Line of Evidence (LOE) for Decision ID 114868, Aldrin
|
Region 9 |
Sacred Pond |
|
|
LOE ID: |
134949 |
|
Pollutant: |
Aldrin |
LOE Subgroup: |
Pollutant-Tissue |
Matrix: |
Tissue |
Fraction: |
Fish fillet |
|
Beneficial Use: |
Warm Freshwater Habitat |
|
Number of Samples: |
1 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP RWB9 Monitoring data for Sacred Pond to determine beneficial use support and the results are as follows 0 of the 1 samples exceeded the water quality threshold for Aldrin. Data were collected for 1 fish species (1 composite(s) of Largemouth Bass each composed of 3 fish per composite). |
Data Reference: |
Field, Habitat, Sediment, Tissue, Water data for the 2020/2022 integrated report in Region 9. |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
All waters shall be maintained free of toxic substances in concentrations that are toxic to, or that produce detrimental physiological responses in human, plant, animal, or aquatic life (Water Quality Control Plan, San Diego Basin). |
Objective/Criterion Reference: |
Water Quality Control Plan for the San Diego Basin |
|
Evaluation Guideline: |
National Academy of Science guidelines (NAS 1972) establish a maximum Aldrin concentration of 100 ug/Kg (wet weight) in tissue samples for protection of aquatic life from bioaccumulation of toxic substances. |
Guideline Reference: |
National Academy of Sciences. Water Quality Criteria 1972. EPA-R3-73-033. Washington, D.C.: U.S. Environmental Protection Agency |
|
Spatial Representation: |
Data was collected from 1 station(s) with the station code(s): 907SDRMPW. |
Temporal Representation: |
Data for this line of evidence were collected between 2014-07-08 and 2014-07-08. When composited fish were collected over multiple days, the first day of fish collection was used as the sample date in the LOE, both for LOE writing, and for averaging period purposes. |
Environmental Conditions: |
|
QAPP Information: |
SWAMP QAPrP 2008, Nagoda and Busse, 2013. Quality Assurance Project Plan for Screening of Cyanotoxins in Lakes/Reservoirs and Coastal Wetlands in the San Diego Region, SWAMP QAPrP 2017 |
QAPP Information Reference(s): |
Quality Assurance Program Plans, Quality Assurance Project Plans, and Standard Operating Procedures for the SWAMP program |
|
Line of Evidence (LOE) for Decision ID 114858, Chlordane
|
Region 9 |
Sacred Pond |
|
|
LOE ID: |
135083 |
|
Pollutant: |
Chlordane |
LOE Subgroup: |
Pollutant-Tissue |
Matrix: |
Tissue |
Fraction: |
Fish fillet |
|
Beneficial Use: |
Commercial or recreational collection of fish, shellfish, or organisms |
|
Number of Samples: |
1 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP RWB9 Monitoring data for Sacred Pond to determine beneficial use support and the results are as follows 0 of the 1 samples exceeded the water quality threshold for Total Chlordanes. Data were collected for 1 fish species (1 composite(s) of Largemouth Bass each composed of 3 fish per composite). |
Data Reference: |
Field, Habitat, Sediment, Tissue, Water data for the 2020/2022 integrated report in Region 9. |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
All waters shall be maintained free of toxic substances in concentrations that are toxic to, or that produce detrimental physiological responses in human, plant, animal, or aquatic life (Water Quality Control Plan, San Diego Basin). |
Objective/Criterion Reference: |
Water Quality Control Plan for the San Diego Basin |
|
Evaluation Guideline: |
The modified OEHHA Fish Contaminant Goal for total chlordane in fish tissue is 3.9 ppb. This screening level assumes an average body weight of 70 kg and a consumption rate of 32 g/day for a 30 year exposure over a 70-year lifetime. This constituent is a carcinogen therefore the risk level is set to one in a million. A cooking reduction factor of 1 is applied for skin-off fillets. (Klasing, S., and R. Brodberg, 2008) |
Guideline Reference: |
Development of Fish Contaminant Goals and Advisory Tissue Levels for Common Contaminants in California Sport Fish: Chlordane, DDTs, Dieldrin, Methylmercury, PCBs, Selenium, and Toxaphene |
|
Spatial Representation: |
Data was collected from 1 station(s) with the station code(s): 907SDRMPW. |
Temporal Representation: |
Data for this line of evidence were collected between 2014-07-08 and 2014-07-08. When composited fish were collected over multiple days, the first day of fish collection was used as the sample date in the LOE, both for LOE writing, and for averaging period purposes. |
Environmental Conditions: |
|
QAPP Information: |
SWAMP QAPrP 2008, Nagoda and Busse, 2013. Quality Assurance Project Plan for Screening of Cyanotoxins in Lakes/Reservoirs and Coastal Wetlands in the San Diego Region, SWAMP QAPrP 2017 |
QAPP Information Reference(s): |
Quality Assurance Program Plans, Quality Assurance Project Plans, and Standard Operating Procedures for the SWAMP program |
|
Line of Evidence (LOE) for Decision ID 114858, Chlordane
|
Region 9 |
Sacred Pond |
|
|
LOE ID: |
135066 |
|
Pollutant: |
Chlordane |
LOE Subgroup: |
Pollutant-Tissue |
Matrix: |
Tissue |
Fraction: |
Fish fillet |
|
Beneficial Use: |
Warm Freshwater Habitat |
|
Number of Samples: |
1 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP RWB9 Monitoring data for Sacred Pond to determine beneficial use support and the results are as follows 0 of the 1 samples exceeded the water quality threshold for Total Chlordanes. Data were collected for 1 fish species (1 composite(s) of Largemouth Bass each composed of 3 fish per composite). |
Data Reference: |
Field, Habitat, Sediment, Tissue, Water data for the 2020/2022 integrated report in Region 9. |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
All waters shall be maintained free of toxic substances in concentrations that are toxic to, or that produce detrimental physiological responses in human, plant, animal, or aquatic life (Water Quality Control Plan, San Diego Basin). |
Objective/Criterion Reference: |
Water Quality Control Plan for the San Diego Basin |
|
Evaluation Guideline: |
National Academy of Science guidelines (NAS 1972) establish a maximum total Chlordane concentration of 100 ug/Kg (wet weight) in tissue samples for protection of aquatic life from bioaccumulation of toxic substances. |
Guideline Reference: |
National Academy of Sciences. Water Quality Criteria 1972. EPA-R3-73-033. Washington, D.C.: U.S. Environmental Protection Agency |
|
Spatial Representation: |
Data was collected from 1 station(s) with the station code(s): 907SDRMPW. |
Temporal Representation: |
Data for this line of evidence were collected between 2014-07-08 and 2014-07-08. When composited fish were collected over multiple days, the first day of fish collection was used as the sample date in the LOE, both for LOE writing, and for averaging period purposes. |
Environmental Conditions: |
|
QAPP Information: |
SWAMP QAPrP 2008, Nagoda and Busse, 2013. Quality Assurance Project Plan for Screening of Cyanotoxins in Lakes/Reservoirs and Coastal Wetlands in the San Diego Region, SWAMP QAPrP 2017 |
QAPP Information Reference(s): |
Quality Assurance Program Plans, Quality Assurance Project Plans, and Standard Operating Procedures for the SWAMP program |
|
Line of Evidence (LOE) for Decision ID 114859, Dieldrin
|
Region 9 |
Sacred Pond |
|
|
LOE ID: |
135115 |
|
Pollutant: |
Dieldrin |
LOE Subgroup: |
Pollutant-Tissue |
Matrix: |
Tissue |
Fraction: |
Fish fillet |
|
Beneficial Use: |
Warm Freshwater Habitat |
|
Number of Samples: |
1 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP RWB9 Monitoring data for Sacred Pond to determine beneficial use support and the results are as follows 0 of the 1 samples exceeded the water quality threshold for Dieldrin. Data were collected for 1 fish species (1 composite(s) of Largemouth Bass each composed of 3 fish per composite). |
Data Reference: |
Field, Habitat, Sediment, Tissue, Water data for the 2020/2022 integrated report in Region 9. |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
All waters shall be maintained free of toxic substances in concentrations that are toxic to, or that produce detrimental physiological responses in human, plant, animal, or aquatic life (Water Quality Control Plan, San Diego Basin). |
Objective/Criterion Reference: |
Water Quality Control Plan for the San Diego Basin |
|
Evaluation Guideline: |
National Academy of Science guidelines (NAS 1972) establish a maximum Dieldrin concentration of 100 ug/Kg (wet weight) in tissue samples for protection of aquatic life from bioaccumulation of toxic substances. |
Guideline Reference: |
National Academy of Sciences. Water Quality Criteria 1972. EPA-R3-73-033. Washington, D.C.: U.S. Environmental Protection Agency |
|
Spatial Representation: |
Data was collected from 1 station(s) with the station code(s): 907SDRMPW. |
Temporal Representation: |
Data for this line of evidence were collected between 2014-07-08 and 2014-07-08. When composited fish were collected over multiple days, the first day of fish collection was used as the sample date in the LOE, both for LOE writing, and for averaging period purposes. |
Environmental Conditions: |
|
QAPP Information: |
SWAMP QAPrP 2008, Nagoda and Busse, 2013. Quality Assurance Project Plan for Screening of Cyanotoxins in Lakes/Reservoirs and Coastal Wetlands in the San Diego Region, SWAMP QAPrP 2017 |
QAPP Information Reference(s): |
Quality Assurance Program Plans, Quality Assurance Project Plans, and Standard Operating Procedures for the SWAMP program |
|
Line of Evidence (LOE) for Decision ID 114859, Dieldrin
|
Region 9 |
Sacred Pond |
|
|
LOE ID: |
135102 |
|
Pollutant: |
Dieldrin |
LOE Subgroup: |
Pollutant-Tissue |
Matrix: |
Tissue |
Fraction: |
Fish fillet |
|
Beneficial Use: |
Commercial or recreational collection of fish, shellfish, or organisms |
|
Number of Samples: |
0 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Waterboard staff assessed SWAMP RWB9 Monitoring data for Sacred Pond to determine beneficial use support and the results are as follows: Zero of Zero samples exceeded the water quality threshold for Dieldrin. Although data was collected for 1 fish species (1 composite(s) of Largemouth Bass each composed of 3 fish per composite), all 1 sample(s) had to be thrown out due to quantitation issues. |
Data Reference: |
Field, Habitat, Sediment, Tissue, Water data for the 2020/2022 integrated report in Region 9. |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
All waters shall be maintained free of toxic substances in concentrations that are toxic to, or that produce detrimental physiological responses in human, plant, animal, or aquatic life (Water Quality Control Plan, San Diego Basin). |
Objective/Criterion Reference: |
Water Quality Control Plan for the San Diego Basin |
|
Evaluation Guideline: |
The modified OEHHA Fish Contaminant Goal for dieldrin in fish tissue is 0.32 ppb. This screening level assumes an average body weight of 70 kg and a consumption rate of 32 g/day for a 30 year exposure over a 70-year lifetime. This constituent is a carcinogen therefore the risk level is set to one in a million. A cooking reduction factor of 1 is applied for skin-off fillets. (Klasing, S., and R. Brodberg, 2008) |
Guideline Reference: |
Development of Fish Contaminant Goals and Advisory Tissue Levels for Common Contaminants in California Sport Fish: Chlordane, DDTs, Dieldrin, Methylmercury, PCBs, Selenium, and Toxaphene |
|
Spatial Representation: |
Data was collected from 1 station(s) with the station code(s): 907SDRMPW. |
Temporal Representation: |
Data for this line of evidence were collected between 2014-07-08 and 2014-07-08. When composited fish were collected over multiple days, the first day of fish collection was used as the sample date in the LOE, both for LOE writing, and for averaging period purposes. |
Environmental Conditions: |
|
QAPP Information: |
SWAMP QAPrP 2008, Nagoda and Busse, 2013. Quality Assurance Project Plan for Screening of Cyanotoxins in Lakes/Reservoirs and Coastal Wetlands in the San Diego Region, SWAMP QAPrP 2017 |
QAPP Information Reference(s): |
Quality Assurance Program Plans, Quality Assurance Project Plans, and Standard Operating Procedures for the SWAMP program |
|
Line of Evidence (LOE) for Decision ID 114860, Endosulfan
|
Region 9 |
Sacred Pond |
|
|
LOE ID: |
134925 |
|
Pollutant: |
Endosulfan |
LOE Subgroup: |
Pollutant-Tissue |
Matrix: |
Tissue |
Fraction: |
Fish fillet |
|
Beneficial Use: |
Warm Freshwater Habitat |
|
Number of Samples: |
1 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP RWB9 Monitoring data for Sacred Pond to determine beneficial use support and the results are as follows 0 of the 1 samples exceeded the water quality threshold for Endosulfan. Data were collected for 1 fish species (1 composite(s) of Largemouth Bass each composed of 3 fish per composite). |
Data Reference: |
Field, Habitat, Sediment, Tissue, Water data for the 2020/2022 integrated report in Region 9. |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
All waters shall be maintained free of toxic substances in concentrations that are toxic to, or that produce detrimental physiological responses in human, plant, animal, or aquatic life (Water Quality Control Plan, San Diego Basin). |
Objective/Criterion Reference: |
Water Quality Control Plan for the San Diego Basin |
|
Evaluation Guideline: |
National Academy of Science guidelines (NAS 1972) establish a maximum Endosulfan, Total concentration of 100 ug/Kg (wet weight) in tissue samples for protection of aquatic life from bioaccumulation of toxic substances. |
Guideline Reference: |
National Academy of Sciences. Water Quality Criteria 1972. EPA-R3-73-033. Washington, D.C.: U.S. Environmental Protection Agency |
|
Spatial Representation: |
Data was collected from 1 station(s) with the station code(s): 907SDRMPW. |
Temporal Representation: |
Data for this line of evidence were collected between 2014-07-08 and 2014-07-08. When composited fish were collected over multiple days, the first day of fish collection was used as the sample date in the LOE, both for LOE writing, and for averaging period purposes. |
Environmental Conditions: |
|
QAPP Information: |
SWAMP QAPrP 2008, Nagoda and Busse, 2013. Quality Assurance Project Plan for Screening of Cyanotoxins in Lakes/Reservoirs and Coastal Wetlands in the San Diego Region, SWAMP QAPrP 2017 |
QAPP Information Reference(s): |
Quality Assurance Program Plans, Quality Assurance Project Plans, and Standard Operating Procedures for the SWAMP program |
|
Line of Evidence (LOE) for Decision ID 114860, Endosulfan
|
Region 9 |
Sacred Pond |
|
|
LOE ID: |
134968 |
|
Pollutant: |
Endosulfan |
LOE Subgroup: |
Pollutant-Tissue |
Matrix: |
Tissue |
Fraction: |
Fish fillet |
|
Beneficial Use: |
Commercial or recreational collection of fish, shellfish, or organisms |
|
Number of Samples: |
1 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP RWB9 Monitoring data for Sacred Pond to determine beneficial use support and the results are as follows 0 of the 1 samples exceeded the water quality threshold for Endosulfan. Data were collected for 1 fish species (1 composite(s) of Largemouth Bass each composed of 3 fish per composite). |
Data Reference: |
Field, Habitat, Sediment, Tissue, Water data for the 2020/2022 integrated report in Region 9. |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
All waters shall be maintained free of toxic substances in concentrations that are toxic to, or that produce detrimental physiological responses in human, plant, animal, or aquatic life (Water Quality Control Plan, San Diego Basin). |
Objective/Criterion Reference: |
Water Quality Control Plan for the San Diego Basin |
|
Evaluation Guideline: |
The modified OEHHA Fish Contaminant Goal for endosulfan (l and ll) in fish tissue is 13,000 ppb. This screening level assumes an average body weight of 70 kg and a consumption rate of 32 g/day. A cooking reduction factor of 1 is applied for skin-off fillets. (Klasing, S., and R. Brodberg, 2008; USEPA, 2000) |
Guideline Reference: |
Development of Fish Contaminant Goals and Advisory Tissue Levels for Common Contaminants in California Sport Fish: Chlordane, DDTs, Dieldrin, Methylmercury, PCBs, Selenium, and Toxaphene |
Guideline Reference: |
Guidance for Assessing Chemical Contaminant Data for Use In Fish Advisories Volume 1: Fish Sampling and Analysis |
|
Spatial Representation: |
Data was collected from 1 station(s) with the station code(s): 907SDRMPW. |
Temporal Representation: |
Data for this line of evidence were collected between 2014-07-08 and 2014-07-08. When composited fish were collected over multiple days, the first day of fish collection was used as the sample date in the LOE, both for LOE writing, and for averaging period purposes. |
Environmental Conditions: |
|
QAPP Information: |
SWAMP QAPrP 2008, Nagoda and Busse, 2013. Quality Assurance Project Plan for Screening of Cyanotoxins in Lakes/Reservoirs and Coastal Wetlands in the San Diego Region, SWAMP QAPrP 2017 |
QAPP Information Reference(s): |
Quality Assurance Program Plans, Quality Assurance Project Plans, and Standard Operating Procedures for the SWAMP program |
|
Line of Evidence (LOE) for Decision ID 114861, Endrin
|
Region 9 |
Sacred Pond |
|
|
LOE ID: |
135044 |
|
Pollutant: |
Endrin |
LOE Subgroup: |
Pollutant-Tissue |
Matrix: |
Tissue |
Fraction: |
Fish fillet |
|
Beneficial Use: |
Commercial or recreational collection of fish, shellfish, or organisms |
|
Number of Samples: |
1 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP RWB9 Monitoring data for Sacred Pond to determine beneficial use support and the results are as follows 0 of the 1 samples exceeded the water quality threshold for Endrin. Data were collected for 1 fish species (1 composite(s) of Largemouth Bass each composed of 3 fish per composite). |
Data Reference: |
Field, Habitat, Sediment, Tissue, Water data for the 2020/2022 integrated report in Region 9. |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
All waters shall be maintained free of toxic substances in concentrations that are toxic to, or that produce detrimental physiological responses in human, plant, animal, or aquatic life (Water Quality Control Plan, San Diego Basin). |
Objective/Criterion Reference: |
Water Quality Control Plan for the San Diego Basin |
|
Evaluation Guideline: |
The modified OEHHA Fish Contaminant Goal for endrin in fish tissue is 660 ppb. This screening level assumes an average body weight of 70 kg and a consumption rate of 32 g/day. A cooking reduction factor of 1 is applied for skin-off fillets. (Klasing, S., and R. Brodberg, 2008; USEPA, 2000) |
Guideline Reference: |
Development of Fish Contaminant Goals and Advisory Tissue Levels for Common Contaminants in California Sport Fish: Chlordane, DDTs, Dieldrin, Methylmercury, PCBs, Selenium, and Toxaphene |
Guideline Reference: |
Guidance for Assessing Chemical Contaminant Data for Use In Fish Advisories Volume 1: Fish Sampling and Analysis |
|
Spatial Representation: |
Data was collected from 1 station(s) with the station code(s): 907SDRMPW. |
Temporal Representation: |
Data for this line of evidence were collected between 2014-07-08 and 2014-07-08. When composited fish were collected over multiple days, the first day of fish collection was used as the sample date in the LOE, both for LOE writing, and for averaging period purposes. |
Environmental Conditions: |
|
QAPP Information: |
SWAMP QAPrP 2008, Nagoda and Busse, 2013. Quality Assurance Project Plan for Screening of Cyanotoxins in Lakes/Reservoirs and Coastal Wetlands in the San Diego Region, SWAMP QAPrP 2017 |
QAPP Information Reference(s): |
Quality Assurance Program Plans, Quality Assurance Project Plans, and Standard Operating Procedures for the SWAMP program |
|
Line of Evidence (LOE) for Decision ID 114861, Endrin
|
Region 9 |
Sacred Pond |
|
|
LOE ID: |
134984 |
|
Pollutant: |
Endrin |
LOE Subgroup: |
Pollutant-Tissue |
Matrix: |
Tissue |
Fraction: |
Fish fillet |
|
Beneficial Use: |
Warm Freshwater Habitat |
|
Number of Samples: |
1 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP RWB9 Monitoring data for Sacred Pond to determine beneficial use support and the results are as follows 0 of the 1 samples exceeded the water quality threshold for Endrin. Data were collected for 1 fish species (1 composite(s) of Largemouth Bass each composed of 3 fish per composite). |
Data Reference: |
Field, Habitat, Sediment, Tissue, Water data for the 2020/2022 integrated report in Region 9. |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
All waters shall be maintained free of toxic substances in concentrations that are toxic to, or that produce detrimental physiological responses in human, plant, animal, or aquatic life (Water Quality Control Plan, San Diego Basin). |
Objective/Criterion Reference: |
Water Quality Control Plan for the San Diego Basin |
|
Evaluation Guideline: |
National Academy of Science guidelines (NAS 1972) establish a maximum Endrin concentration of 100 ug/Kg (wet weight) in tissue samples for protection of aquatic life from bioaccumulation of toxic substances. |
Guideline Reference: |
National Academy of Sciences. Water Quality Criteria 1972. EPA-R3-73-033. Washington, D.C.: U.S. Environmental Protection Agency |
|
Spatial Representation: |
Data was collected from 1 station(s) with the station code(s): 907SDRMPW. |
Temporal Representation: |
Data for this line of evidence were collected between 2014-07-08 and 2014-07-08. When composited fish were collected over multiple days, the first day of fish collection was used as the sample date in the LOE, both for LOE writing, and for averaging period purposes. |
Environmental Conditions: |
|
QAPP Information: |
SWAMP QAPrP 2008, Nagoda and Busse, 2013. Quality Assurance Project Plan for Screening of Cyanotoxins in Lakes/Reservoirs and Coastal Wetlands in the San Diego Region, SWAMP QAPrP 2017 |
QAPP Information Reference(s): |
Quality Assurance Program Plans, Quality Assurance Project Plans, and Standard Operating Procedures for the SWAMP program |
|
Line of Evidence (LOE) for Decision ID 114862, Heptachlor
|
Region 9 |
Sacred Pond |
|
|
LOE ID: |
135150 |
|
Pollutant: |
Heptachlor |
LOE Subgroup: |
Pollutant-Tissue |
Matrix: |
Tissue |
Fraction: |
Fish fillet |
|
Beneficial Use: |
Warm Freshwater Habitat |
|
Number of Samples: |
1 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP RWB9 Monitoring data for Sacred Pond to determine beneficial use support and the results are as follows 0 of the 1 samples exceeded the water quality threshold for Heptachlor. Data were collected for 1 fish species (1 composite(s) of Largemouth Bass each composed of 3 fish per composite). |
Data Reference: |
Field, Habitat, Sediment, Tissue, Water data for the 2020/2022 integrated report in Region 9. |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
All waters shall be maintained free of toxic substances in concentrations that are toxic to, or that produce detrimental physiological responses in human, plant, animal, or aquatic life (Water Quality Control Plan, San Diego Basin). |
Objective/Criterion Reference: |
Water Quality Control Plan for the San Diego Basin |
|
Evaluation Guideline: |
National Academy of Science guidelines (NAS 1972) establish a maximum Heptachlor concentration of 100 ug/Kg (wet weight) in tissue samples for protection of aquatic life from bioaccumulation of toxic substances. |
Guideline Reference: |
National Academy of Sciences. Water Quality Criteria 1972. EPA-R3-73-033. Washington, D.C.: U.S. Environmental Protection Agency |
|
Spatial Representation: |
Data was collected from 1 station(s) with the station code(s): 907SDRMPW. |
Temporal Representation: |
Data for this line of evidence were collected between 2014-07-08 and 2014-07-08. When composited fish were collected over multiple days, the first day of fish collection was used as the sample date in the LOE, both for LOE writing, and for averaging period purposes. |
Environmental Conditions: |
|
QAPP Information: |
SWAMP QAPrP 2008, Nagoda and Busse, 2013. Quality Assurance Project Plan for Screening of Cyanotoxins in Lakes/Reservoirs and Coastal Wetlands in the San Diego Region, SWAMP QAPrP 2017 |
QAPP Information Reference(s): |
Quality Assurance Program Plans, Quality Assurance Project Plans, and Standard Operating Procedures for the SWAMP program |
|
Line of Evidence (LOE) for Decision ID 114863, Heptachlor epoxide
|
Region 9 |
Sacred Pond |
|
|
LOE ID: |
134986 |
|
Pollutant: |
Heptachlor epoxide |
LOE Subgroup: |
Pollutant-Tissue |
Matrix: |
Tissue |
Fraction: |
Fish fillet |
|
Beneficial Use: |
Commercial or recreational collection of fish, shellfish, or organisms |
|
Number of Samples: |
0 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Waterboard staff assessed SWAMP RWB9 Monitoring data for Sacred Pond to determine beneficial use support and the results are as follows: Zero of Zero samples exceeded the water quality threshold for Heptachlor Epoxide. Although data was collected for 1 fish species (1 composite(s) of Largemouth Bass each composed of 3 fish per composite), all 1 sample(s) had to be thrown out due to quantitation issues. |
Data Reference: |
Field, Habitat, Sediment, Tissue, Water data for the 2020/2022 integrated report in Region 9. |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
All waters shall be maintained free of toxic substances in concentrations that are toxic to, or that produce detrimental physiological responses in human, plant, animal, or aquatic life (Water Quality Control Plan, San Diego Basin). |
Objective/Criterion Reference: |
Water Quality Control Plan for the San Diego Basin |
|
Evaluation Guideline: |
The modified OEHHA Fish Contaminant Goal for heptachlor epoxide in fish tissue is 0.93 ppb. This screening level assumes an average body weight of 70 kg and a consumption rate of 32 g/day for a 30 year exposure over a 70-year lifetime. This constituent is a carcinogen therefore the risk level is set to one in a million. A cooking reduction factor of 1 is applied for skin-off fillets. (Klasing, S., and R. Brodberg, 2008; OEHHA, 1999) |
Guideline Reference: |
Development of Fish Contaminant Goals and Advisory Tissue Levels for Common Contaminants in California Sport Fish: Chlordane, DDTs, Dieldrin, Methylmercury, PCBs, Selenium, and Toxaphene |
Guideline Reference: |
Public Health Goal for Heptachlor and Heptachlor Epoxide in Drinking Water |
|
Spatial Representation: |
Data was collected from 1 station(s) with the station code(s): 907SDRMPW. |
Temporal Representation: |
Data for this line of evidence were collected between 2014-07-08 and 2014-07-08. When composited fish were collected over multiple days, the first day of fish collection was used as the sample date in the LOE, both for LOE writing, and for averaging period purposes. |
Environmental Conditions: |
|
QAPP Information: |
SWAMP QAPrP 2008, Nagoda and Busse, 2013. Quality Assurance Project Plan for Screening of Cyanotoxins in Lakes/Reservoirs and Coastal Wetlands in the San Diego Region, SWAMP QAPrP 2017 |
QAPP Information Reference(s): |
Quality Assurance Program Plans, Quality Assurance Project Plans, and Standard Operating Procedures for the SWAMP program |
|
Line of Evidence (LOE) for Decision ID 114863, Heptachlor epoxide
|
Region 9 |
Sacred Pond |
|
|
LOE ID: |
134988 |
|
Pollutant: |
Heptachlor epoxide |
LOE Subgroup: |
Pollutant-Tissue |
Matrix: |
Tissue |
Fraction: |
Fish fillet |
|
Beneficial Use: |
Warm Freshwater Habitat |
|
Number of Samples: |
1 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP RWB9 Monitoring data for Sacred Pond to determine beneficial use support and the results are as follows 0 of the 1 samples exceeded the water quality threshold for Heptachlor Epoxide. Data were collected for 1 fish species (1 composite(s) of Largemouth Bass each composed of 3 fish per composite). |
Data Reference: |
Field, Habitat, Sediment, Tissue, Water data for the 2020/2022 integrated report in Region 9. |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
All waters shall be maintained free of toxic substances in concentrations that are toxic to, or that produce detrimental physiological responses in human, plant, animal, or aquatic life (Water Quality Control Plan, San Diego Basin). |
Objective/Criterion Reference: |
Water Quality Control Plan for the San Diego Basin |
|
Evaluation Guideline: |
National Academy of Science guidelines (NAS 1972) establish a maximum Heptachlor Epoxide concentration of 100 ug/Kg (wet weight) in tissue samples for protection of aquatic life from bioaccumulation of toxic substances. |
Guideline Reference: |
National Academy of Sciences. Water Quality Criteria 1972. EPA-R3-73-033. Washington, D.C.: U.S. Environmental Protection Agency |
|
Spatial Representation: |
Data was collected from 1 station(s) with the station code(s): 907SDRMPW. |
Temporal Representation: |
Data for this line of evidence were collected between 2014-07-08 and 2014-07-08. When composited fish were collected over multiple days, the first day of fish collection was used as the sample date in the LOE, both for LOE writing, and for averaging period purposes. |
Environmental Conditions: |
|
QAPP Information: |
SWAMP QAPrP 2008, Nagoda and Busse, 2013. Quality Assurance Project Plan for Screening of Cyanotoxins in Lakes/Reservoirs and Coastal Wetlands in the San Diego Region, SWAMP QAPrP 2017 |
QAPP Information Reference(s): |
Quality Assurance Program Plans, Quality Assurance Project Plans, and Standard Operating Procedures for the SWAMP program |
|
Line of Evidence (LOE) for Decision ID 114864, Hexachlorobenzene/ HCB
|
Region 9 |
Sacred Pond |
|
|
LOE ID: |
135016 |
|
Pollutant: |
Hexachlorobenzene/ HCB |
LOE Subgroup: |
Pollutant-Tissue |
Matrix: |
Tissue |
Fraction: |
Fish fillet |
|
Beneficial Use: |
Commercial or recreational collection of fish, shellfish, or organisms |
|
Number of Samples: |
1 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP RWB9 Monitoring data for Sacred Pond to determine beneficial use support and the results are as follows 0 of the 1 samples exceeded the water quality threshold for Hexachlorobenzene. Data were collected for 1 fish species (1 composite(s) of Largemouth Bass each composed of 3 fish per composite). |
Data Reference: |
Field, Habitat, Sediment, Tissue, Water data for the 2020/2022 integrated report in Region 9. |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
All waters shall be maintained free of toxic substances in concentrations that are toxic to, or that produce detrimental physiological responses in human, plant, animal, or aquatic life (Water Quality Control Plan, San Diego Basin). |
Objective/Criterion Reference: |
Water Quality Control Plan for the San Diego Basin |
|
Evaluation Guideline: |
The modified OEHHA Fish Contaminant Goal for hexachlorobenzene in fish tissue is 2.8 ppb. This screening level assumes an average body weight of 70 kg and a consumption rate of 32 g/day for a 30 year exposure over a 70-year lifetime. This constituent is a carcinogen therefore the risk level is set to one in a million. A cooking reduction factor of 1 is applied for skin-off fillets. (Klasing, S., and R. Brodberg, 2008; OEHHA, 2005) |
Guideline Reference: |
Development of Fish Contaminant Goals and Advisory Tissue Levels for Common Contaminants in California Sport Fish: Chlordane, DDTs, Dieldrin, Methylmercury, PCBs, Selenium, and Toxaphene |
Guideline Reference: |
Air Toxics Hotspots Program Risk Assessment Guidelines. Part ll Technical Support Document for Describing Available Cancer Potency Values. |
|
Spatial Representation: |
Data was collected from 1 station(s) with the station code(s): 907SDRMPW. |
Temporal Representation: |
Data for this line of evidence were collected between 2014-07-08 and 2014-07-08. When composited fish were collected over multiple days, the first day of fish collection was used as the sample date in the LOE, both for LOE writing, and for averaging period purposes. |
Environmental Conditions: |
|
QAPP Information: |
SWAMP QAPrP 2008, Nagoda and Busse, 2013. Quality Assurance Project Plan for Screening of Cyanotoxins in Lakes/Reservoirs and Coastal Wetlands in the San Diego Region, SWAMP QAPrP 2017 |
QAPP Information Reference(s): |
Quality Assurance Program Plans, Quality Assurance Project Plans, and Standard Operating Procedures for the SWAMP program |
|
Line of Evidence (LOE) for Decision ID 114865, Lindane/gamma Hexachlorocyclohexane (gamma-HCH)
|
Region 9 |
Sacred Pond |
|
|
LOE ID: |
135107 |
|
Pollutant: |
Lindane/gamma Hexachlorocyclohexane (gamma-HCH) |
LOE Subgroup: |
Pollutant-Tissue |
Matrix: |
Tissue |
Fraction: |
Fish fillet |
|
Beneficial Use: |
Commercial or recreational collection of fish, shellfish, or organisms |
|
Number of Samples: |
1 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP RWB9 Monitoring data for Sacred Pond to determine beneficial use support and the results are as follows 0 of the 1 samples exceeded the water quality threshold for HCH, gamma-. Data were collected for 1 fish species (1 composite(s) of Largemouth Bass each composed of 3 fish per composite). |
Data Reference: |
Field, Habitat, Sediment, Tissue, Water data for the 2020/2022 integrated report in Region 9. |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
All waters shall be maintained free of toxic substances in concentrations that are toxic to, or that produce detrimental physiological responses in human, plant, animal, or aquatic life (Water Quality Control Plan, San Diego Basin). |
Objective/Criterion Reference: |
Water Quality Control Plan for the San Diego Basin |
|
Evaluation Guideline: |
The modified OEHHA Fish Contaminant Goal for lindane in fish tissue is 4.6 ppb. This screening level assumes an average body weight of 70 kg and a consumption rate of 32 g/day for a 30 year exposure over a 70-year lifetime. This constituent is a carcinogen therefore the risk level is set to one in a million. A cooking reduction factor of 1 is applied for skin-off fillets. (Klasing, S., and R. Brodberg, 2008; OEHHA, 2005) |
Guideline Reference: |
Development of Fish Contaminant Goals and Advisory Tissue Levels for Common Contaminants in California Sport Fish: Chlordane, DDTs, Dieldrin, Methylmercury, PCBs, Selenium, and Toxaphene |
Guideline Reference: |
Air Toxics Hotspots Program Risk Assessment Guidelines. Part ll Technical Support Document for Describing Available Cancer Potency Values. |
|
Spatial Representation: |
Data was collected from 1 station(s) with the station code(s): 907SDRMPW. |
Temporal Representation: |
Data for this line of evidence were collected between 2014-07-08 and 2014-07-08. When composited fish were collected over multiple days, the first day of fish collection was used as the sample date in the LOE, both for LOE writing, and for averaging period purposes. |
Environmental Conditions: |
|
QAPP Information: |
SWAMP QAPrP 2008, Nagoda and Busse, 2013. Quality Assurance Project Plan for Screening of Cyanotoxins in Lakes/Reservoirs and Coastal Wetlands in the San Diego Region, SWAMP QAPrP 2017 |
QAPP Information Reference(s): |
Quality Assurance Program Plans, Quality Assurance Project Plans, and Standard Operating Procedures for the SWAMP program |
|
Line of Evidence (LOE) for Decision ID 114865, Lindane/gamma Hexachlorocyclohexane (gamma-HCH)
|
Region 9 |
Sacred Pond |
|
|
LOE ID: |
135119 |
|
Pollutant: |
Lindane/gamma Hexachlorocyclohexane (gamma-HCH) |
LOE Subgroup: |
Pollutant-Tissue |
Matrix: |
Tissue |
Fraction: |
Fish fillet |
|
Beneficial Use: |
Warm Freshwater Habitat |
|
Number of Samples: |
1 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP RWB9 Monitoring data for Sacred Pond to determine beneficial use support and the results are as follows 0 of the 1 samples exceeded the water quality threshold for HCH, gamma-. Data were collected for 1 fish species (1 composite(s) of Largemouth Bass each composed of 3 fish per composite). |
Data Reference: |
Field, Habitat, Sediment, Tissue, Water data for the 2020/2022 integrated report in Region 9. |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
All waters shall be maintained free of toxic substances in concentrations that are toxic to, or that produce detrimental physiological responses in human, plant, animal, or aquatic life (Water Quality Control Plan, San Diego Basin). |
Objective/Criterion Reference: |
Water Quality Control Plan for the San Diego Basin |
|
Evaluation Guideline: |
National Academy of Science guidelines (NAS 1972) establish a maximum Lindane concentration of 100 ug/Kg (wet weight) in tissue samples for protection of aquatic life from bioaccumulation of toxic substances. |
Guideline Reference: |
National Academy of Sciences. Water Quality Criteria 1972. EPA-R3-73-033. Washington, D.C.: U.S. Environmental Protection Agency |
|
Spatial Representation: |
Data was collected from 1 station(s) with the station code(s): 907SDRMPW. |
Temporal Representation: |
Data for this line of evidence were collected between 2014-07-08 and 2014-07-08. When composited fish were collected over multiple days, the first day of fish collection was used as the sample date in the LOE, both for LOE writing, and for averaging period purposes. |
Environmental Conditions: |
|
QAPP Information: |
SWAMP QAPrP 2008, Nagoda and Busse, 2013. Quality Assurance Project Plan for Screening of Cyanotoxins in Lakes/Reservoirs and Coastal Wetlands in the San Diego Region, SWAMP QAPrP 2017 |
QAPP Information Reference(s): |
Quality Assurance Program Plans, Quality Assurance Project Plans, and Standard Operating Procedures for the SWAMP program |
|
Line of Evidence (LOE) for Decision ID 128222, Mercury
|
Region 9 |
Sacred Pond |
|
|
LOE ID: |
221067 |
|
Pollutant: |
Mercury |
LOE Subgroup: |
Pollutant-Tissue |
Matrix: |
Tissue |
Fraction: |
Fish fillet |
|
Beneficial Use: |
Wildlife Habitat |
|
Number of Samples: |
1 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP RWB9 Monitoring data for Sacred Pond to determine beneficial use support and the results are as follows: 0 of the 1 samples exceeded the water quality threshold for Mercury. This LOE contains data only for trophic level 4 fish. The concentration of Mercury in fish collected within the same calendar year, for the same trophic level were averaged into a single sample for comparison with the objective. A total of 3 fish were aggregated into 1 annual averages, which consisted of 1 fish species (1 composite(s) of Largemouth Bass each composed of 3 fish per composite). This LOE does not contain data from fish who's average length was outside of the legal size limits as described by the California Department of Fish and Wildlife Fishing Regulations. |
Data Reference: |
Field, Habitat, Sediment, Tissue, Water data for the 2020/2022 integrated report in Region 9. |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
All waters shall be maintained free of toxic substances in concentrations that are toxic to, or that produce detrimental physiological responses in human, plant, animal, or aquatic life (Water Quality Control Plan, San Diego Basin). |
Objective/Criterion Reference: |
Water Quality Control Plan for the San Diego Basin |
|
Evaluation Guideline: |
The Statewide Sport Fish Water Quality Objective for the protection of Wildlife Habitat comes from the Statewide Water Quality Control Plan for Inland Surface Waters, Enclosed Bays, and Estuaries of California, and is 0.2 mg/Kg wet weight skinless fillet samples of trophic level 3, or trophic level 4 fish (whichever is highest in the water body) over a one year averaging period. If trophic level 3 fish are used in the assessment then the Prey Fish Water Quality Objective must also be used to determine that the Sport Fish Objective is being met. Trophic levels of applicable fish are defined in, but not limited to those in Attachment C of the Final Regulatory Language document (Appendix A) of State Water Resources Control Board Resolution No. 2017-0027. |
Guideline Reference: |
Inland Surface Waters, Enclosed Bays, and Estuaries Plan. Part 1: Trash Provisions; Part 2: Tribal Subsistence Beneficial Uses and Mercury Provisions; Part 3: Bacteria Provisions and Variance Policy |
|
Spatial Representation: |
Data was collected from 1 station(s) with the station code(s): 907SDRMPW. |
Temporal Representation: |
Data for this line of evidence were collected between 2014-07-08 and 2014-07-08. When composited fish were collected over multiple days, the first day of fish collection was used as the sample date in the LOE, both for LOE writing, and for averaging period purposes. |
Environmental Conditions: |
|
QAPP Information: |
SWAMP QAPrP 2008, Nagoda and Busse, 2013. Quality Assurance Project Plan for Screening of Cyanotoxins in Lakes/Reservoirs and Coastal Wetlands in the San Diego Region, SWAMP QAPrP 2017 |
QAPP Information Reference(s): |
Quality Assurance Program Plans, Quality Assurance Project Plans, and Standard Operating Procedures for the SWAMP program |
|
Line of Evidence (LOE) for Decision ID 128222, Mercury
|
Region 9 |
Sacred Pond |
|
|
LOE ID: |
221219 |
|
Pollutant: |
Mercury |
LOE Subgroup: |
Pollutant-Tissue |
Matrix: |
Tissue |
Fraction: |
Fish fillet |
|
Beneficial Use: |
Commercial or recreational collection of fish, shellfish, or organisms |
|
Number of Samples: |
1 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP RWB9 Monitoring data for Sacred Pond to determine beneficial use support and the results are as follows: 0 of the 1 samples exceeded the water quality threshold for Mercury. This LOE contains data only for trophic level 4 fish. The concentration of Mercury in fish collected within the same calendar year, for the same trophic level were averaged into a single sample for comparison with the objective. A total of 3 fish were aggregated into 1 annual averages, which consisted of 1 fish species (1 composite(s) of Largemouth Bass each composed of 3 fish per composite). This LOE does not contain data from fish who's average length was outside of the legal size limits as described by the California Department of Fish and Wildlife Fishing Regulations. |
Data Reference: |
Field, Habitat, Sediment, Tissue, Water data for the 2020/2022 integrated report in Region 9. |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
All waters shall be maintained free of toxic substances in concentrations that are toxic to, or that produce detrimental physiological responses in human, plant, animal, or aquatic life (Water Quality Control Plan, San Diego Basin). |
Objective/Criterion Reference: |
Water Quality Control Plan for the San Diego Basin |
|
Evaluation Guideline: |
The Statewide Sport Fish Water Quality Objective for the protection of the Commercial and Sport Fishing beneficial comes from the Statewide Water Quality Control Plan for Inland Surface Waters, Enclosed Bays, and Estuaries of California, and is 0.2 mg/Kg wet weight skinless fillet samples of trophic level 3, or trophic level 4 fish (whichever is highest in the water body) over a one year averaging period. Trophic levels of applicable fish are defined in, but not limited to those in Attachment C of the Final Regulatory Language document (Appendix A) of State Water Resources Control Board Resolution No. 2017-0027. |
Guideline Reference: |
Inland Surface Waters, Enclosed Bays, and Estuaries Plan. Part 1: Trash Provisions; Part 2: Tribal Subsistence Beneficial Uses and Mercury Provisions; Part 3: Bacteria Provisions and Variance Policy |
|
Spatial Representation: |
Data was collected from 1 station(s) with the station code(s): 907SDRMPW. |
Temporal Representation: |
Data for this line of evidence were collected between 2014-07-08 and 2014-07-08. When composited fish were collected over multiple days, the first day of fish collection was used as the sample date in the LOE, both for LOE writing, and for averaging period purposes. |
Environmental Conditions: |
|
QAPP Information: |
SWAMP QAPrP 2008, Nagoda and Busse, 2013. Quality Assurance Project Plan for Screening of Cyanotoxins in Lakes/Reservoirs and Coastal Wetlands in the San Diego Region, SWAMP QAPrP 2017 |
QAPP Information Reference(s): |
Quality Assurance Program Plans, Quality Assurance Project Plans, and Standard Operating Procedures for the SWAMP program |
|
Line of Evidence (LOE) for Decision ID 128222, Mercury
|
Region 9 |
Sacred Pond |
|
|
LOE ID: |
221218 |
|
Pollutant: |
Mercury |
LOE Subgroup: |
Pollutant-Tissue |
Matrix: |
Tissue |
Fraction: |
Fish fillet |
|
Beneficial Use: |
Commercial or recreational collection of fish, shellfish, or organisms |
|
Number of Samples: |
1 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP RWB9 Monitoring data for Sacred Pond to determine beneficial use support and the results are as follows: 0 of the 1 samples exceeded the water quality threshold for Mercury. This LOE contains data only for trophic level 4 fish. The concentration of Mercury in fish collected within the same calendar year, for the same trophic level were averaged into a single sample for comparison with the objective. A total of 3 fish were aggregated into 1 annual averages, which consisted of 1 fish species (1 composite(s) of Largemouth Bass each composed of 3 fish per composite). |
Data Reference: |
Field, Habitat, Sediment, Tissue, Water data for the 2020/2022 integrated report in Region 9. |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
All waters shall be maintained free of toxic substances in concentrations that are toxic to, or that produce detrimental physiological responses in human, plant, animal, or aquatic life (Water Quality Control Plan, San Diego Basin). |
Objective/Criterion Reference: |
Water Quality Control Plan for the San Diego Basin |
|
Evaluation Guideline: |
The Statewide Sport Fish Water Quality Objective for the protection of the Commercial and Sport Fishing beneficial comes from the Statewide Water Quality Control Plan for Inland Surface Waters, Enclosed Bays, and Estuaries of California, and is 0.2 mg/Kg wet weight skinless fillet samples of trophic level 3, or trophic level 4 fish (whichever is highest in the water body) over a one year averaging period. Trophic levels of applicable fish are defined in, but not limited to those in Attachment C of the Final Regulatory Language document (Appendix A) of State Water Resources Control Board Resolution No. 2017-0027. |
Guideline Reference: |
Inland Surface Waters, Enclosed Bays, and Estuaries Plan. Part 1: Trash Provisions; Part 2: Tribal Subsistence Beneficial Uses and Mercury Provisions; Part 3: Bacteria Provisions and Variance Policy |
|
Spatial Representation: |
Data was collected from 1 station(s) with the station code(s): 907SDRMPW. |
Temporal Representation: |
Data for this line of evidence were collected between 2014-07-08 and 2014-07-08. When composited fish were collected over multiple days, the first day of fish collection was used as the sample date in the LOE, both for LOE writing, and for averaging period purposes. |
Environmental Conditions: |
|
QAPP Information: |
SWAMP QAPrP 2008, Nagoda and Busse, 2013. Quality Assurance Project Plan for Screening of Cyanotoxins in Lakes/Reservoirs and Coastal Wetlands in the San Diego Region, SWAMP QAPrP 2017 |
QAPP Information Reference(s): |
Quality Assurance Program Plans, Quality Assurance Project Plans, and Standard Operating Procedures for the SWAMP program |
|
Line of Evidence (LOE) for Decision ID 128222, Mercury
|
Region 9 |
Sacred Pond |
|
|
LOE ID: |
221066 |
|
Pollutant: |
Mercury |
LOE Subgroup: |
Pollutant-Tissue |
Matrix: |
Tissue |
Fraction: |
Fish fillet |
|
Beneficial Use: |
Wildlife Habitat |
|
Number of Samples: |
1 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP RWB9 Monitoring data for Sacred Pond to determine beneficial use support and the results are as follows: 0 of the 1 samples exceeded the water quality threshold for Mercury. This LOE contains data only for trophic level 4 fish. The concentration of Mercury in fish collected within the same calendar year, for the same trophic level were averaged into a single sample for comparison with the objective. A total of 3 fish were aggregated into 1 annual averages, which consisted of 1 fish species (1 composite(s) of Largemouth Bass each composed of 3 fish per composite). |
Data Reference: |
Field, Habitat, Sediment, Tissue, Water data for the 2020/2022 integrated report in Region 9. |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
All waters shall be maintained free of toxic substances in concentrations that are toxic to, or that produce detrimental physiological responses in human, plant, animal, or aquatic life (Water Quality Control Plan, San Diego Basin). |
Objective/Criterion Reference: |
Water Quality Control Plan for the San Diego Basin |
|
Evaluation Guideline: |
The Statewide Sport Fish Water Quality Objective for the protection of Wildlife Habitat comes from the Statewide Water Quality Control Plan for Inland Surface Waters, Enclosed Bays, and Estuaries of California, and is 0.2 mg/Kg wet weight skinless fillet samples of trophic level 3, or trophic level 4 fish (whichever is highest in the water body) over a one year averaging period. If trophic level 3 fish are used in the assessment then the Prey Fish Water Quality Objective must also be used to determine that the Sport Fish Objective is being met. Trophic levels of applicable fish are defined in, but not limited to those in Attachment C of the Final Regulatory Language document (Appendix A) of State Water Resources Control Board Resolution No. 2017-0027. |
Guideline Reference: |
Inland Surface Waters, Enclosed Bays, and Estuaries Plan. Part 1: Trash Provisions; Part 2: Tribal Subsistence Beneficial Uses and Mercury Provisions; Part 3: Bacteria Provisions and Variance Policy |
|
Spatial Representation: |
Data was collected from 1 station(s) with the station code(s): 907SDRMPW. |
Temporal Representation: |
Data for this line of evidence were collected between 2014-07-08 and 2014-07-08. When composited fish were collected over multiple days, the first day of fish collection was used as the sample date in the LOE, both for LOE writing, and for averaging period purposes. |
Environmental Conditions: |
|
QAPP Information: |
SWAMP QAPrP 2008, Nagoda and Busse, 2013. Quality Assurance Project Plan for Screening of Cyanotoxins in Lakes/Reservoirs and Coastal Wetlands in the San Diego Region, SWAMP QAPrP 2017 |
QAPP Information Reference(s): |
Quality Assurance Program Plans, Quality Assurance Project Plans, and Standard Operating Procedures for the SWAMP program |
|
Line of Evidence (LOE) for Decision ID 114866, Mirex
|
Region 9 |
Sacred Pond |
|
|
LOE ID: |
135049 |
|
Pollutant: |
Mirex |
LOE Subgroup: |
Pollutant-Tissue |
Matrix: |
Tissue |
Fraction: |
Fish fillet |
|
Beneficial Use: |
Commercial or recreational collection of fish, shellfish, or organisms |
|
Number of Samples: |
0 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Waterboard staff assessed SWAMP RWB9 Monitoring data for Sacred Pond to determine beneficial use support and the results are as follows: Zero of Zero samples exceeded the water quality threshold for Mirex. Although data was collected for 1 fish species (1 composite(s) of Largemouth Bass each composed of 3 fish per composite), all 1 sample(s) had to be thrown out due to quantitation issues. |
Data Reference: |
Field, Habitat, Sediment, Tissue, Water data for the 2020/2022 integrated report in Region 9. |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
All waters shall be maintained free of toxic substances in concentrations that are toxic to, or that produce detrimental physiological responses in human, plant, animal, or aquatic life (Water Quality Control Plan, San Diego Basin). |
Objective/Criterion Reference: |
Water Quality Control Plan for the San Diego Basin |
|
Evaluation Guideline: |
The modified OEHHA Fish Contaminant Goal for mirex in fish tissue is 0.28 ppb. This screening level assumes an average body weight of 70 kg and a consumption rate of 32 g/day. This constituent is a carcinogen therefore the risk level is set to one in a million. A cooking reduction factor of 1 is applied for skin-off fillets. (Klasing, S., and R. Brodberg, 2008; OEHHA, 1992) |
Guideline Reference: |
Development of Fish Contaminant Goals and Advisory Tissue Levels for Common Contaminants in California Sport Fish: Chlordane, DDTs, Dieldrin, Methylmercury, PCBs, Selenium, and Toxaphene |
Guideline Reference: |
Expedited Cancer Potency Values and Proposed Regulatory Levels for Certain Proposition 65 Carcinogens. |
|
Spatial Representation: |
Data was collected from 1 station(s) with the station code(s): 907SDRMPW. |
Temporal Representation: |
Data for this line of evidence were collected between 2014-07-08 and 2014-07-08. When composited fish were collected over multiple days, the first day of fish collection was used as the sample date in the LOE, both for LOE writing, and for averaging period purposes. |
Environmental Conditions: |
|
QAPP Information: |
SWAMP QAPrP 2008, Nagoda and Busse, 2013. Quality Assurance Project Plan for Screening of Cyanotoxins in Lakes/Reservoirs and Coastal Wetlands in the San Diego Region, SWAMP QAPrP 2017 |
QAPP Information Reference(s): |
Quality Assurance Program Plans, Quality Assurance Project Plans, and Standard Operating Procedures for the SWAMP program |
|
Line of Evidence (LOE) for Decision ID 114867, Selenium
|
Region 9 |
Sacred Pond |
|
|
LOE ID: |
134917 |
|
Pollutant: |
Selenium |
LOE Subgroup: |
Pollutant-Tissue |
Matrix: |
Tissue |
Fraction: |
Fish fillet |
|
Beneficial Use: |
Commercial or recreational collection of fish, shellfish, or organisms |
|
Number of Samples: |
1 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP RWB9 Monitoring data for Sacred Pond to determine beneficial use support and the results are as follows 0 of the 1 samples exceeded the water quality threshold for Selenium. Data were collected for 1 fish species (1 composite(s) of Largemouth Bass each composed of 3 fish per composite). |
Data Reference: |
Field, Habitat, Sediment, Tissue, Water data for the 2020/2022 integrated report in Region 9. |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
All waters shall be maintained free of toxic substances in concentrations that are toxic to, or that produce detrimental physiological responses in human, plant, animal, or aquatic life (Water Quality Control Plan, San Diego Basin). |
Objective/Criterion Reference: |
Water Quality Control Plan for the San Diego Basin |
|
Evaluation Guideline: |
The OEHHA Fish Contaminant Goal for selenium in fish tissue is 7.4 ppm. This screening level assumes an average body weight of 70 kg and a consumption rate of 32 g/day. A background dietary consumption rate of 0.114 mg/day is applied for this micronutrient. (Klasing, S., and R. Brodberg, 2008) |
Guideline Reference: |
Development of Fish Contaminant Goals and Advisory Tissue Levels for Common Contaminants in California Sport Fish: Chlordane, DDTs, Dieldrin, Methylmercury, PCBs, Selenium, and Toxaphene |
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Spatial Representation: |
Data was collected from 1 station(s) with the station code(s): 907SDRMPW. |
Temporal Representation: |
Data for this line of evidence were collected between 2014-07-08 and 2014-07-08. When composited fish were collected over multiple days, the first day of fish collection was used as the sample date in the LOE, both for LOE writing, and for averaging period purposes. |
Environmental Conditions: |
|
QAPP Information: |
SWAMP QAPrP 2008, Nagoda and Busse, 2013. Quality Assurance Project Plan for Screening of Cyanotoxins in Lakes/Reservoirs and Coastal Wetlands in the San Diego Region, SWAMP QAPrP 2017 |
QAPP Information Reference(s): |
Quality Assurance Program Plans, Quality Assurance Project Plans, and Standard Operating Procedures for the SWAMP program |
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Line of Evidence (LOE) for Decision ID 126595, Total DDT (sum of 4,4'- and 2,4'- isomers of DDT, DDE, and DDD)
|
Region 9 |
Sacred Pond |
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LOE ID: |
135143 |
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Pollutant: |
Total DDT (sum of 4,4'- and 2,4'- isomers of DDT, DDE, and DDD) |
LOE Subgroup: |
Pollutant-Tissue |
Matrix: |
Tissue |
Fraction: |
Fish fillet |
|
Beneficial Use: |
Commercial or recreational collection of fish, shellfish, or organisms |
|
Number of Samples: |
1 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP RWB9 Monitoring data for Sacred Pond to determine beneficial use support and the results are as follows 0 of the 1 samples exceeded the water quality threshold for Total DDT (sum of 4,4'- and 2,4'- isomers of DDT, DDE, and DDD). Data were collected for 1 fish species (1 composite(s) of Largemouth Bass each composed of 3 fish per composite). |
Data Reference: |
Field, Habitat, Sediment, Tissue, Water data for the 2020/2022 integrated report in Region 9. |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
All waters shall be maintained free of toxic substances in concentrations that are toxic to, or that produce detrimental physiological responses in human, plant, animal, or aquatic life (Water Quality Control Plan, San Diego Basin). |
Objective/Criterion Reference: |
Water Quality Control Plan for the San Diego Basin |
|
Evaluation Guideline: |
The modified OEHHA Fish Contaminant Goal for total DDT in fish tissue is 15 ppb. This screening level assumes an average body weight of 70 kg and a consumption rate of 32 g/day for a 30 year exposure over a 70-year lifetime. This constituent is a carcinogen therefore the risk level is set to one in a million. A cooking reduction factor of 1 is applied for skin-off fillets. (Klasing, S., and R. Brodberg, 2008) |
Guideline Reference: |
Development of Fish Contaminant Goals and Advisory Tissue Levels for Common Contaminants in California Sport Fish: Chlordane, DDTs, Dieldrin, Methylmercury, PCBs, Selenium, and Toxaphene |
|
Spatial Representation: |
Data was collected from 1 station(s) with the station code(s): 907SDRMPW. |
Temporal Representation: |
Data for this line of evidence were collected between 2014-07-08 and 2014-07-08. When composited fish were collected over multiple days, the first day of fish collection was used as the sample date in the LOE, both for LOE writing, and for averaging period purposes. |
Environmental Conditions: |
|
QAPP Information: |
SWAMP QAPrP 2008, Nagoda and Busse, 2013. Quality Assurance Project Plan for Screening of Cyanotoxins in Lakes/Reservoirs and Coastal Wetlands in the San Diego Region, SWAMP QAPrP 2017 |
QAPP Information Reference(s): |
Quality Assurance Program Plans, Quality Assurance Project Plans, and Standard Operating Procedures for the SWAMP program |
|
Line of Evidence (LOE) for Decision ID 126595, Total DDT (sum of 4,4'- and 2,4'- isomers of DDT, DDE, and DDD)
|
Region 9 |
Sacred Pond |
|
|
LOE ID: |
134934 |
|
Pollutant: |
Total DDT (sum of 4,4'- and 2,4'- isomers of DDT, DDE, and DDD) |
LOE Subgroup: |
Pollutant-Tissue |
Matrix: |
Tissue |
Fraction: |
Fish fillet |
|
Beneficial Use: |
Warm Freshwater Habitat |
|
Number of Samples: |
1 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP RWB9 Monitoring data for Sacred Pond to determine beneficial use support and the results are as follows 0 of the 1 samples exceeded the water quality threshold for Total DDT (sum of 4,4'- and 2,4'- isomers of DDT, DDE, and DDD). Data were collected for 1 fish species (1 composite(s) of Largemouth Bass each composed of 3 fish per composite). |
Data Reference: |
Field, Habitat, Sediment, Tissue, Water data for the 2020/2022 integrated report in Region 9. |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
All waters shall be maintained free of toxic substances in concentrations that are toxic to, or that produce detrimental physiological responses in human, plant, animal, or aquatic life (Water Quality Control Plan, San Diego Basin). |
Objective/Criterion Reference: |
Water Quality Control Plan for the San Diego Basin |
|
Evaluation Guideline: |
National Academy of Science guidelines (NAS 1972) establish a maximum total DDT concentration of 1000 ug/Kg (wet weight) in tissue samples for protection of aquatic life from bioaccumulation of toxic substances. |
Guideline Reference: |
National Academy of Sciences. Water Quality Criteria 1972. EPA-R3-73-033. Washington, D.C.: U.S. Environmental Protection Agency |
|
Spatial Representation: |
Data was collected from 1 station(s) with the station code(s): 907SDRMPW. |
Temporal Representation: |
Data for this line of evidence were collected between 2014-07-08 and 2014-07-08. When composited fish were collected over multiple days, the first day of fish collection was used as the sample date in the LOE, both for LOE writing, and for averaging period purposes. |
Environmental Conditions: |
|
QAPP Information: |
SWAMP QAPrP 2008, Nagoda and Busse, 2013. Quality Assurance Project Plan for Screening of Cyanotoxins in Lakes/Reservoirs and Coastal Wetlands in the San Diego Region, SWAMP QAPrP 2017 |
QAPP Information Reference(s): |
Quality Assurance Program Plans, Quality Assurance Project Plans, and Standard Operating Procedures for the SWAMP program |
|