Line of Evidence (LOE) for Decision ID 113572, Alkalinity as CaCO3
|
Region 9 |
Fry Creek |
|
|
LOE ID: |
139604 |
|
Pollutant: |
Alkalinity as CaCO3 |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Total |
|
Beneficial Use: |
Cold Freshwater Habitat |
|
Number of Samples: |
2 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP RWB9 Monitoring data for Fry Creek to determine beneficial use support and results are as follows: 0 of 2 samples exceeded the water quality threshold for Alkalinity as CaCO3. |
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 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 CCC of 20mg/L is a minimum value except where alkalinity is naturally lower, in which case the criterion cannot be lower than 25% of the natural level (USEPA National Recommended Water Quality Criteria Aquatic Life) |
Guideline Reference: |
National Recommended Water Quality Criteria. United States Environmental Protection Agency. Office of Water. Office of Science and Technology |
|
Spatial Representation: |
The samples were collected at 1 monitoring site (903SLFRCx) |
Temporal Representation: |
The samples were collected between the dates of 2015-05-22 and 2017-05-03 |
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 113572, Alkalinity as CaCO3
|
Region 9 |
Fry Creek |
|
|
LOE ID: |
139794 |
|
Pollutant: |
Alkalinity as CaCO3 |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Total |
|
Beneficial Use: |
Warm Freshwater Habitat |
|
Number of Samples: |
2 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP RWB9 Monitoring data for Fry Creek to determine beneficial use support and results are as follows: 0 of 2 samples exceeded the water quality threshold for Alkalinity as CaCO3. |
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 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 CCC of 20mg/L is a minimum value except where alkalinity is naturally lower, in which case the criterion cannot be lower than 25% of the natural level (USEPA National Recommended Water Quality Criteria Aquatic Life) |
Guideline Reference: |
National Recommended Water Quality Criteria. United States Environmental Protection Agency. Office of Water. Office of Science and Technology |
|
Spatial Representation: |
The samples were collected at 1 monitoring site (903SLFRCx) |
Temporal Representation: |
The samples were collected between the dates of 2015-05-22 and 2017-05-03 |
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 127831, Ammonia
|
Region 9 |
Fry Creek |
|
|
LOE ID: |
185091 |
|
Pollutant: |
Nitrogen, ammonia (Total Ammonia) |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Total |
|
Beneficial Use: |
Warm Freshwater Habitat |
|
Number of Samples: |
2 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP RWB9 Monitoring data for Fry Creek to determine beneficial use support and results are as follows: 0 of 2 samples exceeded the water quality threshold for Ammonia as N. |
Data Reference: |
Field, Habitat, Sediment, Tissue, Water data for the 2020/2022 integrated report in Region 9. |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
The Total Ammonia criterion continuous concentration (expressed as a 30-day average) to protect aquatic life in freshwater is Temperature and pH dependent, and was calculated according to the formula listed in the Aquatic Life Ambient Water Quality Criteria for Ammonia - Freshwater 2013 document. |
Objective/Criterion Reference: |
Aquatic Life Ambient Water Quality Criteria for Ammonia - Freshwater 2013 |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
The samples were collected at 1 monitoring site (903SLFRCx) |
Temporal Representation: |
The samples were collected between the dates of 2015-05-22 and 2017-05-03 |
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 127831, Ammonia
|
Region 9 |
Fry Creek |
|
|
LOE ID: |
185297 |
|
Pollutant: |
Nitrogen, ammonia (Total Ammonia) |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Total |
|
Beneficial Use: |
Cold Freshwater Habitat |
|
Number of Samples: |
2 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP RWB9 Monitoring data for Fry Creek to determine beneficial use support and results are as follows: 0 of 2 samples exceeded the water quality threshold for Ammonia as N. |
Data Reference: |
Field, Habitat, Sediment, Tissue, Water data for the 2020/2022 integrated report in Region 9. |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
The Total Ammonia criterion continuous concentration (expressed as a 30-day average) to protect aquatic life in freshwater is Temperature and pH dependent, and was calculated according to the formula listed in the Aquatic Life Ambient Water Quality Criteria for Ammonia - Freshwater 2013 document. |
Objective/Criterion Reference: |
Aquatic Life Ambient Water Quality Criteria for Ammonia - Freshwater 2013 |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
The samples were collected at 1 monitoring site (903SLFRCx) |
Temporal Representation: |
The samples were collected between the dates of 2015-05-22 and 2017-05-03 |
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 115535, Ammonia (Unionized)
|
Region 9 |
Fry Creek |
|
|
LOE ID: |
185529 |
|
Pollutant: |
Ammonia (Unionized) |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Total |
|
Beneficial Use: |
Warm Freshwater Habitat |
|
Number of Samples: |
1 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP RWB9 Monitoring data for Fry Creek to determine beneficial use support and the results are as follows: 0 of the 1 samples exceeded the water quality threshold for Ammonia as N, Unionized. Although a total of 2 samples were collected, 1 of these samples were not included in the assessment because the laboratory data reporting limit(s) was above the water quality threshold and therefore the results could not be quantified with the level of certainty required by the Listing Policy Section 6.1.5.5. |
Data Reference: |
Field, Habitat, Sediment, Tissue, Water data for the 2020/2022 integrated report in Region 9. |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
The discharge of wastes shall not cause concentrations of un-ionized ammonia (NH3) to exceed 0.025 mg/l (as N) in inland surface waters, enclosed bays and estuaries and coastal lagoons (Water Quality Control Plan, San Diego Basin). |
Objective/Criterion Reference: |
Water Quality Control Plan for the San Diego Basin |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
The samples were collected at 1 monitoring site (903SLFRCx). |
Temporal Representation: |
Data for this waterbody was collected over the date range 2015-05-22 to 2017-05-03 |
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 115535, Ammonia (Unionized)
|
Region 9 |
Fry Creek |
|
|
LOE ID: |
185521 |
|
Pollutant: |
Ammonia (Unionized) |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Total |
|
Beneficial Use: |
Cold Freshwater Habitat |
|
Number of Samples: |
1 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP RWB9 Monitoring data for Fry Creek to determine beneficial use support and the results are as follows: 0 of the 1 samples exceeded the water quality threshold for Ammonia as N, Unionized. Although a total of 2 samples were collected, 1 of these samples were not included in the assessment because the laboratory data reporting limit(s) was above the water quality threshold and therefore the results could not be quantified with the level of certainty required by the Listing Policy Section 6.1.5.5. |
Data Reference: |
Field, Habitat, Sediment, Tissue, Water data for the 2020/2022 integrated report in Region 9. |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
The discharge of wastes shall not cause concentrations of un-ionized ammonia (NH3) to exceed 0.025 mg/l (as N) in inland surface waters, enclosed bays and estuaries and coastal lagoons (Water Quality Control Plan, San Diego Basin). |
Objective/Criterion Reference: |
Water Quality Control Plan for the San Diego Basin |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
The samples were collected at 1 monitoring site (903SLFRCx). |
Temporal Representation: |
Data for this waterbody was collected over the date range 2015-05-22 to 2017-05-03 |
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 126066, Benthic Community Effects
|
Region 9 |
Fry Creek |
|
|
LOE ID: |
215626 |
|
Pollutant: |
Benthic-Macroinvertebrate Bioassessments |
LOE Subgroup: |
Population/Community Degradation |
Matrix: |
Water |
Fraction: |
None |
|
Beneficial Use: |
Cold Freshwater Habitat |
|
Number of Samples: |
2 |
Number of Exceedances: |
2 |
|
Data and Information Type: |
Benthic macroinvertebrate surveys |
Data Used to Assess Water Quality: |
Water Board staff assessed data for 903SLFRCx to determine beneficial use support and the results are as follows: 2 of 2 samples exceeded the threshold. CSCI scores were from 0.5595 to 0.7077 . |
Data Reference: |
California Stream Condition Index Scores for the 2020 Integrated Report |
|
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 or animal, or aquatic life. Compliance with this objective will be determined by use of indicator organisms, analysis of species diversity, population density, growth anomalies, bioassays of appropriate duration, or other appropriate methods as specified by the Regional Board. Region 9 Basin Plan. |
Objective/Criterion Reference: |
Water Quality Control Plan for the San Diego Basin |
|
Evaluation Guideline: |
The California Stream Condition Index (CSCI) is a biological scoring tool that helps aquatic resource managers translate complex data about benthic macroinvertebrates found living in a stream into an overall measure of stream health. The CSCI score is calculated by comparing the expected condition with actual (observed) results (Rhen, A.C. et al., 2015). CSCI scores range from 0 (highly degraded) to greater than 1 (equivalent to reference). CSCI scoring of biological condition are as follows (per the scientific paper supporting the development of the CSCI scoring tool): greater than or equal to 0.92 = likely intact condition, 0.91 to 0.80 = possibly altered condition, 0.79 to 0.63 = likely altered condition, less than or equal to 0.62 = very likely altered condition. Sites with scores below 0.79 are considered to have exceeded the water quality objective for the aquatic life beneficial use. |
Guideline Reference: |
Bioassessment in complex environments: designing an
index for consistent meaning in different settings
|
|
Spatial Representation: |
Samples were collected from station 903SLFRCx |
Temporal Representation: |
Samples were collected from 5/22/2015 to 5/3/2017. |
Environmental Conditions: |
|
QAPP Information: |
Data collected following SWAMP QA protocols. |
QAPP Information Reference(s): |
Quality Assurance Program Plans, Quality Assurance Project Plans, and Standard Operating Procedures for the SWAMP program |
|
Line of Evidence (LOE) for Decision ID 126066, Benthic Community Effects
|
Region 9 |
Fry Creek |
|
|
LOE ID: |
95921 |
|
Pollutant: |
Benthic-Macroinvertebrate Bioassessments |
LOE Subgroup: |
Population/Community Degradation |
Matrix: |
Water |
Fraction: |
None |
|
Beneficial Use: |
Cold Freshwater Habitat |
|
Number of Samples: |
1 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
Benthic macroinvertebrate surveys |
Data Used to Assess Water Quality: |
The CSCI score for this site is 1.127907, and is therefore not exceeding the water quality objective for the aquatic life beneficial use. This water body also passed several screening criteria and was identified as a reference water body for the purpose of developing the CSCI. Reference sites where human disturbance is absent or minimal are used to set benchmark expectations for healthy streams. A large set of nearly 600 reference sites (see map), representing the broad diversity of natural stream types found across California, was used to develop the CSCI. |
Data Reference: |
Complete data set for all CSCI reference sites for the entire State. |
|
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 or animal, or aquatic life. Compliance with this objective will be determined by use of indicator organisms, analysis of species diversity, population density, growth anomalies, bioassays of appropriate duration, or other appropriate methods as specified by the Regional Board. Region 9 Basin Plan. |
Objective/Criterion Reference: |
Water Quality Control Plan for the San Diego Basin |
|
Evaluation Guideline: |
The California Stream Condition Index (CSCI) is a biological scoring tool that helps aquatic resource managers translate complex data about benthic macroinvertebrates found living in a stream into an overall measure of stream health. The CSCI score is calculated by comparing the expected condition with actual (observed) results (Rhen, A.C. et al., 2015). CSCI scores range from 0 (highly degraded) to greater than 1 (equivalent to reference). CSCI scoring of biological condition are as follows (per the scientific paper supporting the development of the CSCI scoring tool): greater than or equal to 0.92 = likely intact condition, 0.91 to 0.80 = possibly altered condition, 0.79 to 0.63 = likely altered condition, less than or equal to 0.62 = very likely altered condition. Sites with scores below 0.79 are considered to have exceeded the water quality objective for the aquatic life beneficial use. |
Guideline Reference: |
Bioassessment in complex environments: designing an
index for consistent meaning in different settings
|
|
Spatial Representation: |
Samples were collected at the following station: 903SLFRCx (Fry Creek (FRC)). |
Temporal Representation: |
Survey done 5/22/2001. |
Environmental Conditions: |
|
QAPP Information: |
Data collected following SWAMP QA protocols for the RWB9 Status Sampling 2007 and 2008 water quality monitoring project. |
QAPP Information Reference(s): |
RWB9 Status Sampling 2007 and 2008 |
|
Line of Evidence (LOE) for Decision ID 126066, Benthic Community Effects
|
Region 9 |
Fry Creek |
|
|
LOE ID: |
79482 |
|
Pollutant: |
Benthic-Macroinvertebrate Bioassessments |
LOE Subgroup: |
Population/Community Degradation |
Matrix: |
Water |
Fraction: |
None |
|
Beneficial Use: |
Cold Freshwater Habitat |
|
Number of Samples: |
1 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
Benthic macroinvertebrate surveys |
Data Used to Assess Water Quality: |
The CSCI score for this site is above the 0.79 threshold, and is therefore not exceeding the water quality objective for the aquatic life beneficial use. |
Data Reference: |
RWB9 Status Sampling 2007 and 2008 |
|
Region 9 CSCI Scores & Water Body Information |
|
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 or animal, or aquatic life. Compliance with this objective will be determined by use of indicator organisms, analysis of species diversity, population density, growth anomalies, bioassays of appropriate duration, or other appropriate methods as specified by the Regional Board. Region 9 Basin Plan. |
Objective/Criterion Reference: |
Water Quality Control Plan for the San Diego Basin |
|
Evaluation Guideline: |
The California Stream Condition Index (CSCI) is a biological scoring tool that helps aquatic resource managers translate complex data about benthic macroinvertebrates found living in a stream into an overall measure of stream health. The CSCI score is calculated by comparing the expected condition with actual (observed) results (Rhen, A.C. et al., 2015). CSCI scores range from 0 (highly degraded) to greater than 1 (equivalent to reference). CSCI scoring of biological condition are as follows (per the scientific paper supporting the development of the CSCI scoring tool): greater than or equal to 0.92 = likely intact condition, 0.91 to 0.80 = possibly altered condition, 0.79 to 0.63 = likely altered condition, less than or equal to 0.62 = very likely altered condition. Sites with scores below 0.79 are considered to have exceeded the water quality objective for the aquatic life beneficial use. |
Guideline Reference: |
Bioassessment in complex environments: designing an
index for consistent meaning in different settings
|
|
Spatial Representation: |
Samples were collected at the following station: 903SLFRCx (Fry Creek (FRC)). |
Temporal Representation: |
Survey done May 7, 2008. |
Environmental Conditions: |
|
QAPP Information: |
Data collected following SWAMP QA protocols for the RWB9 Status Sampling 2007 and 2008 water quality monitoring project. |
QAPP Information Reference(s): |
RWB9 Status Sampling 2007 and 2008 |
|
Line of Evidence (LOE) for Decision ID 126066, Benthic Community Effects
|
Region 9 |
Fry Creek |
|
|
LOE ID: |
73754 |
|
Pollutant: |
Benthic-Macroinvertebrate Bioassessments |
LOE Subgroup: |
Population/Community Degradation |
Matrix: |
Water |
Fraction: |
None |
|
Beneficial Use: |
Cold Freshwater Habitat |
|
Number of Samples: |
1 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
Benthic macroinvertebrate surveys |
Data Used to Assess Water Quality: |
The IBI score for this water body was 53 which indicates that this water body is not considered to have impaired conditions. |
Data Reference: |
RWB9 Status Sampling 2007 and 2008 |
|
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. |
Objective/Criterion Reference: |
Water Quality Control Plan for the San Diego Basin |
|
Evaluation Guideline: |
The IBI is a multi-metric assessment that employs biological metrics that respond to a habitat or water quality impairment. Each of the biological metrics measured at a site are converted to an IBI score then summed. These cumulative scores are then ranked. For the Southern California IBI, sites with scores below 40 are considered to have impaired conditions. |
Guideline Reference: |
Development of a Benthic Index of Biotic Integrity (B-IBI) for Wadeable Streams in Northern Coastal California and its Application to Regional 305(b) Assessment |
|
Spatial Representation: |
Samples were collected at the following station: 903SLFRCx (Fry Creek (FRC)). |
Temporal Representation: |
Survey done May 7, 2008. |
Environmental Conditions: |
|
QAPP Information: |
Data collected following SWAMP QA protocols for the RWB9 Status Sampling 2007 and 2008 water quality monitoring project. |
QAPP Information Reference(s): |
|
Line of Evidence (LOE) for Decision ID 126066, Benthic Community Effects
|
Region 9 |
Fry Creek |
|
|
LOE ID: |
26387 |
|
Pollutant: |
Benthic Community Effects |
LOE Subgroup: |
Adverse Biological Responses |
Matrix: |
Water |
Fraction: |
None |
|
Beneficial Use: |
Warm Freshwater Habitat |
|
Number of Samples: |
2 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
Benthic macroinvertebrate surveys |
Data Used to Assess Water Quality: |
Two samples of IBI data were taken on May 2001 and June of 2005 at one sampling site. None of the samples exceeded the IBI impairment threshold. |
Data Reference: |
Fish and Game IBI Data |
|
SWAMP Data: |
Non-SWAMP |
|
Water Quality Objective/Criterion: |
From the San Diego Basin Plan the objective is: All waters shall be maintained free of toxic substances in concentrations that are toxic to, or that produce detrimental physiological responses in human, plant, animal, or aquatic life. Compliance with this objective will be determined by use of indicator organisms, analyses of species diversity, population density, growth anomalies, bioassays of appropriate duration, or other appropriate methods as specified by the Regional Board. |
Objective/Criterion Reference: |
Water Quality Control Plan for the San Diego Basin |
|
Evaluation Guideline: |
The Index of Biological Integrity (IBI) is an analytical tool that can be used to assess the biological and physical condition of streams and rivers within a zero to one hundred scoring range: Very Poor 0-19, Poor 20-39, Fair 40-59, Good 60- 79, Very Good 80-100. The IBI score of 39 was set as an impairment threshold because it is a statistical criterion of two standard deviations below the mean reference site score which defines the boundary between 'fair' and 'poor' IBI creek conditions. (Ode, p. 9) |
Guideline Reference: |
A Quantitative Tool for Assessing the Integrity of Southern Coastal California Streams. Environmental Management. Volume 35, number 1 (2005): pp. 1-13
|
|
Spatial Representation: |
Samples were collected at one site: 903FCFCCx on Fry Creek. |
Temporal Representation: |
Sampling occurred during two events on May 2001 and June of 2005. |
Environmental Conditions: |
|
QAPP Information: |
Quality Control for collection and identification was conducted in accordance with the Quality Assurance Project Plan for the California Stream Bioassessment Procedure and the State of California, California Monitoring an Assessment Program: "CMAP", Quality Assurance Project Plan. |
QAPP Information Reference(s): |
Quality Assurance Project Plan for the California Stream Bioassessment Procedure |
QAPP Information Reference(s): |
State of California, California Monitoring and Assessment Program: "CMAP". |
QAPP Information Reference(s): |
The San Diego Stream Team Quality Assurance Project Plan |
|
Line of Evidence (LOE) for Decision ID 113566, Chloride
|
Region 9 |
Fry Creek |
|
|
LOE ID: |
140732 |
|
Pollutant: |
Chloride |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Dissolved |
|
Beneficial Use: |
Cold Freshwater Habitat |
|
Number of Samples: |
2 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP RWB9 Monitoring data for Fry Creek to determine beneficial use support and results are as follows: 0 of 2 samples exceeded the water quality threshold for Chloride. |
Data Reference: |
Field, Habitat, Sediment, Tissue, Water data for the 2020/2022 integrated report in Region 9. |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
The Chloride water quality threshold in this HSA is 250 mg/L, and this concentration is not to be exceeded more than 10% of the time during any one year period (Basin Plan, Table 3-2). |
Objective/Criterion Reference: |
Water Quality Control Plan for the San Diego Basin |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
The samples were collected at 1 monitoring site (903SLFRCx) |
Temporal Representation: |
The samples were collected between the dates of 2015-05-22 and 2017-05-03 |
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 113566, Chloride
|
Region 9 |
Fry Creek |
|
|
LOE ID: |
140891 |
|
Pollutant: |
Chloride |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Dissolved |
|
Beneficial Use: |
Agricultural Supply |
|
Number of Samples: |
2 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP RWB9 Monitoring data for Fry Creek to determine beneficial use support and results are as follows: 0 of 2 samples exceeded the water quality threshold for Chloride. |
Data Reference: |
Field, Habitat, Sediment, Tissue, Water data for the 2020/2022 integrated report in Region 9. |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
The Chloride water quality threshold in this HSA is 250 mg/L, and this concentration is not to be exceeded more than 10% of the time during any one year period (Basin Plan, Table 3-2). |
Objective/Criterion Reference: |
Water Quality Control Plan for the San Diego Basin |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
The samples were collected at 1 monitoring site (903SLFRCx) |
Temporal Representation: |
The samples were collected between the dates of 2015-05-22 and 2017-05-03 |
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 113566, Chloride
|
Region 9 |
Fry Creek |
|
|
LOE ID: |
140890 |
|
Pollutant: |
Chloride |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Dissolved |
|
Beneficial Use: |
Municipal & Domestic Supply |
|
Number of Samples: |
2 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP RWB9 Monitoring data for Fry Creek to determine beneficial use support and results are as follows: 0 of 2 samples exceeded the water quality threshold for Chloride. |
Data Reference: |
Field, Habitat, Sediment, Tissue, Water data for the 2020/2022 integrated report in Region 9. |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
The Chloride water quality threshold in this HSA is 250 mg/L, and this concentration is not to be exceeded more than 10% of the time during any one year period (Basin Plan, Table 3-2). |
Objective/Criterion Reference: |
Water Quality Control Plan for the San Diego Basin |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
The samples were collected at 1 monitoring site (903SLFRCx) |
Temporal Representation: |
The samples were collected between the dates of 2015-05-22 and 2017-05-03 |
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 113566, Chloride
|
Region 9 |
Fry Creek |
|
|
LOE ID: |
141088 |
|
Pollutant: |
Chloride |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Dissolved |
|
Beneficial Use: |
Warm Freshwater Habitat |
|
Number of Samples: |
2 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP RWB9 Monitoring data for Fry Creek to determine beneficial use support and results are as follows: 0 of 2 samples exceeded the water quality threshold for Chloride. |
Data Reference: |
Field, Habitat, Sediment, Tissue, Water data for the 2020/2022 integrated report in Region 9. |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
The Chloride water quality threshold in this HSA is 250 mg/L, and this concentration is not to be exceeded more than 10% of the time during any one year period (Basin Plan, Table 3-2). |
Objective/Criterion Reference: |
Water Quality Control Plan for the San Diego Basin |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
The samples were collected at 1 monitoring site (903SLFRCx) |
Temporal Representation: |
The samples were collected between the dates of 2015-05-22 and 2017-05-03 |
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 113567, Nitrate/Nitrite (Nitrite + Nitrate as N)
|
Region 9 |
Fry Creek |
|
|
LOE ID: |
143752 |
|
Pollutant: |
Nitrate/Nitrite (Nitrite + Nitrate as N) |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Dissolved |
|
Beneficial Use: |
Municipal & Domestic Supply |
|
Number of Samples: |
1 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP RWB9 Monitoring data for Fry Creek to determine beneficial use support and results are as follows: 0 of 1 samples exceeded the water quality threshold for Nitrate + Nitrite as N. |
Data Reference: |
Field, Habitat, Sediment, Tissue, Water data for the 2020/2022 integrated report in Region 9. |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
The California Maximum Contaminant Level for nitrate + nitrite (as N) is 10.0 mg/L (Title 22 of the California Code of Regulations). |
Objective/Criterion Reference: |
Title 22. Division 4. Chapter 15. Sections 64400 et seq. California Code of Regulations |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
The samples were collected at 1 monitoring site (903SLFRCx) |
Temporal Representation: |
The samples were collected between the dates of 2017-05-03 and 2017-05-03 |
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 113567, Nitrate/Nitrite (Nitrite + Nitrate as N)
|
Region 9 |
Fry Creek |
|
|
LOE ID: |
143993 |
|
Pollutant: |
Nitrate/Nitrite (Nitrite + Nitrate as N) |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Total |
|
Beneficial Use: |
Municipal & Domestic Supply |
|
Number of Samples: |
1 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP RWB9 Monitoring data for Fry Creek to determine beneficial use support and results are as follows: 0 of 1 samples exceeded the water quality threshold for Nitrate + Nitrite as N. |
Data Reference: |
Field, Habitat, Sediment, Tissue, Water data for the 2020/2022 integrated report in Region 9. |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
The California Maximum Contaminant Level for nitrate + nitrite (as N) is 10.0 mg/L (Title 22 of the California Code of Regulations). |
Objective/Criterion Reference: |
Title 22. Division 4. Chapter 15. Sections 64400 et seq. California Code of Regulations |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
The samples were collected at 1 monitoring site (903SLFRCx) |
Temporal Representation: |
The samples were collected between the dates of 2015-05-22 and 2015-05-22 |
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 127572, Nitrogen
|
Region 9 |
Fry Creek |
|
|
LOE ID: |
144028 |
|
Pollutant: |
Total Nitrogen as N |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Total |
|
Beneficial Use: |
Cold Freshwater Habitat |
|
Number of Samples: |
2 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP RWB9 Monitoring data for Fry Creek to determine beneficial use support and results are as follows: 0 of 2 samples exceeded the water quality threshold for Nitrogen, Total. |
Data Reference: |
Field, Habitat, Sediment, Tissue, Water data for the 2020/2022 integrated report in Region 9. |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
Concentrations of nitrogen and phosphorus, by themselves or in combination with other nutrients, shall be maintained at levels below those which stimulate algae and emergent plant growth. A desired goal in order to prevent plant nuisance in streams and other flowing waters appears to be 0.1 mg/L total P. Analogous threshold values have not been set for nitrogen compounds; however, natural ratios of nitrogen to phosphorus are to be determined by surveillance and monitoring and upheld. If data are lacking, a ratio of N:P = 10:1, on a weight to weight basis shall be used (Water Quality Control Plan, San Diego Basin). |
Objective/Criterion Reference: |
Water Quality Control Plan for the San Diego Basin |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
The samples were collected at 1 monitoring site (903SLFRCx) |
Temporal Representation: |
The samples were collected between the dates of 2015-05-22 and 2017-05-03 |
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 127572, Nitrogen
|
Region 9 |
Fry Creek |
|
|
LOE ID: |
144129 |
|
Pollutant: |
Total Nitrogen as N |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Total |
|
Beneficial Use: |
Warm Freshwater Habitat |
|
Number of Samples: |
2 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP RWB9 Monitoring data for Fry Creek to determine beneficial use support and results are as follows: 0 of 2 samples exceeded the water quality threshold for Nitrogen, Total. |
Data Reference: |
Field, Habitat, Sediment, Tissue, Water data for the 2020/2022 integrated report in Region 9. |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
Concentrations of nitrogen and phosphorus, by themselves or in combination with other nutrients, shall be maintained at levels below those which stimulate algae and emergent plant growth. A desired goal in order to prevent plant nuisance in streams and other flowing waters appears to be 0.1 mg/L total P. Analogous threshold values have not been set for nitrogen compounds; however, natural ratios of nitrogen to phosphorus are to be determined by surveillance and monitoring and upheld. If data are lacking, a ratio of N:P = 10:1, on a weight to weight basis shall be used (Water Quality Control Plan, San Diego Basin). |
Objective/Criterion Reference: |
Water Quality Control Plan for the San Diego Basin |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
The samples were collected at 1 monitoring site (903SLFRCx) |
Temporal Representation: |
The samples were collected between the dates of 2015-05-22 and 2017-05-03 |
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 113568, Oxygen, Dissolved
|
Region 9 |
Fry Creek |
|
|
LOE ID: |
144726 |
|
Pollutant: |
Oxygen, Dissolved |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Total |
|
Beneficial Use: |
Warm Freshwater Habitat |
|
Number of Samples: |
2 |
Number of Exceedances: |
1 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP RWB9 Monitoring data for Fry Creek to determine beneficial use support and results are as follows: 1 of 2 samples exceeded the water quality threshold for Oxygen, Dissolved. |
Data Reference: |
Field, Habitat, Sediment, Tissue, Water data for the 2020/2022 integrated report in Region 9. |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
Dissolved oxygen levels shall not be less than 5.0 mg/l in inland surface waters with the WARM beneficial use designated (Water Quality Control Plan, San Diego Basin). |
Objective/Criterion Reference: |
Water Quality Control Plan for the San Diego Basin |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
The samples were collected at 1 monitoring site (903SLFRCx) |
Temporal Representation: |
The samples were collected between the dates of 2015-05-22 and 2017-05-03 |
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 113568, Oxygen, Dissolved
|
Region 9 |
Fry Creek |
|
|
LOE ID: |
144479 |
|
Pollutant: |
Oxygen, Dissolved |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Total |
|
Beneficial Use: |
Cold Freshwater Habitat |
|
Number of Samples: |
2 |
Number of Exceedances: |
2 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP RWB9 Monitoring data for Fry Creek to determine beneficial use support and results are as follows: 2 of 2 samples exceeded the water quality threshold for Oxygen, Dissolved. |
Data Reference: |
Field, Habitat, Sediment, Tissue, Water data for the 2020/2022 integrated report in Region 9. |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
Dissolved oxygen levels shall not be less than 6.0 mg/l in inland surface waters with the COLD beneficial use designated (Water Quality Control Plan, San Diego Basin). |
Objective/Criterion Reference: |
Water Quality Control Plan for the San Diego Basin |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
The samples were collected at 1 monitoring site (903SLFRCx) |
Temporal Representation: |
The samples were collected between the dates of 2015-05-22 and 2017-05-03 |
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 113570, Phosphorus
|
Region 9 |
Fry Creek |
|
|
LOE ID: |
145864 |
|
Pollutant: |
Phosphorus |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Total |
|
Beneficial Use: |
Cold Freshwater Habitat |
|
Number of Samples: |
2 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP RWB9 Monitoring data for Fry Creek to determine beneficial use support and results are as follows: 0 of 2 samples exceeded the water quality threshold for Phosphorus as P. |
Data Reference: |
Field, Habitat, Sediment, Tissue, Water data for the 2020/2022 integrated report in Region 9. |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
Concentrations of nitrogen and phosphorus, by themselves or in combination with other nutrients, shall be maintained at levels below those which stimulate algae and emergent plant growth. A desired goal in order to prevent plant nuisance in streams and other flowing waters appears to be 0.1 mg/L total P. Analogous threshold values have not been set for nitrogen compounds; however, natural ratios of nitrogen to phosphorus are to be determined by surveillance and monitoring and upheld. If data are lacking, a ratio of N:P = 10:1, on a weight to weight basis shall be used (Water Quality Control Plan, San Diego Basin). |
Objective/Criterion Reference: |
Water Quality Control Plan for the San Diego Basin |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
The samples were collected at 1 monitoring site (903SLFRCx) |
Temporal Representation: |
The samples were collected between the dates of 2015-05-22 and 2017-05-03 |
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 113570, Phosphorus
|
Region 9 |
Fry Creek |
|
|
LOE ID: |
145973 |
|
Pollutant: |
Phosphorus |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Total |
|
Beneficial Use: |
Warm Freshwater Habitat |
|
Number of Samples: |
2 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP RWB9 Monitoring data for Fry Creek to determine beneficial use support and results are as follows: 0 of 2 samples exceeded the water quality threshold for Phosphorus as P. |
Data Reference: |
Field, Habitat, Sediment, Tissue, Water data for the 2020/2022 integrated report in Region 9. |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
Concentrations of nitrogen and phosphorus, by themselves or in combination with other nutrients, shall be maintained at levels below those which stimulate algae and emergent plant growth. A desired goal in order to prevent plant nuisance in streams and other flowing waters appears to be 0.1 mg/L total P. Analogous threshold values have not been set for nitrogen compounds; however, natural ratios of nitrogen to phosphorus are to be determined by surveillance and monitoring and upheld. If data are lacking, a ratio of N:P = 10:1, on a weight to weight basis shall be used (Water Quality Control Plan, San Diego Basin). |
Objective/Criterion Reference: |
Water Quality Control Plan for the San Diego Basin |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
The samples were collected at 1 monitoring site (903SLFRCx) |
Temporal Representation: |
The samples were collected between the dates of 2015-05-22 and 2017-05-03 |
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 113571, Turbidity
|
Region 9 |
Fry Creek |
|
|
LOE ID: |
147665 |
|
Pollutant: |
Turbidity |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Total |
|
Beneficial Use: |
Cold Freshwater Habitat |
|
Number of Samples: |
2 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP RWB9 Monitoring data for Fry Creek to determine beneficial use support and results are as follows: 0 of 2 samples exceeded the water quality threshold for Turbidity. |
Data Reference: |
Field, Habitat, Sediment, Tissue, Water data for the 2020/2022 integrated report in Region 9. |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
The Turbidity water quality threshold in this HSA is 20 NTU, and this level is not to be exceeded more than 10% of the time during any one year period (Basin Plan, Table 3-2). |
Objective/Criterion Reference: |
Water Quality Control Plan for the San Diego Basin |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
The samples were collected at 1 monitoring site (903SLFRCx) |
Temporal Representation: |
The samples were collected between the dates of 2015-05-22 and 2017-05-03 |
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 113571, Turbidity
|
Region 9 |
Fry Creek |
|
|
LOE ID: |
147557 |
|
Pollutant: |
Turbidity |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Total |
|
Beneficial Use: |
Municipal & Domestic Supply |
|
Number of Samples: |
2 |
Number of Exceedances: |
1 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP RWB9 Monitoring data for Fry Creek to determine beneficial use support and results are as follows: 1 of 2 samples exceeded the water quality threshold for Turbidity. |
Data Reference: |
Field, Habitat, Sediment, Tissue, Water data for the 2020/2022 integrated report in Region 9. |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
The Secondary California Maximum Contaminant Level for Turbidity is 5 NTU (Title 22 of the California Code of Regulations). |
Objective/Criterion Reference: |
Maximum Contaminant Levels for organic and inorganic chemicals. CCR Title 22 |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
The samples were collected at 1 monitoring site (903SLFRCx) |
Temporal Representation: |
The samples were collected between the dates of 2015-05-22 and 2017-05-03 |
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 113571, Turbidity
|
Region 9 |
Fry Creek |
|
|
LOE ID: |
147402 |
|
Pollutant: |
Turbidity |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
Total |
|
Beneficial Use: |
Warm Freshwater Habitat |
|
Number of Samples: |
2 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP RWB9 Monitoring data for Fry Creek to determine beneficial use support and results are as follows: 0 of 2 samples exceeded the water quality threshold for Turbidity. |
Data Reference: |
Field, Habitat, Sediment, Tissue, Water data for the 2020/2022 integrated report in Region 9. |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
The Turbidity water quality threshold in this HSA is 20 NTU, and this level is not to be exceeded more than 10% of the time during any one year period (Basin Plan, Table 3-2). |
Objective/Criterion Reference: |
Water Quality Control Plan for the San Diego Basin |
|
Evaluation Guideline: |
|
Guideline Reference: |
|
Spatial Representation: |
The samples were collected at 1 monitoring site (903SLFRCx) |
Temporal Representation: |
The samples were collected between the dates of 2015-05-22 and 2017-05-03 |
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 113569, pH
|
Region 9 |
Fry Creek |
|
|
LOE ID: |
145183 |
|
Pollutant: |
pH |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
None |
|
Beneficial Use: |
Warm Freshwater Habitat |
|
Number of Samples: |
2 |
Number of Exceedances: |
0 |
|
Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP RWB9 Monitoring data for Fry Creek to determine beneficial use support and results are as follows: 0 of 2 samples exceeded the water quality threshold for pH. |
Data Reference: |
Field, Habitat, Sediment, Tissue, Water data for the 2020/2022 integrated report in Region 9. |
|
SWAMP Data: |
SWAMP |
|
Water Quality Objective/Criterion: |
In inland surface waters the pH shall not be depressed below 6.5 nor raised above 8.5. |
Objective/Criterion Reference: |
Water Quality Control Plan for the San Diego Basin |
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Evaluation Guideline: |
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Guideline Reference: |
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Spatial Representation: |
The samples were collected at 1 monitoring site (903SLFRCx) |
Temporal Representation: |
The samples were collected between the dates of 2015-05-22 and 2017-05-03 |
Environmental Conditions: |
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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 113569, pH
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Region 9 |
Fry Creek |
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LOE ID: |
145341 |
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Pollutant: |
pH |
LOE Subgroup: |
Pollutant-Water |
Matrix: |
Water |
Fraction: |
None |
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Beneficial Use: |
Cold Freshwater Habitat |
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Number of Samples: |
2 |
Number of Exceedances: |
0 |
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Data and Information Type: |
PHYSICAL/CHEMICAL MONITORING |
Data Used to Assess Water Quality: |
Water Board staff assessed SWAMP RWB9 Monitoring data for Fry Creek to determine beneficial use support and results are as follows: 0 of 2 samples exceeded the water quality threshold for pH. |
Data Reference: |
Field, Habitat, Sediment, Tissue, Water data for the 2020/2022 integrated report in Region 9. |
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SWAMP Data: |
SWAMP |
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Water Quality Objective/Criterion: |
In inland surface waters the pH shall not be depressed below 6.5 nor raised above 8.5. |
Objective/Criterion Reference: |
Water Quality Control Plan for the San Diego Basin |
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Evaluation Guideline: |
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Guideline Reference: |
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Spatial Representation: |
The samples were collected at 1 monitoring site (903SLFRCx) |
Temporal Representation: |
The samples were collected between the dates of 2015-05-22 and 2017-05-03 |
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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