Freshwater Habitat |
Aquatic Life 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: |
Central Coast Regional Board Staff assessed CCAMP Diurnal Dissolved Oxygen Sampling (DO) data for San Antonio Creek (313) to determine beneficial use support and results are as follows: 0 of 2 samples exceed the criterion for Turbidity(NTU). |
Data Reference: |
Final Data File used for assessment: CCAMP Water Quality Data_file1 |
|
Final Data File used for assessment: CCAMP Water Quality Data_file2 |
|
Final Data File used for assessment: CCAMP Water Quality Data_file3 |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
Waters shall be free of changes in turbidity that cause nuisance or adversely affect beneficial uses. Water Quality Control Plan, Central Coast Basin, Chapter III, Section II.A.2 Objectives for all Inland Surface Waters, Enclosed Bays and Estuaries. |
Objective/Criterion Reference: |
Water Quality Control Plan (Basin Plan) - Central Coast Region (Region 3) |
|
Evaluation Guideline: |
Sigler et al. (1984) states that turbidities of 25 NTU's or greater caused reduction in juvenile salmonid growth due to interference with their ability to find food. |
Guideline Reference: |
Effects of chronic turbidity on density and growth of steelheads and coho salmon. Transactions of the American Fisheries Society 113:142-150 |
|
Spatial Representation: |
Data for this line of evidence for San Antonio Creek (313) was collected at 2 monitoring sites [ 313SAB-San Antonio Creek at Rancho de las Flores Bridge and Highway 135, 313SAI-San Antonio Creek at San Antonio Road West] |
Temporal Representation: |
Data was collected on a single day 7/18/2001. Diurnal monitoring conducted in summer months at all CCAMP monitoring sites. |
Environmental Conditions: |
Staff is not aware of any special conditions that might effect interpretation of the data. |
QAPP Information: |
All data was collected following the Standard Operating Procedures and Data Quality Objectives outlined in the SWAMP QAMP, (Puckett, 2002). QA data are included in submission. All data are flagged as appropriate. |
QAPP Information Reference(s): |
|
Line of Evidence (LOE) for Decision ID 25242, Turbidity
|
Region 3 |
San Antonio Creek (San Antonio Watershed, Rancho del las Flores Bridge at Hwy 135 to downstream at Railroad Bridge) |
|
|
LOE ID: |
13240 |
|
Pollutant: |
Turbidity |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
None |
|
Beneficial Use: |
Warm Freshwater Habitat |
Aquatic Life Use: |
Warm Freshwater Habitat |
|
Number of Samples: |
30 |
Number of Exceedances: |
7 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Central Coast Regional Board Staff assessed CCAMP Santa Barbara (SantaBarb) data for San Antonio Creek (313) to determine beneficial use support and results are as follows: 7 of 30 samples exceed the criterion for Turbidity(NTU). |
Data Reference: |
Final Data File used for assessment: CCAMP Water Quality Data_file1 |
|
Final Data File used for assessment: CCAMP Water Quality Data_file2 |
|
Final Data File used for assessment: CCAMP Water Quality Data_file3 |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
Waters shall be free of changes in turbidity that cause nuisance or adversely affect beneficial uses. Water Quality Control Plan, Central Coast Basin, Chapter III, Section II.A.2 Objectives for all Inland Surface Waters, Enclosed Bays and Estuaries. |
Objective/Criterion Reference: |
Water Quality Control Plan (Basin Plan) - Central Coast Region (Region 3) |
|
Evaluation Guideline: |
Sigler et al. (1984) states that turbidities of 25 NTU's or greater caused reduction in juvenile salmonid growth due to interference with their ability to find food. |
Guideline Reference: |
Effects of chronic turbidity on density and growth of steelheads and coho salmon. Transactions of the American Fisheries Society 113:142-150 |
|
Spatial Representation: |
Data for this line of evidence for San Antonio Creek (313) was collected at 3 monitoring sites [ 313SAB-San Antonio Creek at Rancho de las Flores Bridge and Highway 135, 313SAE-San Antonio Creek at San Antonio Road East, 313SAI-San Antonio Creek at San Antonio Road West] |
Temporal Representation: |
Data was collected over the time period 1/18/2001-3/17/2002. Santa Barbara Coast is one of five annual rotation areas that are monitored for conventional pollutants by CCAMP staff monthly for one year. Toxicity monitoring is conducted twice during the rotation year (winter and summer) at a subset of sites. |
Environmental Conditions: |
Staff is not aware of any special conditions that might effect interpretation of the data. |
QAPP Information: |
All data was collected following the Standard Operating Procedures and Data Quality Objectives outlined in the SWAMP QAMP, (Puckett, 2002). QA data are included in submission. All data are flagged as appropriate. |
QAPP Information Reference(s): |
|
Line of Evidence (LOE) for Decision ID 25242, Turbidity
|
Region 3 |
San Antonio Creek (San Antonio Watershed, Rancho del las Flores Bridge at Hwy 135 to downstream at Railroad Bridge) |
|
|
LOE ID: |
13312 |
|
Pollutant: |
Turbidity |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
None |
|
Beneficial Use: |
Warm Freshwater Habitat |
Aquatic Life Use: |
Warm Freshwater Habitat |
|
Number of Samples: |
49 |
Number of Exceedances: |
10 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Central Coast Regional Board Staff assessed CCAMP Coastal Confluences (CC) data for San Antonio Creek (313) to determine beneficial use support and results are as follows: 10 of 49 samples exceed the criterion for Turbidity(NTU). |
Data Reference: |
Final Data File used for assessment: CCAMP Water Quality Data_file1 |
|
Final Data File used for assessment: CCAMP Water Quality Data_file2 |
|
Final Data File used for assessment: CCAMP Water Quality Data_file3 |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
Waters shall be free of changes in turbidity that cause nuisance or adversely affect beneficial uses. Water Quality Control Plan, Central Coast Basin, Chapter III, Section II.A.2 Objectives for all Inland Surface Waters, Enclosed Bays and Estuaries. |
Objective/Criterion Reference: |
Water Quality Control Plan (Basin Plan) - Central Coast Region (Region 3) |
|
Evaluation Guideline: |
Sigler et al. (1984) states that turbidities of 25 NTU's or greater caused reduction in juvenile salmonid growth due to interference with their ability to find food. |
Guideline Reference: |
Effects of chronic turbidity on density and growth of steelheads and coho salmon. Transactions of the American Fisheries Society 113:142-150 |
|
Spatial Representation: |
Data for this line of evidence for San Antonio Creek (313) was collected at 2 monitoring sites [ 313SAC-San Antonio Creek at Rail Road Bridge, u/s lagoon , 313SAI-San Antonio Creek at San Antonio Road West] |
Temporal Representation: |
Data was collected over the time period 1/18/2001-12/6/2006. CCAMP Coastal confluence monitoring is conducted monthly (with the exception of April 2003 - December 2003) and is ongoing. |
Environmental Conditions: |
Staff is not aware of any special conditions that might effect interpretation of the data. |
QAPP Information: |
All data was collected following the Standard Operating Procedures and Data Quality Objectives outlined in the SWAMP QAMP, (Puckett, 2002). QA data are included in submission. All data are flagged as appropriate. |
QAPP Information Reference(s): |
|
Line of Evidence (LOE) for Decision ID 25242, Turbidity
|
Region 3 |
San Antonio Creek (San Antonio Watershed, Rancho del las Flores Bridge at Hwy 135 to downstream at Railroad Bridge) |
|
|
LOE ID: |
13239 |
|
Pollutant: |
Turbidity |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
None |
|
Beneficial Use: |
Cold Freshwater Habitat |
Aquatic Life Use: |
Cold Freshwater Habitat |
|
Number of Samples: |
30 |
Number of Exceedances: |
7 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Central Coast Regional Board Staff assessed CCAMP Santa Barbara (SantaBarb) data for San Antonio Creek (313) to determine beneficial use support and results are as follows: 7 of 30 samples exceed the criterion for Turbidity(NTU). |
Data Reference: |
Final Data File used for assessment: CCAMP Water Quality Data_file1 |
|
Final Data File used for assessment: CCAMP Water Quality Data_file2 |
|
Final Data File used for assessment: CCAMP Water Quality Data_file3 |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
Waters shall be free of changes in turbidity that cause nuisance or adversely affect beneficial uses. Water Quality Control Plan, Central Coast Basin, Chapter III, Section II.A.2 Objectives for all Inland Surface Waters, Enclosed Bays and Estuaries. |
Objective/Criterion Reference: |
Water Quality Control Plan (Basin Plan) - Central Coast Region (Region 3) |
|
Evaluation Guideline: |
Sigler et al. (1984) states that turbidities of 25 NTU's or greater caused reduction in juvenile salmonid growth due to interference with their ability to find food. |
Guideline Reference: |
Effects of chronic turbidity on density and growth of steelheads and coho salmon. Transactions of the American Fisheries Society 113:142-150 |
|
Spatial Representation: |
Data for this line of evidence for San Antonio Creek (313) was collected at 3 monitoring sites [ 313SAB-San Antonio Creek at Rancho de las Flores Bridge and Highway 135, 313SAE-San Antonio Creek at San Antonio Road East, 313SAI-San Antonio Creek at San Antonio Road West] |
Temporal Representation: |
Data was collected over the time period 1/18/2001-3/17/2002. Santa Barbara Coast is one of five annual rotation areas that are monitored for conventional pollutants by CCAMP staff monthly for one year. Toxicity monitoring is conducted twice during the rotation year (winter and summer) at a subset of sites. |
Environmental Conditions: |
Staff is not aware of any special conditions that might effect interpretation of the data. |
QAPP Information: |
All data was collected following the Standard Operating Procedures and Data Quality Objectives outlined in the SWAMP QAMP, (Puckett, 2002). QA data are included in submission. All data are flagged as appropriate. |
QAPP Information Reference(s): |
|
Line of Evidence (LOE) for Decision ID 25697, Unknown Toxicity
|
Region 3 |
San Antonio Creek (San Antonio Watershed, Rancho del las Flores Bridge at Hwy 135 to downstream at Railroad Bridge) |
|
|
LOE ID: |
24430 |
|
Pollutant: |
Vertebrate Toxicity |
LOE Subgroup: |
Toxicity |
Matrix: |
Water |
Fraction: |
None |
|
Beneficial Use: |
Cold Freshwater Habitat |
Aquatic Life Use: |
Cold Freshwater Habitat |
|
Number of Samples: |
6 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
TOXICITY TESTING |
Data Used to Assess Water Quality: |
Central Coast Regional Board Staff assessed CCAMP_SWAMP Monitoring (00SW3001) data for San Antonio Creek (313) to determine beneficial use support and results are as follows: 0 of 6 samples exceed the criterion for Toxicity, Pimephales promelas Survival (%) 7 days. Toxicity is defined by SWAMP (2004) as follows: Significant toxicity in the survival endpoint when compared to the negative control based on a statistical test with alpha of less than 5%, and less than the evaluation threshold (both criteria are met). |
Data Reference: |
Final Data File used for assessment: SWAMP Toxicity Data 2001-06 |
|
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. Compliance with this objective will be determined by use of indicator organisms, analyses of species diversity, population density, growth anomalies, toxicity bioassays of appropriate duration, or other appropriate methods as specified by the Regional Board (Water Quality Control Plan, Central Coast Basin, Chapter III, Section II.A.2 Objectives for all Inland Surface Waters, Enclosed Bays and Estuaries). |
Objective/Criterion Reference: |
Water Quality Control Plan (Basin Plan) - Central Coast Region (Region 3) |
|
Evaluation Guideline: |
Significant reduction of survival of test organism relative to the control (alpha < 0.05) and test organism survival is 20% less than the control survival. |
Guideline Reference: |
Quality Assurance Management Plan for the State of California's Surface Water Ambient Monitoring Program. Sacramento, CA. State Water Resources Control Board. SWAMP. December 2002 (1st version)
|
|
Spatial Representation: |
Data for this line of evidence for San Antonio Creek (313) was collected at 3 monitoring sites [ 313SAB-San Antonio Creek at Rancho de las Flores Bridge and Highway 135, 313SAI-San Antonio Creek at San Antonio Road West, 313SAC-San Antonio Creek at Rail Road Bridge, u/s lagoon ] |
Temporal Representation: |
Data was collected over the time period 12/10/2001-3/17/2002. SWAMP toxicity monitoring includes both water samples (collected in both winter and summer) and sediment samples (collected in spring). |
Environmental Conditions: |
Staff is not aware of any special conditions that might effect interpretation of the data. |
QAPP Information: |
All data was collected following the Standard Operating Procedures and Data Quality Objectives outlined in the SWAMP QAMP, (Puckett, 2002). QA data are included in submission. All data are flagged as appropriate. |
QAPP Information Reference(s): |
|
Line of Evidence (LOE) for Decision ID 25697, Unknown Toxicity
|
Region 3 |
San Antonio Creek (San Antonio Watershed, Rancho del las Flores Bridge at Hwy 135 to downstream at Railroad Bridge) |
|
|
LOE ID: |
24404 |
|
Pollutant: |
Invertebrate Toxicity |
LOE Subgroup: |
Toxicity |
Matrix: |
Water |
Fraction: |
None |
|
Beneficial Use: |
Cold Freshwater Habitat |
Aquatic Life Use: |
Cold Freshwater Habitat |
|
Number of Samples: |
6 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
TOXICITY TESTING |
Data Used to Assess Water Quality: |
Central Coast Regional Board Staff assessed CCAMP_SWAMP Monitoring (00SW3001) data for San Antonio Creek (313) to determine beneficial use support and results are as follows: 0 of 6 samples exceed the criterion for Toxicity, Ceriodaphnia dubia Survival (%) 7 days. Toxicity is defined by SWAMP (2004) as follows: Significant toxicity in the survival endpoint when compared to the negative control based on a statistical test with alpha of less than 5%, and less than the evaluation threshold (both criteria are met). |
Data Reference: |
Final Data File used for assessment: SWAMP Toxicity Data 2001-06 |
|
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. Compliance with this objective will be determined by use of indicator organisms, analyses of species diversity, population density, growth anomalies, toxicity bioassays of appropriate duration, or other appropriate methods as specified by the Regional Board (Water Quality Control Plan, Central Coast Basin, Chapter III, Section II.A.2 Objectives for all Inland Surface Waters, Enclosed Bays and Estuaries). |
Objective/Criterion Reference: |
Water Quality Control Plan (Basin Plan) - Central Coast Region (Region 3) |
|
Evaluation Guideline: |
Significant reduction of survival of test organism relative to the control (alpha < 0.05) and test organism survival is 20% less than the control survival. |
Guideline Reference: |
Quality Assurance Management Plan for the State of California's Surface Water Ambient Monitoring Program. Sacramento, CA. State Water Resources Control Board. SWAMP. December 2002 (1st version)
|
|
Spatial Representation: |
Data for this line of evidence for San Antonio Creek (313) was collected at 3 monitoring sites [ 313SAB-San Antonio Creek at Rancho de las Flores Bridge and Highway 135, 313SAC-San Antonio Creek at Rail Road Bridge, u/s lagoon , 313SAI-San Antonio Creek at San Antonio Road West] |
Temporal Representation: |
Data was collected over the time period 12/10/2001-3/17/2002. SWAMP toxicity monitoring includes both water samples (collected in both winter and summer) and sediment samples (collected in spring). |
Environmental Conditions: |
Staff is not aware of any special conditions that might effect interpretation of the data. |
QAPP Information: |
All data was collected following the Standard Operating Procedures and Data Quality Objectives outlined in the SWAMP QAMP, (Puckett, 2002). QA data are included in submission. All data are flagged as appropriate. |
QAPP Information Reference(s): |
|
Line of Evidence (LOE) for Decision ID 25697, Unknown Toxicity
|
Region 3 |
San Antonio Creek (San Antonio Watershed, Rancho del las Flores Bridge at Hwy 135 to downstream at Railroad Bridge) |
|
|
LOE ID: |
24251 |
|
Pollutant: |
Vertebrate Toxicity |
LOE Subgroup: |
Toxicity |
Matrix: |
Water |
Fraction: |
None |
|
Beneficial Use: |
Warm Freshwater Habitat |
Aquatic Life Use: |
Warm Freshwater Habitat |
|
Number of Samples: |
6 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
TOXICITY TESTING |
Data Used to Assess Water Quality: |
Central Coast Regional Board Staff assessed CCAMP_SWAMP Monitoring (00SW3001) data for San Antonio Creek (313) to determine beneficial use support and results are as follows: 0 of 6 samples exceed the criterion for Toxicity, Pimephales promelas Survival (%) 7 days. Toxicity is defined by SWAMP (2004) as follows: Significant toxicity in the survival endpoint when compared to the negative control based on a statistical test with alpha of less than 5%, and less than the evaluation threshold (both criteria are met). |
Data Reference: |
Final Data File used for assessment: SWAMP Toxicity Data 2001-06 |
|
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. Compliance with this objective will be determined by use of indicator organisms, analyses of species diversity, population density, growth anomalies, toxicity bioassays of appropriate duration, or other appropriate methods as specified by the Regional Board (Water Quality Control Plan, Central Coast Basin, Chapter III, Section II.A.2 Objectives for all Inland Surface Waters, Enclosed Bays and Estuaries). |
Objective/Criterion Reference: |
Water Quality Control Plan (Basin Plan) - Central Coast Region (Region 3) |
|
Evaluation Guideline: |
Significant reduction of survival of test organism relative to the control (alpha < 0.05) and test organism survival is 20% less than the control survival. |
Guideline Reference: |
Quality Assurance Management Plan for the State of California's Surface Water Ambient Monitoring Program. Sacramento, CA. State Water Resources Control Board. SWAMP. December 2002 (1st version)
|
|
Spatial Representation: |
Data for this line of evidence for San Antonio Creek (313) was collected at 3 monitoring sites [ 313SAB-San Antonio Creek at Rancho de las Flores Bridge and Highway 135, 313SAI-San Antonio Creek at San Antonio Road West, 313SAC-San Antonio Creek at Rail Road Bridge, u/s lagoon ] |
Temporal Representation: |
Data was collected over the time period 12/10/2001-3/17/2002. SWAMP toxicity monitoring includes both water samples (collected in both winter and summer) and sediment samples (collected in spring). |
Environmental Conditions: |
Staff is not aware of any special conditions that might effect interpretation of the data. |
QAPP Information: |
All data was collected following the Standard Operating Procedures and Data Quality Objectives outlined in the SWAMP QAMP, (Puckett, 2002). QA data are included in submission. All data are flagged as appropriate. |
QAPP Information Reference(s): |
|
Line of Evidence (LOE) for Decision ID 25697, Unknown Toxicity
|
Region 3 |
San Antonio Creek (San Antonio Watershed, Rancho del las Flores Bridge at Hwy 135 to downstream at Railroad Bridge) |
|
|
LOE ID: |
24405 |
|
Pollutant: |
Invertebrate Toxicity |
LOE Subgroup: |
Toxicity |
Matrix: |
Water |
Fraction: |
None |
|
Beneficial Use: |
Warm Freshwater Habitat |
Aquatic Life Use: |
Warm Freshwater Habitat |
|
Number of Samples: |
6 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
TOXICITY TESTING |
Data Used to Assess Water Quality: |
Central Coast Regional Board Staff assessed CCAMP_SWAMP Monitoring (00SW3001) data for San Antonio Creek (313) to determine beneficial use support and results are as follows: 0 of 6 samples exceed the criterion for Toxicity, Ceriodaphnia dubia Survival (%) 7 days. Toxicity is defined by SWAMP (2004) as follows: Significant toxicity in the survival endpoint when compared to the negative control based on a statistical test with alpha of less than 5%, and less than the evaluation threshold (both criteria are met). |
Data Reference: |
Final Data File used for assessment: SWAMP Toxicity Data 2001-06 |
|
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. Compliance with this objective will be determined by use of indicator organisms, analyses of species diversity, population density, growth anomalies, toxicity bioassays of appropriate duration, or other appropriate methods as specified by the Regional Board (Water Quality Control Plan, Central Coast Basin, Chapter III, Section II.A.2 Objectives for all Inland Surface Waters, Enclosed Bays and Estuaries). |
Objective/Criterion Reference: |
Water Quality Control Plan (Basin Plan) - Central Coast Region (Region 3) |
|
Evaluation Guideline: |
Significant reduction of survival of test organism relative to the control (alpha < 0.05) and test organism survival is 20% less than the control survival. |
Guideline Reference: |
Quality Assurance Management Plan for the State of California's Surface Water Ambient Monitoring Program. Sacramento, CA. State Water Resources Control Board. SWAMP. December 2002 (1st version)
|
|
Spatial Representation: |
Data for this line of evidence for San Antonio Creek (313) was collected at 3 monitoring sites [ 313SAB-San Antonio Creek at Rancho de las Flores Bridge and Highway 135, 313SAC-San Antonio Creek at Rail Road Bridge, u/s lagoon , 313SAI-San Antonio Creek at San Antonio Road West] |
Temporal Representation: |
Data was collected over the time period 12/10/2001-3/17/2002. SWAMP toxicity monitoring includes both water samples (collected in both winter and summer) and sediment samples (collected in spring). |
Environmental Conditions: |
Staff is not aware of any special conditions that might effect interpretation of the data. |
QAPP Information: |
All data was collected following the Standard Operating Procedures and Data Quality Objectives outlined in the SWAMP QAMP, (Puckett, 2002). QA data are included in submission. All data are flagged as appropriate. |
QAPP Information Reference(s): |
|
Line of Evidence (LOE) for Decision ID 25438, Zinc
|
Region 3 |
San Antonio Creek (San Antonio Watershed, Rancho del las Flores Bridge at Hwy 135 to downstream at Railroad Bridge) |
|
|
LOE ID: |
17721 |
|
Pollutant: |
Zinc |
LOE Subgroup: |
Pollutant-Sediment |
Matrix: |
Sediment |
Fraction: |
None |
|
Beneficial Use: |
Warm Freshwater Habitat |
Aquatic Life 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: |
Central Coast Regional Board Staff assessed CCAMP_SWAMP Monitoring (00SW3001) data for San Antonio Creek (313) to determine beneficial use support and results are as follows: 0 of 2 samples exceed the criterion for Zinc. |
Data Reference: |
Final Data File used for assessment: SWAMP Toxicity Data 2001-06 |
|
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. (Water Quality Control Plan, Central Coast Basin, General Objective Chapter III, Section II.A.2 Objectives for all Inland Surface Waters, Enclosed Bays and Estuaries). |
Objective/Criterion Reference: |
Water Quality Control Plan (Basin Plan) - Central Coast Region (Region 3) |
|
Evaluation Guideline: |
In fresh water sediments the probable effects level (predictive of sediment toxicity) for zinc is 459 mg/Kg dry weight (MacDonald et al. 2000). |
Guideline Reference: |
Development and evaluation of consensus-based sediment effect concentrations for polychlorinated biphenyls. Environmental Toxicology and Chemistry. 19(5): 1403-1413 |
|
Spatial Representation: |
Data for this line of evidence for San Antonio Creek (313) was collected at 2 monitoring sites [ 313SAC-San Antonio Creek at Rail Road Bridge, u/s lagoon , 313SAI-San Antonio Creek at San Antonio Road West] |
Temporal Representation: |
Data was collected on a single day 3/28/2002. SWAMP toxicity monitoring includes both water samples (collected in both winter and summer) and sediment samples (collected in spring). |
Environmental Conditions: |
Staff is not aware of any special conditions that might effect interpretation of the data. |
QAPP Information: |
All data was collected following the Standard Operating Procedures and Data Quality Objectives outlined in the SWAMP QAMP, (Puckett, 2002). QA data are included in submission. All data are flagged as appropriate. |
QAPP Information Reference(s): |
|
Line of Evidence (LOE) for Decision ID 25438, Zinc
|
Region 3 |
San Antonio Creek (San Antonio Watershed, Rancho del las Flores Bridge at Hwy 135 to downstream at Railroad Bridge) |
|
|
LOE ID: |
17741 |
|
Pollutant: |
Zinc |
LOE Subgroup: |
Pollutant-Sediment |
Matrix: |
Sediment |
Fraction: |
None |
|
Beneficial Use: |
Warm Freshwater Habitat |
Aquatic Life 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: |
Central Coast Regional Board Staff assessed CCAMP_SWAMP Monitoring (03SW3001) data for San Antonio Creek (313) to determine beneficial use support and results are as follows: 0 of 1 samples exceed the criterion for Zinc. |
Data Reference: |
Final Data File used for assessment: SWAMP Toxicity Data 2001-06 |
|
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. (Water Quality Control Plan, Central Coast Basin, General Objective Chapter III, Section II.A.2 Objectives for all Inland Surface Waters, Enclosed Bays and Estuaries). |
Objective/Criterion Reference: |
Water Quality Control Plan (Basin Plan) - Central Coast Region (Region 3) |
|
Evaluation Guideline: |
In fresh water sediments the probable effects level (predictive of sediment toxicity) for zinc is 459 mg/Kg dry weight (MacDonald et al. 2000). |
Guideline Reference: |
Development and evaluation of consensus-based sediment effect concentrations for polychlorinated biphenyls. Environmental Toxicology and Chemistry. 19(5): 1403-1413 |
|
Spatial Representation: |
Data for this line of evidence for San Antonio Creek (313) was collected at 1 monitoring site [ 313SAI-San Antonio Creek at San Antonio Road West] |
Temporal Representation: |
Data was collected on a single day 3/31/2004. SWAMP toxicity monitoring includes both water samples (collected in both winter and summer) and sediment samples (collected in spring). |
Environmental Conditions: |
Staff is not aware of any special conditions that might effect interpretation of the data. |
QAPP Information: |
All data was collected following the Standard Operating Procedures and Data Quality Objectives outlined in the SWAMP QAMP, (Puckett, 2002). QA data are included in submission. All data are flagged as appropriate. |
QAPP Information Reference(s): |
|
Line of Evidence (LOE) for Decision ID 25438, Zinc
|
Region 3 |
San Antonio Creek (San Antonio Watershed, Rancho del las Flores Bridge at Hwy 135 to downstream at Railroad Bridge) |
|
|
LOE ID: |
17720 |
|
Pollutant: |
Zinc |
LOE Subgroup: |
Pollutant-Sediment |
Matrix: |
Sediment |
Fraction: |
None |
|
Beneficial Use: |
Cold Freshwater Habitat |
Aquatic Life 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: |
Central Coast Regional Board Staff assessed CCAMP_SWAMP Monitoring (00SW3001) data for San Antonio Creek (313) to determine beneficial use support and results are as follows: 0 of 2 samples exceed the criterion for Zinc. |
Data Reference: |
Final Data File used for assessment: SWAMP Toxicity Data 2001-06 |
|
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. (Water Quality Control Plan, Central Coast Basin, General Objective Chapter III, Section II.A.2 Objectives for all Inland Surface Waters, Enclosed Bays and Estuaries). |
Objective/Criterion Reference: |
Water Quality Control Plan (Basin Plan) - Central Coast Region (Region 3) |
|
Evaluation Guideline: |
In fresh water sediments the probable effects level (predictive of sediment toxicity) for zinc is 459 mg/Kg dry weight (MacDonald et al. 2000). |
Guideline Reference: |
Development and evaluation of consensus-based sediment effect concentrations for polychlorinated biphenyls. Environmental Toxicology and Chemistry. 19(5): 1403-1413 |
|
Spatial Representation: |
Data for this line of evidence for San Antonio Creek (313) was collected at 2 monitoring sites [ 313SAC-San Antonio Creek at Rail Road Bridge, u/s lagoon , 313SAI-San Antonio Creek at San Antonio Road West] |
Temporal Representation: |
Data was collected on a single day 3/28/2002. SWAMP toxicity monitoring includes both water samples (collected in both winter and summer) and sediment samples (collected in spring). |
Environmental Conditions: |
Staff is not aware of any special conditions that might effect interpretation of the data. |
QAPP Information: |
All data was collected following the Standard Operating Procedures and Data Quality Objectives outlined in the SWAMP QAMP, (Puckett, 2002). QA data are included in submission. All data are flagged as appropriate. |
QAPP Information Reference(s): |
|
Line of Evidence (LOE) for Decision ID 25438, Zinc
|
Region 3 |
San Antonio Creek (San Antonio Watershed, Rancho del las Flores Bridge at Hwy 135 to downstream at Railroad Bridge) |
|
|
LOE ID: |
17740 |
|
Pollutant: |
Zinc |
LOE Subgroup: |
Pollutant-Sediment |
Matrix: |
Sediment |
Fraction: |
None |
|
Beneficial Use: |
Cold Freshwater Habitat |
Aquatic Life Use: |
Cold Freshwater Habitat |
|
Number of Samples: |
1 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Central Coast Regional Board Staff assessed CCAMP_SWAMP Monitoring (03SW3001) data for San Antonio Creek (313) to determine beneficial use support and results are as follows: 0 of 1 samples exceed the criterion for Zinc. |
Data Reference: |
Final Data File used for assessment: SWAMP Toxicity Data 2001-06 |
|
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. (Water Quality Control Plan, Central Coast Basin, General Objective Chapter III, Section II.A.2 Objectives for all Inland Surface Waters, Enclosed Bays and Estuaries). |
Objective/Criterion Reference: |
Water Quality Control Plan (Basin Plan) - Central Coast Region (Region 3) |
|
Evaluation Guideline: |
In fresh water sediments the probable effects level (predictive of sediment toxicity) for zinc is 459 mg/Kg dry weight (MacDonald et al. 2000). |
Guideline Reference: |
Development and evaluation of consensus-based sediment effect concentrations for polychlorinated biphenyls. Environmental Toxicology and Chemistry. 19(5): 1403-1413 |
|
Spatial Representation: |
Data for this line of evidence for San Antonio Creek (313) was collected at 1 monitoring site [ 313SAI-San Antonio Creek at San Antonio Road West] |
Temporal Representation: |
Data was collected on a single day 3/31/2004. SWAMP toxicity monitoring includes both water samples (collected in both winter and summer) and sediment samples (collected in spring). |
Environmental Conditions: |
Staff is not aware of any special conditions that might effect interpretation of the data. |
QAPP Information: |
All data was collected following the Standard Operating Procedures and Data Quality Objectives outlined in the SWAMP QAMP, (Puckett, 2002). QA data are included in submission. All data are flagged as appropriate. |
QAPP Information Reference(s): |
|
Line of Evidence (LOE) for Decision ID 25492, pH
|
Region 3 |
San Antonio Creek (San Antonio Watershed, Rancho del las Flores Bridge at Hwy 135 to downstream at Railroad Bridge) |
|
|
LOE ID: |
11395 |
|
Pollutant: |
pH |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
None |
|
Beneficial Use: |
Agricultural Supply |
|
Number of Samples: |
30 |
Number of Exceedances: |
1 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Central Coast Regional Board Staff assessed CCAMP Santa Barbara (SantaBarb) data for San Antonio Creek (313) to determine beneficial use support and results are as follows: 1 of 30 samples exceed the criterion for pH. |
Data Reference: |
Final Data File used for assessment: CCAMP Water Quality Data_file1 |
|
Final Data File used for assessment: CCAMP Water Quality Data_file2 |
|
Final Data File used for assessment: CCAMP Water Quality Data_file3 |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
Waters shall not contain concentrations of chemical constituents in amounts which adversely affect the agricultural beneficial use. Interpretation of adverse effect shall be as derived from the University of California Agricultural Extension Service guidelines provided in Table 3-3 (Central Coast Waterboard Basin Plan, Chapter III, Section II.A.2 Objectives for all Inland and Surface Waters, Enclosed Bays and Estuaries). In Table 3-3 of the Basin Plan (page III-8), water quality guidelines state that severe problems may occur when pH is greater than 8.4 or less than 6.5 in irrigation supply water. |
Objective/Criterion Reference: |
Water Quality Control Plan (Basin Plan) - Central Coast Region (Region 3) |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
Data for this line of evidence for San Antonio Creek (313) was collected at 3 monitoring sites [ 313SAB-San Antonio Creek at Rancho de las Flores Bridge and Highway 135, 313SAE-San Antonio Creek at San Antonio Road East, 313SAI-San Antonio Creek at San Antonio Road West] |
Temporal Representation: |
Data was collected over the time period 1/18/2001-3/17/2002. Santa Barbara Coast is one of five annual rotation areas that are monitored for conventional pollutants by CCAMP staff monthly for one year. Toxicity monitoring is conducted twice during the rotation year (winter and summer) at a subset of sites. |
Environmental Conditions: |
Staff is not aware of any special conditions that might effect interpretation of the data. |
QAPP Information: |
All data was collected following the Standard Operating Procedures and Data Quality Objectives outlined in the SWAMP QAMP, (Puckett, 2002). QA data are included in submission. All data are flagged as appropriate. |
QAPP Information Reference(s): |
|
Line of Evidence (LOE) for Decision ID 25492, pH
|
Region 3 |
San Antonio Creek (San Antonio Watershed, Rancho del las Flores Bridge at Hwy 135 to downstream at Railroad Bridge) |
|
|
LOE ID: |
11413 |
|
Pollutant: |
pH |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
None |
|
Beneficial Use: |
Municipal & Domestic Supply |
|
Number of Samples: |
6 |
Number of Exceedances: |
1 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Central Coast Regional Board Staff assessed CCAMP Diurnal Dissolved Oxygen Sampling (DO) data for San Antonio Creek (313) to determine beneficial use support and results are as follows: 1 of 6 samples exceed the criterion for pH. |
Data Reference: |
Final Data File used for assessment: CCAMP Water Quality Data_file1 |
|
Final Data File used for assessment: CCAMP Water Quality Data_file2 |
|
Final Data File used for assessment: CCAMP Water Quality Data_file3 |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
The Water Quality Control Plan, Central Coast Basin, Section II.A.2. Municipal and Domestic Supply Objectives, Section II.A.2.a states the following: The pH value shall neither be depressed below 6.5 or raised above 8.3. |
Objective/Criterion Reference: |
Water Quality Control Plan (Basin Plan) - Central Coast Region (Region 3) |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
Data for this line of evidence for San Antonio Creek (313) was collected at 2 monitoring sites [ 313SAB-San Antonio Creek at Rancho de las Flores Bridge and Highway 135, 313SAI-San Antonio Creek at San Antonio Road West] |
Temporal Representation: |
Data was collected over the time period 7/18/2001-8/11/2006. Diurnal monitoring conducted in summer months at all CCAMP monitoring sites. |
Environmental Conditions: |
Staff is not aware of any special conditions that might effect interpretation of the data. |
QAPP Information: |
All data was collected following the Standard Operating Procedures and Data Quality Objectives outlined in the SWAMP QAMP, (Puckett, 2002). QA data are included in submission. All data are flagged as appropriate. |
QAPP Information Reference(s): |
|
Line of Evidence (LOE) for Decision ID 25492, pH
|
Region 3 |
San Antonio Creek (San Antonio Watershed, Rancho del las Flores Bridge at Hwy 135 to downstream at Railroad Bridge) |
|
|
LOE ID: |
11554 |
|
Pollutant: |
pH |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
None |
|
Beneficial Use: |
Warm Freshwater Habitat |
Aquatic Life Use: |
Warm Freshwater Habitat |
|
Number of Samples: |
30 |
Number of Exceedances: |
1 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Central Coast Regional Board Staff assessed CCAMP Santa Barbara (SantaBarb) data for San Antonio Creek (313) to determine beneficial use support and results are as follows: 1 of 30 samples exceed the criterion for pH. |
Data Reference: |
Final Data File used for assessment: CCAMP Water Quality Data_file1 |
|
Final Data File used for assessment: CCAMP Water Quality Data_file2 |
|
Final Data File used for assessment: CCAMP Water Quality Data_file3 |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
Water Quality Control Plan, Central Coast Basin, General Objective, Chapter III, Section II.A.2 General Objectives for all Inland Surface Waters, Enclosed Bays and Estuaries states the following: For waters not mentioned by a specific beneficial use, the pH value shall not be depressed below 7.0 or raised above 8.5. |
Objective/Criterion Reference: |
Water Quality Control Plan (Basin Plan) - Central Coast Region (Region 3) |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
Data for this line of evidence for San Antonio Creek (313) was collected at 3 monitoring sites [ 313SAB-San Antonio Creek at Rancho de las Flores Bridge and Highway 135, 313SAE-San Antonio Creek at San Antonio Road East, 313SAI-San Antonio Creek at San Antonio Road West] |
Temporal Representation: |
Data was collected over the time period 1/18/2001-3/17/2002. Santa Barbara Coast is one of five annual rotation areas that are monitored for conventional pollutants by CCAMP staff monthly for one year. Toxicity monitoring is conducted twice during the rotation year (winter and summer) at a subset of sites. |
Environmental Conditions: |
Staff is not aware of any special conditions that might effect interpretation of the data. |
QAPP Information: |
All data was collected following the Standard Operating Procedures and Data Quality Objectives outlined in the SWAMP QAMP, (Puckett, 2002). QA data are included in submission. All data are flagged as appropriate. |
QAPP Information Reference(s): |
|
Line of Evidence (LOE) for Decision ID 25492, pH
|
Region 3 |
San Antonio Creek (San Antonio Watershed, Rancho del las Flores Bridge at Hwy 135 to downstream at Railroad Bridge) |
|
|
LOE ID: |
11451 |
|
Pollutant: |
pH |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
None |
|
Beneficial Use: |
Non-Contact Recreation |
|
Number of Samples: |
57 |
Number of Exceedances: |
2 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Central Coast Regional Board Staff assessed CCAMP Coastal Confluences (CC) data for San Antonio Creek (313) to determine beneficial use support and results are as follows: 2 of 57 samples exceed the criterion for pH. |
Data Reference: |
Final Data File used for assessment: CCAMP Water Quality Data_file1 |
|
Final Data File used for assessment: CCAMP Water Quality Data_file2 |
|
Final Data File used for assessment: CCAMP Water Quality Data_file3 |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
The Water Quality Control Plan, Central Coast Basin objective for non-contact water recreation uses (Section II.A.2. Objectives for All Inland Surface Waters, Enclosed Bays, and Estuaries, II.A.2.a) states the following: pH value shall neither be depressed below 6.5 nor raised above 8.3. |
Objective/Criterion Reference: |
Water Quality Control Plan (Basin Plan) - Central Coast Region (Region 3) |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
Data for this line of evidence for San Antonio Creek (313) was collected at 2 monitoring sites [ 313SAC-San Antonio Creek at Rail Road Bridge, u/s lagoon , 313SAI-San Antonio Creek at San Antonio Road West] |
Temporal Representation: |
Data was collected over the time period 1/18/2001-12/6/2006. CCAMP Coastal confluence monitoring is conducted monthly (with the exception of April 2003 - December 2003) and is ongoing. |
Environmental Conditions: |
Staff is not aware of any special conditions that might effect interpretation of the data. |
QAPP Information: |
All data was collected following the Standard Operating Procedures and Data Quality Objectives outlined in the SWAMP QAMP, (Puckett, 2002). QA data are included in submission. All data are flagged as appropriate. |
QAPP Information Reference(s): |
|
Line of Evidence (LOE) for Decision ID 25492, pH
|
Region 3 |
San Antonio Creek (San Antonio Watershed, Rancho del las Flores Bridge at Hwy 135 to downstream at Railroad Bridge) |
|
|
LOE ID: |
11397 |
|
Pollutant: |
pH |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
None |
|
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: |
Central Coast Regional Board Staff assessed CCAMP Diurnal Dissolved Oxygen Sampling (DO) data for San Antonio Creek (313) to determine beneficial use support and results are as follows: 0 of 6 samples exceed the criterion for pH. |
Data Reference: |
Final Data File used for assessment: CCAMP Water Quality Data_file1 |
|
Final Data File used for assessment: CCAMP Water Quality Data_file2 |
|
Final Data File used for assessment: CCAMP Water Quality Data_file3 |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
Waters shall not contain concentrations of chemical constituents in amounts which adversely affect the agricultural beneficial use. Interpretation of adverse effect shall be as derived from the University of California Agricultural Extension Service guidelines provided in Table 3-3 (Central Coast Waterboard Basin Plan, Chapter III, Section II.A.2 Objectives for all Inland and Surface Waters, Enclosed Bays and Estuaries). In Table 3-3 of the Basin Plan (page III-8), water quality guidelines state that severe problems may occur when pH is greater than 8.4 or less than 6.5 in irrigation supply water. |
Objective/Criterion Reference: |
Water Quality Control Plan (Basin Plan) - Central Coast Region (Region 3) |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
Data for this line of evidence for San Antonio Creek (313) was collected at 2 monitoring sites [ 313SAB-San Antonio Creek at Rancho de las Flores Bridge and Highway 135, 313SAI-San Antonio Creek at San Antonio Road West] |
Temporal Representation: |
Data was collected over the time period 7/18/2001-8/11/2006. Diurnal monitoring conducted in summer months at all CCAMP monitoring sites. |
Environmental Conditions: |
Staff is not aware of any special conditions that might effect interpretation of the data. |
QAPP Information: |
All data was collected following the Standard Operating Procedures and Data Quality Objectives outlined in the SWAMP QAMP, (Puckett, 2002). QA data are included in submission. All data are flagged as appropriate. |
QAPP Information Reference(s): |
|
Line of Evidence (LOE) for Decision ID 25492, pH
|
Region 3 |
San Antonio Creek (San Antonio Watershed, Rancho del las Flores Bridge at Hwy 135 to downstream at Railroad Bridge) |
|
|
LOE ID: |
11415 |
|
Pollutant: |
pH |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
None |
|
Beneficial Use: |
Non-Contact Recreation |
|
Number of Samples: |
6 |
Number of Exceedances: |
1 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Central Coast Regional Board Staff assessed CCAMP Diurnal Dissolved Oxygen Sampling (DO) data for San Antonio Creek (313) to determine beneficial use support and results are as follows: 1 of 6 samples exceed the criterion for pH. |
Data Reference: |
Final Data File used for assessment: CCAMP Water Quality Data_file1 |
|
Final Data File used for assessment: CCAMP Water Quality Data_file2 |
|
Final Data File used for assessment: CCAMP Water Quality Data_file3 |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
The Water Quality Control Plan, Central Coast Basin objective for non-contact water recreation uses (Section II.A.2. Objectives for All Inland Surface Waters, Enclosed Bays, and Estuaries, II.A.2.a) states the following: pH value shall neither be depressed below 6.5 nor raised above 8.3. |
Objective/Criterion Reference: |
Water Quality Control Plan (Basin Plan) - Central Coast Region (Region 3) |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
Data for this line of evidence for San Antonio Creek (313) was collected at 2 monitoring sites [ 313SAB-San Antonio Creek at Rancho de las Flores Bridge and Highway 135, 313SAI-San Antonio Creek at San Antonio Road West] |
Temporal Representation: |
Data was collected over the time period 7/18/2001-8/11/2006. Diurnal monitoring conducted in summer months at all CCAMP monitoring sites. |
Environmental Conditions: |
Staff is not aware of any special conditions that might effect interpretation of the data. |
QAPP Information: |
All data was collected following the Standard Operating Procedures and Data Quality Objectives outlined in the SWAMP QAMP, (Puckett, 2002). QA data are included in submission. All data are flagged as appropriate. |
QAPP Information Reference(s): |
|
Line of Evidence (LOE) for Decision ID 25492, pH
|
Region 3 |
San Antonio Creek (San Antonio Watershed, Rancho del las Flores Bridge at Hwy 135 to downstream at Railroad Bridge) |
|
|
LOE ID: |
11537 |
|
Pollutant: |
pH |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
None |
|
Beneficial Use: |
Municipal & Domestic Supply |
|
Number of Samples: |
30 |
Number of Exceedances: |
1 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Central Coast Regional Board Staff assessed CCAMP Santa Barbara (SantaBarb) data for San Antonio Creek (313) to determine beneficial use support and results are as follows: 1 of 30 samples exceed the criterion for pH. |
Data Reference: |
Final Data File used for assessment: CCAMP Water Quality Data_file1 |
|
Final Data File used for assessment: CCAMP Water Quality Data_file2 |
|
Final Data File used for assessment: CCAMP Water Quality Data_file3 |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
The Water Quality Control Plan, Central Coast Basin, Section II.A.2. Municipal and Domestic Supply Objectives, Section II.A.2.a states the following: The pH value shall neither be depressed below 6.5 or raised above 8.3. |
Objective/Criterion Reference: |
Water Quality Control Plan (Basin Plan) - Central Coast Region (Region 3) |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
Data for this line of evidence for San Antonio Creek (313) was collected at 3 monitoring sites [ 313SAB-San Antonio Creek at Rancho de las Flores Bridge and Highway 135, 313SAE-San Antonio Creek at San Antonio Road East, 313SAI-San Antonio Creek at San Antonio Road West] |
Temporal Representation: |
Data was collected over the time period 1/18/2001-3/17/2002. Santa Barbara Coast is one of five annual rotation areas that are monitored for conventional pollutants by CCAMP staff monthly for one year. Toxicity monitoring is conducted twice during the rotation year (winter and summer) at a subset of sites. |
Environmental Conditions: |
Staff is not aware of any special conditions that might effect interpretation of the data. |
QAPP Information: |
All data was collected following the Standard Operating Procedures and Data Quality Objectives outlined in the SWAMP QAMP, (Puckett, 2002). QA data are included in submission. All data are flagged as appropriate. |
QAPP Information Reference(s): |
|
Line of Evidence (LOE) for Decision ID 25492, pH
|
Region 3 |
San Antonio Creek (San Antonio Watershed, Rancho del las Flores Bridge at Hwy 135 to downstream at Railroad Bridge) |
|
|
LOE ID: |
11536 |
|
Pollutant: |
pH |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
None |
|
Beneficial Use: |
Cold Freshwater Habitat |
Aquatic Life Use: |
Cold Freshwater Habitat |
|
Number of Samples: |
30 |
Number of Exceedances: |
1 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Central Coast Regional Board Staff assessed CCAMP Santa Barbara (SantaBarb) data for San Antonio Creek (313) to determine beneficial use support and results are as follows: 1 of 30 samples exceed the criterion for pH. |
Data Reference: |
Final Data File used for assessment: CCAMP Water Quality Data_file1 |
|
Final Data File used for assessment: CCAMP Water Quality Data_file2 |
|
Final Data File used for assessment: CCAMP Water Quality Data_file3 |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
Water Quality Control Plan, Central Coast Basin, General Objective, Chapter III, Section II.A.2 General Objectives for all Inland Surface Waters, Enclosed Bays and Estuaries states the following: For waters not mentioned by a specific beneficial use, the pH value shall not be depressed below 7.0 or raised above 8.5. |
Objective/Criterion Reference: |
Water Quality Control Plan (Basin Plan) - Central Coast Region (Region 3) |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
Data for this line of evidence for San Antonio Creek (313) was collected at 3 monitoring sites [ 313SAB-San Antonio Creek at Rancho de las Flores Bridge and Highway 135, 313SAE-San Antonio Creek at San Antonio Road East, 313SAI-San Antonio Creek at San Antonio Road West] |
Temporal Representation: |
Data was collected over the time period 1/18/2001-3/17/2002. Santa Barbara Coast is one of five annual rotation areas that are monitored for conventional pollutants by CCAMP staff monthly for one year. Toxicity monitoring is conducted twice during the rotation year (winter and summer) at a subset of sites. |
Environmental Conditions: |
Staff is not aware of any special conditions that might effect interpretation of the data. |
QAPP Information: |
All data was collected following the Standard Operating Procedures and Data Quality Objectives outlined in the SWAMP QAMP, (Puckett, 2002). QA data are included in submission. All data are flagged as appropriate. |
QAPP Information Reference(s): |
|
Line of Evidence (LOE) for Decision ID 25492, pH
|
Region 3 |
San Antonio Creek (San Antonio Watershed, Rancho del las Flores Bridge at Hwy 135 to downstream at Railroad Bridge) |
|
|
LOE ID: |
11552 |
|
Pollutant: |
pH |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
None |
|
Beneficial Use: |
Water Contact Recreation |
|
Number of Samples: |
30 |
Number of Exceedances: |
1 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Central Coast Regional Board Staff assessed CCAMP Santa Barbara (SantaBarb) data for San Antonio Creek (313) to determine beneficial use support and results are as follows: 1 of 30 samples exceed the criterion for pH. |
Data Reference: |
Final Data File used for assessment: CCAMP Water Quality Data_file1 |
|
Final Data File used for assessment: CCAMP Water Quality Data_file2 |
|
Final Data File used for assessment: CCAMP Water Quality Data_file3 |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
The Water Quality Control Plan, Central Coast Basin objective for water contact recreation uses (Section II.A.2. Objectives for All Inland Surface Waters, Enclosed Bays, and Estuaries, II.A.2.a) states the following: pH value shall neither be depressed below 6.5 nor raised above 8.3. |
Objective/Criterion Reference: |
Water Quality Control Plan (Basin Plan) - Central Coast Region (Region 3) |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
Data for this line of evidence for San Antonio Creek (313) was collected at 3 monitoring sites [ 313SAB-San Antonio Creek at Rancho de las Flores Bridge and Highway 135, 313SAE-San Antonio Creek at San Antonio Road East, 313SAI-San Antonio Creek at San Antonio Road West] |
Temporal Representation: |
Data was collected over the time period 1/18/2001-3/17/2002. Santa Barbara Coast is one of five annual rotation areas that are monitored for conventional pollutants by CCAMP staff monthly for one year. Toxicity monitoring is conducted twice during the rotation year (winter and summer) at a subset of sites. |
Environmental Conditions: |
Staff is not aware of any special conditions that might effect interpretation of the data. |
QAPP Information: |
All data was collected following the Standard Operating Procedures and Data Quality Objectives outlined in the SWAMP QAMP, (Puckett, 2002). QA data are included in submission. All data are flagged as appropriate. |
QAPP Information Reference(s): |
|
Line of Evidence (LOE) for Decision ID 25492, pH
|
Region 3 |
San Antonio Creek (San Antonio Watershed, Rancho del las Flores Bridge at Hwy 135 to downstream at Railroad Bridge) |
|
|
LOE ID: |
11412 |
|
Pollutant: |
pH |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
None |
|
Beneficial Use: |
Cold Freshwater Habitat |
Aquatic Life 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: |
Central Coast Regional Board Staff assessed CCAMP Diurnal Dissolved Oxygen Sampling (DO) data for San Antonio Creek (313) to determine beneficial use support and results are as follows: 0 of 6 samples exceed the criterion for pH. |
Data Reference: |
Final Data File used for assessment: CCAMP Water Quality Data_file1 |
|
Final Data File used for assessment: CCAMP Water Quality Data_file2 |
|
Final Data File used for assessment: CCAMP Water Quality Data_file3 |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
Water Quality Control Plan, Central Coast Basin, General Objective, Chapter III, Section II.A.2 General Objectives for all Inland Surface Waters, Enclosed Bays and Estuaries states the following: For waters not mentioned by a specific beneficial use, the pH value shall not be depressed below 7.0 or raised above 8.5. |
Objective/Criterion Reference: |
Water Quality Control Plan (Basin Plan) - Central Coast Region (Region 3) |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
Data for this line of evidence for San Antonio Creek (313) was collected at 2 monitoring sites [ 313SAB-San Antonio Creek at Rancho de las Flores Bridge and Highway 135, 313SAI-San Antonio Creek at San Antonio Road West] |
Temporal Representation: |
Data was collected over the time period 7/18/2001-8/11/2006. Diurnal monitoring conducted in summer months at all CCAMP monitoring sites. |
Environmental Conditions: |
Staff is not aware of any special conditions that might effect interpretation of the data. |
QAPP Information: |
All data was collected following the Standard Operating Procedures and Data Quality Objectives outlined in the SWAMP QAMP, (Puckett, 2002). QA data are included in submission. All data are flagged as appropriate. |
QAPP Information Reference(s): |
|
Line of Evidence (LOE) for Decision ID 25492, pH
|
Region 3 |
San Antonio Creek (San Antonio Watershed, Rancho del las Flores Bridge at Hwy 135 to downstream at Railroad Bridge) |
|
|
LOE ID: |
11448 |
|
Pollutant: |
pH |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
None |
|
Beneficial Use: |
Cold Freshwater Habitat |
Aquatic Life Use: |
Cold Freshwater Habitat |
|
Number of Samples: |
57 |
Number of Exceedances: |
6 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Central Coast Regional Board Staff assessed CCAMP Coastal Confluences (CC) data for San Antonio Creek (313) to determine beneficial use support and results are as follows: 6 of 57 samples exceed the criterion for pH. |
Data Reference: |
Final Data File used for assessment: CCAMP Water Quality Data_file1 |
|
Final Data File used for assessment: CCAMP Water Quality Data_file2 |
|
Final Data File used for assessment: CCAMP Water Quality Data_file3 |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
Water Quality Control Plan, Central Coast Basin, General Objective, Chapter III, Section II.A.2 General Objectives for all Inland Surface Waters, Enclosed Bays and Estuaries states the following: For waters not mentioned by a specific beneficial use, the pH value shall not be depressed below 7.0 or raised above 8.5. |
Objective/Criterion Reference: |
Water Quality Control Plan (Basin Plan) - Central Coast Region (Region 3) |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
Data for this line of evidence for San Antonio Creek (313) was collected at 2 monitoring sites [ 313SAC-San Antonio Creek at Rail Road Bridge, u/s lagoon , 313SAI-San Antonio Creek at San Antonio Road West] |
Temporal Representation: |
Data was collected over the time period 1/18/2001-12/6/2006. CCAMP Coastal confluence monitoring is conducted monthly (with the exception of April 2003 - December 2003) and is ongoing. |
Environmental Conditions: |
Staff is not aware of any special conditions that might effect interpretation of the data. |
QAPP Information: |
All data was collected following the Standard Operating Procedures and Data Quality Objectives outlined in the SWAMP QAMP, (Puckett, 2002). QA data are included in submission. All data are flagged as appropriate. |
QAPP Information Reference(s): |
|
Line of Evidence (LOE) for Decision ID 25492, pH
|
Region 3 |
San Antonio Creek (San Antonio Watershed, Rancho del las Flores Bridge at Hwy 135 to downstream at Railroad Bridge) |
|
|
LOE ID: |
11449 |
|
Pollutant: |
pH |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
None |
|
Beneficial Use: |
Municipal & Domestic Supply |
|
Number of Samples: |
57 |
Number of Exceedances: |
2 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Central Coast Regional Board Staff assessed CCAMP Coastal Confluences (CC) data for San Antonio Creek (313) to determine beneficial use support and results are as follows: 2 of 57 samples exceed the criterion for pH. |
Data Reference: |
Final Data File used for assessment: CCAMP Water Quality Data_file1 |
|
Final Data File used for assessment: CCAMP Water Quality Data_file2 |
|
Final Data File used for assessment: CCAMP Water Quality Data_file3 |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
The Water Quality Control Plan, Central Coast Basin, Section II.A.2. Municipal and Domestic Supply Objectives, Section II.A.2.a states the following: The pH value shall neither be depressed below 6.5 or raised above 8.3. |
Objective/Criterion Reference: |
Water Quality Control Plan (Basin Plan) - Central Coast Region (Region 3) |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
Data for this line of evidence for San Antonio Creek (313) was collected at 2 monitoring sites [ 313SAC-San Antonio Creek at Rail Road Bridge, u/s lagoon , 313SAI-San Antonio Creek at San Antonio Road West] |
Temporal Representation: |
Data was collected over the time period 1/18/2001-12/6/2006. CCAMP Coastal confluence monitoring is conducted monthly (with the exception of April 2003 - December 2003) and is ongoing. |
Environmental Conditions: |
Staff is not aware of any special conditions that might effect interpretation of the data. |
QAPP Information: |
All data was collected following the Standard Operating Procedures and Data Quality Objectives outlined in the SWAMP QAMP, (Puckett, 2002). QA data are included in submission. All data are flagged as appropriate. |
QAPP Information Reference(s): |
|
Line of Evidence (LOE) for Decision ID 25492, pH
|
Region 3 |
San Antonio Creek (San Antonio Watershed, Rancho del las Flores Bridge at Hwy 135 to downstream at Railroad Bridge) |
|
|
LOE ID: |
11553 |
|
Pollutant: |
pH |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
None |
|
Beneficial Use: |
Non-Contact Recreation |
|
Number of Samples: |
30 |
Number of Exceedances: |
1 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Central Coast Regional Board Staff assessed CCAMP Santa Barbara (SantaBarb) data for San Antonio Creek (313) to determine beneficial use support and results are as follows: 1 of 30 samples exceed the criterion for pH. |
Data Reference: |
Final Data File used for assessment: CCAMP Water Quality Data_file1 |
|
Final Data File used for assessment: CCAMP Water Quality Data_file2 |
|
Final Data File used for assessment: CCAMP Water Quality Data_file3 |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
The Water Quality Control Plan, Central Coast Basin objective for non-contact water recreation uses (Section II.A.2. Objectives for All Inland Surface Waters, Enclosed Bays, and Estuaries, II.A.2.a) states the following: pH value shall neither be depressed below 6.5 nor raised above 8.3. |
Objective/Criterion Reference: |
Water Quality Control Plan (Basin Plan) - Central Coast Region (Region 3) |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
Data for this line of evidence for San Antonio Creek (313) was collected at 3 monitoring sites [ 313SAB-San Antonio Creek at Rancho de las Flores Bridge and Highway 135, 313SAE-San Antonio Creek at San Antonio Road East, 313SAI-San Antonio Creek at San Antonio Road West] |
Temporal Representation: |
Data was collected over the time period 1/18/2001-3/17/2002. Santa Barbara Coast is one of five annual rotation areas that are monitored for conventional pollutants by CCAMP staff monthly for one year. Toxicity monitoring is conducted twice during the rotation year (winter and summer) at a subset of sites. |
Environmental Conditions: |
Staff is not aware of any special conditions that might effect interpretation of the data. |
QAPP Information: |
All data was collected following the Standard Operating Procedures and Data Quality Objectives outlined in the SWAMP QAMP, (Puckett, 2002). QA data are included in submission. All data are flagged as appropriate. |
QAPP Information Reference(s): |
|
Line of Evidence (LOE) for Decision ID 25492, pH
|
Region 3 |
San Antonio Creek (San Antonio Watershed, Rancho del las Flores Bridge at Hwy 135 to downstream at Railroad Bridge) |
|
|
LOE ID: |
11452 |
|
Pollutant: |
pH |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
None |
|
Beneficial Use: |
Warm Freshwater Habitat |
Aquatic Life Use: |
Warm Freshwater Habitat |
|
Number of Samples: |
57 |
Number of Exceedances: |
6 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Central Coast Regional Board Staff assessed CCAMP Coastal Confluences (CC) data for San Antonio Creek (313) to determine beneficial use support and results are as follows: 6 of 57 samples exceed the criterion for pH. |
Data Reference: |
Final Data File used for assessment: CCAMP Water Quality Data_file1 |
|
Final Data File used for assessment: CCAMP Water Quality Data_file2 |
|
Final Data File used for assessment: CCAMP Water Quality Data_file3 |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
Water Quality Control Plan, Central Coast Basin, General Objective, Chapter III, Section II.A.2 General Objectives for all Inland Surface Waters, Enclosed Bays and Estuaries states the following: For waters not mentioned by a specific beneficial use, the pH value shall not be depressed below 7.0 or raised above 8.5. |
Objective/Criterion Reference: |
Water Quality Control Plan (Basin Plan) - Central Coast Region (Region 3) |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
Data for this line of evidence for San Antonio Creek (313) was collected at 2 monitoring sites [ 313SAC-San Antonio Creek at Rail Road Bridge, u/s lagoon , 313SAI-San Antonio Creek at San Antonio Road West] |
Temporal Representation: |
Data was collected over the time period 1/18/2001-12/6/2006. CCAMP Coastal confluence monitoring is conducted monthly (with the exception of April 2003 - December 2003) and is ongoing. |
Environmental Conditions: |
Staff is not aware of any special conditions that might effect interpretation of the data. |
QAPP Information: |
All data was collected following the Standard Operating Procedures and Data Quality Objectives outlined in the SWAMP QAMP, (Puckett, 2002). QA data are included in submission. All data are flagged as appropriate. |
QAPP Information Reference(s): |
|
Line of Evidence (LOE) for Decision ID 25492, pH
|
Region 3 |
San Antonio Creek (San Antonio Watershed, Rancho del las Flores Bridge at Hwy 135 to downstream at Railroad Bridge) |
|
|
LOE ID: |
11433 |
|
Pollutant: |
pH |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
None |
|
Beneficial Use: |
Agricultural Supply |
|
Number of Samples: |
57 |
Number of Exceedances: |
1 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Central Coast Regional Board Staff assessed CCAMP Coastal Confluences (CC) data for San Antonio Creek (313) to determine beneficial use support and results are as follows: 1 of 57 samples exceed the criterion for pH. |
Data Reference: |
Final Data File used for assessment: CCAMP Water Quality Data_file1 |
|
Final Data File used for assessment: CCAMP Water Quality Data_file2 |
|
Final Data File used for assessment: CCAMP Water Quality Data_file3 |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
Waters shall not contain concentrations of chemical constituents in amounts which adversely affect the agricultural beneficial use. Interpretation of adverse effect shall be as derived from the University of California Agricultural Extension Service guidelines provided in Table 3-3 (Central Coast Waterboard Basin Plan, Chapter III, Section II.A.2 Objectives for all Inland and Surface Waters, Enclosed Bays and Estuaries). In Table 3-3 of the Basin Plan (page III-8), water quality guidelines state that severe problems may occur when pH is greater than 8.4 or less than 6.5 in irrigation supply water. |
Objective/Criterion Reference: |
Water Quality Control Plan (Basin Plan) - Central Coast Region (Region 3) |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
Data for this line of evidence for San Antonio Creek (313) was collected at 2 monitoring sites [ 313SAC-San Antonio Creek at Rail Road Bridge, u/s lagoon , 313SAI-San Antonio Creek at San Antonio Road West] |
Temporal Representation: |
Data was collected over the time period 1/18/2001-12/6/2006. CCAMP Coastal confluence monitoring is conducted monthly (with the exception of April 2003 - December 2003) and is ongoing. |
Environmental Conditions: |
Staff is not aware of any special conditions that might effect interpretation of the data. |
QAPP Information: |
All data was collected following the Standard Operating Procedures and Data Quality Objectives outlined in the SWAMP QAMP, (Puckett, 2002). QA data are included in submission. All data are flagged as appropriate. |
QAPP Information Reference(s): |
|
Line of Evidence (LOE) for Decision ID 25492, pH
|
Region 3 |
San Antonio Creek (San Antonio Watershed, Rancho del las Flores Bridge at Hwy 135 to downstream at Railroad Bridge) |
|
|
LOE ID: |
11414 |
|
Pollutant: |
pH |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
None |
|
Beneficial Use: |
Water Contact Recreation |
|
Number of Samples: |
6 |
Number of Exceedances: |
1 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Central Coast Regional Board Staff assessed CCAMP Diurnal Dissolved Oxygen Sampling (DO) data for San Antonio Creek (313) to determine beneficial use support and results are as follows: 1 of 6 samples exceed the criterion for pH. |
Data Reference: |
Final Data File used for assessment: CCAMP Water Quality Data_file1 |
|
Final Data File used for assessment: CCAMP Water Quality Data_file2 |
|
Final Data File used for assessment: CCAMP Water Quality Data_file3 |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
The Water Quality Control Plan, Central Coast Basin objective for water contact recreation uses (Section II.A.2. Objectives for All Inland Surface Waters, Enclosed Bays, and Estuaries, II.A.2.a) states the following: pH value shall neither be depressed below 6.5 nor raised above 8.3. |
Objective/Criterion Reference: |
Water Quality Control Plan (Basin Plan) - Central Coast Region (Region 3) |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
Data for this line of evidence for San Antonio Creek (313) was collected at 2 monitoring sites [ 313SAB-San Antonio Creek at Rancho de las Flores Bridge and Highway 135, 313SAI-San Antonio Creek at San Antonio Road West] |
Temporal Representation: |
Data was collected over the time period 7/18/2001-8/11/2006. Diurnal monitoring conducted in summer months at all CCAMP monitoring sites. |
Environmental Conditions: |
Staff is not aware of any special conditions that might effect interpretation of the data. |
QAPP Information: |
All data was collected following the Standard Operating Procedures and Data Quality Objectives outlined in the SWAMP QAMP, (Puckett, 2002). QA data are included in submission. All data are flagged as appropriate. |
QAPP Information Reference(s): |
|
Line of Evidence (LOE) for Decision ID 25492, pH
|
Region 3 |
San Antonio Creek (San Antonio Watershed, Rancho del las Flores Bridge at Hwy 135 to downstream at Railroad Bridge) |
|
|
LOE ID: |
11416 |
|
Pollutant: |
pH |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
None |
|
Beneficial Use: |
Warm Freshwater Habitat |
Aquatic Life 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: |
Central Coast Regional Board Staff assessed CCAMP Diurnal Dissolved Oxygen Sampling (DO) data for San Antonio Creek (313) to determine beneficial use support and results are as follows: 0 of 6 samples exceed the criterion for pH. |
Data Reference: |
Final Data File used for assessment: CCAMP Water Quality Data_file1 |
|
Final Data File used for assessment: CCAMP Water Quality Data_file2 |
|
Final Data File used for assessment: CCAMP Water Quality Data_file3 |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
Water Quality Control Plan, Central Coast Basin, General Objective, Chapter III, Section II.A.2 General Objectives for all Inland Surface Waters, Enclosed Bays and Estuaries states the following: For waters not mentioned by a specific beneficial use, the pH value shall not be depressed below 7.0 or raised above 8.5. |
Objective/Criterion Reference: |
Water Quality Control Plan (Basin Plan) - Central Coast Region (Region 3) |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
Data for this line of evidence for San Antonio Creek (313) was collected at 2 monitoring sites [ 313SAB-San Antonio Creek at Rancho de las Flores Bridge and Highway 135, 313SAI-San Antonio Creek at San Antonio Road West] |
Temporal Representation: |
Data was collected over the time period 7/18/2001-8/11/2006. Diurnal monitoring conducted in summer months at all CCAMP monitoring sites. |
Environmental Conditions: |
Staff is not aware of any special conditions that might effect interpretation of the data. |
QAPP Information: |
All data was collected following the Standard Operating Procedures and Data Quality Objectives outlined in the SWAMP QAMP, (Puckett, 2002). QA data are included in submission. All data are flagged as appropriate. |
QAPP Information Reference(s): |
|
Line of Evidence (LOE) for Decision ID 25492, pH
|
Region 3 |
San Antonio Creek (San Antonio Watershed, Rancho del las Flores Bridge at Hwy 135 to downstream at Railroad Bridge) |
|
|
LOE ID: |
11450 |
|
Pollutant: |
pH |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
None |
|
Beneficial Use: |
Water Contact Recreation |
|
Number of Samples: |
57 |
Number of Exceedances: |
2 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Central Coast Regional Board Staff assessed CCAMP Coastal Confluences (CC) data for San Antonio Creek (313) to determine beneficial use support and results are as follows: 2 of 57 samples exceed the criterion for pH. |
Data Reference: |
Final Data File used for assessment: CCAMP Water Quality Data_file1 |
|
Final Data File used for assessment: CCAMP Water Quality Data_file2 |
|
Final Data File used for assessment: CCAMP Water Quality Data_file3 |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
The Water Quality Control Plan, Central Coast Basin objective for water contact recreation uses (Section II.A.2. Objectives for All Inland Surface Waters, Enclosed Bays, and Estuaries, II.A.2.a) states the following: pH value shall neither be depressed below 6.5 nor raised above 8.3. |
Objective/Criterion Reference: |
Water Quality Control Plan (Basin Plan) - Central Coast Region (Region 3) |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
Data for this line of evidence for San Antonio Creek (313) was collected at 2 monitoring sites [ 313SAC-San Antonio Creek at Rail Road Bridge, u/s lagoon , 313SAI-San Antonio Creek at San Antonio Road West] |
Temporal Representation: |
Data was collected over the time period 1/18/2001-12/6/2006. CCAMP Coastal confluence monitoring is conducted monthly (with the exception of April 2003 - December 2003) and is ongoing. |
Environmental Conditions: |
Staff is not aware of any special conditions that might effect interpretation of the data. |
QAPP Information: |
All data was collected following the Standard Operating Procedures and Data Quality Objectives outlined in the SWAMP QAMP, (Puckett, 2002). QA data are included in submission. All data are flagged as appropriate. |
QAPP Information Reference(s): |
|
Line of Evidence (LOE) for Decision ID 25592, Ammonia (Unionized)
|
Region 3 |
San Antonio Creek (San Antonio Watershed, Rancho del las Flores Bridge at Hwy 135 to downstream at Railroad Bridge) |
|
|
LOE ID: |
9694 |
|
Pollutant: |
Ammonia (Unionized) |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
None |
|
Beneficial Use: |
Warm Freshwater Habitat |
Aquatic Life Use: |
Warm Freshwater Habitat |
|
Number of Samples: |
56 |
Number of Exceedances: |
9 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Central Coast Regional Board Staff assessed CCAMP Coastal Confluences (CC) data for San Antonio Creek (313) to determine beneficial use support and results are as follows: 9 of 56 samples exceed the criterion for Ammonia as N, Unionized. |
Data Reference: |
Final Data File used for assessment: CCAMP Water Quality Data_file1 |
|
Final Data File used for assessment: CCAMP Water Quality Data_file2 |
|
Final Data File used for assessment: CCAMP Water Quality Data_file3 |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
Water Quality Control Plan, Central Coast Basin General Objective, Chapter III, Section II.A.2 (General Objectives for all Inland Surface Waters, Enclosed Bays and Estuaries) states that the discharge of wastes shall not cause concentrations of unionized ammonia (NH3) to exceed 0.025 mg/l (as N) in receiving waters (page III-4) . |
Objective/Criterion Reference: |
Water Quality Control Plan (Basin Plan) - Central Coast Region (Region 3) |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
Data for this line of evidence for San Antonio Creek (313) was collected at 2 monitoring sites [ 313SAC-San Antonio Creek at Rail Road Bridge, u/s lagoon , 313SAI-San Antonio Creek at San Antonio Road West] |
Temporal Representation: |
Data was collected over the time period 1/18/2001-12/6/2006. CCAMP Coastal confluence monitoring is conducted monthly (with the exception of April 2003 - December 2003) and is ongoing. |
Environmental Conditions: |
Staff is not aware of any special conditions that might effect interpretation of the data. |
QAPP Information: |
All data was collected following the Standard Operating Procedures and Data Quality Objectives outlined in the SWAMP QAMP, (Puckett, 2002). QA data are included in submission. All data are flagged as appropriate. |
QAPP Information Reference(s): |
|
Line of Evidence (LOE) for Decision ID 25592, Ammonia (Unionized)
|
Region 3 |
San Antonio Creek (San Antonio Watershed, Rancho del las Flores Bridge at Hwy 135 to downstream at Railroad Bridge) |
|
|
LOE ID: |
9693 |
|
Pollutant: |
Ammonia (Unionized) |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
None |
|
Beneficial Use: |
Cold Freshwater Habitat |
Aquatic Life Use: |
Cold Freshwater Habitat |
|
Number of Samples: |
56 |
Number of Exceedances: |
9 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Central Coast Regional Board Staff assessed CCAMP Coastal Confluences (CC) data for San Antonio Creek (313) to determine beneficial use support and results are as follows: 9 of 56 samples exceed the criterion for Ammonia as N, Unionized. |
Data Reference: |
Final Data File used for assessment: CCAMP Water Quality Data_file1 |
|
Final Data File used for assessment: CCAMP Water Quality Data_file2 |
|
Final Data File used for assessment: CCAMP Water Quality Data_file3 |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
Water Quality Control Plan, Central Coast Basin General Objective, Chapter III, Section II.A.2 (General Objectives for all Inland Surface Waters, Enclosed Bays and Estuaries) states that the discharge of wastes shall not cause concentrations of unionized ammonia (NH3) to exceed 0.025 mg/l (as N) in receiving waters (page III-4) . |
Objective/Criterion Reference: |
Water Quality Control Plan (Basin Plan) - Central Coast Region (Region 3) |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
Data for this line of evidence for San Antonio Creek (313) was collected at 2 monitoring sites [ 313SAC-San Antonio Creek at Rail Road Bridge, u/s lagoon , 313SAI-San Antonio Creek at San Antonio Road West]. |
Temporal Representation: |
Data was collected over the time period 1/18/2001-12/6/2006. CCAMP Coastal confluence monitoring is conducted monthly (with the exception of April 2003 - December 2003) and is ongoing. |
Environmental Conditions: |
Staff is not aware of any special conditions that might effect interpretation of the data. |
QAPP Information: |
All data was collected following the Standard Operating Procedures and Data Quality Objectives outlined in the SWAMP QAMP, (Puckett, 2002). QA data are included in submission. All data are flagged as appropriate. |
QAPP Information Reference(s): |
|
Line of Evidence (LOE) for Decision ID 25592, Ammonia (Unionized)
|
Region 3 |
San Antonio Creek (San Antonio Watershed, Rancho del las Flores Bridge at Hwy 135 to downstream at Railroad Bridge) |
|
|
LOE ID: |
9660 |
|
Pollutant: |
Ammonia (Unionized) |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
None |
|
Beneficial Use: |
Warm Freshwater Habitat |
Aquatic Life Use: |
Warm Freshwater Habitat |
|
Number of Samples: |
30 |
Number of Exceedances: |
7 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Central Coast Regional Board Staff assessed CCAMP Santa Barbara (SantaBarb) data for San Antonio Creek (313) to determine beneficial use support and results are as follows: 7 of 30 samples exceed the criterion for Ammonia as N, Unionized. |
Data Reference: |
Final Data File used for assessment: CCAMP Water Quality Data_file1 |
|
Final Data File used for assessment: CCAMP Water Quality Data_file2 |
|
Final Data File used for assessment: CCAMP Water Quality Data_file3 |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
Water Quality Control Plan, Central Coast Basin General Objective, Chapter III, Section II.A.2 (General Objectives for all Inland Surface Waters, Enclosed Bays and Estuaries) states that the discharge of wastes shall not cause concentrations of unionized ammonia (NH3) to exceed 0.025 mg/l (as N) in receiving waters (page III-4) . |
Objective/Criterion Reference: |
Water Quality Control Plan (Basin Plan) - Central Coast Region (Region 3) |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
Data for this line of evidence for San Antonio Creek (313) was collected at 3 monitoring sites [ 313SAB-San Antonio Creek at Rancho de las Flores Bridge and Highway 135, 313SAE-San Antonio Creek at San Antonio Road East, 313SAI-San Antonio Creek at San Antonio Road West]. |
Temporal Representation: |
Data was collected over the time period 1/18/2001-3/17/2002. Santa Barbara Coast is one of five annual rotation areas that are monitored for conventional pollutants by CCAMP staff monthly for one year. |
Environmental Conditions: |
Staff is not aware of any special conditions that might effect interpretation of the data. |
QAPP Information: |
All data was collected following the Standard Operating Procedures and Data Quality Objectives outlined in the SWAMP QAMP, (Puckett, 2002). QA data are included in submission. All data are flagged as appropriate. |
QAPP Information Reference(s): |
|
Line of Evidence (LOE) for Decision ID 25592, Ammonia (Unionized)
|
Region 3 |
San Antonio Creek (San Antonio Watershed, Rancho del las Flores Bridge at Hwy 135 to downstream at Railroad Bridge) |
|
|
LOE ID: |
9647 |
|
Pollutant: |
Ammonia (Unionized) |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
None |
|
Beneficial Use: |
Cold Freshwater Habitat |
Aquatic Life Use: |
Cold Freshwater Habitat |
|
Number of Samples: |
30 |
Number of Exceedances: |
7 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Central Coast Regional Board Staff assessed CCAMP Santa Barbara (SantaBarb) data for San Antonio Creek (313) to determine beneficial use support and results are as follows: 7 of 30 samples exceed the criterion for Ammonia as N, Unionized. |
Data Reference: |
Final Data File used for assessment: CCAMP Water Quality Data_file1 |
|
Final Data File used for assessment: CCAMP Water Quality Data_file2 |
|
Final Data File used for assessment: CCAMP Water Quality Data_file3 |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
Water Quality Control Plan, Central Coast Basin General Objective, Chapter III, Section II.A.2 (General Objectives for all Inland Surface Waters, Enclosed Bays and Estuaries) states that the discharge of wastes shall not cause concentrations of unionized ammonia (NH3) to exceed 0.025 mg/l (as N) in receiving waters (page III-4) . |
Objective/Criterion Reference: |
Water Quality Control Plan (Basin Plan) - Central Coast Region (Region 3) |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
Data for this line of evidence for San Antonio Creek (313) was collected at 3 monitoring sites [ 313SAB-San Antonio Creek at Rancho de las Flores Bridge and Highway 135, 313SAE-San Antonio Creek at San Antonio Road East, 313SAI-San Antonio Creek at San Antonio Road West]. |
Temporal Representation: |
Data was collected over the time period 1/18/2001-3/17/2002. Santa Barbara Coast is one of five annual rotation areas that are monitored for conventional pollutants by CCAMP staff monthly for one year. |
Environmental Conditions: |
Staff is not aware of any special conditions that might effect interpretation of the data. |
QAPP Information: |
All data was collected following the Standard Operating Procedures and Data Quality Objectives outlined in the SWAMP QAMP, (Puckett, 2002). QA data are included in submission. All data are flagged as appropriate. |
QAPP Information Reference(s): |
|
Line of Evidence (LOE) for Decision ID 25218, Chlorpyrifos
|
Region 3 |
San Antonio Creek (San Antonio Watershed, Rancho del las Flores Bridge at Hwy 135 to downstream at Railroad Bridge) |
|
|
LOE ID: |
16053 |
|
Pollutant: |
Chlorpyrifos |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
None |
|
Beneficial Use: |
Cold Freshwater Habitat |
Aquatic Life Use: |
Cold Freshwater Habitat |
|
Number of Samples: |
1 |
Number of Exceedances: |
1 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Central Coast Regional Board Staff assessed CCAMP_SWAMP Monitoring (03SW3001) data for San Antonio Creek (313) to determine beneficial use support and results are as follows: 1 of 1 samples exceed the criterion for Chlorpyrifos. |
Data Reference: |
Final Data File used for assessment: SWAMP Toxicity Data 2001-06 |
|
Final Data File used for assessment: SWAMP Sediment Chemistry Data from Region 3 Harbors, 2004
|
|
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. (Water Quality Control Plan, Central Coast Basin, Chapter III, Section II.A.2 Objectives for all Inland Surface Waters, Enclosed Bays and Estuaries). |
Objective/Criterion 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 |
|
Water Quality Control Plan (Basin Plan) - Central Coast Region (Region 3) |
|
Evaluation Guideline: |
One hour average maximum concentration 0.025 ug/L as stated in Sipmann 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 for this line of evidence for San Antonio Creek (313) was collected at 1 monitoring site [ 313SAI-San Antonio Creek at San Antonio Road West] |
Temporal Representation: |
Data was collected on a single day 3/31/2004. SWAMP toxicity monitoring includes both water samples (collected in both winter and summer) and sediment samples (collected in spring). |
Environmental Conditions: |
Staff is not aware of any special conditions that might effect interpretation of the data. |
QAPP Information: |
All data was collected following the Standard Operating Procedures and Data Quality Objectives outlined in the SWAMP QAMP, (Puckett, 2002). QA data are included in submission. All data are flagged as appropriate. |
QAPP Information Reference(s): |
|
Line of Evidence (LOE) for Decision ID 25218, Chlorpyrifos
|
Region 3 |
San Antonio Creek (San Antonio Watershed, Rancho del las Flores Bridge at Hwy 135 to downstream at Railroad Bridge) |
|
|
LOE ID: |
16277 |
|
Pollutant: |
Chlorpyrifos |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
None |
|
Beneficial Use: |
Warm Freshwater Habitat |
Aquatic Life Use: |
Warm Freshwater Habitat |
|
Number of Samples: |
8 |
Number of Exceedances: |
1 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Central Coast Regional Board Staff assessed CCAMP_SWAMP Monitoring (00SW3001) data for San Antonio Creek (313) to determine beneficial use support and results are as follows: 1 of 8 samples exceed the criterion for Chlorpyrifos. |
Data Reference: |
Final Data File used for assessment: SWAMP Toxicity Data 2001-06 |
|
Final Data File used for assessment: SWAMP Sediment Chemistry Data from Region 3 Harbors, 2004
|
|
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. (Water Quality Control Plan, Central Coast Basin, Chapter III, Section II.A.2 Objectives for all Inland Surface Waters, Enclosed Bays and Estuaries). |
Objective/Criterion 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 |
|
Water Quality Control Plan (Basin Plan) - Central Coast Region (Region 3) |
|
Evaluation Guideline: |
One hour average maximum concentration 0.025 ug/L as stated in Sipmann 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 for this line of evidence for San Antonio Creek (313) was collected at 3 monitoring sites [ 313SAB-San Antonio Creek at Rancho de las Flores Bridge and Highway 135, 313SAC-San Antonio Creek at Rail Road Bridge, u/s lagoon , 313SAI-San Antonio Creek at San Antonio Road West] |
Temporal Representation: |
Data was collected over the time period 12/10/2001-3/17/2002. SWAMP toxicity monitoring includes both water samples (collected in both winter and summer) and sediment samples (collected in spring). |
Environmental Conditions: |
Staff is not aware of any special conditions that might effect interpretation of the data. |
QAPP Information: |
All data was collected following the Standard Operating Procedures and Data Quality Objectives outlined in the SWAMP QAMP, (Puckett, 2002). QA data are included in submission. All data are flagged as appropriate. |
QAPP Information Reference(s): |
|
Line of Evidence (LOE) for Decision ID 25218, Chlorpyrifos
|
Region 3 |
San Antonio Creek (San Antonio Watershed, Rancho del las Flores Bridge at Hwy 135 to downstream at Railroad Bridge) |
|
|
LOE ID: |
16276 |
|
Pollutant: |
Chlorpyrifos |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
None |
|
Beneficial Use: |
Cold Freshwater Habitat |
Aquatic Life Use: |
Cold Freshwater Habitat |
|
Number of Samples: |
8 |
Number of Exceedances: |
1 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Central Coast Regional Board Staff assessed CCAMP_SWAMP Monitoring (00SW3001) data for San Antonio Creek (313) to determine beneficial use support and results are as follows: 1 of 8 samples exceed the criterion for Chlorpyrifos. |
Data Reference: |
Final Data File used for assessment: SWAMP Toxicity Data 2001-06 |
|
Final Data File used for assessment: SWAMP Sediment Chemistry Data from Region 3 Harbors, 2004
|
|
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. (Water Quality Control Plan, Central Coast Basin, Chapter III, Section II.A.2 Objectives for all Inland Surface Waters, Enclosed Bays and Estuaries). |
Objective/Criterion 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 |
|
Water Quality Control Plan (Basin Plan) - Central Coast Region (Region 3) |
|
Evaluation Guideline: |
One hour average maximum concentration 0.025 ug/L as stated in Sipmann 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 for this line of evidence for San Antonio Creek (313) was collected at 3 monitoring sites [ 313SAB-San Antonio Creek at Rancho de las Flores Bridge and Highway 135, 313SAC-San Antonio Creek at Rail Road Bridge, u/s lagoon , 313SAI-San Antonio Creek at San Antonio Road West] |
Temporal Representation: |
Data was collected over the time period 12/10/2001-3/17/2002. SWAMP toxicity monitoring includes both water samples (collected in both winter and summer) and sediment samples (collected in spring). |
Environmental Conditions: |
Staff is not aware of any special conditions that might effect interpretation of the data. |
QAPP Information: |
All data was collected following the Standard Operating Procedures and Data Quality Objectives outlined in the SWAMP QAMP, (Puckett, 2002). QA data are included in submission. All data are flagged as appropriate. |
QAPP Information Reference(s): |
|
Line of Evidence (LOE) for Decision ID 25218, Chlorpyrifos
|
Region 3 |
San Antonio Creek (San Antonio Watershed, Rancho del las Flores Bridge at Hwy 135 to downstream at Railroad Bridge) |
|
|
LOE ID: |
16054 |
|
Pollutant: |
Chlorpyrifos |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
None |
|
Beneficial Use: |
Warm Freshwater Habitat |
Aquatic Life 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: |
Central Coast Regional Board Staff assessed CCAMP_SWAMP Monitoring (03SW3001) data for San Antonio Creek (313) to determine beneficial use support and results are as follows: 1 of 1 samples exceed the criterion for Chlorpyrifos. |
Data Reference: |
Final Data File used for assessment: SWAMP Toxicity Data 2001-06 |
|
Final Data File used for assessment: SWAMP Sediment Chemistry Data from Region 3 Harbors, 2004
|
|
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. (Water Quality Control Plan, Central Coast Basin, Chapter III, Section II.A.2 Objectives for all Inland Surface Waters, Enclosed Bays and Estuaries). |
Objective/Criterion 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 |
|
Water Quality Control Plan (Basin Plan) - Central Coast Region (Region 3) |
|
Evaluation Guideline: |
One hour average maximum concentration 0.025 ug/L as stated in Sipmann 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 for this line of evidence for San Antonio Creek (313) was collected at 1 monitoring site [ 313SAI-San Antonio Creek at San Antonio Road West] |
Temporal Representation: |
Data was collected on a single day 3/31/2004. SWAMP toxicity monitoring includes both water samples (collected in both winter and summer) and sediment samples (collected in spring). |
Environmental Conditions: |
Staff is not aware of any special conditions that might effect interpretation of the data. |
QAPP Information: |
All data was collected following the Standard Operating Procedures and Data Quality Objectives outlined in the SWAMP QAMP, (Puckett, 2002). QA data are included in submission. All data are flagged as appropriate. |
QAPP Information Reference(s): |
|
Line of Evidence (LOE) for Decision ID 25644, Fecal Coliform
|
Region 3 |
San Antonio Creek (San Antonio Watershed, Rancho del las Flores Bridge at Hwy 135 to downstream at Railroad Bridge) |
|
|
LOE ID: |
11378 |
|
Pollutant: |
Fecal Coliform |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
None |
|
Beneficial Use: |
Water Contact Recreation |
|
Number of Samples: |
29 |
Number of Exceedances: |
13 |
|
Data and Information Type: |
PATHOGEN MONITORING |
Data Used to Assess Water Quality: |
Central Coast Regional Board Staff assessed CCAMP Santa Barbara (SantaBarb) data for San Antonio Creek (313) to determine beneficial use support and results are as follows: 13 of 29 samples exceed the criterion for Coliform, Fecal. |
Data Reference: |
Final Data File used for assessment: CCAMP Water Quality Data_file1 |
|
Final Data File used for assessment: CCAMP Water Quality Data_file2 |
|
Final Data File used for assessment: CCAMP Water Quality Data_file3 |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
The Water Quality Control Plan, Central Coast Basin objective for water contact recreation uses (Section II.A.2. Objectives for All Inland Surface Waters, Enclosed Bays, and Estuaries, II.A.2.a) states the following: Fecal coliform concentration, based on a minimum of not less than five samples for any 30-day period, shall not exceed a log mean of 200 MPN/100 ml, nor shall more than ten percent of total samples during any 30-day period exceed 400 MPN/100 ml. |
Objective/Criterion Reference: |
Water Quality Control Plan (Basin Plan) - Central Coast Region (Region 3) |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
Data for this line of evidence for San Antonio Creek (313) was collected at 3 monitoring sites [ 313SAB-San Antonio Creek at Rancho de las Flores Bridge and Highway 135, 313SAE-San Antonio Creek at San Antonio Road East, 313SAI-San Antonio Creek at San Antonio Road West] |
Temporal Representation: |
Data was collected over the time period 12/10/2000-3/11/2002. Santa Barbara Coast is one of five annual rotation areas that are monitored for conventional pollutants by CCAMP staff monthly for one year. Toxicity monitoring is conducted twice during the rotation year (winter and summer) at a subset of sites. |
Environmental Conditions: |
Staff is not aware of any special conditions that might effect interpretation of the data. |
QAPP Information: |
All data was collected following the Standard Operating Procedures and Data Quality Objectives outlined in the SWAMP QAMP, (Puckett, 2002). QA data are included in submission. All data are flagged as appropriate. |
QAPP Information Reference(s): |
|
Line of Evidence (LOE) for Decision ID 25644, Fecal Coliform
|
Region 3 |
San Antonio Creek (San Antonio Watershed, Rancho del las Flores Bridge at Hwy 135 to downstream at Railroad Bridge) |
|
|
LOE ID: |
11379 |
|
Pollutant: |
Fecal Coliform |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
None |
|
Beneficial Use: |
Non-Contact Recreation |
|
Number of Samples: |
29 |
Number of Exceedances: |
3 |
|
Data and Information Type: |
PATHOGEN MONITORING |
Data Used to Assess Water Quality: |
Central Coast Regional Board Staff assessed CCAMP Santa Barbara (SantaBarb) data for San Antonio Creek (313) to determine beneficial use support and results are as follows: 3 of 29 samples exceed the criterion for Coliform, Fecal. |
Data Reference: |
Final Data File used for assessment: CCAMP Water Quality Data_file1 |
|
Final Data File used for assessment: CCAMP Water Quality Data_file2 |
|
Final Data File used for assessment: CCAMP Water Quality Data_file3 |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
The Water Quality Control Plan, Central Coast Basin objective for non-contact water recreation uses (Section II.A.2. Objectives for All Inland Surface Waters, Enclosed Bays, and Estuaries, II.A.2.a) states the following: Fecal coliform concentration, based on a minimum of not less than five samples for any 30-day period, shall not exceed a log mean of 2000/100 ml, nor shall more than ten percent of samples collected during any 30-day period exceed 4000/100 ml. |
Objective/Criterion Reference: |
Water Quality Control Plan (Basin Plan) - Central Coast Region (Region 3) |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
Data for this line of evidence for San Antonio Creek (313) was collected at 3 monitoring sites [ 313SAB-San Antonio Creek at Rancho de las Flores Bridge and Highway 135, 313SAE-San Antonio Creek at San Antonio Road East, 313SAI-San Antonio Creek at San Antonio Road West] |
Temporal Representation: |
Data was collected over the time period 12/10/2000-3/11/2002. Santa Barbara Coast is one of five annual rotation areas that are monitored for conventional pollutants by CCAMP staff monthly for one year. Toxicity monitoring is conducted twice during the rotation year (winter and summer) at a subset of sites. |
Environmental Conditions: |
Staff is not aware of any special conditions that might effect interpretation of the data. |
QAPP Information: |
All data was collected following the Standard Operating Procedures and Data Quality Objectives outlined in the SWAMP QAMP, (Puckett, 2002). QA data are included in submission. All data are flagged as appropriate. |
QAPP Information Reference(s): |
|
Line of Evidence (LOE) for Decision ID 25644, Fecal Coliform
|
Region 3 |
San Antonio Creek (San Antonio Watershed, Rancho del las Flores Bridge at Hwy 135 to downstream at Railroad Bridge) |
|
|
LOE ID: |
11430 |
|
Pollutant: |
Fecal Coliform |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
None |
|
Beneficial Use: |
Water Contact Recreation |
|
Number of Samples: |
55 |
Number of Exceedances: |
12 |
|
Data and Information Type: |
PATHOGEN MONITORING |
Data Used to Assess Water Quality: |
Central Coast Regional Board Staff assessed CCAMP Coastal Confluences (CC) data for San Antonio Creek (313) to determine beneficial use support and results are as follows: 12 of 55 samples exceed the criterion for Coliform, Fecal. |
Data Reference: |
Final Data File used for assessment: CCAMP Water Quality Data_file1 |
|
Final Data File used for assessment: CCAMP Water Quality Data_file2 |
|
Final Data File used for assessment: CCAMP Water Quality Data_file3 |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
The Water Quality Control Plan, Central Coast Basin objective for water contact recreation uses (Section II.A.2. Objectives for All Inland Surface Waters, Enclosed Bays, and Estuaries, II.A.2.a) states the following: Fecal coliform concentration, based on a minimum of not less than five samples for any 30-day period, shall not exceed a log mean of 200 MPN/100 ml, nor shall more than ten percent of total samples during any 30-day period exceed 400 MPN/100 ml. |
Objective/Criterion Reference: |
Water Quality Control Plan (Basin Plan) - Central Coast Region (Region 3) |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
Data for this line of evidence for San Antonio Creek (313) was collected at 2 monitoring sites [ 313SAC-San Antonio Creek at Rail Road Bridge, u/s lagoon , 313SAI-San Antonio Creek at San Antonio Road West] |
Temporal Representation: |
Data was collected over the time period 1/18/2001-12/6/2006. CCAMP Coastal confluence monitoring is conducted monthly (with the exception of April 2003 - December 2003) and is ongoing. |
Environmental Conditions: |
Staff is not aware of any special conditions that might effect interpretation of the data. |
QAPP Information: |
All data was collected following the Standard Operating Procedures and Data Quality Objectives outlined in the SWAMP QAMP, (Puckett, 2002). QA data are included in submission. All data are flagged as appropriate. |
QAPP Information Reference(s): |
|
Line of Evidence (LOE) for Decision ID 25644, Fecal Coliform
|
Region 3 |
San Antonio Creek (San Antonio Watershed, Rancho del las Flores Bridge at Hwy 135 to downstream at Railroad Bridge) |
|
|
LOE ID: |
11431 |
|
Pollutant: |
Fecal Coliform |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
None |
|
Beneficial Use: |
Non-Contact Recreation |
|
Number of Samples: |
55 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PATHOGEN MONITORING |
Data Used to Assess Water Quality: |
Central Coast Regional Board Staff assessed CCAMP Coastal Confluences (CC) data for San Antonio Creek (313) to determine beneficial use support and results are as follows: 0 of 55 samples exceed the criterion for Coliform, Fecal. |
Data Reference: |
Final Data File used for assessment: CCAMP Water Quality Data_file1 |
|
Final Data File used for assessment: CCAMP Water Quality Data_file2 |
|
Final Data File used for assessment: CCAMP Water Quality Data_file3 |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
The Water Quality Control Plan, Central Coast Basin objective for non-contact water recreation uses (Section II.A.2. Objectives for All Inland Surface Waters, Enclosed Bays, and Estuaries, II.A.2.a) states the following: Fecal coliform concentration, based on a minimum of not less than five samples for any 30-day period, shall not exceed a log mean of 2000/100 ml, nor shall more than ten percent of samples collected during any 30-day period exceed 4000/100 ml. |
Objective/Criterion Reference: |
Water Quality Control Plan (Basin Plan) - Central Coast Region (Region 3) |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
Data for this line of evidence for San Antonio Creek (313) was collected at 2 monitoring sites [ 313SAC-San Antonio Creek at Rail Road Bridge, u/s lagoon , 313SAI-San Antonio Creek at San Antonio Road West] |
Temporal Representation: |
Data was collected over the time period 1/18/2001-12/6/2006. CCAMP Coastal confluence monitoring is conducted monthly (with the exception of April 2003 - December 2003) and is ongoing. |
Environmental Conditions: |
Staff is not aware of any special conditions that might effect interpretation of the data. |
QAPP Information: |
All data was collected following the Standard Operating Procedures and Data Quality Objectives outlined in the SWAMP QAMP, (Puckett, 2002). QA data are included in submission. All data are flagged as appropriate. |
QAPP Information Reference(s): |
|
Line of Evidence (LOE) for Decision ID 25353, Low Dissolved Oxygen
|
Region 3 |
San Antonio Creek (San Antonio Watershed, Rancho del las Flores Bridge at Hwy 135 to downstream at Railroad Bridge) |
|
|
LOE ID: |
13293 |
|
Pollutant: |
Oxygen, Dissolved |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Dissolved |
|
Beneficial Use: |
Warm Freshwater Habitat |
Aquatic Life Use: |
Warm Freshwater Habitat |
|
Number of Samples: |
57 |
Number of Exceedances: |
6 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Central Coast Regional Board Staff assessed CCAMP Coastal Confluences (CC) data for San Antonio Creek (313) to determine beneficial use support and results are as follows: 6 of 57 samples exceed the criterion for Oxygen, Dissolved. |
Data Reference: |
Final Data File used for assessment: CCAMP Water Quality Data_file1 |
|
Final Data File used for assessment: CCAMP Water Quality Data_file2 |
|
Final Data File used for assessment: CCAMP Water Quality Data_file3 |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
Water Quality Control Plan, Central Coast Basin, General Objective, Chapter III, Section II.A.2 General Objectives for all Inland Surface Waters, Enclosed Bays and Estuaries states the following: For waters not mentioned by a specific beneficial use, dissolved oxygen concentration shall not be reduced below 5.0 mg/l at any time. |
Objective/Criterion Reference: |
Water Quality Control Plan (Basin Plan) - Central Coast Region (Region 3) |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
Data for this line of evidence for San Antonio Creek (313) was collected at 2 monitoring sites [ 313SAC-San Antonio Creek at Rail Road Bridge, u/s lagoon , 313SAI-San Antonio Creek at San Antonio Road West] |
Temporal Representation: |
Data was collected over the time period 1/18/2001-12/6/2006. CCAMP Coastal confluence monitoring is conducted monthly (with the exception of April 2003 - December 2003) and is ongoing. |
Environmental Conditions: |
Staff is not aware of any special conditions that might effect interpretation of the data. |
QAPP Information: |
All data was collected following the Standard Operating Procedures and Data Quality Objectives outlined in the SWAMP QAMP, (Puckett, 2002). QA data are included in submission. All data are flagged as appropriate. |
QAPP Information Reference(s): |
|
Line of Evidence (LOE) for Decision ID 25353, Low Dissolved Oxygen
|
Region 3 |
San Antonio Creek (San Antonio Watershed, Rancho del las Flores Bridge at Hwy 135 to downstream at Railroad Bridge) |
|
|
LOE ID: |
13256 |
|
Pollutant: |
Oxygen, Dissolved |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Dissolved |
|
Beneficial Use: |
Cold Freshwater Habitat |
Aquatic Life Use: |
Cold Freshwater Habitat |
|
Number of Samples: |
8 |
Number of Exceedances: |
4 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Central Coast Regional Board Staff assessed CCAMP Diurnal Dissolved Oxygen Sampling (DO) data for San Antonio Creek (313) to determine beneficial use support and results are as follows: 4 of 8 samples exceed the criterion for Oxygen, Dissolved. |
Data Reference: |
Final Data File used for assessment: CCAMP Water Quality Data_file1 |
|
Final Data File used for assessment: CCAMP Water Quality Data_file2 |
|
Final Data File used for assessment: CCAMP Water Quality Data_file3 |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
Water Quality Control Plan, Central Coast Basin, Cold Water Habitat Objective, Chapter III, Section II.A.2 General Objectives for all Inland Surface Waters, Enclosed Bays and Estuaries states the following: The dissolved oxygen concentration shall not be reduced below 7.0 mg/l at any time. |
Objective/Criterion Reference: |
Water Quality Control Plan (Basin Plan) - Central Coast Region (Region 3) |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
Data for this line of evidence for San Antonio Creek (313) was collected at 2 monitoring sites [ 313SAB-San Antonio Creek at Rancho de las Flores Bridge and Highway 135, 313SAI-San Antonio Creek at San Antonio Road West] |
Temporal Representation: |
Data was collected over the time period 7/18/2001-8/11/2006. Diurnal monitoring conducted in summer months at all CCAMP monitoring sites. |
Environmental Conditions: |
Staff is not aware of any special conditions that might effect interpretation of the data. |
QAPP Information: |
All data was collected following the Standard Operating Procedures and Data Quality Objectives outlined in the SWAMP QAMP, (Puckett, 2002). QA data are included in submission. All data are flagged as appropriate. |
QAPP Information Reference(s): |
|
Line of Evidence (LOE) for Decision ID 25353, Low Dissolved Oxygen
|
Region 3 |
San Antonio Creek (San Antonio Watershed, Rancho del las Flores Bridge at Hwy 135 to downstream at Railroad Bridge) |
|
|
LOE ID: |
13258 |
|
Pollutant: |
Dissolved oxygen saturation |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
None |
|
Beneficial Use: |
Cold Freshwater Habitat |
Aquatic Life Use: |
Cold Freshwater Habitat |
|
Number of Samples: |
8 |
Number of Exceedances: |
6 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Central Coast Regional Board Staff assessed CCAMP Diurnal Dissolved Oxygen Sampling (DO) data for San Antonio Creek (313) to determine beneficial use support and results are as follows: 6 of 8 samples exceed the criterion for Oxygen, Saturation. |
Data Reference: |
Final Data File used for assessment: CCAMP Water Quality Data_file1 |
|
Final Data File used for assessment: CCAMP Water Quality Data_file2 |
|
Final Data File used for assessment: CCAMP Water Quality Data_file3 |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
Water Quality Control Plan, Central Coast Basin, General Objective, Chapter III, Section II.A.2 General Objectives for all Inland Surface Waters, Enclosed Bays and Estuaries states the following: Median values should not fall below 85% saturation as a result of controllable water quality conditions. |
Objective/Criterion Reference: |
Water Quality Control Plan (Basin Plan) - Central Coast Region (Region 3) |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
Data for this line of evidence for San Antonio Creek (313) was collected at 2 monitoring sites [ 313SAB-San Antonio Creek at Rancho de las Flores Bridge and Highway 135, 313SAI-San Antonio Creek at San Antonio Road West] |
Temporal Representation: |
Data was collected over the time period 7/18/2001-8/11/2006. Diurnal monitoring conducted in summer months at all CCAMP monitoring sites. |
Environmental Conditions: |
Staff is not aware of any special conditions that might effect interpretation of the data. |
QAPP Information: |
All data was collected following the Standard Operating Procedures and Data Quality Objectives outlined in the SWAMP QAMP, (Puckett, 2002). QA data are included in submission. All data are flagged as appropriate. |
QAPP Information Reference(s): |
|
Line of Evidence (LOE) for Decision ID 25353, Low Dissolved Oxygen
|
Region 3 |
San Antonio Creek (San Antonio Watershed, Rancho del las Flores Bridge at Hwy 135 to downstream at Railroad Bridge) |
|
|
LOE ID: |
13257 |
|
Pollutant: |
Oxygen, Dissolved |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Dissolved |
|
Beneficial Use: |
Warm Freshwater Habitat |
Aquatic Life Use: |
Warm Freshwater Habitat |
|
Number of Samples: |
8 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Central Coast Regional Board Staff assessed CCAMP Diurnal Dissolved Oxygen Sampling (DO) data for San Antonio Creek (313) to determine beneficial use support and results are as follows: 0 of 8 samples exceed the criterion for Oxygen, Dissolved. |
Data Reference: |
Final Data File used for assessment: CCAMP Water Quality Data_file1 |
|
Final Data File used for assessment: CCAMP Water Quality Data_file2 |
|
Final Data File used for assessment: CCAMP Water Quality Data_file3 |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
Water Quality Control Plan, Central Coast Basin, General Objective, Chapter III, Section II.A.2 General Objectives for all Inland Surface Waters, Enclosed Bays and Estuaries states the following: For waters not mentioned by a specific beneficial use, dissolved oxygen concentration shall not be reduced below 5.0 mg/l at any time. |
Objective/Criterion Reference: |
Water Quality Control Plan (Basin Plan) - Central Coast Region (Region 3) |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
Data for this line of evidence for San Antonio Creek (313) was collected at 2 monitoring sites [ 313SAB-San Antonio Creek at Rancho de las Flores Bridge and Highway 135, 313SAI-San Antonio Creek at San Antonio Road West] |
Temporal Representation: |
Data was collected over the time period 7/18/2001-8/11/2006. Diurnal monitoring conducted in summer months at all CCAMP monitoring sites. |
Environmental Conditions: |
Staff is not aware of any special conditions that might effect interpretation of the data. |
QAPP Information: |
All data was collected following the Standard Operating Procedures and Data Quality Objectives outlined in the SWAMP QAMP, (Puckett, 2002). QA data are included in submission. All data are flagged as appropriate. |
QAPP Information Reference(s): |
|
Line of Evidence (LOE) for Decision ID 25353, Low Dissolved Oxygen
|
Region 3 |
San Antonio Creek (San Antonio Watershed, Rancho del las Flores Bridge at Hwy 135 to downstream at Railroad Bridge) |
|
|
LOE ID: |
13295 |
|
Pollutant: |
Dissolved oxygen saturation |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
None |
|
Beneficial Use: |
Warm Freshwater Habitat |
Aquatic Life Use: |
Warm Freshwater Habitat |
|
Number of Samples: |
57 |
Number of Exceedances: |
38 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Central Coast Regional Board Staff assessed CCAMP Coastal Confluences (CC) data for San Antonio Creek (313) to determine beneficial use support and results are as follows: 38 of 57 samples exceed the criterion for Oxygen, Saturation. |
Data Reference: |
Final Data File used for assessment: CCAMP Water Quality Data_file1 |
|
Final Data File used for assessment: CCAMP Water Quality Data_file2 |
|
Final Data File used for assessment: CCAMP Water Quality Data_file3 |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
Water Quality Control Plan, Central Coast Basin, General Objective, Chapter III, Section II.A.2 General Objectives for all Inland Surface Waters, Enclosed Bays and Estuaries states the following: Median values should not fall below 85% saturation as a result of controllable water quality conditions. |
Objective/Criterion Reference: |
Water Quality Control Plan (Basin Plan) - Central Coast Region (Region 3) |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
Data for this line of evidence for San Antonio Creek (313) was collected at 2 monitoring sites [ 313SAC-San Antonio Creek at Rail Road Bridge, u/s lagoon , 313SAI-San Antonio Creek at San Antonio Road West] |
Temporal Representation: |
Data was collected over the time period 1/18/2001-12/6/2006. CCAMP Coastal confluence monitoring is conducted monthly (with the exception of April 2003 - December 2003) and is ongoing. |
Environmental Conditions: |
Staff is not aware of any special conditions that might effect interpretation of the data. |
QAPP Information: |
All data was collected following the Standard Operating Procedures and Data Quality Objectives outlined in the SWAMP QAMP, (Puckett, 2002). QA data are included in submission. All data are flagged as appropriate. |
QAPP Information Reference(s): |
|
Line of Evidence (LOE) for Decision ID 25353, Low Dissolved Oxygen
|
Region 3 |
San Antonio Creek (San Antonio Watershed, Rancho del las Flores Bridge at Hwy 135 to downstream at Railroad Bridge) |
|
|
LOE ID: |
13222 |
|
Pollutant: |
Dissolved oxygen saturation |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
None |
|
Beneficial Use: |
Cold Freshwater Habitat |
Aquatic Life Use: |
Cold Freshwater Habitat |
|
Number of Samples: |
30 |
Number of Exceedances: |
5 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Central Coast Regional Board Staff assessed CCAMP Santa Barbara (SantaBarb) data for San Antonio Creek (313) to determine beneficial use support and results are as follows: 5 of 30 samples exceed the criterion for Oxygen, Saturation. |
Data Reference: |
Final Data File used for assessment: CCAMP Water Quality Data_file1 |
|
Final Data File used for assessment: CCAMP Water Quality Data_file2 |
|
Final Data File used for assessment: CCAMP Water Quality Data_file3 |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
Water Quality Control Plan, Central Coast Basin, General Objective, Chapter III, Section II.A.2 General Objectives for all Inland Surface Waters, Enclosed Bays and Estuaries states the following: Median values should not fall below 85% saturation as a result of controllable water quality conditions. |
Objective/Criterion Reference: |
Water Quality Control Plan (Basin Plan) - Central Coast Region (Region 3) |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
Data for this line of evidence for San Antonio Creek (313) was collected at 3 monitoring sites [ 313SAB-San Antonio Creek at Rancho de las Flores Bridge and Highway 135, 313SAE-San Antonio Creek at San Antonio Road East, 313SAI-San Antonio Creek at San Antonio Road West] |
Temporal Representation: |
Data was collected over the time period 1/18/2001-3/17/2002. Santa Barbara Coast is one of five annual rotation areas that are monitored for conventional pollutants by CCAMP staff monthly for one year. Toxicity monitoring is conducted twice during the rotation year (winter and summer) at a subset of sites. |
Environmental Conditions: |
Staff is not aware of any special conditions that might effect interpretation of the data. |
QAPP Information: |
All data was collected following the Standard Operating Procedures and Data Quality Objectives outlined in the SWAMP QAMP, (Puckett, 2002). QA data are included in submission. All data are flagged as appropriate. |
QAPP Information Reference(s): |
|
Line of Evidence (LOE) for Decision ID 25353, Low Dissolved Oxygen
|
Region 3 |
San Antonio Creek (San Antonio Watershed, Rancho del las Flores Bridge at Hwy 135 to downstream at Railroad Bridge) |
|
|
LOE ID: |
13294 |
|
Pollutant: |
Dissolved oxygen saturation |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
None |
|
Beneficial Use: |
Cold Freshwater Habitat |
Aquatic Life Use: |
Cold Freshwater Habitat |
|
Number of Samples: |
57 |
Number of Exceedances: |
38 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Central Coast Regional Board Staff assessed CCAMP Coastal Confluences (CC) data for San Antonio Creek (313) to determine beneficial use support and results are as follows: 38 of 57 samples exceed the criterion for Oxygen, Saturation. |
Data Reference: |
Final Data File used for assessment: CCAMP Water Quality Data_file1 |
|
Final Data File used for assessment: CCAMP Water Quality Data_file2 |
|
Final Data File used for assessment: CCAMP Water Quality Data_file3 |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
Water Quality Control Plan, Central Coast Basin, General Objective, Chapter III, Section II.A.2 General Objectives for all Inland Surface Waters, Enclosed Bays and Estuaries states the following: Median values should not fall below 85% saturation as a result of controllable water quality conditions. |
Objective/Criterion Reference: |
Water Quality Control Plan (Basin Plan) - Central Coast Region (Region 3) |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
Data for this line of evidence for San Antonio Creek (313) was collected at 2 monitoring sites [ 313SAC-San Antonio Creek at Rail Road Bridge, u/s lagoon , 313SAI-San Antonio Creek at San Antonio Road West] |
Temporal Representation: |
Data was collected over the time period 1/18/2001-12/6/2006. CCAMP Coastal confluence monitoring is conducted monthly (with the exception of April 2003 - December 2003) and is ongoing. |
Environmental Conditions: |
Staff is not aware of any special conditions that might effect interpretation of the data. |
QAPP Information: |
All data was collected following the Standard Operating Procedures and Data Quality Objectives outlined in the SWAMP QAMP, (Puckett, 2002). QA data are included in submission. All data are flagged as appropriate. |
QAPP Information Reference(s): |
|
Line of Evidence (LOE) for Decision ID 25353, Low Dissolved Oxygen
|
Region 3 |
San Antonio Creek (San Antonio Watershed, Rancho del las Flores Bridge at Hwy 135 to downstream at Railroad Bridge) |
|
|
LOE ID: |
13259 |
|
Pollutant: |
Dissolved oxygen saturation |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
None |
|
Beneficial Use: |
Warm Freshwater Habitat |
Aquatic Life Use: |
Warm Freshwater Habitat |
|
Number of Samples: |
8 |
Number of Exceedances: |
6 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Central Coast Regional Board Staff assessed CCAMP Diurnal Dissolved Oxygen Sampling (DO) data for San Antonio Creek (313) to determine beneficial use support and results are as follows: 6 of 8 samples exceed the criterion for Oxygen, Saturation. |
Data Reference: |
Final Data File used for assessment: CCAMP Water Quality Data_file1 |
|
Final Data File used for assessment: CCAMP Water Quality Data_file2 |
|
Final Data File used for assessment: CCAMP Water Quality Data_file3 |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
Water Quality Control Plan, Central Coast Basin, General Objective, Chapter III, Section II.A.2 General Objectives for all Inland Surface Waters, Enclosed Bays and Estuaries states the following: Median values should not fall below 85% saturation as a result of controllable water quality conditions. |
Objective/Criterion Reference: |
Water Quality Control Plan (Basin Plan) - Central Coast Region (Region 3) |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
Data for this line of evidence for San Antonio Creek (313) was collected at 2 monitoring sites [ 313SAB-San Antonio Creek at Rancho de las Flores Bridge and Highway 135, 313SAI-San Antonio Creek at San Antonio Road West] |
Temporal Representation: |
Data was collected over the time period 7/18/2001-8/11/2006. Diurnal monitoring conducted in summer months at all CCAMP monitoring sites. |
Environmental Conditions: |
Staff is not aware of any special conditions that might effect interpretation of the data. |
QAPP Information: |
All data was collected following the Standard Operating Procedures and Data Quality Objectives outlined in the SWAMP QAMP, (Puckett, 2002). QA data are included in submission. All data are flagged as appropriate. |
QAPP Information Reference(s): |
|
Line of Evidence (LOE) for Decision ID 25353, Low Dissolved Oxygen
|
Region 3 |
San Antonio Creek (San Antonio Watershed, Rancho del las Flores Bridge at Hwy 135 to downstream at Railroad Bridge) |
|
|
LOE ID: |
13237 |
|
Pollutant: |
Dissolved oxygen saturation |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
None |
|
Beneficial Use: |
Warm Freshwater Habitat |
Aquatic Life Use: |
Warm Freshwater Habitat |
|
Number of Samples: |
30 |
Number of Exceedances: |
5 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Central Coast Regional Board Staff assessed CCAMP Santa Barbara (SantaBarb) data for San Antonio Creek (313) to determine beneficial use support and results are as follows: 5 of 30 samples exceed the criterion for Oxygen, Saturation. |
Data Reference: |
Final Data File used for assessment: CCAMP Water Quality Data_file1 |
|
Final Data File used for assessment: CCAMP Water Quality Data_file2 |
|
Final Data File used for assessment: CCAMP Water Quality Data_file3 |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
Water Quality Control Plan, Central Coast Basin, General Objective, Chapter III, Section II.A.2 General Objectives for all Inland Surface Waters, Enclosed Bays and Estuaries states the following: Median values should not fall below 85% saturation as a result of controllable water quality conditions. |
Objective/Criterion Reference: |
Water Quality Control Plan (Basin Plan) - Central Coast Region (Region 3) |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
Data for this line of evidence for San Antonio Creek (313) was collected at 3 monitoring sites [ 313SAB-San Antonio Creek at Rancho de las Flores Bridge and Highway 135, 313SAE-San Antonio Creek at San Antonio Road East, 313SAI-San Antonio Creek at San Antonio Road West] |
Temporal Representation: |
Data was collected over the time period 1/18/2001-3/17/2002. Santa Barbara Coast is one of five annual rotation areas that are monitored for conventional pollutants by CCAMP staff monthly for one year. Toxicity monitoring is conducted twice during the rotation year (winter and summer) at a subset of sites. |
Environmental Conditions: |
Staff is not aware of any special conditions that might effect interpretation of the data. |
QAPP Information: |
All data was collected following the Standard Operating Procedures and Data Quality Objectives outlined in the SWAMP QAMP, (Puckett, 2002). QA data are included in submission. All data are flagged as appropriate. |
QAPP Information Reference(s): |
|
Line of Evidence (LOE) for Decision ID 25353, Low Dissolved Oxygen
|
Region 3 |
San Antonio Creek (San Antonio Watershed, Rancho del las Flores Bridge at Hwy 135 to downstream at Railroad Bridge) |
|
|
LOE ID: |
13292 |
|
Pollutant: |
Oxygen, Dissolved |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Dissolved |
|
Beneficial Use: |
Cold Freshwater Habitat |
Aquatic Life Use: |
Cold Freshwater Habitat |
|
Number of Samples: |
57 |
Number of Exceedances: |
21 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Central Coast Regional Board Staff assessed CCAMP Coastal Confluences (CC) data for San Antonio Creek (313) to determine beneficial use support and results are as follows: 21 of 57 samples exceed the criterion for Oxygen, Dissolved. |
Data Reference: |
Final Data File used for assessment: CCAMP Water Quality Data_file1 |
|
Final Data File used for assessment: CCAMP Water Quality Data_file2 |
|
Final Data File used for assessment: CCAMP Water Quality Data_file3 |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
Water Quality Control Plan, Central Coast Basin, Cold Water Habitat Objective, Chapter III, Section II.A.2 General Objectives for all Inland Surface Waters, Enclosed Bays and Estuaries states the following: The dissolved oxygen concentration shall not be reduced below 7.0 mg/l at any time. |
Objective/Criterion Reference: |
Water Quality Control Plan (Basin Plan) - Central Coast Region (Region 3) |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
Data for this line of evidence for San Antonio Creek (313) was collected at 2 monitoring sites [ 313SAC-San Antonio Creek at Rail Road Bridge, u/s lagoon , 313SAI-San Antonio Creek at San Antonio Road West] |
Temporal Representation: |
Data was collected over the time period 1/18/2001-12/6/2006. CCAMP Coastal confluence monitoring is conducted monthly (with the exception of April 2003 - December 2003) and is ongoing. |
Environmental Conditions: |
Staff is not aware of any special conditions that might effect interpretation of the data. |
QAPP Information: |
All data was collected following the Standard Operating Procedures and Data Quality Objectives outlined in the SWAMP QAMP, (Puckett, 2002). QA data are included in submission. All data are flagged as appropriate. |
QAPP Information Reference(s): |
|
Line of Evidence (LOE) for Decision ID 25353, Low Dissolved Oxygen
|
Region 3 |
San Antonio Creek (San Antonio Watershed, Rancho del las Flores Bridge at Hwy 135 to downstream at Railroad Bridge) |
|
|
LOE ID: |
13220 |
|
Pollutant: |
Oxygen, Dissolved |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Dissolved |
|
Beneficial Use: |
Cold Freshwater Habitat |
Aquatic Life Use: |
Cold Freshwater Habitat |
|
Number of Samples: |
30 |
Number of Exceedances: |
1 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Central Coast Regional Board Staff assessed CCAMP Santa Barbara (SantaBarb) data for San Antonio Creek (313) to determine beneficial use support and results are as follows: 1 of 30 samples exceed the criterion for Oxygen, Dissolved. |
Data Reference: |
Final Data File used for assessment: CCAMP Water Quality Data_file1 |
|
Final Data File used for assessment: CCAMP Water Quality Data_file2 |
|
Final Data File used for assessment: CCAMP Water Quality Data_file3 |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
Water Quality Control Plan, Central Coast Basin, Cold Water Habitat Objective, Chapter III, Section II.A.2 General Objectives for all Inland Surface Waters, Enclosed Bays and Estuaries states the following: The dissolved oxygen concentration shall not be reduced below 7.0 mg/l at any time. |
Objective/Criterion Reference: |
Water Quality Control Plan (Basin Plan) - Central Coast Region (Region 3) |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
Data for this line of evidence for San Antonio Creek (313) was collected at 3 monitoring sites [ 313SAB-San Antonio Creek at Rancho de las Flores Bridge and Highway 135, 313SAE-San Antonio Creek at San Antonio Road East, 313SAI-San Antonio Creek at San Antonio Road West] |
Temporal Representation: |
Data was collected over the time period 1/18/2001-3/17/2002. Santa Barbara Coast is one of five annual rotation areas that are monitored for conventional pollutants by CCAMP staff monthly for one year. Toxicity monitoring is conducted twice during the rotation year (winter and summer) at a subset of sites. |
Environmental Conditions: |
Staff is not aware of any special conditions that might effect interpretation of the data. |
QAPP Information: |
All data was collected following the Standard Operating Procedures and Data Quality Objectives outlined in the SWAMP QAMP, (Puckett, 2002). QA data are included in submission. All data are flagged as appropriate. |
QAPP Information Reference(s): |
|
Line of Evidence (LOE) for Decision ID 25353, Low Dissolved Oxygen
|
Region 3 |
San Antonio Creek (San Antonio Watershed, Rancho del las Flores Bridge at Hwy 135 to downstream at Railroad Bridge) |
|
|
LOE ID: |
13221 |
|
Pollutant: |
Oxygen, Dissolved |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Dissolved |
|
Beneficial Use: |
Warm Freshwater Habitat |
Aquatic Life Use: |
Warm Freshwater Habitat |
|
Number of Samples: |
30 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Central Coast Regional Board Staff assessed CCAMP Santa Barbara (SantaBarb) data for San Antonio Creek (313) to determine beneficial use support and results are as follows: 0 of 30 samples exceed the criterion for Oxygen, Dissolved. |
Data Reference: |
Final Data File used for assessment: CCAMP Water Quality Data_file1 |
|
Final Data File used for assessment: CCAMP Water Quality Data_file2 |
|
Final Data File used for assessment: CCAMP Water Quality Data_file3 |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
Water Quality Control Plan, Central Coast Basin, General Objective, Chapter III, Section II.A.2 General Objectives for all Inland Surface Waters, Enclosed Bays and Estuaries states the following: For waters not mentioned by a specific beneficial use, dissolved oxygen concentration shall not be reduced below 5.0 mg/l at any time. |
Objective/Criterion Reference: |
Water Quality Control Plan (Basin Plan) - Central Coast Region (Region 3) |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
Data for this line of evidence for San Antonio Creek (313) was collected at 3 monitoring sites [ 313SAB-San Antonio Creek at Rancho de las Flores Bridge and Highway 135, 313SAE-San Antonio Creek at San Antonio Road East, 313SAI-San Antonio Creek at San Antonio Road West] |
Temporal Representation: |
Data was collected over the time period 1/18/2001-3/17/2002. Santa Barbara Coast is one of five annual rotation areas that are monitored for conventional pollutants by CCAMP staff monthly for one year. Toxicity monitoring is conducted twice during the rotation year (winter and summer) at a subset of sites. |
Environmental Conditions: |
Staff is not aware of any special conditions that might effect interpretation of the data. |
QAPP Information: |
All data was collected following the Standard Operating Procedures and Data Quality Objectives outlined in the SWAMP QAMP, (Puckett, 2002). QA data are included in submission. All data are flagged as appropriate. |
QAPP Information Reference(s): |
|