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*Formerly Environmental Scientist with Central Valley Water Board and currently a Staff Environmental Scientist with Department of Fish and Game
San Joaquin River Basin: Main Stem and Drainage Basin Sites, October 2000 – September 2005
O c t o b e r 2 0 0 9
2009 Technical Report
This project was jointly funded by SWAMP and other partners, including Agricultural Subsurface Drainage Program, Total Maximum Daily Load Program, Watershed Management Initiative Program and the Grant Program
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State of California
Arnold Schwarzenegger, Governor
California Environmental Protection Agency Linda S. Adams, Secretary for Environmental Protection
REGIONAL WATER QUALITY CONTROL BOARD
CENTRAL VALLEY REGION
Karl E. Longley, Chair Katherine Hart, Vice- Chair
Nicole M. Bell, Member Cheryl K. Maki, Member
Sandra O. Meraz, Member Soapy Mulholland, Member Dan Odenweller, Member
Pamela C. Creedon, Executive Officer
11020 Sun Center Drive #200 Rancho Cordova, CA 95670
Phone: (916) 464-3291
Email: [email protected] Web site: http://www.waterboards.ca.gov/centralvalley/
D I S C L A I M E R
This publication is a technical report by staff of the California Regional Water Quality Control Board, Central Valley Region.
No policy or regulation is either expressed or intended.
*Formerly Environmental Scientist with Central Valley Water Board and currently a Staff Environmental Scientist with Department of Fish and Game
REPORT PREPARED BY:
Victoria Bowles, Environmental Scientist Chad Dibble, Environmental Scientist*
Jeremy Starr, Project Assistant Lee Xiong, Student Intern
UNDER DIRECTION OF: JEANNE CHILCOTT,
Chief, San Joaquin River Watershed Unit
REGIONAL WATER QUALITY CONTROL BOARD CENTRAL VALLEY REGION
CALIFORNIA ENVIRONMENTAL PROTECTION AGENCY
ACKNOWLEDGEMENTS: This report has been many years in the making and would not be possible without support from the 32 students and staff that have contributed tremendously over the life of the project. Spe-cifically, Lee Xiong contributed much time and effort. Major portions of the field, lab and analyti-cal work were funded through coordination and cooperation with multiple Board Programs (e.g. Surface Water Ambient Monitoring Program, Agricultural Subsurface Drainage Program, Total Maximum Daily Load Program, Watershed Management Initiative Program and the Grant Pro-gram).
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TABLE OF CONTENTS PAGE
1.0 EXECUTIVE SUMMARY ................................................................................................................. 8 2.0 GLOSSARY/KEY TERMS ............................................................................................................. 12 3.0 INTRODUCTION ............................................................................................................................. 13 4.0 BACKGROUND............................................................................................................................... 15 5.0 STUDY AREA .................................................................................................................................. 16
5.1 San Joaquin River Hydrology ................................................................................................ 16 5.2 San Joaquin River Sub-Basins .............................................................................................. 17
6.0 SAMPLING PROGRAM................................................................................................................. 18 6.1 Program Objectives .................................................................................................................. 18 6.2 Design........................................................................................................................................... 19 6.3 Sampling Procedures............................................................................................................... 24
7.0 QUALITY ASSURANCE AND QUALITY CONTROL............................................................... 24 8.0 PRECIPITATION AND FLOW: WATER YEARS 2000-2005 .................................................. 25 9.0 BENEFICIAL USES AND APPLICABLE WATER QUALITY OBJECTIVES AND GOALS................................................................................................................................................................... 28
9.1 Applicable Beneficial Uses ..................................................................................................... 29 9.2 Applicable Water Quality Objectives and Goals ............................................................... 29
10.0 RESULTS ....................................................................................................................................... 32 10.1 Result Summaries................................................................................................................... 32
12.0 DISCUSSION................................................................................................................................. 43 12.1 Temporal and Spatial Trends............................................................................................... 43
12.1.1 TEMPERATURE .................................................................................................................. 43 12.1.2 SPECIFIC CONDUCTANCE ............................................................................................... 46 12.1.3 MEASURED pH.................................................................................................................... 51 12.1.4 DISSOLVED OXYGEN ....................................................................................................... 54 12.1.5 TURBIDITY.......................................................................................................................... 56 12.1.6 TOTAL SUSPENDED SOLIDS ........................................................................................... 61 12.1.7 TOTAL ORGANIC CARBON.............................................................................................. 65 12.1.8 BACTERIA............................................................................................................................ 69 12.1.9 NUTRIENTS ......................................................................................................................... 73 12.1.10 BIOCHEMICAL OXYGEN DEMAND ............................................................................. 77 12.1.11 MINERAL ANALYSIS....................................................................................................... 79 12.1.12 TRACE ELEMENTS........................................................................................................... 79 12.1.13 TOXICITY........................................................................................................................... 81
12.2 Evaluation of Beneficial Uses.............................................................................................. 83 13.0 SUMMARY/CONCLUSION ......................................................................................................... 93 14.0 FUTURE ACTIVITIES .................................................................................................................. 95 15.0 REFERENCES .............................................................................................................................. 97
List of Figures Figure 1: San Joaquin River Basin .......................................................................................................... 15 Figure 2: San Joaquin River Sub-Basins .................................................................................................. 18 Figure 4: Merced River Near Stevinson (MST) Mean Daily Flow .......................................................... 26
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Figure 5: San Joaquin River Near Newman (NEW) Mean Daily Flow ................................................... 27 Figure 6: San Joaquin River Near Vernalis (VNS) Mean Daily Flow ..................................................... 27 Figure 7: San Joaquin River Watershed Monthly Rainfall Data Water Year 2001-2005 ........................ 28 Figure 8: San Joaquin River Northeast Basin Temperature WY01-WY05.............................................. 44 Figure 9: San Joaquin River Main Stem Temperature WY01-WY05...................................................... 44 Figure 10: Basin Temperatures WY01-WY05 ......................................................................................... 45 Figure 11: San Joaquin River Main Stem Temperature WY01-WY05.................................................... 45 Figure 12: San Joaquin River Northeast Basin Specific Conductivity WY01-WY05 ............................. 48 Figure 13: San Joaquin River Main Stem Specific Conductivity WY01-WY05 ..................................... 48 Figure 14: San Joaquin River Grassland Basin Specific Conductivity WY01-WY05............................. 49 Figure 15: Basin Specific Conductivity WY01-WY05 ............................................................................ 49 Figure 15: Basin Specific Conductivity WY01-WY05 ............................................................................ 50 Figure 16: San Joaquin River Main Stem Specific Conductivity WY01-WY05 ..................................... 50 Figure 17: San Joaquin River Northeast Basin pH WY01-WY05 ........................................................... 52 Figure 18: San Joaquin River Main Stem Specific Conductivity WY01-WY05 ..................................... 52 Figure 19: Basin pH WY01-WY05 .......................................................................................................... 53 Figure 20: San Joaquin River Main Stem pH WY01-WY05 ................................................................... 53 Figure 21: San Joaquin River Main Stem Dissolved Oxygen WY01-WY05........................................... 55 Figure 22: San Joaquin River Northeast Basin Dissolved Oxygen WY01-WY05................................... 55 Figure 23: San Joaquin River Northeast Basin Turbidity WY02-WY04 ................................................. 57 Figure 24: San Joaquin River Main Stem Turbidity WY01-WY05 ......................................................... 57 Figure 25: Basin Turbidity WY02-WY04 ................................................................................................ 58 Figure 26: San Joaquin River Main Stem Turbidity WY02-WY04 ......................................................... 58 Figure 27: Turbidity Influences on the San Joaquin River from Lander to Airport Way/ Vernalis 3-25-03
and 3-27-03. .................................................................................................................................. 59 Figure 28: Turbidity Influences on the San Joaquin River from Lander to Airport Way/ Vernalis 12-18-
02 and 12-19-02. ........................................................................................................................... 60 Figure 29: San Joaquin River Main Stem Total Suspended Solids WY01-WY05................................... 62 Figure 30: San Joaquin River Westside Basin Total Suspended Solids Irrigation Season WY01 and
WY05............................................................................................................................................ 62 Figure 31: Basin Total Suspended Solids WY01-WY05 ......................................................................... 63 Figure 32: San Joaquin River Main Stem Total Suspended Solids WY01-WY05................................... 63 Figure 33: San Joaquin River Northeast Basin Total Suspended Solids WY01 ...................................... 64 Figure 34: San Joaquin River Eastside Basin Total Organic Carbon WY01-WY05 ............................... 66 Figure 35: San Joaquin River Northeast Basin Total Organic Carbon WY01 – WY05 .......................... 67 Figure 36: San Joaquin River Main Stem Total Organic Carbon WY01 – WY05................................... 67 Figure 37: Basin Total Organic Carbon WY01-WY05 ............................................................................ 68 Figure 38: San Joaquin River Main Stem Total Organic Carbon WY01-WY05 ..................................... 68 Figure 39: San Joaquin River Northeast Basin Total Coliform WY02-WY05 ........................................ 70 Figure 40: San Joaquin River Northeast Basin E. coli WY02-WY05...................................................... 71 Figure 41: San Joaquin River Main Stem E. coli WY01 – WY05 ........................................................... 71 Figure 42: Basin E. coli WY02-WY05..................................................................................................... 72 Figure 43: San Joaquin River Main Stem E. coli WY02-WY05.............................................................. 72 Figure 44: San Joaquin River Main Stem Nitrate WY01 – WY04........................................................... 74 Figure 45: San Joaquin River Northeast Basin Nitrate WY01 ................................................................. 75 Figure 46: San Joaquin River Westside Basin Nitrate WY01 .................................................................. 75 Figure 47: Basin Nitrate WY01-WY02 .................................................................................................... 76 Figure 48: San Joaquin River Main Stem Nitrate WY02-WY04 ............................................................. 76
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Figure 49: Basin BOD-5 Day WY02-WY03............................................................................................ 78 Figure 50: San Joaquin River Main Stem BOD-5 Day WY02-WY03..................................................... 78 Figure 51: Percentage of Total Organic Carbon samples greater than the Bay-Delta Authority Target
(3.0 mg/L) ................................................................................................................................... 87 Figure 52: Percentage of E. coli samples greater than the USEPA Guideline: Designated Beach Area
(235 MPN/100ml)......................................................................................................................... 91 List of Tables Table 1: SJR SWAMP Station Information and Sampling Frequencies* ................................................22 Table 2: Water Year Classifications........................................................................................................26 Table 3: Indicator and Beneficial Uses ...................................................................................................30 Table 4: Applicable Beneficial Uses .......................................................................................................31 Table 5a: Temperature, Specific Conductance (SC) and pH Results Summary ....................................33 Table 5b: Dissolved Oxygen (DO), Turbidity and Total Suspended Solids (TSS) Results Summary.....34 Table 5c: Total Organic Carbon (TOC), Total Coliform and E. coli Results Summary ...........................35 Table 5d: Nitrate, Nitrate-N, and Total Kjeldahl Nitrogen Results Summary ..........................................36 Table 5e: Ammonia as N, Phosphorus and Ortho-Phosphate as P Results Summary ..........................37 Table 5f: Potassium, Biochemical Oxygen Demand (5-day) and Biochemical Oxygen Demand (10-day)
Results Summary........................................................................................................................38 Table 5g: Chloride, Sulfate, and Calcium Results Summary ..................................................................39 Table 5h: Magnesium, Total Dissolved Solids (TDS), and Carbonate Results Summary ......................40 Table 5i: Bicarbonate, Total Alkalinity and Sodium Results Summary ...................................................41 Table 6: Toxicity Toxic Event Summary..................................................................................................42 Table 7: Selected Upstream Site Locations and Number of Turbidity Samples Greater than Selected
Upstream site ..............................................................................................................................84 Table 8: Summary of Potential Beneficial Use Concerns: San Joaquin River and Sub-Basin Sites
(2000 to 2005).............................................................................................................................92 APPENDIX A: SJR Main Stem Results (A1-A8) APPENDIX B: Northeast Basin Results (B1-B5) APPENDIX C: Eastside Basin Results (C1-C7) APPENDIX D: Southeast Basin Results (D1-D4) APPENDIX E: Grasslands Basin Results (E1-E4) APPENDIX F: Westside Basin Results (F1-F6) APPENDIX G: South Delta Basin Results (G1-G4) APPENDIX H: Parameters, Detection Levels, Holding Times and Analytical Recoveries APPENDIX I: SJR Main Stem Site information and Photographic Documentation (I1-I8) APPENDIX J: Northeast Basin Site information and Photographic Documentation (J1-J5) APPENDIX K: Eastside Basin Site information and Photographic Documentation (K1-K7) APPENDIX L: Southeast Basin Site information and Photographic Documentation (L1-L4) APPENDIX M: Grasslands Basin Site information and Photographic Documentation (M1-M4) APPENDIX N: Westside Basin Site information and Photographic Documentation (N1-N6) APPENDIX O: South Delta Basin Site information and Photographic Documentation (O1-O4) APPENDIX P: Exceedance/ elevated levels Summary
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APPENDIX Q: Water Quality Objectives/Goals and Related Beneficial Use Tables (Q1-Q3) APPENDIX R: Graphical summary of results collected
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1.0 EXECUTIVE SUMMARY The Central Valley Regional Water Quality Control Board’s (Central Valley Water Board) San Joaquin River Surface Water Ambient Monitoring Program (SWAMP) was implemented in October 2000 as part of the statewide effort to assess and monitor California’s surface water quality. The San Joaquin River (SJR) Basin covers 17,720 square miles (CVRWQCB, 1998) with fresh water flows originating from the Sierra Nevada along the east side and ephemeral streams providing seasonal flows along the west side and within the foothill regions. The hydrology of the basin has been highly modified and regulated since the advent of the Central Valley Project in the late 1940’s, and the valley floor is dominated by irrigated agriculture (approximately 2.0 million acres (DWR, 2001)). The SWAMP within the SJR Basin was designed with a 3-tiered monitoring framework: 1) long-term monitoring in the main stem of the river; 2) long-term monitoring in selected tributaries draining major sub-basins; and 3) more intensive monitoring on a 5-year rotation within the sub-basins themselves. This report focuses on the results for the first two tiers of the SWAMP effort, the main stem of the San Joaquin River and the major inflows from sub-watersheds, between October 2000 and September 2005. Results for the third tier, the Intensive Basin Monitoring Program (IBP), can be found on the fol-lowing website:
http://www.waterboards.ca.gov/centralvalley/water_issues/water_quality_studies/surface_water_ambient_monitoring/sjr_swamp.shtml The final sampling design for the first two tiers included eight SJR main stem sites and 30 drainage ba-sin sites, which were sampled monthly or weekly depending on the site, with a total of 39 separate con-stituents sampled over the course of the sampling period. At a minimum, each site was analyzed for standard field measurements (specific conductance, pH, temperature, turbidity, and dissolved oxygen) as well as total coliform and E. coli. Monthly photo documentation was taken at each site. Sampling expanded to include total organic carbon, total suspended sediments, trace elements (arsenic, copper, chromium, lead, nickel, zinc, and mercury), biochemical oxygen demand, mineral data (chloride, sul-fate, calcium, magnesium, total dissolved solids, carbonate, bicarbonate, total alkalinity and sodium) and water column toxicity when additional funding was available. The purpose of this report is to summarize the data gathered over the five year sampling period and attempt to address the SJR SWAMP’s main questions within the SJR valley, which include evaluating spatial and temporal trends and providing a preliminary assessment of potential beneficial use con-cerns. Constituents monitored displayed distinct spatial and temporal trends within the SJR watershed and some areas were identified for further review of potential impacts to beneficial uses. Spatial Trend Findings: Within the river, the majority of constituents, i.e. specific conductance, TSS, turbidity, and most miner-als and metals demonstrated increasing concentrations from Sack Dam (essentially the headwaters of the lower SJR) to Hills Ferry (a main stem site just upstream of the first freshwater flow from the Sierra Nevada). Many of the increases corresponded with inflows from the Grassland sub-basin. A pattern of decreasing concentrations from Hills Ferry to Vernalis (the boundary of the Sacramento-San Joaquin Delta) corresponded to dilution from the high volume fresh water flows from the east-side rivers that drain the Sierras. Most constituent concentrations decreased to roughly the same concentrations at Sack Dam after the 110-mile journey to Vernalis.
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Comparing tributary sub-basin inflows, those from the western side of the SJR Basin had higher con-centrations of most constituents than those on the eastern side. The distribution may in part be due to minimal natural run off from the Coastal Range and replacement supply water from the Delta along the west side and more continuous fresh water flows and captured snowmelt as supply water for the east side. Temporal Trend Findings: Strong seasonal trends were found for temperature i.e., temperatures increase in the summer and de-crease during the winter. Dissolved oxygen (DO) had the opposite seasonal trend of temperature with a decrease in DO in the summer months and an increase in the winter months. Specific conductivity (SC), total organic carbon (TOC), turbidity, and total suspended solids (TSS) were influenced both by storm events, especially SC during the first storm runoff, and the irrigation season. Concentrations tended to spike during storm events, but remain at a lower but still elevated level during the irrigation season. Preliminary Assessment of Potential Beneficial Use Concerns: Potential impacts to key beneficial uses were evaluated by using selected indicators and comparing results against published water quality goals, targets and/or guidelines as follows:
• Drinking Water (SC, TOC, Nitrate, trace elements (arsenic, cadmium, copper, mercury, nickel, lead and zinc) and E. coli)
• Aquatic Life (pH, temperature, DO, turbidity, trace elements (cadmium, copper, nickel, arsenic, lead, zinc, and mercury), chloride and water column toxicity)
• Irrigation water supply (SC, and minerals (chloride, sodium and total dissolved solids)) • Recreation (E. coli)
In summary: Drinking Water/Municipal Supply: Total organic carbon was found to be elevated throughout the SJR Basin when compared to the 3.0 mg/L Bay Delta Authority’s guideline for water quality in the Sacra-mento-San Joaquin Delta (Delta). The entire SJR Basin drains into the southern portion of the Delta. Aquatic Life: Elevated temperatures during the spring and fall were a concern for fish passage along the SJR when compared to the Bay-Delta Authority target for the San Joaquin River at Vernalis of 20ºC from April 1–June 30 and from September 1–November 30. Higher levels of turbidity in the Westside basin were a concern but the current Basin Plan objective is based on background concentrations so it was difficult to evaluate for the existing ephemeral streams. Various levels of water column toxicity were reported sporadically on multiple occasions around the basin. A higher percentage of chronic tox-icity was reported as compared to acute toxicity. Samples for acute algae toxicity were collected less frequently but had a higher percentage (50 percent excluding Fremont Ford) of reduction and an in-crease in growth toxic events. For information on sediment toxicity around the basin see Sediment Toxicity Testing in the San Joaquin River Basin, October 2001 through September 2005 (http://www.waterboards.ca.gov/centralvalley/water_issues/water_quality_studies/surface_water_ambient_monitoring/swamp_water_quality_reports/index.shtml). Irrigation Water Supply: Specific conductance was found elevated above optimal irrigation water sup-ply concentrations throughout most of the SJR Basin when compared to the Water Quality Goal for Ag-riculture of 700 umhos/cm. In addition, individual samples were at times elevated above the Basin Plan objective for Vernalis of 700 umhos/cm April through August and 1000 umhos/cm September through March, although it should be noted that the objective is to be applied as a 30-day maximum running
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average and was not intended to determine impairment using a single grab sample. The highest SC concentrations were measured within the Grasslands and Westside Basin. High salt concentrations can be attributed to a variety of components not limited to local geology/hydrology, importation and de-portation of water from and to different basins, waste products from urban, industrial, and agricultural practices—and is being evaluated separately under the Central Valley Salinity Alternatives for Long-Term Sustainability (CV-SALTS) project. Recreation: Occasional spikes of E. coli above the USEPA guideline of 235 MPN/100 ml (full contact recreation) were detected sporadically throughout the year, but the summer months were of particular concern due to the potential for recreational use increases for most of the waterways. Future Activities By the end of this study (2005), other Central Valley Water Board surface water monitoring efforts had expanded—notably the Irrigated Lands Regulatory Program (ILRP) and monitoring conducted under various grant efforts. The Central Valley Water Board SWAMP efforts became more focused on inter-nal and external monitoring coordination rather than continuing to maintain a separate monitoring strat-egy with shrinking resources. Some of these efforts are listed below.
• Development of the Central Valley Regional Board SWAMP website that documents monitoring activities supported by SWAMP and provides links to final reports and selected water quality data (http://www.waterboards.ca.gov/centralvalley/water_issues/water_quality_studies/surface_water_ambient_monitoring/index.shtml)
• Continued water quality monitoring support for the multi-agency Grassland Bypass Project (se-lenium control program)
• Leveraging funds with a separate USEPA project to continue development of a web-based monitoring directory designed to display active monitoring within the entire Central Valley (http://www.centralvalleymonitoring.org)
• Providing resources (staff and contract dollars) to facilitate development of a Regional Monitor-ing Program for the Sacramento-San Joaquin Delta
• Supporting Department of Water Resources staff to continue long-term trend monitoring at 41-sites in the northern Sacramento River Basin in exchange for the addition of selected constitu-ents of concern identified through Central Valley Regional Board efforts (TOC, nutrients, and toxicity) and realignment of 11-sites to correspond with sites utilized by the state-wide SWAMP sediment toxicity study
• Providing resources to insure ILRP water quality information is captured in the state-wide SWAMP master data base
• Developing a region-wide, long-term trend monitoring framework based on the 30-sites within the Central Valley that are part of the state-wide SWAMP contaminant trend monitoring effort.
• Providing assistance to other monitoring efforts to facilitate SWAMP comparability (e.g. review-ing quality assurance project plans)
Efforts related specifically to the elevated E. coli concentrations found within the SJR Basin as well as in other areas of the Central Valley as part of ILRP monitoring, are as follows:
• A survey of E. coli concentrations in local swimming holes before during and after a holiday weekend (coordinated with Central Valley watershed groups during both 2007 and 2008)
• A pilot bacteria source identification project with the University of California, Davis, in selected streams demonstrating elevated E. coli concentrations
• Continued, seasonal E. coli monitoring at 30-major integrator sites throughout the Central Val-ley.
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Recommendations for future monitoring for each sub-basin and river site are summarized in Table 8 within the discussion and conclusion section of this report. Data collected as part of this study has been posted annually on our website since 2003 and was assessed in combination with other available data during the development of the Clean Water Act Sections 305(b) and 303(d) Integrated Report for the Central Valley Region (CVRWQCB, 2009 Draft).
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2.0 GLOSSARY/KEY TERMS Central Valley Water Board – Central Valley Regional Water Quality Control Board (CVRWQCB) IBP – Intensive Basin Program ILRP- Irrigated Lands Regulatory Program MCL- Maximum Contamination Level MUN - Municipal and Domestic Supply NPDES - National Pollutant Discharge Elimination System SC- Specific Conductance SJR – San Joaquin River SWAMP – Surface Water Ambient Monitoring Program State Water Board – State Water Resources Control Board TKN- Total Kjeldahl Nitrogen TOC- Total Organic Carbon TSS-Total Suspended Solids QA- Quality Assurance QC- Quality Control WY- Water Year
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3.0 INTRODUCTION The San Joaquin River Watershed Unit of the Central Valley Regional Water Quality Control Board (Central Valley Water Board) initiated a water quality monitoring program in October of 2000 as part of California Assembly Bill AB 982 (Chapter 495, Statutes of 1999). AB 982 focuses State Water Re-sources Control Board (State Water Board) efforts on developing a comprehensive ambient surface water quality monitoring program known as the Surface Water Ambient Monitoring Program (SWAMP). At the Central Valley Water Board, SWAMP is attempting to answer the following overarching question and related sub-questions.
What is/are the status and trends of ambient water quality in streams and rivers in the Sacramento River, San Joaquin River, and Tulare Lake Basins? --Are there spatial and temporal trends in water quality? --What is the location and extent of various levels of water quality? --Is there evidence of beneficial use impairment? (and over the long-term) --Is water quality getting better or worse? --Are Board programs (regulatory/non-regulatory) and management actions effective?
The SWAMP for the San Joaquin River (SJR) Basin (Figure 1) is built upon a monitoring framework developed as part of the agricultural subsurface drainage management program that focuses on sele-nium, salt and boron and has evolved since 1985 (discussed in more detail in section 4.0). The current SWAMP program contains 3 tiers. The first tier is a selection of sites along the main stem of the river, downstream of major inflows. The second tier is a series of sites representing inflows from specific sub-watersheds into the main stem of the river (drainage basin inflows component). These first two tiers consist of long term trend sites where monitoring is conducted weekly to monthly, depending on site and constituent. The final tier, the Intensive Basin Monitoring Program (IBP), is a more detailed, yearlong survey of the water quality within each of six sub-watersheds once every 5-years. Each of these sub-basins included water bodies with similar hydrologies, geologies, management issues, land use and land cover. The sixth basin, the southern Sacramento – San Joaquin Delta (South Delta), has not been included as part of the rotation due to the extensive monitoring and modeling already conducted by other agencies. A detailed discussion of the design of the 3-tier monitoring program is presented in section 6.2. This study focuses on the results for the first two tiers of the effort, the main stem San Joaquin River and inflows from sub-watersheds, between October 2000 and September 2005. Prior to initial water quality sampling, state, federal, and local agencies as well as known watershed groups were surveyed to identify current monitoring efforts and local concerns. These contacts included but were not limited to the Department of Water Resources, Department of Fish and Game, University of California, US Geological Survey, US Environmental Protection Agency, US Fish and Wildlife Service, Natural Re-sources Conservation Service, CalFed, San Luis Delta-Mendota Water Authority, Grassland Area Far-mers, local Resource Conservation Districts, and groups receiving water quality improvement bond grants.
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Concerns were varied, but most consistently included potential impacts to aquatic life and recreation, in particular concerns with temperature, sedimentation, selenium, off-site movement of pesticides, and pathogens, with additional concerns of irrigation supply (elevated salt) and drinking water (elevated to-tal organic carbon). The final sampling design incorporated the survey findings as funding permitted. At a minimum, each site was analyzed for standard field measurements (SC, pH, temperature, turbidity, and DO) as well as total coliform and E. coli. Monthly photo documentation was taken at each site. Sampling expanded to include total organic carbon, total suspended sediments, trace elements (arse-nic, copper, chromium, lead, nickel, zinc, selenium, molybdenum, and mercury), biochemical oxygen demand, mineral data (chloride, sulfate, calcium, magnesium, total dissolved solids, carbonate, bicar-bonate, total alkalinity and sodium) and water column toxicity when additional funding was available. Data gathered over the five year period provides information on the spatial and temporal trends in water quality and preliminary indications on potential beneficial use impairments. Key beneficial uses evalu-ated and the indicators utilized are listed below.
• Drinking Water (Salt/Specific Conductance, Total Organic Carbon, Trace Elements, Nu-
trients, E. coli) • Aquatic Life (Toxicity, Temperature, Dissolved Oxygen, Trace Elements, Ammonia, pH) • Recreation (E. coli) • Irrigation Supply (Salt/Specific Conductance)
Details for overall SWAMP monitoring objectives and indicators, as well as data for expanded sub-basin monitoring and the selenium control program, can be found on the Central Valley Regional Water Quality Control Board SWAMP website at: http://www.swrcb.ca.gov/centralvalley/water_issues/water_quality_studies/surface_water_ambient_monitoring/sjr_swamp.shtml Since 2003, all data collected as part of the San Joaquin River SWAMP effort that met quality assur-ance requirements, has been posted annually at the above website.
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Figure 1: San Joaquin River Basin 4.0 BACKGROUND
In 1985, an extensive water quality survey to evaluate the impacts of agricultural drainage on the lower San Joaquin River (SJR) was initiated. Although a number of issues of concern were identified, salt, boron and selenium impacts were the priority and a resulting multi-agency water quality monitoring pro-gram was created focusing its limited resources on evaluating these constituents. The area has since been the focus of the Region’s subsurface agricultural drainage program and considerable staff effort and resources have been directed to the effort of developing a comprehensive monitoring program, en-suring stakeholder involvement, and adopting Basin Plan Amendments and Waste Discharge Require-ments in order to develop a workable and comprehensive selenium control program. The compliance monitoring portion of this effort is the responsibility of the Data Collection and Report-ing Team (DCRT) whose members include representatives from the US EPA, US Geological Survey, US Bureau of Reclamation, US Fish and Wildlife Service, CA Department of Fish and Game, Central Valley Water Board, and Grassland Area Farmers. The DCRT monitoring program evaluates selenium concentrations, loading, and potential impacts in water, sediment, and biota. Water quality analyses for selenium salt and boron are conducted at nine sites within the Grassland Watershed and seven sites along the main stem of the SJR. Grab samples are collected weekly, with daily composites also col-lected at two key sites: the consolidated agricultural subsurface drainage discharge point on the San
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Luis Drain; and at Crows Landing on the SJR. (See Grassland Bypass Program on the Central Valley Regional Board SWAMP website for more detailed information.) The SJR SWAMP program was built upon this established framework. Basin priorities include maintaining the Grassland Bypass Program and expanding it to facilitate real-time monitoring activities. Other issues of concern include: aquatic toxicity from waterborne pesticides; aquatic life impacts from pesticides in bed sediment; habitat impacts from sedimentation; elevated nu-trient and BOD levels; pathogens; elevated temperatures; impacts from abandoned mines, timber har-vesting and grazing; and establishing baseline condition in rural Coastal Range streams in areas slated for future urban development. 5.0 STUDY AREA 5.1 San Joaquin River Hydrology The San Joaquin River (SJR) is the principal drainage artery of the San Joaquin Valley. The basin covers 17,720 square miles (CVRWQCB, 1998) and yields an average annual surface runoff of about 1.6 million acre-feet. The SJR basin drains the portion of the Central Valley south of the Sacramento-San Joaquin Delta and north of the Tulare Lake Basin. The lower Basin (below Millerton Reservoir) has had a highly managed hydrology since implementation of the Central Valley Project (CVP) in 1951. From the Sierra Nevada, the river channel drains west-ward to the Mendota Pool near the town of Mendota. As the river channel continues past the Mendota Pool it turns northward to narrow by the constrictions of the Merced River and Orestimba Creek alluvial fans. From there, the river channel makes its way north to the Sacramento-San Joaquin Delta and out to the Suisun Bay. Most of the flow released from Friant Dam is diverted into the Friant-Kern Canal, leaving the river chan-nel upstream of the Mendota Pool dry except during periods of wet weather flow and major snow melt, which was the case in early 2005. The majority of the water in the Mendota Pool has been transported from the Delta via the Delta Mendota Canal (DMC) for irrigation use and to replace water lost thru di-version of the upper SJR flows. The majority of that poorer quality (higher salinity) water is then dis-charged to irrigation supply channels along the west side of the river, while some flows are released to the main river channel and continue to Sack Dam. Remaining flows not diverted for agricultural use out of the main channel are then diverted at Sack Dam leaving flows in the lower San Joaquin River (below Sack Dam) mainly dependent on releases from upstream reservoirs, agricultural return flows, and groundwater seepage, although wetland releases and storm water run-off can have considerable im-pacts on the flows as well. During the irrigation season, the flows in the river between Sack Dam and Salt Slough consist largely of groundwater accretions. Salt Slough and Mud Slough (north) are the principal drainage arteries for the Grassland Sub-Basin and add significantly to the flows and waste loads in the SJR upstream of its confluence with the Merced River. Eastside discharges dominate flows in the SJR, as higher quality (lower salinity) water is released from reservoirs on the Merced, Tuolumne, and Stanislaus Rivers. Flows from the west side of the river basin are dominated by agricultural return flows since west side streams are ephemeral and their downstream channels are used to transport agricultural return flows to the main river channel (Steenson, et al., 1998)
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The principal streams in the basin are the San Joaquin River and its larger tributaries: the Cosumnes, Mokelumne, Calaveras, Stanislaus, Tuolumne, Merced, Chowchilla, and Fresno Rivers which all drain the east side of the basin. Major land use along the San Joaquin Valley floor is agricultural, occupying approximately 2.0 million acres, representing approximately 23% of the irrigated acreage in California (DWR, 2001). Urban growth along the I-5 corridor between Fresno and Stockton is rapidly converting historical agricultural lands to urban areas. As more and more people choose to commute from the Central Valley to the Bay Area, the rapid conversion of land is leading to increasing potential for storm water and urban impacts to local waterways. Timber activities, grazing, abandoned mines, rural com-munities, and recreation can impact upper watershed areas (Graham, 2009). 5.2 San Joaquin River Sub-Basins To help characterize the SJR watershed and develop a monitoring program targeting specific problems affecting water quality, the watershed was broken into six smaller sub-basins bound by the Sierra Ne-vada Mountains or the Coastal Range and comprised of similar land use and drainage patterns (Figure 2). All of the agricultural-dominated and constructed water bodies within each of the sub-basins have been identified (Chilcott, 1992), as well as the potential water quality concerns and major representa-tive discharges to the lower SJR. These sub-basins are similar to and based on, Total Maximum Daily Load (TMDL) efforts for salinity and boron in the lower SJR.
1. The Northeast Basin consists of the Cosumnes, Mokelumne, and Calaveras River Water-sheds, providing a combined drainage of 4,360 square miles.
2. The Eastside Basin contains the three largest SJR tributaries, in terms of flow: the Merced,
Stanislaus, and Tuolumne River Watersheds, along with the Farmington Drainage Basin and the lower Valley Floor Drainage Area, which drain directly to the SJR. The Eastside Basin is approximately 6,091 square miles.
3. The Southeast Basin is approximately 4,338 square miles and reaches from the headwaters of
the SJR north to the watershed divide between Bear Creek and the Merced River in Merced County.
4. The Westside Basin encompasses the watersheds of the creeks draining the eastern slope of
the Coast Range from the Orestimba watershed in the south to the Lone Tree Creek in the north. The Westside Basin is approximately 670 square miles.
5. The Grasslands Basin is a valley floor sub-basin of the SJR Basin, south of the Orestimba wa-
tershed, covering approximately 1,360 square miles. This basin lies on the west side of the SJR in portions of Merced, San Benito, and Madera Counties.
6. The South Delta Basin covers approximately 677 square miles and includes creeks on the
northwest side of the SJR, as well as the southern portion of the Sacramento-San Joaquin Delta waterways down toward the confluence of the SJR and the Sacramento River. Waters inside the Delta boundaries are tidally influenced and typically higher in salinity than other surface wa-ter throughout the SJR Basin.
18
Figure 2: San Joaquin River Sub-Basins 6.0 SAMPLING PROGRAM 6.1 Program Objectives In keeping with the overall Central Valley Regional Board SWAMP goals of being able to answer water quality questions related to spatial and temporal trends as well as whether or not there is evidence of beneficial use impairment, the following objectives were adopted for this effort:
1. Spatial and Temporal Trends a. Spatial includes the evaluation of the SJR moving progressively downstream as well as
comparisons between sub-basins b. Temporal includes seasonal variations and annual variations (by water year type)
2. Evaluation of Beneficial Use Protection a. Using selected indicators to determine whether there is evidence of impairment
3. Utilizing information gathered from the long-term trend sites within each sub-basin to help direct future monitoring program design within that sub-basin.
19
6.2 Design The SJR SWAMP program was designed as a trend-monitoring program that used a tiered approach. By using a tiered approach the SJR SWAMP program was able to adjust sampling constituents and monitoring frequencies to coincide with the year-to-year fluctuations in funding, as well as adjust for time delays associated with contracting to analytical laboratories. The use of available funds was then prioritized based on these tiers and the objectives of the program. This design resulted in less interrup-tion to monitoring activities that were considered higher priority for the program. Creating a tiered moni-toring design and selecting long-term sites and constituents also allows for the monitoring data to be evaluated over different water year types and facilitates assessment of implementation efforts going on throughout the valley. Monitoring sites for this program were selected from information gathered through existing monitoring efforts, historic data sets, the Inland Surface Waters Plan (Chilcott, J.,1992), the report Water Diversion and Discharge Points Along the San Joaquin River (James, E. W., et al.,1989), and reconnaissance done by Regional Board staff prior to initiation of any monitoring ef-forts. The first tier of the program is the Main Stem Program. In that program, eight sites were selected along the lower section of the SJR and monitored on a daily, weekly, monthly, or quarterly basis, depending on the constituent. Those sites were selected as long-term sites and are located downstream of major influences to the river. Those sites were the most important to the program since they represent the “bottom” of the system and could show potential changes to the river over time. Many of the sites se-lected were already being monitored as part of the Grassland Bypass Program (multi-agency selenium control effort), so coordination with those monitoring and data management efforts was incorporated. The second tier of the program is the Sub-Basin Program. The Sub-Basin Program moved the monitor-ing away from the main stem of the SJR and up into lower sections of the valley floor. In this program, 29 sites were selected as long-term trend sites representing the main inflows to the SJR from each of six sub-basins. The third tier, the Intensive Basin Program, was not directly part of the trend monitoring, but rather fo-cused on a 5-year rotational approach. This program contained approximately 20 sites per sub-basin, in addition to sites already part of the Sub-Basin Program, and focused solely on one sub-basin at a time. Sites selected within a sub-basin were monitored for one year, with the intent to rotate through the sub-basins once every 5 years.
To evaluate potential impact to beneficial uses, indicators were chosen for five broad beneficial uses: drinking water; recreation (swimming); aquatic life; irrigation; and waterfowl. The choice of indicators came from an evaluation of USEPA EPIC indicators (USEPA, 2003), water quality objectives and goals, and the fact that many of the indicators monitored as part of the SJR SWAMP efforts support high prior-ity region-wide program assessments as listed in the 2005 Triennial Review of the Water Quality Con-trol Plan for the Sacramento River and San Joaquin River Basins. Regional programs utilizing SJR SWAMP monitoring data include: Drinking Water Policy, Water Quality Objectives for Bacteria Indica-tors, Salinity and Boron TMDL, Central Valley Salinity Policy Development, Erosion/Sediment guide-lines, and SJR Dissolved Oxygen TMDL. In general, the first five years of the program were set-up to continually monitor sites on the SJR as part of the main stem program on a weekly basis, monthly for certain constituents, with the Sub-Basin sites being monitored on a monthly basis. The remaining funding was utilized in the Intensive Basin Pro-
20
gram. At the end of Water Year 2002 (i.e., 30 September 2002), a preliminary evaluation of the data collected as part of the first two years of the program was done and showed that the monthly monitor-ing frequency for nutrients, trace metals, minerals and TSS was not sufficient to develop useful trend information due to insufficient funding. Those analyses were then dropped from the program for a ma-jority of the sites (mainly the Sub-Basin sites). Table 1 lists the monitoring sites and sampling frequen-cies associated with the constituents monitored for each site. As funding permitted, samples were collected for: total suspended solids (TSS); total organic carbon (TOC); total coliform; E. coli; nutrients, including nitrate, nitrate-N, total kjeldahl nitrogen (TKN), ammo-nia, phosphorus, ortho-phosphate, and potassium; biochemical oxygen demand (5 and 10 day); chlo-ride; sulfate; calcium; magnesium; total dissolved solids (TDS); carbonate; bicarbonate; total alkalinity; sodium; water column toxicity [Pimephales promelas (P. promelas), Ceriodaphnia dubia (C. dubia), Se-lenastrum capriconutum (algae)]; hardness; arsenic; cadmium; chromium; copper; lead; nickel; zinc; and mercury. Figure 3 displays the distribution of the sites within the SJR Basin. For more information on the moni-toring sites location including specific sampling location, summary of land-use, available water quality information, and monthly photograph documentation over the course of WY 2004-2005 for each site see Appendix I-O or refer to the central valley water quality web site: http://www.swrcb.ca.gov/centralvalley/water_issues/water_quality_studies/surface_water_ambient_monitoring/sjr_swamp.shtml The results presented in this report focus on the first and second tier monitoring of the SJR SWAMP effort. Reports on the first three Intensive Basin Programs (Northeast Basin, Eastside Basin, and Westside Basin), the third tier of the program, as well as all water quality data can be found at: http://www.waterboards.ca.gov/centralvalley/water_issues/water_quality_studies/
21
Figure 3: Monitoring Site Locations
22
Cor
resp
ondi
ng
Map
Num
ber
Station Name Station CodeWater Body Type
Target Lat Target Long
SC
(spe
cific
co
nduc
tanc
e)
pH
DO
(dis
solv
ed
oxyg
en)
Tem
p
E.c
oli
Tot
al C
olifo
rm
TO
C (t
otal
or
gani
c ca
rbon
)
TSS
(tot
al
susp
ende
d so
lids)
Nut
rient
s +
Trac
e M
etal
s (T
otal
&
Dis
solv
ed)
Min
eral
s **
Chr
onic
To
xici
ty
Acu
te T
oxic
ity
BO
D
(bio
chem
ical
ox
ygen
de
man
d)
Main Stem 1 SJR @ Sack Dam 541MAD007 R 36.98361 -120.50027 M M M M M M M M M M M M2 SJR @ Lander Avenue 541MER522 R 37.29527 -120.85027 W W W W M+ M+ W W M M M M M M3 SJR @ Fremont Ford 541MER538 R 37.30944 -120.92916 W W W W M+ M+ W W M M M M4 SJR @ Hills Ferry 541STC512 R 37.3425 -120.97722 M M M M M M M M M M M M M M5 SJR @ Crows Landing 535STC504 R 37.43194 -121.01166 W W W W M+ M+ W W M M M M M M6 SJR @ Patterson 541STC507 R 37.49777 -121.08166 W W W W M+ M+ W W M M M M M M7 SJR @ Maze 541STC510 R 37.64194 -121.22777 W W W W M+ M+ W W M M M M8 SJR @ Airport Way 541SJC501 R 37.67555 -121.26416 W W W W M+ M+ W W M M M M M M
Drainage Basin
9 Cosumnes River at Twin Cities Road 531SAC001 ER 38.29083 -121.37583 M M M M M M M M M M M M M10 Mokelumne River at New Hope Road 544SAC002 ER 38.23611 -121.41889 M M M M M M M M M M M M M11 Pixley Slough at Davis Road 531SJC507 Eph/SL 38.05611 -121.33305 M M M M M M M M M M M M M12 Bear Creek at Thornton Road (J8) 544SJC508 Eph/SL 38.04305 -121.34861 M M M M M M M M M M M M13 Bear Creek at Lower Sacramento Road 531SJC515 Eph/SL 38.04277 -121.32139 M M M M M M M M M M M M M
14 Lone Tree Creek at Austin Road 531SJC503 Eph 37.85555 -121.185 M M M M M M M M M M M M M15 French Camp Slough at Airport Way 531SJC504 SL 37.88166 -121.24944 M M M M M M M M M M M M M16 Turner Slough at Fourth Ave. 535MER576 Eph/SL 37.32055 -120.88916 M M M M M M M M M M M M M17 Merced River @ River Road 535MER546 ER 37.34972 -120.95777 M M M M M M M M M M M M M18 TID 5 Harding Drain @ Carpenter Road 535STC501 Eph 37.46444 -121.03028 M M M M M M M M M M M M M19 Tuolumne River at Shiloh Fishing Access 535STC513 ER 37.60305 -121.13166 M M M M M M M M M M M M M20 Stanislaus River at Caswell Park 535STC514 ER 37.7025 -121.17722 M M M M M M M M M M M M M
21 Lone Willow Slough at Road No. 9 545MAD006 Eph 36.86694 -120.38194 M M M M M M M M M M M M22 Santa Rita Slough at HWY 152 541MER015 Eph 37.0475 -120.59361 M M M M M M M M M M M M23 Deep Slough at Green House Road 535MER577 Eph 37.22972 -120.72833 M M M M M M M M M M M M24 Bear Creek near Bert Crane Road 535MER007 Eph 37.25555 -120.65194 M M M M M M M M M M M M M
Northeast Basin
Eastside Basin
Southeast Basin
Table 1: SJR SWAMP Station Information and Sampling Frequencies*
23
Cor
resp
ondi
ng
Map
Num
ber
Station Name Station CodeWater Body Type
Target Lat Target Long
SC
(spe
cific
co
nduc
tanc
e)
pH
DO
(dis
solv
ed
oxyg
en)
Tem
p
E.c
oli
Tot
al C
olifo
rm
TO
C (t
otal
or
gani
c ca
rbon
)
TSS
(tot
al
susp
ende
d so
lids)
Nut
rient
s +
Trac
e M
etal
s (T
otal
&
Dis
solv
ed)
Min
eral
s **
Chr
onic
To
xici
ty
Acu
te T
oxic
ity
BO
D
(bio
chem
ical
ox
ygen
de
man
d)
25 Salt Slough @ Lander Avenue 541MER531 Eph 37.24861 -120.85111 M M M M M M M M M M M M M M26 Mud Slough Upstream of SLD Terminus 541MER536 Eph 37.25416 -120.90694 M M M M M M M M M M M M27 San Luis Drain @ Terminus 541MER535 SD 37.25944 -120.90388 M M M M M M M M M M M M28 Mud Slough @ San Luis Drain 541MER542 Eph 37.26388 -120.90611 M M M M M M M M M M M M
29 Orestimba Creek @ River Road 541STC019 Eph 37.41388 -121.01416 M M M M M M M M M M M M M30 Salado Creek at HWY 33 541STC515 Eph 37.48138 -121.13555 M M M M M M M M M M M M M31 Del Puerto Creek at Vineyard Avenue 541STC516 Eph 37.52138 -121.14861 M M M M M M M M M M M M M32 Ingram Creek at River Road 541STC040 Eph 37.60027 -121.22416 M M M M M M M M M M M M M33 Hospital Creek at River Road 541STC042 Eph 37.61055 -121.22861 M M M M M M M M M M M M M34 Grayson Road Drain at Grayson 541STC030 Eph 37.56194 -121.17416 M M M M M M M M M M M M M
35 New Jerusalem Tile Drain 544SJC001 SD 37.70888 -121.29861 M M M M M M M M M M M M M36 Tom Paine Slough at Paradise Road 544SJC505 SL 37.77416 -121.38222 M M M M M M M M M M M M37 Old River at Tracy Blvd. 544SJC506 SL 37.80472 -121.44944 M M M M M M M M M M M M38 Mt. House Creek @ Mt. House Parkway 544SJC509 Eph 37.78555 -121.53472 M M M M M M M M M M M M M
CDEC Gauging Station Sites39 Merced River Near Stevinson (Flow) MST NA 37.37100 -120.93100 NA NA NA NA NA NA NA NA NA NA NA NA NA NA40 SJR near Newman (Flow) NEW NA 37.35000 -120.97700 NA NA NA NA NA NA NA NA NA NA NA NA NA NA41 SJR Near Vernalis (Flow) VNS NA 37.66700 -121.26700 NA NA NA NA NA NA NA NA NA NA NA NA NA NA42 Stockton Fire Station 4 (Precipitation) STK NA 38.00100 -121.31700 NA NA NA NA NA NA NA NA NA NA NA NA NA NA43 Tracy Carbona (Precipitation) TCR NA 37.70000 -121.43300 NA NA NA NA NA NA NA NA NA NA NA NA NA NA44 Merced (Precipitation) MFS NA 37.28300 -120.51700 NA NA NA NA NA NA NA NA NA NA NA NA NA NA45 Los Banos (Precipitation) LSB NA 37.05000 -120.86700 NA NA NA NA NA NA NA NA NA NA NA NA NA NA
* Sample frequencies shown indicate frequency of samples taken as funding allowed+ Nutrient analysis includes nitrate, nitrate-N, total kjeldahl nitrogen (TKN), ammonia, phosphorus, ortho-phosphate, and potassium** Mineral analysis includes chloride, sulfate, calcium, magnesium, total dissolved solids, carbonate, bicarbonate, total alkalinity and sodiumW = weeklyM = MonthlyM+ = 2X/MonthR = Main Stem RiverER = Eastside River Draining SierraEph = Ephemeral Stream usually dominated by AG return flows during irrigation seasonSL = Backwater or Slough that can experience tidal influencesSD = Subsurface Drainage (shallow groundwater)NA = Not Applicable
Westside Basin
Delta Basin
Grasslands Basin
Table 1: SJR SWAMP Station Information and Sample Frequencies* continued...
24
6.3 Sampling Procedures All samples were measured and collected in compliance with the Agricultural Subsurface Drainage Program Procedures Manual (Chilcott, et al., 1996) and the Quality Assurance Program Plan for the State of California’s Surface Water Ambient Monitoring Program “SWAMP” (SWRCB, 2002). Field measurements for temperature, specific conductance, pH, dissolved oxygen and turbidity were taken using one of three meters; Myron 6P Ultra Meter II (temp, SC, and pH only, Oct 2000- July 2001) Yellow Springs Instrument (YSI) 600 XLM Sonde (no turbidity), or a YSI 6600 Sonde (turbidity). All YSI readings were read from YSI 650 data logger. Clean sample containers were rinsed three times with ambient water prior to grab sample collection, except for sample containers that were pre-acidified (ammonia and TOC) or contained other neutraliz-ing agents (sodium thiosulfate for total coliform and E. coli). Water for pre-acidified samples was col-lected in a stainless steel cup or a sample bottle that was being collected for a separate constituent at the same site and poured into the sample container. All samples were kept at 4 degrees Celsius by storing them on ice after collection and during transport and in a refrigerator while in-house. Appendix H lists the laboratories, detection levels, holding times and acceptable recoveries for the pa-rameters monitored. 7.0 QUALITY ASSURANCE AND QUALITY CONTROL All quality assurance (QA) and quality control (QC) log-books for the constituents analyzed by outside laboratories were maintained by the Regional Board contract manager or their designee. QA/QC re-cords for bacteria analysis and equipment maintenance are recorded in the respective QA/QC log-books, found in the Central Valley Water Board laboratory where samples were analyzed. At a minimum, field sampling equipment was calibrated as per manufacturer’s instructions at the start and end of each sampling event and/or after 10-15 sites. If it was found that calibrations were off, the instruments were recalibrated and if needed, measurements re-taken. Field and handling contamination was evaluated by submitting blind travel blanks on a monthly basis, and on each run for bacteria monitoring. Travel blank samples traveled through the sampling run, and were processed with the sample set. For most constituents, the travel blank consisted of a sample of de-ionized (DI) water that was produced at the Central Valley Water Board laboratory. For bacteria monitoring, the travel blanks were prepared by the Department of Plant Sciences, University of Califor-nia Davis (UC Davis). After thorough discussion with UC Davis, the travel blanks were initially prepara-tions of boiled deionized water and NaCl, which was then switched to Type II water in July 2002, and ultimately, phosphate buffered saline was added to the Type II water travel blanks at the end of WY 2005. For toxicity monitoring, Sierra Foothill Labs, Inc provided de-mineralized water (DMW) to be used for travel blanks. All data sets used for this report had travel blank results that fell below the ana-lytical detection limits for the elements of concern. Consistency in sample collection and analysis was evaluated by collecting replicate samples for all samples needing laboratory analysis. The Central Valley Water Board San Joaquin River Watershed Unit uses a SWAMP compliant standard quality assurance procedure that includes 10% replicate sam-ples.
25
Precision and accuracy were evaluated using blind split and spiked samples. Blind split samples were collected at a 10% frequency for each sampling event by collecting the sample in a container double the normal sample volume and splitting that sample into two equal amounts for submittal to the analyz-ing laboratory. On a monthly basis, and when appropriate, half of the blind split samples were spiked with known concentrations of constituents to be analyzed. Comparing the spiked split to the back-ground split provided information on analytical accuracy. Comparing data from non-spiked splits pro-vided information on analytical precision. Potential contamination from the reagent grade nitric acid used to control pH was evaluated by submit-ting a deionized water matrix preserved with 1 mL of acid per 500 mL of sample, to the contract labora-tories at monthly intervals to be analyzed for the trace elements of concern. All reported recoveries for these acid check samples were below the analytical detection limit. Only data from sample sets whose blind QA/QC met specifications outlined in Appendix H have been included in this report. These specifications are consistent with the QAPP for this program. 8.0 PRECIPITATION AND FLOW: WATER YEARS 2000-2005 The San Joaquin River is the principal drainage artery of the San Joaquin Valley, draining the area south of the Sacramento-San Joaquin Delta and north of the Tulare Lake Basin, approximately 13,500 square miles (Graham, 2009; Steensen, et al., 1998). Precipitation varies throughout the SJR Water-shed and occurs as both rainfall and snow. Mean annual precipitation on the valley floor ranges from less than 5 inches in the south to 15 inches in the north. Average annual precipitation in the Sierra Ne-vada, mostly in the form of snow, ranges from about 20 inches in the lower foothills to more than 80 inches at some higher altitude sites. Precipitation in the Coast Ranges varies from less than 10 inches to more than 20 inches. As in the valley, precipitation in the Sierra Nevada and Coast Ranges in-creases from south to north (Dubrovsky, et al., 1998).
The San Joaquin River Index, as described in the Water Quality Control Plan for the San Francisco Bay/Sacramento-San Joaquin Delta Estuary is used to classify the water year type in the river basin based on runoff. The 60-20-20 Index includes five classifications: wet, above normal, be-low normal, dry, and critical, based on millions of acre-feet of calculated unimpaired flow. (SWRCB, 1995)
A Water Year begins 1 October and ends 30 September of the following year. Because of the timing of this study, October 2000 through September 2005, five full water years are represented. Table 2 lists the Water Year Classifications based on rainfall and snow totals in the SJR Watershed during the pro-ject.
26
Table 2: Water Year Classifications
(Data source DWR, 2007) Figures 4, 5, and 6 display the mean daily flow for the Merced River and the San Joaquin River near Newman and Vernalis during this project. These sites represent the main flows coming in and out of the San Joaquin River watershed: the Merced River represents flow from the Sierras, Newman represents the upstream flow of the SJR and Vernalis represents the downstream flow from the SJR entering the Sacramento-San Joaquin Delta. Figure 4: Merced River Near Stevinson (MST) Mean Daily Flow
(Data Source, DWR-California Data Exchange Center (CDEC))
Water Year 2001 – Dry Water Year 2002 – Dry Water Year 2003 – Below normal Water Year 2004 – Dry Water Year 2005 – Wet
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27
Figure 5: San Joaquin River Near Newman (NEW) Mean Daily Flow
(DATA SOURCE, DWR-CALIFORNIA DATA EXCHANGE CENTER (CDEC))
Figure 6: San Joaquin River Near Vernalis (VNS) Mean Daily Flow
(DATA SOURCE, DWR-CALIFORNIA DATA EXCHANGE CENTER (CDEC))
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28
Figure 7 displays the San Joaquin River Watershed Monthly Rainfall Data during the project. These sites represent precipitation throughout the basin and were chosen for their extensive reliable record. Figure 7: San Joaquin River Watershed Monthly Rainfall Data Water Year 2001-2005
(Data Source, DWR-California Data Exchange Center (CDEC)) 9.0 BENEFICIAL USES AND APPLICABLE WATER QUALITY OBJECTIVES AND GOALS One component of the Central Valley Water Boards SWAMP efforts is to evaluate ambient water quality to determine whether there is any indication that beneficial uses are being impacted. Information gath-ered during this study allowed analysis of a broad spectrum of water bodies at key integrator sites in order to determine existing quality at the site itself and allow some inference of the water quality within identified sub-basins. Potential beneficial uses applicable to each site monitored were identified using the designated listing from the Sacramento/San Joaquin Water Quality Control Plan (Basin Plan) (CVRWQCB, 1998). To evaluate potential impact, indicators were chosen for five broad beneficial uses: drinking water (salt, TOC, trace elements, nutrients, bacteria); aquatic life (pH, temperature, dis-solved oxygen, turbidity, and water column toxicity); irrigation water supply (salt); recreation (bacteria); and waterfowl (selenium). Selenium was not assessed in this report due to the in-depth analysis of the same data through the Grassland Bypass Project. Not all of the indicators could be monitored at each site, due to funding limitations, but at least one indicator for each beneficial use evaluated was included at each site for the study.
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Jul-0
1
Oct
-01
Jan-
02
Apr
-02
Jul-0
2
Oct
-02
Jan-
03
Apr
-03
Jul-0
3
Oct
-03
Jan-
04
Apr
-04
Jul-0
4
Oct
-04
Jan-
05
Apr
-05
Jul-0
5
M onth
Inch
es
Stockton Fire Station 4 (STK) Tracy Carbona (TCR) Merced (MFS) Los Banos (LSB)
29
The following two sections highlight: 1) the beneficial uses that apply to each of the water bodies sam-pled; and 2) the objectives and goals that were utilized when evaluating results to determine whether there was any indication that water quality was not supporting a specific beneficial use.
9.1 Applicable Beneficial Uses In the SJR Basin, all natural water bodies have potential municipal and industrial supply designated through the statewide Sources of Drinking Water Policy (State Water Resources Control Board Resolu-tion No. 88-63). Other specific beneficial uses have been designated to individual water bodies as well as the San Joaquin River/Sacramento-San Joaquin Delta—to which the entire SJR Basin drains. The beneficial uses of any specifically identified water body generally apply to its tributary streams. The applicable beneficial uses for each sampling site have been summarized in Table 4, under the general headings of Drinking Water, Recreation Use, Irrigation Supply and Aquatic Life. Table 4 indi-cates whether the use has been specifically designated or is being applied as a tributary. Appendix Q3 provides more detail on the subcategories of use that have been specifically designated in the Sacra-mento-San Joaquin Basin Plan. 9.2 Applicable Water Quality Objectives and Goals Water quality information collected during this study was evaluated using water quality objectives adopted in the Sacramento River and San Joaquin River Basin Plan (CVRWQCB, 1998), a compilation of water quality goals identified by state and federal agencies (Marshack, 2003) and targets developed by the Bay-Delta Authority (CFBDP, 2000). The Basin Plan objectives are enforceable criteria that are linked to protecting designated beneficial uses such as domestic, municipal, agricultural and industrial supply, recreation, and preservation and enhancement of fish, wildlife and other aquatic resources. These objectives are both numeric and narrative and may be specific to certain reaches of various wa-ter bodies or apply to entire basins. The water quality goals are scientifically defensible numeric criteria developed by diverse agencies to protect specific uses; primarily aquatic life, drinking water, and irrigation supply. In many cases, the goals are national guidelines. These goals may be used to determine compliance with some of the nar-rative Basin Plan objectives (e.g. toxicity). Both the objectives and the goals apply to the indicators used to evaluate beneficial use protection. A summary of the general groups of indicators that can be utilized to evaluate a beneficial use and the most limiting use (e.g. if the objective/goal is met for that use than it would be met for the remaining uses) is listed in Table 3. Appendix Q1 lists the applicable Basin Plan objectives for this study. For turbidity, pH, temperature, and total suspended sediment, the listed objectives refer to changes impacting “normal” and “natural” conditions. For this study, natural conditions have been assumed to be conditions at the furthest up-stream sampling location or upstream of a specific discharge. Appendix Q1 also includes targets iden-tified by the Bay-Delta Authority (a joint State and Federal agency) to protect fish passage (temperatures not to exceed 20-degrees Celsius) and drinking water (total organic carbon to remain below 3.0-mg/L). Appendix Q2 shows the applicable goals sorted by generalized beneficial uses.
30
SC X X XpH X X X
Temp. XDO X
Turbidity X X XMinerals X X
X X X fNutrient Scan X X X
TSS X X X XTDS X XTOC X X XBOD X
Bacteria X X X
P. promelas 96 hr X X X XC. dubia 48 hr X X X X
S. capricornutum Acute X X X XP. promelas Chronic X X X X
C. dubia Chronic X X X X
Toxicity
Trace Elements (Total & Diss.)
Drinking Water
Aquatic Life
Water Column AnalysesINDICATOR(S)
SJR BENEFICIAL USE(S)Irrig. Water Supply Rec. Use
f=Major recreational use concern is in fish consumptionMinerals= B, Ca, Cl, CO3, HCO3, K, Mg, Na, SO4, Alkalinity, TDS, Total Hardness, pH, ConductivityTrace Elements (Total & Diss.)= As, Cd, Cr, Cu, Hg, Ni, Pb, Zn, Nutrient Scan= K, P, PO4, NH3-N, NO3, TKN
= Most limiting beneficial use(s). For reference of actual numerical valuesof water quality objectives see "A Compilation of Water Quality Goals " (Marshack, 2000)
Table 3: Indicators and Beneficial Uses
31
Table 4: Applicable Beneficial Uses
Drinking Water Irrigation
REC-2
Con
tact
Can
oein
g an
d R
aftin
g
Oth
er N
onco
ntac
t
War
m
Col
d
War
m
Col
d
War
m
Col
d
SJR @Sack Dam 541MAD007 P E E E E E E E E P D
SJR @ Lander 541MER522 P E E E E E E E E P D
SJR @ Fremont Ford 541MER538 P E E E E E E E E P D
SJR @ Hills Ferry 541STC512 P E E E E E E E E P D
SJR @ Crows 535STC504 P E E E E E E E E D
SJR @ Patterson 541STC507 P E E E E E E E E D
SJR @ Maze 541STC510 P E E E E E E E E D
SJR @ Airport Way/Vernalis 541SJC501 P E E E E E E E E D
North East Basin
Cosumnes River @ Twin Cities Rd. 531SAC001 E E E E E E E E E E E D
Mokelumne River @ New Hope Rd. 544SAC002 E E E E E E E E E E D
Pixley Slough @Davis Rd. * 544SJC507 E E E E E E E E E T
Bear Creek @Thornton Rd (J8) * 544SJC508 E E E E E E E E E T
Bear Creek @Lower Sacramento Rd. * 531SJC515 E E E E E E E E E T
Eastside Basin
Lone Tree Creek * 531SJC503 E E E E E E E E E T
French Camp Slough @ Airport * 531SJC504 E E E E E E E E E T
Merced River Hatfield Park (River Road) 541MER546 E E E E E E E E E E D
Turner Slough @ 4th Avenue * 535MER576 P E E E E E E E E P T
TID 5 (Harding Drain)* 535STC501 P E E E E E E E E T
Tuolumne River @ Shiloh 535STC513 P E E E E E E E E E D
Stanislaus River @Caswell 535STC514 P E E E E E E E E E D
Southeast Basin
Lone Willow Slough * 545MAD006 P E E E E E E E E P T
Bear Creek @ Bert Crane Rd. * 535MER007 P E E E E E E E E P T
Deep Slough Green House Rd. * 535MER577 P E E E E E E E E P T
Grassland Basin
Discharge from San Luis Drain (SLD)* 541MER535 L E E E E T
Mud Slough (upstream of SLD) 541MER536 L E E E E D
Mud Slough (Downstream of SLD) 541MER542 L E E E E D
Salt Slough @Lander/Hwy 165 541MER531 E E E E E D
West Side Basin
Orestimba Creek @ River Rd. * 541STC019 P E E E E E E E E T
Solado Creek @ Hwy 33 * 541STC515 P E E E E E E E E T
Del Puerto Creek @Vineyard * 541STC516 P E E E E E E E E T
Grayson Drain * 541STC030 P E E E E E E E E T
Ingram Creek @River Rd. * 541STC040 P E E E E E E E E T
Hospital Creek @River Rd. * 541STC042 P E E E E E E E E T
Delta Basin
New Jerusalem Drain* 544SJC501 E E E E E E E E T
Tom Payne Slough @Paradise Rd. 544SJC505 E E E E E E E E E D
Old River @Tracy Blvd 544SJC506 E E E E E E E E E D
Mt. House Creek @ Mt. House Parkway S544SJC509 E E E E E E E E E T
* = Beneficial uses not specifically designated, therefore current listing based on downstream beneficial useE = Exisiting beneficial usesP = Potential beneficial usesL=Existing Limited Beneficial Use
Spawning
SITE SPECIFIC MONITORING BY PROGRAM AND SUB-AREA BASIN Site ID
DRAINAGE BASIN INFLOWS TO SJR
Des
igna
ted
(D) o
r Trib
utar
y (T
)
REC-1
RecreationFreshwater
Habitat Migration
Aquatic Life
Mun
icip
al a
nd
Dom
estic
Sup
ply
(MU
N)
MAIN STEM SAN JOAQUIN RIVER
32
10.0 RESULTS 10.1 Result Summaries All data collected is presented in Appendices A-G. Summary tables of the information were created using the appendices and indicate the number of samples taken, minimum and maximum values ob-served, mean, geo mean, median, quartile 1 and quartile 3 for all of the sites sampled. These summary tables also include sub-basin summaries. These sub-basin summaries do not include the San Luis Drain and New Jerusalem Drain—two sites unique to the basin since they represent shallow groundwa-ter/sub-surface drainage and not typical surface flows. Table 5a provides a summary of the field tem-perature, specific conductance (SC) and pH. Table 5b lists summary results for dissolved oxygen (DO), turbidity and total suspended solids (TSS). Table 5c lists total organic carbon (TOC), total coli-form and E. coli. Table 5d summarizes nitrate, nitrate-N, and total kjeldahl nitrogen. Table 5e lists ammonia as N, phosphorus and ortho-phosphate as P. Table 5f summarizes potassium, biochemical oxygen demand (5-day and 10-day). Table 5g summarizes chloride, sulfate, and calcium. Table 5h provides summaries of magnesium, total dissolved solids (TDS), and carbonate. Table 5i lists bicar-bonate, total alkalinity and sodium. Sample collection for metals and toxicity were limited, so results have been provided in the appendices and are evaluated in the discussion section of the report. A toxic event summary table (Table 6) of the toxicity data collected was created by defining a toxic event as statistically significant and at least a 20% difference from the control. Table 6 shows toxic events for acute fathead minnows, acute Ceriodaphnia dubia, acute algae, chronic fathead minnow and chronic Ceriodaphnia dubia.
33
Table 5a: Temperature, Specific Conductance (SC) and pH Results Summary
Main Stem Site Code Count Min Max MeanGeo
Mean Median Q1 Q3 Count Min Max MeanGeo
Mean Median Q1 Q3 Count Min Max MeanGeo
Mean Median Q1 Q3SJR @Sack Dam 541MAD007 65 5.5 26.4 17.2 16.0 17.1 12.5 22.7 65 85.0 1010 553 519 558 465 661 65 6.2 8.8 7.8 7.8 7.8 7.6 8.0SJR @ Lander 541MER522 265 7.4 30.0 18.1 17.0 18.4 12.9 23.6 265 59.0 2260 1270 1080 1360 867 1720 261 6.5 9.0 7.9 7.9 7.9 7.7 8.2SJR @ Fremont Ford 541MER538 258 6.2 27.5 17.5 17.2 17.9 12.6 23.1 256 171 2730 1462 1340 1465 1170 1760 256 6.3 8.2 7.6 7.6 7.7 7.5 7.8SJR @ Hills Ferry 541STC512 83 8.0 27.8 18.8 17.9 19.2 14.5 23.7 83 220 3080 1760 1650 1790 1500 2100 82 6.6 8.3 7.8 7.8 7.8 7.6 8.0SJR @ Crows 535STC504 261 6.6 28.4 17.5 16.5 17.7 12.9 22.5 261 100 1900 1165 1078 1250 965 1430 259 6.6 8.4 7.8 7.8 7.8 7.7 7.9SJR @ Patterson 541STC507 262 6.9 27.7 18.2 17.2 18.4 13.5 23.3 262 140 1820 1176 1110 1230 988 1420 260 6.6 8.6 7.8 7.8 7.8 7.7 8.0SJR @ Maze 541STC510 260 7.4 27.5 17.8 16.8 17.1 13.1 23.1 260 100 1410 847 786 904 673 1020 258 6.7 9.0 7.9 7.9 7.9 7.7 8.0SJR @ Airport Way/Vernalis 541SJC501 264 7.1 27.1 17.4 16.5 17.0 13.1 22.3 265 97.0 1200 685 636 705 496 848 263 6.1 9.1 7.9 7.9 7.9 7.7 8.1
Southeast Basin Deep Slough Green House Rd 535MER577 54 5.6 29.5 17.4 16.1 17.4 12.0 23.3 54 48.0 983 484 423 470 326 601 54 6.6 8.9 8.0 8.0 7.9 7.7 8.3Santa Rita Slough at Highway 152 541MER015 5 5.7 21.7 14.9 13.3 16.3 9.6 21.2 5 615 830 728 722 731 643 820 5 7.0 8.2 7.5 7.5 7.4 7.1 7.7 Bear Creek Bert Crane Rd 535MER007 60 5.2 27.7 16.9 15.8 17.8 12.0 22.1 60 54.0 238 116 108 106 84.0 137 60 6.8 8.7 7.9 7.9 7.9 7.7 8.1
Southeast Basin Summary 119 5.2 29.5 17.0 15.8 17.5 12.0 22.2 119 48.0 983 309 217 193 102 497 119 6.6 8.9 7.9 7.9 7.9 7.7 8.2
Grassland BasinSalt Slough @Lander/Hwy 165 541MER531 262 6.7 28.1 17.3 16.4 17.5 12.4 22.6 262 769 2470 1420 1370 1400 1130 1670 260 6.3 8.6 7.7 7.7 7.7 7.6 7.8Mud Slough (n) (upstream) @ SLD 541MER536 260 6.6 32.8 18.0 16.8 18.1 12.7 23.1 259 652 3820 1660 1540 1550 1200 2030 257 6.5 8.7 7.9 7.9 7.9 7.8 8.1Discharge from SLD 541MER535 264 7.6 28.7 18.2 17.2 18.5 13.1 23.6 264 3250 5960 4450 4410 4430 4080 4720 261 5.5 8.9 8.1 8.1 8.2 7.9 8.4Mud Slough (n) (downstream) @ SLD 541MER542 264 6.9 29.3 17.9 16.9 18.2 12.6 23.4 264 1200 5140 2854 2710 2805 2040 3503 261 6.6 8.7 8.0 8.0 8.0 7.8 8.3
Grassland Basin Summary* 786 6.6 32.8 17.7 16.7 17.9 12.6 22.9 785 652 5140 1420 1793 1400 1290 2460 778 6.3 8.7 7.9 7.9 7.9 7.7 8.1
Eastside BasinTurner Slough at 4th Avenue 535MER576 51 5.0 29.6 18.5 17.2 19.3 12.7 24.2 51 68.0 474 230 216 212 175 269 51 6.4 9.1 7.7 7.7 7.7 7.5 8.0Merced River Hatfield Park(River Rd) 541MER546 54 8.4 26.8 17.6 16.7 16.7 13.1 23.1 54 41.0 454 183 152 155 100 241 54 6.9 9.2 7.9 7.9 7.8 7.7 8.1Lone Tree Creek @ Austin Rd 531SJC503 49 1.9 24.2 15.1 13.8 15.5 10.6 20.6 49 69.0 605 254 217 225 129 331 49 5.4 8.9 7.6 7.6 7.6 7.4 7.8French Camp Slough @ Airport 531SJC504 48 5.8 25.7 16.0 15.0 15.8 11.4 20.8 48 84.0 738 215 190 171 139 256 47 6.6 8.7 7.6 7.6 7.6 7.4 7.8Harding Drain @ SJR (TID5) 535STC501 74 10.5 26.4 19.0 18.4 18.6 16.0 22.8 74 258 1460 759 710 703 533 1015 74 7.0 8.5 7.7 7.7 7.7 7.6 7.8 Tuolumne River @ Shiloh 535STC513 84 7.7 26.4 17.3 16.5 16.4 12.5 22.1 84 45.0 396 193 175 200 160 240 84 6.7 9.0 7.9 7.8 7.9 7.6 8.1 Stanislaus River @Caswell 535STC514 49 7.3 23.8 15.5 14.9 14.7 11.7 18.9 49 60.0 183 108 104 105 88.0 125 49 6.6 9.0 7.8 7.8 7.8 7.6 8.0
Eastside Basin Summary 409 1.9 29.6 17.2 16.2 17.3 12.5 21.9 409 41.0 1460 299 221 199 133 346 408 5.4 9.2 7.7 7.7 7.7 7.6 7.9
Westside BasinOrestimba Creek @ River Rd. 541STC019 197 3.6 25.8 16.6 15.6 17.3 12.7 20.9 197 8.00 1290 723 692 720 627 820 197 7.3 8.9 8.0 8.0 8.0 7.9 8.1Solado Creek @ Hwy 33 541STC515 70 5.1 26.0 17.4 16.6 17.4 13.5 21.7 70 123 4160 961 838 827 655 1040 70 6.6 9.0 8.2 8.2 8.2 8.1 8.4Del Puerto Creek @Vineyard 541STC516 68 6.7 27.6 17.7 16.7 19.0 12.5 22.1 68 207 1860 874 808 818 629 1090 68 7.2 8.9 8.0 8.0 8.0 7.8 8.2Grayson Drain 541STC030 56 7.1 30.9 18.6 17.9 19.2 14.3 22.1 56 145 1630 836 745 803 649 1038 56 7.3 8.8 8.0 8.0 8.1 7.9 8.2Ingram Creek @River Rd. 541STC040 72 4.5 25.2 16.5 15.8 16.4 13.0 20.6 72 101 2190 1202 1037 1095 800 1575 72 6.3 8.3 7.8 7.8 7.9 7.7 8.0Hospital Creek @River Rd. 541STC042 53 8.8 25.3 17.6 17.0 17.5 14.4 21.0 53 75.0 1980 726 626 662 449 962 53 6.5 8.7 7.8 7.8 7.9 7.7 8.1
Westside Basin Summary 516 3.6 30.9 17.2 16.3 17.5 13.2 21.3 516 8.00 4160 855 765 770 633 995 516 6.3 9.0 8.0 8.0 8.0 7.8 8.2
Northeast BasinCosumnes River @ Twin Cities Rd. 531SAC001 38 5.2 24.9 13.8 12.8 12.7 9.7 19.0 38 46.0 427 106 96.2 97.5 73.3 118 38 6.0 9.3 7.6 7.6 7.8 6.9 8.1Mokelumne River @New Hope Rd. 544SAC002 58 7.0 24.4 15.4 14.7 14.8 11.5 18.9 58 41.0 104 52.1 51.3 49.0 46.3 53.0 57 6.9 10.1 7.8 7.8 7.7 7.4 8.1Pixley Slough @ Davis Rd 531SJC507 54 5.0 23.5 16.5 15.8 17.8 13.0 20.2 54 48.0 275 87.6 79.9 72.5 61.3 97.8 53 6.7 9.4 7.5 7.5 7.4 7.2 7.6Bear Creek @ Thorton Road (J8) 544SJC508 26 5.6 24.2 15.8 14.7 17.2 11.0 20.2 26 57.0 481 153 132 117 87.0 207 25 6.3 8.8 7.4 7.4 7.3 7.1 7.7Bear Creek @Lower Sacramento Rd. 531SJC515 36 7.2 25.9 16.5 15.7 16.4 12.4 21.4 36 55.0 378 151 126 107 70.5 230 36 6.9 7.8 7.3 7.3 7.3 7.1 7.5
Northeast Basin Summary 212 5.0 25.9 15.6 14.7 15.9 11.4 19.8 212 41.0 481 100 84.1 73.0 53.0 111 209 6.0 10.1 7.5 7.5 7.5 7.2 7.8
South Delta Basin
New Jerusalem Drain 544SJC001 52 11.0 20.7 18.0 17.9 18.4 17.4 19.2 52 1340 2790 2420 2410 2440 2300 2560 51 7.1 8.3 7.6 7.6 7.6 7.4 7.9Tom Payne Slough @ Paradise Rd. 544SJC505 56 7.2 25.7 17.2 16.3 17.1 13.2 21.6 56 762 3180 1770 1580 1450 1070 2720 55 6.9 8.2 7.5 7.5 7.5 7.3 7.7Old River @Tracy Blvd 544SJC506 60 8.4 26.6 17.7 16.8 18.4 13.2 22.4 60 150 1230 826 787 826 725 959 59 6.5 8.5 7.7 7.7 7.7 7.5 8.0Mountain House Creek 544SJC509 20 6.8 23.9 15.6 14.5 17.5 10.0 20.2 20 246 2930 1280 863 666 520 1940 20 7.2 8.8 7.7 7.7 7.8 7.6 7.8
South Delta Basin Summary^ 136 6.8 26.6 17.2 16.3 17.6 13.0 21.6 136 150 3180 1770 1063 1450 1070 1438 134 6.5 8.8 7.6 7.6 7.6 7.4 7.8*Discharge from SLD not included into calculations^New Jerusalem Drain not included into calculationsNA = Data not applicableNOTE: For values reported as < (less than), half the detection limit was used
TempºC Field SC (umhos) pH
34
Table 5b: Dissolved Oxygen (DO), Turbidity and Total Suspended Solids (TSS) Results Summary
Main Stem Site Code Count Min Max MeanGeo
Mean Median Q1 Q3 Count Min Max MeanGeo
Mean Median Q1 Q3 Count Min Max MeanGeo
Mean Median Q1 Q3SJR @Sack Dam 541MAD007 51 0.6 13.9 8.8 8.3 8.4 7.7 10.1 18 7.3 112 49.8 39.1 50.7 24.8 69.1 8 18 57 36 34 33 31 43SJR @ Lander 541MER522 217 3.4 23.3 10.2 9.8 9.7 8.5 11.6 60 12.9 114 29.9 27.1 24.5 20.8 34.7 158 15 130 32 30 30 24 37SJR @ Fremont Ford 541MER538 214 1.6 18.5 9.0 8.7 8.7 7.7 10.1 56 12.3 176 76.7 70.4 68.7 59.1 96.5 151 24 180 72 65 66 50 90SJR @ Hills Ferry 541STC512 67 3.9 12.6 8.9 8.7 8.8 8.1 9.7 18 27.5 194 90.8 78.5 66.1 51.4 138 6 34 150 76 66 59 46 98SJR @ Crows 535STC504 216 5.1 15.9 9.5 9.4 9.3 8.5 10.4 55 12.3 273 53.9 48.1 47.9 36.3 61.2 162 16 120 47 44 44 35 56SJR @ Patterson 541STC507 215 7.0 16.3 10.2 10.0 9.8 9.0 11.2 55 12.4 170 46.0 41.5 40.2 31.8 51.9 156 14 170 46 42 42 34 54SJR @ Maze 541STC510 213 4.1 16.4 10.5 10.3 10.3 9.3 11.2 54 12.4 82.0 39.9 37.1 36.6 29.9 47.4 158 14 160 48 44 45 35 54SJR @ Airport Way/Vernalis 541SJC501 216 1.3 16.6 10.6 10.4 10.5 9.5 11.5 54 12.3 86.6 35.2 33.2 30.8 27.2 42.2 163 11 160 44 40 42 33 52
Southeast Basin Deep Slough Green House Rd 535MER577 43 4.2 15.8 8.7 8.4 8.0 7.2 10.1 17 48.6 480 127 98.8 79.3 68.3 113 8 34 220 100 89 93 77 100Santa Rita Slough at Highway 152 541MER015 1 6.2 6.2 6.2 6.2 6.2 6.2 6.2 NA NA NA NA NA NA NA NA 4 2.5 42 19 12 16 8 26 Bear Creek Bert Crane Rd 535MER007 49 6.6 13.8 9.5 9.4 9.1 8.1 10.6 21 10.1 110 43.9 37.5 42.0 20.1 53.4 8 16 170 57 46 50 33 54
Southeast Basin Summary 93 4.2 15.8 9.1 8.9 8.7 7.6 10.3 38 10.1 480 81.0 57.8 56.9 38.6 80.0 20 2.5 220 66 46 53 33 92
Grassland BasinSalt Slough @Lander/Hwy 165 541MER531 216 1.2 14.9 8.3 8.0 8.1 6.8 9.6 60 18.8 330 94.2 84.3 83.2 61.9 119 10 34 170 89 78 74 60 114Mud Slough (n) (upstream) @ SLD 541MER536 210 2.1 19.0 9.5 9.1 9.4 7.9 11.0 54 12.2 142 54.1 44.8 44.1 29.3 68.7 11 11 150 33 24 22 14 30Discharge from SLD 541MER535 218 3.2 30.0 12.9 12.6 12.5 11.5 13.9 55 12.7 70.6 32.1 29.5 26.5 22.5 40.7 234 14 96 45 43 43 36 52Mud Slough (n) (downstream) @ SLD 541MER542 218 2.6 27.6 9.9 9.7 9.8 8.8 10.8 55 13.3 218 45.8 39.0 38.6 26.0 52.7 12 15 72 39 35 41 27 48
Grassland Basin Summary* 644 1.2 27.6 9.2 8.9 9.2 7.7 10.6 169 12.2 330 66 53.6 54.0 34.2 84 33 11 170 52 39 37 25 60
Eastside BasinTurner Slough at 4th Avenue 535MER576 47 3.2 13.3 8.1 7.7 7.8 6.2 9.9 19 62.4 515 146 127 113 94.7 154 6 28 88 46 42 35 30 56Merced River Hatfield Park(River Rd) 541MER546 46 6.7 12.2 9.6 9.5 9.6 8.6 10.4 10 4.3 45.3 14.0 10.4 9.5 5.8 15.5 5 2.5 14 5.1 3.9 3.0 3.0 3.0Lone Tree Creek @ Austin Rd 531SJC503 37 0.4 11.4 8.2 7.7 8.2 7.6 9.5 6 38.8 288 90.4 67.3 51.4 50.1 60.4 10 6.0 130 37 26 23 18 47French Camp Slough @ Airport 531SJC504 38 0.4 13.2 8.6 8.0 8.7 7.5 10.1 8 7.0 335 71.4 36.4 46.1 15.9 51.9 9 3.0 80 33 23 24 15 50Harding Drain @ SJR (TID5) 535STC501 62 5.2 15.3 9.7 9.5 9.5 8.5 10.7 27 0.7 698 53.9 11.2 7.0 5.0 17.9 14 3.0 49 13 10 9.0 7.0 13 Tuolumne River @ Shiloh 535STC513 69 6.8 12.5 9.7 9.6 9.7 8.7 10.5 30 2.1 94.5 12.4 8.1 7.1 4.9 11.8 16 2.5 32 9.0 7.1 7.5 5.3 11 Stanislaus River @Caswell 535STC514 40 7.8 15.1 10.0 9.9 9.9 9.1 10.8 9 0.8 52.3 12.8 7.5 6.2 5.1 14.3 7 2.8 16 8.8 6.9 11 3.0 13
Eastside Basin Summary 339 0.4 15.3 9.2 8.9 9.4 8.1 10.4 109 0.7 698 54.8 18.1 13.0 5.7 57.0 67 2.5 130 20 12 11 6.0 25
Westside BasinOrestimba Creek @ River Rd. 541STC019 176 6.0 17.2 9.9 9.8 9.7 8.7 10.8 52 14.1 810 190 143 165 84.4 258 32 10 780 134 81 76 41 155Solado Creek @ Hwy 33 541STC515 61 6.0 14.9 10.2 10.1 10.1 9.1 11.1 15 14.4 1990 277 82.2 43.5 26.0 224 30 2.0 3200 214 35 37 7.8 91Del Puerto Creek @Vineyard 541STC516 56 4.5 17.8 9.6 9.3 9.2 8.1 11.1 13 5.7 244 75.5 51.0 70.4 37.3 89.0 27 6.0 660 100 52 48 32 87Grayson Drain 541STC030 47 3.4 12.0 9.3 9.1 9.3 8.6 10.2 11 5.3 1340 450 143 477 45.4 651 23 2.5 28000 1821 195 180 59 825Ingram Creek @River Rd. 541STC040 63 7.0 14.5 9.7 9.6 9.5 8.6 10.4 17 3.6 1900 409 132 139 27.9 580 21 0.5 6200 840 180 570 22 1100Hospital Creek @River Rd. 541STC042 47 4.8 15.2 9.6 9.4 9.5 8.5 10.6 13 6.8 365 200 126 208 80.6 307 15 27 3300 900 310 420 85 1100
Westside Basin Summary 450 3.4 17.8 9.8 9.6 9.5 8.5 10.7 121 3.6 1990 244 117 122 53.7 280 148 0.5 28000 584 93 79 35 345
Northeast BasinCosumnes River @ Twin Cities Rd. 531SAC001 27 7.9 14.1 10.7 10.6 10.8 9.6 11.5 11 3.2 248 34.1 14.1 13.4 7.6 16.3 9 2.5 49 22 17 20 11 34Mokelumne River @New Hope Rd. 544SAC002 48 6.6 13.4 9.6 9.5 9.6 8.7 10.8 18 2.6 42.0 11.8 9.2 8.2 6.1 13.2 10 2.5 8.0 4.2 3.7 2.8 2.5 5.8Pixley Slough @ Davis Rd 531SJC507 47 0.7 13.5 7.8 7.3 7.7 6.2 9.1 18 16.1 124 44.3 38.0 40.8 28.4 46.9 7 2.5 57 23 16 25 12 26Bear Creek @ Thorton Road (J8) 544SJC508 16 4.8 11.8 7.7 7.5 7.7 6.4 8.8 2 21.6 39.1 30.4 29.1 30.4 26 34.7 10 2.5 30 15 11 15 7.0 21Bear Creek @Lower Sacramento Rd. 531SJC515 36 2.4 13.9 6.8 6.4 6.3 5.6 8.0 18 11.6 191 48.6 34.8 31.4 17.8 63.9 NA NA NA NA NA NA NA NA
Northeast Basin Summary 174 0.7 14.1 8.5 8.1 8.6 6.7 10.4 67 2.6 248 34.6 21.4 21.6 12.6 42.3 36 2.5 57 15 10 11 3.8 24
South Delta Basin
New Jerusalem Drain 544SJC001 42 8.3 14.6 10.2 10.2 10.1 9.3 10.9 13 0.2 290 30.7 4.1 2.6 0.9 13.9 10 2.5 33 6.7 4.0 2.9 2.5 3.0Tom Payne Slough @ Paradise Rd. 544SJC505 46 2.2 16.2 7.6 7.0 7.1 5.4 9.4 17 3.9 110 25.9 16.9 15.1 10.5 38.1 10 18 59 29 27 27 23 30Old River @Tracy Blvd 544SJC506 50 3.3 14.4 8.8 8.5 8.8 7.4 10.1 20 19.3 55.9 34.6 33.1 32.3 26.8 42.0 10 14 44 28 26 25 21 35Mountain House Creek 544SJC509 12 2.9 11.9 8.9 8.4 9.1 8.1 10.3 6 41.0 274 152 125 131 87.0 230 9 15 110 43 35 34 25 49
South Delta Basin Summary^ 108 2.2 16.2 8.3 7.8 8.3 6.6 10.0 43 3.9 274 47.6 30.5 32.1 17.0 49.7 29 14 110 33 29 27 22 36*Discharge from SLD not included into calculations^New Jerusalem Drain not included into calculationsNA = Data not applicableNOTE: For values reported as < (less than), half the detection limit was used
Dissolved Oxygen (mg/L) Turbidity (ntu) TSS (mg/L)
35
Table 5c: Total Organic Carbon (TOC), Total Coliform and E. coli Results Summary
Main Stem Site Code Count Min Max MeanGeo
Mean Median Q1 Q3 Count Min Max Mean Geo Mean Median Q1 Q3 Count Min Max MeanGeo
Mean Median Q1 Q3SJR @Sack Dam 541MAD007 33 0.5 11 3.9 3.3 3.4 2.5 4.7 30 727 >2420 NA 1944 >2420 1986 >2420 30 19 248 NA 46 43 30 63SJR @ Lander 541MER522 162 0.5 27 8.7 7.6 8.2 5.5 12 47 816 >2420 NA 2273 >2420 >2420 >2420 46 7 >2420 NA 59 50 22 103SJR @ Fremont Ford 541MER538 160 0.5 22 7.9 7.1 7.6 5.3 9.9 46 870 >2420 NA 2321 >2420 >2420 >2420 46 20 >2420 NA 101 83 60 124SJR @ Hills Ferry 541STC512 30 0.5 16 8.2 7.4 8.1 6.3 10 29 >2420 >2420 NA >2420 >2420 >2420 >2420 29 27 >2420 NA 162 124 77 291SJR @ Crows 535STC504 162 0.5 15 6.3 5.6 5.8 3.9 8.2 46 >2420 >2420 NA >2420 >2420 >2420 >2420 46 30 >2420 NA 111 93 60 142SJR @ Patterson 541STC507 161 0.5 22 6.6 5.8 5.8 4.1 8.4 46 >2420 >2420 NA >2420 >2420 >2420 >2420 46 24 >2420 NA 129 114 75 162SJR @ Maze 541STC510 157 0.5 16 5.1 4.4 4.3 3.0 6.4 46 961 >2420 NA 2340 >2420 >2420 >2420 46 24 >2420 NA 95 65 47 156SJR @ Airport Way/Vernalis 541SJC501 163 0.5 18 4.5 3.9 3.8 2.8 5.2 46 457 >2420 NA 2263 >2420 >2420 >2420 46 16 >2420 NA 86 60 38 151
Southeast Basin Deep Slough Green House Rd 535MER577 31 0.5 14 7.3 6.0 6.9 4.4 10 25 866 >2420 NA 2323 >2420 >2420 >2420 25 9 >2420 NA 238 199 96 980Santa Rita Slough at Highway 152 541MER015 5 0.5 24 9.8 5.5 8.4 4.3 12 NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA Bear Creek Bert Crane Rd 535MER007 31 0.5 21 5.9 4.4 4.8 3.3 7.0 30 1553 >2420 NA 2384 >2420 >2420 >2420 30 44 >2420 NA 502 448 265 1276
Southeast Basin Summary 67 0.5 24 6.8 5.2 6.0 3.6 9.6 55 866 >2420 NA 2356 >2420 >2420 >2420 55 9 >2420 NA 358 435 122 1203
Grassland BasinSalt Slough @Lander/Hwy 165 541MER531 38 0.5 21 7.5 6.1 6.9 4.8 8.8 30 613 >2420 NA 2271 >2420 >2420 >2420 30 42 921 NA 124 101 64 159Mud Slough (n) (upstream) @ SLD 541MER536 38 0.5 27 11 9.4 10 8.3 13 29 727 >2420 NA 2295 >2420 >2420 >2420 29 33 >2420 NA 179 152 96 326Discharge from SLD 541MER535 33 0.5 16 8.5 7.2 8.8 5.9 11 30 272 >2420 NA 1800 >2420 1905 >2420 21 1 770 NA 12 9 6 23Mud Slough (n) (downstream) @ SLD 541MER542 39 0.5 32 12 9.6 11 8.6 13 28 1011 >2420 NA 2346 >2420 >2420 >2420 28 6 >2420 NA 76 75 44 101
Grassland Basin Summary* 115 0.5 32 10 8 9.5 6.6 13 87 613 >2420 NA 2303 >2420 >2420 >2420 87 6 >2420 NA 120 101 63 185
Eastside BasinTurner Slough at 4th Avenue 535MER576 29 0.5 53 11.5 8 7.6 5.8 13 28 1414 >2420 NA 2374 >2420 >2420 >2420 28 115 >2420 NA 654 749 381 1363Merced River Hatfield Park(River Rd) 541MER546 26 0.5 9.3 2.9 2.5 2.3 1.8 3.1 26 344 >2420 NA 1973 >2420 >2420 >2420 26 19 1986 NA 120 96 73 276Lone Tree Creek @ Austin Rd 531SJC503 23 2.8 67 19 14 17 6.6 23 21 1011 >2420 NA 2321 >2420 >2420 >2420 21 82 >2420 NA 468 435 238 816French Camp Slough @ Airport 531SJC504 28 0.5 34 8.9 6.3 7.4 4.5 11 22 727 >2420 NA 2291 >2420 >2420 >2420 22 17 1986 NA 182 182 81 304Harding Drain @ SJR (TID5) 535STC501 34 2.3 24 6.9 5.9 5.4 3.9 8.9 40 1733 >2420 NA 2400 >2420 >2420 >2420 40 16 >2420 NA 422 399 258 829 Tuolumne River @ Shiloh 535STC513 34 0.5 8.7 2.7 2.2 2.2 1.7 2.7 46 179 >2420 NA 1843 >2420 >2420 >2420 46 8 649 NA 83 75 43 133 Stanislaus River @Caswell 535STC514 23 0.5 7.0 2.7 2.2 2.1 1.5 3.2 22 411 >2420 NA 1796 >2420 1472 >2420 22 30 308 NA 78 76 50 101
Eastside Basin Summary 197 0.5 67 7.5 4.6 5 2.3 8.0 205 179 >2420 NA 2118 >2420 >2420 >2420 205 8 >2420 NA 205 201 80 517
Westside BasinOrestimba Creek @ River Rd. 541STC019 33 0.5 14 5.0 4.1 4.5 2.6 5.8 39 1011 >2420 NA 2340 >2420 >2420 >2420 39 40 >2420 NA 418 517 182 951Solado Creek @ Hwy 33 541STC515 36 0.5 30 6.1 4.5 4.1 3.2 6.7 40 145 >2420 NA 2117 >2420 >2420 >2420 40 2 >2420 NA 288 387 105 782Del Puerto Creek @Vineyard 541STC516 33 1.8 19 5.5 4.8 4.9 3.2 7.0 38 1300 >2420 NA 2368 >2420 >2420 >2420 38 73 >2420 NA 819 1203 371 >2420Grayson Drain 541STC030 27 2.1 21 6.7 5.9 5.4 4.1 8.8 31 1120 >2420 NA 2361 >2420 >2420 >2420 31 7 >2420 NA 337 260 123 1484Ingram Creek @River Rd. 541STC040 25 0.5 17 5.3 4.0 4.1 2.8 6.2 40 691 >2420 NA 2258 >2420 >2420 >2420 40 9 >2420 NA 214 202 131 463Hospital Creek @River Rd. 541STC042 18 2.8 23 7.6 6.2 5.3 4.0 9.3 33 691 >2420 NA 2330 >2420 >2420 >2420 33 8 >2420 NA 353 272 162 691
Westside Basin Summary 172 0.5 30 5.9 4.8 4.7 3.2 7.5 221 145 >2420 NA 2289 >2420 >2420 >2420 221 2 >2420 NA 368 387 150 1203
Northeast BasinCosumnes River @ Twin Cities Rd. 531SAC001 21 0.5 20 3.6 2.6 2.3 1.8 3.7 16 130 >2420 NA 956 1553 431 >2420 16 29 1046 NA 93 82 42 111Mokelumne River @New Hope Rd. 544SAC002 30 0.5 5.5 2.2 1.9 1.7 1.5 2.9 28 231 >2420 NA 1498 >2420 1147 >2420 28 28 >2420 NA 79 67 46 110Pixley Slough @ Davis Rd 531SJC507 24 1.0 10 3.7 3.0 2.8 2.2 3.8 28 1203 >2420 NA 2316 >2420 >2420 >2420 28 51 >2420 NA 268 256 126 406Bear Creek @ Thorton Road (J8) 544SJC508 15 2.4 23 7.4 5.9 5.8 3.9 7.7 2 411 >2420 NA 997 1416 913 1918 2 46 166 NA 87 106 76 136Bear Creek @Lower Sacramento Rd. 531SJC515 14 2.9 16 8.9 7.7 8.5 4.5 13 28 1553 >2420 NA 2326 >2420 >2420 >2420 28 15 >2420 NA 113 96 47 151
Northeast Basin Summary 104 0.5 23 4.5 3.2 3.0 1.7 5.1 102 130 >2420 NA 1761 >2420 1733 >2420 102 15 >2420 NA 125 102 53 206
South Delta Basin
New Jerusalem Drain 544SJC001 28 0.1 21 3.9 1.6 2.0 0.5 2.7 23 52 >2420 NA 1052 1986 548 >2420 20 1 27 NA 6 6 4 15Tom Payne Slough @ Paradise Rd. 544SJC505 30 0.5 31 6.2 4.5 4.9 4.2 6.2 26 313 >2420 NA 2017 >2420 >2420 >2420 26 7 816 NA 61 47 29 104Old River @Tracy Blvd 544SJC506 31 1.4 17 5.0 4.3 4.1 3.3 5.7 30 770 >2420 NA 2169 >2420 >2420 >2420 30 25 345 NA 74 61 50 104Mountain House Creek 544SJC509 14 2.6 14 7.2 6.1 6.0 4.3 9.7 2 >2420 >2420 NA >2420 >2420 >2420 >2420 2 1046 1203 NA 1122 1125 1085 1164
South Delta Basin Summary^ 75 0.5 31 5.9 4.7 4.6 3.7 6.5 58 313 >2420 NA 2108 >2420 >2420 >2420 58 7 1203 NA 74 60 39 116*Discharge from SLD not included into calculations^New Jerusalem Drain not included into calculationsNA = Data not applicableNOTE: For values reported as < (less than), half the detection limit was used
For values reported as > (greater than), 2420 was used
TOC (mg/L) Total Coliform E. coli
36
Table 5d: Nitrate, Nitrate-N, and Total Kjeldahl Nitrogen Results Summary
Main Stem Site Code Count Min Max MeanGeo
Mean Median Q1 Q3 Count Min Max MeanGeo
Mean Median Q1 Q3 Count Min Max MeanGeo
Mean Median Q1 Q3SJR @Sack Dam 541MAD007 14 2.4 9.7 4.8 4.3 3.9 3.1 5.7 NA NA NA NA NA NA NA NA 23 0.1 1.3 0.8 0.7 1.0 0.7 1.0SJR @ Lander 541MER522 22 1.0 16.0 3.8 2.3 1.0 1.0 6.8 NA NA NA NA NA NA NA NA 21 0.5 3.9 1.5 1.3 1.0 1.0 1.8SJR @ Fremont Ford 541MER538 37 1.0 16.0 5.8 4.7 5.2 2.9 7.4 24 0.1 3.7 1.1 0.8 0.8 0.6 1.6 71 0.5 3.0 1.1 1.0 1.0 1.0 1.2SJR @ Hills Ferry 541STC512 11 3.4 19.0 9.3 8.0 9.6 5.0 13.0 NA NA NA NA NA NA NA NA 21 0.2 2.6 1.1 1.0 1.0 1.0 1.3SJR @ Crows 535STC504 39 4.2 23.0 12.1 11.3 11.0 8.8 15.0 27 0.2 4.5 2.1 1.8 2.1 1.4 2.9 73 0.3 3.0 1.0 0.9 1.0 0.8 1.1SJR @ Patterson 541STC507 20 5.0 18.0 12.7 12.1 13.5 9.1 15.3 NA NA NA NA NA NA NA NA 19 0.5 2.1 1.0 1.0 1.0 1.0 1.0SJR @ Maze 541STC510 19 5.8 15.0 10.5 10.1 11.0 9.1 12.0 NA NA NA NA NA NA NA NA 18 0.5 1.2 1.0 1.0 1.0 1.0 1.0SJR @ Airport Way/Vernalis 541SJC501 23 3.8 12.0 8.4 8.1 8.4 7.6 10.0 NA NA NA NA NA NA NA NA 30 0.2 1.9 0.9 0.9 1.0 0.8 1.0
Southeast Basin Deep Slough Green House Rd 535MER577 11 1.0 23.0 4.8 2.4 1.0 1.0 4.8 NA NA NA NA NA NA NA NA 18 1.0 6.2 1.8 1.5 1.3 1.0 2.1Santa Rita Slough at Highway 152 541MER015 4 1.0 10.0 4.7 2.9 4.0 1.0 7.7 NA NA NA NA NA NA NA NA 3 1.0 1.0 1.0 1.0 1.0 1.0 1.0 Bear Creek Bert Crane Rd 535MER007 11 1.0 31.0 5.5 3.1 3.0 1.8 3.9 NA NA NA NA NA NA NA NA 19 0.2 9.8 1.3 0.9 1.0 0.7 1.0
Southeast Basin Summary 26 1.0 31.0 5.1 2.8 3.0 1.0 5.1 NA NA NA NA NA NA NA NA 40 0.2 9.8 1.5 1.2 1.0 1.0 1.3
Grassland BasinSalt Slough @Lander/Hwy 165 541MER531 14 1.0 15.0 6.0 4.3 5.4 2.4 7.9 NA NA NA NA NA NA NA NA 13 0.5 1.0 1.0 0.9 1.0 1.0 1.0Mud Slough (n) (upstream) @ SLD 541MER536 30 1.0 5.1 1.9 1.5 1.0 1.0 2.6 25 0.03 2.9 0.5 0.3 0.4 0.1 0.6 62 0.5 2.6 1.2 1.1 1.0 1.0 1.4Discharge from SLD 541MER535 19 11.0 110 66.3 58.2 73.0 45.5 89.5 27 5.3 33.0 15.4 13.6 14.0 8.7 20.5 46 0.5 2.5 1.4 1.3 1.2 1.0 1.8Mud Slough (n) (downstream) @ SLD 541MER542 19 4.2 84.0 34.0 23.6 35.0 11.0 53.5 27 1.4 13.0 6.2 5.2 6.1 4.2 8.0 47 0.5 4.5 1.6 1.4 1.5 1.0 1.8
Grassland Basin Summary* 63 1.0 84.0 12.5 4.4 3.9 1.0 11.5 52 0.0 13.0 3.5 1.2 1.6 0.4 6.2 122 0.5 4.5 1.3 1.2 1.1 1.0 1.6
Eastside BasinTurner Slough at 4th Avenue 535MER576 9 1.0 9.9 4.9 3.8 4.2 3.9 5.7 NA NA NA NA NA NA NA NA 16 0.8 32.0 3.5 1.5 1.0 1.0 1.4Merced River Hatfield Park(River Rd) 541MER546 10 1.0 15.0 7.6 6.0 7.3 5.3 10.3 NA NA NA NA NA NA NA NA 9 1.0 2.4 1.2 1.1 1.0 1.0 1.0Lone Tree Creek @ Austin Rd 531SJC503 14 1.0 10.0 4.8 3.8 3.8 3.0 7.1 NA NA NA NA NA NA NA NA 23 0.7 17.0 3.6 2.3 1.5 1.0 4.8French Camp Slough @ Airport 531SJC504 11 2.6 29.0 10.1 7.3 7.3 3.6 12.1 NA NA NA NA NA NA NA NA 19 0.6 4.1 1.4 1.2 1.0 1.0 1.1Harding Drain @ SJR (TID5) 535STC501 14 9.9 44.0 23.1 21.2 21.0 15.0 26.5 NA NA NA NA NA NA NA NA 23 0.1 16.0 5.4 3.4 4.0 2.3 8.4 Tuolumne River @ Shiloh 535STC513 14 2.5 9.3 6.5 6.2 6.7 6.0 7.5 NA NA NA NA NA NA NA NA 14 0.3 2.2 1.0 1.0 1.0 1.0 1.0 Stanislaus River @Caswell 535STC514 11 1.0 3.7 2.1 1.7 1.0 1.0 3.3 NA NA NA NA NA NA NA NA 11 0.1 1.0 0.9 0.8 1.0 1.0 1.0
Eastside Basin Summary 83 1.0 44.0 8.9 5.7 6.3 3.4 10.0 NA NA NA NA NA NA NA NA 115 0.1 32.0 2.8 1.6 1.0 1.0 2.8
Westside BasinOrestimba Creek @ River Rd. 541STC019 10 4.3 20.0 11.1 9.9 10.1 7.4 14.8 NA NA NA NA NA NA NA NA 11 0.5 1.0 1.0 0.9 1.0 1.0 1.0Solado Creek @ Hwy 33 541STC515 12 2.9 23.0 11.1 9.5 9.5 6.9 15.5 NA NA NA NA NA NA NA NA 20 0.6 2.4 1.1 1.1 1.0 1.0 1.0Del Puerto Creek @Vineyard 541STC516 11 1.0 73.0 19.5 11.0 8.5 6.2 28.5 NA NA NA NA NA NA NA NA 16 0.7 16.0 2.5 1.6 1.0 1.0 2.3Grayson Drain 541STC030 11 1.0 30.0 11.1 8.4 8.7 6.2 13.5 NA NA NA NA NA NA NA NA 19 0.2 13.0 1.9 1.1 1.0 0.9 1.5Ingram Creek @River Rd. 541STC040 12 2.3 74.0 34.7 24.6 22.5 16.3 62.0 NA NA NA NA NA NA NA NA 21 0.1 5.8 2.0 1.5 1.8 1.0 2.4Hospital Creek @River Rd. 541STC042 8 7.1 25.0 12.8 11.9 11.0 9.5 13.5 NA NA NA NA NA NA NA NA 12 1.0 4.2 1.7 1.5 1.0 1.0 2.2
Westside Basin Summary 64 1.0 74.0 17.2 11.8 11.0 7.3 20.0 NA NA NA NA NA NA NA NA 99 0.1 16.0 1.7 1.3 1.0 1.0 2.0
Northeast BasinCosumnes River @ Twin Cities Rd. 531SAC001 9 1.0 6.1 2.4 1.8 1.0 1.0 3.6 NA NA NA NA NA NA NA NA 9 1.0 1.0 1.0 1.0 1.0 1.0 1.0Mokelumne River @New Hope Rd. 544SAC002 12 0.5 1.0 1.0 0.9 1.0 1.0 1.0 NA NA NA NA NA NA NA NA 12 1.0 1.0 1.0 1.0 1.0 1.0 1.0Pixley Slough @ Davis Rd 531SJC507 9 1.0 2.1 1.2 1.2 1.0 1.0 1.0 NA NA NA NA NA NA NA NA 15 0.5 1.4 1.0 0.9 1.0 1.0 1.0Bear Creek @ Thorton Road (J8) 544SJC508 12 1.0 5.4 2.3 1.9 2.3 1.0 2.7 NA NA NA NA NA NA NA NA 16 0.5 2.5 1.1 1.1 1.0 1.0 1.0Bear Creek @Lower Sacramento Rd. 531SJC515 NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA 4 0.8 3.7 1.7 1.4 1.2 0.8 2.1
Northeast Basin Summary 42 0.5 6.1 1.7 1.4 1.0 1.0 2.3 NA NA NA NA NA NA NA NA 56 0.5 3.7 1.1 1.0 1.0 1.0 1.0
South Delta Basin
New Jerusalem Drain 544SJC001 10 49.0 77.0 59.1 58.6 58.0 53.0 60.8 NA NA NA NA NA NA NA NA 19 0.8 4.5 1.3 1.1 1.0 1.0 1.0Tom Payne Slough @ Paradise Rd. 544SJC505 12 1.0 8.0 3.8 2.8 3.4 1.0 5.7 NA NA NA NA NA NA NA NA 20 0.6 2.1 1.1 1.1 1.0 1.0 1.3Old River @Tracy Blvd 544SJC506 12 4.8 10.0 7.6 7.4 7.9 6.8 8.4 NA NA NA NA NA NA NA NA 20 0.6 2.1 1.1 1.1 1.0 1.0 1.1Mountain House Creek 544SJC509 10 1.0 7.6 4.5 3.9 5.1 3.1 5.5 NA NA NA NA NA NA NA NA 13 0.6 3.4 1.5 1.3 1.0 1.0 2.1
South Delta Basin Summary^ 34 1.0 10.0 5.3 4.4 5.4 3.1 7.6 NA NA NA NA NA NA NA NA 53 0.6 3.4 1.2 1.1 1.0 1.0 1.2*Discharge from SLD not included into calculations^New Jerusalem Drain not included into calculationsNA = Data not applicableNOTE: For values reported as < (less than), half the detection limit was used
Nitrate (mg/L) Nitrate-N (mg/L) TKN (mg/L)
37
Table 5e: Ammonia as N, Phosphorus and Ortho-Phosphate as P Results Summary
Main Stem Site Code Count Min Max MeanGeo
Mean Median Q1 Q3 Count Min Max MeanGeo
Mean Median Q1 Q3 Count Min Max MeanGeo
Mean Median Q1 Q3SJR @Sack Dam 541MAD007 NA NA NA NA NA NA NA NA 22 0.03 0.2 0.1 0.1 0.1 0.1 0.2 30 0.02 0.5 0.3 0.2 0.5 0.1 0.5SJR @ Lander 541MER522 NA NA NA NA NA NA NA NA 22 0.2 0.5 0.3 0.3 0.3 0.2 0.4 24 0.02 0.5 0.5 0.4 0.5 0.5 0.5SJR @ Fremont Ford 541MER538 17 0.1 0.3 0.1 0.1 0.1 0.1 0.1 67 0.1 0.7 0.3 0.3 0.3 0.2 0.4 78 0.02 0.5 0.3 0.3 0.3 0.1 0.5SJR @ Hills Ferry 541STC512 NA NA NA NA NA NA NA NA 19 0.1 0.4 0.3 0.2 0.3 0.2 0.3 23 0.02 0.5 0.3 0.2 0.5 0.1 0.5SJR @ Crows 535STC504 17 0.1 0.5 0.1 0.1 0.1 0.1 0.1 69 0.1 0.4 0.2 0.2 0.2 0.2 0.3 79 0.02 0.5 0.3 0.2 0.2 0.1 0.5SJR @ Patterson 541STC507 1 0.5 0.5 0.5 0.5 0.5 0.5 0.5 19 0.2 0.5 0.3 0.3 0.3 0.2 0.3 20 0.1 0.5 0.5 0.4 0.5 0.5 0.5SJR @ Maze 541STC510 1 0.5 0.5 0.5 0.5 0.5 0.5 0.5 19 0.1 0.4 0.2 0.2 0.2 0.2 0.3 19 0.1 0.5 0.5 0.4 0.5 0.5 0.5SJR @ Airport Way/Vernalis 541SJC501 1 0.5 0.5 0.5 0.5 0.5 0.5 0.5 31 0.03 0.4 0.2 0.2 0.2 0.2 0.2 33 0.02 0.5 0.4 0.3 0.5 0.2 0.5
Southeast Basin Deep Slough Green House Rd 535MER577 NA NA NA NA NA NA NA NA 18 0.2 1.3 0.5 0.5 0.4 0.3 0.6 24 0.02 1.7 0.5 0.4 0.5 0.2 0.5Santa Rita Slough at Highway 152 541MER015 NA NA NA NA NA NA NA NA 4 0.2 1.0 0.5 0.4 0.4 0.3 0.6 5 0.5 1.5 0.7 0.6 0.5 0.5 0.5 Bear Creek Bert Crane Rd 535MER007 NA NA NA NA NA NA NA NA 19 0.03 0.3 0.2 0.1 0.1 0.1 0.2 25 0.02 2.0 0.3 0.2 0.2 0.1 0.5
Southeast Basin Summary NA NA NA NA NA NA NA NA 41 0.03 1.3 0.4 0.3 0.3 0.2 0.4 54 0.02 2.0 0.5 0.3 0.5 0.1 0.5
Grassland BasinSalt Slough @Lander/Hwy 165 541MER531 NA NA NA NA NA NA NA NA 13 0.2 0.4 0.3 0.3 0.3 0.2 0.4 16 0.1 0.5 0.5 0.5 0.5 0.5 0.5Mud Slough (n) (upstream) @ SLD 541MER536 18 0.1 0.5 0.2 0.2 0.2 0.1 0.3 56 0.1 0.8 0.3 0.3 0.3 0.2 0.4 62 0.02 0.6 0.3 0.3 0.5 0.2 0.5Discharge from SLD 541MER535 19 0.1 1.0 0.2 0.1 0.1 0.1 0.1 41 0.01 0.4 0.1 0.1 0.1 0.1 0.1 35 0.01 0.5 0.3 0.1 0.5 0.02 0.5Mud Slough (n) (downstream) @ SLD 541MER542 21 0.1 0.5 0.2 0.2 0.1 0.1 0.2 42 0.1 0.6 0.3 0.2 0.2 0.1 0.4 44 0.01 0.5 0.3 0.1 0.3 0.02 0.5
Grassland Basin Summary* 39 0.1 0.5 0.2 0.2 0.2 0.1 0.2 111 0.1 0.8 0.3 0.3 0.3 0.2 0.4 122 0.01 0.6 0.3 0.2 0.5 0.2 0.5
Eastside BasinTurner Slough at 4th Avenue 535MER576 NA NA NA NA NA NA NA NA 18 0.1 12.0 1.2 0.3 0.2 0.2 0.3 22 0.02 11.0 1.3 0.3 0.3 0.1 0.5Merced River Hatfield Park(River Rd) 541MER546 NA NA NA NA NA NA NA NA 8 0.1 0.1 0.1 0.1 0.1 0.1 0.1 11 0.5 0.5 0.5 0.5 0.5 0.5 0.5Lone Tree Creek @ Austin Rd 531SJC503 NA NA NA NA NA NA NA NA 24 0.2 4.8 1.3 0.9 0.9 0.5 1.3 26 0.02 2.8 1.0 0.7 0.7 0.5 1.3French Camp Slough @ Airport 531SJC504 NA NA NA NA NA NA NA NA 21 0.1 1.5 0.5 0.3 0.3 0.2 0.5 23 0.02 1.5 0.5 0.3 0.5 0.3 0.5Harding Drain @ SJR (TID5) 535STC501 NA NA NA NA NA NA NA NA 24 0.2 7.5 1.8 1.3 1.6 0.8 2.0 27 0.02 4.4 1.6 1.0 1.4 0.5 2.3 Tuolumne River @ Shiloh 535STC513 NA NA NA NA NA NA NA NA 14 0.1 0.4 0.1 0.1 0.1 0.1 0.2 15 0.1 0.5 0.5 0.4 0.5 0.5 0.5 Stanislaus River @Caswell 535STC514 NA NA NA NA NA NA NA NA 11 0.1 0.1 0.1 0.1 0.1 0.1 0.1 12 0.02 0.5 0.5 0.4 0.5 0.5 0.5
Eastside Basin Summary NA NA NA NA NA NA NA NA 120 0.05 12.0 0.9 0.3 0.3 0.1 1.0 136 0.02 11.0 0.9 0.5 0.5 0.5 1.1
Westside BasinOrestimba Creek @ River Rd. 541STC019 1 0.5 0.5 0.5 0.5 0.5 0.5 0.5 10 0.1 0.4 0.2 0.2 0.2 0.1 0.4 10 0.1 0.5 0.5 0.4 0.5 0.5 0.5Solado Creek @ Hwy 33 541STC515 NA NA NA NA NA NA NA NA 22 0.03 0.4 0.2 0.2 0.2 0.1 0.2 24 0.1 0.5 0.3 0.2 0.4 0.1 0.5Del Puerto Creek @Vineyard 541STC516 NA NA NA NA NA NA NA NA 17 0.1 0.6 0.2 0.2 0.2 0.1 0.3 19 0.1 3.5 0.5 0.4 0.5 0.3 0.5Grayson Drain 541STC030 NA NA NA NA NA NA NA NA 20 0.03 2.9 0.6 0.3 0.3 0.2 0.5 21 0.02 2.5 0.5 0.3 0.5 0.2 0.5Ingram Creek @River Rd. 541STC040 NA NA NA NA NA NA NA NA 23 0.03 1.4 0.3 0.2 0.2 0.1 0.5 25 0.02 0.5 0.3 0.2 0.4 0.1 0.5Hospital Creek @River Rd. 541STC042 NA NA NA NA NA NA NA NA 12 0.1 4.0 0.7 0.5 0.5 0.4 0.6 12 0.1 0.5 0.4 0.4 0.5 0.5 0.5
Westside Basin Summary 1 0.5 0.5 0.5 0.5 0.5 0.5 0.5 104 0.0 4.0 0.4 0.2 0.2 0.1 0.4 111 0.02 3.5 0.4 0.3 0.5 0.2 0.5
Northeast BasinCosumnes River @ Twin Cities Rd. 531SAC001 NA NA NA NA NA NA NA NA 9 0.1 0.4 0.3 0.3 0.3 0.3 0.4 10 0.02 1.0 0.5 0.4 0.5 0.5 0.5Mokelumne River @New Hope Rd. 544SAC002 NA NA NA NA NA NA NA NA 10 0.1 0.1 0.1 0.1 0.1 0.1 0.1 13 0.02 0.5 0.4 0.3 0.5 0.5 0.5Pixley Slough @ Davis Rd 531SJC507 NA NA NA NA NA NA NA NA 16 0.1 0.4 0.2 0.1 0.1 0.1 0.2 16 0.02 0.5 0.3 0.2 0.5 0.1 0.5Bear Creek @ Thorton Road (J8) 544SJC508 NA NA NA NA NA NA NA NA 17 0.1 1.0 0.3 0.2 0.2 0.1 0.3 19 0.10 1.1 0.4 0.3 0.5 0.2 0.5Bear Creek @Lower Sacramento Rd. 531SJC515 NA NA NA NA NA NA NA NA 5 0.1 1.4 0.6 0.3 0.4 0.1 0.8 3 0.02 0.3 0.1 0.1 0.1 0.1 0.2
Northeast Basin Summary NA NA NA NA NA NA NA NA 57 0.1 1.4 0.2 0.2 0.2 0.1 0.3 61 0.02 1.1 0.4 0.3 0.5 0.1 0.5
South Delta Basin
New Jerusalem Drain 544SJC001 NA NA NA NA NA NA NA NA 19 0.03 0.1 0.1 0.1 0.1 0.04 0.1 21 0.02 0.5 0.3 0.1 0.5 0.1 0.5Tom Payne Slough @ Paradise Rd. 544SJC505 NA NA NA NA NA NA NA NA 22 0.1 0.4 0.2 0.2 0.2 0.2 0.3 24 0.02 0.5 0.3 0.2 0.3 0.1 0.5Old River @Tracy Blvd 544SJC506 NA NA NA NA NA NA NA NA 22 0.2 0.7 0.3 0.2 0.2 0.2 0.3 24 0.1 0.5 0.3 0.3 0.2 0.2 0.5Mountain House Creek 544SJC509 NA NA NA NA NA NA NA NA 13 0.1 0.4 0.2 0.2 0.2 0.2 0.3 14 0.02 0.5 0.4 0.3 0.5 0.2 0.5
South Delta Basin Summary^ NA NA NA NA NA NA NA NA 57 0.1 0.7 0.2 0.2 0.2 0.2 0.3 62 0.02 0.5 0.3 0.2 0.4 0.1 0.5*Discharge from SLD not included into calculations^New Jerusalem Drain not included into calculationsNA = Data not applicableNOTE: For values reported as < (less than), half the detection limit was used
Ammonia-N (mg/L) Phosphorus (mg/L) Ortho-phosphate-P (mg/L)
38
Table 5f: Potassium, Biochemical Oxygen Demand (5-day) and Biochemical Oxygen Demand (10-day) Results Summary
Main Stem Site Code Count Min Max MeanGeo
Mean Median Q1 Q3 Count Min Max MeanGeo
Mean Median Q1 Q3 Count Min Max MeanGeo
Mean Median Q1 Q3SJR @Sack Dam 541MAD007 27 3.0 6.9 4.8 4.6 4.6 4.1 5.3 24 0.3 1.2 0.8 0.8 0.8 0.7 0.9 24 0.5 2.0 1.3 1.3 1.4 1.2 1.5SJR @ Lander 541MER522 24 5.4 10 8.1 8.0 8.3 7.1 8.8 42 1.6 9.2 5.6 5.0 6.2 3.1 8.1 42 3.1 17 9.9 8.8 10 5.5 14SJR @ Fremont Ford 541MER538 54 3.3 12 8.3 8.1 8.7 7.7 9.3 41 1.3 4.6 2.6 2.5 2.6 2.0 3.0 41 2.5 6.8 4.5 4.4 4.4 3.6 5.4SJR @ Hills Ferry 541STC512 21 5.4 13 9.4 9.1 10 7.7 11 22 1.7 5.4 3.1 2.9 2.9 2.2 3.9 22 2.7 10 5.6 5.2 5.4 3.8 6.9SJR @ Crows 535STC504 53 3.4 10 6.5 6.3 6.6 5.8 7.6 40 0.7 4.1 1.9 1.7 1.6 1.3 2.5 40 1.4 6.6 3.4 3.1 2.9 2.3 4.6SJR @ Patterson 541STC507 21 3.6 9.3 7.0 6.8 7.4 6.1 8.3 40 1.1 5.8 2.5 2.3 2.3 1.5 3.2 40 2.1 11 4.7 4.3 4.3 3.1 6.1SJR @ Maze 541STC510 20 3.1 7.2 5.7 5.6 6.2 5.3 6.4 39 0.9 6.3 2.1 1.9 1.7 1.3 2.3 39 1.7 13 3.7 3.2 2.9 2.3 4.1SJR @ Airport Way/Vernalis 541SJC501 33 2.4 6.7 4.6 4.4 4.6 4.1 5.2 41 0.7 5.1 1.7 1.5 1.4 1.1 1.9 41 1.3 8.5 3.0 2.6 2.3 1.9 3.3
Southeast Basin Deep Slough Green House Rd 535MER577 23 4.4 16 8.1 7.7 7.4 6.0 9.9 23 2.4 8.5 5.1 4.8 4.6 3.5 6.2 23 4.0 17 9.3 8.6 8.2 6.8 11Santa Rita Slough at Highway 152 541MER015 5 5.0 23 10.3 8.8 8.4 6.0 8.9 4 1.6 8.4 3.8 3.0 2.5 2.2 4.1 4 2.9 17 7.4 5.8 5.0 3.7 8.7 Bear Creek Bert Crane Rd 535MER007 24 1.3 11 2.7 2.4 2.0 1.8 2.9 24 0.7 7.6 2.3 1.8 1.6 1.1 1.9 24 1.4 16 4.2 3.3 2.8 2.1 4.1
Southeast Basin Summary 52 1.3 23 5.9 4.5 4.9 2.2 7.9 51 0.7 8.5 3.7 2.9 2.9 1.6 5.5 51 1.4 17 6.7 5.3 5.2 2.9 8.6
Grassland BasinSalt Slough @Lander/Hwy 165 541MER531 15 8.2 10 8.9 8.9 9.0 8.6 9.2 27 1.0 4.2 2.1 2.0 2.0 1.6 2.5 27 2.0 7.1 3.6 3.5 3.3 2.8 4.3Mud Slough (n) (upstream) @ SLD 541MER536 41 5.7 15 9.2 8.9 9.4 7.2 11 26 1.2 5.7 2.8 2.6 2.5 2.2 3.3 26 2.4 10 5.0 4.7 4.7 3.9 6.1Discharge from SLD 541MER535 20 5.4 13 9.2 9.0 8.6 8.2 10 22 0.9 5.8 3.2 2.8 3.3 1.6 4.5 22 1.6 11 5.6 4.7 5.0 2.6 8.4Mud Slough (n) (downstream) @ SLD 541MER542 21 8.3 12 10 10 10 9.6 11 26 1.2 7.3 3.4 3.0 3.2 2.2 4.6 26 2.3 12 5.9 5.4 5.6 3.8 7.4
Grassland Basin Summary* 77 5.7 15 9.5 9.3 9.5 8.5 11 79 1.0 7.3 2.7 2.5 2.4 1.9 3.3 79 2.0 12 4.8 4.4 4.2 3.3 5.9
Eastside BasinTurner Slough at 4th Avenue 535MER576 21 2.4 100 17.1 6.8 4.2 3.4 5.6 20 2.1 8.7 4.9 4.3 3.9 2.9 7.6 20 3.6 17 8.6 7.4 6.1 5.0 13Merced River Hatfield Park(River Rd) 541MER546 10 0.5 2.5 1.4 1.2 1.5 0.7 1.7 22 0.1 3.3 0.6 0.4 0.5 0.3 0.6 22 0.3 7.3 1.1 0.8 0.7 0.6 0.9Lone Tree Creek @ Austin Rd 531SJC503 24 2.4 53 19 14 19 5.8 29 23 1.3 8.3 5.1 4.2 5.6 2.4 8.0 23 2.2 17 9.6 7.7 8.0 4.4 16French Camp Slough @ Airport 531SJC504 24 1.9 37 9.8 7.5 7.2 4.6 11 23 1.0 16 3.6 2.7 2.2 1.6 3.6 23 1.8 34 6.6 4.7 3.7 2.9 6.2Harding Drain @ SJR (TID5) 535STC501 25 1.2 21 11 9.5 9.9 7.3 15 24 1.0 8.2 5.9 5.4 6.4 4.6 7.5 24 3.3 17 12 11 13 8.4 16 Tuolumne River @ Shiloh 535STC513 14 1.1 6.2 2.4 2.1 1.8 1.6 2.9 24 0.1 5.6 0.7 0.5 0.5 0.3 0.7 24 0.2 8.4 1.2 0.8 0.8 0.7 1.2 Stanislaus River @Caswell 535STC514 11 0.5 2.3 1.5 1.4 1.7 1.2 1.8 21 0.2 6.2 0.8 0.6 0.5 0.4 0.7 21 0.4 8.8 1.3 1.0 0.9 0.8 1.0
Eastside Basin Summary 129 0.5 100 11 5.6 5.0 2.3 14 157 0.1 16.4 3.1 1.6 2.0 0.5 5.2 157 0.2 34 5.8 2.9 3.5 0.9 8.5
Westside BasinOrestimba Creek @ River Rd. 541STC019 11 5.2 9.4 7.1 7.0 6.8 6.2 7.9 23 0.5 4.0 1.6 1.4 1.3 1.0 2.1 23 0.9 8.4 2.9 2.4 2.1 1.7 3.4Solado Creek @ Hwy 33 541STC515 22 3.3 12 6.9 6.4 6.6 4.9 7.9 23 0.2 8.3 2.0 1.4 1.5 1.0 1.9 23 0.6 15 3.5 2.5 2.6 1.5 3.1Del Puerto Creek @Vineyard 541STC516 18 2.6 16 6.7 6.1 5.9 5.4 7.5 17 0.7 6.9 2.2 1.7 1.4 0.9 3.1 17 0.9 12 4.2 3.0 2.2 1.5 6.2Grayson Drain 541STC030 20 2.7 15 7.0 6.0 5.8 4.2 8.4 18 0.6 8.5 3.3 2.2 2.0 0.9 4.8 18 1.0 17 6.3 4.0 3.7 1.7 7.5Ingram Creek @River Rd. 541STC040 23 0.9 15 6.6 5.1 5.2 3.0 10 23 0.2 7.6 2.2 1.3 1.7 0.6 3.1 23 0.3 16 3.7 2.1 3.1 0.8 5.0Hospital Creek @River Rd. 541STC042 12 4.0 13 8.0 7.5 7.5 5.6 11 12 0.5 8.3 3.0 2.0 2.5 1.1 4.0 12 1.0 14 5.2 3.6 3.9 1.8 6.9
Westside Basin Summary 106 0.9 16 7.0 6.2 6.3 4.6 8.5 116 0.2 8.5 2.3 1.6 1.5 0.9 3.1 116 0.3 17 4.1 2.7 2.6 1.5 5.3
Northeast BasinCosumnes River @ Twin Cities Rd. 531SAC001 10 1.7 8.4 3.6 3.3 3.3 2.9 3.8 19 0.3 3.9 1.1 0.8 0.6 0.5 1.4 19 0.4 6.1 1.8 1.3 1.0 0.8 2.7Mokelumne River @New Hope Rd. 544SAC002 13 0.5 1.5 0.7 0.6 0.5 0.5 0.5 24 0.1 1.2 0.4 0.4 0.4 0.3 0.5 24 0.2 1.9 0.6 0.6 0.5 0.4 0.6Pixley Slough @ Davis Rd 531SJC507 19 1.1 5.4 2.3 2.1 2.3 1.5 2.7 18 0.7 4.8 1.9 1.6 1.4 1.0 2.6 18 1.0 8.5 3.4 2.7 2.4 1.7 4.5Bear Creek @ Thorton Road (J8) 544SJC508 20 1.4 19 6.8 5.0 4.6 2.4 10 19 0.4 8.4 2.4 1.9 2.0 1.1 2.8 19 0.9 15 4.5 3.6 3.9 2.1 6.1Bear Creek @Lower Sacramento Rd. 531SJC515 5 1.9 17 10 8.3 10 9.9 12 5 0.9 8.0 2.6 1.8 1.3 1.3 1.5 5 1.5 16 5.1 3.3 2.5 2.2 2.7
Northeast Basin Summary 67 0.5 19 4.1 2.5 2.5 1.4 4.3 85 0.1 8.4 1.5 1.0 0.9 0.5 1.9 85 0.2 16 2.6 1.6 1.6 0.6 3.7
South Delta Basin
New Jerusalem Drain 544SJC001 24 1.8 19 4.7 4.1 4.2 3.8 4.8 23 0.1 0.4 0.1 0.1 0.1 0.1 0.2 23 0.1 0.7 0.2 0.1 0.1 0.1 0.3Tom Payne Slough @ Paradise Rd. 544SJC505 25 2.0 14 6.6 6.1 6.7 4.5 7.8 23 0.8 8.6 4.5 3.7 4.4 2.5 6.7 23 1.5 16 7.7 6.4 7.2 4.5 12Old River @Tracy Blvd 544SJC506 25 3.0 8.1 5.3 5.1 5.3 4.4 5.9 24 1.2 6.1 3.0 2.6 2.6 1.9 3.7 24 2.5 10 5.1 4.6 4.2 3.3 6.4Mountain House Creek 544SJC509 15 3.9 22 11 9.4 7.4 6.0 19 12 1.2 8.0 3.3 2.6 2.3 1.6 3.9 12 2.0 15 6.2 5.0 4.2 3.4 7.9
South Delta Basin Summary^ 65 2.0 22 7.2 6.3 5.9 4.5 7.6 59 0.8 8.6 3.6 3.0 2.9 1.9 5.1 59 1.5 16 6.3 5.3 4.9 3.4 8.1*Discharge from SLD not included into calculations^New Jerusalem Drain not included into calculationsNA = Data not applicableNOTE: For values reported as < (less than), half the detection limit was used
BOD 5-Day (mg/L) BOD 10-Day (mg/L)Potassium (mg/L)
39
Table 5g: Chloride, Sulfate, and Calcium Results Summary
Main Stem Site Code Count Min Max MeanGeo
Mean Median Q1 Q3 Count Min Max MeanGeo
Mean Median Q1 Q3 Count Min Max MeanGeo
Mean Median Q1 Q3SJR @Sack Dam 541MAD007 26 24 150 86 81 89 72 100 26 27 130 66 61 55 46 87 27 17 45 28 27 25 23 32SJR @ Lander 541MER522 20 120 390 260 240 240 200 320 20 62 210 110 100 96 84 150 21 38 96 59 58 57 52 62SJR @ Fremont Ford 541MER538 26 150 440 260 250 240 220 300 27 130 330 210 200 200 170 240 28 51 96 68 67 67 58 75SJR @ Hills Ferry 541STC512 25 160 460 300 290 290 250 340 24 180 550 380 360 390 290 450 25 56 130 90 88 89 72 100SJR @ Crows 535STC504 26 49 250 164 158 160 153 180 29 49 310 206 190 210 150 270 29 20 78 56 54 60 48 70SJR @ Patterson 541STC507 17 95 240 160 160 160 140 180 19 78 280 190 180 200 170 230 19 30 74 58 56 59 49 69SJR @ Maze 541STC510 16 25 180 110 100 120 89 140 18 26 200 110 100 120 89 150 18 25 59 42 41 43 35 50SJR @ Airport Way/Vernalis 541SJC501 27 18 400 100 87 97 70 110 30 19 470 100 85 90 65 100 30 18 52 35 34 36 31 40
Southeast Basin Deep Slough Green House Rd 535MER577 25 7 98 38 32 32 19 53 25 16 64 37 34 36 27 47 26 20 52 34 33 34 28 40Santa Rita Slough at Highway 152 541MER015 5 61 100 84 82 84 81 92 5 49 150 104 96 120 71 130 5 26 67 47 45 46 38 59 Bear Creek Bert Crane Rd 535MER007 26 3 8 4 4 3 3 6 25 4 13 6 6 5 5 7 27 7 18 11 11 10 9 14
Southeast Basin Summary 56 3 100 27 13 16 4 45 55 4 150 29 17 19 5 45 58 7 67 25 20 22 10 37
Grassland BasinSalt Slough @Lander/Hwy 165 541MER531 18 150 310 230 220 230 200 260 19 140 290 200 200 210 160 250 19 54 79 65 64 64 59 71Mud Slough (n) (upstream) @ SLD 541MER536 26 53 490 240 220 220 190 270 29 40 910 320 260 270 180 440 29 36 160 62 59 56 48 70Discharge from SLD 541MER535 18 430 690 520 520 520 470 550 20 1300 1900 1490 1480 1450 1380 1600 20 230 350 290 290 290 270 310Mud Slough (n) (downstream) @ SLD 541MER542 18 140 560 380 360 400 270 470 20 200 1700 950 810 1100 480 1300 20 61 310 170 160 190 100 220
Grassland Basin Summary* 62 53 560 230 220 250 200 345 68 40 1700 200 200 280 195 250 68 36 310 95 81 66 56 93
Eastside BasinTurner Slough at 4th Avenue 535MER576 23 5 260 43 15 9 7 16 23 6 110 25 17 13 10 21 24 12 41 20 19 17 15 22Merced River Hatfield Park(River Rd) 541MER546 11 3 35 12 9 9 6 12 10 3 17 8 7 9 4 10 11 4 20 11 10 12 8 14Lone Tree Creek @ Austin Rd 531SJC503 23 3 41 15 11 16 4 19 22 4 21 10 9 10 5 13 24 6 37 18 17 17 13 24French Camp Slough @ Airport 531SJC504 20 3 55 15 10 11 5 20 20 4 53 16 11 12 5 19 20 7 52 20 17 17 12 24Harding Drain @ SJR (TID5) 535STC501 29 20 250 88 77 71 57 120 27 12 81 43 39 45 29 54 29 17 76 44 41 42 33 52 Tuolumne River @ Shiloh 535STC513 18 3 28 15 13 15 12 16 17 3 14 8 8 8 7 9 19 5 22 14 14 15 13 17 Stanislaus River @Caswell 535STC514 11 2 7 4 4 4 3 6 9 3 7 5 5 6 3 7 11 7 13 10 10 10 8 12
Eastside Basin Summary 135 2 260 34 16 15 6 42 128 3 110 20 13 12 7 24 138 4 76 22 19 17 13 28
Westside BasinOrestimba Creek @ River Rd. 541STC019 15 53 120 88 86 90 75 99 17 46 150 93 88 97 59 120 17 24 66 44 41 42 28 56Solado Creek @ Hwy 33 541STC515 26 32 150 99 94 100 89 110 24 40 380 130 110 120 71 150 26 19 80 41 39 39 31 47Del Puerto Creek @Vineyard 541STC516 20 35 170 120 110 120 110 140 20 130 470 250 230 250 180 300 20 22 60 42 41 46 33 50Grayson Drain 541STC030 23 35 410 130 120 120 96 150 21 32 360 130 110 130 83 140 23 17 82 46 43 40 37 58Ingram Creek @River Rd. 541STC040 26 85 300 180 170 170 120 250 24 59 310 190 170 180 130 270 26 30 150 78 71 64 57 110Hospital Creek @River Rd. 541STC042 16 27 160 100 90 110 80 130 14 33 160 97 86 92 66 130 16 21 79 46 43 44 32 56
Westside Basin Summary 126 27 410 124 111 110 91 140 120 32 470 153 130 130 91 183 128 17 150 51 46 46 35 59
Northeast BasinCosumnes River @ Twin Cities Rd. 531SAC001 13 2 10 6 5 5 4 9 13 1 12 7 6 7 4 9 13 5 10 8 8 8 7 8Mokelumne River @New Hope Rd. 544SAC002 16 3 5 3 3 3 3 3 16 2 3 3 3 3 2 3 16 4 5 4 4 4 4 4Pixley Slough @ Davis Rd 531SJC507 20 3 40 8 5 4 4 6 20 3 22 5 4 4 3 5 20 5 18 9 8 8 7 10Bear Creek @ Thorton Road (J8) 544SJC508 17 4 17 8 7 6 5 11 17 3 14 6 5 5 4 7 17 6 21 11 10 9 8 15Bear Creek @Lower Sacramento Rd. 531SJC515 7 4 19 9 7 5 4 14 7 3 8 5 4 3 3 6 7 5 16 10 9 7 6 16
Northeast Basin Summary 73 2 40 7 5 4 3 8 73 1 22 5 4 4 3 6 73 4 21 8 7 7 5 9
South Delta Basin
New Jerusalem Drain 544SJC001 25 220 360 310 310 310 290 320 25 320 610 470 460 470 420 510 25 51 180 150 150 150 140 160Tom Payne Slough @ Paradise Rd. 544SJC505 25 100 500 280 250 240 150 450 25 95 490 280 240 220 140 450 25 42 160 94 84 74 55 150Old River @Tracy Blvd 544SJC506 25 8 180 120 100 120 100 130 25 65 180 110 100 100 87 120 25 25 59 43 42 41 38 48Mountain House Creek 544SJC509 15 26 410 190 129 130 63 385 15 23 490 182 87 45 32 450 15 19 86 42 35 24 22 77
South Delta Basin Summary^ 65 8 500 280 250 140 100 250 65 23 490 280 240 130 87 250 65 19 160 62 52 48 38 74*Discharge from SLD not included into calculations^New Jerusalem Drain not included into calculationsNA = Data not applicableNOTE: For values reported as < (less than), half the detection limit was used
Chloride (mg/L) Sulfate (mg/L) Calcium (mg/L)
40
Table 5h: Magnesium, Total Dissolved Solids (TDS), and Carbonate Results Summary
Main Stem Site Code Count Min Max MeanGeo
Mean Median Q1 Q3 Count Min Max MeanGeo
Mean Median Q1 Q3 Count Min Max MeanGeo
Mean Median Q1 Q3SJR @Sack Dam 541MAD007 27 8 23 16 16 16 14 18 17 260 600 385 375 380 340 430 23 0.5 0.5 0.5 0.5 0.5 0.5 0.5SJR @ Lander 541MER522 21 16 46 28 27 23 22 33 16 520 1200 830 810 800 710 970 17 0.5 13 1.2 0.6 0.5 0.5 0.5SJR @ Fremont Ford 541MER538 27 25 53 39 38 39 34 43 21 600 1400 960 950 970 850 1100 24 0.5 0.5 0.5 0.5 0.5 0.5 0.5SJR @ Hills Ferry 541STC512 25 31 68 50 49 49 42 57 15 150 1700 1100 1000 1100 1100 1300 22 0.5 4.0 0.7 0.5 0.5 0.5 0.5SJR @ Crows 535STC504 29 10 45 30 28 31 27 34 24 220 1100 704 667 715 625 845 25 0.5 0.5 0.5 0.5 0.5 0.5 0.5SJR @ Patterson 541STC507 19 15 41 29 28 31 27 34 15 390 1100 740 710 750 660 880 15 0.5 0.5 0.5 0.5 0.5 0.5 0.5SJR @ Maze 541STC510 18 13 33 23 22 24 18 27 14 310 690 500 500 540 480 550 14 0.5 0.5 0.5 0.5 0.5 0.5 0.5SJR @ Airport Way/Vernalis 541SJC501 30 9 29 18 18 19 16 22 25 180 630 420 400 410 370 510 26 0.5 4.0 0.6 0.5 0.5 0.5 0.5
Southeast Basin Deep Slough Green House Rd 535MER577 26 9 30 18 17 18 13 22 17 190 530 330 320 320 290 420 22 0.5 52 3.6 0.8 0.5 0.5 0.5Santa Rita Slough at Highway 152 541MER015 5 14 23 19 18 21 15 21 5 360 510 430 430 440 370 470 5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 Bear Creek Bert Crane Rd 535MER007 27 3 11 5 5 4 4 7 17 50 150 97 94 92 84 110 23 0.5 0.5 0.5 0.5 0.5 0.5 0.5
Southeast Basin Summary 58 3 30 12 9 12 4 19 39 50 530 243 195 210 96 360 50 0.5 52 1.9 0.6 0.5 0.5 0.5
Grassland BasinSalt Slough @Lander/Hwy 165 541MER531 19 25 44 36 35 36 33 39 15 550 1100 880 860 880 750 1000 16 0.5 0.5 0.5 0.5 0.5 0.5 0.5Mud Slough (n) (upstream) @ SLD 541MER536 29 25 90 49 46 43 36 56 24 160 2700 1100 980 990 850 1400 25 0.5 10 1.2 0.6 0.5 0.5 0.5Discharge from SLD 541MER535 20 82 110 93 93 90 86 100 89 2500 4400 3300 3300 3300 3100 3600 16 0.5 20 2.7 0.9 0.5 0.5 0.5Mud Slough (n) (downstream) @ SLD 541MER542 20 31 110 73 69 72 52 90 16 800 3900 2400 2100 2700 1400 3200 16 0.5 20 2.2 0.9 0.5 0.5 0.9
Grassland Basin Summary* 68 25 110 52 48 43 36 70 55 160 3900 880 860 1000 855 1700 57 0.5 20 1.3 0.6 0.5 0.5 0.5
Eastside BasinTurner Slough at 4th Avenue 535MER576 24 5 21 9 8 8 6 9 15 92 2000 450 260 170 140 520 20 0.5 23 2.0 0.7 0.5 0.5 0.5Merced River Hatfield Park(River Rd) 541MER546 11 1 7 4 3 4 3 5 10 57 220 100 92 88 61 130 12 0.5 0.5 0.5 0.5 0.5 0.5 0.5Lone Tree Creek @ Austin Rd 531SJC503 24 3 17 9 8 8 5 11 16 54 410 220 200 230 190 273 24 0.5 0.5 0.5 0.5 0.5 0.5 0.5French Camp Slough @ Airport 531SJC504 20 3 40 11 9 9 6 12 14 84 460 210 190 200 110 240 20 0.5 30 2.5 0.7 0.5 0.5 0.5Harding Drain @ SJR (TID5) 535STC501 29 5 18 12 11 11 9 15 17 160 760 500 460 530 330 660 25 0.5 0.5 0.5 0.5 0.5 0.5 0.5 Tuolumne River @ Shiloh 535STC513 19 2 9 6 6 6 6 7 11 68 190 121 116 120 99 140 14 0.5 0.5 0.5 0.5 0.5 0.5 0.5 Stanislaus River @Caswell 535STC514 11 2 6 4 4 4 3 5 9 42 120 73 69 75 52 87 12 0.5 0.5 0.5 0.5 0.5 0.5 0.5
Eastside Basin Summary 138 1 40 9 7 8 5 11 92 42 2000 100 187 170 108 130 127 0.5 30 1.0 0.6 0.5 0.5 0.5
Westside BasinOrestimba Creek @ River Rd. 541STC019 17 16 35 25 25 26 19 33 13 320 550 430 420 420 380 500 13 0.5 0.5 0.5 0.5 0.5 0.5 0.5Solado Creek @ Hwy 33 541STC515 26 11 69 31 28 29 21 37 15 330 940 543 520 500 430 600 23 0.5 24 2.1 0.7 0.5 0.5 0.5Del Puerto Creek @Vineyard 541STC516 20 16 94 35 31 31 24 39 10 340 770 570 550 560 470 670 17 0.5 28 2.5 0.8 0.5 0.5 0.5Grayson Drain 541STC030 23 12 54 30 28 27 22 42 12 240 800 500 480 480 380 630 20 0.5 2.0 0.6 0.5 0.5 0.5 0.5Ingram Creek @River Rd. 541STC040 26 17 59 40 38 38 33 51 15 380 1700 1100 953 1300 625 1400 23 0.5 6.0 0.9 0.6 0.5 0.5 0.5Hospital Creek @River Rd. 541STC042 16 10 62 28 25 23 18 33 6 200 740 530 490 570 480 620 13 0.5 4.0 0.8 0.6 0.5 0.5 0.5
Westside Basin Summary 128 10 94 32 29 31 22 39 71 200 1700 430 420 520 425 670 109 0.5 28 1.3 0.6 0.5 0.5 0.5
Northeast BasinCosumnes River @ Twin Cities Rd. 531SAC001 13 2 5 4 4 4 3 4 8 60 120 93 90 100 75 110 9 0.5 0.5 0.5 0.5 0.5 0.5 0.5Mokelumne River @New Hope Rd. 544SAC002 16 1 2 1 1 1 1 2 9 24 47 36 35 33 30 45 12 0.5 0.5 0.5 0.5 0.5 0.5 0.5Pixley Slough @ Davis Rd 531SJC507 20 2 5 3 3 3 2 3 10 5 140 81 62 85 59 120 16 0.5 0.5 0.5 0.5 0.5 0.5 0.5Bear Creek @ Thorton Road (J8) 544SJC508 17 2 10 5 4 4 3 6 12 45 190 104 92 91 58 140 17 0.5 0.5 0.5 0.5 0.5 0.5 0.5Bear Creek @Lower Sacramento Rd. 531SJC515 7 2 8 5 4 3 3 8 2 160 190 180 170 180 170 180 3 0.5 0.5 0.5 0.5 0.5 0.5 0.5
Northeast Basin Summary 73 1 10 3 3 3 2 4 41 5 190 85 70 100 45 120 57 0.5 0.5 0.5 0.5 0.5 0.5 0.5
South Delta Basin
New Jerusalem Drain 544SJC001 25 5 72 61 60 61 58 67 15 1100 1900 1600 1600 1600 1600 1700 21 0.5 0.5 0.5 0.5 0.5 0.5 0.5Tom Payne Slough @ Paradise Rd. 544SJC505 25 21 89 53 46 43 29 83 15 450 2000 1400 1200 1800 670 1900 21 0.5 0.5 0.5 0.5 0.5 0.5 0.5Old River @Tracy Blvd 544SJC506 25 13 32 23 22 22 20 26 15 280 720 510 500 490 460 590 21 0.5 16 1.2 0.6 0.5 0.5 0.5Mountain House Creek 544SJC509 15 8 64 30 23 17 14 59 9 240 1900 1157 837 1800 390 1800 13 0.5 0.5 0.5 0.5 0.5 0.5 0.5
South Delta Basin Summary^ 65 8 89 36 30 26 20 44 39 240 2000 1400 1200 610 465 1900 55 0.5 16 0.8 0.5 0.5 0.5 0.5*Discharge from SLD not included into calculations^New Jerusalem Drain not included into calculationsNA = Data not applicableNOTE: For values reported as < (less than), half the detection limit was used
Magnesium (mg/L) TDS (mg/L) Carbonate (mg/L)
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Table 5i: Bicarbonate, Total Alkalinity and Sodium Results Summary
Main Stem Site Code Count Min Max MeanGeo
Mean Median Q1 Q3 Count Min Max MeanGeo
Mean Median Q1 Q3 Count Min Max MeanGeo
Mean Median Q1 Q3SJR @Sack Dam 541MAD007 22 78 170 110 110 110 100 120 22 78.0 140 92.5 91.6 90.0 83.3 94.0 23 49.0 170 76.1 73.2 75.0 62.0 83.0SJR @ Lander 541MER522 17 130 300 240 230 240 220 250 17 130 260 200 200 200 180 210 17 95.0 320 200 200 200 160 240SJR @ Fremont Ford 541MER538 23 140 270 220 210 220 200 240 22 140 220 180 180 180 170 200 24 130 310 220 210 220 190 250SJR @ Hills Ferry 541STC512 22 150 290 240 230 250 200 260 22 150 240 200 200 200 180 220 22 160 370 280 280 280 240 330SJR @ Crows 535STC504 24 72.0 230 166 160 180 145 200 23 60.0 190 139 135 150 125 160 25 41.0 250 154 143 150 140 180SJR @ Patterson 541STC507 14 80.0 220 170 160 180 150 200 13 80.0 180 150 140 150 140 160 15 62.0 200 150 140 160 140 190SJR @ Maze 541STC510 13 68.0 290 150 140 160 120 180 12 70.0 240 130 130 140 120 140 14 47.0 140 100 100 110 89.5 120SJR @ Airport Way/Vernalis 541SJC501 25 50.0 150 120 120 130 112 150 24 53.0 130 100 100 110 98.0 120 26 30.0 130 83.8 79.6 83.5 72.3 99.8
Southeast Basin Deep Slough Green House Rd 535MER577 21 96.0 270 190 180 200 140 240 21 96.0 260 170 160 160 120 210 22 23.0 94.0 52.0 48.0 53.5 35.3 66.0Santa Rita Slough at Highway 152 541MER015 5 100 140 122 121 120 120 130 5 80.0 120 101 100 98.0 97.0 110 5 32.0 87.0 67.8 64.3 73.0 71.0 76.0 Bear Creek Bert Crane Rd 535MER007 22 34.0 120 58.9 55.3 49.0 44.0 67.5 22 30.0 100 49.1 46.2 40.0 36.5 57.5 23 3.00 70.0 8.5 5.93 5.00 4.00 7.50
Southeast Basin Summary 48 34.0 270 123 101 120 53.0 180 48 30.0 256 105 85.7 97.5 43.0 150 50 3.00 94.0 33.6 18.9 26.0 5.00 55.0
Grassland BasinSalt Slough @Lander/Hwy 165 541MER531 16 150 250 210 210 220 180 240 16 130 210 180 180 180 160 200 15 130 250 200 200 210 170 230Mud Slough (n) (upstream) @ SLD 541MER536 24 180 400 280 270 280 250 320 23 150 330 230 230 230 200 265 25 100 630 280 250 230 190 410Discharge from SLD 541MER535 15 76.0 260 190 180 190 150 230 14 96.0 210 160 150 160 130 200 16 560 800 660 660 670 600 708Mud Slough (n) (downstream) @ SLD 541MER542 15 140 290 220 210 240 170 270 14 120 240 190 180 190 160 220 16 150 740 480 440 520 300 650
Grassland Basin Summary* 55 140 400 210 210 250 180 280 53 120 330 180 180 200 160 230 56 100 740 200 200 240 170 230
Eastside BasinTurner Slough at 4th Avenue 535MER576 19 56.0 1290 250 150 110 83.5 150 19 56.0 1100 210 120 89 68.5 120 20 11.0 500 85.9 33.6 21.5 15.5 42.5Merced River Hatfield Park(River Rd) 541MER546 12 18.0 120 54.8 48.1 50.0 32.3 68.3 12 15.0 96.0 46.1 41.3 42.0 29.3 56.0 12 3.00 35.0 13.1 10.5 11.0 6.00 14.8Lone Tree Creek @ Austin Rd 531SJC503 24 34.0 300 110 93.8 96.5 59.5 140 24 28.0 250 92.3 78.6 82.0 48.8 110 24 3.00 27.0 11.1 9.39 11.5 5.75 14.3French Camp Slough @ Airport 531SJC504 20 39.0 350 110 89.6 78.5 61.5 120 19 32.0 240 88.9 75.5 73.0 51.0 99.0 20 3.00 45.0 13.3 10.1 10.5 6.00 14.5Harding Drain @ SJR (TID5) 535STC501 25 80.0 560 240 221 250 160 290 25 60.0 460 200 184 200 130 240 25 22.0 210 102 91.7 92.0 64.0 130 Tuolumne River @ Shiloh 535STC513 14 37.0 110 73.7 70.7 71.5 67.8 89.0 14 30.0 93.0 62.5 60.2 60.0 56.3 73.3 14 5.00 25.0 15.1 14.1 14.0 13.3 18.8 Stanislaus River @Caswell 535STC514 12 30.0 110 55.3 51.5 55.5 39.0 66.3 12 27.0 86.0 45.8 43.5 46.0 33.5 54.3 12 3.00 8.00 5.00 4.72 4.50 3.75 6.25
Eastside Basin Summary 126 18 1290 142 101 90.0 60.3 150 125 15.0 1100 118 85.3 76.0 52.0 120 127 3.00 500 41.3 18.0 14.0 7.00 38.5
Westside BasinOrestimba Creek @ River Rd. 541STC019 12 110 210 140 130 120 110 160 11 90.0 170 120 120 110 92.0 140 13 56.0 94.0 74.4 73.3 75.0 62.0 86.0Solado Creek @ Hwy 33 541STC515 23 100 220 150 140 130 120 180 23 84.0 180 120 120 120 97.0 150 23 52.0 150 97.3 94.2 94.0 82.5 110Del Puerto Creek @Vineyard 541STC516 17 82.0 460 180 160 170 140 180 17 82.0 380 150 140 140 110 150 17 62.0 160 110 100 110 91.0 130Grayson Drain 541STC030 20 44.0 360 160 150 160 130 180 20 54.0 290 130 120 130 110 150 20 24.0 180 98.7 90.5 110 72.0 120Ingram Creek @River Rd. 541STC040 23 110 320 200 190 180 150 260 23 93.0 270 170 160 150 130 210 23 73.0 240 150 140 140 100 220Hospital Creek @River Rd. 541STC042 13 100 180 140 140 150 110 160 13 80.0 150 120 120 130 100 130 13 24.0 130 95.1 88.7 99.0 80.0 120
Westside Basin Summary 108 44 460 140 130 150 120 160 107 54.0 380 120 120 130 100 150 109 24.0 240 108 100 100 80.0 120
Northeast BasinCosumnes River @ Twin Cities Rd. 531SAC001 9 43.0 70.0 51.1 50.6 50.0 46.0 51.0 9 35.0 60.0 42.8 42.3 40.0 40.0 44.0 9 4.00 15.0 10.8 10.0 12.0 7.00 13.0Mokelumne River @New Hope Rd. 544SAC002 12 18.0 30.0 23.9 23.6 22.5 20.8 27.5 12 15.0 30.0 20.7 20.3 20.0 18.0 22.5 12 2.00 4.00 2.75 2.68 3.00 2.00 3.00Pixley Slough @ Davis Rd 531SJC507 16 20.0 55.0 38.5 36.9 38.0 29.8 47.0 15 20.0 45.0 32.3 31.2 30.0 25.5 39.0 16 3.00 16.0 5.88 5.10 4.50 4.00 6.00Bear Creek @ Thorton Road (J8) 544SJC508 17 26.0 130 58.0 51.4 51.0 32.0 79.0 16 21.0 110 49.0 43.1 40.0 29.3 66.3 17 4.00 17.0 7.82 6.80 7.00 4.00 12.0Bear Creek @Lower Sacramento Rd. 531SJC515 3 29.0 100 72.0 63.2 87.0 58.0 93.5 3 24.0 84.0 59.7 52.3 71.0 47.5 77.5 3 4.00 16.0 12.0 10.1 16.0 10.0 16.0
Northeast Basin Summary 57 18.0 130 45.0 40.1 41.0 28.0 51.0 55 15.0 110 37.8 33.7 34.0 23.5 43.0 57 2.00 17.0 6.89 5.60 5.00 4.00 12.0
South Delta Basin
New Jerusalem Drain 544SJC001 21 260 380 360 350 370 350 370 20 210 310 290 290 300 300 310 21 210 340 300 300 310 290 320Tom Payne Slough @ Paradise Rd. 544SJC505 21 110 410 280 260 290 190 390 20 110 340 240 220 260 160 320 21 85.0 380 240 210 270 130 360Old River @Tracy Blvd 544SJC506 21 84.0 190 148 144 150 130 160 20 69.0 160 130 120 130 180 140 21 10.0 140 97.8 88.7 100 84.0 110Mountain House Creek 544SJC509 13 82.0 480 238 178 110 99.0 450 12 79.0 400 208 159 94.5 83.0 373 13 35.0 490 224 135 93.0 57.0 480
South Delta Basin Summary^ 55 82.0 480 280 260 170 130 345 52 69.0 400 240 220 260 160 293 55 10.0 490 240 210 120 90 310*Discharge from SLD not included into calculations^New Jerusalem Drain not included into calculationsNA = Data not applicableNOTE: For values reported as < (less than), half the detection limit was used
Total Alkalinity (mg/L)Bicarbonate (mg/L) Sodium (mg/L)
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Table 6: Toxicity Toxic Event Summary
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12.0 DISCUSSION The main stem river and sub-basin tiers of the SJR SWAMP effort have two main objectives: evaluate overall water quality, both temporally and spatially, and assess whether there is any indication that beneficial uses are not being protected. A third adaptive objective is to utilize the information gathered at the long-term sites for the sub-basins to help design future monitoring efforts within that sub-basin. This section discusses the results in the context of those objectives. This five-year study covered: three dry water years, one below normal water year, and one wet year. The final year of this study was one of the wettest years on record. The overall water year effects as well as seasonal effects between storm, snowmelt, irrigation and dry seasons are depicted in a series of paired line graphs for each constituent specifically evaluated: one graph for the SJR sites and one for the Northeast Basin sites (representing temporal trends within sub-basins). If trends within one of the other sub-basins differed greatly from the Northeast Basin, a separate figure was included within the discussion. Similarly, spatial trends were depicted using paired box and whisker figures: one figure showing sum-mary information for SJR sites moving downstream; and the second figure showing summary informa-tion for each sub-basin, also moving downstream, as well as summary information for the San Luis Drain and New Jerusalem Drain which represent shallow groundwater within the Grassland and Delta sub-basins, respectively. Drainage basin sites were selected as being representative of the major flows to the SJR from each basin. While graphical summary information for each sub-basin was not included within this section of the report, the figures are available in Appendix R. Wherever possible, water quality objectives, guidelines and/or targets have been noted on the figures to help put the results in context. Evaluation of the constituents and their potential impacts on the beneficial uses is evaluated in section 12.2. The data collected was utilized in combination with other available data sets during the development of the draft 2009 Clean Water Act Section 305(b) and 303(d) Integrated Report for the Central Valley Region that identifies specific beneficial use impair-ments for water body segments throughout the Central Valley. A summary of potential concerns for each sub-basin that may aid future monitoring design is included in the summary/conclusion of this re-port. All the sites are located relatively close together in the lower reaches of the individual sub-basin prior to discharge into the SJR, therefore have similar localized land use influences, the most notable being dominance by agricultural return flows during the irrigation season. Source water does vary widely, from Sierra snow melt to imports from the Sacramento-San Joaquin Delta and may also include storm water, wetland drainage, operational spill, and ground water discharge. 12.1 Temporal and Spatial Trends 12.1.1 TEMPERATURE Temperature was measured in degrees Celsius and ranged from 1.9 – 32.8 throughout the Basin dur-ing the 5-year study. A very consistent seasonal oscillation was seen at all the sites and tracked those within the Northeast Basin. The lowest temperatures were seen in January around 5ºC with a gradual climb to its peak in July around 25ºC (Figures 8 and 9). The majority of the South Delta Basin sites showed the same seasonal oscillation as the Northeast Ba-sin except New Jerusalem Drain. The New Jerusalem Tile Drain had relatively higher temperatures and shorter amplitude oscillations then the rest of the South Delta Basin sites. Through dry and wet years the temperature showed no significant differences.
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No significant spatial differences were observed either moving upstream to downstream along the main stem of the SJR, nor between sub-basins. Figures 10 and 11 show the relatively consistent ranges in temperature within the basins and SJR, respectively. Figure 8: San Joaquin River Northeast Basin Temperature WY01-WY05
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Cosumnes River @ Twin Cities Rd. Mokelumne River @New Hope Rd. Pixley Slough @ Davis RdBear Creek @ Thorton Road (J8)Bear Creek @Lower Sacramento Rd. Bay-Delta Authority Target, SJR @ Vernalis (Apr 1-Jun 30 & Sept 1- Nov 30, 20ºC)
Figure 9: San Joaquin River Main Stem Temperature WY01-WY05
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Figure 10: Basin Temperatures WY01-WY05
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Figure 11: San Joaquin River Main Stem Temperature WY01-WY05
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12.1.2 SPECIFIC CONDUCTANCE Specific conductance (SC) values ranged from 8.0 - 5,960 µmhos/cm across the SJR Basin. Seasonal patterns in SC were not as clearly defined as for temperature. In general, SC tended to decrease dur-ing the dry season (September through November), sometimes showing a peak during the first storm runoff and then decreasing until the irrigation season began in May/June with the highest concentra-tions recorded during the irrigation season. Exceptions to this rule include water bodies that receive wetland releases in early spring (Grasslands sub-Basin and SJR), where additional spikes are evident (Steenson, et al., 1998). This pattern is depicted in Figures 12 and 13, the NE Basin and SJR sites, respectively. In addition, overall SC values appeared to decrease during wet WY 2005, although the seasonal trend patterns remained similar. Temporal anomalies within each sub-basin are discussed below. Northeast Basin: The Northeast basin was managed from April through October by diverting water into different channels to supply agricultural use. Each growing season, Bear Creek, which naturally would be dry for the summer months like the Cosumnes River, was dominated by agricultural supply that was diverted from the Mokelumne River. This change in water type was observed each year when the Bear Creek SC dropped to about 50 µmhos/cm, the approximate year round SC of the Mokelumne River. Pixley Slough is also dominated by agricultural supply during the growing season and seemed to follow the same trend, but it wasn’t as dramatic as Bear Creek. The one notable difference between the dif-ferent water year types was that Bear Creek was about 100 µmhos/cm higher during winter months of a wet year than during the dry years. Eastside Basin: French Camp Slough and Lone Tree Creek followed the Northeast Basin’s Bear Creek trend with having lower concentrations of SC in the growing season and higher concentrations during the winter. The Harding Drain also followed this same trend of higher levels during the winter months and lower levels during the agricultural season but the levels of SC are much higher than any of the other agricultural influenced sites in this basin (e.g. Turner Slough). The Eastside river sites were fairly consistent throughout the 5 years with Stanislaus River demonstrating little seasonal variability. The Tuolumne River is a little more sporadic, but always seemed to drop in April. The Merced River had the opposite trend when compared to Bear Creek in the Northeast Basin. Specific conductance levels on the Merced River went up during the growing season and down in the winter months. Southeast Basin: Bear Creek in the Southeast Basin, like the Eastside rivers, didn’t fluctuate drastically and showed sporadic levels similar to the Tuolumne River although no seasonal trends seemed to be evident in Bear Creek. Dramatic changes were identified in Deep Slough, similar to the Harding Drain, but seemed to drop drastically in the 2005 wet year when compared to the previous consecutive dry years. South Delta Basin: The South Delta Basin’s SC levels were mostly above 500 µmhos/cm unlike the Northeast basin where all the samples were below 500 µmhos/cm. The New Jerusalem Drain (dis-charging shallow groundwater from the basin) reported consistently high SC levels all year long fluctu-ating around 2500 µmhos/cm with no noticeable consistent trend. Mountain House Creek, an ephemeral stream which historically received agricultural tail water, was dry for about half of the sampling period through 2003. In 2004, the site was removed from the sampling program due to the rapid community development with about 43,500 residents settling on the land ad-jacent to and surrounding the creek (Weston, 2009). The change in localized land use included rerout-ing storm water runoff into a collection system and resulted in continuous dry conditions for the original creek bed. During sampling conducted prior to the development (from December 2000 through Febru-ary 2001), Mountain House Creek had seasonally stable SC values (typically below 1000 umhos/cm), similar to New Jerusalem Drain.
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Old River is dominated by estuary flow characteristics. Old River followed the same SC characteristics of the Tuolumne River on the Eastside Basin fluctuating throughout the year with lower SC levels measured during the 2005 wet year, but overall Old River fluctuated at a higher SC level. Tom Payne Slough fluctuated like the Harding Drain with drastic fluctuations between summer and win-ter months. Like the Harding Drain, Tom Payne Slough has influences other than agricultural which include NPDES discharges and tidal influences. However, similar to the rest of the Delta Basin sites, Tom Payne Slough generally reported higher SC concentrations than the Harding Drain. Westside Basin: Like the Delta Basin, the Westside Basin had higher SC levels than the Northeast Ba-sin. Westside sites Del Puerto Creek, Grayson Drain, Ingram Creek, Hospital Creek and Orestimba Creek are ephemeral streams dominated by irrigation return flows. Ingram Creek had the largest SC fluctuations during the irrigation season and was the only creek to have very high distinct SC values during the winter months. Orestimba Creek receives operational spill from the CCID (Central California Irrigation District) Main Canal which could result in dilution and may have contributed to the narrower range of fluctuation in SC levels when compared to the other Westside sites. Grassland Basin: The Grassland Sites had higher values of SC than most of the other basin sites. The San Luis Drain represents shallow groundwater discharge from approximately 97,000-acres (Bureau of Reclamation, 1995) of irrigated agriculture and affects SC values observed in Mud Slough (Figure 14). All the Grassland sites had an oscillating trend that peaked in March or April, which corresponds to both wetland releases and pre-irrigation runoff (Figure 14). The Grassland Basin is highly managed and does not demonstrate a significant difference between water year types aside from slightly lower SC values during the 2005 wet year. Spatially, the Northeast, Eastside and Southeast Basins had considerably lower levels of SC as com-pared to the South Delta, Westside, and Grassland Basins (Figure 15). The eastern basins draining the Sierra watershed begin with less saline water than those dependent on imports from the Delta. Al-though each basin had unique seasonal and temporal trends, during the 2005 wet water year there was a slight decrease in the SC values at most sites. Inflows from the various sub-basins appear to have a dramatic overall effect on the SJR as the inflows progressively reach the river (Figures 15 and 16). As we travel downstream, Southeast Basin flows tend to be trapped at Sack Dam and diverted. The SJR at Lander Avenue is dominated by ground wa-ter accretion for much of the year and provides a background elevated SC in the river. High SC levels in Salt Slough and Mud Slough, resulting from wetland as well as surface and subsurface agricultural drainage, increase the already elevated river levels. Starting immediately downstream of the Hills Ferry site, the Eastside tributaries (Merced, Tuolumne and Stanislaus Rivers) begin to influence SC levels along the SJR and gradually lower them resulting in levels observed at Vernalis that are just slightly higher than at Sack Dam.
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Figure 12: San Joaquin River Northeast Basin Specific Conductivity WY01-WY05
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Figure 13: San Joaquin River Main Stem Specific Conductivity WY01-WY05
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hos/
cm)
Salt Slough @Lander/Hwy 165 Mud Slough (n) (upstream) @ San Luis Dra in Dis charge from SLD Mud Slough (n) (downstream) @ San Luis Dra in Basin Plan Objective for SJR @ Vernal is (Apr 1-Aug 31, 700 µm hos/cm; Sep 1-Mar 31,1000 µmhos/cm)
Figure 14: San Joaquin River Grassland Basin Specific Conductivity WY01-WY05
50
Figure 15: Basin Specific Conductivity WY01-WY05 Figure 16: San Joaquin River Main Stem Specific Conductivity WY01-WY05
0
1000
2000
3000
4000
5000
6000
SJR @Sack Dam
SJR @LanderAvenue
SJR @Fremont
Ford
SJR @Hills Ferry
SJR @Crows
Landing
SJR @Patterson
SJR @Maze
SJR @AirportWay
Spec
ific
Con
duct
ivity
(µm
hos/
cm)
Median
0
1000
2000
3000
4000
5000
6000
Sou
thea
stB
asin
Gra
ssla
ndB
asin
Eas
tsid
e B
asin
Wes
tsid
e B
asin
Nor
thea
stBa
sin
Del
ta B
asin
Dis
char
ge a
tS
LD New
Jeru
sale
mD
rain
Spec
ific
Cond
uctiv
ity (
µmho
s/cm
)
Median
51
12.1.3 MEASURED pH The pH values ranged from 5.4 – 10.1 across the basin. Mean values in the SJR ranged from 7.6 to 7.9 units. Few levels dropped below 6.5 pH units, though several appeared to seasonally exceed 7.5 units—during the irrigation season in the SJR and during the storm season in the Northeast Basin. Seasonal variability appeared reduced during wet WY 2005. Occasional spikes, both high and low, were seen throughout the sampling season (Figures 17 and 18). Most of the basins appeared to follow the general trend of the Northeast Basin, with the majority of pH values falling between 7 and 8 units. The Cosumnes River had a wider range of variability compared to the Mokelumne River and the other sites. The variability seen in the Cosumnes River seemed to be most pronounced following its natural annual dry period. The Westside Basin showed similar occa-sional fluctuations as the Northeast Basin but reported slightly higher concentrations ranging most fre-quently from 7.7 to 8.4 pH units. The Grassland Basin and the SJR sites were sampled more frequently (weekly) and demonstrated clear seasonal fluctuations with the exception of Salt Slough. The pH values found in the river and Grasslands would peak in July and drop around January, following the same trend seen in temperature results. During the 2005 wet water year, there was no peak in July which can probably be attributed to the greater flows seen during this time when compared to the previous dry years. Spatially, the Northeast, Eastside and Southeast basins reported slightly lower pH than the Westside and Grassland Basin’s (Figure 19). Those differences did not appear to impact the SJR, as there does not appear to be any distinct difference in pH moving downstream (Figure 20). All of the river sites are approximately the same range and like the basin sites show occasional fluctuations, with the smallest minimums and greatest maximums recorded at the furthest upstream (SJR at Sack Dam) and down-stream (SJR at Airport) sites.
52
Figure 17: San Joaquin River Northeast Basin pH WY01-WY05 Figure 18: San Joaquin River Main Stem Specific Conductivity WY01-WY05
5
6
7
8
9
10O
ct-0
0
Jan-
01
Apr
-01
Jul-0
1
Oct
-01
Jan-
02
Apr
-02
Jul-0
2
Oct
-02
Jan-
03
Apr
-03
Jul-0
3
Oct
-03
Jan-
04
Apr
-04
Jul-0
4
Oct
-04
Jan-
05
Apr
-05
Jul-0
5
Sample Date
pH
Cosumnes River @ Twin Cities Rd. Mokelumne River @New Hope Rd. Pixley Slough @ Davis Rd Bear Creek @ Thorton Road (J8)Bear Creek @Lower Sacramento Rd. Basin Plan Objective (6.5-8.5)
5
6
7
8
9
10
Oct
-00
Jan-
01
Apr
-01
Jul-0
1
Oct
-01
Jan-
02
Apr
-02
Jul-0
2
Oct
-02
Jan-
03
Apr
-03
Jul-0
3
Oct
-03
Jan-
04
Apr-0
4
Jul-0
4
Oct
-04
Jan-
05
Apr-0
5
Jul-0
5
Sample Date
pH
SJR @Sack Dam SJR @ Lander SJR @ Fremont FordSJR @ Hills Ferry SJR @ Crows SJR @ Patterson SJR @ Maze SJR @ Airport Way/Vernalis Basin Plan Objective (6.5-8.5)
53
Figure 19: Basin pH WY01-WY05 Figure 20: San Joaquin River Main Stem pH WY01-WY05
5
6
7
8
9
10
SJR @Sack Dam
SJR @LanderAvenue
SJR @Fremont
Ford
SJR @Hills Ferry
SJR @Crows
Landing
SJR @Patterson
SJR @Maze
SJR @AirportWay
pH
Median Basin Plan Objective (6.5-8.5)
5
6
7
8
9
10So
uthe
ast
Bas
in
Gra
ssla
nd
Bas
in
Eas
tsid
eB
asin
Wes
tsid
eB
asin
Nor
thea
stB
asin
Del
ta B
asin
Dis
char
ge
atSL
D
New
Jeru
sale
mD
rain
pH
Med ian Basin P lan Ob jective (6 .5 -8.5 )
54
12.1.4 DISSOLVED OXYGEN Dissolved oxygen is well known to have clear diurnal patterns which make grab sampling for trend ana-lyses challenging, even if collecting at the same time each day. It was interesting to note that during this sampling effort, the variability in collecting weekly samples (Figure 21—the San Joaquin River sites) almost masked the seasonal pattern that was more evident with monthly sample collection (Fig-ure 22—the Northeast Basin). In general, dissolved oxygen (DO) had a defined seasonal oscillation that is opposite of temperature. Dissolved oxygen concentrations tended to increase from October through April and decrease from May through September. The same pattern was evident during wet WY 2005, but the range in concentrations was much less. Only discharge from the San Luis and New Jerusalem Drains (both carrying shallow groundwater from their respective basins) did not appear to have significant seasonal patterns with concentrations remaining near 10 mg/L at both sites. Spatially, the Grassland and Westside Basins had consistently higher DO levels than the Northeast Basin and non-river Eastside Basin sites, with the non-river sites of French Camp Slough and Lone Tree Creek reporting the lowest recorded DO concentration (0.4 mg/L) in May 2002 and October 2004, respectively. The highest values were observed in the San Luis Drain which had a mean of 12.5 mg/L. The river itself did not demonstrate much spatial variability with the majority of the reported values tracking near 10 mg/L DO. The greatest overall site variability was noted at Lander Avenue, with high and low spikes that did not tend to track the remaining sites. The two lowest overall DO concentrations of 0.6-mg/L and 1.3-mg/L were recorded at Sack Dam and at Airport Way, the most upstream and most downstream sites, respectively
55
Figure 21: San Joaquin River Main Stem Dissolved Oxygen WY01-WY05
0
5
10
15
20
25
Apr
-01
Jul-0
1
Oct
-01
Jan-
02
Apr
-02
Jul-0
2
Oct
-02
Jan-
03
Apr
-03
Jul-0
3
Oct
-03
Jan-
04
Apr-0
4
Jul-0
4
Oct
-04
Jan-
05
Apr-0
5
Jul-0
5
Sample Date
DO (m
g/L)
SJR @Sack Dam SJR @ Lander SJR @ Fremont Ford SJR @ Hills Ferry SJR @ Crows SJR @ Patterson SJR @ Maze SJR @ Airport Way/Vernalis Basin Plan Objective (7.0 mg/L)
Figure 22: San Joaquin River Northeast Basin Dissolved Oxygen WY01-WY05
0
5
10
15
20
25
Apr-0
1
Jul-0
1
Oct
-01
Jan-
02
Apr
-02
Jul-0
2
Oct
-02
Jan-
03
Apr
-03
Jul-0
3
Oct
-03
Jan-
04
Apr
-04
Jul-0
4
Oct
-04
Jan-
05
Apr
-05
Jul-0
5
Sample Date
DO
(mg/
L)
Cosumnes River @ Twin Cities Rd. Mokelumne River @New Hope Rd. Pix ley Slough @ Davis Rd Bear Creek @ Thorton Road (J8)Bear Creek @Lower Sacramento Rd. Basin Plan Objective (7.0 mg/L)
56
12.1.5 TURBIDITY Turbidity findings are based on samples taken from July 2002 through June 2004, which encompasses portions of three water years: WY2001 (dry); WY2002 (dry); and WY2003 (below normal). The limited data set does not appear to demonstrate specific seasonal trends reporting spikes and dips throughout the year with individual sites both in the Northeast Basin and along the SJR. However, most sites did demonstrate a spike in turbidity that corresponded to a winter storm in December 2002 (Figures 23 and 24). Most of the sites appeared to show the greatest fluctuation in concentrations during the WY2003 irrigation season (April through August 2003), with a number of high values recorded. Mud Slough (north) and Salt Slough within the Grassland Sub-Basin also demonstrated increases during wetland flood-up (September) and wetland releases (April). Both these water bodies receive drainage from wet-land habitat. These spikes were echoed in data for the San Joaquin River at Hills Ferry and at Fremont Ford—sites downstream of the Grasslands’ inflows but upstream of the first Eastside river inflow (the Merced River). Spatially, the Westside and Grassland Basins reported higher overall turbidity than basins draining the Sierra or the Delta. The exception was the Southeast Basin which had overall turbidity concentrations similar to the Grassland Basin. Both basins receive wetland drainage. The Westside basin consists of ephemeral streams dominated by agricultural discharges and reported greater and more frequent fluctuations in turbidity then the rest of the Basins (Figure 25). Storm water inflows and run-off were the most evident in Salado Creek during the 2002 storm event resulting in a turbidity value of 1990 NTU. The differences in the Basins are clearly shown by how they affect the SJR (Figure 26). Figure 27 pro-vides an example of the impact that sub-basin inflow can have on the SJR during a pre-irrigation and wetland drainage period (23 – 27 March 2003). The dashed pink line representing a 5% increase over “background” Lander Avenue concentrations, helps visualize Westside inflows to the river increasing turbidity until the main Eastside rivers provide fresh water and bring the turbidity back down to slightly above SJR at Lander levels. Figure 28 is an example during the winter storm event (18 – 19 December 2002). The Westside influences again raise the turbidity above “background” Lander Avenue concen-trations until after Hills Ferry when the Eastside Rivers enter the system. Figure 28 shows that during a winter storm event, turbidity in the SJR at Lander is greater than the turbidity downstream at Vernalis—opposite the finding during early spring.
57
Figure 23: San Joaquin River Northeast Basin Turbidity WY02-WY04 Figure 24: San Joaquin River Main Stem Turbidity WY01-WY05
0
50
100
150
200
250
300
350
Jul-0
2
Oct
-02
Jan-
03
Apr
-03
Jul-0
3
Oct
-03
Jan-
04
Apr
-04
Sample Date
Turb
idity
(NTU
)
Cosumnes River @ Twin Cities Rd. Mokelumne River @New Hope Rd. Pixley Slough @ Davis Rd Bear Creek @ Thorton Road (J8)Bear Creek @Lower Sacramento Rd.
0
50
100
150
200
250
300
350
Apr
-02
Jul-0
2
Oct
-02
Jan-
03
Apr
-03
Jul-0
3
Oct
-03
Jan-
04
Sample Date
Turb
idity
(ntu
)
SJR @Sack Dam SJR @ Lander SJR @ Fremont FordSJR @ Hills Ferry SJR @ Crows SJR @ Patterson SJR @ Maze SJR @ Airport Way/Vernalis
58
Figure 25: Basin Turbidity WY02-WY04
0
50
100
150
200
250
300
350
Sou
thea
stB
asin
Gra
ssla
ndB
asin
Eas
tsid
eBa
sin
Wes
tsid
eB
asin
Nor
thea
stB
asin
Del
ta B
asin
Dis
char
ge a
tSL
D
New
Jeru
sale
mDr
ain
Turb
idity
(ntu
)
1990
698
Median
480
Figure 26: San Joaquin River Main Stem Turbidity WY02-WY04
0
50
100
150
200
250
300
350
SJR @Sack Dam
SJR @LanderAvenue
SJR @Fremont
Ford
SJR @Hills Ferry
SJR @Crows
Landing
SJR @Patterson
SJR @Maze
SJR @AirportWay
Turb
idity
(ntu
) Median
59
0
20
40
60
80
100
120
140
708090100110120130
SJR Mileage
Turb
idity
(NTU
)
Basin Plan objective with Lander as natural background
Basin Plan Objective with the river sites as natural background
Land
er
Frem
ont F
ord
Hill
s Fe
rry
Pat
ters
onCro
ws
Maz
e
Airp
ort
Way
/Ver
nalis
(Sal
t Slo
ugh
@ L
ande
r/Hw
y 16
5: 1
50 N
TU)
(Tur
ner S
loug
h at
4th
Ave
nue:
102
NTU
)
(Mud
slo
ugh
(n) (
dow
nstre
am)
@S
an L
uis
Dra
in: 8
2.5
NTU
)
(Mer
ced
Riv
e rH
atfie
ld P
ark
(Riv
erR
oad)
: 15.
9 N
TU)
(Ore
stim
ba C
reek
@
Riv
er R
d: 8
6.3
NTU
)
(Sta
nisl
aus
Riv
er @
Cas
wel
l: 6
.2 N
TU)
(Ingr
am C
reek
@ R
iver
Rd:
139
NTU
)
(Tuo
lum
ne ri
ver @
Shi
loh:
5.7
NTU
)
(Gra
yson
Dra
in: 5
.9 N
TU)
(Del
Pue
rto C
reek
@ V
iney
ard:
122
NTU
)
(Sal
ado
Cre
ek @
Hw
y 33
: 19.
2 N
TU)
(Har
ding
Dra
in d
isch
arge
@ S
anJo
aqui
n R
iver
(TID
5): 6
98 N
TU)
NorthSouth Flow
Figure 27: Turbidity Influences on the San Joaquin River from Lander to Airport Way/ Vernalis 3-25-03 and 3-27-03. Blue data points represent turbidity concentrations on the river. Pink lines are the Basin Plan objective with the river sites as background. Orange arrows represent west side influences, green arrows represent eastside influences and blue arrows repre-sent major tributary input.
60
60
80
100
120
140
160
180
200
708090100110120130
SJR Mileage
Turb
idity
(NTU
)
Basin Plan Objective with Lander as natural background
Basin Plan Objective with the river sites as natural background
Land
er
Frem
ont F
ord
Hill
s Fe
rry
Pat
ters
on
Cro
ws
Maz
e
Airp
ort
Way
/Ver
nalis
(Sal
t Slo
ugh
@ L
ande
r/Hw
y 16
5: 5
5.0
(Tur
ner S
loug
h at
4th
Ave
nue:
182
NTU
)
(Mud
slo
ugh
(n) (
dow
nstre
am)
@S
an L
uis
Dra
in: 2
4.8
NTU
)
(Mer
ced
Riv
er H
atfie
ldP
ark
(Riv
er R
oad)
: 45.
3 N
TU)
(Ore
stim
ba C
reek
@ R
iver
Rd:
49.
4 N
TU)
(Sta
nisl
aus
Riv
er @
Cas
wel
l: 5
2.3
NTU
)
(Ingr
am C
reek
@ R
iver
Rd:
103
NTU
)
(Tuo
lum
ne ri
ver @
Shi
loh:
94.
5 N
TU)
(Gra
yson
Dra
in: D
RY )
(Del
Pue
rto C
reek
@ V
iney
ard:
67.
6
(Sal
ado
Cre
ek @
Hw
y 33
: 199
0 N
TU)
(Har
ding
Dra
in d
isch
arge
@ S
anJo
aqui
n R
iver
(TID
5): 1
6.2
NTU
)
NorthSouth Flow
Figure 28: Turbidity Influences on the San Joaquin River from Lander to Airport Way/ Vernalis 12-18-02 and 12-19-02. Blue data points represent turbidity concentrations on the river. Pink lines are the Basin Plan objective with the river sites as background. Orange arrows represent west side influences, green arrows represent eastside influences and blue arrows repre-sent major tributary input.
61
12.1.6 TOTAL SUSPENDED SOLIDS Total suspended solids (TSS) samples were generally collected weekly at the SJR main stem sites (ex-cept during WY04 where no TSS samples were collected due to funding shortfalls) and monthly during WY01 at all the drainage basin sites. TSS was also collected monthly during the irrigation season (June thru August) in WY05 at the Westside Basin sites. Elevated levels in both the SJR and Basins between January and April 2001 correspond to a series of significant (greater than 1-inch) rainfall events. The TSS begins to climb again at the beginning of the irrigation season (June) and remain ele-vated, but concentrations remained lower than the spikes seen during storm events. For the SJR sites, there was no obvious difference in concentrations during wet WY 2005, except for an increased fre-quency of spikes during winter rainfall events (Figure 29). Figure 30 displays the TSS data available during the irrigation season (March thru September) during both WY01 and WY05 for the Westside Basin sites. The incomplete data sets indicate increasing con-centrations, particularly in Ingram and Hospital Creeks and Grayson Drain which show a number of spikes above 3,000 mg/L TSS. The variability in findings indicates the need for more continuous data sets during the irrigation season. Spatially, similar to turbidity, the Westside and Grassland Basins had higher concentrations of TSS when compared to the other Basins (Figure 31). Most of the larger waterways seemed to track consis-tently with the river sites downstream of their inflows. In particular, the highest overall levels of TSS in the SJR were recorded at Fremont Ford and Hills Ferry (Figure 32)—downstream of Grassland Basin and some Westside Basin inflows, but upstream of the Merced River and other Eastside Basin influ-ences. Overall concentrations in the SJR remained below 100-mg/L TSS with a median near 50-mg/L, as did all the sub-basins except the Westside. Although median Westside Basin TSS concentrations remained near 75-mg/L, 50% of the concentrations ranged between 40 mg/L and 345 mg/L. Some unique findings within selected sub-basins are noted below. Northeast Basin: Although similar in land use and size, the Cosumnes River TSS concentrations ap-peared to more directly track storm events when compared to the Mokelumne River (Figure 33). The one major difference between the basins is that flow from the Mokelumne River is regulated by Caman-che Reservoir. Reservoirs on other major rivers in the SJR Basin likely have similar buffering effects. Eastside Basin: Similar to turbidity, Turner Slough and Harding Drain had larger and more fluctuating TSS values than that of the rivers sites. Grassland Basin: The Discharge from SLD was monitored for TSS weekly through the Grassland By-pass Program. Flow in the drain is specifically regulated to minimize potential for bed sediment sus-pension and storm event influences. The TSS concentrations in the drain remained relatively constant just below 50-mg/L and did not reflect patterns noted in other Grassland waterbodies.
62
Figure 29: San Joaquin River Main Stem Total Suspended Solids WY01-WY05 Figure 30: San Joaquin River Westside Basin Total Suspended Solids Irrigation Season WY01 and WY05
0
20
40
60
80
100
120
140
160
180
200O
ct-0
0
Jan-
01
Apr
-01
Jul-0
1
Oct
-01
Jan-
02
Apr-0
2
Jul-0
2
Oct
-02
Jan-
03
Apr
-03
Jul-0
3
Oct
-03
Jan-
04
Apr-0
4
Jul-0
4
Oct
-04
Jan-
05
Apr
-05
Jul-0
5
Sample Date
TSS
(mg/
L)
SJR @Sack Dam SJR @ Lander SJR @ Fremont FordSJR @ Hills Ferry SJR @ Crows SJR @ Patterson SJR @ Maze SJR @ Airport Way/Vernalis
0
500
1000
1500
2000
2500
3000
3500
Sample Dates
TSS
(mg/
L)
Orestimba Creek @ River Rd. Grayson Drain Ingram Creek @River Rd. Hospital Creek @River Rd. Solado Creek @ Hwy 33 Del Puerto Creek @Vineyard
28000
Apr
-01
Mar
-01
Jun-
01
May
-01
July
-01
Aug
-01
Jun-
0 5
Mar
-05
Apr
-05
May
-05
Aug
-05
Jul-0
5
Dry WY 01 Irrigation Season Wet WY 05 Irrigation Season
63
Figure 31: Basin Total Suspended Solids WY01-WY05
0
50
100
150
200
250
300
350So
uthe
ast
Bas
in
Gra
ssla
ndB
asin
East
side
Bas
in
Wes
tsid
eBa
sin
Nor
thea
stB
asin
Del
ta B
asin
Dis
char
ge a
tSL
D
New
Jeru
sale
mD
rain
TSS
(mg/
L)
28000
Median
Figure 32: San Joaquin River Main Stem Total Suspended Solids WY01-WY05
0
50
100
150
200
250
300
350
SJR @Sack Dam
SJR @LanderAvenue
SJR @Fremont
Ford
SJR @Hills Ferry
SJR @Crows
Landing
SJR @Patterson
SJR @Maze
SJR @AirportWay
TSS
(mg/
L) Median
64
Figure 33: San Joaquin River Northeast Basin Total Suspended Solids WY01
0
10
20
30
40
50
60O
ct-0
0
Jan-
01
Apr
-01
Jul-0
1
Sample Date
TSS
(mg/
L)
Cosumnes River @ Twin Cities Rd. Mokelumne River @New Hope Rd. Pixley Slough @ Davis Rd Bear Creek @ Thorton Road (J8)
65
12.1.7 TOTAL ORGANIC CARBON Total organic carbon (TOC) samples were to be collected weekly at the SJR main stem sites and monthly at the drainage basin sites. Unfortunately, major gaps exist in the data due to both limited funding and sample quality control. Key gaps exist for the river sites during the winter storm periods (January thru March) of 2002, 2003 and 2004. Data for sites collected in the basin demonstrate the same gaps with the addition of no data between May 2003 and October 2004. The distinct data gaps make trend analyses difficult. In general, the major river sites appear less susceptible to random spikes in concentration and demon-strate elevated levels during winter storm events and the irrigation season. Using the Eastside Basin as an example (Figure 34) the river sites (Merced and Tuolumne Rivers) do not fluctuate as drastically as Turner Slough and Lone Tree Creek. Some of the spikes in TOC concentrations correspond to storm events, such as the spike seen in Lone Tree Creek in the winter of WY2005. Other spikes (Turner Slough in Dec 2000 and French Camp Slough in May 2002) don’t correspond to a large or first-flush storm event. The Cosumnes River was an exception to the other major river sites in that it did show a dramatic spike in June of 2001, which corresponds to a small rain event just before this ephemeral stretch of the river dried (Figure 35). At no other time did TOC concentrations rise as dras-tically at this site before the seasonal dry periods. Sites moving downstream along the SJR that receive wetland discharge (Lander Avenue, Fremont Ford and Hills Ferry) also show elevated concentrations during wetland releases in early spring. During wet WY05, TOC concentrations in the SJR tended to decrease after the final storms in April and did not show the same magnitude of increase during the irrigation season as was evident during previous dry years (Figure 36). Overall, total organic carbon values ranged from <1.0 mg/L at many of the sites to a maximum of 67 mg/L at Lone Tree Creek. Between the basins, the Grassland basin has a higher median TOC than all the other basins (Figure 37). The Northeast and Eastside river sites have the lowest concentration of TOC. The non-river sites for the rest of the basins have higher concentrations, fluctuations and high spikes of TOC. These spikes could be influenced by storm events, agricultural and wetland manage-ment practices. Some unique characteristics for selected basins are discussed below: South Delta Basin: The South Delta Basin on average had lower concentrations of TOC than the East-side Basin non-river sites. The New Jerusalem Drain had the lowest concentration of TOC throughout the sampling period. There was one large TOC spike found in the New Jerusalem Drain, Tom Payne Slough, and Old River between the end of August and October of 2001. No rainfall was measured dur-ing August 2001, with the first rains starting in September 2001. The early spike measured in TOC could have been attributed to agricultural influence with the later part being a combination of agricul-tural influence and storm flows. Westside Basin: Westside Basin TOC concentrations fluctuated like the Eastside Basin non-river sites, but without as large of spikes. In addition to spikes in June of 2001, the same distinct spike noted in the South Delta in October of 2001 also occurred in Westside water bodies—. The October 2001 spike corresponded to the first rains after a very dry summer. Grassland Basin: The Grassland Basin’s fluctuations looked very similar to the Westside Basin’s, with major spikes in the fall of 2001. Levels of TOC were typically higher early in the fall, when local flows also increase due to spill from the seasonal flooding of surrounding wetland habitat. Levels typically dropped after the initial week of wetland flood-up and prior to the first storm event. Concentrations of TOC during wet WY of 2005 for the Grassland basin were noticeably more stable than those measured during the dry WY of 2001.
66
Moving down the main stem of the SJR (Figure 38), Sack Dam had a median background concentra-tion of 3-mg/L TOC. The median TOC concentrations then peaks to 8-mg/L at the next downstream site (SJR at Lander) and progressively decreases until reaching the boundary of the Delta (Airport Way) with a median TOC back near 3-mg/L. The Lander Avenue site had the highest concentrations and most dramatic fluctuations of TOC along the SJR. Inflows from the sub-basins seem to contribute to the drop in concentration of TOC moving toward the Delta. Figure 34: San Joaquin River Eastside Basin Total Organic Carbon WY01-WY05
0
5
10
15
20
25
30
Oct
-00
Jan-
01
Apr
-01
Jul-0
1
Oct
-01
Jan-
02
Apr
-02
Jul-0
2
Oct
-02
Jan-
03
Apr
-03
Jul-0
3
Oct
-03
Jan-
04
Apr
-04
Jul-0
4
Oct
-04
Jan-
05
Apr
-05
Jul-0
5
Sample Date
TOC
(mg/
L)
Turner Slough at 4th Avenue Merced River Hatf ield Park (River Road)
Stanis laus River @Casw ell Bay -Delta Authority Target (3 mg/L)
Lone Tree Creek @ Aus tin Rd French Camp Slough @ Airport
53 675234
67
Figure 35: San Joaquin River Northeast Basin Total Organic Carbon WY01 – WY05 Figure 36: San Joaquin River Main Stem Total Organic Carbon WY01 – WY05
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Cosumnes River @ Twin Cities Rd. Mokelumne River @New Hope Rd. Pix ley Slough @ Davis Rd Bear Creek @ Thorton Road (J8)Bear Creek @Lower Sacramento Rd. Bay-Delta Authority Target (3 mg/L)
68
Figure 37: Basin Total Organic Carbon WY01-WY05 Figure 38: San Joaquin River Main Stem Total Organic Carbon WY01-WY05
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SJR @Sack Dam
SJR @LanderAvenue
SJR @Fremont
Ford
SJR @Hills Ferry
SJR @Crows
Landing
SJR @Patterson
SJR @Maze
SJR @AirportWay
TOC
(mg/
L)
Median Bay-Delta Authority (3.0 mg/L)
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Sout
heas
tB
asin
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ssla
ndB
asin
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Nort
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tB
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in
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LD New
Jeru
sale
mD
rain
TOC
(mg/
L)
32 Median Bay-Delta Authority (3.0 mg/L)
67 31
69
12.1.8 BACTERIA Total coliform and Escherichia coli (E. coli) sampling began in July 2002 and continued through WY05. The analytical method used for bacteria analyses during this study (IDEXX) has a maximum detection limit of 2419.6 MPN/100ml and a minimum detection limit of 1 MPN/100ml, numbers which were used as the upper and lower boundaries for median concentration calculations and graphs. Results ranged from 52 MPN to >2419.6 MPN for total coliform and1.0 MPN to >2419.6 MPN for E.coli. Total coliform concentrations tended to exceed the maximum detection limits at most sites except dur-ing storm events—when the concentrations decreased rapidly. Figure 39 demonstrates the trend for the Northeast Basin. In contrast, the majority of E. coli concentrations (a subset of total coliform) were reported within the detectable ranges and showed sporadic spikes in concentration, some related to storm events and oth-ers related to dry periods. Figures 40 and 41 demonstrate the variability seen in the results for the Northeast Basin and SJR sites, respectively. A number of the E. coli spikes during the winter season occurred when the sample was collected during the first flush of a major storm series—at a time when the total coliform was still above reporting limits, with subsequent samples showing much lower con-centrations. Of particular note is that during WY02, sampling frequency at the Northeast Basin sites increased to twice a month as that watershed cycled into the rotational basin sampling schedule. The increased sampling related to an increase in the number of spikes reported at those sites. In addition, a greater number of elevated E. coli concentrations were detected in the SJR between January and June during wet WY05 when compared to previous water years. Spatially, total coliform appeared uniformly high throughout the SJR Basin and was normally above de-tection limits with lower concentrations mostly seen during high flow events. For E. coli, the Grassland and South Delta Basin had lower concentrations compared to the rest of the basins (Figure 42). The Westside Basin had a considerable increased number of E. coli spikes when compared to the rest of the basins as well as higher overall spikes during low flow time periods. Both the Westside and South-east Basins reported 50% of samples collected falling between 200 MPN/100ml and 1200 MPN/100ml—much higher than the remaining basins. The river itself had the highest median E. coli concentration (124 MPN/100ml) at the Hills Ferry site, just prior to inflow from the Eastside rivers. The Hills Ferry site also had the highest overall concentra-tions in the SJR, but the majority of samples remained well below 235 MPN/100ml (the US EPA guide-line for full contact recreation) (Figure 43). Some unique characteristics noted for selected sub-basins follow. Northeast Basin: The Northeast Basin’s total coliform stayed mostly at the maximum detection limit until higher flow events during which the levels dropped (Figure 39). Lower concentrations during high flow events were more pronounced for the river sites than Bear Creek and Pixley Slough. E. coli was mostly found to be around the lower level of detection and would spike upwards during lower flow events (Fig-ure 40). The river sites did not seem to spike as frequently as Bear Creek and Pixley Slough. E. coli in Bear Creek and Pixley Slough also spiked periodically during higher flow events. South Delta Basin: South Delta Basin bacteria concentrations had a similar trend to the Northeast Ba-sin, but overall E. coli had much lower concentrations. E. coli for the New Jerusalem Drain never went above 27 MPN/100ml, which is likely related to the fact that it is a collection system for shallow ground water (subsurface tile drainage). The two samples collect in Mountain House Creek prior to drainage diversion after urban conversion, were both very high with the lowest sample at 1046.0 MPN/100ml.
70
Westside Basin: The Westside Basin showed the same trend as the Northeast Basin river sites. E. coli found in the Westside Basin showed the greatest number of spikes throughout the whole year. Ores-timba Creek had the lowest number of samples above the detection limit for E. coli, but the second highest geometric mean. Grassland Basin: The Grassland Basin had lower E. coli levels, similar to the Delta Basin, with only two samples found above the detection limit. The discharge from SLD had the lowest levels of E. coli in the basin. The SLD also consists of subsurface tile drainage, similar to the New Jerusalem Drain, but for a larger area. Figure 39: San Joaquin River Northeast Basin Total Coliform WY02-WY05
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Sample Date
Tota
l Col
iform
(MPN
/100
ml)
Cosumnes River @ Twin Cities Rd. Mokelumne River @New Hope Rd. Pixley Slough @ Davis Rd Bear Creek @ Thorton Road (J8)Bear Creek @Lower Sacramento Rd.
71
Figure 40: San Joaquin River Northeast Basin E. coli WY02-WY05
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E. c
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(MP
N/1
00m
l)
Cosumnes River @ Twin Cities Rd. Mokelumne River @New Hope Rd. Pixley Slough @ Davis RdBear Creek @ Thorton Road (J8)Bear Creek @Lower Sacramento Rd. USEPA Guideline: Designated Beach Area (235 MPN/100ml)
Figure 41: San Joaquin River Main Stem E. coli WY01 – WY05
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E. c
oli
(MPN
/100
ml)
SJR @Sack Dam SJR @ Lander SJR @ Fremont FordSJR @ Hills Ferry SJR @ Crows SJR @ Patterson SJR @ Maze SJR @ Airport Way/Vernalis USEPA Guideline: Designated Beach Area (235 MPN/100ml)
72
Figure 42: Basin E. coli WY02-WY05
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outh
east
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in
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e at
SLD New
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E. c
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(MP
N)
Median USEPA Guidline (235 MPN/100ml)
Figure 43: San Joaquin River Main Stem E. coli WY02-WY05
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SJR @Sack Dam
SJR @LanderAvenue
SJR @Fremont
Ford
SJR @Hills Ferry
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Landing
SJR @Patterson
SJR @Maze
SJR @AirportWay
E. c
oli
(MP
N)
Median USEPA Guidline (235MPN/100ml)
73
12.1.9 NUTRIENTS Nutrient samples were collected throughout the basin on a monthly basis through WY02 (excluding ni-trate-N and ammonia-N). At the end of fiscal year 02/03, an initial review of the data collected and a review of collaboration efforts with the Total Maximum Daily Load (TMDL) programs (specifically the TMDL for dissolved oxygen) were completed. With a redirection of the DO TMDL program to conduct continuous measurements at select sites and add additional monitoring for chlorophyll a, nutrient col-lection at most of the drainage basin sites was discontinued to avoid duplication of effort. The excep-tions were Mud Slough upstream of SLD, Discharge at SLD and Mud Slough (downstream) @ SLD which are monitored in conjunction with the Grassland Bypass Program, and continued collection at the SJR main stem sites of SJR @ Fremont Ford and SJR @ Crows Landing until December 2004. Much of the data for WY02 and the first half of WY03 was removed from the data set due to failed QA/QC. Most of the nutrients at sites within the SJR Basin had relatively low levels, with the exception of nitrate; however, the limited data set makes trend analyses difficult. Figure 44 depicts available SJR nitrate information for this program. From the information collected in WY01, nitrate increases during both the storm season (January thru March) and then again during the irrigation season. The available data mirrors portions of those trends in 2002 and 2003. Nitrate concentrations reported for the Northeast Basin were all below 6-mg/L, with little discernible trends during the single water year of data (WY01)(Figure 45). The Westside Basin reported higher overall concentrations and a distinct spike in Orestimba Creek during the storm season and spikes in Del Puerto during April (typically a pre-irrigation period) as well as June thru September (Figure 46). Spatially, nitrate is high at several sites throughout the basin especially the Discharge at SLD and New Jerusalem Drain—both of which carry subsurface agricultural drainage (shallow groundwater) and had the majority of concentrations reported above 45-mg/L. The Harding Drain within the Eastside Basin was also somewhat elevated with values ranging from 9.9 mg/L to 44 mg/L. Overall, the Westside Ba-sin had the highest median nitrate concentration (12-mg/L) when compared to the rest of the SJR Basin (Figure 47). Information from the specific sub-basins is listed below. Northeast Basin: The Northeast Basin had very low levels of nutrients and most of the collected sample results were non-detect. The Mokelumne River had only 5 samples that were just slightly above detec-tion levels. The Cosumnes River had slightly higher levels of nitrate, phosphorus and potassium than the Mokelumne River. Pixley Slough nutrient levels, unlike Bear Creek, have lower levels of nutrients than the Cosumnes River. Bear Creek had the highest concentrations of nutrients for the Northeast Basin. Higher concentrations of nutrients mostly occurred during the winter months. Eastside Basin: The Eastside Basin river sites had low concentrations similar to the Northeast Basin river sites. French Camp Slough and Lone Tree Creek had higher fluctuating levels than Bear Creek in the Northeast Basin. Harding Drain had higher fluctuating levels for all nutrient samples collected in the basin. Turner Slough had high levels during January 2001 through April 2001 for TKN, phosphorus, orthophosphate-P and potassium. For the rest of the sampling period the concentrations at Turner Slough were comparable to the river sites within the basin. Southeast Basin: The Southeast Basin had fluctuating levels of nutrients similar to Bear Creek in the Northeast Basin. South Delta Basin: All sites within the South Delta Basin reported low levels of nutrients except for ni-trate levels in the New Jerusalem Drain. The nitrate levels in the New Jerusalem Drain were six times higher than the other South Delta Basin sites as well as the river sites of the Northeast Basin.
74
Westside Basin: Overall the Westside Basin reported higher nitrate levels than the other Basins (Figure 47). Salado and Orestimba Creeks showed higher concentrations during the winter months and Del Puerto Creek typically showed a spike during the irrigation season. Grassland Basin: The discharge from SLD had the highest concentration of nitrate, but had lower con-centrations of the other nutrients compared to the rest of the Grassland sites. Nitrate concentrations in the SLD were highly elevated in the winter and decreased somewhat but remained elevated above 45-mg/L through the irrigation season. Mud Slough (north) downstream of the SLD discharge tracked the drain’s concentrations and had much higher concentrations of nitrates than Mud Slough upstream. The Main Stem SJR showed increasing nitrate concentrations between Lander and Patterson—the stretch of river receiving inflows from the Grassland (including SLD) and Westside Basins and the Merced River (Figure 48). Nitrates decrease from SJR at Patterson to Airport Way with inflows from the Tuolumne and Stanislaus Rivers. Most other nutrient concentrations decreased in the main stem of the river moving down the system or stayed the same resulting in very low concentrations. The New Jerusalem Drain enters the SJR downstream of Airport Way. Figure 44: San Joaquin River Main Stem Nitrate WY01 – WY04
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75
Figure 45: San Joaquin River Northeast Basin Nitrate WY01 Figure 46: San Joaquin River Westside Basin Nitrate WY01
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ate
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Cosumnes River @ Twin Cities Rd. Mokelumne River @New Hope Rd. Pixley Slough @ Davis Rd Bear Creek @ Thorton Road (J8)California Primary MCL (45mg/L)
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Orestimba Creek @ River Rd. Solado Creek @ Hwy 33 Del Puerto Creek @Vineyard Grayson Drain Ingram Creek @River Rd. Hospital Creek @River Rd. California Primary MCL (45mg/L)
76
Figure 47: Basin Nitrate WY01-WY02 Figure 48: San Joaquin River Main Stem Nitrate WY02-WY04
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Ford
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Landing
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SJR @Maze
SJR @AirportWay
Nitr
ate
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L)
Median California Primary MCL (45 mg/L)
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ate
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Median California Primary MCL(45mg/L)
110
77
12.1.10 BIOCHEMICAL OXYGEN DEMAND As with the nutrient samples, Biochemical Oxygen Demand (BOD) samples were collected throughout the basin on a monthly basis through WY02. At the end of fiscal year 02/03, an initial review of the data collected was completed, as well as a review of collaboration efforts with the DO Total Maximum Daily Load (TMDL) effort. A change in the monitoring strategy for the DO TMDL eliminated the need for continued BOD analyses by this effort. Biochemical Oxygen Demand (BOD) is a procedure that measures how fast biological organisms use oxygen in a body of water. Bodies of water with higher concentrations of organic matter have aerobic bacteria that decompose organic matter using the available oxygen within the water body. High nitrates and phosphates also contribute to higher BOD because they contribute to increased plant and algae growth which increase plant loss contributing to higher organic waste. Increased temperatures also contribute to higher algae growth. For this discussion we will be looking only at BOD5 (biochemical oxygen demand 5-day test). Higher fluctuations in BOD5 occurred at most sites during the winter months and corresponded to spikes in flow and TOC. Concentrations of BOD5 also increased and remained elevated during sum-mer months, peaking during September, which again tracked TOC concentrations. Spatially, all of the Eastside river sites had low concentrations of BOD5 which reflect their low concen-trations of TSS and TOC, when compared to the rest of the SJR Basin sites. The rest of the basin sites, except New Jerusalem Drain, had higher levels of TOC and TSS, and BOD5. Figure 49 shows the Northeast basin as a whole had the lowest BOD5 compared to the rest of the Basins. Some distinct findings within each sub-basin are noted below. Northeast Basin: The Northeast Basin Mokelumne River had BOD5 concentrations at or below 1 mg/L. The Cosumnes River had levels similar to the Mokelumne River most of the time except during June 2001, which was just before the river dried and the BOD5 level increased to about 4 mg/L. This in-crease corresponds to the light rain event that occurred just before the river went dry and a similar spike in the TOC concentration. Potential inflow of nutrients and organic matter during the rain event, coupled with the already decreased flows and increased temperatures encourages algae growth, and may have contributed to higher BOD5 levels. Pixley Slough and Bear Creek had higher fluctuations of BOD during the winter months of January and February. Eastside Basin: The Eastside Basin river sites had BOD5 levels mostly under 1 mg/L. There was one very large spike within all the river sites in December 2002, which corresponds to a storm event. The rest of the Eastside Basin sites fluctuate between 2 mg/L to 8 mg/L. The Harding Drain had the highest quartiles compared to the other Eastside Basin sites that had agricultural influences. Southeast and Westside Basins: The BOD5 concentrations in both basins fluctuated like the non-river sites of the Eastside Basin with multiple spikes in the summer and winter. South Delta Basin: The BOD5 concentrations at most of the South Delta Basin sites fluctuated like the non-river sites of the Eastside Basin except for the New Jerusalem Drain. Although the New Jerusalem Drain had high nitrate concentrations, it also had very low TSS and TOC concentrations, and BOD5 levels hovering just above the detection limit of 0.1 mg/L. Grassland Basin: The Grassland Basin fluctuated like the non-river sites of the Eastside Basin as well but fluctuated at slightly lower levels. The Main Stem SJR sites whisker plot (Figure 50) looks very similar to the TOC whisker plot (Figure 38). BOD5 has a very similar trend to TOC with Sack Dam having concentrations below 1 mg/L. The
78
SJR at Lander had the highest fluctuations of BOD5 when compared to all the other sampling locations along the SJR. The BOD5 concentrations tend to decrease from SJR at Lander to the SJR at Airport Way where BOD5 is mostly under 2 mg/L. Figure 49: Basin BOD-5 Day WY02-WY03 Figure 50: San Joaquin River Main Stem BOD-5 Day WY02-WY03
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SJR @Sack Dam
SJR @LanderAvenue
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Ford
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SJR @Crows
Landing
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SJR @Maze
SJR @AirportWay
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D-5
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79
12.1.11 MINERAL ANALYSIS Mineral samples were collected throughout the basin on a monthly basis during WY01 and sporadically during WY02 and WY03. At the end of fiscal year 02/03, an initial review of the data collected was done, as well as a review of collaboration efforts with other in-house programs, which resulted in a re-prioritization of monitoring efforts and the elimination of minerals from monitoring efforts. Within the limited dataset, some general patterns are discernible. In general, the highest mineral con-centrations occur along the western side of the SJR Basin, with elevated sodium concentrations and sulfate the dominant anion draining from the Grassland and Westside Basins and chloride the dominant anion from the Delta Basin. The eastern side of the SJR Basin reported much lower overall mineral concentrations with chloride the dominant anion. Carbonate was typically not detected or detected at very low levels, usually within the Westside Basin. Along the western side of the valley, the SLD influences overall mineral discharges from the Grassland Basin, with elevated concentrations year-round. Concentrations of chloride and sulfate from the drain tend to dominate concentrations in Mud Slough (north) as winter dilution flow decreases. In contrast, during the dry season, sodium levels are elevated in Mud Slough (north) both upstream and down-stream of the SLD discharge. The upstream concentrations are likely due to shallow groundwater dis-charge into the channel. For the remainder of the western side of the valley, mineral concentrations tended to increase during the winter then decrease but become somewhat elevated during the irrigation season. Sulfate and chloride concentrations all remained below the secondary drinking water MCL (250 mg/L), but sodium tended to remain above the irrigation supply guideline of 69-mg/L. The New Jerusalem Drain was the exception for sodium on the western side of the valley with concentrations remaining near 300 mg/L year-round. Along the eastern side of the valley (the Southeast, Eastside, and Northeast Basins), sodium, chloride and sulfate concentrations all remained well below guidelines. Sodium did tend to show low level spik-ing throughout the year. Some sites did show unique characteristics. Within the Westside Basin, Ingram Creek displayed pro-nounced seasonal fluctuation, similar to Tom Payne Slough of the Delta Basin, with marked increases in all minerals during storm events. Mud Slough (north) upstream of the SLD, was lower than the SLD in all mineral concentrations except total alkalinity and bicarbonate. While seasonal fluctuations of mineral concentrations are not distinctly seen within the SJR, the Main Stem sites do reflect the inflows from the various sub-basins. Mud Slough (north)’s influence on Hills Ferry is distinctly seen with all the mineral concentrations at this site consistently higher compared to the rest of the river. Sack Dam has the lowest concentrations within the river, but with the influences from the Southeast Basin, Grassland Basin and Turner Slough, mineral concentrations peak at Hills Ferry. Once the Eastside Basin rivers enter the SJR, mineral concentrations substantially decrease moving downstream to Airport Way, even with elevated concentrations coming in from the Westside Basin. 12.1.12 TRACE ELEMENTS Trace element samples were collected throughout the basin on a monthly basis through WY02. Hard-ness was analyzed simultaneously for each trace element sample in order to allow evaluation against aquatic life criteria. At the end of fiscal year 02/03, an initial review of the data collected and a review of collaboration efforts with other in-house programs were completed. Re-prioritization of monitoring efforts resulted in a removal of trace element collection. Note that during the collection period reporting limits changed for some constituents.
80
Many of the results for this study were below the analytical reporting level. Some trace elements did appear to show some trends, depending on the location within the SJR valley. In general, the North-east and Eastside Basin river sites have lower concentrations than the other basins within the SJR val-ley. One issue to note with this finding is that the hardness levels in the northeast basin are also lower when compared to the other sub-basins. Hardness concentration is particularly important for aquatic life because hardness tends to buffer toxic impacts, allowing tolerance of higher concentrations of many trace elements. Some distinct findings within each sub-basin are listed below. Northeast Basin: Most of the trace elements sampled in the Northeast Basin had results below the re-porting limit. Copper and zinc were the only two metals that were consistently above minimum report-ing levels for all the sites within the Northeast Basin. Chromium had multiple samples above detection for most sites except the Mokelumne River which only had two samples for total chromium above de-tection levels. Eastside Basin: The Eastside Basin river sites were similar to the Mokelumne River with non-detect values for all metal constituents, except copper and zinc. The Eastside Basin river sites had more non-detect values for zinc than the Mokelumne River. The non-river sites were comparable to the river sites data, except for having higher concentrations of copper, zinc and total chromium. Nickel was also reported at concentrations above minimum reporting levels for the non-river sites during the winter higher flow periods. Southeast Basin: The Southeast Basin sites were similar to the non-river sites of the Eastside Basin. One exception was Deep Slough which had high levels of arsenic and total nickel reported year-round. South Delta Basin: The New Jerusalem Drain had non-detect values for most of the trace elements except for chromium where high concentrations were detected. Tom Payne Slough trace element con-centrations were similar to that of the Deep Slough, having higher levels of arsenic, but with minimal total nickel. Old River and Mountain House Creek both had very low levels of arsenic. Mountain House Creek, similar to Deep Slough, had total nickel concentrations found throughout the sampling period. Westside Basin: The Westside Basin unlike the Northeast Basin had more detected concentrations of total lead and had higher concentrations and major spikes of copper, zinc, and chromium. Hospital Creek had the largest spikes of copper, zinc, nickel and chromium. These very large spikes seemed to occur mostly during the irrigation season. Del Puerto Creek was the only Westside basin site that did not have any samples above the minimum detection level for lead. Grassland Basin: Salt Slough had very similar concentrations of trace elements compared to Deep Slough with just slightly lower levels of arsenic. Mud Slough Upstream was similar to Salt Slough hav-ing detectable arsenic but at slightly lower concentrations. The dominant trace element concentrations at the Discharge from SLD site were chromium and copper. The majority of the concentrations of trace elements that were seen in the Main Stem SJR were the dominant trace elements identified in the sub-basins including; arsenic, chromium, copper, nickel and zinc. With most of these constituents, trace element concentrations went up from Sack Dam to Hills Ferry due to the Grassland influences and from Hills Ferry downstream to Airport Way concentrations decreased due to the Eastside river influences. This trend is similar to the trend seen with minerals.
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12.1.13 TOXICITY Funding constraints limited the overall number of full (three species) water column toxicity tests. The three species tested were fathead minnow (Pimephelas promelas, sensitive to elevated nutrients, es-pecially ammonia), Ceriodaphnia dubia (sensitive to organic chemicals such as orthophosphorus-pesticides), and algae (such as Selanastrum capricornutum, sensitive to trace elements). During Water Years 01, 02 and partially in 03 acute toxicity tests were run on fathead minnow and Ceriodaphnia dubia, and while it was encouraging to see limited if any acute effects, there was concern that dilution flows might be masking some effect. Analyzing samples for chronic toxicity was more costly, but con-sidered a more conservative option. With limited funding during WY 04, toxicity samples for chronic fathead minnow and chronic Cerio-daphnia dubia were collected in the Main Stem during the irrigation season only. During WY 05, toxic-ity samples for acute and chronic fathead minnows, acute and chronic Ceriodaphnia dubia, and acute algae were collected once a month at the various sites shown in Table 1. Funding was not available to run toxicity identification evaluations (TIE) on samples identified as a toxic event and therefore results can only be evaluated against data collected during each sampling event. The sporadic sampling did not discern specific trends. Results in Table 6 are discussed by sub-basin below. Northeast Basin: Northeast Basin had recorded toxicity in the Cosumnes River and Bear Creek for the acute fathead minnow test (Table 6). One hundred percent of the four samples collected at Cosumnes River for the acute algae test had a reduction of cell growth. The Mokelumne River only displayed tox-icity for the chronic fathead minnow test. The rest of the samples during the sampling period displayed no toxic event. Eastside Basin: Within the Eastside Basin acute fathead minnow toxic events were only reported for French Camp Slough. Lone Tree Creek had one toxic event for acute Ceriodaphnia dubia. Acute al-gae and chronic fathead minnow test were only conducted at the river sites, except for four acute algae samples collected at Harding drain, and each site had toxic events (for algae reduction and increase in cell growth were found). Over 50 percent of the samples collected at Tuolumne River reported toxic events for the chronic fathead minnow test. Southeast Basin: Bear Creek at Bert Crane Road had three toxic events for the acute fathead minnow test. The remainder of the samples displayed no toxic events. South Delta Basin: The New Jerusalem Drain had one toxic event for the acute fathead minnow test and the acute Ceriodaphnia dubia test. Both of the two samples collected for the acute algae toxicity had a growth statistical difference which could be due to the very high nitrate concentrations within the New Jerusalem Drain. Tom Payne Slough had one toxic event (reduction of cell growth) out of one sample collected for the acute algae test. Mountain House Creek had one toxic event (increase in cell growth) out of two samples collected for the acute algae test. Westside Basin: Toxic events were seen at Orestimba Creek, Grayson Drain and Hospital Creek for the acute Ceriodaphnia dubia test. No other toxic events were observed. Note that only acute fathead minnow and Ceriodaphnia dubia samples were collected and analyzed within the Westside Basin. Grassland Basin: Salt Slough had a total of three acute algae samples collected with two having a re-duction in growth and one being an increase in algae growth. None of the seventeen samples col-lected at Salt Slough for acute fathead minnow or acute Ceriodaphnia dubia had toxic events.
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Spatially, not one basin stands out from the rest. As a whole, a majority of the acute algae samples within the SJR Basin had a toxic reduction or growth in algae. Only twelve samples out of 59 collected throughout the basin did not have a statistical difference from the control whether being a reduction or increase in algae growth. The Main Stem SJR sites reflected the same finding of the Basin sites with only eight out of the 31 samples of acute algae not having a statistical reduction or increase in growth when compared to the controls. At least one toxic event was found in each of the Main Stem sites sampled for the chronic fathead minnow and chronic Ceriodaphnia dubia tests.
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12.2 Evaluation of Beneficial Uses To evaluate potential impact, indicators were chosen for four broad beneficial uses as shown in Table 3:
1. Drinking water (Specific Conductivity, Total Organic Carbon, Trace Metals, Nutrients); 2. Aquatic life (pH, Temperature, Dissolved Oxygen, Turbidity, Trace Metals, Minerals and Water
Column Toxicity); 3. Irrigation water supply (Specific Conductivity, Minerals); and 4. Recreation (bacteria).
Exceedances/ elevated levels tables were created with the data collected using the applicable water quality goals and objectives as described in section 9.2. Appendix P provides the exceedance/ ele-vated levels tables which compare the total number of samples collected with the total number showing elevated levels for temperature, pH, SC, TOC, DO, turbidity (within the legal boundaries of the Delta), bacteria, nitrate, nitrate-N, ammonia-N, chloride, sulfate, TDS, sodium, total and dissolved arsenic, total and dissolved cadmium, total chromium, total and dissolved copper, total and dissolved lead, total and dissolved nickel, total and dissolved zinc and total mercury. Most of the criteria used to set trace ele-ment limits take into account the hardness of the water at the time of sample collection since increasing hardness will tend to buffer the effect of particular trace elements. The hardness calculations were taken into account in both the summary tables presented in Appendix P and the discussion here. Con-stituents in Appendix P are evaluated against multiple objectives and goals, when applicable, for com-parison of beneficial use impacts. Turbidity outside the Delta is discussed separately below. The Basin Plan Objective for turbidity within the San Joaquin River Basin was designed for point source discharges. When evaluating turbidity basin wide, with weeks between turbidity results and miles be-tween sites, the following evaluations should be looked at objectively and viewed as an overall com-parison of the basin. With this in mind, see Table 7 for the selected upstream sites that were chosen to describe “natural background” for this Basin Plan Objective. Note for Cosumnes River at Twin Cities Road, Bear Creek at Lower Sacramento Road, French Camp Slough at Airport, and Lone Tree Creek at Austin Rd that the sites were compared to the Delta objective because they discharge directly into the Delta. Also, upstream sites are really not applicable to compare with the Main Stem river sites and were not evaluated using the above approach. Turbidity effects along the Main Stem are discussed in section 12.1 of the discussion section. Monthly geometric means were used because of collection time differences. See Table 7 for the number of times the monthly geometric mean of a site is greater than the monthly geometric mean of the selected upstream site using the calculations of the Basin plan objective. The following discussion highlights information from Appendix P and Table 7 to assess beneficial use status in the SJR Basin.
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Table 7: Selected Upstream Site Locations and Number of Turbidity Samples Greater than Selected Upstream site
Location Site Selected Upstream location
Selected Upstream
Site
Turbidity's Monthly
GeoMean Count*
Number of samples greater
than Selected Upstream site
using the Basin Plan Turbidity
ObjectiveMain StemSJR @Sack Dam 541MAD007 NA NA NA NASJR @ Lander 541MER522 NA NA NA NASJR @ Fremont Ford 541MER538 NA NA NA NASJR @ Hills Ferry 541STC512 NA NA NA NA
SJR @ Crows 535STC504 NA NA NA NASJR @ Patterson 541STC507 NA NA NA NASJR @ Maze 541STC510 NA NA NA NASJR @ Airport Way/Vernalis 541SJC501 NA NA NA NA
Total Main Stem Count 0 0Southeast Bas in Deep Slough Green House Rd 535MER577 SJR @Sack Dam 541MAD007 17 8Santa Rita Slough at Highway 152 541MER015 SJR @Sack Dam 541MAD007 NA NA Bear Creek Bert Crane Rd 535MER007 SJR @Sack Dam 541MAD007 13 10
Total Southeast Basin Count 30 18Grassland BasinSalt Slough @Lander/Hwy 165 541MER531 SJR @ Lander 541MER522 23 21Mud Slough (n) (upstream) @ San Luis Drain 541MER536 SJR @ Fremont Ford 541MER538 21 3Discharge from SLD 541MER535 Mud Slough (n) (upstream) @ San Luis Drain 541MER536 21 5
Mud Slough (n) (downstream) @ San Luis Drain 541MER542 SJR @ Fremont Ford 541MER538 22 2Total Grassland Basin Count 87 31
Eastside BasinTurner Slough at 4th Avenue 535MER576 SJR @ Lander 541MER522 17 17Merced River Hatf ield Park (River Road) 541MER546 SJR @ Hills Ferry 541STC512 10 0Harding Drain discharge @ San Joaquin River (TID5535STC501 SJR @ Crows 535STC504 13 1 Tuolumne River @ Shiloh 535STC513 SJR @ Patterson 541STC507 16 1 Stanislaus River @Caswell 535STC514 SJR @ Maze 541STC510 9 1
Total Eastside Basin Count 65 20West Side BasinOres timba Creek @ River Rd. 541STC019 SJR @ Hills Ferry 541STC512 17 14Solado Creek @ Hwy 33 541STC515 SJR @ Patterson 541STC507 11 8Del Puerto Creek @Vineyard 541STC516 SJR @ Patterson 541STC507 16 11Grayson Drain 541STC030 SJR @ Patterson 541STC507 13 11Ingram Creek @River Rd. 541STC040 SJR @ Patterson 541STC507 14 7Hospital Creek @River Rd. 541STC042 SJR @ Patterson 541STC507 13 9
Total West Side Basin Count 84 60Northeast BasinCosumnes River @ Twin Cities Rd. 531SAC001 Discharges into Delta waters 150NTU 11 0Mokelumne River @New Hope Rd. 544SAC002 Delta Waters NA NA
Pixley Slough @ Davis Rd 531SJC507 Bear Creek @Lower Sacramento Rd. 531SJC515 16 6Bear Creek @ Thorton Road (J8) 544SJC508 Delta Waters NA NABear Creek @Lower Sacramento Rd. 531SJC515 Discharges into Delta waters 150NTU 17 0French Camp Slough @ Airport 531SJC504 Discharges into Delta waters 150NTU 8 0Lone Tree Creek @ Austin Rd 531SJC503 Discharges into Delta waters 150NTU 6 0
Total Northeast Basin Count 58 6Delta Basin New Jerusalem Drain 544SJC001 Delta Waters NA NA Tom Payne Slough @Paradise Rd. 544SJC505 Delta Waters NA NAOld River @Tracy Blvd 544SJC506 Delta Waters NA NAMountain House Creek 544SJC509 Delta Waters NA NA
Total Delta Basin Count 0 0*Number of times the monthly geomean was able to be calculated
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Drinking Water (Specific Conductivity, Total Organic Carbon, Trace Metals, E. coli, Nutrients) Indicators used to evaluate a potential impact to drinking water (sources of municipal and domestic supply) included salt measured as specific conductivity (umhos/cm), total organic carbon (TOC), se-lected trace elements (total arsenic, cadmium, copper, mercury, nickel, lead and zinc), nitrate and E. coli. For all of the indicators except E. coli, there are specific numeric objectives or goals for drinking water that results can be evaluated against (Appendix Q1 and Q2). There are no specific numeric cri-teria for E. coli related to consumption but the presence of E. coli would indicate that the water would need to be treated prior to consumption. For specific conductivity, the California Secondary MCL of 2200 umhos/cm for short term exposure was utilized. Elevated levels are found in the South Delta Basin non-river sites and in Salado Creek within the Westside Basin. The Main Stem sites that displayed elevated levels above this goal were SJR at Lander, SJR at Fremont Ford and SJR at Hills Ferry. These Main Stem sites are located upstream of the first eastside inflow (Merced River) and are therefore dominated by groundwater accretion and in-flows from the Southeast and Grassland Sub-basins. Once the Eastside rivers flow into the SJR, the specific conductivity within the SJR declines until Vernalis. The TOC goal of 3.0 mg/L is based on the Bay Delta Authority’s guideline for water quality in the Sac-ramento-San Joaquin Delta (Cal Fed Bay-Delta Program, 2000). This indicator was chosen to help identify potential sources of TOC to the Delta since all water bodies monitored flow into the San Joa-quin River and ultimately into the Delta. Overall TOC concentrations were reported above 3.0-mg/L throughout the SJR Basin (Figure 51). The Northeast Basin had the lowest concentrations of TOC compared to the rest of the SJR Basins, but still exceeded 3.0-mg/L about half of the time. Storm events and agricultural runoff during the irrigation season correlated well with many of the spikes in concentration, but the goal was surpassed in the majority of the sites at other times of the year as well and at sites that were not identified as receiving agricultural return flows. Roughly 10-percent of the 526-nitrate samples collected exceeded the nitrate California Primary MCL (45 mg/L). All of the 10 samples collected at New Jerusalem Drain (representing shallow ground water in the Westside Basin) were above this objective. The Grasslands Basin also had elevated levels of nitrate at all sites except Mud Slough upstream of SLD. Two sites (Discharge at SLD and Mud Slough (downstream) @ SLD—both within the Grassland Basin) had samples that exceeded the nitrate-N Cali-fornia Primary MCL (10 mg/L). For total arsenic two goals were evaluated for drinking water: 1) the Basin Plan Objective for the Cali-fornia Primary MCL of 50 µg/L and 2) the USEPA Primary MCL of 10 µg/L. No samples exceeded the Basin Plan objective during the 5 year sampling period. Thirteen samples exceeded the USEPA pri-mary MCL. The three sites that had elevated levels above this goal were SJR at Lander, Deep Slough and the Grayson Drain. The total cadmium Basin Plan Objective for the California Primary MCL of 5 µg/L, total copper Basin Plan Objective for the California Primary MCL of 1000 µg/L, and the total zinc Basin Plan Objective for the California Primary MCL of 5000 µg/L were never exceeded during the 5 year study. The total chromium Basin Plan Objective for the California Primary MCL of 50 µg/L, total lead Basin Plan Objective for the California Primary MCL of 15 µg/L, and the total nickel Basin Plan Objective for
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California Primary MCL of 100 µg/L were all exceeded by three sites in the Westside Basin. Hospital Creek, Ingram Creek and Grayson Drain exceeded these goals during the irrigation season. The total mercury Basin Plan Objective for the California Primary MCL of 2 µg/L was never exceeded during the 5 year sampling period. Total mercury was found elevated above the California Toxics Rule (USEPA) for sources of drinking water, 0.05 µg/L, once in Hospital Creek (0.2 µg/L). Table 8 is a quick summary to show whether the river or any of the basins have potential beneficial use impacts based on the indicators evaluated.
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Figure 51: Percentage of Total Organic Carbon samples greater than the Bay-Delta Authority Target (3.0 mg/L)
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Aquatic Life (pH, Temperature, Dissolved Oxygen, Turbidity, Trace Metals, Minerals and Water Column Toxicity) The Basin Plan objective for pH for freshwater with COLD or WARM beneficial uses is a range between 6.5 to 8.5 units. Each of the Basins exceeded this objective multiple times, but no site exceeded this objective more than 18 percent of the time. The Main Stem and the Grasslands exceeded this objec-tive during the summer irrigation season. The other basins exceeded this objective randomly with dras-tic fluctuations. The Bay-Delta Authority target for a temperature of 20ºC from April 1 – June 30 and from September 1 – November 30 applies to the San Joaquin River at Vernalis. Samples collected at Vernalis had tem-peratures recorded above this target 41% of the time during the 5-year study. Every site within the SJR Basin reported temperatures above this target at least once during the sampling period with the highest percentages seen within the Southeast and Grassland Basins. The dissolved oxygen Basin Plan objective of 7.0-mg/L (described in Appendix Q1 as outside the Delta for cold/spawning beneficial use) was used for all non-Delta sites. Results were found below the above objective at least once for every site except for the Cosumnes and Stanislaus Rivers. The basin with the highest percentage of results below the objective was the Northeast Basin in the non-river sites and the lowest percentages were found in the Westside Basin. Sites within the legal boundaries of the Delta were evaluated against the Basin Plan objective of 5.0 mg/L for dissolved oxygen. All Delta sites were below this objective at least once except New Jerusalem Drain. Tom Payne Slough had the high-est percentage of results below this objective with 19 out of 47 samples. Sites within the legal boundaries of the Delta were evaluated against the Basin Plan objective of 150 NTU for turbidity. This objective was only exceeded once at Mountain House Creek during a non-storm event. New Jerusalem Drain and Mountain House Creek both exceeded the objective during the De-cember 2002 storm event, however this objective doesn’t apply for storm events. For non-Delta sites the Basin Plan objective was designed for specific discharges. As described in the turbidity results sec-tion of this report, Table 7 attempts to use the Basin Plan objective to have an overall assessment of the SJR Basin turbidity concentrations. The Westside Basin had greater turbidity 71 percent of the time compared to the selected upstream sites. Higher turbidity levels were typically associated with major storm events and irrigation seasons. The USEPA California Toxics Rule for total and dissolved cadmium, total and dissolved nickel, dis-solved arsenic, dissolved lead, and dissolved zinc was never surpassed during the sampling period. No samples were elevated above the USEPA National Ambient Water Quality Criteria for 1 hour aver-age of 1.4 µg/L for total mercury during the sampling period. The USEPA California Toxics Rule for total and dissolved copper was exceeded in multiple samples, primarily in the non-river sites of the Northeast and Eastside Basin, particularly in French Camp Slough, Lone Tree Creek, and Pixley Slough. In addition the Westside and Southeast Basin had a few elevated samples for total copper as well. The USEPA California Toxics Rule for total lead was exceeded once in the Mokelumne River. Pixley Slough reported one sample above the USEPA California Toxics Rule for total zinc. Even though the concentrations of the metals were lower in the Northeast and Eastside Basins when compared to the Westside Basin, the hardness levels were also comparatively low which resulted in lower concentration thresholds that could impact aquatic life.
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No sample was reported above the chloride USEPA National Ambient Water Quality Criteria for 1-hour average of 860 mg/L during the study. Various levels of water column toxicity were reported on multiple occasions (Table 6). A higher per-centage of chronic toxicity was reported as compared to acute toxicity. Acute algae toxicity samples were collected less frequently than other toxicity samples, but had the highest percentage (50 percent) of toxic findings (samples having a reduction or increase in growth at all sites except for Fremont Ford). In summary there were multiple concerns throughout the basin for aquatic life. Drastic fluctuations of pH occur at multiple locations, but for the majority of the time most sites are within range of the Basin Plan objective. Elevated temperatures during the spring and fall may impact fish migration. Low DO levels were seen in multiple sites, most consistently in non-river sites, but no overt impact (e.g. fish kills) was ever noted. Trace element results exceeding hardness adjusted criteria were mostly reported in the Northeast and Eastside basins—as were the lowest hardness concentrations. Total copper was the primary trace element of concern having higher percentages of elevated levels in French Camp Slough, Lone Tree Creek, and Pixley Slough. Turbidity concentrations can become highly elevated during storm events and the irrigation season but become difficult to interpret with the fluctuation of background concentrations. Irrigation Water Supply (Specific Conductivity, Minerals) For specific conductivity the Basin Plan has an objective of 700 umhos/cm April through August and 1000 umhos/cm September through March for SJR at Airport Way (also known as Vernalis). This ob-jective only applies to a maximum thirty day running average. Although approximately 21 percent of individual samples collected at Vernalis had concentrations above the noted objective during the sam-pling period, exceedances can not be determined using the limited grab samples. Multiple samples at concentrations above the Water Quality Goal for Agriculture of 700 umhos/cm (Marshack, 2003) were found in all basins except the Northeast Basin. The Eastside Basin had the lowest percentage of elevated samples (39 out of 409—9.5%) and the Grasslands (1047 out of 1049--~100%), Westside (330 out of 516—64%) and the South Delta Basin (163 out of 188—87%) had the highest percentages of elevated samples. Multiple samples collected along the SJR also had concen-trations reported above the Water Quality Goal for Agriculture. The elevated concentrations were con-sistently clustered between Lander Avenue (primarily ground water accretions) and Maze Blvd., a stretch of river receiving inflows from the Grassland, Eastside and Westside Basins. Chloride and sodium concentrations that were above water quality goals of 106 mg/L and 69-mg/L, re-spectively, tracked elevated levels of specific conductance. Concentrations above the total dissolved solids Water Quality for Agriculture goal of 450 mg/L occurred mostly in the Grasslands and Westside Basin. The Northeast Basin was never above this goal and most of the elevated concentrations reported in the Eastside Basin were found in the Harding Drain. In summary, salt concentrations throughout the SJR Basin appear to be elevated above optimal con-centrations for irrigation water supply, except within the Northeast and Eastside Basins. Salt is a well documented issue within the Grasslands and Westside Basins, with the natural background of the area being highly saline and high salinity water being pumped from the Delta to meet agricultural needs. Huge continuous efforts to control salt have been implemented in the past and continue to this day.
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See the future actives section 14.0 of this report for more information on the current efforts being made to address salt in the SJR valley. Recreation (Bacteria) All the sites monitored during this study are either specifically designated or tributary to a water body designated for full contact recreation (e.g. swimming), except for the San Luis Drain and New Jerusa-lem Drain. As a conservative approach, the USEPA Guideline for full contact of 235 MPN/100ml E. coli was used to evaluate the entire SJR basin. Many of sites may not support full recreational contact due to physical attribute (e.g. ankle deep water), however, the use of a single guideline provided consis-tency for the review. The highest percentages of E. coli concentrations exceeding 235 MPN/100ml were found in the West-side Basin and the non-river sites of the Eastside Basin (Figure 52). E. coli spikes were seen during high and low flow events meaning E. coli spikes are randomly present during both winter storm events when it would be unlikely to find people swimming and during the warmer summer season when most recreational contact would occur.
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Figure 52: Percentage of E. coli samples greater than the USEPA Guideline: Designated Beach Area (235 MPN/100ml)
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Table 8: Summary of Potential Beneficial Use Concerns: San Joaquin River and Sub-Basin Sites (2000 to 2005) San Joaquin River Sub-Basins
Beneficial Use/Indicator Sack
Dam
Land
er A
ve
Frem
ont
Ford
Cro
ws
Land
ing
Pat
ters
on
Maz
e
Airp
ort
SE Grassland East West NE S. Delta
Drinking Water Specific Conductivity NA Total Organic Carbon Trace Elements T. Arsenic T. Arsenic 4 E. coli Nutrients3 Nitrate Nitrate Nitrate
Aquatic Life pH Temperature Dissolved Oxygen Turbidity NA NA NA NA NA NA NA Trace Elements T. Copper T. Copper 5 Minerals Water Column Toxicity 7 1 2
Irrigation Water Supply Specific Conductivity Minerals
Recreation (Swimming) E. coli =One or more result above a goal or objective NA = There is no goal or objective applicable to the location 1Only had three samples taken with no toxic event found 2 Only had one sample taken with no toxic event found 3 Found for Nitrate only 4 total arsenic, total chromium, total lead, total nickel and total mercury results were found above drinking water goals 5 total and dissolved copper, total lead, and total zinc were found above aquatic life goals 6 total and dissolved copper were found above aquatic life goals 7 no samples were taken
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13.0 SUMMARY/CONCLUSION In general the SJR receives drainage from a variety of diverse basins. For example, the Grassland Ba-sin is a highly managed system that is dominated by agricultural influences (both traditional cropland and managed wetlands) and receives water from the Sacramento-San Joaquin Delta to support the land use. The Northeast Basin contains the Cosumnes watershed which drains snowmelt from the Si-erras and is the last major water body within the Central Valley that does not have flow regulated by a major reservoir. Most of the drainage basin sites are within the valley floor which is dominated by agri-cultural use and urban development. Even though the land uses are similar for most of the drainage basin sites, the source water from their upper watersheds are completely different across the basins and create a truly unique and complex system. The spatial trend for most constituents (SC, TSS, turbidity, metals, and minerals) within the SJR is that concentrations seem to increase from Sack Dam to Hills Ferry, as a result of the Grassland influences, and decrease from Hills Ferry down to Vernalis due to the Eastside Basin river sites contribution of high flow Sierra snow melt and reservoir storage flows. Other constituents displayed strong seasonal trends that were consistent throughout the whole SJR valley floor. For instance, temperature increased at all sites during the warm summer months. Dis-solved oxygen concentrations decreased at all sites during the warmer summer months, which may be offset by algal blooms as well as temperature, with a decrease in dramatic fluctuation within SJR sites during the wet WY of 2005. Specific conductivity, TOC, turbidity, and TSS were influenced by storm events, specifically for SC the first storm runoff, and the irrigation season. Findings by individual Basins included: Northeast Basin:
Northeast basin had the lowest levels for most constituents compared to the rest of the SJR ba-sin. All of the four samples collected for acute algae at Cosumnes River had a reduction of cell growth. This reduction could be due to the minimal nutrients and minerals found in the Cosum-nes River watershed, but a toxicity identification evaluation was not conducted.
Eastside Basin:
The Eastside Basin river sites (Merced, Tuolumne and Stanislaus) typically followed the North-east basin with low levels for most constituents compared to the rest of the basins. In contrast, the Harding Drain reported the elevated levels of SC, E. coli, nutrients, BOD and min-erals. Harding Drain also had dramatic fluctuations of DO.
Southeast Basin:
Deep Slough had high year round levels of arsenic and total nickel which was unique for the en-tire SJR Basin and had the majority of detected samples during high flow events.
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South Delta Basin:
New Jerusalem Tile Drain, which represents shallow ground water within the South Delta Basin, had higher temperature, SC, nitrate levels, and minerals compared to the rest of the South Delta Basin. The New Jerusalem Drain, even with its high nitrate concentrations, had very low TSS and TOC concentrations with the BOD typically just above the detection limit of 0.1 mg/L--unlike the rest of the South Delta Basin. The New Jerusalem Drain had non-detect values for most of the metals except high concentrations of chromium.
Tom Payne Slough had a consistent seasonal fluctuation of minerals. High concentrations of minerals are seen during the winter months with a drastic drop in mineral concentrations during the summer months.
Westside Basin:
The Westside Basin sites on average had greater turbidity and TSS than the remainder of the SJR Basin sites with concentrations fluctuating greatly during the irrigation season and storm events. The Westside Basin also had relatively higher concentrations of nutrients and minerals than other basin sites. The Westside Basin had a high volume of detected values for total lead and had overall higher concentrations and major spikes of copper, zinc, and chromium.
Grassland Basin:
The Grassland Basin was sampled more frequently for every site other than those on the main stem of the SJR due to the compliance monitoring program for the Grassland Bypass Project (se-lenium control program). For all sites within the Grassland Basin, other than for Salt Slough, there is a clear seasonal fluctuation for pH. The pH tends to peak in July and drop to its lowest around January mirroring the temperature results. The Grassland Basin has high levels of SC, TSS, and minerals compared to the eastern basins. Salt Slough, having a total of three algal toxicity samples collected, had two toxic events for the increase in growth for acute algae and one toxic event for a reduction in algal growth. Of the se-venteen samples within Salt Slough collected for acute fathead minnow and acute Ceriodaphnia dubia, no toxic events were found.
When evaluated against the water quality objectives and goals found in Appendix Q1 and Q2 there are multiple areas of concern within the SJR Basin. Drinking Water/Municipal Supply: High TOC levels throughout the SJR valley are elevated above guidelines for the delta intended to pro-tect drinking water.
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Aquatic life: Elevated temperatures throughout the basin were a concern during the spring and fall. Total copper had high occurrences in French Camp Slough, Lone Tree Creek, and Pixley Slough. Turbidity was a concern within the Westside Basin, but a more applicable Basin Plan objective is needed to determine potential for impairment. Irrigation Water Supply: When compared against the Water Quality Goal for Agriculture of 700 umhos/cm, large areas of the basin appear to be elevated above optimal irrigation water quality guidelines for specific conductance. Salt is an overwhelming ongoing concern for most of the SJR Basin particularly the Grasslands and Westside basin. Recreation: E. coli had occasional spikes during the summer months when most of the waterways have a potential for recreational use. A majority of the sites with high percentages of samples exceeding the conserva-tive level percentages may need further evaluation to determine actual level of potential recreational use. 14.0 FUTURE ACTIVITIES While information collected during this study was utilized to help fine tune the monitoring programs for the Northeast, Eastside and Westside Sub-basins during the rotational portion of the overall effort, after WY 2005 the SJR SWAMP effort was not able to continue the Drainage Basin or Intensive Rotational Basin sites due to funding reductions. Since 2005, the SJR SWAMP sampling has been limited to maintaining the water quality monitoring for the multi-agency Grassland Bypass Project (GBP), with ad-dition of E. coli analyses twice a month at the GBP sites. Since 2003, expanded monitoring of agricultural drainage inflows to the SJR have been conducted by various Agricultural Coalition Groups as part of the Irrigated Lands Regulatory Program (ILRP). SWAMP is providing resources to ensure ILRP water quality information is captured in the statewide SWAMP master database. To address the salt issue within the SJR Basin the Central Valley Water Board formed the Central Val-ley Salinity Alternatives for Long-Term Sustainability (CV-SALTS). This program is an effort to address the salinity problems within the Central Valley and will adopt long-term solutions to improve water qual-ity and economic sustainability. The following website has up-to-date information about CV-SALTS: http://www.swrcb.ca.gov/centralvalley/water_issues/salinity/index.shtml . The Central Valley Water Board SWAMP effort has refocused limited resources on better identifying current monitoring efforts conducted by both internal programs (GBP, ILRP, NPDES receiving water requirements, TMDL, and others) and major external efforts (Department of Water Resources, US Bu-reau of Reclamation, US Geological Survey, University of California and watershed groups) through the development of a web-based surface water monitoring directory. The directory builds off of a pilot pro-ject with the San Francisco Estuary Institute (SFEI) begun by the US EPA within the San Joaquin River Basin, and has been expanded by the Central Valley Water Board SWAMP to include the entire Central
96
Valley (Sacramento, San Joaquin, and Tulare Basins and Delta). The web-based monitoring directory is designed to only display active monitoring efforts and to identify what is being monitored where, how frequently, for how long, and by which agency. While actual data is not captured, the directory will pro-vide links to any web based database and contact information for the monitoring program manager. Initial feeding of the directory has focused on multi-agency efforts within the Sacramento-San Joaquin Delta to help identify available water quality information in order to facilitate a more thorough evaluation of water quality. In addition, the directory has been beta-tested by loading information on the internal GBP, ILRP, NPDES, statewide SWAMP, and DWR Northern District efforts for the entire Central Val-ley. The directory can currently be viewed at the following website http://www.centralvalleymonitoring.org/. It is anticipated that beta testing will be complete and the di-rectory will be available for data entry from interested parties during late spring 2009. Central Valley SWAMP is also currently:
• Providing resources (staff and contract dollars) to facilitate development of a Regional Monitor-ing Program for the Sacramento-San Joaquin Delta.
• Supporting the Department of Water Resources staff to continue long-term trend monitoring at
41-sites in the northern Sacramento River Basin in exchange for the addition of selected con-stituents of concern identified through Central Valley Regional Board efforts (TOC, nutrients, and toxicity) and realignment of 11-sites to correspond with sites utilized by the statewide SWAMP sediment toxicity study.
• Developing a region-wide, long-term trend monitoring framework based on the 30-sites within
the Central Valley that are part of the state-wide SWAMP contaminant trend monitoring effort
• Development of the Central Valley Regional Board SWAMP website that documents monitoring activities supported by SWAMP and provides links to final reports and selected water quality data (http://www.waterboards.ca.gov/centralvalley/water_issues/water_quality_studies/surface_water_ambient_monitoring/index.shtml)
Efforts related specifically to the elevated E. coli concentrations found within the SJR Basin as well as in other areas of the Central Valley as part of ILRP monitoring, include:
o A survey of E. coli concentrations in local swimming holes before during and after a holiday weekend (coordinated with Central Valley watershed groups during both 2007 and 2008)
o A pilot bacteria source identification project with the University of California, Davis, in selected streams with a history of elevated E. coli concentrations
o Continued, seasonal E. coli monitoring at 30-major integrator sites throughout the Central Val-ley.
Recommendations for future monitoring for each sub-basin and river site include those parameters identified in Table 8. Data has been posted annually on our website since 2003 and utilized in combi-nation with other available data for assessment in the Clean Water Act Sections 305(b) and 303(d) In-tegrated Report for the Central Valley Region (CVRWQCB, 2009 Draft).
97
15.0 REFERENCES
1. Bureau of Reclamation. 1995. Grassland Bypass Project. http://www.usbr.gov/mp/grassland/index.html (Accessed: April 16, 2009).
2. Cal Fed Bay-Delta Program (CFBDP). 2000. Water Quality Program Plan. 3-52, D-5.
3. California Code of Regulations. Register 2006, No 38. Title 22, Division 4, Chapter 15, Article 4, s 64431; Article 16, s 64449; Article 18, s 64468.1. Updated 9/22/06. http://ccr.oal.ca.gov/linkedslice/default.asp?SP=CCR-1000&Action=Welcome. Accessed 9/29/06.
4. Central Valley Regional Water Quality Control Board (CVRWQCB). 1998. Water Quality Control Plan (Basin Plan) for the Sacramento River and San Joaquin River Basins, Fourth Edition, Au-gust 2006.
5. Central Valley Regional Water Quality Control Board (CVRWQCB). 2009. The 2008 Update to
the 303(d) List and Development of the 2008 303(d)/305(b) Integrated Report. http://www.waterboards.ca.gov/centralvalley/water_issues/tmdl/impaired_waters_list/303d_list.shtml
6. Chilcott, J., Laguna, C., Dinkler, L., 1996. Agricultural Subsurface Drainage Program Proce-
dures Manual. Regional Water Quality Control Board, Central Valley Region Report
7. Chilcott, J., 1992. Consideration of Water Body Designations to Comply with Provisions of the Water Quality Control Plan for Inland Surface Waters of California (ISWP). Regional Water Quality Control Board, Central Valley Region Report
8. Dubrovsky, Neil M., Kratzer, Charles R., Brown, Larry R., Gronberg, Jo Ann M., Burow, Karen
R. 1998 Water Quality in the San Joaquin-Tulare Basins, California, 1992-1995. United States Geological Survey. Circular 1159. p. 5
9. DWR. 2001. Annual Land and Water Use Data: Irrigated Crop Area. State of California
http://www.landwateruse.water.ca.gov/annualdata/landuse/2001/landuselevels.cfm . (Accessed: April 2, 2009)
10. DWR. 2007. California Data Exchange Center (CDEC). Access to the Department of Water
Resources Operational Hydrologic Data http://cdec.water.ca.gov/
11. DWR. 2007. California Cooperative Snow Surveys. Chronological Reconstructed Sacramento and San Joaquin Valley Water Year Hydrologic Classification Indices. WSIHIST (11/30/04 1136). http://cdec.water.ca.gov/cgi-progs/iodir/WSIHIST
12. Graham, C., 2009. San Joaquin River Basin Rotational Sub-basin Monitoring: Consumnes,
Mokelumne, and Calaveras River Watersheds, January – December 2002. Regional Water Quality Control Board, Central Valley Region.
13. James, E. W., Westcot, D. W., & Gonzalez, J. L. 1989.The Water Diversion and Discharge
Points Along the San Joaquin River. Regional Water Quality Control Board, Central Valley Re-gion (CVRWQCB)
98
14. Marshack, J.B., 2003. A Compilation of Water Quality Goals. California Environmental Protec-tion Agency, Regional Water Quality Control Board, Central Valley Region. Sacramento, CA.
15. Morris, R.D., 1992. Chlorination, Chlorination By-products, and Cancer; A Meta-analysis. Amer-
ican Journal of Public Health. July 1992, Vol. 82, 955-963.
16. State Water Resources Control Board (SWRCB). 1995. Water Quality Control Plan for the San Francisco Bay/Sacramento-San Joaquin Delta Estuary.
17. State Water Resources Control Board (SWRCB). 2002. Quality Assurance Program Plan for the
State of California’s Surface Water Ambient Monitoring Program “SWAMP”. Prepared by Puckett, Max. California Department of Fish and Game.
18. Steensen, R., Chilcott, J. E., Grober, L. F., Jensen, L. D., Eppinger, J. L., Burns, T..1998. Com-
pilation of Electrical Conductivity, Boron, and Selenium Water Quality Data for the Grassland Watershed and San Joaquin River. Regional Water Quality Control Board, Central Valley Re-gion.
19. U.S. Environmental Protection Agency. 1986. Ambient Water Quality Criteria for Bacteria. Bac-
teriological Ambient Water Quality Criteria for Marine and Fresh Recreational Waters.14-15.
20. U.S Environmental Protection Agency (USEPA). 2003. Elements of a State Water Monitoring and Assessment Program. Washington D.C.
21. Weston. Mason. 2009. Mountain House.
http://www.mountainhouse.net/town/community_planning.php (Accessed: April 16, 2009)
iv
APPENDIX A
SJR MAIN STEM
APPENDIX A: SJR MAIN STEM A1: 541MAD007 – SJR @ Sack Dam………………………………………….03-14 A2: 541MER522 – SJR @ Lander Avenue…………………………………….15-37 A3: 541MER538 – SJR @ Fremont Ford………………………………………38-61 A4: 541STC512 – SJR @ Hills Ferry………………………………………….62-76 A5: 535STC504 – SJR @ Crows Landing……………………………………..77-101 A6: 541STC507 – SJR @ Patterson…………………………………………….102-125 A7: 541STC510 – SJR @ Maze………………………………………………...126-147 A8: 541SJC501 – SJR @ Airport Way…………………………………………148-171
2
A1: 541MAD007 – SJR @ Sack Dam Station Code:514MAD007
Location: Latitude 36.98361, Longitude -120.50028
Date TimeTemp (ºC)
Field SC (umhos) pH
Dissolved Oxygen (mg/L)
Turbidity (ntu)
10/26/2000 8:50 AM 13.1 510 7.411/30/2000 6:35 AM 9.3 663 6.812/28/2000 8:00 AM 5.6 616 8.01/25/2001 8:50 AM 7.5 760 7.22/7/2001 8:52 AM 8.3 726 8.82/22/2001 8:15 AM 10.3 697 8.13/13/2001 9:36 AM 16.7 568 6.93/29/2001 8:30 AM 18.2 913 8.04/18/2001 9:30 AM 17.5 602 7.54/26/2001 1:30 PM 26.3 679 7.25/15/2001 9:40 AM 19.1 509 6.65/31/2001 11:30 AM 24.1 530 7.96/28/2001 9:52 AM 22.1 465 7.6 6.87/26/2001 10:30 AM 25.7 380 7.6 NA8/14/2001 9:29 AM 23.9 514 7.9 7.58/30/2001 10:50 AM 23.2 641 8.3 NA9/27/2001 9:28 AM 20.9 713 7.9 7.7
10/25/2001 9:21 AM 15.6 661 8.5 9.711/29/2001 11:24 AM 10.3 1010 8.0 10.912/27/2001 10:55 AM 8.8 748 7.9 11.41/31/2002 9:25 AM 5.5 651 7.6 12.92/28/2002 9:14 AM 14.3 745 7.8 9.13/28/2002 9:42 AM 16.4 691 8.1 11.74/24/2002 9:13 AM 18.3 477 8.4 8.65/30/2002 10:13 AM 23.1 520 7.9 4.96/20/2002 9:05 AM 22.6 462 7.2 7.9 NA7/30/2002 9:20 AM 24.2 466 7.6 6.6 71.18/29/2002 9:00 AM 22.8 558 7.7 7.7 NA9/26/2002 9:28 AM 21.3 650 7.8 7.6
10/17/2002 9:59 AM 16.6 615 7.8 8.3 51.910/31/2002 9:55 AM 13.8 624 7.6 10.7 NA11/21/2002 9:40 AM 12.2 609 7.9 10.3 12.612/19/2002 9:08 AM 8.1 642 7.3 10.4 7.31/14/2003 9:07 AM 11.4 701 7.9 9.5 30.01/30/2003 9:45 AM 13.0 600 7.0 10.8 31.13/27/2003 11:12 AM 15.8 682 8.1 13.9 25.64/24/2003 10:10 AM 17.3 449 7.6 8.1 85.95/29/2003 9:05 AM 24.5 583 7.4 7.1 1126/26/2003 8:50 AM 24.0 272 7.8 8.7 55.6
3
A1: 541MAD007 – SJR @ Sack Dam continued…
Date TimeTemp (ºC)
Field SC (umhos) pH
Dissolved Oxygen (mg/L)
Turbidity (ntu)
7/31/2003 9:40 AM 26.3 337 7.6 6.4 73.28/28/2003 9:32 AM 23.4 505 7.7 7.4 56.79/25/2003 9:27 AM 20.9 391 7.6 7.8 111
10/30/2003 9:47 AM 16.2 530 8.0 7.6 18.111/20/2003 9:51 AM 12.7 540 7.9 9.9 16.91/29/2004 9:42 AM 9.0 446 8.0 13.6 62.92/26/2004 9:25 AM 11.9 678 7.9 8.9 NA3/24/2004 9:53 AM 17.1 384 7.8 9.0 NA4/29/2004 9:02 AM 16.8 528 8.3 8.6 24.55/27/2004 9:29 AM 20.1 479 7.6 8.0 49.46/24/2004 9:25 AM 22.7 544 7.8 5.4 NA7/29/2004 9:04 AM 25.1 380 8.2 7.8 NA8/26/2004 9:08 AM 22.6 443 7.8 0.6 NA9/30/2004 8:46 AM 18.3 506 8.6 7.7 NA
10/28/2004 8:55 AM 12.5 561 8.4 9.311/23/2004 9:02 AM 9.6 559 7.8 11.812/29/2004 8:41 AM 9.3 581 7.8 10.91/27/2005 8:50 AM 11.1 479 8.1 11.62/24/2005 9:41 AM 14.0 888 7.9 9.73/29/2005 10:00 AM 14.4 725 8.0 9.84/28/2005 9:01 AM 16.8 223 8.1 8.45/26/2005 8:52 AM 20.2 85 7.7 8.16/30/2005 9:00 AM 23.3 109 7.9 7.77/28/2005 9:03 AM 26.4 348 7.9 7.08/25/2005 9:07 AM 23.9 404 8.0 8.09/29/2005 9:19 AM 20.6 402 6.2 7.4
Count 65 65 65 51 18Min 5.5 85 6.2 0.6 7.3Max 26.4 1010 8.8 13.9 112Mean 17.2 553 7.8 8.8 49.8Geo Mean 16.0 519 7.8 8.3 39.1Median 17.1 558 7.8 8.4 50.7Quartile 1 12.5 465 7.6 7.7 24.8Quartile 3 22.7 661 8.0 10.1 69.1NOTE: For values reported as < (less than), half the detection limit was used.
NA = Data not applicableINA = Site was inaccessibleDRY = Site had no flow
4
A1: 541MAD007 – SJR @ Sack Dam continued…
DateTSS
(mg/L)TOC
(mg/L)Total Coli
MPNE. coli MPN
10/26/2000 18 2.411/30/2000 57 2.212/28/2000 NA 1.81/25/2001 40 3.82/22/2001 32 2.93/29/2001 NA <14/26/2001 45/31/2001 26 46/28/2001 33 5.57/26/2001 38/30/2001 32 6.59/27/2001 50
10/25/2001 9.511/29/2001 <11/31/2002 3.53/28/2002 NA4/24/2002 7.85/30/2002 2.96/20/2002 2.97/30/2002 >2419.6 199/26/2002 2.7
10/17/2002 >2419.6 2910/31/2002 NA11/21/2002 2.112/19/2002 2.61/14/2003 816 403/27/2003 2.34/24/2003 NA 1986 595/29/2003 4.76/26/2003 2.97/31/2003 >2419.6 208/28/2003 >2419.6 239/25/2003 >2419.6 29
10/30/2003 >2419.6 3811/20/2003 1986 301/29/2004 727 242/26/2004 770 1383/24/2004 >2419.6 504/29/2004 >2419.6 2485/27/2004 >2419.6 916/24/2004 >2419.6 317/29/2004 >2419.6 73
5
6
DateTSS
(mg/L)TOC
(mg/L)Total Coli
MPNE. coli MPN
8/26/2004 >2419.6 1019/30/2004 >2419.6 36
10/28/2004 3.4 >2419.6 6111/23/2004 4 1203 4412/29/2004 4.4 1986 471/27/2005 11 2420 392/24/2005 6.4 1986 633/29/2005 5.3 1120 264/28/2005 4.8 >2419.6 445/26/2005 4.6 >2419.6 1056/30/2005 NA 1011 467/28/2005 NA >2419.6 328/25/2005 2.4 >2419.6 419/29/2005 2.5 >2419.6 64
C
A1: 541MAD007 – SJR @ Sack Dam continued…
ount 8 33 30 30Min 18 0.5 727 19Max 57 11 2420 248Mean 36 3.9 NA NAGeo Mean 34 3.3 1944 46Median 33 3.4 2420 43Quartile 1 31 2.5 1986 30Quartile 3 43 4.7 2420 63
OTE: For values reported as < (less than), half the detection limit was used For values reported as > (greater than), 2420 was used
A = Data not applicableINA = Site was inaccessible
RY = Site had no flow
N
N
D
A1: 541MAD007 – SJR @ Sack Dam continued…
DateNitrate (mg/L)
Nitrate-N (mg/L)
TKN (mg/L)
Ammonia-N (mg/L)
Phosphorus (mg/L)
Ortho-phosphate-
P (mg/L)
Potassium (mg/L)
BOD 5-Day (mg/L)
BOD 10-Day (mg/L)
10/26/2000 3.5 <2 NA <1 4.3 0.7 111/30/2000 5 <2 <0.1 <1 6 0.9 1.512/28/2000 5 <2 <0.1 <1 5.2 0.8 11/25/2001 NA NA 0.2 <1 5.9 1 1.72/7/2001 NA <2 NA <1 NA2/22/2001 9 <2 NA <1 5.4 0.7 1.43/29/2001 9.7 NA 0.2 <1 6.9 0.7 1.44/18/2001 5.9 <2 0.1 <1 4.84/26/2001 7.6 <2 0.2 <1 5.1 0.9 1.75/15/2001 4 <2 0.1 <1 4.65/31/2001 3.7 <2 0.1 <1 4.6 0.7 1.26/28/2001 3.6 <2 0.2 <1 4.3 0.5 1.28/14/2001 2.4 <2 0.2 <1 4.88/30/2001 2.4 <2 0.2 <1 5.29/27/2001 2.9 <2 0.2 <1 6.8
10/25/2001 2.7 <2 0.1 <1 6 0.6 0.811/29/2001 NA NA NA 0.1 NA 1.2 212/27/2001 NA NA 0.1 0.1 4.6 0.6 1.41/31/2002 NA 1.3 0.2 0.1 NA 1 1.62/28/2002 NA NA 0.1 0.1 3.5 0.6 1.23/28/2002 NA 0.4 0.1 0.1 3.5 0.8 1.24/24/2002 NA NA 0.2 0.1 4.1 0.9 1.55/30/2002 NA NA NA 0.1 4.7 0.7 0.96/20/2002 NA 0.4 NA 0.1 4 0.7 1.38/29/2002 NA 1 NA 0.1 4.5 0.8 1.39/26/2002 NA 0.3 0.1 0.1 5.7 0.8 1.4
10/31/2002 NA 0.1 0.1 0.1 3.7 0.3 0.5
7
A1: 541MAD007 – SJR @ Sack Dam continued…
DateNitrate (mg/L)
Nitrate-N (mg/L)
TKN (mg/L)
Ammonia-N (mg/L)
Phosphorus (mg/L)
Ortho-phosphate-
P (mg/L)
Potassium (mg/L)
BOD 5-Day (mg/L)
BOD 10-Day (mg/L)
11/21/2002 NA 0.4 <0.05 <0.03 3.4 0.8 112/19/2002 NA 0.4 <0.05 <0.03 3.7 1.1 1.41/30/2003 NA 1.2 NA 0.1 3 1 1.5
Count 14 NA 23 NA 22 30 27 24 24Min 2.4 NA 0.1 NA 0.03 0.02 3.0 0.3 0.5Max 9.7 NA 1.3 NA 0.2 0.5 6.9 1.2 2.0Mean 4.8 NA 0.8 NA 0.1 0.3 4.8 0.8 1.3Geo Mean 4.3 NA 0.7 NA 0.1 0.2 4.6 0.8 1.3Median 3.9 NA 1.0 NA 0.1 0.5 4.6 0.8 1.4Quartile 1 3.1 NA 0.7 NA 0.1 0.1 4.1 0.7 1.2Quartile 3 5.7 NA 1.0 NA 0.2 0.5 5.3 0.9 1.5NOTE: For values reported as < (less than), half the detection limit was used.
NA = Data not applicableINA = Site was inaccessibleDRY = Site had no flow
8
A1: 541MAD007 – SJR @ Sack Dam continued…
DateHardness
(mg/L)
Total Arsenic (ug/L)
Total Cadmium
(ug/L)
Total Chromium
(ug/L)
Total Copper (ug/L)
Total Lead (ug/L)
Total Nickel (ug/L)
Total Zinc (ug/L)
Total Mercury (ug/L)
11/30/2000 110 2 3.5 <5 <5 6.712/28/2000 140 <1 2.2 <5 <5 <21/25/2001 130 1.8 3.8 <5 <5 4.82/22/2001 160 1.6 3.6 <5 <5 5.13/29/2001 160 2.2 3.8 <5 <5 5.54/26/2001 210 1.8 3 <5 <5 3.75/31/2001 170 1.1 2.8 <5 <5 4.16/28/2001 120 3.1 <1 1.9 3.4 <5 <5 4.8 <0.27/26/2001 110 NA NA 2.6 3.4 <5 <5 NA NA8/30/2001 120 3.5 <1 1.5 2.3 <5 <5 4.29/27/2001 130 <4 <0.1 2.5 4.7 <5 <5 6.5 <0.2
10/25/2001 120 <4 <0.1 <1 1.9 <5 <5 <2 NA11/29/2001 100 <4 <0.1 3.9 4 <5 6 12 <0.212/27/2001 150 <4 <0.1 3 4.2 <5 5.2 7.9 <0.22/28/2002 150 <4.0 <0.1 1.3 4 <5.0 <5.0 7 <0.23/28/2002 190 <4.0 <0.1 <1.0 2.6 <5.0 NA 4.2 <0.24/24/2002 120 4.1 <0.1 <1.0 1.9 <5.0 <5.0 <2.0 <0.25/30/2002 120 <4.0 <0.1 1 2.6 <5.0 <5.0 <2.0 <0.26/20/2002 110 <4.0 <0.1 1 2.5 <5.0 <5.0 3.5 <0.29/26/2002 130 <4.0 <0.1 2 3.7 <5.0 <5.0 5.2 <0.2
10/31/2002 130 <4.0 <0.1 <1.0 1.7 <5.0 <5.0 <2.0 <0.211/21/2002 130 <4.0 <0.1 <1.0 2.5 <5.0 <5.0 2.1 <0.23/27/2003 150 <4.0 <0.1 1.4 2.9 <5.0 <5.0 2.9 <0.24/24/2003 120 <4.0 <0.1 4.3 5.2 <5.0 5.9 9.4 <0.25/29/2003 140 <4.0 <0.1 1.6 4 <5.0 <5.0 3.5 <0.26/26/2003 76 <4.0 <0.1 2.4 3.4 <5.0 <5.0 5.7 NA
9
A1: 541MAD007 – SJR @ Sack Dam continued…
DateHardness
(mg/L)
Total Arsenic (ug/L)
Total Cadmium
(ug/L)
Total Chromium
(ug/L)
Total Copper (ug/L)
Total Lead (ug/L)
Total Nickel (ug/L)
Total Zinc (ug/L)
Total Mercury (ug/L)
Count 26 18 18 26 26 26 25 25 15Min 76 2.0 0.1 0.5 1.7 2.5 2.5 1.0 0.1Max 210 4.1 0.5 4.3 5.2 2.5 6.0 12.0 0.1Mean 134 2.3 0.1 1.7 3.2 2.5 2.9 4.6 0.1Geo Mean 132 2.2 0.1 1.4 3.1 2.5 2.8 3.6 0.1Median 130 2.0 0.1 1.6 3.4 2.5 2.5 4.2 0.1Quartile 1 120 2.0 0.1 1.0 2.5 2.5 2.5 2.9 0.1Quartile 3 150 2.0 0.1 2.2 3.8 2.5 2.5 5.7 0.1NOTE: For values reported as < (less than), half the detection limit was used.
NA = Data not applicableINA = Site was inaccessibleDRY = Site had no flow
10
A1: 541MAD007 – SJR @ Sack Dam continued…
DateHardness
(mg/L)
Dissolved Arsenic (ug/L)
Dissolved Cadmium
(ug/L)
Dissolved Chromium
(ug/L)
Dissolved Copper (ug/L)
Dissolved Lead (ug/L)
Dissolved Nickel (ug/L)
Dissolved Zinc
(ug/L)
Dissolved Mercury (ug/L)
11/30/2000 110 <1 1.1 <5 <5 3.212/28/2000 140 <1 <1 <5 <5 <21/25/2001 130 <1 <1 <5 <5 <22/22/2001 160 <1 1.5 <5 <5 <23/29/2001 160 <1 2.3 <5 <5 <24/26/2001 210 <1 1.2 <5 <5 <25/31/2001 170 <1 1.4 <5 <5 <26/28/2001 120 2.8 <1 <1 <1 <5 <5 <2 <0.27/26/2001 110 NA NA NA NA NA NA NA NA8/30/2001 120 2.9 <1 <1 1.2 <5 <5 <29/27/2001 130 <4 <0.1 <1 1.6 <5 <5 <2 <0.2
10/25/2001 120 <4 <0.1 <1 1.7 <5 <5 <2 NA11/29/2001 100 <4 <0.1 <1 <1 <5 <5 5.7 <0.212/27/2001 150 <4 <0.1 <1 2.3 <5 <5 2.1 <0.22/28/2002 150 <4.0 <0.1 <1.0 2.3 <5.0 <5.0 4.6 <0.23/28/2002 190 <4.0 <0.1 <1.0 1.2 <5.0 <5.0 2.9 <0.24/24/2002 120 5.6 <0.1 <1.0 3.2 <5.0 <5.0 <2.0 <0.25/30/2002 120 <4.0 <0.1 <1.0 1.9 <5.0 <5.0 <2.0 <0.26/20/2002 110 <4.0 <0.1 <1.0 1.9 <5.0 <5.0 2.5 <0.29/26/2002 130 <4.0 <0.1 <1.0 1.1 <5.0 <5.0 <2.0 <0.2
10/31/2002 130 <4.0 <0.1 <1.0 <1.0 <5.0 <5.0 <2.0 <0.211/21/2002 130 <4.0 <0.1 <1.0 1.6 <5.0 <5.0 <2.0 <0.2
11
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DateHardness
(mg/L)
Dissolved Arsenic (ug/L)
Dissolved Cadmium
(ug/L)
Dissolved Chromium
(ug/L)
Dissolved Copper (ug/L)
Dissolved Lead (ug/L)
Dissolved Nickel (ug/L)
Dissolved Zinc
(ug/L)
Dissolved Mercury (ug/L)
Count 22 14 14 21 21 21 21 21 12Min 100 2.0 0.1 0.5 0.5 2.5 2.5 1.0 0.1Max 210 5.6 0.5 0.5 3.2 2.5 2.5 5.7 0.1Mean 137 2.4 0.1 0.5 1.4 2.5 2.5 1.7 0.1Geo Mean 134 2.3 0.1 0.5 1.2 2.5 2.5 1.4 0.1Median 130 2.0 0.1 0.5 1.4 2.5 2.5 1.0 0.1Quartile 1 120 2.0 0.1 0.5 1.1 2.5 2.5 1.0 0.1Quartile 3 150 2.0 0.1 0.5 1.9 2.5 2.5 2.1 0.1NOTE: For values reported as < (less than), half the detection limit was used.
NA = Data not applicableINA = Site was inaccessibleDRY = Site had no flow
12
A1: 541MAD007 – SJR @ Sack Dam continued…
DateChloride (mg/L)
Sulfate (mg/L)
Calcium (mg/L)
Magnesium (mg/L)
TDS (mg/L)
Carbonate (mg/L)
Bicarbonate (mg/L)
Total Alkalinity
(mg/L)Sodium (mg/L)
10/26/2000 72 46 22 12 280 <1 104 90 5511/30/2000 90 68 29 17 380 <1 100 90 7512/28/2000 94 61 26 16 340 <1 110 90 691/25/2001 110 86 31 19 430 <1 110 90 882/22/2001 77 92 34 18 430 <1 120 94 773/29/2001 100 130 45 23 580 <1 140 120 1004/26/2001 73 120 37 18 430 <1 94 94 715/31/2001 72 55 24 14 300 <1 78 78 576/28/2001 61 47 23 13 260 <1.0 100 83 508/30/2001 100 46 22 15 340 <1 110 87 739/27/2001 120 48 23 18 380 <1 110 90 89
10/25/2001 110 44 22 16 NA <1 100 86 8011/29/2001 150 97 22 12 600 <1 170 140 17012/27/2001 110 72 29 18 400 <1 120 98 841/31/2002 74 87 32 17 NA <1 NA NA 662/28/2002 94 110 40 21 450 <1 130 110 883/28/2002 88 96 35 19 NA <1.0 120 98 754/24/2002 64 51 25 14 NA <1.0 100 82 505/30/2002 37 27 24 15 270 <1.0 98 80 586/20/2002 59 50 23 13 NA <1.0 98 80 499/26/2002 120 39 23 17 NA <1.0 100 84 82
10/31/2002 100 49 25 16 340 <1.0 110 89 7511/21/2002 100 41 25 16 340 <1.0 100 82 703/27/2003 33 174/24/2003 50 55 25 145/29/2003 85 73 29 16
13
14
A1: 541MAD007 – SJR @ Sack Dam continued…
DateChloride (mg/L)
Sulfate (mg/L)
Calcium (mg/L)
Magnesium (mg/L)
TDS (mg/L)
Carbonate (mg/L)
Bicarbonate (mg/L)
Total Alkalinity
(mg/L)Sodium (mg/L)
6/26/2003 24 30 17 8
Count 26 26 27 27 17 23 22 22 23Min 24 27 17 8 260 0.5 78 78 49Max 150 130 45 23 600 0.5 170 140 170Mean 86 66 28 16 385 0.5 110 93 76Geo Mean 81 61 27 16 375 0.5 110 92 73Median 89 55 25 16 380 0.5 110 90 75Quartile 1 72 46 23 14 340 0.5 100 83 62Quartile 3 100 87 32 18 430 0.5 120 94 83NOTE: For values reported as < (less than), half the detection limit was used.
NA = Data not applicableINA = Site was inaccessibleDRY = Site had no flow
A2: 541MER522 – SJR @ Lander Avenue Station Code:541MER522
Location: Latitude 37.29528, Longitude -120.85028
Date TimeTemp (ºC)
Field SC (umhos) pH
Dissolved Oxygen (mg/L)
Turbidity (ntu)
10/5/2000 10:00 AM 20.8 1700 7.010/12/2000 10:55 AM 17.4 1610 7.810/19/2000 8:40 AM 17.5 809 7.910/26/2000 1:40 PM 15.9 1020 7.011/2/2000 9:41 AM 14.5 204 7.311/9/2000 9:25 AM 13.5 663 7.8
11/16/2000 10:10 AM 10.9 1150 6.711/21/2000 7:40 AM 9.6 1410 8.211/30/2000 9:12 AM 9.9 1430 6.612/7/2000 9:00 AM 10.1 872 7.9
12/12/2000 8:50 AM 11.1 1250 7.612/21/2000 10:55 AM 10.0 1330 7.812/28/2000 10:25 AM 8.9 1310 7.21/4/2001 9:00 AM 8.5 1260 7.81/11/2001 10:45 AM 9.1 927 7.71/18/2001 9:00 AM 7.4 966 7.81/25/2001 11:30 AM 10.4 1260 7.32/1/2001 10:22 AM 8.0 731 7.42/8/2001 9:50 AM 10.5 1100 7.92/10/2001 8:20 AM 10.2 1160 NA2/11/2001 12:28 AM 10.1 1230 7.82/15/2001 10:50 AM 9.9 515 7.32/22/2001 11:35 AM 12.9 1150 7.33/1/2001 8:45 AM 11.6 504 6.83/8/2001 9:30 AM 15.3 260 7.23/15/2001 11:05 AM 16.9 625 7.23/22/2001 11:22 AM 20.1 1060 7.73/29/2001 10:25 AM 21.3 1980 7.44/5/2001 11:50 AM 16.8 1320 7.74/12/2001 9:40 AM 14.2 851 6.84/19/2001 11:35 AM 17.2 1170 8.54/26/2001 10:29 AM 22.5 846 7.45/3/2001 10:00 AM 18.5 1800 7.95/10/2001 8:15 AM 22.9 1490 7.85/17/2001 11:35 AM 24.2 1740 7.75/24/2001 8:50 AM 22.1 1690 6.85/31/2001 9:00 AM 25.0 1840 8.26/7/2001 10:45 AM 24.7 1990 8.5 8.6
15
A2: 541MER522 – SJR @ Lander Avenue continued…
Date TimeTemp (ºC)
Field SC (umhos) pH
Dissolved Oxygen (mg/L)
Turbidity (ntu)
6/14/2001 9:52 AM 23.2 1710 7.9 8.86/21/2001 12:04 PM 30.0 1590 8.9 22.06/28/2001 12:15 PM 24.6 1920 8.2 10.17/5/2001 8:36 AM 26.1 1670 8.0 7.87/11/2001 10:55 AM 26.5 1960 8.7 22.07/19/2001 10:59 AM 26.2 1190 8.8 23.37/26/2001 2:00 PM 29.6 1380 8.8 NA8/2/2001 9:05 AM 25.1 939 8.4 14.48/9/2001 8:44 AM 26.5 1610 8.1 11.38/16/2001 9:50 AM 24.8 1460 8.6 14.38/23/2001 8:46 AM 23.8 1010 8.5 11.18/30/2001 12:55 PM 26.0 1290 8.3 NA9/6/2001 8:09 AM 23.6 1370 7.9 7.89/13/2001 8:42 AM 21.8 1290 7.8 7.29/20/2001 10:51 AM 25.7 1640 7.5 8.99/27/2001 11:43 AM 23.2 1760 8.3 11.110/4/2001 8:18 AM 21.6 1600 7.9 7.0
10/11/2001 9:00 AM 18.5 1710 8.1 8.810/18/2001 8:52 AM 18.9 1550 8.0 8.310/25/2001 11:15 AM 16.6 1120 8.1 12.311/1/2001 9:19 AM 16.8 1420 7.8 9.011/8/2001 9:00 AM 15.1 1020 8.4 9.6
11/15/2001 9:01 AM 13.5 1230 8.1 9.611/20/2001 10:58 AM 14.7 1140 7.6 8.611/29/2001 9:58 AM 10.8 1390 7.9 10.412/6/2001 8:30 AM 9.7 353 7.5 9.6
12/13/2001 8:59 AM 9.9 1180 7.9 9.212/20/2001 10:02 AM 10.1 1330 7.9 10.512/27/2001 9:47 AM 10.1 840 7.5 8.51/3/2002 8:56 AM 12.4 226 7.7 9.41/10/2002 8:47 AM 11.5 332 7.6 8.91/17/2002 8:02 AM 8.1 555 7.8 10.41/24/2002 12:03 PM 8.0 713 7.5 10.51/31/2002 11:27 AM 7.4 609 7.9 11.92/7/2002 8:28 AM 10.4 883 7.9 11.72/14/2002 8:24 AM 12.1 867 7.6 10.12/21/2002 10:15 AM 14.0 826 8.0 11.42/28/2002 1:48 PM 16.8 1320 8.2 11.63/7/2002 8:30 AM 15.2 1360 8.2 12.0
16
A2: 541MER522 – SJR @ Lander Avenue continued…
Date TimeTemp (ºC)
Field SC (umhos) pH
Dissolved Oxygen (mg/L)
Turbidity (ntu)
3/14/2002 11:22 AM 13.7 1820 8.0 12.23/21/2002 11:19 AM 15.1 1840 7.7 11.63/28/2002 12:44 PM 18.0 1880 8.2 15.94/4/2002 8:28 AM 19.8 1820 7.9 9.94/11/2002 8:51 AM 18.9 1820 7.9 9.54/18/2002 7:03 AM 16.8 1570 8.1 9.14/24/2002 11:17 AM 20.4 2100 8.3 12.85/2/2002 7:57 AM 18.1 1850 8.2 11.25/9/2002 8:57 AM 20.3 1610 8.2 14.15/16/2002 9:03 AM 21.9 1740 8.6 13.7 22.85/23/2002 6:45 AM 18.0 1860 7.9 NA5/30/2002 11:33 AM 26.2 2030 8.2 10.86/6/2002 7:40 AM 25.1 2030 7.9 NA6/13/2002 10:52 AM 25.2 1970 7.9 NA6/20/2002 11:07 AM 25.2 1960 8.3 7.8 28.76/27/2002 9:23 AM 25.0 1810 8.1 5.47/3/2002 9:45 AM 26.2 1670 8.3 NA7/11/2002 11:39 AM 27.7 1880 8.7 NA7/18/2002 8:45 AM 25.4 2010 8.5 8.9 21.57/25/2002 8:14 AM 24.8 1720 8.3 8.37/30/2002 10:59 AM 25.9 1360 9.0 19.1 35.18/1/2002 8:28 AM 24.9 1560 8.7 13.78/8/2002 9:43 AM 23.9 1510 8.9 15.48/15/2002 8:14 AM 24.7 1590 8.6 13.28/22/2002 8:36 AM 23.3 1510 8.3 10.18/29/2002 11:11 AM 25.0 1710 8.8 13.8 35.29/5/2002 8:15 AM 23.7 1690 7.8 4.79/12/2002 8:03 AM 22.8 1740 7.9 4.89/19/2002 8:36 AM 22.1 1910 7.9 7.5 NA9/26/2002 11:18 AM 23.5 2060 8.3 11.610/3/2002 8:58 AM 16.0 2080 8.2 8.9
10/10/2002 11:05 AM 20.9 2050 7.9 7.510/17/2002 11:43 AM 18.8 2070 8.1 11.1 18.810/24/2002 9:39 AM 16.4 1870 8.2 12.510/31/2002 11:50 AM 15.7 2200 8.2 11.3 34.511/7/2002 8:54 AM 13.6 2260 7.9 9.6
11/14/2002 9:30 AM 14.8 540 7.3 4.611/21/2002 8:29 AM 13.5 1040 7.1 6.1 20.811/26/2002 11:10 AM 13.6 1350 8.1 14.9
17
A2: 541MER522 – SJR @ Lander Avenue continued…
Date TimeTemp (ºC)
Field SC (umhos) pH
Dissolved Oxygen (mg/L)
Turbidity (ntu)
12/5/2002 8:49 AM 11.3 1640 7.7 11.4 42.712/12/2002 8:51 AM 11.0 1450 7.6 9.612/19/2002 11:17 AM 9.6 153 7.4 8.1 11412/24/2002 9:49 AM 7.8 251 7.7 11.41/2/2003 11:06 AM 9.6 311 8.1 14.11/9/2003 9:56 AM 10.1 658 8.0 10.61/16/2003 10:27 AM 10.9 402 7.8 8.9 49.31/23/2003 8:18 AM 11.8 926 6.5 10.01/30/2003 9:00 AM 13.0 872 7.5 7.5 38.22/6/2003 9:44 AM 10.2 1070 7.9 11.92/13/2003 10:54 AM 12.7 1280 7.9 13.4 19.82/20/2003 10:48 AM 12.9 1430 8.0 12.2 23.62/27/2003 8:15 AM 14.1 1470 7.5 9.63/6/2003 8:42 AM 14.2 1650 8.3 13.7 NA3/13/2003 8:39 AM 17.6 1730 7.9 12.8 18.03/20/2003 8:15 AM 15.8 2060 7.6 9.9 14.03/27/2003 1:17 PM 17.5 1830 8.6 21.8 34.14/3/2003 1:50 PM 18.0 2150 7.1 9.0 24.94/10/2003 8:15 AM 18.3 1970 8.3 14.3 20.74/17/2003 8:30 AM 17.3 1870 8.2 14.4 23.44/24/2003 8:50 AM 18.0 1350 8.3 13.8 22.25/1/2003 8:42 AM 18.4 1460 8.1 12.4 NA5/8/2003 8:07 AM 18.1 1550 8.0 14.2 33.45/15/2003 8:30 AM 20.9 1250 8.0 8.75/22/2003 8:52 AM 22.9 1510 7.9 8.1 20.85/29/2003 8:50 AM 25.3 1800 7.7 6.76/5/2003 8:31 AM 25.0 1940 7.7 7.0 42.16/12/2003 9:25 AM 23.4 2110 7.9 9.0 24.86/19/2003 8:33 AM 24.2 1620 7.9 3.7 26.86/26/2003 8:48 AM 24.6 1700 8.0 6.9 25.17/3/2003 8:25 AM 24.3 1600 8.3 11.77/10/2003 8:53 AM 25.0 1610 8.3 10.17/17/2003 8:48 AM 26.3 1490 8.8 11.47/24/2003 8:36 AM 27.5 1520 8.1 6.3 31.77/31/2003 8:38 AM 26.8 1410 8.2 7.5 30.98/7/2003 8:37 AM 24.1 1170 8.4 11.1 12.98/14/2003 8:16 AM 23.6 1450 8.3 12.48/21/2003 8:37 AM 25.0 1490 8.0 8.1 31.88/28/2003 8:38 AM 24.6 1620 8.2 NA 38.89/4/2003 8:35 AM 25.3 1680 7.9 7.8 35.89/11/2003 9:20 AM 22.7 1750 8.2 10.9 22.79/18/2003 8:31 AM 20.7 1790 8.3 10.8 20.29/25/2003 8:43 AM 22.4 1900 8.2 8.9 27.2
18
A2: 541MER522 – SJR @ Lander Avenue continued…
Date TimeTemp (ºC)
Field SC (umhos) pH
Dissolved Oxygen (mg/L)
Turbidity (ntu)
10/2/2003 9:01 AM 21.3 1890 8.1 9.5 24.210/9/2003 8:23 AM 20.7 1880 8.1 12.7 17.5
10/16/2003 10:46 AM 17.7 1950 8.2 14.3 19.310/23/2003 8:56 AM 19.3 2000 8.2 8.9 21.110/30/2003 8:37 AM 16.4 1970 8.2 9.4 16.011/6/2003 8:30 AM 13.5 1910 8.0 9.0 22.0
11/13/2003 8:11 AM 13.2 1510 8.0 9.1 20.611/20/2003 8:24 AM 13.1 928 7.8 8.9 14.611/26/2003 8:12 AM 8.7 916 7.9 11.1 20.812/4/2003 8:16 AM 11.6 961 8.3 9.3
12/11/2003 8:16 AM 11.5 966 7.4 9.6 NA12/18/2003 8:41 AM 8.5 664 7.9 11.5 NA12/23/2003 8:26 AM 10.9 820 7.1 9.6 NA12/30/2003 8:27 AM 9.3 605 7.6 10.9 NA1/8/2004 8:00 AM 9.5 648 7.8 8.7 NA1/15/2004 8:34 AM 10.3 1180 7.7 9.6 NA1/22/2004 8:36 AM 9.9 1320 7.5 12.2 42.61/29/2004 8:44 AM 10.9 1360 7.5 10.3 37.02/5/2004 8:31 AM 10.5 1250 7.8 11.1 59.92/12/2004 8:22 AM 11.8 1230 7.4 11.8 NA2/19/2004 8:28 AM 12.8 1430 7.4 10.3 NA2/26/2004 8:26 AM 12.0 627 7.9 9.5 NA3/4/2004 8:31 AM 12.2 491 7.9 10.0 1033/11/2004 8:37 AM 17.5 823 7.9 11.4 NA3/18/2004 7:56 AM 18.8 1300 8.6 13.33/25/2004 8:27 AM 18.4 1510 8.0 11.2 19.44/1/2004 8:31 AM 16.9 1650 7.8 8.64/8/2004 8:26 AM 18.2 1650 8.2 11.1 21.44/15/2004 8:40 AM 19.1 1860 8.2 13.3 26.14/22/2004 8:40 AM 17.7 1760 8.3 12.8 19.64/29/2004 9:41 AM 19.2 1660 8.3 NA 35.15/6/2004 8:42 AM 22.2 1730 8.0 15.4 27.05/13/2004 9:00 AM 20.8 1710 8.1 15.1 24.15/20/2004 8:39 AM 21.6 1830 7.6 6.2 23.75/27/2004 8:21 AM 23.2 1920 8.1 NA NA6/3/2004 9:15 AM 24.0 1750 8.3 14.2 25.66/10/2004 9:02 AM 22.2 1680 8.3 12.4 45.36/17/2004 9:03 AM 24.5 1770 8.3 12.6 23.36/24/2004 8:43 AM 24.2 1800 8.1 11.2 NA7/1/2004 8:43 AM 24.3 1660 8.0 7.7 NA
19
A2: 541MER522 – SJR @ Lander Avenue continued…
Date TimeTemp (ºC)
Field SC (umhos) pH
Dissolved Oxygen (mg/L)
Turbidity (ntu)
7/8/2004 8:36 AM 25.4 1560 7.9 9.2 NA7/15/2004 8:52 AM 24.8 1650 8.1 8.9 NA7/22/2004 10:33 AM 26.6 1330 8.2 12.3 NA7/29/2004 8:18 AM 26.1 1450 7.9 9.2 NA8/5/2004 8:05 AM 23.5 1520 7.2 3.4 NA8/12/2004 8:25 AM 25.8 1450 8.1 7.7 NA8/19/2004 10:38 AM 25.9 1360 8.2 9.8 NA8/26/2004 8:28 AM 24.1 1470 8.4 7.1 NA9/2/2004 8:10 AM 24.1 1510 7.9 7.3 NA9/9/2004 9:38 AM 24.1 1810 8.0 8.7 NA9/16/2004 10:19 AM 22.6 1790 8.1 8.8 NA9/23/2004 8:48 AM 19.7 1960 8.3 7.1 NA9/30/2004 8:23 AM 19.7 2040 7.3 9.8 NA10/7/2004 8:01 AM 20.5 2130 8.0 13.2
10/14/2004 8:19 AM 18.7 2210 8.2 11.710/21/2004 8:55 AM 15.8 2170 NA 9.710/28/2004 8:15 AM 14.1 927 7.6 6.911/4/2004 8:51 AM 13.3 879 7.7 5.4
11/11/2004 8:06 AM 14.4 792 6.5 8.011/18/2004 8:15 AM 13.6 415 7.6 5.611/23/2004 10:57 AM 10.0 656 7.5 8.912/2/2004 8:33 AM 8.0 1180 7.9 13.012/9/2004 8:15 AM 10.0 953 8.2 10.5
12/16/2004 8:07 AM 10.8 538 8.2 9.212/22/2004 11:07 AM 8.7 720 7.8 10.912/29/2004 9:33 AM 9.2 886 7.9 9.91/6/2005 7:44 AM 9.6 162 8.5 10.21/13/2005 8:30 AM 9.2 110 8.6 11.41/20/2005 8:27 AM 8.7 244 7.9 9.81/27/2005 8:08 AM 11.3 485 8.2 9.02/3/2005 8:29 AM 10.5 392 8.0 9.72/10/2005 7:59 AM 12.5 529 8.1 9.72/17/2005 8:38 AM 14.2 293 7.9 9.72/24/2005 8:08 AM 15.5 340 8.3 9.83/3/2005 8:16 AM 15.5 425 8.0 9.03/10/2005 8:59 AM 18.8 590 7.5 8.93/17/2005 8:10 AM 16.3 355 8.5 14.83/24/2005 8:12 AM 14.1 134 7.8 7.83/31/2005 8:17 AM 15.1 204 8.2 9.6
20
A2: 541MER522 – SJR @ Lander Avenue continued…
Date TimeTemp (ºC)
Field SC (umhos) pH
Dissolved Oxygen (mg/L)
Turbidity (ntu)
4/7/2005 8:23 AM 18.6 447 8.0 7.64/14/2005 8:19 AM 16.0 443 8.2 9.84/21/2005 8:14 AM 17.7 1180 8.3 11.74/28/2005 8:11 AM 18.9 1080 8.3 7.65/5/2005 8:37 AM 20.9 807 7.4 10.65/12/2005 8:14 AM 19.3 215 7.9 8.35/19/2005 8:37 AM 20.8 95 7.6 6.35/26/2005 8:31 AM 20.6 76 7.0 6.36/2/2005 8:27 AM 19.4 64 8.0 7.46/9/2005 7:58 AM 18.9 59 8.0 8.16/16/2005 8:14 AM 23.1 326 7.8 6.96/23/2005 8:58 AM 22.8 436 NA 7.56/30/2005 8:16 AM 25.4 183 8.2 6.87/7/2005 8:25 AM 25.6 833 7.9 NA7/13/2005 11:55 AM 29.8 719 7.9 11.57/21/2005 8:10 AM 26.7 1120 8.2 10.17/28/2005 8:26 AM 26.3 1240 8.0 8.08/4/2005 8:24 AM 26.0 814 7.7 5.88/11/2005 8:35 AM 25.5 1090 NA 7.08/18/2005 8:50 AM 24.9 631 7.3 5.98/25/2005 8:25 AM 24.3 762 7.8 6.79/1/2005 8:24 AM 22.5 996 7.6 8.69/8/2005 8:32 AM 22.6 897 7.9 6.89/15/2005 8:16 AM 20.0 1060 7.9 9.69/21/2005 8:17 AM 20.8 1100 8.1 8.79/22/2005 8:52 AM 21.8 1150 7.8 10.39/29/2005 8:16 AM 20.6 659 7.9 6.6
Count 265 265 261 217 60Min 7.4 59 6.5 3.4 12.9Max 30.0 2260 9.0 23.3 114Mean 18.1 1270 7.9 10.2 29.9Geo Mean 17.0 1080 7.9 9.8 27.1Median 18.4 1360 7.9 9.7 24.5Quartile 1 12.9 867 7.7 8.5 20.8Quartile 3 23.6 1720 8.2 11.6 34.7NOTE: For values reported as < (less than), half the detection limit was used.
NA = Data not applicableINA = Site was inaccessibleDRY = Site had no flow
21
A2: 541MER522 – SJR @ Lander Avenue continued…
DateTSS
(mg/L)TOC
(mg/L)Total Coli
MPNE. coli MPN
10/5/2000 2710/12/2000 24 7.510/19/2000 3.110/26/2000 41 2.711/2/2000 57 4.611/9/2000 28 3.4
11/16/2000 18 3.911/21/2000 27 NA11/30/2000 28 1.812/7/2000 25 1.7
12/12/2000 22 2.912/21/2000 NA 4.412/28/2000 NA 4.31/4/2001 20 3.81/11/2001 34 4.31/18/2001 32 6.01/25/2001 29 3.72/1/2001 38 6.82/8/2001 30 5.62/10/2001 25 5.32/11/2001 23 4.92/15/2001 42 3.32/22/2001 33 5.73/1/2001 37 9.33/8/2001 73 113/15/2001 46 9.23/22/2001 25 9.33/29/2001 NA <14/5/2001 30 NA4/12/2001 38 6.74/19/2001 39 104/26/2001 6.85/3/2001 36 8.45/10/2001 24 6.45/17/2001 9.35/24/2001 31 7.95/31/2001 41 126/7/2001 50 206/14/2001 35 156/21/2001 NA 186/28/2001 37 127/5/2001 137/11/2001 16
22
A2: 541MER522 – SJR @ Lander Avenue continued…
DateTSS
(mg/L)TOC
(mg/L)Total Coli
MPNE. coli MPN
7/19/2001 137/26/2001 128/2/2001 138/9/2001 128/16/2001 33 148/23/2001 37 148/30/2001 36 179/6/2001 42 159/13/2001 32 149/20/2001 NA9/27/2001 2410/4/2001 NA 19
10/11/2001 22 2310/18/2001 23 2711/1/2001 2611/8/2001 30
11/15/2001 29 5.511/20/2001 22 NA11/29/2001 20 <112/6/2001 43 7.2
12/13/2001 22 3.012/20/2001 30 6.712/27/2001 201/3/2002 541/10/2002 421/17/2002 371/24/2002 321/31/2002 24 3.82/7/2002 27 NA2/14/2002 25 NA2/21/2002 302/28/2002 NA3/7/2002 20 5.83/14/2002 25 7.43/21/2002 16 5.93/28/2002 19 NA4/4/2002 27 NA4/11/2002 914/18/2002 30 8.34/24/2002 22 14
23
A2: 541MER522 – SJR @ Lander Avenue continued…
DateTSS
(mg/L)TOC
(mg/L)Total Coli
MPNE. coli MPN
5/2/2002 22 6.15/9/2002 52 NA5/16/2002 31 NA5/23/2002 41 NA5/30/2002 19 6.06/6/2002 29 9.36/13/2002 NA NA6/20/2002 NA 6.66/27/2002 21 167/30/2002 >2419.68/15/2002 7.68/22/2002 7.78/29/2002 459/5/2002 5.59/12/2002 30 NA9/19/2002 29 NA9/26/2002 32 9.510/3/2002 34 7.7
10/10/2002 32 5.710/17/2002 18 5.9 >2419.6 2510/24/2002 28 5.010/31/2002 26 NA11/7/2002 26 NA
11/14/2002 29 7.411/21/2002 17 5.011/26/2002 24 5.512/5/2002 21 4.3
12/12/2002 15 3.412/19/2002 68 9.812/24/2002 371/2/2003 341/9/2003 281/16/2003 49 >2419.6 681/23/2003 311/30/2003 322/6/2003 182/13/2003 232/20/2003 152/27/2003 203/6/2003 25
24
A2: 541MER522 – SJR @ Lander Avenue continued…
DateTSS
(mg/L)TOC
(mg/L)Total Coli
MPNE. coli MPN
3/13/2003 NA 8.33/20/2003 NA 5.73/27/2003 54 4.84/3/2003 NA4/10/2003 NA 5.04/17/2003 32 8.14/24/2003 46 8.6 >2419.6 575/1/2003 31 9.65/8/2003 NA 9.25/15/2003 37 8.75/22/2003 20 6.15/29/2003 24 8.96/5/2003 31 146/12/2003 30 9.46/19/2003 30 106/26/2003 29 8.87/31/2003 >2419.6 248/28/2003 >2419.6 229/25/2003 >2419.6 11
10/30/2003 >2419.6 711/20/2003 >2419.6 281/29/2004 1553 172/26/2004 >2419.6 4883/11/2004 123/18/2004 9.43/25/2004 1986 154/1/2004 114/8/2004 144/15/2004 124/22/2004 124/29/2004 16 >2419.6 2615/6/2004 145/13/2004 125/20/2004 125/27/2004 12 >2419.6 1126/3/2004 166/10/2004 166/17/2004 13 >2419.6 61
25
A2: 541MER522 – SJR @ Lander Avenue continued…
DateTSS
(mg/L)TOC
(mg/L)Total Coli
MPNE. coli MPN
6/24/2004 >2419.6 1057/1/2004 167/8/2004 13 >2419.6 3877/15/2004 127/22/2004 137/29/2004 12 >2419.6 468/5/2004 9.58/12/2004 12 >2419.6 648/19/2004 118/26/2004 >2419.6 169/16/2004 >2419.6 229/30/2004 >2419.6 19
10/14/2004 >2419.6 1510/28/2004 17 8.2 >2419.6 4411/4/2004 19 9.8 1011 96
11/11/2004 18 8.811/18/2004 17 12 >2419.6 8411/23/2004 8.912/2/2004 23 9.512/9/2004 18 7.7 >2419.6 41
12/16/2004 21 6.912/22/2004 19 7.5 1733 3312/29/2004 26 6.71/6/2005 33 13 >2419.6 6491/13/2005 42 121/20/2005 27 >2419.6 501/27/2005 42 102/3/2005 26 12 >2419.6 752/10/2005 36 8.72/17/2005 57 15 >2419.6 >2419.62/24/2005 34 8.23/3/2005 33 113/10/2005 22 NA 816 403/17/2005 31 9.53/24/2005 130 11 >2419.6 >2419.63/31/2005 32 8.04/7/2005 27 9.2 >2419.6 1944/14/2005 32 NA4/21/2005 40 7.8 >2419.6 744/28/2005 48 NA5/5/2005 NA 6.6 >2419.6 77
26
27
DateTSS
(mg/L)TOC
(mg/L)Total Coli
MPNE. coli MPN
5/12/2005 47 8.85/19/2005 62 5.2 >2419.6 4885/26/2005 33 3.76/2/2005 36 2.06/9/2005 31 NA >2419.6 1166/16/2005 37 5.16/23/2005 40 6.3 >2419.6 1616/30/2005 35 3.27/7/2005 60 4.5 >2419.6 267/13/2005 19 4.77/21/2005 30 6.2 >2419.6 107/28/2005 28 6.38/4/2005 43 5.7 >2419.6 498/11/2005 NA 4.78/18/2005 36 5.1 >2419.6 81
C
A2: 541MER522 – SJR @ Lander Avenue continued…
8/25/2005 37 4.79/1/2005 26 4.4 >2419.6 99/8/2005 34 6.6 >2419.6 229/15/2005 35 5.59/21/2005 >2419.6 169/22/2005 37 NA9/29/2005 32 5.4
ount 158 162 47 46Min 15 0.5 816 7Max 130 27 2420 2420Mean 32 8.7 NA NAGeo Mean 30 8 2273 59Median 30 8.2 2420 50Quartile 1 24 5.5 2420 22Quartile 3 37 12 2420 103
OTE: For values reported as < (less than), half the detection limit was used For values reported as > (greater than), 2420 was used
A = Data not applicableINA = Site was inaccessible
RY = Site had no flow
N
N
D
A2: 541MER522 – SJR @ Lander Avenue continued…
DateNitrate (mg/L)
Nitrate-N (mg/L)
TKN (mg/L)
Ammonia-N (mg/L)
Phosphorus (mg/L)
Ortho-phosphate-
P (mg/L)
Potassium (mg/L)
BOD 5-Day (mg/L)
BOD 10-Day (mg/L)
10/12/2000 6.5 10.310/26/2000 <2 <2 0.3 <1 6.5 6.7 10.911/16/2000 2.7 3.911/30/2000 <2 <2 0.2 <1 7.1 4.0 6.912/12/2000 3.5 5.712/28/2000 4.3 <2 0.3 <1 8.8 5.9 8.41/11/2001 5.3 11.21/25/2001 NA NA 0.4 <1 9.6 3.5 7.12/8/2001 7.2 <2 0.4 <1 10 3.1 5.22/10/2001 7.3 <2 0.4 <1 10 2.2 5.02/11/2001 7.5 <2 0.4 <1 102/22/2001 3.9 <2 NA <1 7.6 2.7 4.73/15/2001 9.9 <2 0.4 <1 7.1 3.4 5.83/29/2001 16 NA 0.3 <1 8.8 8.1 16.14/19/2001 2.2 <2 0.2 <1 7.7 8.7 14.94/26/2001 8.4 <2 0.3 <1 6.9 7.0 11.95/17/2001 <2 2.3 0.2 <1 8.4 8.8 15.75/31/2001 <2 3.9 0.4 <1 9 8.2 16.66/7/2001 <2 <1.0 0.5 <1 7.1 8.2 15.56/14/2001 <2 2.5 <1 8.6 7.6 15.96/21/2001 <2 3.5 0.3 <1 8.8 8.3 16.76/28/2001 <2 <2 0.4 <1 8.6 8.0 16.58/16/2001 5.6 3.2 0.3 <1 7.18/30/2001 <2 <2 0.2 <1 8.19/27/2001 <2 <2 0.2 <1 7.8
10/25/2001 <2 <2 0.2 <1 6.5 4.6 7.811/29/2001 NA NA NA <0.03 NA 3.0 4.912/13/2001 1.8 3.912/27/2001 2.4 5.4
28
A2: 541MER522 – SJR @ Lander Avenue continued…
DateNitrate (mg/L)
Nitrate-N (mg/L)
TKN (mg/L)
Ammonia-N (mg/L)
Phosphorus (mg/L)
Ortho-phosphate-
P (mg/L)
Potassium (mg/L)
BOD 5-Day (mg/L)
BOD 10-Day (mg/L)
1/17/2002 1.6 3.11/31/2002 2.4 4.42/14/2002 3.0 4.92/28/2002 5.1 7.33/14/2002 9.2 13.93/28/2002 NA 1.8 0.2 NA 5.4 6.7 9.64/24/2002 8.8 13.45/16/2002 8.6 14.45/30/2002 7.8 11.96/13/2002 <2.0 NA 0.3 <1.0 8.8 7.0 10.96/20/2002 6.6 11.58/29/2002 8.7 17.29/26/2002 8.3 15.6
10/31/2002 7.2 11.011/21/2002 3.1 6.412/19/2002 5.6 8.51/30/2003 2.0 3.7
Count 22 NA 21 NA 22 24 24 42 42Min 1.0 NA 0.5 NA 0.2 0.0 5.4 1.6 3.1Max 16.0 NA 3.9 NA 0.5 0.5 10.0 9.2 17.2Mean 3.8 NA 1.5 NA 0.3 0.5 8.1 5.6 9.9Geo Mean 2.3 NA 1.3 NA 0.3 0.4 8.0 5.0 8.8Median 1.0 NA 1.0 NA 0.3 0.5 8.3 6.2 10.0Quartile 1 1.0 NA 1.0 NA 0.2 0.5 7.1 3.1 5.5Quartile 3 6.8 NA 1.8 NA 0.4 0.5 8.8 8.1 14.3NOTE: For values reported as < (less than), half the detection limit was used.
NA = Data not applicableINA = Site was inaccessibleDRY = Site had no flow
29
A2: 541MER522 – SJR @ Lander Avenue continued…
DateHardness
(mg/L)
Total Arsenic (ug/L)
Total Cadmium
(ug/L)
Total Chromium
(ug/L)
Total Copper (ug/L)
Total Lead (ug/L)
Total Nickel (ug/L)
Total Zinc (ug/L)
Total Mercury (ug/L)
10/26/2000 1.2 2.4 <5 <511/30/2000 240 <1 1.5 <5 <5 3.512/28/2000 230 <1 1.9 <5 <5 <21/25/2001 240 1.6 3.2 <5 <5 4.62/10/2001 240 <1 2.6 <5 <5 5.72/11/2001 240 <1 2.4 <5 <5 3.52/22/2001 220 1.2 3.4 <5 <5 5.43/29/2001 430 <1 2.4 <5 <5 3.64/26/2001 190 <1 3.2 <5 <5 3.75/31/2001 290 1.4 2.1 <5 <5 3.66/7/2001 320 13 <1 1.6 3.1 <5 <5 <2 <0.26/14/2001 300 10 <1 <1 2.1 <5 <5 3.9 <0.26/21/2001 NA 8.2 <1 <1 1.8 <5 <5 3 <0.26/28/2001 270 12 <1 <1 1.5 <5 <5 2.5 <0.27/26/2001 NA NA <1 1.6 <5 <5 NA NA8/30/2001 180 8.6 <1 <1 1.2 <5 <5 <29/27/2001 230 11 <0.1 <1 1.5 <5 <5 2.2 <0.2
10/25/2001 180 6.9 <0.1 <1 1.2 <5 <5 <2 NA11/29/2001 200 4.9 <0.1 <1 <1 <5 <5 3.5 <0.212/27/2001 4.7 <0.1 2.4 3.5 <5 <5 6.1 <0.22/28/2002 <4.0 <0.1 <1.0 2.8 <5.0 <5.0 6.1 <0.23/28/2002 5 <0.1 3 <1.0 <5.0 NA 4.3 <0.24/24/2002 6.8 <0.1 <1.0 <1.0 <5.0 <5.0 <2.0 <0.25/30/2002 12 <0.1 <1.0 1.3 <5.0 <5.0 <2.0 <0.26/20/2002 300 11 <0.1 <1.0 <1.0 <5.0 <5.0 <2.0 <0.29/26/2002 230 8.6 <0.1 <1.0 1.4 <5.0 <5.0 <2.0 <0.2
10/31/2002 250 7.2 <0.1 <1.0 <1.0 <5.0 <5.0 <2.0 <0.211/21/2002 160 6.2 <0.1 <1.0 1.4 <5.0 <5.0 2.1 <0.2
30
A2: 541MER522 – SJR @ Lander Avenue continued…
DateHardness
(mg/L)
Total Arsenic (ug/L)
Total Cadmium
(ug/L)
Total Chromium
(ug/L)
Total Copper (ug/L)
Total Lead (ug/L)
Total Nickel (ug/L)
Total Zinc (ug/L)
Total Mercury (ug/L)
3/27/2003 370 6.7 <0.1 1.1 2.4 <5.0 <5.0 3.1 <0.24/24/2003 260 7 <0.1 NA NA NA <5.0 <2.0 <0.25/29/2003 340 12 <0.1 <1.0 2.2 <5.0 <5.0 <2.0 <0.26/26/2003 290 12 <0.1 <1.0 <1.0 <5.0 <5.0 <2.0 <0.2
Count 24 21 21 31 31 31 31 30 19Min 160 2.0 0.1 0.5 0.5 2.5 2.5 1.0 0.1Max 430 13.0 0.5 3.0 3.5 2.5 2.5 6.1 0.1Mean 258 8.4 0.2 0.8 1.8 2.5 2.5 2.7 0.1Geo Mean 251 7.7 0.1 0.7 1.6 2.5 2.5 2.2 0.1Median 240 8.2 0.1 0.5 1.8 2.5 2.5 2.8 0.1Quartile 1 228 6.7 0.1 0.5 1.3 2.5 2.5 1.0 0.1Quartile 3 293 11.0 0.1 0.8 2.4 2.5 2.5 3.7 0.1NOTE: For values reported as < (less than), half the detection limit was used.
NA = Data not applicableINA = Site was inaccessibleDRY = Site had no flow
31
A2: 541MER522 – SJR @ Lander Avenue continued…
DateHardness
(mg/L)
Dissolved Arsenic (ug/L)
Dissolved Cadmium
(ug/L)
Dissolved Chromium
(ug/L)
Dissolved Copper (ug/L)
Dissolved Lead (ug/L)
Dissolved Nickel (ug/L)
Dissolved Zinc
(ug/L)
Dissolved Mercury (ug/L)
10/26/2000 <1 <1 <5 <5 <211/30/2000 240 <1 <1 <5 <5 <212/28/2000 230 <1 <1 <5 <5 <21/25/2001 240 <1 <1 <5 <5 <22/10/2001 240 <1 1.5 <5 <5 2.72/11/2001 240 <1 1.4 <5 <5 <22/22/2001 220 <1 <1 <5 <5 <23/29/2001 430 <1 1.6 <5 <5 <24/26/2001 190 <1 1.4 <5 <5 <25/31/2001 290 <1 <1 <5 <5 <26/7/2001 320 11 <1 <1 2.3 <5 <5 <2 <0.26/14/2001 300 8.8 <1 <1 <1 <5 <5 <2 <0.26/21/2001 NA 6.5 <1 <1 <1 <5 <5 <2 <0.26/28/2001 270 8.7 <1 <1 <1 <5 <5 <2 <0.27/26/2001 NA NA NA NA NA NA NA NA8/30/2001 180 8 <1 <1 1.2 <5 <5 <29/27/2001 230 9.1 <0.1 <1 1.1 <5 <5 <2 <0.2
10/25/2001 180 4.7 <0.1 <1 <1 <5 <5 <2 NA11/29/2001 200 <4 <0.1 <1 <1 <5 <5 7.8 <0.212/27/2001 <4 <0.1 <1 1.6 <5 <5 2.3 <0.22/28/2002 <4.0 <0.1 <1.0 3 <5.0 <5.0 5.3 <0.23/28/2002 <4.0 <0.1 <1.0 <1.0 <5.0 <5.0 2.7 <0.24/24/2002 8 <0.1 <1.0 1.1 <5.0 <5.0 <2.0 <0.25/30/2002 11 <0.1 <1.0 1.1 <5.0 <5.0 <2.0 <0.26/20/2002 300 6.8 <0.1 <1.0 <1.0 <5.0 <5.0 <2.0 <0.29/26/2002 230 6.1 <0.1 <1.0 <1.0 <5.0 <5.0 <2.0 <0.2
10/31/2002 250 6.8 <0.1 <1.0 <1.0 <5.0 <5.0 <2.0 <0.211/21/2002 160 4.8 <0.1 <1.0 1.2 <5.0 <5.0 <2.0 <0.2
32
A2: 541MER522 – SJR @ Lander Avenue continued…
DateHardness
(mg/L)
Dissolved Arsenic (ug/L)
Dissolved Cadmium
(ug/L)
Dissolved Chromium
(ug/L)
Dissolved Copper (ug/L)
Dissolved Lead (ug/L)
Dissolved Nickel (ug/L)
Dissolved Zinc
(ug/L)
Dissolved Mercury (ug/L)
Count 20 17 17 27 27 27 27 27 15Min 160.0 2.0 0.1 0.5 0.5 2.5 2.5 1.0 0.1Max 430.0 11.0 0.5 0.5 3.0 2.5 2.5 7.8 0.1Mean 247.0 6.4 0.2 0.5 1.0 2.5 2.5 1.6 0.1Geo Mean 240.6 5.5 0.1 0.5 0.8 2.5 2.5 1.3 0.1Median 240.0 6.8 0.1 0.5 0.5 2.5 2.5 1.0 0.1Quartile 1 215.0 4.7 0.1 0.5 0.5 2.5 2.5 1.0 0.1Quartile 3 275.0 8.7 0.5 0.5 1.3 2.5 2.5 1.0 0.1NOTE: For values reported as < (less than), half the detection limit was used.
NA = Data not applicableINA = Site was inaccessibleDRY = Site had no flow
33
A2: 541MER522 – SJR @ Lander Avenue continued…
DateChloride (mg/L)
Sulfate (mg/L)
Calcium (mg/L)
Magnesium (mg/L)
TDS (mg/L)
Carbonate (mg/L)
Bicarbonate (mg/L)
Total Alkalinity
(mg/L)Sodium (mg/L)
11/30/2000 250 91 59 23 810 <1 270 220 21012/28/2000 220 86 56 22 740 <1 260 210 1801/25/2001 220 85 57 23 720 <1 240 190 1702/10/2001 190 78 57 23 660 <1 250 200 1502/11/2001 200 78 58 23 530 <1 250 210 1602/22/2001 170 79 52 22 620 <1 220 180 1303/29/2001 340 210 96 46 1200 13 230 210 2404/26/2001 120 77 43 19 520 <1 130 130 955/31/2001 370 150 62 33 1000 <1 210 210 2706/7/2001 390 170 67 36 1100 <1 290 230 3206/14/2001 320 160 60 36 950 <1 220 180 2406/21/2001 280 150 52 31 930 <1 220 180 2306/28/2001 340 150 54 32 1000 <1.0 250 210 2808/30/2001 220 100 38 22 730 <1 200 170 1909/27/2001 310 98 57 22 950 <1 300 260 270
10/25/2001 180 62 44 16 NA <1 250 200 16011/29/2001 240 88 50 18 790 <1 230 190 2003/27/2003 86 384/24/2003 240 120 60 285/29/2003 170 94 74 37
34
35
A2: 541MER522 – SJR @ Lander Avenue continued…
DateChloride (mg/L)
Sulfate (mg/L)
Calcium (mg/L)
Magnesium (mg/L)
TDS (mg/L)
Carbonate (mg/L)
Bicarbonate (mg/L)
Total Alkalinity
(mg/L)Sodium (mg/L)
6/26/2003 330 140 63 32
Count 20 20 21 21 16 17 17 17 17Min 120 62 38 16 520 0.5 130 130 95Max 390 210 96 46 1200 13 300 260 320Mean 260 110 59 28 830 1.2 240 200 200Geo Mean 240 100 58 27 810 0.6 230 200 200Median 240 96 57 23 800 0.5 240 200 200Quartile 1 200 84 52 22 710 0.5 220 180 160Quartile 3 320 150 62 33 970 0.5 250 210 240NOTE: For values reported as < (less than), half the detection limit was used.
NA = Data not applicableINA = Site was inaccessibleDRY = Site had no flow
A2: 541MER522 – SJR @ Lander Avenue continued…
Date Result Control Result Control
Result (million/m
l)
Control (million/
ml) MDD(%)10/26/2000 100 100 NA NA1/25/2001 90 100 100 1002/22/2001 100 100 100 1003/29/2001 95 100 100 1004/26/2001 95 100 90 905/31/2001 100 90 100 1006/28/2001 90 100 100 100
10/25/2001 100 100 100 10011/29/2001 NA NA 100 10012/27/2001 95 100 100 1001/31/2002 100 100 100 1002/28/2002 100 100 100 1004/24/2002 100 100 100 905/30/2002 100 100 100 1006/20/2002 100 100 100 1008/29/2002 95 100 100 1009/26/2002 100 95 100 100
10/31/2002 100 100 100 10011/21/2002 95 100 100 10012/19/2002 100 100 100 100 2.71* 2.93 N/A3/27/2003 100 100 100 100 3.17** 1.73 N/A5/29/2003 100 100 100 100 6.53** 2.03 7.5
Count 21 21 21 21 3 3 1
* Significantly reduced from the lab control.** Significantly greater than the lab control.^ Fish were from a "forced hatch," duplicate failed QA.1 Duplicate sample for the set was low - 77% recovery.
3 Samples qualified, but duplicate sample recovery for the set was high - 126% (53.8%/42.5%)NA = Data not applicableINA = Site was inaccessibleDRY = Site had no flow
2 Testing for the Fathead minnow was initiated when samples were approx. 48h old due to untimely shipping of fish by fish supplier.
96h Acute Fathead Minnow
(% Survival)
48h Acute Ceriodaphnia Dubia
(% Survival) Algae Cell Growth
36
A2: 541MER522 – SJR @ Lander Avenue continued…
DateResult
(% Survival)
Control (%
Survival)
Avg Dry Weight Result (mg)
Avg Dry Weight Control
(mg)Growth MDD(%)
Result (% Survival)
Control (%
Survival)
Avg # Young /
Adult Result
Avg # Young /
Adult Control
Repro MDD(%)
3/11/2004 86.7 97.5 0.55 0.60 46 100.0 100.0 18.3 20 283/25/2004 100.0 97.5 0.64 0.68 9 100.0 100.0 21.9 20.9 234/15/2004 93.3 97.5 0.56 0.59 10 100.0 100.0 21.6 21.8 144/29/2004 90.0 100.0 0.50* 0.62 12 100.0 100.0 25.7 20 145/13/2004 87.1* 100.0 0.57 0.68 16 100.0 100.0 22.9 17.3 25
05/27/2004^ N/A N/A N/A N/A N/A N/A N/A N/A N/A N/A6/10/2004 70.0* 97.6 0.46 0.58 62 100.0 100.0 25.9 25.2 136/24/2004 100.0 100.0 0.6 0.67 23 100.0 100.0 38 21.1 18
11/18/2004 90.0 100.0 0.45 0.46 1912/22/2004 85.0 95.2 0.51 0.61 191/20/2005 87.5 97.4 0.74* 0.92 152/17/2005 72.5* 97.5 0.22* 0.38 233/24/2005 82.1* 97.5 0.43 0.41 204/21/2005 N/A N/A N/A N/A N/A5/19/2005 80.0* 100.0 0.51* 0.62 166/23/2005 N/A N/A N/A N/A N/A9/22/2005 94.7 97.5 0.41 0.45 10
Count 14 14 14 14 14 7 7 7 7 7
* Significantly reduced from the lab control.** Significantly greater than the lab control.^ Fish were from a "forced hatch," duplicate failed QA.1 Duplicate sample for the set was low - 77% recovery.
3 Samples qualified, but duplicate sample recovery for the set was high - 126% (53.8%/42.5%)NA = Data not applicableINA = Site was inaccessibleDRY = Site had no flow
2 Testing for the Fathead minnow was initiated when samples were approx. 48h old due to untimely shipping of fish by fish supplier.
Chronic Ceriodaphnia Dubia - 6 dayChronic Fathead Minnow - 7day
37
A3: 541MER538 – SJR @ Fremont Ford Station Code:541MER538
Location: Latitude 37.30944, Longitude -120.92917
Date TimeTemp (ºC)
Field SC (umhos) pH
Dissolved Oxygen (mg/L)
Turbidity (ntu)
10/5/2000 9:40 AM 18.8 1380 6.310/12/2000 10:30 AM 15.7 897 7.310/19/2000 8:15 AM 16.2 1160 7.210/26/2000 11:30 AM 13.7 1390 7.511/2/2000 9:20 AM 14.2 654 6.311/9/2000 8:50 AM 12.1 1240 7.8
11/16/2000 9:55 AM 10.1 1570 7.411/21/2000 7:20 AM 8.8 1700 7.211/30/2000 9:45 AM 9.4 1750 7.412/7/2000 8:40 AM 9.3 1560 7.1
12/12/2000 8:30 AM 10.6 1530 7.412/21/2000 10:40 AM 8.9 1850 7.712/28/2000 11:10 AM 7.6 1910 7.21/4/2001 8:35 AM 7.5 2030 6.91/11/2001 10:30 AM 8.7 1300 7.61/18/2001 8:35 AM 6.2 1680 8.01/25/2001 12:05 PM 9.9 1850 7.32/1/2001 10:07 AM 8.1 1610 7.62/8/2001 9:20 AM 8.9 1720 7.62/15/2001 10:30 AM 9.7 1210 7.32/22/2001 12:40 PM 14.6 1620 7.83/1/2001 10:50 AM 12.7 1160 7.03/8/2001 9:00 AM 13.9 551 7.63/15/2001 10:35 AM 15.8 1370 7.53/22/2001 11:00 AM 19.3 1830 7.73/29/2001 11:30 AM 19.1 1680 8.14/5/2001 11:30 AM 15.7 1830 8.04/12/2001 9:15 AM 13.2 1510 6.94/19/2001 11:20 AM 16.8 2090 7.84/26/2001 9:48 AM 21.7 1230 7.45/3/2001 9:00 AM 17.5 2100 7.05/10/2001 10:36 AM 23.7 1440 7.65/17/2001 11:13 AM 22.4 1170 7.05/24/2001 12:30 PM 26.8 1690 6.85/31/2001 12:05 PM 27.5 1670 7.66/7/2001 11:20 AM 23.1 1390 7.9 7.06/14/2001 NA 22.2 1480 7.8 9.06/21/2001 11:13 AM 26.8 1220 7.8 8.46/28/2001 2:58 PM 26.0 1020 8.1 6.9
38
A3: 541MER538 – SJR @ Fremont Ford continued…
Date TimeTemp (ºC)
Field SC (umhos) pH
Dissolved Oxygen (mg/L)
Turbidity (ntu)
7/5/2001 8:18 AM 25.3 1550 7.6 6.17/11/2001 10:26 AM 24.6 1180 7.7 7.97/19/2001 10:34 AM 23.7 1180 7.8 9.37/26/2001 10:08 AM 24.7 1230 7.7 7.78/2/2001 8:44 AM 26.6 1050 7.6 6.38/9/2001 10:38 AM 26.4 1320 7.7 7.38/16/2001 9:32 AM 23.3 1170 7.7 6.88/23/2001 10:36 AM 22.2 1100 7.7 8.58/30/2001 8:46 AM 22.2 1580 7.4 6.49/6/2001 10:21 AM 21.8 1890 7.6 8.09/13/2001 11:48 AM 22.2 2020 7.8 7.59/20/2001 11:08 AM 22.1 2130 7.8 7.59/27/2001 12:22 PM 21.8 2180 7.7 8.410/4/2001 8:00 AM 20.7 2190 7.5 7.2
10/11/2001 8:39 AM 16.8 1360 7.8 7.810/18/2001 8:30 AM 18.1 1250 7.7 7.410/25/2001 8:35 AM 14.2 1800 7.7 8.511/1/2001 8:50 AM 15.7 1760 7.8 8.611/8/2001 8:23 AM 13.7 1440 7.7 8.8
11/15/2001 8:50 AM 15.4 1240 8.1 8.011/20/2001 10:32 AM 13.6 1640 7.7 8.611/29/2001 9:25 AM 9.6 1790 7.6 10.212/6/2001 11:00 AM 10.2 1320 7.4 10.6
12/13/2001 8:38 AM 8.6 2110 7.7 10.212/20/2001 9:47 AM 9.7 2690 7.8 10.412/27/2001 1:00 PM 10.6 2430 7.7 7.51/3/2002 8:35 AM 12.7 583 7.6 8.11/10/2002 11:04 AM 11.7 1000 8.0 9.81/17/2002 10:42 AM 8.0 1540 7.6 10.91/24/2002 11:49 AM 7.7 1890 7.3 11.41/31/2002 10:30 AM 7.0 1760 7.7 12.52/7/2002 10:18 AM 10.5 1760 7.4 11.32/14/2002 10:47 AM 11.5 1740 7.8 9.82/21/2002 11:47 AM 14.3 1390 7.3 9.42/28/2002 2:29 PM 16.8 1650 7.8 11.43/7/2002 9:48 AM 14.8 1650 7.6 9.03/14/2002 11:10 AM 13.3 1850 7.43/21/2002 11:01 AM 14.9 1760 7.3 9.13/28/2002 2:00 PM 19.5 2730 7.8 15.54/4/2002 10:13 AM 18.9 1930 7.9 8.34/11/2002 9:32 AM 18.6 NA 7.2 NA
39
A3: 541MER538 – SJR @ Fremont Ford continued…
Date TimeTemp (ºC)
Field SC (umhos) pH
Dissolved Oxygen (mg/L)
Turbidity (ntu)
4/18/2002 9:30 AM 15.4 1990 7.8 8.94/25/2002 10:04 AM 19.5 2080 7.8 8.05/2/2002 9:37 AM 17.2 2000 7.3 10.45/9/2002 INA INA INA INA INA5/16/2002 8:42 AM 20.6 2330 7.8 6.9 74.15/23/2002 6:30 AM 16.9 1240 7.6 NA5/30/2002 11:57 AM 26.3 1950 7.8 7.66/6/2002 9:44 AM 24.7 1420 7.9 NA6/13/2002 10:34 AM 23.3 1340 7.2 NA6/20/2002 11:55 AM 25.0 1460 7.9 8.2 93.96/27/2002 8:57 AM 24.2 1110 7.7 6.07/3/2002 9:25 AM 25.1 1160 7.9 NA7/11/2002 11:25 AM 27.2 1300 7.9 NA7/18/2002 8:30 AM 23.5 1260 7.8 6.4 1097/25/2002 9:46 AM 23.9 1100 7.8 6.48/1/2002 10:51 AM 24.8 980 7.8 6.88/8/2002 9:23 AM 21.9 1160 7.8 6.98/15/2002 10:15 AM 24.4 1160 7.9 7.38/22/2002 10:05 AM 21.9 1200 7.8 8.08/29/2002 12:25 PM 24.3 1460 8.0 9.3 75.09/5/2002 9:50 AM 21.2 1250 7.8 7.59/12/2002 10:10 AM 21.8 1490 7.5 8.49/19/2002 8:18 AM 20.7 1820 7.8 6.5 NA9/26/2002 11:53 AM 21.9 1490 8.0 8.810/3/2002 8:39 AM 13.6 1550 7.8 9.9
10/10/2002 10:35 AM 19.6 1960 7.8 7.710/17/2002 12:25 PM 17.1 1470 7.8 9.0 96.810/24/2002 11:31 AM 15.2 1200 7.3 8.910/31/2002 9:08 AM 13.0 1450 7.4 8.8 96.611/7/2002 8:38 AM 13.3 1400 7.6 8.9
11/14/2002 10:51 AM 14.2 1210 7.5 8.311/21/2002 11:42 AM 12.8 1500 7.6 9.4 62.911/26/2002 10:55 AM 12.3 NA 7.7 9.312/5/2002 8:34 AM 10.3 1650 7.7 10.2 60.0
12/12/2002 8:40 AM 11.2 1850 7.6 10.212/19/2002 12:28 PM 9.8 713 7.5 7.7 12012/24/2002 11:04 AM 8.2 1000 6.9 12.51/2/2003 10:51 AM 9.8 1210 7.7 14.01/9/2003 9:38 AM 9.9 1780 7.9 11.21/16/2003 12:49 PM 11.5 1330 7.8 10.8 57.11/23/2003 9:40 AM 11.0 1810 7.2 14.2
40
A3: 541MER538 – SJR @ Fremont Ford continued…
Date TimeTemp (ºC)
Field SC (umhos) pH
Dissolved Oxygen (mg/L)
Turbidity (ntu)
1/30/2003 8:41 AM 12.8 2070 7.4 9.5 68.32/6/2003 9:28 AM 9.4 2450 7.7 11.22/13/2003 10:37 AM 12.3 2420 7.7 10.4 34.32/20/2003 10:30 AM 11.2 1470 7.9 11.0 96.42/27/2003 9:57 AM 13.1 1490 7.8 8.83/6/2003 11:44 AM 14.5 1680 7.9 11.7 NA3/13/2003 11:15 AM 17.5 1650 7.6 10.2 36.83/20/2003 9:45 AM 15.1 1780 7.5 9.3 46.63/27/2003 1:56 PM 17.6 1890 7.9 13.3 61.84/3/2003 12:12 PM 16.0 2020 7.3 8.8 52.34/10/2003 11:10 AM 19.2 2170 7.7 10.2 68.24/17/2003 10:07 AM 16.7 1780 7.5 8.7 60.74/24/2003 11:08 AM 17.3 2090 7.8 4.9 12.35/1/2003 10:30 AM 17.9 1910 7.6 8.0 NA5/8/2003 9:44 AM 16.8 1920 7.2 8.5 48.35/15/2003 10:11 AM 19.4 2460 7.7 10.15/22/2003 11:06 AM 23.6 1520 7.7 7.0 66.95/29/2003 8:35 AM 24.9 1440 7.7 6.86/5/2003 11:11 AM 25.2 1440 7.9 7.3 1376/12/2003 9:05 AM 20.7 1570 7.6 7.0 94.26/19/2003 11:08 AM 23.5 1550 7.9 6.4 98.16/26/2003 10:35 AM 24.1 1060 7.7 6.9 1147/3/2003 10:32 AM 24.5 1070 7.8 10.17/10/2003 10:24 AM 24.8 1180 7.8 7.77/17/2003 10:37 AM 26.8 1090 7.6 1.67/24/2003 10:14 AM 27.0 1080 7.8 6.9 NA7/31/2003 10:38 AM 26.1 1060 7.6 4.9 98.88/7/2003 10:03 AM 23.6 901 7.8 6.7 1368/14/2003 10:17 AM 23.3 1270 7.7 7.78/21/2003 9:51 AM 24.2 940 7.8 7.6 91.08/28/2003 10:26 AM 23.9 995 8.1 7.3 1769/4/2003 10:04 AM 24.6 1510 7.9 7.4 61.89/11/2003 12:29 PM 23.1 1680 8.1 10.0 39.29/18/2003 10:52 AM 19.0 2200 7.9 8.7 38.79/25/2003 11:10 AM 21.3 1690 8.0 9.2 63.010/2/2003 10:58 AM 19.7 1570 7.8 9.0 78.110/9/2003 10:19 AM 19.5 1240 7.6 10.5 100
10/16/2003 12:27 PM 17.9 1350 7.9 9.7 74.310/23/2003 11:34 AM 18.9 1350 7.8 8.8 12410/30/2003 9:52 AM 15.2 1560 7.5 10.1 80.211/6/2003 10:40 AM 13.2 1300 7.9 10.7 100
11/13/2003 9:25 AM 12.8 1580 7.7 9.1 59.8
41
A3: 541MER538 – SJR @ Fremont Ford continued…
Date TimeTemp (ºC)
Field SC (umhos) pH
Dissolved Oxygen (mg/L)
Turbidity (ntu)
11/20/2003 10:14 AM 13.4 1480 7.3 4.3 NA11/26/2003 9:28 AM 7.8 1560 7.8 11.3 4012/4/2003 10:05 AM 12.1 2000 8.0 11.3
12/11/2003 9:37 AM 11.3 2210 7.5 6.7 NA12/18/2003 10:27 AM 8.9 1780 8.2 10.8 NA12/23/2003 10:05 AM 10.9 1840 7.6 14.2 NA12/30/2003 10:45 AM 8.5 1520 7.6 12.7 NA1/8/2004 9:09 AM 8.4 1370 7.4 9.2 NA1/15/2004 10:39 AM 9.8 1730 7.8 9.3 NA1/22/2004 10:05 AM 9.3 1890 7.9 16.3 69.11/29/2004 10:51 AM 10.8 1880 7.8 11.4 NA2/5/2004 9:53 AM 9.9 1510 7.4 17.4 71.82/12/2004 10:06 AM 10.6 1900 7.5 12.5 NA2/19/2004 9:45 AM 12.4 1610 7.6 8.7 NA2/26/2004 10:29 AM 12.4 1300 7.5 9.0 NA3/4/2004 9:57 AM 12.5 1010 8.1 9.1 50.03/11/2004 10:37 AM 17.6 1490 7.9 8.3 NA3/18/2004 9:12 AM 19.1 1960 7.7 11.53/25/2004 11:00 AM 18.3 1910 8.0 9.7 53.04/1/2004 10:15 AM 16.3 2250 8.0 9.64/8/2004 10:38 AM 18.2 2110 7.8 8.1 65.04/15/2004 10:29 AM 17.9 2380 8.0 9.2 67.04/22/2004 10:44 AM 16.9 1930 7.9 11.0 96.14/29/2004 11:57 AM 19.2 2530 8.1 NA 36.35/6/2004 11:24 AM 22.9 1620 7.7 12.5 68.15/13/2004 11:06 AM 20.5 1560 7.8 18.5 54.55/20/2004 10:46 AM 20.9 1570 7.5 8.5 67.55/27/2004 10:15 AM 22.7 2150 7.8 NA NA6/3/2004 11:08 AM 24.4 1560 8.0 8.2 72.56/10/2004 10:54 AM 21.2 1040 7.9 8.3 1406/17/2004 11:30 AM 25.0 1390 7.9 8.2 79.26/24/2004 10:39 AM 23.7 1370 7.9 7.9 NA7/1/2004 10:36 AM 23.3 1510 7.5 9.9 NA7/8/2004 10:28 AM 24.8 1310 7.5 8.0 NA7/15/2004 10:49 AM 24.8 833 7.5 5.3 NA7/22/2004 10:14 AM 26.5 1130 7.9 8.4 NA7/29/2004 10:22 AM 24.8 1390 8.1 4.4 NA8/5/2004 9:52 AM 23.8 987 7.9 7.1 NA8/12/2004 10:43 AM 25.9 1210 8.1 8.1 NA8/19/2004 10:25 AM 25.5 1110 7.9 7.7 NA
42
A3: 541MER538 – SJR @ Fremont Ford continued…
Date TimeTemp (ºC)
Field SC (umhos) pH
Dissolved Oxygen (mg/L)
Turbidity (ntu)
8/26/2004 10:49 AM 23.3 1250 8.2 7.5 NA9/2/2004 10:14 AM 23.6 2050 7.5 7.6 NA9/9/2004 9:21 AM 23.1 1340 7.9 7.8 NA9/16/2004 10:02 AM 20.8 1310 7.8 7.5 NA9/23/2004 1:30 PM 22.4 1510 8.0 11.5 NA9/30/2004 10:40 AM 18.8 1660 7.9 8.6 NA10/7/2004 10:11 AM 19.3 1710 7.6 9.2
10/14/2004 9:41 AM 18.4 1500 7.4 3.010/21/2004 11:13 AM 15.6 938 NA 8.510/28/2004 10:07 AM 12.6 1080 7.8 11.611/4/2004 11:48 AM 12.8 1290 7.9 9.5
11/11/2004 9:44 AM 14.2 1450 7.2 8.211/18/2004 10:03 AM 13.5 1120 7.7 8.111/23/2004 10:35 AM 9.2 1310 7.8 10.312/2/2004 11:13 AM 7.3 1750 7.6 12.412/9/2004 9:52 AM 10.8 1740 7.9 10.9
12/16/2004 10:53 AM 11.0 1110 7.4 10.512/22/2004 12:43 PM 9.1 1610 7.9 10.812/29/2004 9:19 AM 9.5 1850 7.8 9.91/6/2005 9:07 AM 8.6 344 7.5 9.61/13/2005 11:03 AM 9.3 179 7.6 9.11/20/2005 10:22 AM 8.5 579 7.2 8.71/27/2005 10:14 AM 10.9 1170 7.3 10.32/3/2005 10:50 AM 10.9 954 7.2 8.52/10/2005 10:14 AM 12.6 1410 7.7 9.82/17/2005 10:41 AM 14.1 762 7.5 10.12/24/2005 10:38 AM 14.7 853 7.1 8.13/3/2005 9:35 AM 15.4 866 7.2 9.43/10/2005 11:49 AM 18.9 1350 7.9 9.93/17/2005 9:40 AM 16.5 1670 7.3 13.83/24/2005 10:30 AM 14.7 350 7.2 8.83/31/2005 10:11 AM 14.7 564 7.2 10.04/7/2005 10:50 AM 18.0 1170 7.0 8.04/14/2005 9:44 AM 15.6 1160 7.2 11.04/21/2005 10:31 AM 17.8 1580 7.3 11.24/28/2005 9:57 AM 18.4 1500 7.0 13.55/5/2005 10:54 AM 20.6 1350 7.2 9.05/12/2005 9:58 AM 19.9 551 7.2 7.8
43
A3: 541MER538 – SJR @ Fremont Ford continued…
Date TimeTemp (ºC)
Field SC (umhos) pH
Dissolved Oxygen (mg/L)
Turbidity (ntu)
5/19/2005 10:44 AM 20.9 171 7.0 6.55/26/2005 10:56 AM INA INA INA INA6/2/2005 INA INA INA INA INA6/9/2005 9:25 AM INA INA INA INA6/16/2005 10:26 AM 24.0 539 7.0 6.96/23/2005 11:15 AM 23.9 864 NA 7.56/30/2005 11:35 AM 25.9 394 7.3 8.47/7/2005 10:07 AM 25.6 1050 7.0 8.47/13/2005 9:30 AM 27.4 947 7.7 8.17/21/2005 9:50 AM 27.0 1220 7.8 7.47/28/2005 11:52 AM 27.2 1310 7.8 7.48/4/2005 10:03 AM 26.4 1120 7.7 7.48/11/2005 11:44 AM 26.5 1010 7.9 7.88/18/2005 10:35 AM 24.9 972 8.0 7.18/25/2005 10:39 AM 24.3 946 7.5 7.89/1/2005 10:09 AM 23.2 1010 7.9 10.29/8/2005 10:33 AM 22.4 1040 7.2 8.69/15/2005 10:13 AM 19.8 970 7.3 8.99/21/2005 8:29 AM 20.5 933 7.9 7.99/22/2005 11:15 AM 22.1 771 7.1 8.69/29/2005 10:14 AM 20.5 1090 7.4 7.8
Count 258 256 256 214 56Min 6.2 171 6.3 1.6 12.3Max 27.5 2730 8.2 18.5 176Mean 17.5 1462 7.6 9.0 76.7Geo Mean 17.2 1340 7.6 8.7 70.4Median 17.9 1465 7.7 8.7 68.7Quartile 1 12.6 1170 7.5 7.7 59.1Quartile 3 23.1 1760 7.8 10.1 96.5NOTE: For values reported as < (less than), half the detection limit was used.
NA = Data not applicableINA = Site was inaccessibleDRY = Site had no flow
44
A3: 541MER538 – SJR @ Fremont Ford continued…
DateTSS
(mg/L)TOC
(mg/L)Total Coli
MPNE. coli MPN
10/5/2000 9710/12/2000 160 6.210/19/2000 NA 2.410/26/2000 120 5.611/2/2000 95 5.311/9/2000 66 5
11/16/2000 53 311/21/2000 56 NA11/30/2000 39 3.112/7/2000 61 1.6
12/12/2000 64 2.712/21/2000 NA 4.612/28/2000 NA 4.51/4/2001 36 5.21/11/2001 98 5.51/18/2001 35 5.91/25/2001 63 7.62/1/2001 50 6.92/8/2001 54 6.52/15/2001 77 3.92/22/2001 67 9.13/1/2001 67 8.53/8/2001 68 113/15/2001 61 6.63/22/2001 82 3.63/29/2001 NA <14/5/2001 76 NA4/12/2001 86 7.54/19/2001 90 8.34/26/2001 6.15/3/2001 86 6.55/10/2001 130 5.95/17/2001 65/24/2001 87 5.95/31/2001 69 106/7/2001 110 146/14/2001 81 146/21/2001 NA 146/28/2001 180 9.97/5/2001 8.77/11/2001 8.17/19/2001 9
45
A3: 541MER538 – SJR @ Fremont Ford continued…
DateTSS
(mg/L)TOC
(mg/L)Total Coli
MPNE. coli MPN
7/26/2001 6.88/2/2001 6.68/9/2001 8.98/16/2001 88 9.18/23/2001 120 9.48/30/2001 65 129/6/2001 45 129/13/2001 50 149/20/2001 NA 169/27/2001 73 1610/4/2001 NA 14
10/11/2001 41 1510/18/2001 66 2210/25/2001 2011/1/2001 4211/8/2001 86
11/15/2001 58 8.211/20/2001 63 NA11/29/2001 46 <112/6/2001 66 6
12/13/2001 39 412/20/2001 50 1112/27/2001 371/3/2002 761/10/2002 621/17/2002 431/24/2002 371/31/2002 32 NA2/7/2002 54 NA2/14/2002 62 NA2/21/2002 1002/28/2002 NA3/7/2002 110 9.93/14/2002 81 7.73/21/2002 74 7.63/28/2002 37 NA4/4/2002 86 NA4/11/2002 624/18/2002 42 7.84/25/2002 97 NA5/2/2002 63 6.85/16/2002 61 NA5/23/2002 110 NA
46
A3: 541MER538 – SJR @ Fremont Ford continued…
DateTSS
(mg/L)TOC
(mg/L)Total Coli
MPNE. coli MPN
5/30/2002 67 4.56/6/2002 120 46/13/2002 NA NA6/20/2002 NA 56/27/2002 32 8.28/1/2002 >2419.6 918/15/2002 3.88/22/2002 4.38/29/2002 719/5/2002 4.29/12/2002 89 NA9/19/2002 60 NA9/26/2002 NA 5.310/3/2002 41 4.4
10/10/2002 46 3.910/17/2002 66 4.7 >2419.6 11110/24/2002 110 3.710/31/2002 86 611/7/2002 110 NA
11/14/2002 88 6.311/21/2002 56 6.411/26/2002 47 612/5/2002 66 4.8
12/12/2002 63 412/19/2002 110 7.812/24/2002 441/2/2003 541/9/2003 511/16/2003 61 980 681/23/2003 561/30/2003 662/6/2003 362/13/2003 322/20/2003 662/27/2003 793/6/2003 613/13/2003 NA 8.23/20/2003 NA 6.73/27/2003 4.84/3/2003 NA NA4/10/2003 NA 5.34/17/2003 71 10
47
A3: 541MER538 – SJR @ Fremont Ford continued…
DateTSS
(mg/L)TOC
(mg/L)Total Coli
MPNE. coli MPN
4/24/2003 56 8 >2419.6 1425/1/2003 68 8.55/8/2003 NA 7.65/15/2003 29 6.75/22/2003 94 4.65/29/2003 110 7.26/5/2003 120 106/12/2003 110 6.56/19/2003 110 7.56/26/2003 130 7.37/31/2003 >2419.6 938/28/2003 >2419.6 1119/25/2003 >2419.6 84
10/30/2003 >2419.6 11511/20/2003 >2419.6 1241/29/2004 870 342/26/2004 >2419.6 1193/11/2004 123/18/2004 133/25/2004 >2419.6 584/1/2004 104/8/2004 9.34/15/2004 9.94/22/2004 9.44/29/2004 13 >2419.6 1225/6/2004 125/13/2004 9.75/20/2004 8.55/27/2004 9.1 >2419.6 1796/3/2004 106/10/2004 106/17/2004 11 >2419.6 826/24/2004 >2419.6 557/1/2004 117/8/2004 8.8 >2419.6 517/15/2004 9.37/22/2004 8.17/29/2004 11 >2419.6 658/5/2004 7.68/12/2004 9.7 >2419.6 828/19/2004 9.6
48
A3: 541MER538 – SJR @ Fremont Ford continued…
DateTSS
(mg/L)TOC
(mg/L)Total Coli
MPNE. coli MPN
8/26/2004 >2419.6 619/16/2004 >2419.6 629/30/2004 >2419.6 148
10/14/2004 >2419.6 8110/28/2004 7 >2419.6 36511/4/2004 78 10 >2419.6 144
11/11/2004 67 1011/18/2004 73 9.7 >2419.6 11211/23/2004 51 9.112/2/2004 35 7.812/9/2004 59 7.6 >2419.6 129
12/16/2004 42 8.112/22/2004 66 7.6 >2419.6 8012/29/2004 92 7.71/6/2005 27 13 >2419.6 2601/13/2005 24 131/20/2005 25 >2419.6 821/27/2005 43 8.62/3/2005 27 12 >2419.6 822/10/2005 46 102/17/2005 53 11 >2419.6 14142/24/2005 26 113/3/2005 28 9.23/10/2005 25 NA 2420 203/17/2005 40 103/24/2005 98 9 >2419.6 >2419.63/31/2005 27 9.34/7/2005 39 10 >2419.6 414/14/2005 54 NA4/21/2005 78 7.7 >2419.6 444/28/2005 80 NA5/5/2005 NA 10 >2419.6 845/12/2005 60 9.15/19/2005 70 6.7 >2419.6 3875/26/2005 INA INA6/2/2005 INA INA6/9/2005 INA INA INA INA6/16/2005 92 5.66/23/2005 96 6.7 >2419.6 596/30/2005 59 3.77/7/2005 140 4.8 >2419.6 60
49
50
DateTSS
(mg/L)TOC
(mg/L)Total Coli
MPNE. coli MPN
7/13/2005 120 4.57/21/2005 110 5.1 >2419.6 327/28/2005 86 5.48/4/2005 100 5.5 >2419.6 738/11/2005 120 4.58/18/2005 130 4.6 >2419.6 508/25/2005 100 4.69/1/2005 120 4.4 >2419.6 429/8/2005 140 4.4 >2419.6 849/15/2005 96 4.59/21/2005 >2419.6 6879/22/2005 88 NA9/29/2005 50 5.3
Count 151 160 46 46Min 24.0 0.5 870 20Max
A3: 541MER538 – SJR @ Fremont Ford continued…
180 22 2420 2420n 72 7.9 NA NA Mean 65 7.1 2321 101ian 66 7.6 2420 83rtile 1 50 5.3 2420 60rtile 3 90 9.9 2420 124E: For values reported as < (less than), half the detection limit was used For values reported as > (greater than), 2420 was used
Data not applicable Site was inaccessible
= Site had no flow
MeaGeoMedQuaQuaNOT
NA =INA =DRY
A3: 541MER538 – SJR @ Fremont Ford continued…
DateNitrate (mg/L)
Nitrate-N (mg/L)
TKN (mg/L)
Ammonia-N (mg/L)
Phosphorus (mg/L)
Ortho-phosphate-
P (mg/L)
Potassium (mg/L)
BOD 5-Day (mg/L)
BOD 10-Day (mg/L)
10/12/2000 2.3 3.810/26/2000 2.2 <2 NA <1 8.2 2 3.411/16/2000 1.8 3.111/30/2000 2.4 <2 0.2 <1 8.6 2.4 4.312/12/2000 2.6 4.312/28/2000 2.5 <2 0.2 <1 9.1 2.4 4.21/11/2001 2.8 4.51/25/2001 NA NA 0.2 <1 9.8 2.6 4.32/8/2001 8.2 <2 0.2 <1 9.7 3.5 5.72/22/2001 16 2.2 NA <1 10 3.6 6.13/15/2001 11 <2 0.4 <1 8.9 2.4 4.43/29/2001 7.8 NA 0.3 <1 9.9 3.4 5.74/19/2001 5 <2 0.2 <1 11 3.4 5.94/26/2001 7.1 <2 0.3 <1 8.1 2.5 4.45/17/2001 5 <2 0.4 <1 9.2 2.8 4.95/31/2001 4.5 <2 0.3 NA 9.3 2.9 5.46/7/2001 7.2 <1.0 0.3 <1 9.1 4.5 6.76/14/2001 11 <2 <1 10 3.3 6.86/21/2001 7.4 <2 0.4 <1 9.2 3.3 5.56/28/2001 6.6 <2 0.3 <1 7.9 2.9 5.48/16/2001 4.1 <2 0.4 <1 6.88/30/2001 2.4 <2 0.4 <1 8.49/27/2001 <2 <2 0.3 <1 10
10/25/2001 1.6 3.711/29/2001 NA NA NA 0.1 NA 1.9 3.512/13/2001 1.4 2.812/27/2001 NA NA 0.1 <0.03 5.1 1.6 3.21/17/2002 1.3 2.51/31/2002 NA NA 0.2 NA NA 2.1 3.4
51
A3: 541MER538 – SJR @ Fremont Ford continued…
DateNitrate (mg/L)
Nitrate-N (mg/L)
TKN (mg/L)
Ammonia-N (mg/L)
Phosphorus (mg/L)
Ortho-phosphate-
P (mg/L)
Potassium (mg/L)
BOD 5-Day (mg/L)
BOD 10-Day (mg/L)
2/14/2002 NA 0.9 0.2 0.1 7 2 3.32/28/2002 NA NA 0.2 0.1 6.1 2.2 3.73/14/2002 NA NA NA 0.1 5.8 3.4 5.33/28/2002 NA 1.1 0.2 0.1 6.6 3.9 6.14/11/2002 NA 0.7 0.2 NA 8.94/25/2002 NA NA 0.3 NA 9.9 3 4.75/16/2002 NA NA NA 0.1 9.2 2.8 55/30/2002 NA NA NA 0.2 9.8 2.6 4.46/13/2002 12 NA 0.3 0.1 7.8 2.8 5.36/20/2002 NA 1.2 NA 0.1 9.1 2.5 4.77/18/2002 6 <2.0 NA 0.2 9.17/25/2002 6.2 <2.0 0.3 0.2 8.58/15/2002 4.2 <2.0 0.3 0.2 8.28/29/2002 NA 1 NA 0.2 6.7 2.5 4.49/26/2002 NA 0.6 0.2 0.1 7.4 2.8 5.1
10/31/2002 NA 0.8 0.2 0.1 5.6 2 3.411/21/2002 NA 1.1 0.1 NA 3.3 2 3.612/19/2002 NA 1.8 0.2 0.1 5 4.6 6.71/30/2003 NA 0.5 0.2 0.1 4 1.9 2.93/13/2003 13 3 0.4 <1.0 8.83/27/2003 8.1 1.5 0.3 <1.0 8.64/10/2003 5.5 1.8 0.4 <1.0 9.74/24/2003 3.6 <2.0 0.1 <1.0 105/15/2003 2.9 <2.0 0.2 <1.0 125/29/2003 3.5 <2.0 NA <1.0 9.36/12/2003 5.3 <2.0 0.4 <1.0 106/26/2003 9.7 <2.0 NA <1.0 7.6
52
A3: 541MER538 – SJR @ Fremont Ford continued…
DateNitrate (mg/L)
Nitrate-N (mg/L)
TKN (mg/L)
Ammonia-N (mg/L)
Phosphorus (mg/L)
Ortho-phosphate-
P (mg/L)
Potassium (mg/L)
BOD 5-Day (mg/L)
BOD 10-Day (mg/L)
7/17/2003 5.9 1.4 0.4 <1.0 8.17/31/2003 5.2 NA 0.5 <1.0 7.88/14/2003 3.6 1.2 0.4 <1.0 7.98/28/2003 2.1 1.4 0.4 <1.0 7.49/25/2003 <2.0 1.2 0.2 <1.0 8.6
10/30/2003 2 1.1 0.3 <1.0 911/20/2003 2.3 <1.0 0.2 <1.0 9.21/29/2004 0.6 0.8 0.1 0.2 0.12/26/2004 3.7 1 NA 0.3 0.23/11/2004 0.8 1.9 0.2 0.7 0.23/25/2004 2.1 1.1 0.1 0.3 0.24/15/2004 1 1.2 0.2 0.4 0.34/29/2004 0.8 1.4 0.1 0.3 0.15/13/2004 1 1 0.1 0.4 0.36/10/2004 2.6 1.3 0.1 0.4 0.26/24/2004 2.2 1.4 0.1 0.5 0.24/15/2004 1.2 0.4 0.34/29/2004 1.4 0.3 0.15/13/2004 1 0.4 0.37/15/2004 1.6 0.9 0.1 0.4 0.28/26/2004 0.7 1.1 NA 0.4 0.19/16/2004 0.2 0.8 0.1 0.4 0.19/30/2004 0.1 0.7 0.1 NA 0.1
10/28/2004 0.3 1.2 NA 0.4 0.411/23/2004 0.5 1 NA 0.3 0.212/29/2004 0.4 1 0.1 0.4 0.21/27/2005 1.8 1 0.3 0.4 0.32/24/2005 1.7 0.9 0.1 0.4 0.33/31/2005 0.7 0.8 0.1 0.3 0.2
53
A3: 541MER538 – SJR @ Fremont Ford continued…
DateNitrate (mg/L)
Nitrate-N (mg/L)
TKN (mg/L)
Ammonia-N (mg/L)
Phosphorus (mg/L)
Ortho-phosphate-
P (mg/L)
Potassium (mg/L)
BOD 5-Day (mg/L)
BOD 10-Day (mg/L)
4/28/2005 1 1.5 0.3 NA 0.45/12/2005 0.7 NA NA 0.3 0.26/16/2005 NA 0.7 NA NA NA6/30/2005 0.7 0.6 0.1 0.2 0.17/13/2005 1.4 0.9 NA NA 0.29/29/2005 0.4 0.9 NA NA 0.2
Count 37 24 71 17 67 78 54 41 41Min 1.0 0.1 0.5 0.1 0.1 0.0 3.3 1.3 2.5Max 16.0 3.7 3.0 0.3 0.7 0.5 12.0 4.6 6.8Mean 5.8 1.1 1.1 0.1 0.3 0.3 8.3 2.6 4.5Geo Mean 4.7 0.8 1.0 0.1 0.3 0.3 8.1 2.5 4.4Median 5.2 0.8 1.0 0.1 0.3 0.3 8.7 2.6 4.4Quartile 1 2.9 0.6 1.0 0.1 0.2 0.1 7.7 2.0 3.6Quartile 3 7.4 1.6 1.2 0.1 0.4 0.5 9.3 3.0 5.4NOTE: For values reported as < (less than), half the detection limit was used.
NA = Data not applicableINA = Site was inaccessibleDRY = Site had no flow
54
A3: 541MER538 – SJR @ Fremont Ford continued…
DateHardness
(mg/L)
Total Arsenic (ug/L)
Total Cadmium
(ug/L)
Total Chromium
(ug/L)
Total Copper (ug/L)
Total Lead (ug/L)
Total Nickel (ug/L)
Total Zinc (ug/L)
Total Mercury (ug/L)
10/26/2000 260 6.8 7 <5 9.5 2211/30/2000 330 1.2 1.7 <5 <5 1612/28/2000 370 <1 2 <5 <5 4.11/25/2001 360 2 3.6 <5 <5 52/22/2001 350 2.2 5.2 <5 5.5 8.43/29/2001 370 3.9 3.8 <5 6.5 9.14/26/2001 270 3.1 4.4 <5 5.2 105/31/2001 340 2.4 3.4 <5 <5 7.96/7/2001 290 6.7 1 3.9 4.9 <5 6.5 12 <0.26/14/2001 320 6 <1 2.5 5.5 <5 5.3 7.7 <0.26/21/2001 NA 7 <1 5.2 5.7 <5 8.6 16 <0.26/28/2001 240 5.9 <1 4.1 4.8 <5 6.7 13 <0.27/26/2001 NA NA 5 5 <5 7 15 NA8/30/2001 280 6.1 <1 2.1 3.4 <5 <5 7.79/27/2001 340 6 <1 <1 2.2 <5 <5 <2 <0.2
10/25/2001 330 4.3 <0.1 1.4 2.4 <5 <5 4.8 <0.211/29/2001 350 4.8 <0.1 <1 <1 <5 <5 5.8 <0.212/27/2001 420 4.8 <0.1 3.1 3.3 <5 5.3 7.3 <0.21/31/2002 <4.0 <0.1 <1.0 NA <5.0 <5.0 <2.0 <0.22/28/2002 360 5.8 <0.1 3.8 5.7 <5.0 6.5 14 <0.23/28/2002 460 <4.0 <0.1 1.5 2 <5.0 NA 5.1 <0.24/25/2002 5.8 <0.1 <1.0 1.7 <5.0 <5.0 <2.0 <0.25/30/2002 380 5.7 <0.1 1.6 2.4 <5.0 <5.0 2.9 <0.26/20/2002 310 6.6 <0.1 3.2 3.9 <5.0 5.1 8.8 <0.29/26/2002 290 5.4 <0.1 3.3 4.2 <5.0 5.5 11 <0.2
10/31/2002 280 <4.0 <0.1 2.9 3.6 <5.0 5 8.2 <0.211/21/2002 290 4.5 <0.1 3.8 3.9 <5.0 6.1 8.6 <0.2
55
A3: 541MER538 – SJR @ Fremont Ford continued…
DateHardness
(mg/L)
Total Arsenic (ug/L)
Total Cadmium
(ug/L)
Total Chromium
(ug/L)
Total Copper (ug/L)
Total Lead (ug/L)
Total Nickel (ug/L)
Total Zinc (ug/L)
Total Mercury (ug/L)
3/27/2003 400 6 <0.1 1.7 2.6 <5.0 <5.0 3.4 <0.24/24/2003 430 5.1 <0.1 NA NA NA <5.0 3.9 <0.25/29/2003 310 7.5 <0.1 4.8 6.2 <5.0 <5.0 13 <0.26/26/2003 240 8.6 <0.1 6.6 6.4 <5.0 8.7 16 <0.2
Count 27 22 22 30 29 30 30 31 21Min 240.0 2.0 0.1 0.5 0.5 2.5 2.5 1.0 0.1Max 460.0 8.6 1.0 6.8 7.0 2.5 9.5 22.0 0.1Mean 332.2 5.4 0.2 2.8 3.8 2.5 4.6 8.7 0.1Geo Mean 327.6 5.0 0.1 2.2 3.4 2.5 4.1 6.8 0.1Median 330.0 5.8 0.1 2.7 3.8 2.5 5.1 8.2 0.1Quartile 1 290.0 4.8 0.1 1.5 2.4 2.5 2.5 4.9 0.1Quartile 3 365.0 6.1 0.4 3.9 5.0 2.5 6.4 12.5 0.1NOTE: For values reported as < (less than), half the detection limit was used.
NA = Data not applicableINA = Site was inaccessibleDRY = Site had no flow
56
A3: 541MER538 – SJR @ Fremont Ford continued…
DateHardness
(mg/L)
Dissolved Arsenic (ug/L)
Dissolved Cadmium
(ug/L)
Dissolved Chromium
(ug/L)
Dissolved Copper (ug/L)
Dissolved Lead (ug/L)
Dissolved Nickel (ug/L)
Dissolved Zinc
(ug/L)
Dissolved Mercury (ug/L)
10/26/2000 260 <1 1.1 <5 <5 <211/30/2000 330 <1 <1 <5 <5 <212/28/2000 370 <1 <1 <5 <5 <21/25/2001 360 <1 <1 <5 <5 <22/22/2001 350 <1 1.2 <5 <5 <23/29/2001 370 <1 2.1 <5 <5 <24/26/2001 270 <1 1.0 <5 <5 <25/31/2001 340 <1 1.4 <5 <5 <26/7/2001 290 4.7 <1 <1 1.6 <5 <5 <2 <0.26/14/2001 320 4.9 <1 <1 3.1 <5 <5 <2 <0.26/21/2001 NA 4.7 <1 <1 <1 <5 <5 <2 <0.26/28/2001 240 4.9 <1 <1 <1 <5 <5 <2 <0.27/26/2001 NA NA NA NA NA NA NA NA8/30/2001 280 4 <1 <1 3.2 <5 <5 <29/27/2001 340 4 <1 <1 1.0 <5 <5 <2 <0.2
10/25/2001 330 <4 <0.1 <1 <1 <5 <5 <2 <0.211/29/2001 350 <4 <0.1 <1 <1 <5 <5 8.2 <0.212/27/2001 420 <4 <0.1 <1 <1 <5 <5 <2 <0.21/31/2002 <4.0 <0.1 <1.0 NA <5.0 <5.0 <2.0 <0.22/28/2002 360 <4.0 <0.1 <1.0 1.9 <5.0 <5.0 3.8 <0.23/28/2002 460 <4.0 <0.1 <1.0 1.0 <5.0 <5.0 3.1 <0.24/25/2002 4.7 <0.1 <1.0 1.2 <5.0 <5.0 NA <0.25/30/2002 380 4.3 <0.1 <1.0 1.5 <5.0 <5.0 <2.0 <0.26/20/2002 310 <4.0 <0.1 1.5 2.5 <5.0 <5.0 6.1 <0.29/26/2002 290 <4.0 <0.1 <1.0 1.5 <5.0 <5.0 <2.0 <0.2
10/31/2002 280 <4.0 <0.1 <1.0 1.0 <5.0 <5.0 <2.0 <0.2
57
A3: 541MER538 – SJR @ Fremont Ford continued…
DateHardness
(mg/L)
Dissolved Arsenic (ug/L)
Dissolved Cadmium
(ug/L)
Dissolved Chromium
(ug/L)
Dissolved Copper (ug/L)
Dissolved Lead (ug/L)
Dissolved Nickel (ug/L)
Dissolved Zinc
(ug/L)
Dissolved Mercury (ug/L)
11/21/2002 290 4.1 <0.1 <1.0 2.1 <5.0 <5.0 <2.0 <0.2
Count 23 18 18 26 25 26 26 25 17Min 240.0 2.0 0.1 0.5 0.5 2.5 2.5 1.0 0.1Max 460.0 4.9 0.5 1.5 3.2 2.5 2.5 8.2 0.1Mean 330.0 3.2 0.2 0.5 1.3 2.5 2.5 1.7 0.1Geo Mean 326.1 3.0 0.1 0.5 1.1 2.5 2.5 1.3 0.1Median 330.0 3.0 0.1 0.5 1.1 2.5 2.5 1.0 0.1Quartile 1 290.0 2.0 0.1 0.5 0.5 2.5 2.5 1.0 0.1Quartile 3 360.0 4.6 0.5 0.5 1.6 2.5 2.5 1.0 0.1NOTE: For values reported as < (less than), half the detection limit was used.
NA = Data not applicableINA = Site was inaccessibleDRY = Site had no flow
58
A3: 541MER538 – SJR @ Fremont Ford continued…
DateChloride (mg/L)
Sulfate (mg/L)
Calcium (mg/L)
Magnesium (mg/L)
TDS (mg/L)
Carbonate (mg/L)
Bicarbonate (mg/L)
Total Alkalinity
(mg/L)Sodium (mg/L)
10/26/2000 200 170 53 31 830 <1 220 180 18011/30/2000 270 210 67 39 1000 <1 240 200 24012/28/2000 310 250 73 44 1100 <1 250 200 2601/25/2001 280 270 75 42 1100 <1 240 200 2502/22/2001 240 210 75 39 970 <1 220 180 2003/29/2001 240 240 79 NA 1000 <1 230 190 2104/26/2001 180 160 58 31 750 <1 140 140 1505/31/2001 330 200 69 40 990 <1 160 160 2106/7/2001 220 160 62 34 800 <1 190 160 1806/14/2001 230 190 69 36 890 <1 200 170 1906/21/2001 190 160 58 30 750 <1 190 150 1506/28/2001 160 130 51 27 600 <1 170 140 1308/30/2001 240 160 57 34 920 <1 220 180 2209/27/2001 NA 220 66 43 1100 <1 NA NA 250
10/25/2001 300 220 65 41 1000 <1 240 NA 26011/29/2001 300 240 70 42 1100 <1 240 200 25012/27/2001 440 310 84 52 1400 <1 270 220 3102/28/2002 260 230 76 41 970 <1.0 230 190 2303/28/2002 340 330 96 53 NA <1.0 260 210 2905/30/2002 150 240 79 46 1200 <1.0 220 180 2706/20/2002 240 190 67 36 NA <1.0 200 170 1909/26/2002 260 170 58 35 NA <1.0 210 170 220
10/31/2002 240 170 56 33 850 <1.0 220 180 20011/21/2002 240 190 60 34 910 <1.0 220 180 1803/27/2003 87 454/24/2003 400 280 87 525/29/2003 240 170 65 35
59
60
A3: 541MER538 – SJR @ Fremont Ford continued…
DateChloride (mg/L)
Sulfate (mg/L)
Calcium (mg/L)
Magnesium (mg/L)
TDS (mg/L)
Carbonate (mg/L)
Bicarbonate (mg/L)
Total Alkalinity
(mg/L)Sodium (mg/L)
6/26/2003 160 130 53 25
Count 26 27 28 27 21 24 23 22 24Min 150 130 51 25 600 0.5 140 140 130Max 440 330 96 53 1400 0.5 270 220 310Mean 260 210 68 39 960 0.5 220 180 220Geo Mean 250 200 67 38 950 0.5 210 180 210Median 240 200 67 39 970 0.5 220 180 220Quartile 1 220 170 58 34 850 0.5 200 170 190Quartile 3 300 240 75 43 1100 0.5 240 200 250NOTE: For values reported as < (less than), half the detection limit was used.
NA = Data not applicableINA = Site was inaccessibleDRY = Site had no flow
A3: 541MER538 – SJR @ Fremont Ford continued…
Date Result Control Result Control
Result (million/m
l)
Control (million/
ml) MDD(%)3/27/2003 100 100 100 100 4.74 1.73 N/A
Count 1 1 1 1 1 1 N/A
* Significantly reduced from the lab control.** Significantly greater than the lab control.^ Fish were from a "forced hatch," duplicate failed QA.1 Duplicate sample for the set was low - 77% recovery.
3 Samples qualified, but duplicate sample recovery for the set was high - 126% (53.8%/42.5%)NA = Data not applicableINA = Site was inaccessibleDRY = Site had no flow
96h Acute Fathead Minnow
(% Survival)
48h Acute Ceriodaphnia Dubia
(% Survival) Algae Cell Growth
2 Testing for the Fathead minnow was initiated when samples were approx. 48h old due to
61
A4: 541STC512 – SJR @ Hills Ferry Station Code:541STC512
Location: Latitude 37.3425, Longitude -120.97722
Date TimeTemp (ºC)
Field SC (umhos) pH
Dissolved Oxygen (mg/L)
Turbidity (ntu)
10/26/2000 12:30 PM 14.6 1280 7.511/30/2000 10:30 AM 10.2 1830 7.512/28/2000 12:10 PM 8.7 2050 7.61/25/2001 1:15 PM 10.3 2060 7.62/7/2001 10:23 AM 10.1 2170 6.62/22/2001 1:55 PM 15.1 2050 8.13/13/2001 11:35 AM 16.7 1700 7.43/29/2001 12:30 PM 20.5 2340 7.94/18/2001 11:20 AM 19.2 2450 7.74/26/2001 9:22 AM 21.2 1540 6.95/15/2001 11:45 AM 21.9 1620 6.95/30/2001 1:25 PM 26.6 2070 7.26/6/2001 10:15 AM 22.2 2060 7.9 6.26/13/2001 9:45 AM 21.0 2400 8.1 7.76/20/2001 9:45 AM 26.0 1800 7.8 6.96/27/2001 12:27 PM 23.6 1740 7.9 7.77/25/2001 12:49 PM 27.0 1690 8.2 9.68/14/2001 11:17 AM 23.0 1920 8.3 10.18/29/2001 1:13 PM 27.0 1950 8.2 3.99/26/2001 11:49 AM 21.4 1750 7.9 8.6
10/24/2001 1:21 PM 16.4 1760 7.9 8.611/28/2001 12:00 PM 10.1 1790 8.1 10.512/26/2001 11:50 AM 10.2 2340 7.9 9.91/30/2002 12:20 PM 8.0 2520 8.1 11.82/27/2002 11:18 AM 15.6 2300 7.8 8.83/27/2002 10:52 AM 16.5 2570 8.0 10.14/30/2002 11:53 AM 17.9 2480 8.0 10.65/29/2002 11:58 AM 24.8 2200 8.0 9.46/19/2002 11:37 AM 24.7 2360 8.2 9.37/30/2002 9:05 AM 23.7 1410 7.6 6.6 1418/28/2002 12:45 PM 26.9 1840 8.2 NA9/25/2002 1:20 PM 24.4 1640 7.9 8.9
10/15/2002 9:14 AM 17.4 1910 7.4 7.8 NA10/30/2002 INA INA INA INA INA11/20/2002 11:49 AM 13.5 1660 7.8 9.412/18/2002 11:26 AM 10.6 1460 7.7 8.5 1501/14/2003 INA INA INA INA INA INA1/29/2003 12:05 PM 13.4 2140 7.7 8.5 57.9
62
A4: 541STC512 – SJR @ Hills Ferry continued…
Date TimeTemp (ºC)
Field SC (umhos) pH
Dissolved Oxygen (mg/L)
Turbidity (ntu)
3/25/2003 10:27 AM 16.7 2300 7.7 9.5 88.64/24/2003 12:33 PM 17.5 2900 7.9 8.8 27.55/29/2003 11:27 AM 26.1 2160 7.8 7.4 1426/26/2003 11:06 AM 24.8 1850 8.1 8.2 1307/31/2003 11:52 AM 26.2 1550 7.8 5.9 1548/28/2003 11:35 AM 24.3 1490 7.9 8.0 1169/25/2003 11:45 AM 22.2 1550 7.9 8.8 64.8
10/30/2003 11:42 AM 16.7 1630 7.8 7.5 67.411/20/2003 12:11 PM 13.7 1610 7.8 9.1 44.31/29/2004 11:30 AM 11.4 2240 7.7 11.4 44.82/26/2004 11:28 AM 12.6 1500 7.8 9.7 NA3/11/2004 10:58 AM 18.2 1880 8.0 8.7 NA3/25/2004 11:37 AM 18.5 2390 8.0 8.9 56.24/15/2004 10:54 AM 18.7 3080 8.0 9.8 49.84/29/2004 12:25 PM 18.7 2780 8.2 NA 46.85/13/2004 11:29 AM 21.2 1830 8.0 NA 59.85/27/2004 10:38 AM 22.7 2140 8.0 NA NA6/10/2004 12:04 PM 22.2 1900 8.1 9.3 1946/24/2004 11:10 AM 24.3 1160 8.1 8.8 NA7/15/2004 11:21 AM 24.8 1830 8.1 10.67/29/2004 10:53 AM 25.4 1960 8.2 9.78/26/2004 11:16 AM 23.7 1160 8.2 8.89/30/2004 11:05 AM 19.5 2180 7.8 9.4
10/28/2004 10:27 AM 12.9 1150 7.7 10.311/18/2004 10:29 AM 13.5 1340 7.6 7.811/23/2004 11:48 AM 9.6 1580 7.4 11.812/22/2004 10:27 AM 8.7 1840 7.9 12.612/29/2004 11:05 AM 9.7 1820 7.5 10.91/20/2005 10:52 AM 8.6 821 7.4 8.61/27/2005 1:06 PM 11.4 1630 7.4 12.22/17/2005 11:59 AM 14.4 1330 7.7 11.22/24/2005 11:15 AM 14.9 1090 7.5 8.23/24/2005 10:59 AM 14.9 960 7.4 9.33/29/2005 1:16 PM 15.6 859 7.3 9.24/21/2005 10:54 AM 16.9 1620 7.8 10.34/28/2005 11:36 AM 18.0 1580 7.7 9.35/19/2005 10:55 AM 20.3 307 7.2 7.25/26/2005 12:34 PM 22.8 220 7.3 5.26/23/2005 11:41 AM 23.0 993 NA 8.86/30/2005 12:06 PM 26.1 520 7.7 8.27/21/2005 10:15 AM 27.8 1680 8.1 8.57/28/2005 11:34 AM 27.3 1820 7.7 8.7
63
A4: 541STC512 – SJR @ Hills Ferry continued…
Date TimeTemp (ºC)
Field SC (umhos) pH
Dissolved Oxygen (mg/L)
Turbidity (ntu)
8/18/2005 11:00 AM 25.1 1420 8.0 7.58/25/2005 11:55 AM 25.0 1500 7.7 8.39/21/2005 8:45 AM 21.1 1190 7.8 7.79/22/2005 11:40 AM 23.0 1260 7.4 8.79/29/2005 11:58 AM 22.0 1490 7.0 8.0
Count 83 83 82 67 18Min 8.0 220 6.6 3.9 27.5Max 27.8 3080 8.3 12.6 194Mean 18.8 1760 7.8 8.9 90.8Geo Mean 17.9 1650 7.8 8.7 78.5Median 19.2 1790 7.8 8.8 66.1Quartile 1 14.5 1500 7.6 8.1 51.4Quartile 3 23.7 2100 8.0 9.7 138NOTE: For values reported as < (less than), half the detection limit was used.
NA = Data not applicableINA = Site was inaccessibleDRY = Site had no flow
64
A4: 541STC512 – SJR @ Hills Ferry continued…
DateTSS
(mg/L)TOC
(mg/L)Total Coli
MPNE. coli MPN
10/26/2000 42 8.611/30/2000 34 3.712/28/2000 NA 6.51/25/2001 56 7.22/22/2001 61 9.53/29/2001 NA <14/26/2001 5.55/30/2001 110 116/27/2001 150 117/25/2001 6.58/29/2001 NA 149/26/2001 NA 16
11/28/2001 NA12/26/2001 9.83/27/2002 NA4/30/2002 NA5/29/2002 6.16/19/2002 NA7/30/2002 >2419.6 1249/25/2002 NA
10/15/2002 >2419.6 7711/20/2002 7.912/18/2002 7.01/14/2003 INA INA3/25/2003 6.74/24/2003 NA >2419.6 8165/29/2003 9.76/26/2003 6.27/31/2003 >2419.6 >2419.68/28/2003 >2419.6 1559/25/2003 >2419.6 238
10/30/2003 >2419.6 12011/20/2003 >2419.6 3281/29/2004 >2419.6 332/26/2004 >2419.6 3873/25/2004 >2419.6 694/29/2004 >2419.6 2365/27/2004 10 >2419.6 2146/24/2004 >2419.6 757/29/2004 11 >2419.6 998/26/2004 >2419.6 919/30/2004 >2419.6 78
10/28/2004 >2419.6 291
65
66
DateTSS
(mg/L)TOC
(mg/L)Total Coli
MPNE. coli MPN
11/18/2004 9.3 >2419.6 15212/22/2004 8.3 >2419.6 441/20/2005 >2419.6 272/17/2005 11 >2419.6 12033/24/2005 11 >2419.6 12034/21/2005 8.7 >2419.6 1145/19/2005 6.6 >2419.6 4116/23/2005 6.2 >2419.6 777/21/2005 6.2 >2419.6 318/18/2005 5.4 >2419.6 1089/21/2005 >2419.6 1929/22/2005 NA
Count 6 30 29 29Min 34 0.5 2420 27Max 150 16 2420 2420Mea
A4: 541STC512 – SJR @ Hills Ferry continued…
n 76 8 NA NA Mean 66Geo 7 2420 162ian 59 8.1 2420 124rtile 1 46 6.3 2420 77rtile
MedQuaQua 3 98 10 2420 291
E: For values reported as < (less than), half the detection limit was used For values reported as > (greater than), 2420 was used
Data not applicable Site was inaccessible
= Site had no flow
NOT
NA =INA =DRY
A4: 541STC512 – SJR @ Hills Ferry continued…
DateNitrate (mg/L)
Nitrate-N (mg/L)
TKN (mg/L)
Ammonia-N (mg/L)
Phosphorus (mg/L)
Ortho-phosphate-
P (mg/L)
Potassium (mg/L)
BOD 5-Day (mg/L)
BOD 10-Day (mg/L)
10/26/2000 3.4 <2 NA <1 11 2.3 4.411/30/2000 6.4 <2 0.2 <1 9.9 1.8 3.512/28/2000 7.1 <2 0.2 <1 10 1.7 31/25/2001 NA NA 0.3 <1 11 2.9 52/7/2001 NA <2 NA <1 NA2/22/2001 19 2.6 NA <1 12 4.3 8.13/29/2001 14 NA 0.4 <1 12 3.8 6.64/26/2001 10 <2 0.2 <1 8.1 2.7 5.35/30/2001 13 <2 0.3 <1 10 4.2 7.26/27/2001 13 <2 0.4 <1 11 3.3 6.68/29/2001 9.6 <2 0.3 <1 NA9/26/2001 3.5 <2 0.3 <1 10
10/24/2001 3.5 <2 0.4 <1 11 2.9 611/28/2001 NA 0.2 NA <0.03 11 1.8 3.512/26/2001 NA 0.7 0.2 0.1 6.2 1.8 3.41/30/2002 NA 1.3 0.2 0.1 13 1.7 2.72/27/2002 NA 1 0.3 0.1 NA 2.7 4.53/27/2002 NA 1.4 NA 0.1 7.7 4.2 74/30/2002 NA NA 0.2 0.1 NA 5.2 85/29/2002 NA 0.9 NA 0.2 11 3.6 6.26/19/2002 NA 1.4 0.2 NA 8.1 5.4 10.18/28/2002 NA 1.5 0.3 NA 7.1 3.9 89/25/2002 3 5.4
11/20/2002 NA 1.2 0.3 0.1 712/18/2002 NA 1.5 0.1 <0.03 5.4 2.3 4.31/29/2003 NA NA 0.2 0.2 5.6 2.2 3.6
67
A4: 541STC512 – SJR @ Hills Ferry continued…
DateNitrate (mg/L)
Nitrate-N (mg/L)
TKN (mg/L)
Ammonia-N (mg/L)
Phosphorus (mg/L)
Ortho-phosphate-
P (mg/L)
Potassium (mg/L)
BOD 5-Day (mg/L)
BOD 10-Day (mg/L)
Count 11 NA 21 NA 19 23 21 22 22Min 3.4 NA 0.2 NA 0.1 0.02 5.4 1.7 2.7Max 19.0 NA 2.6 NA 0.4 0.5 13.0 5.4 10.1Mean 9.3 NA 1.1 NA 0.3 0.3 9.4 3.1 5.6Geo Mean 8.0 NA 1.0 NA 0.2 0.2 9.1 2.9 5.2Median 9.6 NA 1.0 NA 0.3 0.5 10.0 2.9 5.4Quartile 1 5.0 NA 1.0 NA 0.2 0.1 7.7 2.2 3.8Quartile 3 13.0 NA 1.3 NA 0.3 0.5 11.0 3.9 6.9NOTE: For values reported as < (less than), half the detection limit was used.
NA = Data not applicableINA = Site was inaccessibleDRY = Site had no flow
68
A4: 541STC512 – SJR @ Hills Ferry continued…
DateHardness
(mg/L)
Total Arsenic (ug/L)
Total Cadmium
(ug/L)
Total Chromium
(ug/L)
Total Copper (ug/L)
Total Lead (ug/L)
Total Nickel (ug/L)
Total Zinc (ug/L)
Total Mercury (ug/L)
10/26/2000 270 2.5 2.2 <5 6.4 5.911/30/2000 370 1.7 1.9 <5 <5 3.412/28/2000 410 1.3 2.3 <5 <5 <21/25/2001 410 2 3.2 <5 <5 3.42/22/2001 430 3.2 4.5 <5 6.4 5.63/29/2001 500 5.5 4.8 <5 8.4 194/26/2001 330 2.4 3.3 <5 <5 4.95/30/2001 440 3.4 4.1 <5 6.8 7.67/25/2001 5.8 5.4 <5 8.5 148/29/2001 NA 5.1 <1 2.9 3 <5 5.4 5.49/26/2001 350 <4 <0.1 5.4 4.8 <5 8.5 9.3 <0.2
10/24/2001 350 4.9 <0.1 NA 1.9 <5.0 <5.0 <2.0 <0.211/28/2001 340 5.8 <0.1 <1.0 1.2 <5.0 <5.0 3.2 <0.212/26/2001 440 5.6 <0.1 3.7 3.2 <5 6.2 8.2 <0.21/30/2002 500 <4 <0.1 1 <1 <5 <5 <2 <0.23/27/2002 540 4.6 <0.1 2.6 3.2 <5.0 6.7 6.9 <0.24/30/2002 540 <4.0 <0.1 2.4 2.5 <5.0 5.1 4.3 <0.25/29/2002 490 6 <0.1 4.8 NA <5.0 7.4 7.3 <0.26/19/2002 530 5.8 <0.1 6.9 7.2 <5.0 9.1 12 <0.29/25/2002 330 6.8 <0.1 6.1 NA <5.0 8.9 12 <0.2
11/20/2002 330 <4.0 <0.1 1.1 2.3 <5.0 NA NA <0.23/25/2003 490 8.2 <0.1 7.2 5.4 <5.0 9.3 13 <0.24/24/2003 600 <4.0 <0.1 2.1 2.5 <5.0 <5.0 <2.0 <0.25/29/2003 470 9.4 <0.1 10 7.5 <5.0 13 16 <0.26/26/2003 390 5.8 <0.1 6.8 5.5 <5.0 8.9 13 NA
69
A4: 541STC512 – SJR @ Hills Ferry continued…
DateHardness
(mg/L)
Total Arsenic (ug/L)
Total Cadmium
(ug/L)
Total Chromium
(ug/L)
Total Copper (ug/L)
Total Lead (ug/L)
Total Nickel (ug/L)
Total Zinc (ug/L)
Total Mercury (ug/L)
Count 23 16 16 24 23 25 24 24 14Min 270.0 2.0 0.1 0.5 0.5 2.5 2.5 1.0 0.1Max 600.0 9.4 0.5 10.0 7.5 2.5 13.0 19.0 0.1Mean 428.3 4.9 0.1 3.8 3.6 2.5 6.0 7.4 0.1Geo Mean 419.8 4.3 0.1 3.0 3.1 2.5 5.2 5.4 0.1Median 430.0 5.4 0.1 3.1 3.2 2.5 6.4 6.4 0.1Quartile 1 350.0 2.0 0.1 2.1 2.3 2.5 2.5 3.4 0.1Quartile 3 495.0 5.9 0.1 5.6 4.8 2.5 8.5 12.0 0.1NOTE: For values reported as < (less than), half the detection limit was used.
NA = Data not applicableINA = Site was inaccessibleDRY = Site had no flow
70
A4: 541STC512 – SJR @ Hills Ferry continued…
DateHardness
(mg/L)
Dissolved Arsenic (ug/L)
Dissolved Cadmium
(ug/L)
Dissolved Chromium
(ug/L)
Dissolved Copper (ug/L)
Dissolved Lead (ug/L)
Dissolved Nickel (ug/L)
Dissolved Zinc
(ug/L)
Dissolved Mercury (ug/L)
10/26/2000 270 <1 <1 <5 <5 <211/30/2000 370 <1 1.1 <5 <5 <212/28/2000 410 <1 <1 <5 <5 <21/25/2001 410 <1 <1 <5 <5 <22/22/2001 430 <1 1.4 <5 <5 <23/29/2001 500 <1 2.2 <5 <5 <24/26/2001 330 <1 <1 <5 <5 <25/30/2001 440 <1 1.3 <5 <5 <28/29/2001 NA 4.5 <1 <1 2.1 <5 <5 2.39/26/2001 350 <4 <0.1 <1 1.6 <5 <5 <2 <0.2
10/24/2001 350 4.4 <0.1 NA 1.2 <5.0 <5.0 <2.0 <0.211/28/2001 340 4.9 <0.1 <1.0 <1.0 <5.0 <5.0 NA <0.212/26/2001 440 <4 <0.1 <1 1.1 <5 <5 3.8 <0.21/30/2002 500 <4 <0.1 <1 <1 <5 <5 <2 <0.23/27/2002 540 4.2 <0.1 <1.0 1.5 <5.0 <5.0 <2.0 <0.24/30/2002 540 <4.0 <0.1 <1.0 <1.0 <5.0 <5.0 <2.0 <0.25/29/2002 490 5 <0.1 <1.0 1.3 <5.0 <5.0 <2.0 <0.26/19/2002 530 <4.0 <0.1 3.2 4 <5.0 <5.0 6.1 <0.29/25/2002 330 5.3 <0.1 <1.0 NA <5.0 <5.0 <2.0 <0.2
11/20/2002 330 <4.0 <0.1 <1.0 1.5 <5.0 <5.0 <2.0 <0.2
71
A4: 541STC512 – SJR @ Hills Ferry continued…
DateHardness
(mg/L)
Dissolved Arsenic (ug/L)
Dissolved Cadmium
(ug/L)
Dissolved Chromium
(ug/L)
Dissolved Copper (ug/L)
Dissolved Lead (ug/L)
Dissolved Nickel (ug/L)
Dissolved Zinc
(ug/L)
Dissolved Mercury (ug/L)
Count 19 12 12 19 19 20 20 19 11Min 270.0 2.0 0.1 0.5 0.5 2.5 2.5 1.0 0.1Max 540.0 5.3 0.5 3.2 4.0 2.5 2.5 6.1 0.1Mean 415.8 3.4 0.1 0.6 1.3 2.5 2.5 1.5 0.1Geo Mean 407.8 3.1 0.1 0.6 1.0 2.5 2.5 1.2 0.1Median 410.0 3.1 0.1 0.5 1.2 2.5 2.5 1.0 0.1Quartile 1 345.0 2.0 0.1 0.5 0.5 2.5 2.5 1.0 0.1Quartile 3 495.0 4.6 0.1 0.5 1.5 2.5 2.5 1.0 0.1NOTE: For values reported as < (less than), half the detection limit was used.
NA = Data not applicableINA = Site was inaccessibleDRY = Site had no flow
72
A4: 541STC512 – SJR @ Hills Ferry continued…
DateChloride (mg/L)
Sulfate (mg/L)
Calcium (mg/L)
Magnesium (mg/L)
TDS (mg/L)
Carbonate (mg/L)
Bicarbonate (mg/L)
Total Alkalinity
(mg/L)Sodium (mg/L)
10/26/2000 160 180 56 31 770 <1 220 180 16011/30/2000 240 290 77 43 1100 <1 250 200 25012/28/2000 290 340 83 49 1200 <1 260 210 2801/25/2001 290 370 84 49 1300 <1 270 220 2902/22/2001 280 380 92 50 1300 <1 260 210 2803/29/2001 330 460 110 58 1500 <1 260 220 3204/26/2001 200 280 70 37 950 <1 150 150 2005/30/2001 290 390 94 49 NA 4 172 176 2806/27/2001 220 350 83 41 1100 <1 200 170 2208/29/2001 260 NA NA NA 1200 <1.0 210 169 2609/26/2001 NA NA 72 41 NA <1 200 170 240
10/24/2001 270 250 70 43 1100 <1 250 210 26011/28/2001 260 270 67 43 1100 <1 260 210 25012/26/2001 380 400 83 56 150 <1 280 230 3301/30/2002 390 450 100 61 1600 <1 290 240 3602/27/2002 340 450 100 56 NA <1.0 268 220 3403/27/2002 380 470 110 64 1700 <1.0 290 240 3704/30/2002 360 480 120 59 NA <1.0 220 180 3505/29/2002 290 420 100 55 NA <1.0 200 190 3306/19/2002 320 540 120 57 NA <1.0 200 160 3509/25/2002 230 240 66 39 NA <1.0 210 170 240
11/20/2002 250 240 66 40 1000 <1.0 250 200 2203/25/2003 340 430 100 594/24/2003 460 550 130 685/29/2003 290 450 100 516/26/2003 220 390 89 42
73
74
A4: 541STC512 – SJR @ Hills Ferry continued…
DateChloride (mg/L)
Sulfate (mg/L)
Calcium (mg/L)
Magnesium (mg/L)
TDS (mg/L)
Carbonate (mg/L)
Bicarbonate (mg/L)
Total Alkalinity
(mg/L)Sodium (mg/L)
Count 25 24 25 25 15 22 22 22 22Min 160 180 56 31 150 0.5 150 150 160Max 460 550 130 68 1700 4.0 290 240 370Mean 300 380 90 50 1100 0.7 240 200 280Geo Mean 290 360 88 49 1000 0.5 230 200 280Median 290 390 89 49 1100 0.5 250 200 280Quartile 1 250 290 72 42 1100 0.5 200 180 240Quartile 3 340 450 100 57 1300 0.5 260 220 330NOTE: For values reported as < (less than), half the detection limit was used.
NA = Data not applicableINA = Site was inaccessibleDRY = Site had no flow
A4: 541STC512 – SJR @ Hills Ferry continued…
Date Result Control Result Control
Result (million/m
l)
Control (million/
ml)MDD (%)
10/26/2000 100 100 NA NA10/24/2001 100 100 100 10011/28/2001 NA NA 100 10012/26/2001 100 100 100 1001/30/2002 90 100 100 902/27/2002 95 100 100 1004/30/2002 100 100 100 1005/29/2002 100 100 100 1006/19/2002 100 100 100 1008/28/2002 95 100 NA NA9/25/2002 85 100 100 100
11/20/2002 100 100 100 1001/28/2003 100 100 100 100 4.14** 3.28 N/A
Count 12 12 11 11 1 1 0
* Significantly reduced from the lab control.** Significantly greater than the lab control.^ Fish were from a "forced hatch," duplicate failed QA.1 Duplicate sample for the set was low - 77% recovery.
3 Samples qualified, but duplicate sample recovery for the set was high - 126% (53.8%/42.5%)NA = Data not applicableINA = Site was inaccessibleDRY = Site had no flow
2 Testing for the Fathead minnow was initiated when samples were approx. 48h old due to untimely shipping of fish by fish supplier.
96h Acute Fathead Minnow
(% Survival)
48h Acute Ceriodaphnia Dubia
(% Survival) Algae Cell Growth
75
A4: 541STC512 – SJR @ Hills Ferry continued…
DateResult
(% Survival)Control
(% Survival)
Avg Dry Weight Result (mg)
Avg Dry Weight Control
(mg)
Growth MDD (%)
Result (% Survival)
Control (%
Survival)
Avg # Young /
Adult Result
Avg # Young /
Adult Control
Repro MDD (%)
3/11/2004 96.7 97.5 0.62 0.60 16 100.0 100.0 22.3 20 263/25/2004 85.7 97.5 0.55* 0.68 11 100.0 100.0 28.6 20.9 N/A4/15/2004 100.0 97.5 0.68 0.59 7.2 100.0 100.0 14.0* 21.8 134/29/2004 90.0 100.0 0.46* 0.62 16 100.0 100.0 17.1* 20 115/13/2004 96.2 100.0 0.63 0.68 13 100.0 100.0 22.3 17.3 24
05/27/2004^ N/A N/A N/A N/A N/A N/A N/A N/A N/A N/A6/10/2004 90.0 97.6 0.47* 0.58 13 100.0 100.0 25.3 25.2 126/24/2004 93.1 100.0 0.65 0.67 13 100.0 100.0 38.2 21.1 17
11/18/2004 92.9 100.0 0.56 0.46 1612/22/2004 85.7 95.2 0.51* 0.61 161/20/2005 92.5 97.4 0.82 0.92 192/17/2005 87.2 97.5 0.32* 0.38 143/24/2005 97.4 97.5 0.55 0.41 8.14/21/2005 N/A N/A N/A N/A N/A5/19/2005 87.5* 100.0 0.57 0.62 216/23/2005 N/A N/A N/A N/A N/A9/22/2005 82.5* 97.5 0.31* 0.45 20
Count 14 14 14 14 14 7 7 7 7 6
* Significantly reduced from the lab control.** Significantly greater than the lab control.^ Fish were from a "forced hatch," duplicate failed QA.1 Duplicate sample for the set was low - 77% recovery.
3 Samples qualified, but duplicate sample recovery for the set was high - 126% (53.8%/42.5%)NA = Data not applicableINA = Site was inaccessibleDRY = Site had no flow
Chronic Ceriodaphnia Dubia - 6 dayChronic Fathead Minnow - 7day
2 Testing for the Fathead minnow was initiated when samples were approx. 48h old due to untimely shipping of fish by fish supplier.
76
A5: 535STC504 – SJR @ Crows Landing Station Code:535STC504
Location: Latitude 37.43194, Longitude -121.01167
Date TimeTemp (ºC)
Field SC (umhos) pH
Dissolved Oxygen (mg/L)
Turbidity (ntu)
10/5/2000 11:40 AM 20.8 1000 7.710/12/2000 9:35 AM 16.1 732 7.710/19/2000 11:10 AM 17.2 463 7.410/26/2000 12:30 PM 15.7 394 6.811/2/2000 11:30 AM 15.3 533 6.611/9/2000 12:25 PM 13.3 728 7.4
11/16/2000 9:00 AM 10.1 817 7.311/21/2000 9:40 AM 10.1 814 7.911/30/2000 9:45 AM 9.0 858 7.812/7/2000 12:05 PM 10.3 1050 7.8
12/12/2000 12:20 PM 12.8 1100 8.212/21/2000 10:10 AM 9.4 1150 7.812/28/2000 9:16 AM 6.6 1190 7.91/4/2001 11:53 AM 8.9 1280 7.61/11/2001 9:37 AM 8.7 1120 7.51/18/2001 12:20 PM 8.2 1270 8.11/25/2001 9:47 AM 8.8 1410 7.82/1/2001 9:40 AM 8.2 1380 7.42/8/2001 12:40 PM 10.6 1540 7.62/15/2001 10:00 AM 10.0 1290 7.42/22/2001 10:56 AM 11.9 1540 7.83/1/2001 11:30 AM 13.0 1250 7.73/8/2001 11:52 AM 15.1 721 7.83/15/2001 10:05 AM 15.8 1460 7.73/22/2001 10:00 AM 19.4 1800 7.73/29/2001 1:25 PM 22.2 1590 6.94/5/2001 10:30 AM 15.0 1760 8.04/12/2001 12:30 PM 15.2 1340 6.84/19/2001 10:45 AM 17.3 1260 7.94/26/2001 12:35 PM 22.3 576 8.05/3/2001 12:10 PM 18.1 980 7.25/10/2001 11:04 AM 21.1 593 7.75/17/2001 10:05 AM 19.6 530 6.95/24/2001 1:05 PM 26.2 1250 7.85/31/2001 9:27 AM 28.4 1140 7.46/7/2001 9:45 AM 22.5 1230 8.0 8.16/14/2001 9:10 AM 21.0 1370 8.0 8.26/21/2001 10:31 AM 26.3 1430 7.9 7.9
77
A5: 535STC504 – SJR @ Crows Landing continued…
Date TimeTemp (ºC)
Field SC (umhos) pH
Dissolved Oxygen (mg/L)
Turbidity (ntu)
6/28/2001 10:01 AM 22.5 1250 7.8 6.77/5/2001 11:42 AM 25.4 1470 7.8 7.27/11/2001 9:35 AM 24.3 1370 7.6 7.87/19/2001 9:59 AM 23.9 1400 7.9 10.57/26/2001 11:05 AM 24.9 1320 7.9 9.28/2/2001 12:34 PM 25.0 1260 8.0 9.08/9/2001 11:17 AM 26.1 1390 8.1 8.28/16/2001 12:27 PM 24.0 1320 8.1 9.58/23/2001 11:44 AM 22.5 1130 8.0 8.78/30/2001 12:31 PM 23.9 1450 8.1 9.69/6/2001 11:37 AM 21.9 1470 7.9 7.99/13/2001 1:10 PM 22.5 1330 7.9 9.59/20/2001 8:35 AM 22.0 1270 7.8 6.89/27/2001 9:16 AM 20.7 1100 7.8 6.910/4/2001 10:32 AM 21.8 1340 7.7 7.5
10/11/2001 11:48 AM 17.9 1180 7.7 7.510/18/2001 11:46 AM 18.8 842 7.8 7.810/25/2001 1:08 PM 15.7 610 8.0 9.611/1/2001 12:20 PM 15.8 594 8.0 8.611/8/2001 1:10 PM 15.0 742 8.3 9.9
11/15/2001 10:39 AM 15.8 855 7.8 8.211/20/2001 9:45 AM 14.2 965 7.8 8.511/29/2001 11:10 AM 12.7 960 7.4 NA12/6/2001 11:47 AM 10.5 1010 7.8 10.9
12/13/2001 11:26 AM 9.7 1170 7.6 10.712/20/2001 9:06 AM 9.7 1240 7.9 10.612/27/2001 10:56 AM 10.5 1180 7.8 11.01/3/2002 12:07 PM 13.0 650 7.7 8.91/10/2002 12:45 PM 12.5 1020 8.0 11.41/17/2002 11:20 AM 8.7 1420 7.8 11.01/24/2002 10:11 AM 7.6 1640 7.8 5.11/31/2002 9:20 AM 7.2 1560 8.4 12.22/7/2002 10:58 AM 10.6 1440 8.0 11.52/14/2002 11:37 AM 12.0 1640 7.9 9.72/21/2002 8:59 AM 14.3 1500 7.8 10.82/28/2002 12:01 PM 15.6 1700 7.9 9.53/7/2002 10:24 AM 15.3 1680 7.9 9.23/14/2002 12:11 PM 13.7 1820 8.1 10.13/21/2002 12:30 PM 15.6 1240 8.0 9.13/28/2002 3:00 PM 18.8 1830 8.0 10.64/4/2002 10:50 AM 19.1 1890 8.0 8.14/11/2002 12:31 PM 19.6 1680 8.0 9.0
78
A5: 535STC504 – SJR @ Crows Landing continued…
Date TimeTemp (ºC)
Field SC (umhos) pH
Dissolved Oxygen (mg/L)
Turbidity (ntu)
4/18/2002 10:10 AM 16.1 1380 8.0 9.04/25/2002 9:09 AM 19.3 1120 7.9 8.05/2/2002 10:17 AM 16.1 752 7.9 10.55/9/2002 INA INA INA INA INA5/16/2002 NA NA NA NA NA NA5/23/2002 9:05 AM 18.0 1150 7.6 NA5/30/2002 10:46 AM 24.8 1330 7.9 8.66/6/2002 10:24 AM 24.9 1290 7.9 6.56/13/2002 9:34 AM 22.6 1450 7.8 NA6/20/2002 10:22 AM 24.1 1480 7.5 NA6/27/2002 11:42 AM 25.2 1320 8.2 9.77/3/2002 8:39 AM 24.7 1430 8.1 NA7/11/2002 10:34 AM 26.7 1550 8.1 NA7/18/2002 11:42 AM 23.9 1440 8.2 9.7 55.07/25/2002 10:43 AM 23.8 1220 8.0 7.67/30/2002 9:52 AM 23.5 1210 7.7 6.9 75.78/1/2002 11:27 AM 24.7 1240 8.0 8.58/8/2002 11:43 AM 22.8 1400 8.1 10.58/15/2002 10:51 AM 24.4 1630 8.1 8.58/22/2002 11:04 AM 22.3 1270 7.9 8.38/29/2002 10:23 AM 22.5 1370 8.0 NA9/5/2002 10:40 AM 21.7 1530 7.8 7.59/12/2002 10:41 AM 22.1 1300 7.8 7.79/19/2002 10:39 AM 21.5 1390 7.8 7.3 NA9/26/2002 9:59 AM 21.1 1260 7.7 8.010/3/2002 10:57 AM 15.2 1260 7.8 10.2
10/10/2002 9:39 AM 20.0 1320 7.8 7.510/17/2002 10:44 AM 16.8 890 7.9 8.4 55.410/24/2002 8:59 AM 15.0 563 7.5 8.610/31/2002 11:57 AM 14.1 911 7.8 8.0 36.911/7/2002 11:08 AM 13.8 1090 7.7 9.1
11/14/2002 11:22 AM 14.6 1000 7.6 8.511/21/2002 9:58 AM 12.9 1160 7.7 8.9 36.211/26/2002 9:11 AM 12.1 1280 7.7 9.712/5/2002 11:03 AM 10.8 1330 7.9 11.2 36.4
12/12/2002 10:26 AM 11.1 1370 7.4 11.712/19/2002 10:48 AM 9.7 1130 7.8 NA 75.012/24/2002 9:01 AM 8.3 959 7.4 10.81/2/2003 10:06 AM 9.7 1130 7.8 13.91/9/2003 11:26 AM 10.1 1530 7.9 12.2
79
A5: 535STC504 – SJR @ Crows Landing continued…
Date TimeTemp (ºC)
Field SC (umhos) pH
Dissolved Oxygen (mg/L)
Turbidity (ntu)
1/16/2003 9:49 AM 11.3 1330 7.7 9.3 53.01/23/2003 10:15 AM 11.2 1600 7.6 13.41/30/2003 11:53 AM 13.1 1570 7.6 9.6 53.02/6/2003 8:39 AM 9.6 1650 7.8 10.32/13/2003 9:58 AM 11.7 1730 7.7 9.8 39.12/20/2003 9:06 AM 11.4 1560 7.8 10.5 68.52/27/2003 10:26 AM 13.9 1570 7.8 8.93/6/2003 1:17 PM 15.4 1700 7.8 12.2 NA3/13/2003 11:45 AM 18.1 1710 8.0 9.4 54.73/20/2003 11:05 AM 15.9 1860 8.0 9.3 42.93/27/2003 11:08 AM 16.4 1640 7.9 9.2 54.84/3/2003 10:42 AM 15.6 1730 7.4 8.8 52.24/10/2003 11:48 AM 19.3 1770 8.0 10.1 40.54/17/2003 11:38 AM 16.2 1050 7.8 9.4 33.24/24/2003 11:56 AM 16.7 1080 7.9 9.9 29.15/1/2003 11:26 AM 17.7 1070 7.9 9.6 NA5/8/2003 10:41 AM 15.9 580 7.5 8.0 28.05/15/2003 10:57 AM 19.3 1000 7.8 9.55/22/2003 12:38 PM 23.7 1340 7.9 10.5 12.35/29/2003 11:12 AM 25.7 1350 7.8 8.46/5/2003 12:34 PM 25.4 1370 8.0 8.9 73.76/12/2003 11:30 AM 22.6 1400 7.9 9.6 75.36/19/2003 12:21 PM 24.4 1540 8.2 7.2 74.66/26/2003 11:36 AM 24.7 1280 8.0 8.5 91.27/3/2003 11:06 AM 23.9 1390 8.1 13.47/10/2003 11:12 AM 25.0 1370 8.1 10.07/17/2003 11:10 AM 25.8 1360 8.0 8.17/24/2003 11:13 AM 26.4 1350 7.9 7.4 2737/31/2003 11:50 AM 25.3 1250 7.9 7.8 1058/7/2003 11:11 AM 23.5 1230 8.2 9.2 73.58/14/2003 10:46 AM 23.2 1460 8.2 9.38/21/2003 10:43 AM 24.3 1450 7.9 7.8 51.08/28/2003 11:15 AM 23.1 1300 7.9 8.3 75.09/4/2003 10:35 AM 24.6 1390 8.0 7.2 64.39/11/2003 1:35 PM 23.2 1310 8.0 9.4 41.29/18/2003 11:31 AM 19.3 1450 7.8 8.9 35.59/25/2003 12:12 PM 21.8 1180 8.0 8.9 46.110/2/2003 11:33 AM 20.2 1110 7.8 8.1 47.910/9/2003 11:21 AM 20.2 1060 7.7 8.6 53.8
10/16/2003 9:37 AM 16.9 1100 7.6 9.6 40.5
80
A5: 535STC504 – SJR @ Crows Landing continued…
Date TimeTemp (ºC)
Field SC (umhos) pH
Dissolved Oxygen (mg/L)
Turbidity (ntu)
10/23/2003 12:30 PM 18.4 634 7.7 9.1 43.510/30/2003 10:41 AM 16.5 983 7.7 7.8 30.011/6/2003 11:36 AM 13.6 960 7.8 10.6 36.2
11/13/2003 9:56 AM 13.2 1090 7.8 9.3 32.511/20/2003 11:15 AM 13.3 1090 7.9 9.9 NA11/26/2003 10:08 AM 8.5 1180 7.9 10.9 20.712/4/2003 10:39 AM 12.3 1280 7.9 10.7
12/11/2003 10:20 AM 11.5 1300 7.8 11.0 NA12/18/2003 11:05 AM 9.2 1300 8.0 11.7 NA12/23/2003 10:38 AM 11.2 1300 7.8 14.2 NA12/30/2003 11:26 AM 8.6 1240 7.8 12.8 NA1/8/2004 9:56 AM 9.0 1240 7.8 8.7 NA1/15/2004 11:14 AM 10.0 1440 7.8 9.9 NA1/22/2004 10:50 AM 9.4 1540 7.9 15.9 30.01/29/2004 11:40 AM 11.3 1550 7.9 10.9 NA2/5/2004 10:28 AM 10.4 1310 7.7 14.6 53.22/12/2004 10:38 AM 10.8 1640 7.9 12.3 NA2/19/2004 10:17 AM 12.9 1480 7.9 12.2 NA2/26/2004 11:11 AM 12.0 1110 7.8 9.7 NA3/4/2004 10:33 AM 12.4 1160 7.9 9.9 65.23/11/2004 11:26 AM 17.7 1520 7.9 8.2 NA3/18/2004 9:47 AM 19.4 1840 7.9 10.33/25/2004 12:09 PM 18.5 1710 8.0 9.1 44.54/1/2004 10:49 AM 16.7 1680 8.1 10.74/8/2004 11:16 AM 18.5 1900 7.9 8.9 45.04/15/2004 12:08 PM 18.6 1270 7.9 9.7 43.24/22/2004 11:17 AM 16.9 1000 8.0 11.1 53.04/29/2004 1:15 PM 18.3 772 8.0 NA 29.75/6/2004 12:03 PM 18.9 494 7.9 11.1 35.25/13/2004 12:20 PM 18.2 581 7.8 12.5 34.15/20/2004 11:22 AM 20.8 1120 7.7 8.6 41.35/27/2004 11:22 AM 23.6 1290 8.0 NA NA6/3/2004 11:49 AM 24.0 1410 8.1 8.8 48.26/10/2004 12:52 PM 22.8 1520 8.3 11.9 67.46/17/2004 12:05 PM 25.3 1590 8.2 10.9 58.16/24/2004 11:53 AM 23.7 1480 8.1 9.3 NA7/1/2004 11:07 AM 24.3 1580 8.0 10.9 NA7/8/2004 11:07 AM 25.0 1490 8.0 9.5 NA7/15/2004 11:53 AM 24.3 1520 8.3 12.1 NA7/22/2004 9:11 AM 25.1 1320 8.0 8.9 NA7/29/2004 11:21 AM 24.5 1590 8.2 10.3 NA8/5/2004 10:57 AM 24.0 1310 8.1 9.0 NA
81
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Date TimeTemp (ºC)
Field SC (umhos) pH
Dissolved Oxygen (mg/L)
Turbidity (ntu)
8/12/2004 11:11 AM 25.5 1340 8.0 8.7 NA8/19/2004 9:15 AM 24.9 1280 7.9 7.0 NA8/26/2004 11:41 AM 23.8 1090 8.1 9.5 NA9/2/2004 10:59 AM 23.4 1640 7.8 8.8 NA9/9/2004 8:46 AM 23.1 1290 7.8 6.9 NA9/16/2004 9:30 AM 21.2 1240 7.6 7.3 NA9/23/2004 2:03 PM 21.4 1090 7.9 10.4 NA9/30/2004 11:33 AM 19.8 1450 7.8 8.7 NA10/7/2004 10:35 AM 19.9 1070 7.8 9.7
10/14/2004 10:14 AM 18.5 990 7.6 8.010/21/2004 11:39 AM 15.4 468 NA 8.110/28/2004 11:01 AM 13.3 698 7.7 11.811/4/2004 12:15 PM 13.3 1000 7.8 9.5
11/11/2004 10:15 AM 14.5 1080 7.6 8.511/18/2004 10:55 AM 13.8 991 7.7 8.711/23/2004 9:06 AM 9.4 1100 7.8 10.412/2/2004 11:43 AM 8.0 1310 7.8 12.012/9/2004 10:35 AM 11.1 1270 7.7 10.8
12/16/2004 11:21 AM 11.5 1060 7.7 10.312/22/2004 9:52 AM 8.9 1330 7.9 13.212/29/2004 8:53 AM 9.5 1340 7.8 10.01/6/2005 9:40 AM 9.3 450 7.5 11.41/13/2005 11:34 AM 9.5 399 7.4 8.81/20/2005 11:36 AM 8.7 719 7.5 8.81/27/2005 10:55 AM 11.0 1230 7.6 9.62/3/2005 11:29 AM 10.7 1060 7.5 8.62/10/2005 10:39 AM 12.5 1370 7.8 10.12/17/2005 11:20 AM 14.1 1140 7.7 9.02/24/2005 11:07 AM 14.9 926 7.4 8.73/3/2005 10:18 AM 15.2 1040 7.7 9.13/10/2005 12:22 PM 18.7 1430 7.8 9.13/17/2005 10:08 AM 16.8 1800 7.7 13.73/24/2005 11:33 AM 14.5 741 7.7 9.53/31/2005 10:40 AM 13.1 393 7.5 10.44/7/2005 11:21 AM 14.8 531 7.7 10.14/14/2005 10:20 AM 13.7 553 7.7 11.44/21/2005 11:25 AM 15.0 561 7.9 10.74/28/2005 10:29 AM 15.7 579 7.5 12.95/5/2005 11:19 AM 17.2 601 7.6 10.05/12/2005 10:32 AM 16.8 378 7.5 9.9
82
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Date TimeTemp (ºC)
Field SC (umhos) pH
Dissolved Oxygen (mg/L)
Turbidity (ntu)
5/19/2005 11:30 AM 17.7 205 7.4 8.65/26/2005 11:25 AM 20.6 100 7.8 6.76/2/2005 11:19 AM 19.7 133 7.5 8.06/9/2005 9:46 AM 19.1 182 7.0 7.56/16/2005 11:00 AM 21.2 414 7.3 8.36/23/2005 12:10 PM 20.1 403 NA 9.06/30/2005 12:05 PM 23.2 439 7.4 9.37/7/2005 10:58 AM 22.3 559 7.5 9.57/13/2005 9:02 AM 23.8 691 7.7 8.47/21/2005 10:51 AM 24.7 787 7.7 8.37/28/2005 12:27 PM 25.1 796 7.9 9.18/4/2005 10:41 AM 24.5 778 7.7 8.18/11/2005 12:12 PM 24.0 673 7.9 8.98/18/2005 11:50 AM 22.6 621 7.9 8.58/25/2005 11:06 AM 21.8 538 7.6 8.69/1/2005 10:42 AM 22.5 822 7.8 10.29/8/2005 11:00 AM 21.4 690 7.5 8.69/15/2005 10:55 AM 18.8 474 7.6 9.69/21/2005 9:06 AM 18.9 472 7.8 8.69/22/2005 12:07 PM 20.5 496 7.6 9.29/29/2005 10:49 AM 19.0 479 7.6 8.7
Count 261 261 259 216 55Min 6.6 100 6.6 5.1 12.3Max 28.4 1900 8.4 15.9 273Mean 17.5 1165 7.8 9.5 53.9Geo Mean 16.5 1078 7.8 9.4 48.1Median 17.7 1250 7.8 9.3 47.9Quartile 1 12.9 965 7.7 8.5 36.3Quartile 3 22.5 1430 7.9 10.4 61.2NOTE: For values reported as < (less than), half the detection limit was used.
NA = Data not applicableINA = Site was inaccessibleDRY = Site had no flow
83
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DateTSS
(mg/L)TOC
(mg/L)Total Coli
MPNE. coli MPN
10/5/2000 4910/12/2000 66 6.510/19/2000 NA 1.510/26/2000 50 2.311/2/2000 63 4.711/9/2000 39 3.8
11/16/2000 27 2.911/21/2000 22 NA11/30/2000 28 2.412/7/2000 35 1.6
12/12/2000 30 1.712/21/2000 NA 5.412/28/2000 20 2.91/4/2001 16 4.01/11/2001 69 4.81/18/2001 34 5.21/25/2001 41 5.12/1/2001 35 7.02/8/2001 30 6.52/15/2001 54 3.72/22/2001 NA 2.53/1/2001 63 8.13/8/2001 91 9.53/15/2001 65 8.13/22/2001 40 2.03/29/2001 54 <14/5/2001 34 NA4/12/2001 40 6.54/19/2001 47 5.84/26/2001 2.85/3/2001 51 4.65/10/2001 53 3.55/17/2001 2.65/24/2001 64 5.35/31/2001 37 8.36/7/2001 52 8.66/14/2001 61 106/21/2001 NA 136/28/2001 61 127/5/2001 8.37/11/2001 7.37/19/2001 5.7
84
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DateTSS
(mg/L)TOC
(mg/L)Total Coli
MPNE. coli MPN
7/26/2001 6.38/2/2001 6.28/9/2001 8.48/16/2001 52 138/23/2001 62 9.58/30/2001 56 129/6/2001 38 149/13/2001 38 129/20/2001 NA 129/27/2001 49 1010/4/2001 NA 15
10/11/2001 44 1510/18/2001 64 1310/25/2001 8.411/1/2001 3411/8/2001 26
11/15/2001 37 5.811/20/2001 36 NA11/29/2001 35 NA12/6/2001 42 4.4
12/13/2001 19 2.312/20/2001 23 512/27/2001 241/3/2002 801/10/2002 511/17/2002 221/24/2002 211/31/2002 18 NA2/7/2002 39 NA2/14/2002 29 NA2/18/2002 342/21/2002 542/28/2002 33 8.23/7/2002 353/7/2002 69 8.13/8/2002 453/9/2002 653/11/2002 433/14/2002 55 7.43/21/2002 41 7.43/28/2002 26 6.84/4/2002 35 NA4/11/2002 35
85
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DateTSS
(mg/L)TOC
(mg/L)Total Coli
MPNE. coli MPN
4/18/2002 40 144/25/2002 42 NA5/2/2002 51 1.65/16/2002 38 NA5/23/2002 69 NA5/30/2002 NA 4.46/6/2002 44 4.46/13/2002 NA NA6/20/2002 73 3.76/27/2002 55 7.77/30/2002 >2419.6 1168/15/2002 3.28/22/2002 3.88/29/2002 679/5/2002 4.29/12/2002 55 NA9/19/2002 54 NA9/26/2002 49 NA10/3/2002 32 4.1
10/10/2002 39 3.710/17/2002 50 4.210/24/2002 41 310/31/2002 37 4.411/7/2002 50 NA
11/14/2002 45 6.111/21/2002 38 5.611/26/2002 30 5.312/5/2002 28 4.4
12/12/2002 43 3.512/19/2002 95 5.712/24/2002 611/2/2003 NA1/9/2003 391/16/2003 56 >2419.6 471/23/2003 441/30/2003 502/6/2003 432/13/2003 352/20/2003 912/27/2003 78
86
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DateTSS
(mg/L)TOC
(mg/L)Total Coli
MPNE. coli MPN
3/6/2003 723/13/2003 NA 8.23/20/2003 NA 6.73/27/2003 38 4.54/3/2003 NA NA4/10/2003 NA 3.84/17/2003 36 4.94/24/2003 31 4.6 >2419.6 2915/1/2003 28 5.15/8/2003 NA 3.65/15/2003 42 4.55/22/2003 34 4.25/29/2003 62 5.96/5/2003 58 7.16/12/2003 65 4.96/19/2003 61 5.76/26/2003 61 5.77/31/2003 >2419.6 918/28/2003 >2419.6 1359/25/2003 >2419.6 144
10/30/2003 >2419.6 6511/20/2003 >2419.6 681/29/2004 >2419.6 332/26/2004 >2419.6 8163/11/2004 133/18/2004 103/25/2004 >2419.6 564/1/2004 9.24/8/2004 9.14/15/2004 64/22/2004 5.54/29/2004 4.4 >2419.6 1525/6/2004 3.95/13/2004 4.75/20/2004 6.45/27/2004 7.1 >2419.6 1676/3/2004 8.26/10/2004 8.96/17/2004 9.1 >2419.6 1076/24/2004 >2419.6 1017/1/2004 9.47/8/2004 8.9 >2419.6 122
87
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DateTSS
(mg/L)TOC
(mg/L)Total Coli
MPNE. coli MPN
7/15/2004 107/22/2004 77/29/2004 8.2 >2419.6 688/5/2004 8.48/12/2004 7.5 >2419.6 938/19/2004 8.18/26/2004 >2419.6 619/16/2004 >2419.6 619/30/2004 >2419.6 30
10/14/2004 >2419.6 5010/28/2004 54 7.1 >2419.6 13011/4/2004 48 8.2 >2419.6 160
11/11/2004 49 811/18/2004 60 7.5 >2419.6 7511/23/2004 30 6.712/2/2004 22 6.312/9/2004 39 6.2 >2419.6 49
12/16/2004 48 7.712/22/2004 27 6.3 >2419.6 5612/29/2004 46 6.61/6/2005 75 11 >2419.6 4351/13/2005 64 131/20/2005 33 2420 351/27/2005 48 7.92/3/2005 42 12 >2419.6 992/10/2005 49 8.22/17/2005 98 9.7 >2419.6 13002/24/2005 48 113/3/2005 53 9.83/10/2005 55 NA >2419.6 553/17/2005 59 103/24/2005 120 7.5 >2419.6 >2419.63/31/2005 25 5.84/7/2005 32 5.2 2420 824/14/2005 36 NA4/21/2005 36 3.8 >2419.6 584/28/2005 42 NA5/5/2005 NA 4 >2419.6 8165/12/2005 53 6.25/19/2005 51 4.2 >2419.6 260
88
89
DateTSS
(mg/L)TOC
(mg/L)Total Coli
MPNE. coli MPN
5/26/2005 35 5.26/2/2005 23 4.26/9/2005 35 NA >2419.6 316/16/2005 66 4.16/23/2005 70 3.9 >2419.6 2766/30/2005 66 37/7/2005 64 3.3 >2419.6 887/13/2005 62 3.47/21/2005 51 3.6 >2419.6 607/28/2005 51 3.78/4/2005 38 3.8 >2419.6 668/11/2005 NA 3.68/18/2005 57 3.2 >2419.6 938/25/2005 47 3.39/1/2005 58 3.4 >2419.6 1359/8/2005 43 3.4 >2419.6 1119/19/29/29/2
CounMin MaxMeaGeoMedQuaQua
A5: 535STC504 – SJR @ Crows Landing continued…
5/2005 43 31/2005 >2419.6 1142/2005 38 NA9/2005 28 2.8
t 162 162 46 4616.0 0.5 2420 30
120.0 15.0 2420 2420n 46.9 6.3 NA NA Mean 44.0 5.6 2420 111ian 44.0 5.8 2420 93rtile 1 35.0 3.9 2420 60rtile 3 56.0 8.2 2420 142E: For values reported as < (less than), half the detection limit was used For values reported as > (greater than), 2420 was used
Data not applicable Site was inaccessible
= Site had no flow
NOT
NA =INA =DRY
A5: 535STC504 – SJR @ Crows Landing continued…
DateNitrate (mg/L)
Nitrate-N (mg/L)
TKN (mg/L)
Ammonia-N (mg/L)
Phosphorus (mg/L)
Ortho-phosphate-
P (mg/L)
Potassium (mg/L)
BOD 5-Day (mg/L)
BOD 10-Day (mg/L)
10/12/2000 2.2 3.910/26/2000 4.2 <2 0.1 <1 3.8 1.1 211/16/2000 1 1.611/30/2000 7.3 <2 0.1 <1 4.7 0.8 1.412/12/2000 1 1.612/28/2000 9 <2 <0.1 <1 6 0.8 1.41/11/2001 1.6 2.81/25/2001 8.6 <2 0.2 <1 7.9 1.6 2.92/8/2001 13 <2 0.3 <1 10 2.4 5.22/22/2001 16 <2 0.2 <1 8 1.4 2.93/15/2001 14 <2 0.3 <1 9.2 2.1 4.13/29/2001 11 <2 0.2 <1 8.3 2.2 4.14/19/2001 11 <2 0.2 <1 6.1 2.3 4.24/26/2001 6.4 <2 <1 0.1 <1 3.4 1.6 2.85/17/2001 4.8 <2 0.1 <1 3.5 1.4 2.45/31/2001 11 <1.0 0.2 NA 6 2.1 3.96/7/2001 15 <1.0 0.3 <1 6.3 3.6 5.56/14/2001 20 <2 <1 6.6 3 5.46/21/2001 15 <2 0.3 <1 8 4.1 6.66/28/2001 18 <2 0.3 <1 8.2 2.9 5.58/16/2001 18 <2 0.3 <1 6.48/30/2001 14 <2 0.3 <1 7.49/27/2001 8.5 <2 0.2 <1 6.6
10/25/2001 0.9 2.111/29/2001 NA NA NA 0.1 7.3 1.1 2.112/13/2001 0.9 1.712/27/2001 NA 0.4 0.1 0.1 3.7 0.7 1.61/17/2002 0.7 1.5
90
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DateNitrate (mg/L)
Nitrate-N (mg/L)
TKN (mg/L)
Ammonia-N (mg/L)
Phosphorus (mg/L)
Ortho-phosphate-
P (mg/L)
Potassium (mg/L)
BOD 5-Day (mg/L)
BOD 10-Day (mg/L)
1/31/2002 NA NA 0.2 NA NA 1.5 2.32/14/2002 NA 0.8 0.1 0.1 6.6 1.6 2.82/28/2002 NA NA NA 0.1 NA 1.6 2.63/14/2002 NA NA NA 0.1 5.4 2.7 4.53/28/2002 NA 1.1 0.2 0.1 64/11/2002 NA 0.6 0.2 0.1 6.34/25/2002 NA NA 0.2 NA 5.3 1.9 3.45/16/2002 NA NA NA 0.1 3.8 1.4 2.55/30/2002 NA NA NA 0.1 NA 3 4.96/13/2002 17 NA 0.2 <1.0 6.8 2.9 5.76/20/2002 NA 1.2 0.2 0.1 5.9 3.6 6.67/18/2002 23 <2.0 NA 0.1 7.67/25/2002 11 <2.0 0.3 <1.0 7.38/15/2002 11 <2.0 0.2 <1.0 7.78/29/2002 NA 1.1 0.3 0.1 5.8 3.3 6.29/26/2002 NA 0.6 NA 0.1 6.8 1.9 3.3
10/31/2002 1.6 2.611/21/2002 NA 1.1 0.1 0.1 4.2 1.3 2.512/19/2002 NA 1.3 0.2 <0.03 5.5 3.1 4.71/30/2003 NA 0.5 0.1 0.1 3.7 1.4 2.32/27/2003 19 2.5 0.1 <1.0 8.63/13/2003 15 3.0 0.4 <1.0 8.43/27/2003 13 NA 0.3 <1.0 7.64/10/2003 11 1.7 0.4 <1.0 74/24/2003 8.7 <2.0 <0.1 <1.0 4.45/15/2003 8.8 <2.0 <0.1 <1.0 5.65/29/2003 9.2 <2.0 NA <1.0 76/12/2003 11 <2.0 0.3 <1.0 7.5
91
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DateNitrate (mg/L)
Nitrate-N (mg/L)
TKN (mg/L)
Ammonia-N (mg/L)
Phosphorus (mg/L)
Ortho-phosphate-
P (mg/L)
Potassium (mg/L)
BOD 5-Day (mg/L)
BOD 10-Day (mg/L)
6/26/2003 14 <2.0 NA <1.0 6.67/17/2003 11 1.5 0.3 <1.0 7.57/31/2003 16 NA 0.3 <1.0 7.68/14/2003 8.8 1.6 0.3 <1.0 7.58/28/2003 11 1.5 0.3 <1.0 8.19/25/2003 12 1.4 0.2 <1.0 6.8
10/30/2003 8.2 1.1 0.3 <1.0 5.811/20/2003 7.5 <1.0 0.2 <1.0 6.81/29/2004 2.1 0.8 0.1 0.2 0.12/26/2004 2.8 1.5 NA 0.3 0.13/11/2004 2.9 1.3 0.1 0.4 0.23/25/2004 3.4 1 0.1 0.4 0.24/15/2004 2.2 0.7 0 0.2 0.14/29/2004 1.4 0.6 0.1 0.2 0.15/13/2004 1.3 0.5 0.1 0.2 0.16/10/2004 4.5 1.2 0 0.3 0.16/24/2004 3.1 1.5 0.1 0.3 0.17/15/2004 3.1 1.5 0.1 0.3 NA7/29/2004 4.2 1.5 NA 0.4 0.18/12/2004 2.5 1.1 0.1 0.3 0.18/26/2004 2.2 1.2 NA 0.3 <0.039/16/2004 3.1 0.9 0.1 0.3 0.19/30/2004 2.9 0.6 0.1 NA 0.1
10/28/2004 1.5 0.9 NA 0.2 0.311/23/2004 1.8 0.9 NA 0.2 0.112/29/2004 1.5 0.8 0 0.2 0.11/27/2005 2.7 1.0 0.2 0.4 0.22/24/2005 1.8 1.1 0.1 0.4 0.33/31/2005 0.7 0.6 0.1 0.2 0.1
92
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DateNitrate (mg/L)
Nitrate-N (mg/L)
TKN (mg/L)
Ammonia-N (mg/L)
Phosphorus (mg/L)
Ortho-phosphate-
P (mg/L)
Potassium (mg/L)
BOD 5-Day (mg/L)
BOD 10-Day (mg/L)
4/28/2005 1.3 0.6 0.1 NA 0.15/12/2005 0.9 NA NA 0.2 0.15/26/2005 0.2 0.5 0.1 0.2 0.16/16/2005 NA 0.3 NA NA NA6/30/2005 1 0.5 0.1 0.2 0.17/13/2005 1.2 0.6 NA NA 0.19/29/2005 1.5 0.5 NA NA 0.1
Count 39 27 73 17 69 79 53 40 40Min 4.2 0.2 0.3 0.1 0.1 0.0 3.4 0.7 1.4Max 23.0 4.5 3.0 0.5 0.4 0.5 10.0 4.1 6.6Mean 12.1 2.1 1.0 0.1 0.2 0.3 6.5 1.9 3.4Geo Mean 11.3 1.8 0.9 0.1 0.2 0.2 6.3 1.7 3.1Median 11.0 2.1 1.0 0.1 0.2 0.2 6.6 1.6 2.9Quartile 1 8.8 1.4 0.8 0.1 0.2 0.1 5.8 1.3 2.3Quartile 3 15.0 2.9 1.1 0.1 0.3 0.5 7.6 2.5 4.6NOTE: For values reported as < (less than), half the detection limit was used.
NA = Data not applicableINA = Site was inaccessibleDRY = Site had no flow
93
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DateHardness
(mg/L)
Total Arsenic (ug/L)
Total Cadmium
(ug/L)
Total Chromium
(ug/L)
Total Copper (ug/L)
Total Lead (ug/L)
Total Nickel (ug/L)
Total Zinc (ug/L)
Total Mercury (ug/L)
10/26/2000 91 2.3 2.7 <5 <511/30/2000 180 1.6 1.9 <5 <5 3.612/28/2000 240 1.3 1.9 <5 <5 <21/25/2001 280 2.3 2.8 <5 <5 3.52/22/2001 330 2.3 3.2 <5 <5 3.23/29/2001 340 2.8 3.1 <5 <5 6.64/26/2001 130 1.9 2.8 <5 <5 4.45/31/2001 250 2.6 3.1 <5 <5 <26/7/2001 280 3.2 <1 3.2 4 <5 <5 6.7 <0.26/14/2001 320 2.9 <1 2.5 3.3 <5 <5 5.1 <0.26/21/2001 NA 3.8 <1 2.4 2.9 <5 <5 4.6 <0.26/28/2001 310 5.1 <1 3.6 3.6 <5 5.5 5.9 <0.27/26/2001 NA NA 43 3.5 <5 5.8 6.2 NA8/30/2001 310 3.6 <1 3.3 2.5 <5 <5 3.59/27/2001 230 4 <1 <1 1.5 <5 <5 <2 <0.2
10/25/2001 120 <4 <0.1 1.4 2.5 <5 <5 3.9 <0.211/29/2001 200 <4 <0.1 5.7 2.7 <5 6.5 10 <0.212/27/2001 230 <4 <0.1 3.7 3.8 <5 <5 6.4 <0.21/31/2002 <4.0 <0.1 <1.0 NA <5.0 <5.0 <2.0 <0.22/28/2002 360 4.1 <0.1 1.8 3.4 <5.0 <5.0 3.5 <0.23/28/2002 380 <4.0 <0.1 1.3 2.8 <5.0 <5.0 4.7 <0.24/25/2002 240 <4.0 <0.1 <1.0 <1.0 <5.0 <5.0 <2.0 <0.25/30/2002 290 4.7 <0.1 4.7 4.3 <5.0 6.5 6.8 <0.26/20/2002 330 <4.0 <0.1 3.9 4.3 <5.0 5.9 5.3 <0.29/26/2002 280 7 <0.1 3.9 NA <5.0 <5.0 4.6 <0.2
10/25/2002 300 <4.0 <0.1 2.7 6.4 <5.0 <5.0 4.2 <0.210/31/2002 200 <4.0 <0.1 1.8 2.6 <5.0 <5.0 3 <0.211/15/2002 240 <4.0 <0.1 1.9 2.8 <5.0 <5.0 4.8 <0.211/21/2002 <4.0 <0.1 1.5 1.8 <5.0 <5.0 3.4 <0.23/27/2003 340 4.7 NA 3.6 3.6 <5.0 <5.0 5 <0.2
94
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DateHardness
(mg/L)
Total Arsenic (ug/L)
Total Cadmium
(ug/L)
Total Chromium
(ug/L)
Total Copper (ug/L)
Total Lead (ug/L)
Total Nickel (ug/L)
Total Zinc (ug/L)
Total Mercury (ug/L)
4/24/2003 230 <4.0 <0.1 NA NA NA <5.0 2.2 <0.25/29/2003 300 <4.0 <0.1 2.6 4.8 <5.0 <5.0 4.4 <0.26/26/2003 290 4.1 <0.1 5.4 5 <5.0 7.5 8.5 <0.2
Count 29 24 23 32 30 32 33 32 23Min 91.0 2.0 0.1 0.5 0.5 2.5 2.5 1.0 0.1Max 380.0 7.0 0.5 43.0 6.4 2.5 7.5 10.0 0.1Mean 262.8 3.1 0.2 3.8 3.1 2.5 3.2 4.3 0.1Geo Mean 250.7 2.8 0.1 2.4 2.9 2.5 3.0 3.7 0.1Median 280.0 2.0 0.1 2.5 3.0 2.5 2.5 4.4 0.1Quartile 1 230.0 2.0 0.1 1.8 2.6 2.5 2.5 3.4 0.1Quartile 3 310.0 4.0 0.3 3.6 3.6 2.5 2.5 5.5 0.1NOTE: For values reported as < (less than), half the detection limit was used.
NA = Data not applicableINA = Site was inaccessibleDRY = Site had no flow
95
A5: 535STC504 – SJR @ Crows Landing continued…
DateHardness
(mg/L)
Dissolved Arsenic (ug/L)
Dissolved Cadmium
(ug/L)
Dissolved Chromium
(ug/L)
Dissolved Copper (ug/L)
Dissolved Lead (ug/L)
Dissolved Nickel (ug/L)
Dissolved Zinc
(ug/L)
Dissolved Mercury (ug/L)
10/26/2000 91 <1 <1 <5 <5 <211/30/2000 180 <1 <1 <5 <5 <212/28/2000 240 <1 <1 <5 <5 <21/25/2001 280 <1 <1 <5 <5 <22/22/2001 330 <1 1.1 <5 <5 <23/29/2001 340 <1 1.8 <5 <5 <24/26/2001 130 <1 1.1 <5 <5 2.85/31/2001 250 <1 1.2 <5 <5 <26/7/2001 280 2.4 <1 <1 1.3 <5 <5 <2 <0.26/14/2001 320 2.8 <1 <1 1.4 <5 <5 <2 <0.26/21/2001 NA 3.2 <1 <1 <1 <5 <5 <2 <0.26/28/2001 310 <2 <1 <1 <1 <5 <5 <2 <0.27/26/2001 NA NA NA NA NA NA NA NA8/30/2001 310 2.8 <1 <1 1.4 <5 <5 2.59/27/2001 230 <4 <1 <1 <1 <5 <5 <2 <0.2
10/25/2001 120 <4 <0.1 <1 <1 <5 <5 <2 <0.211/29/2001 200 <4 <0.1 <1 <1 <5 <5 3.2 <0.212/27/2001 230 <4 <0.1 <1 1.2 <5 <5 2.7 <0.21/31/2002 <4.0 <0.1 <1.0 NA <5.0 <5.0 <2.0 <0.22/28/2002 360 <4.0 <0.1 <1.0 2.2 <5.0 <5.0 <2.0 <0.23/28/2002 380 <4.0 <0.1 <1.0 1.7 <5.0 <5.0 2.8 <0.24/25/2002 240 4.6 <0.1 <1.0 <1.0 <5.0 <5.0 NA <0.25/30/2002 290 <4.0 <0.1 <1.0 1.8 <5.0 <5.0 4.8 <0.26/20/2002 330 <4.0 <0.1 <1.0 1.9 <5.0 <5.0 <2.0 <0.29/26/2002 280 4.3 <0.1 <1.0 <1.0 <5.0 <5.0 <2.0 <0.2
10/31/2002 200 <4.0 <0.1 <1.0 1.4 <5.0 <5.0 <2.0 <0.211/21/2002 240 <4.0 <0.1 <1.0 <1.0 <5.0 <5.0 <2.0 <0.2
96
A5: 535STC504 – SJR @ Crows Landing continued…
DateHardness
(mg/L)
Dissolved Arsenic (ug/L)
Dissolved Cadmium
(ug/L)
Dissolved Chromium
(ug/L)
Dissolved Copper (ug/L)
Dissolved Lead (ug/L)
Dissolved Nickel (ug/L)
Dissolved Zinc
(ug/L)
Dissolved Mercury (ug/L)
Count 24 18 18 26 25 26 26 25 17Min 91.0 1.0 0.1 0.5 0.5 2.5 2.5 1.0 0.1Max 380.0 4.6 0.5 0.5 2.2 2.5 2.5 4.8 0.1Mean 256.7 2.4 0.2 0.5 1.0 2.5 2.5 1.5 0.1Geo Mean 243.3 2.3 0.1 0.5 0.9 2.5 2.5 1.3 0.1Median 265.0 2.0 0.1 0.5 1.1 2.5 2.5 1.0 0.1Quartile 1 222.5 2.0 0.1 0.5 0.5 2.5 2.5 1.0 0.1Quartile 3 312.5 2.7 0.5 0.5 1.4 2.5 2.5 1.0 0.1NOTE: For values reported as < (less than), half the detection limit was used.
NA = Data not applicableINA = Site was inaccessibleDRY = Site had no flow
97
A5: 535STC504 – SJR @ Crows Landing continued…
DateChloride (mg/L)
Sulfate (mg/L)
Calcium (mg/L)
Magnesium (mg/L)
TDS (mg/L)
Carbonate (mg/L)
Bicarbonate (mg/L)
Total Alkalinity
(mg/L)Sodium (mg/L)
10/26/2000 49 49 20 10 220 <1 80 60 4111/30/2000 100 120 38 20 520 <1 130 110 10012/28/2000 160 180 51 29 670 <1 170 140 1501/25/2001 180 220 57 33 760 <1 200 160 1802/22/2001 210 280 71 37 940 <1 200 160 2003/29/2001 200 280 71 39 860 <1 200 170 2004/26/2001 94 28 14 350 <1 72 72 605/31/2001 150 190 53 28 680 <1 120 120 1406/7/2001 160 210 62 31 720 <1 160 130 1506/14/2001 160 280 70 34 840 <1 180 150 1806/21/2001 180 270 70 34 920 <1 190 150 1806/28/2001 160 230 68 33 740 <1 180 150 1608/30/2001 180 250 67 34 880 <1 210 170 1909/27/2001 NA 150 48 27 650 <1 NA NA 140
10/25/2001 87 76 26 14 350 <1 110 NA 7111/29/2001 140 140 40 23 580 <1 150 130 12012/27/2001 170 180 46 29 690 <1.0 150 130 1502/28/2002 NA 310 76 41 970 <1.0 211 173 2403/28/2002 250 310 78 45 1100 <1.0 230 190 2504/25/2002 160 200 52 27 640 <1.0 130 100 1405/30/2002 160 230 63 32 810 <1.0 180 140 1706/20/2002 190 290 74 36 NA <1.0 190 160 2009/26/2002 180 170 60 32 740 <1.0 210 170 170
10/31/2002 130 120 41 23 550 <1.0 150 120 12011/21/2002 160 150 49 29 710 <1.0 180 150 1403/27/2003 240 280 72 404/24/2003 150 190 49 255/29/2003 190 260 66 336/26/2003 180 270 66 31
98
99
A5: 535STC504 – SJR @ Crows Landing continued…
DateChloride (mg/L)
Sulfate (mg/L)
Calcium (mg/L)
Magnesium (mg/L)
TDS (mg/L)
Carbonate (mg/L)
Bicarbonate (mg/L)
Total Alkalinity
(mg/L)Sodium (mg/L)
Count 26 29 29 29 24 25 24 23 25Min 49.0 49.0 20.0 10.0 220.0 0.5 72.0 60.0 41.0Max 250.0 310.0 78.0 45.0 1100.0 0.5 230.0 190.0 250.0Mean 164.5 206.2 56.3 29.8 703.8 0.5 166.0 139.3 153.7Geo Mean 157.6 190.2 53.6 28.4 666.5 0.5 159.8 135.0 143.3Median 160.0 210.0 60.0 31.0 715.0 0.5 180.0 150.0 150.0Quartile 1 152.5 150.0 48.0 27.0 625.0 0.5 145.0 125.0 140.0Quartile 3 180.0 270.0 70.0 34.0 845.0 0.5 200.0 160.0 180.0NOTE: For values reported as < (less than), half the detection limit was used.
NA = Data not applicableINA = Site was inaccessibleDRY = Site had no flow
A5: 535STC504 – SJR @ Crows Landing continued…
Date Result Control Result ControlResult
(million/ml)Control
(million/ml)MDD (%)
10/26/2000 100 100 NA NA1/25/2001 95 100 100 1002/22/2001 100 100 100 1003/29/2001 90 100 100 1004/26/2001 90 100 100 905/31/2001 80 90 100 1006/28/2001 75* 100 100 100
10/25/2001 100 100 100 10011/29/2001 NA NA 100 10012/27/2001 100 100 100 1001/31/2002 100 100 100 1002/28/2002 100 100 100 1004/25/2002 90 100 100 1005/30/2002 100 100 100 1006/20/2002 100 100 100 1008/29/2002 100 100 100 1009/26/2002 100 95 100 100
10/31/2002 100 100 100 10011/21/2002 100 100 100 10012/19/2002 95 100 100 100 2.97 2.93 NA1/30/2003 100 100 100 100 5.12** 3.07 NA3/27/2003 100 100 100 100 5.26** 1.73 NA5/29/2003 100 100 100 100 5.35** 2.03 2.1
Count 22 22 22 22 4 4 1
* Significantly reduced from the lab control.** Significantly greater than the lab control.^ Fish were from a "forced hatch," duplicate failed QA.1 Duplicate sample for the set was low - 77% recovery.
3 Samples qualified, but duplicate sample recovery for the set was high - 126% (53.8%/42.5%)NA = Data not applicableINA = Site was inaccessibleDRY = Site had no flow
96h Acute Fathead Minnow
(% Survival)
48h Acute Ceriodaphnia Dubia
(% Survival) Algae Cell Growth
2 Testing for the Fathead minnow was initiated when samples were approx. 48h old due to untimely shipping of fish by fish supplier.
100
A5: 535STC504 – SJR @ Crows Landing continued…
DateResult
(% Survival)
Control (%
Survival)
Avg Dry Weight Result (mg)
Avg Dry Weight Control
(mg)
Growth MDD (%)
Result (% Survival)
Control (%
Survival)
Avg # Young /
Adult Result
Avg # Young /
Adult Control
Repro MDD (%)
3/11/2004 79.3* 97.5 0.54 0.60 33 100.0 100.0 22.6 20 303/25/2004 96.7 97.5 0.64 0.68 11 100.0 100.0 27.2 20.9 N/A4/15/2004 63.3* 97.5 0.41 0.59 31 100.0 100.0 20.6 21.8 154/29/2004 33.3* 100.0 0.14* 0.62 20 100.0 100.0 25.7 20 115/13/2004 90.3 100.0 0.57* 0.68 13 100.0 100.0 27.0 17.3 25
05/27/2004^ N/A N/A N/A N/A N/A N/A N/A N/A N/A N/A6/10/2004 100.0 97.6 0.57 0.58 5 100.0 100.0 31.4 25.2 136/24/2004 93.3 100.0 0.65 0.67 13 100.0 100.0 33.6 21.1 21
11/18/2004 87.5* 100.0 0.48 0.45 2212/22/2004 76.2* 95.2 0.39 0.61 211/20/2005 100.0 97.4 0.82 0.92 9.82/17/2005 87.2 97.5 0.33 0.38 163/24/2005 90.0 97.5 0.51 0.41 244/21/2005 N/A N/A N/A N/A N/A5/19/2005 82.9* 100.0 0.56 0.62 226/23/2005 N/A N/A N/A N/A N/A9/22/2005 81.6* 97.5 0.28* 0.45 24
Count 14 14 14 14 14 7 7 7 7 6
* Significantly reduced from the lab control.** Significantly greater than the lab control.^ Fish were from a "forced hatch," duplicate failed QA.1 Duplicate sample for the set was low - 77% recovery.
3 Samples qualified, but duplicate sample recovery for the set was high - 126% (53.8%/42.5%)NA = Data not applicableINA = Site was inaccessibleDRY = Site had no flow
Chronic Ceriodaphnia Dubia - 6 dayChronic Fathead Minnow - 7day
2 Testing for the Fathead minnow was initiated when samples were approx. 48h old due to untimely shipping of fish by fish supplier.
101
A6: 541STC507 – SJR @ Patterson Station Code:541STC507
Location: Latitude 37.49778, Longitude -121.08167
Date TimeTemp (ºC)
Field SC (umhos) pH
Dissolved Oxygen (mg/L)
Turbidity (ntu)
10/5/2000 12:30 PM 21.5 1210 7.310/12/2000 9:00 AM 16.5 802 7.510/19/2000 11:30 AM 18.0 537 7.810/26/2000 11:40 AM 15.6 419 7.411/2/2000 11:48 AM 14.7 571 6.611/9/2000 12:50 PM 13.6 781 7.7
11/16/2000 8:55 AM 10.4 881 7.011/21/2000 10:00 AM 10.4 879 7.711/30/2000 8:50 AM 9.6 905 7.712/12/2000 1:05 PM 13.4 1140 8.012/21/2000 9:45 AM 9.4 1190 7.612/28/2000 8:23 AM 6.9 1220 7.71/4/2001 12:14 PM 9.2 1320 7.71/11/2001 9:08 AM 8.7 982 7.51/18/2001 12:43 PM 8.7 1280 6.81/25/2001 8:49 AM 9.1 1440 7.72/1/2001 9:20 AM 8.3 1370 7.12/8/2001 1:35 PM 11.5 1570 7.82/15/2001 9:29 AM 9.9 1320 7.42/22/2001 9:55 AM 11.6 1520 7.63/1/2001 11:50 AM 13.1 1210 7.73/8/2001 12:38 PM 15.2 714 7.83/15/2001 9:30 AM 15.7 1440 7.73/22/2001 9:26 AM 19.2 1770 7.73/29/2001 1:50 PM 20.9 1510 8.04/5/2001 10:00 AM 15.3 1660 7.84/12/2001 12:50 PM 16.0 1290 7.34/19/2001 10:00 AM 17.2 1320 7.94/26/2001 1:25 PM 21.9 603 7.95/3/2001 1:00 PM 18.5 997 7.65/10/2001 11:30 AM 22.6 684 7.75/17/2001 9:25 AM 20.2 608 7.05/24/2001 1:30 PM 26.6 1260 7.95/31/2001 8:45 AM 24.6 1170 7.36/7/2001 9:15 AM 23.0 1230 8.0 9.46/14/2001 8:23 AM 21.3 1460 7.9 8.66/21/2001 9:54 AM 26.5 1400 8.0 9.46/28/2001 9:26 AM 23.1 1290 7.8 7.2
102
A6: 541STC507 – SJR @ Patterson continued…
Date TimeTemp (ºC)
Field SC (umhos) pH
Dissolved Oxygen (mg/L)
Turbidity (ntu)
7/5/2001 12:07 PM 26.4 1230 7.9 7.97/11/2001 9:10 AM 24.2 1230 7.8 9.77/19/2001 9:27 AM 24.3 1370 7.9 12.87/26/2001 12:00 PM 26.3 1230 8.2 11.98/2/2001 1:37 PM 27.2 1210 8.3 11.58/9/2001 12:20 PM 27.4 1350 8.4 12.38/16/2001 12:48 PM 24.9 1130 8.2 10.58/23/2001 12:34 PM 24.1 1240 7.8 10.58/30/2001 12:54 PM 26.2 1460 8.3 11.59/6/2001 12:34 PM 23.1 1350 8.2 10.99/13/2001 1:24 PM 24.2 1200 8.1 11.59/20/2001 8:16 AM 21.6 1260 7.7 7.09/27/2001 8:52 AM 20.9 1220 7.8 7.310/4/2001 11:26 AM 22.3 1330 7.8 8.5
10/11/2001 12:12 PM 18.8 1190 7.8 7.910/18/2001 2:50 PM 20.0 975 7.8 8.110/25/2001 2:18 PM 16.4 670 7.7 8.811/1/2001 12:42 PM 16.5 640 7.8 8.211/8/2001 1:31 PM 15.9 871 8.2 10.0
11/15/2001 11:54 AM 15.8 893 7.9 8.411/20/2001 9:15 AM 14.4 991 7.7 8.411/29/2001 11:35 AM 12.7 1010 7.5 NA12/6/2001 12:08 PM 10.9 1030 7.8 10.8
12/13/2001 11:50 AM 10.2 1170 7.8 10.512/20/2001 8:47 AM 9.8 1300 7.8 10.112/27/2001 10:23 AM 10.6 1230 7.8 10.91/3/2002 12:30 PM 13.1 582 7.6 9.01/10/2002 1:05 PM 12.3 1030 7.8 9.31/17/2002 11:39 AM 8.9 1430 7.7 11.01/24/2002 9:15 AM 8.2 1620 7.7 NA1/31/2002 9:00 AM 7.7 1560 8.1 11.42/7/2002 11:38 AM 11.2 1410 8.1 11.62/14/2002 12:08 PM 12.9 1190 7.9 9.82/21/2002 8:30 AM 14.3 1420 7.8 9.92/28/2002 12:35 PM 16.5 1660 8.0 9.73/7/2002 2:20 PM 15.9 1610 7.9 8.73/14/2002 1:00 PM 14.3 1710 8.0 10.1
103
A6: 541STC507 – SJR @ Patterson continued…
Date TimeTemp (ºC)
Field SC (umhos) pH
Dissolved Oxygen (mg/L)
Turbidity (ntu)
3/21/2002 1:10 PM 16.4 1640 7.6 8.93/28/2002 3:31 PM 19.1 1690 8.0 11.14/4/2002 11:29 AM 19.7 1820 8.1 8.84/11/2002 1:07 PM 21.0 1580 7.9 9.54/18/2002 10:39 AM 16.7 1270 7.9 9.14/25/2002 8:29 AM 19.7 1130 7.8 7.95/2/2002 11:02 AM 18.0 887 7.9 9.45/9/2002 12:48 PM 18.9 661 8.3 10.05/16/2002 12:20 PM 22.2 988 7.4 NA NA5/23/2002 9:15 AM 18.1 1120 7.6 NA5/30/2002 9:43 AM 25.0 1360 7.9 8.76/6/2002 10:40 AM 25.7 1280 8.0 8.56/13/2002 9:02 AM 22.7 1470 7.6 NA6/20/2002 10:44 AM 24.8 1530 8.5 NA6/27/2002 12:20 PM 25.8 1320 8.5 12.27/3/2002 8:22 AM 25.1 1330 7.9 NA7/11/2002 10:05 AM 27.0 1480 8.3 NA7/18/2002 12:05 PM 25.9 1580 8.5 12.6 60.07/25/2002 11:04 AM 24.5 1170 8.1 9.27/30/2002 10:22 AM 24.3 1420 7.9 8.9 72.48/1/2002 11:44 AM 25.8 1160 8.2 9.88/8/2002 12:26 PM 24.8 1420 8.5 13.78/15/2002 11:10 AM 25.3 1560 8.2 10.68/22/2002 11:25 AM 23.4 1330 8.1 9.98/29/2002 10:44 AM 23.1 1260 8.3 NA9/5/2002 10:57 AM 22.6 1520 8.1 NA9/12/2002 11:05 AM 23.2 1390 7.9 9.59/19/2002 11:30 AM 23.0 1330 7.8 8.8 NA9/26/2002 9:36 AM 21.4 1280 7.6 8.410/3/2002 11:37 AM 16.8 1240 7.8 9.9
10/10/2002 9:13 AM 20.3 1400 7.8 7.410/17/2002 11:28 AM 17.7 1120 7.8 9.4 34.510/24/2002 8:41 AM 15.4 571 7.4 8.510/31/2002 12:37 PM 14.8 960 7.8 8.4 31.811/7/2002 11:25 AM 14.1 1120 7.8 9.1
11/14/2002 11:59 AM 15.0 1030 7.7 8.411/21/2002 9:20 AM 13.1 1180 7.7 8.7 36.011/26/2002 8:41 AM 12.4 1280 7.8 9.6
104
A6: 541STC507 – SJR @ Patterson continued…
Date TimeTemp (ºC)
Field SC (umhos) pH
Dissolved Oxygen (mg/L)
Turbidity (ntu)
12/5/2002 11:20 AM 11.3 1020 7.8 11.6 25.312/12/2002 11:13 AM 11.4 1380 7.5 11.512/19/2002 11:09 AM 9.9 1110 7.9 NA 71.712/24/2002 8:40 AM 8.4 943 7.2 11.51/2/2003 9:47 AM 9.9 1160 7.8 13.91/9/2003 12:02 PM 10.4 1520 7.7 11.41/16/2003 9:26 AM 11.5 1320 7.7 9.3 51.21/23/2003 10:42 AM 11.7 1600 7.6 14.61/30/2003 12:19 PM 13.6 1620 7.7 9.6 40.22/6/2003 8:17 AM 9.7 1640 7.8 10.52/13/2003 9:37 AM 11.9 1660 7.7 9.7 35.52/20/2003 8:38 AM 11.4 1570 7.8 11.4 68.22/27/2003 10:48 AM 14.4 1580 7.8 8.83/6/2003 2:02 PM 16.0 1670 7.8 12.2 NA3/13/2003 12:07 PM 18.4 1620 7.9 9.7 46.43/20/2003 11:47 AM 16.4 1780 8.0 9.8 41.83/27/2003 11:33 AM 17.0 1640 8.0 9.8 50.64/3/2003 9:35 AM 15.9 1640 7.5 9.0 37.34/10/2003 12:10 PM 20.5 1700 8.1 10.5 57.04/17/2003 12:52 PM 17.0 1050 7.8 9.3 40.54/24/2003 12:15 PM 17.2 1050 7.9 9.2 33.05/1/2003 12:13 PM 18.7 1090 7.9 10.5 NA5/8/2003 11:13 AM 16.6 594 7.6 9.1 32.15/15/2003 11:49 AM 20.6 976 7.8 9.75/22/2003 1:26 PM 25.0 1260 8.3 12.2 12.45/29/2003 12:00 PM 26.8 1330 7.9 10.06/5/2003 1:38 PM 26.9 1350 8.1 10.6 52.66/12/2003 12:28 PM 24.7 1450 8.1 11.3 75.16/19/2003 1:03 PM 25.8 1480 8.4 8.1 65.16/26/2003 12:07 PM 25.6 1160 8.1 9.6 80.47/3/2003 11:25 AM 25.4 1270 8.5 11.27/10/2003 11:42 AM 26.4 1350 8.6 12.17/17/2003 11:40 AM 27.7 1330 8.2 9.97/24/2003 11:45 AM 27.6 1350 8.1 9.5 1707/31/2003 12:20 PM 26.2 1260 8.0 8.5 85.08/7/2003 11:46 AM 24.5 1170 8.5 11.9 49.08/14/2003 11:03 AM 23.7 1280 8.4 11.6
105
A6: 541STC507 – SJR @ Patterson continued…
Date TimeTemp (ºC)
Field SC (umhos) pH
Dissolved Oxygen (mg/L)
Turbidity (ntu)
8/21/2003 11:19 AM 25.0 1410 8.3 11.4 39.08/28/2003 11:38 AM 24.0 1400 8.2 10.6 35.49/4/2003 11:01 AM 25.3 1390 8.1 9.4 46.19/11/2003 2:03 PM 24.5 1470 8.1 11.1 46.49/18/2003 12:18 PM 21.0 1390 7.9 9.9 27.39/25/2003 12:55 PM 23.0 1260 8.0 9.2 37.310/2/2003 12:20 PM 21.5 1160 7.9 9.3 29.010/9/2003 11:46 AM 21.0 1190 7.8 8.2 32.9
10/16/2003 9:12 AM 17.2 1150 7.6 10.2 12.410/23/2003 12:55 PM 19.4 710 7.7 8.5 50.910/30/2003 11:15 AM 17.6 1030 7.8 8.4 29.211/6/2003 12:03 PM 14.1 995 7.9 10.2 31.8
11/13/2003 10:23 AM 13.9 1130 7.9 9.2 30.011/20/2003 11:45 AM 14.3 1100 7.9 10.4 NA11/26/2003 10:26 AM 9.2 1200 7.8 11.2 18.312/4/2003 10:55 AM 12.5 1300 7.9 10.8
12/11/2003 10:36 AM 11.9 1300 7.8 11.3 NA12/18/2003 11:21 AM 10.2 1310 8.0 11.6 NA12/23/2003 11:08 AM 11.5 1330 7.9 13.4 NA12/30/2003 11:44 AM 8.9 1240 7.9 12.9 NA1/8/2004 10:29 AM 9.4 1230 7.9 8.6 NA1/15/2004 11:31 AM 10.4 1420 7.8 10.3 NA1/22/2004 11:51 AM 10.0 1530 7.9 16.3 30.11/29/2004 12:03 PM 12.0 1520 7.9 10.6 NA2/5/2004 11:01 AM 11.3 1370 7.8 13.6 42.62/12/2004 10:54 AM 11.3 1590 7.8 12.8 NA2/19/2004 10:45 AM 13.7 1460 7.9 12.1 NA2/26/2004 11:32 AM 12.3 935 7.8 8.9 NA3/4/2004 10:56 AM 12.9 1130 8.0 10.4 72.53/11/2004 11:48 AM 18.3 1460 8.0 9.2 NA3/18/2004 10:11 AM 19.6 1730 8.0 10.53/25/2004 12:34 PM 18.7 1600 8.1 9.5 38.64/1/2004 11:33 AM 17.3 1690 8.1 11.34/8/2004 11:45 AM 19.6 1660 8.0 10.0 24.04/15/2004 12:43 PM 19.7 1330 8.0 10.1 31.64/22/2004 11:39 AM 17.7 1100 8.0 10.9 58.84/29/2004 1:45 PM 19.5 878 8.0 NA 31.5
106
A6: 541STC507 – SJR @ Patterson continued…
Date TimeTemp (ºC)
Field SC (umhos) pH
Dissolved Oxygen (mg/L)
Turbidity (ntu)
5/6/2004 12:29 PM 20.2 545 7.9 10.9 30.35/13/2004 12:45 PM 19.4 589 7.9 15.2 38.55/20/2004 11:43 AM 21.5 1180 7.8 9.1 70.55/27/2004 11:46 AM 24.5 1400 8.1 NA NA6/3/2004 12:13 PM 24.9 1590 8.3 11.3 42.56/10/2004 1:15 PM 24.7 1680 8.4 13.1 47.56/17/2004 12:29 PM 26.7 1740 8.5 13.8 51.16/24/2004 12:18 PM 25.3 1460 8.4 12.2 NA7/1/2004 11:25 AM 25.4 1550 8.4 14.5 NA7/8/2004 12:28 PM 27.2 1490 8.5 13.9 NA7/15/2004 12:20 PM 26.3 1590 8.5 15.9 NA7/22/2004 8:53 AM 25.5 1450 8.1 9.7 NA7/29/2004 11:48 AM 26.2 1600 8.4 12.3 NA8/5/2004 11:18 AM 25.1 1280 8.2 11.0 NA8/12/2004 11:35 AM 26.5 1450 8.1 9.1 NA8/19/2004 8:47 AM 24.7 1270 8.0 8.1 NA8/26/2004 12:10 PM 24.2 1020 8.1 8.5 NA9/2/2004 11:43 AM 24.6 1600 7.9 11.3 NA9/9/2004 8:26 AM 23.3 1250 7.8 7.4 NA9/16/2004 8:35 AM 21.1 1440 7.3 7.3 NA9/23/2004 2:21 PM 23.2 1340 7.9 10.7 NA9/30/2004 12:12 PM 21.3 1240 7.8 9.4 NA10/7/2004 10:54 AM 20.8 1110 7.7 8.6
10/14/2004 10:49 AM 19.0 1030 7.6 8.610/21/2004 12:01 PM 16.1 552 NA 8.510/28/2004 11:31 AM 13.7 692 7.7 12.011/4/2004 12:32 PM 13.7 1030 7.9 10.3
11/11/2004 10:56 AM 14.7 1040 7.7 8.711/18/2004 11:33 AM 14.1 988 7.7 9.011/23/2004 8:39 AM 9.9 1110 7.8 10.212/2/2004 12:16 PM 8.9 1230 7.8 12.012/9/2004 11:13 AM 11.7 1130 7.8 11.0
12/16/2004 11:42 AM 11.9 1040 7.8 10.812/22/2004 9:15 AM 9.1 1270 7.9 12.912/29/2004 8:32 AM 9.9 1230 7.8 9.61/6/2005 10:00 AM 9.3 483 7.5 11.7
107
A6: 541STC507 – SJR @ Patterson continued…
Date TimeTemp (ºC)
Field SC (umhos) pH
Dissolved Oxygen (mg/L)
Turbidity (ntu)
1/13/2005 11:58 AM 9.7 424 7.5 9.81/20/2005 12:16 PM 8.9 737 7.5 9.51/27/2005 11:21 AM 11.3 1210 7.7 8.72/3/2005 12:04 PM 11.6 1050 7.6 8.82/10/2005 11:02 AM 12.9 1370 7.8 10.02/17/2005 12:31 PM 14.3 1200 7.8 11.32/24/2005 11:27 AM 15.1 973 7.5 8.83/3/2005 10:55 AM 15.8 1060 7.7 9.43/10/2005 12:43 PM 19.3 1410 7.9 9.53/17/2005 11:16 AM 17.0 1790 7.7 14.43/24/2005 12:04 PM 15.6 884 7.9 10.23/31/2005 11:01 AM 13.8 413 7.6 10.34/7/2005 11:44 AM 15.3 548 7.6 10.04/14/2005 11:28 AM 14.2 571 7.8 10.74/21/2005 11:58 AM 15.8 588 8.0 11.14/28/2005 11:07 AM 16.2 611 7.1 13.05/5/2005 11:53 AM 17.3 658 7.7 10.05/12/2005 11:23 AM 17.8 463 7.8 10.05/19/2005 11:58 AM 18.3 265 7.5 8.75/26/2005 11:50 AM 21.3 157 7.6 7.36/2/2005 11:43 AM 20.6 140 7.5 7.86/9/2005 10:35 AM 19.4 210 7.2 7.76/16/2005 11:45 AM 21.9 492 7.4 9.06/23/2005 1:05 PM 21.2 466 NA 9.46/30/2005 12:26 PM 24.4 536 7.6 9.57/7/2005 11:30 AM 23.3 652 7.5 10.47/13/2005 8:41 AM 24.4 797 7.7 8.97/21/2005 12:00 PM 26.0 960 7.9 9.07/28/2005 12:50 PM 26.3 948 8.0 9.68/4/2005 11:09 AM 25.6 804 7.8 9.48/11/2005 12:29 PM 25.7 887 8.0 9.28/18/2005 12:26 PM 23.9 850 7.9 8.88/25/2005 11:24 AM 22.9 682 7.7 8.69/1/2005 11:16 AM 23.3 1070 7.8 11.49/8/2005 11:20 AM 22.5 957 7.7 9.19/15/2005 11:24 AM 19.7 675 7.6 9.69/21/2005 9:31 AM 19.6 585 7.7 9.79/22/2005 12:42 PM 21.7 683 7.6 9.2
108
A6: 541STC507 – SJR @ Patterson continued…
Date TimeTemp (ºC)
Field SC (umhos) pH
Dissolved Oxygen (mg/L)
Turbidity (ntu)
9/29/2005 11:23 AM 20.2 618 7.6 8.7
Count 262 262 260 215 55Min 6.9 140 6.6 7.0 12.4Max 27.7 1820 8.6 16.3 170Mean 18.2 1176 7.8 10.2 46.0Geo Mean 17.2 1110 7.8 10.0 41.5Median 18.4 1230 7.8 9.8 40.2Quartile 1 13.5 988 7.7 9.0 31.8Quartile 3 23.3 1420 8.0 11.2 51.9NOTE: For values reported as < (less than), half the detection limit was used.
NA = Data not applicableINA = Site was inaccessibleDRY = Site had no flow
109
A6: 541STC507 – SJR @ Patterson continued…
DateTSS
(mg/L)TOC
(mg/L)Total Coli
MPNE. coli MPN
10/5/2000 5110/12/2000 52 6.510/19/2000 2.110/26/2000 40 1.511/2/2000 52 4.111/9/2000 30 3.7
11/16/2000 22 3.411/21/2000 1811/30/2000 25 1.912/7/2000 52 2.6
12/12/2000 35 2.512/21/2000 NA 3.912/28/2000 18 2.51/4/2001 14 4.71/11/2001 170 5.31/18/2001 24 5.91/25/2001 33 8.82/1/2001 34 6.42/8/2001 25 6.62/15/2001 54 3.72/22/2001 NA 2.13/1/2001 56 8.23/8/2001 99 103/15/2001 54 9.03/22/2001 42 7.63/29/2001 41 <14/5/2001 27 NA4/12/2001 41 7.04/19/2001 37 5.24/26/2001 2.75/3/2001 48 4.55/10/2001 61 3.25/17/2001 3.25/24/2001 57 4.65/31/2001 52 7.76/7/2001 61 136/14/2001 60 126/21/2001 NA 116/28/2001 56 117/5/2001 6.27/11/2001 5.6
110
A6: 541STC507 – SJR @ Patterson continued…
DateTSS
(mg/L)TOC
(mg/L)Total Coli
MPNE. coli MPN
7/19/2001 8.47/26/2001 7.18/2/2001 6.88/9/2001 108/16/2001 54 9.58/23/2001 48 128/30/2001 42 149/6/2001 44 139/13/2001 38 139/20/2001 NA 149/27/2001 34 1410/4/2001 NA 13
10/11/2001 34 2210/18/2001 48 2010/25/2001 1311/1/2001 4411/8/2001 33
11/15/2001 37 5.211/20/2001 34 NA11/29/2001 34 NA12/6/2001 42 8.9
12/13/2001 26 2.712/20/2001 24 4.812/27/2001 291/3/2002 1011/10/2002 571/17/2002 241/24/2002 181/31/2002 17 NA2/7/2002 38 NA2/14/2002 27 NA2/17/2002 352/18/2002 392/21/2002 502/28/2002 39 7.83/7/2002 283/7/2002 35 8.33/8/2002 44
111
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DateTSS
(mg/L)TOC
(mg/L)Total Coli
MPNE. coli MPN
3/9/2002 363/11/2002 423/14/2002 47 6.93/21/2002 34 5.03/28/2002 24 5.14/4/2002 36 NA4/11/2002 744/18/2002 40 5.94/25/2002 56 NA5/2/2002 60 3.65/9/2002 48 NA5/16/2002 53 NA5/23/2002 54 NA5/30/2002 NA 4.26/6/2002 79 3.66/13/2002 NA NA6/20/2002 67 4.16/27/2002 82 7.77/30/2002 >2419.6 488/15/2002 4.28/22/2002 3.88/29/2002 479/5/2002 3.79/12/2002 43 NA9/19/2002 50 NA9/26/2002 3710/3/2002 21 3.8
10/10/2002 3010/17/2002 33 4.110/24/2002 38 3.010/31/2002 29 3.911/7/2002 50 NA
11/14/2002 42 6.111/21/2002 31 5.111/26/2002 35 4.812/5/2002 25 4.4
12/12/2002 28 3.612/19/2002 57 5.71/16/2003 50 >2419.6 58
112
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DateTSS
(mg/L)TOC
(mg/L)Total Coli
MPNE. coli MPN
3/13/2003 NA 7.83/20/2003 NA 6.03/27/2003 67 4.74/3/2003 NA NA4/10/2003 NA 3.74/17/2003 38 4.54/24/2003 45 4.7 >2419.6 1795/1/2003 33 6.05/8/2003 NA 4.25/15/2003 53 4.15/22/2003 36 4.35/29/2003 65 6.26/5/2003 63 8.16/12/2003 93 5.36/19/2003 69 5.56/26/2003 71 5.87/31/2003 >2419.6 968/28/2003 >2419.6 839/25/2003 >2419.6 104
10/30/2003 >2419.6 6911/20/2003 >2419.6 731/29/2004 >2419.6 372/26/2004 >2419.6 >2419.63/11/2004 123/18/2004 9.63/25/2004 >2419.6 1944/1/2004 9.34/8/2004 8.24/15/2004 5.94/22/2004 5.84/29/2004 4.8 >2419.6 1605/6/2004 5.15/13/2004 4.95/20/2004 5.65/27/2004 6.6 >2419.6 1856/3/2004 9.16/10/2004 9.66/17/2004 11 >2419.6 1176/24/2004 >2419.6 567/1/2004 12
113
A6: 541STC507 – SJR @ Patterson continued…
DateTSS
(mg/L)TOC
(mg/L)Total Coli
MPNE. coli MPN
7/8/2004 10 >2419.6 1317/15/2004 9.97/22/2004 9.37/29/2004 9.5 >2419.6 888/5/2004 8.28/12/2004 9.2 >2419.6 848/19/2004 7.28/26/2004 >2419.6 1089/16/2004 >2419.6 1319/30/2004 >2419.6 140
10/14/2004 >2419.6 12910/28/2004 40 5.4 >2419.6 14711/4/2004 29 7.1 >2419.6 88
11/11/2004 38 7.411/18/2004 52 7.2 >2419.6 17911/23/2004 34 6.212/2/2004 38 6.012/9/2004 42 5.7 >2419.6 82
12/16/2004 44 7.212/22/2004 35 6.2 >2419.6 5912/29/2004 73 6.01/6/2005 75 11 >2419.6 3871/13/2005 66 9.81/20/2005 36 >2419.6 241/27/2005 50 8.52/3/2005 39 13 >2419.6 2012/10/2005 48 7.02/17/2005 92 9.8 >2419.6 >2419.62/24/2005 49 113/3/2005 54 113/10/2005 51 NA >2419.6 563/17/2005 43 8.93/24/2005 49 7.7 >2419.6 11203/31/2005 28 6.64/7/2005 28 5.7 2420 674/14/2005 40 NA4/21/2005 35 4.3 >2419.6 314/28/2005 39 NA5/5/2005 NA 4.4 >2419.6 162
114
115
DateTSS
(mg/L)TOC
(mg/L)Total Coli
MPNE. coli MPN
5/12/2005 44 5.55/19/2005 42 4.3 >2419.6 3285/26/2005 31 4.66/2/2005 20 4.36/9/2005 30 NA >2419.6 696/16/2005 60 4.16/23/2005 69 4.3 >2419.6 1056/30/2005 76 3.17/7/2005 61 3.4 >2419.6 1417/13/2005 57 3.17/21/2005 70 3.8 >2419.6 1317/28/2005 54 3.88/4/2005 43 4.1 >2419.6 1108/11/2005 52 3.58/18/2005 81 3.5 >2419.6 5488/25/2005 42 3.29/9/9/19/29/29/2
Coun
A6: 541STC507 – SJR @ Patterson continued…
1/2005 39 4.0 >2419.6 1408/2005 40 4.1 >2419.6 1085/2005 53 3.11/2005 >2419.6 1422/2005 34 NA9/2005 30 3.1
t 156 161 46 4614 0.5 2420 24
170 2Min Max 2 2420 2420
n 46 6.6 NA NA Mean 42 5.8 2420 129ian 42 5.8 2420 114rtile 1 34 4.1 2420 7
MeaGeoMedQua 5QuaNOT
NA =INA =DRY
rtile 3 54 8.4 2420 162E: For values reported as < (less than), half the detection limit was used For values reported as > (greater than), 2420 was used
Data not applicable Site was inaccessible
= Site had no flow
A6: 541STC507 – SJR @ Patterson continued…
DateNitrate (mg/L)
Nitrate-N (mg/L)
TKN (mg/L)
Ammonia-N (mg/L)
Phosphorus (mg/L)
Ortho-phosphate-
P (mg/L)
Potassium (mg/L)
BOD 5-Day (mg/L)
BOD 10-Day (mg/L)
10/12/2000 3.3 7.210/26/2000 5 <2 0.2 <1 3.6 1.7 2.911/16/2000 1.3 2.711/30/2000 8.6 <2 0.3 <1 5.2 1.1 2.112/12/2000 1.8 3.512/28/2000 9.1 <2 0.2 <1 6.7 1.2 2.81/11/2001 4.1 6.51/25/2001 9 <2 0.4 <1 8.7 2.3 4.92/8/2001 13 <2 0.2 <1 8.4 1.9 3.52/22/2001 16 <2 0.2 <1 8.3 2.2 3.93/15/2001 15 <2 0.5 <1 9.2 2.4 4.63/29/2001 12 <2 0.3 <1 8.2 2.7 5.24/19/2001 11 <2 0.2 <1 6.4 2.1 44/26/2001 7.6 <2 <1 0.2 <1 4 2.4 45/17/2001 7.3 <2 0.2 <1 3.8 1.5 2.75/31/2001 13 <1.0 0.3 NA 6.1 2.4 4.66/7/2001 15 <1.0 0.3 <1 9.3 4.4 6.86/14/2001 17 <2 <1 7.3 3.5 6.46/21/2001 14 2.1 0.2 <1 9 5.7 10.46/28/2001 16 <2 0.3 <1 8 2.9 5.38/16/2001 18 <2 0.5 <1 68/30/2001 18 <2 0.3 <1 7.59/27/2001 15 <2 0.3 <1 7.6
10/25/2001 1.2 3.111/29/2001 NA NA NA 0.1 7.4 1.2 2.212/13/2001 1.2 2.412/27/2001 1.5 3.31/17/2002 1.6 4.4
116
A6: 541STC507 – SJR @ Patterson continued…
DateNitrate (mg/L)
Nitrate-N (mg/L)
TKN (mg/L)
Ammonia-N (mg/L)
Phosphorus (mg/L)
Ortho-phosphate-
P (mg/L)
Potassium (mg/L)
BOD 5-Day (mg/L)
BOD 10-Day (mg/L)
1/31/2002 3.2 6.22/14/2002 2.6 4.92/28/2002 2.3 4.83/14/2002 4.3 7.14/25/2002 2.4 4.25/16/2002 2 3.55/30/2002 3.5 6.16/13/2002 15 NA 0.4 0.3 7.3 3.8 7.76/20/2002 5.8 11.28/29/2002 3.7 7.49/26/2002 2.1 3.9
10/31/2002 1.5 2.311/21/2002 1.4 2.812/19/2002 3 4.61/30/2003 1.5 2.3
Count 20 NA 19 1 19 20 21 40 40Min 5.0 NA 0.5 0.5 0.2 0.1 3.6 1.1 2.1Max 18.0 NA 2.1 0.5 0.5 0.5 9.3 5.8 11.2Mean 12.7 NA 1.0 0.5 0.3 0.5 7.0 2.5 4.7Geo Mean 12.1 NA 1.0 0.5 0.3 0.4 6.8 2.3 4.3Median 13.5 NA 1.0 0.5 0.3 0.5 7.4 2.3 4.3Quartile 1 9.1 NA 1.0 0.5 0.2 0.5 6.1 1.5 3.1Quartile 3 15.3 NA 1.0 0.5 0.3 0.5 8.3 3.2 6.1NOTE: For values reported as < (less than), half the detection limit was used.
NA = Data not applicableINA = Site was inaccessibleDRY = Site had no flow
117
A6: 541STC507 – SJR @ Patterson continued…
DateHardness
(mg/L)
Total Arsenic (ug/L)
Total Cadmium
(ug/L)
Total Chromium
(ug/L)
Total Copper (ug/L)
Total Lead (ug/L)
Total Nickel (ug/L)
Total Zinc (ug/L)
Total Mercury (ug/L)
10/26/2000 2 2.2 <5 <511/30/2000 180 1.5 1.4 <5 <5 4.212/28/2000 240 1.2 1.9 <5 <5 3.51/25/2001 280 2.1 2.8 <5 <5 3.52/22/2001 330 2.1 2.9 <5 <5 3.83/29/2001 320 2.8 3.2 <5 4.2 3.94/26/2001 140 2.3 3.6 <5 <5 8.45/31/2001 260 2.7 3.3 <5 <5 5.26/7/2001 280 3.2 <1 3.3 4.1 <5 5.5 6.8 <0.26/14/2001 330 3.1 <1 3.2 3.9 <5 5.5 10 <0.26/21/2001 NA 3.9 <1 3.1 3.6 <5 5.3 6.1 <0.26/28/2001 300 3.3 <1 3.5 3.6 <5 <5 6.0 <0.27/26/2001 NA NA 3.5 3.1 <5 <5 6.2 NA8/30/2001 310 3.5 <1 2.5 2.4 <5 <5 3.39/27/2001 260 4.3 <1 <1 1.8 <5 <5 2.1 <0.2
10/25/2001 140 <4 <0.1 <1 1.4 <5 <5 <2 <0.211/29/2001 210 <4 <0.1 1.1 <1 <5 <5 3.8 <0.212/27/2001 <4 <0.1 3.8 4.0 <5 <5 8.5 <0.21/31/2002 <4.0 <0.1 <1.0 NA <5.0 <5.0 <2.0 <0.22/28/2002 <4.0 <0.1 1.6 3.4 <5.0 <5.0 4.4 <0.23/28/2002 <4.0 <0.1 1.5 3.0 <5.0 7.1 5.0 <0.24/25/2002 <4.0 <0.1 <1.0 1.1 <5.0 <5.0 <2.0 <0.25/30/2002 <4.0 <0.1 3.1 3.2 <5.0 <5.0 5.8 <0.26/20/2002 310 5.5 <0.1 3.7 3.7 <5.0 <5.0 6.1 <0.29/26/2002 280 6.6 <0.1 2.9 NA <5.0 <5.0 4.4 <0.2
10/31/2002 190 <4.0 <0.1 2 1.9 <5.0 <5.0 3.4 <0.211/21/2002 250 4.2 <0.1 3.4 4.3 <5.0 5.2 6.3 <0.23/27/2003 350 4.8 NA 3.8 3.6 <5.0 <5.0 6.1 <0.24/24/2003 220 <4.0 <0.1 NA NA NA <5.0 4.2 <0.25/29/2003 290 4.2 <0.1 2.6 4.8 <5.0 <5.0 6.9 <0.26/26/2003 260 <4.0 <0.1 4.8 4.8 <5.0 6.9 8.7 <0.2
118
A6: 541STC507 – SJR @ Patterson continued…
DateHardness
(mg/L)
Total Arsenic (ug/L)
Total Cadmium
(ug/L)
Total Chromium
(ug/L)
Total Copper (ug/L)
Total Lead (ug/L)
Total Nickel (ug/L)
Total Zinc (ug/L)
Total Mercury (ug/L)
Count 22 22 21 30 28 30 31 30 21Min 140.0 2.0 0.1 0.5 0.5 2.5 2.5 1.0 0.1Max 350.0 6.6 0.5 4.8 4.8 2.5 7.1 10.0 0.1Mean 260.5 3.1 0.2 2.4 3.0 2.5 3.2 5.0 0.1Geo Mean 252.9 2.9 0.1 2.0 2.7 2.5 3.0 4.3 0.1Median 270.0 2.6 0.1 2.6 3.2 2.5 2.5 4.7 0.1Quartile 1 225.0 2.0 0.1 1.5 2.1 2.5 2.5 3.6 0.1Quartile 3 307.5 4.1 0.5 3.3 3.6 2.5 2.5 6.2 0.1NOTE: For values reported as < (less than), half the detection limit was used.
NA = Data not applicableINA = Site was inaccessibleDRY = Site had no flow
119
A6: 541STC507 – SJR @ Patterson continued…
DateHardness
(mg/L)
Dissolved Arsenic (ug/L)
Dissolved Cadmium
(ug/L)
Dissolved Chromium
(ug/L)
Dissolved Copper (ug/L)
Dissolved Lead (ug/L)
Dissolved Nickel (ug/L)
Dissolved Zinc
(ug/L)
Dissolved Mercury (ug/L)
10/26/2000 <1 <1 <5 <5 <211/30/2000 180 <1 <1 <5 <5 <212/28/2000 240 <1 <1 <5 <5 <21/25/2001 280 <1 <1 <5 <5 <22/22/2001 330 <1 1.0 <5 <5 <23/29/2001 320 <1 1.8 <5 <5 <24/26/2001 140 <1 1.4 <5 <5 3.25/31/2001 260 <1 <1 <5 <5 <26/7/2001 280 2.2 <1 <1 1.5 <5 <5 2.6 <0.26/14/2001 330 2.7 <1 <1 1.3 <5 <5 <2 <0.26/21/2001 NA 3.3 <1 <1 <1 <5 <5 <2 <0.26/28/2001 300 3.3 <1 <1 <1 <5 2.7 <2 <0.27/26/2001 NA NA NA NA NA NA NA NA8/30/2001 310 2.7 <1 <1 1.2 <5 <5 <29/27/2001 260 <4 <1 <1 1.1 <5 <5 <2 <0.2
10/25/2001 140 <4 <0.1 <1 1.4 <5 <5 2.4 <0.211/29/2001 210 <4 <0.1 <1 <1 <5 <5 2.4 <0.212/27/2001 <4 <0.1 <1 1.0 <5 <5 2.4 <0.21/31/2002 <4.0 <0.1 <1.0 NA <5.0 <5.0 3 <0.22/28/2002 <4.0 <0.1 <1.0 4.6 <5.0 <5.0 <2.0 <0.23/28/2002 <4.0 <0.1 <1.0 2.0 <5.0 8.2 4.2 <0.24/25/2002 4.3 <0.1 <1.0 1.1 <5.0 <5.0 NA <0.25/30/2002 <4.0 <0.1 <1.0 2.2 <5.0 <5.0 <2.0 <0.26/20/2002 310 <4.0 <0.1 <1.0 2.3 <5.0 <5.0 2.4 <0.29/26/2002 280 5.4 <0.1 <1.0 3.8 <5.0 <5.0 <2.0 <0.2
10/31/2002 190 <4.0 <0.1 <1.0 1.5 <5.0 <5.0 <2.0 <0.211/21/2002 250 <4.0 <0.1 <1.0 <1.0 <5.0 <5.0 <2.0 <0.2
120
A6: 541STC507 – SJR @ Patterson continued…
DateHardness
(mg/L)
Dissolved Arsenic (ug/L)
Dissolved Cadmium
(ug/L)
Dissolved Chromium
(ug/L)
Dissolved Copper (ug/L)
Dissolved Lead (ug/L)
Dissolved Nickel (ug/L)
Dissolved Zinc
(ug/L)
Dissolved Mercury (ug/L)
Count 18 18 18 26 25 26 26 25 17Min 140.0 2.0 0.1 0.5 0.5 2.5 2.5 1.0 0.1Max 330.0 5.4 0.5 0.5 4.6 2.5 8.2 4.2 0.1Mean 256.1 2.6 0.2 0.5 1.3 2.5 2.7 1.6 0.1Geo Mean 248.0 2.4 0.1 0.5 1.1 2.5 2.6 1.4 0.1Median 270.0 2.0 0.1 0.5 1.1 2.5 2.5 1.0 0.1Quartile 1 217.5 2.0 0.1 0.5 0.5 2.5 2.5 1.0 0.1Quartile 3 307.5 2.7 0.5 0.5 1.5 2.5 2.5 2.4 0.1NOTE: For values reported as < (less than), half the detection limit was used.
NA = Data not applicableINA = Site was inaccessibleDRY = Site had no flow
121
A6: 541STC507 – SJR @ Patterson continued…
DateChloride (mg/L)
Sulfate (mg/L)
Calcium (mg/L)
Magnesium (mg/L)
TDS (mg/L)
Carbonate (mg/L)
Bicarbonate (mg/L)
Total Alkalinity
(mg/L)Sodium (mg/L)
11/30/2000 110 120 41 21 550 <1 140 120 11012/28/2000 160 170 51 28 700 <1 180 150 1501/25/2001 180 220 59 34 810 <1 210 170 1902/22/2001 180 250 70 36 930 <1 200 160 2003/29/2001 170 230 69 37 1100 <1 190 150 1904/26/2001 95 30 15 400 <1 80 80 625/31/2001 140 180 57 28 700 <1 140 140 1406/7/2001 150 200 62 31 710 <1 170 140 1506/14/2001 190 260 74 36 890 <1 190 160 1906/21/2001 180 240 69 33 890 <1 200 160 1806/28/2001 160 220 67 33 780 <1 180 140 1608/30/2001 190 210 73 34 870 <1 220 180 1809/27/2001 NA 160 56 29 750 <1 NA NA 160
10/25/2001 95 78 30 15 390 <1 110 NA 7811/29/2001 150 140 42 24 610 <1 160 130 1303/27/2003 240 280 72 414/24/2003 140 180 47 255/29/2003 190 230 65 316/26/2003 140 200 59 28
Count 17 19 19 19 15 15 14 13 15Min 95 78 30 15 390 0.5 80 80 62Max 240 280 74 41 1100 0.5 220 180 200Mean 160 190 58 29 740 0.5 170 150 150Geo Mean 160 180 56 28 710 0.5 160 140 140Median 160 200 59 31 750 0.5 180 150 160Quartile 1 140 170 49 27 660 0.5 150 140 140Quartile 3 180 230 69 34 880 0.5 200 160 190NOTE: For values reported as < (less than), half the detection limit was used.
NA = Data not applicableINA = Site was inaccessibleDRY = Site had no flow
122
123
A6: 541STC507 – SJR @ Patterson continued…
Date Result Control Result Control
Result (million/m
l)
Control (million/
ml)MDD (%)
11/18/2004 3.47** 1.79 15.012/22/2004 5.28** 1.95 N/A1/20/2005 5.04** 1.92 18.02/17/2005 4.95** 1.78 43.03/24/2005 N/A N/A N/A4/21/2005 3.53** 1.63 4.05/19/2005 2.63 1.94 4.36/23/2005 N/A N/A N/A7/21/2005 3.52** 1.72 25.08/18/2005 3.79** 1.76 32.09/22/2005 4.35 1.72 N/A
Count 0 0 0 0 9 9 7
* Significantly reduced from the lab control.** Significantly greater than the lab control.^ Fish were from a "forced hatch," duplicate failed QA.1 Duplicate sample for the set was low - 77% recovery.
3 Samples qualified, but duplicate sample recovery for the set was high - 126% (53.8%/42.5%)NA = Data not applicableINA = Site was inaccessibleDRY = Site had no flow
2 Testing for the Fathead minnow was initiated when samples were approx. 48h old due to untimely shipping of fish by fish supplier.
96h Acute Fathead Minnow
(% Survival)
48h Acute Ceriodaphnia Dubia
(% Survival) Algae Cell Growth
124
A6: 541STC507 – SJR @ Patterson continued…
DateResult
(% Survival)
Control (%
Survival)
Avg Dry Weight Result (mg)
Avg Dry Weight Control
(mg)
Growth MDD (%)
Result (% Survival)
Control (%
Survival)
Avg # Young /
Adult Result
Avg # Young /
Adult Control
Repro MDD (%)
11/18/2004 85.7* 100.0 0.48 0.46 32 100.0 100.0 18.3 18.4 1212/22/2004 92.9 95.2 0.51 0.61 N/A 100.0 100.0 24.0 24.7 N/A1/20/2005 95.0 97.4 0.83 0.92 16 100.0 100.0 25.4 15.9 252/17/2005 90.2 97.5 0.39 0.38 14 100.0 100.0 22.9* 28.8 9.23/24/2005 95.1 97.5 0.52 0.41 7.3 100.0 100.0 14.9 18.3 194/21/2005 N/A N/A N/A N/A N/A 100.0 100.0 9.5* 19.4 155/19/2005 77.5* 100.0 0.53 0.62 17 100.0 100.0 16.7* 20.50 156/23/2005 N/A N/A N/A N/A N/A 100.0 100.0 24.7 20.90 107/21/2005 97.5 100.0 0.65 0.62 5.3 100.0 100.0 28.5 22.1 118/18/2005 N/A N/A N/A N/A N/A 100.0 100.0 29.4 21.5 189/22/2005 92.5 97.5 0.37* 0.5 13.0 100.0 90.0 13.6* 19.9 14
Count 8 8 8 8 7 11 11 11 11 10
* Significantly reduced from the lab control.** Significantly greater than the lab control.^ Fish were from a "forced hatch," duplicate failed QA.1 Duplicate sample for the set was low - 77% recovery.
3 Samples qualified, but duplicate sample recovery for the set was high - 126% (53.8%/42.5%)NA = Data not applicableINA = Site was inaccessibleDRY = Site had no flow
Chronic Ceriodaphnia Dubia - 6 dayChronic Fathead Minnow - 7day
2 Testing for the Fathead minnow was initiated when samples were approx. 48h old due to untimely shipping of fish by fish supplier.
125
A7: 541STC510 – SJR @ Maze Station Code:541STC510
Location: Latitude 37.64194, Longitude -121.22778
Date TimeTemp (ºC)
Field SC (umhos) pH
Dissolved Oxygen (mg/L)
Turbidity (ntu)
10/5/2000 1:30 PM 20.9 498 7.910/12/2000 8:15 AM 15.6 443 7.710/19/2000 12:15 PM 19.2 437 7.710/26/2000 9:55 AM 16.0 371 7.611/2/2000 12:40 PM 15.0 515 7.211/9/2000 1:35 PM 13.7 676 7.7
11/16/2000 8:00 AM 10.5 739 6.911/21/2000 10:30 AM 11.1 752 7.711/30/2000 8:03 AM 9.9 758 7.712/7/2000 1:20 PM 12.1 865 7.8
12/12/2000 1:45 PM 13.1 919 8.012/21/2000 9:15 AM 9.6 933 7.612/28/2000 7:53 AM 7.4 930 7.61/4/2001 12:53 PM 9.9 933 7.71/11/2001 8:37 AM 9.3 843 7.21/18/2001 2:03 PM 10.0 971 7.31/25/2001 8:14 AM 9.3 1080 7.62/1/2001 8:51 AM 8.6 1050 6.82/8/2001 11:00 AM 11.6 1170 7.82/15/2001 8:55 AM 9.9 801 7.42/22/2001 9:15 AM 11.0 725 7.63/1/2001 1:10 PM 14.0 549 7.83/8/2001 1:45 PM 15.4 511 7.83/15/2001 8:55 AM 15.1 1060 7.63/22/2001 8:50 AM 18.9 1300 7.63/29/2001 2:46 PM 20.9 1150 8.04/5/2001 9:11 AM 15.4 1130 7.34/12/2001 1:37 PM 16.1 923 7.64/19/2001 9:30 AM 16.5 999 7.94/26/2001 2:30 PM 22.5 476 7.95/3/2001 2:10 PM 19.5 463 7.55/10/2001 12:10 PM 21.6 476 7.75/17/2001 8:40 AM 20.1 433 7.05/24/2001 2:40 PM 27.5 982 7.75/31/2001 8:12 AM 24.2 929 7.36/7/2001 8:30 AM 22.9 997 8.1 8.86/14/2001 INA INA INA INA INA6/21/2001 9:04 AM 25.9 1140 8.3 10.3
126
A7: 541STC510 – SJR @ Maze continued…
Date TimeTemp (ºC)
Field SC (umhos) pH
Dissolved Oxygen (mg/L)
Turbidity (ntu)
6/28/2001 8:42 AM 22.6 1060 7.9 7.47/5/2001 12:43 PM 27.0 681 8.2 10.17/11/2001 8:30 AM 23.9 1020 7.9 8.77/19/2001 8:42 AM 23.9 988 7.9 10.57/26/2001 12:49 PM 26.3 923 8.5 13.18/2/2001 2:16 PM 26.2 947 8.5 12.18/9/2001 1:36 PM 27.4 953 8.5 11.18/16/2001 1:57 PM 25.4 882 8.5 12.18/23/2001 1:51 PM 24.0 887 8.2 10.78/30/2001 1:58 PM 25.6 964 8.4 11.19/6/2001 1:25 PM 23.1 898 8.5 11.19/13/2001 2:30 PM 23.3 963 8.2 11.09/20/2001 7:47 AM 22.0 847 7.7 6.59/27/2001 8:08 AM 21.0 925 7.9 6.910/4/2001 12:12 PM 22.5 928 8.0 9.9
10/11/2001 12:58 PM 18.9 849 7.8 8.310/18/2001 2:12 PM 19.7 884 7.8 8.710/25/2001 3:02 PM 16.4 559 7.8 9.111/1/2001 1:49 PM 16.7 594 7.9 8.411/8/2001 2:06 PM 15.3 755 8.3 10.3
11/15/2001 11:42 AM 16.0 766 8.0 8.711/20/2001 8:28 AM 14.5 880 7.7 8.311/29/2001 12:45 PM 13.0 907 7.5 NA12/6/2001 1:00 PM 11.1 917 7.8 10.7
12/13/2001 1:09 PM 10.4 1020 7.8 10.512/20/2001 8:13 AM 9.8 1100 7.8 10.012/27/2001 9:49 AM 10.9 1040 7.9 10.81/3/2002 1:39 PM 12.9 449 7.6 9.11/10/2002 1:57 PM 12.9 849 7.2 11.11/17/2002 12:37 PM 9.0 1160 7.8 10.81/24/2002 8:37 AM 8.2 1310 7.5 14.41/31/2002 8:15 AM 7.9 1240 8.3 11.72/7/2002 12:33 PM 11.5 1290 7.9 11.72/14/2002 1:28 PM 13.3 1310 7.9 10.32/21/2002 7:59 AM 14.6 1250 7.7 9.62/28/2002 1:49 PM 16.2 1370 8.0 9.43/7/2002 12:05 PM 15.7 1380 7.9 9.53/14/2002 1:31 PM 14.0 1290 8.0 10.83/21/2002 2:12 PM 16.1 1260 7.9 8.73/28/2002 4:05 PM 18.7 1300 8.3 10.74/4/2002 11:57 AM 19.5 1230 8.1 9.24/11/2002 2:38 PM 20.5 1110 8.0 10.0
127
A7: 541STC510 – SJR @ Maze continued…
Date TimeTemp (ºC)
Field SC (umhos) pH
Dissolved Oxygen (mg/L)
Turbidity (ntu)
4/18/2002 11:13 AM 14.9 645 8.0 9.84/25/2002 7:53 AM 18.3 550 7.7 8.65/2/2002 12:03 PM 16.6 481 8.0 10.45/9/2002 INA INA INA INA INA5/16/2002 1:30 PM 23.0 691 7.5 NA NA5/23/2002 10:05 AM 19.2 812 7.6 NA5/30/2002 8:50 AM 24.7 903 7.8 8.36/6/2002 11:25 AM 25.6 893 8.3 8.46/13/2002 8:23 AM 22.1 1070 7.5 NA6/20/2002 11:57 AM 25.5 1200 8.6 NA6/27/2002 1:06 PM 25.2 1020 8.9 15.27/3/2002 7:53 AM 24.4 954 8.0 NA7/11/2002 8:41 AM 26.6 1060 8.4 NA7/18/2002 1:13 PM 25.4 1030 8.7 13.8 52.47/25/2002 12:00 PM 24.5 993 8.5 11.37/31/2002 8:52 AM 24.1 1010 7.7 7.9 77.78/1/2002 12:38 PM 25.7 909 8.4 10.58/8/2002 1:39 PM 24.3 988 8.7 15.08/15/2002 11:51 AM 25.1 1030 8.5 12.08/22/2002 12:28 PM 23.4 997 8.5 12.28/29/2002 11:45 AM 23.9 922 8.7 NA9/5/2002 11:52 AM 22.1 1040 8.6 NA9/12/2002 11:47 AM 23.1 965 8.5 13.09/19/2002 12:46 PM 23.0 1030 8.1 10.8 NA9/26/2002 9:00 AM 21.6 880 7.3 8.510/3/2002 12:37 PM 16.8 974 7.9 10.4
10/10/2002 8:39 AM 20.3 968 7.9 7.810/17/2002 12:04 PM 17.6 948 8.0 9.3 17.910/24/2002 8:07 AM 15.6 469 7.3 8.610/31/2002 1:44 PM 14.6 755 7.9 8.5 27.311/7/2002 12:33 PM 13.8 902 7.8 9.0
11/14/2002 12:44 PM 15.1 910 7.7 8.711/21/2002 8:48 AM 13.2 1010 7.7 8.8 31.511/26/2002 8:07 AM 12.5 1070 7.8 9.612/5/2002 12:00 PM 11.6 1050 7.9 11.1 22.5
12/12/2002 12:15 PM 11.5 1130 7.6 10.812/19/2002 11:54 AM 9.8 793 8.0 NA 69.912/24/2002 8:12 AM 8.4 785 6.7 11.71/2/2003 9:13 AM 10.1 1020 7.8 14.01/9/2003 12:59 PM 10.6 1250 7.8 12.31/16/2003 8:51 AM 11.6 1090 7.7 9.4 48.61/23/2003 11:43 AM 12.0 1320 7.7 10.41/30/2003 1:20 PM 13.6 1320 7.8 9.9 36.7
128
A7: 541STC510 – SJR @ Maze continued…
Date TimeTemp (ºC)
Field SC (umhos) pH
Dissolved Oxygen (mg/L)
Turbidity (ntu)
2/6/2003 7:49 AM 9.8 1360 7.8 10.72/13/2003 9:02 AM 11.9 1400 7.7 9.8 48.62/20/2003 8:03 AM 11.6 1310 7.7 11.1 40.62/27/2003 11:46 AM 14.5 1290 7.8 8.73/6/2003 2:43 PM 15.8 1390 7.8 11.9 NA3/13/2003 12:50 PM 18.1 1260 7.8 9.4 46.83/20/2003 12:22 PM 16.4 1410 7.9 9.5 53.33/27/2003 12:06 PM 17.2 1310 8.0 9.7 43.84/3/2003 8:56 AM 15.7 1260 7.2 8.6 47.54/10/2003 12:55 PM 20.6 1280 8.1 10.0 49.04/17/2003 1:42 PM 15.8 546 7.9 9.7 33.74/24/2003 1:15 PM 15.7 525 8.2 9.8 30.45/1/2003 12:52 PM 18.0 693 7.9 10.3 NA5/8/2003 12:01 PM 17.1 477 7.6 8.8 39.15/15/2003 12:28 PM 20.3 664 7.8 10.65/22/2003 2:21 PM 24.5 827 8.4 13.3 28.15/29/2003 1:05 AM 25.1 713 8.1 10.46/5/2003 2:13 PM 25.9 886 8.4 11.8 44.96/12/2003 1:35 PM 24.1 896 8.4 11.6 45.46/19/2003 1:42 PM 24.7 891 8.8 8.8 43.56/26/2003 1:22 PM 25.9 831 8.6 12.6 46.97/3/2003 12:31 PM 25.1 836 8.8 12.27/10/2003 12:42 PM 25.5 889 8.6 12.87/17/2003 12:40 PM 26.8 800 8.5 11.07/24/2003 12:38 PM 27.0 825 8.3 10.3 58.87/31/2003 1:20 PM 26.2 770 8.0 8.2 78.38/7/2003 12:32 PM 23.9 804 8.4 10.9 65.88/14/2003 11:42 AM 23.9 830 9.0 13.18/21/2003 12:13 PM 24.9 780 8.9 11.2 27.08/28/2003 12:33 PM 24.3 810 8.6 12.4 29.29/4/2003 11:52 AM 25.1 827 8.5 10.2 29.89/11/2003 3:14 PM 23.7 916 8.3 12.7 35.59/18/2003 1:51 PM 21.0 859 8.9 10.3 30.79/25/2003 1:39 PM 22.2 769 8.1 9.7 39.410/2/2003 1:00 PM 20.6 770 8.0 9.8 28.510/9/2003 12:45 PM 20.7 840 7.9 9.8 30.0
10/16/2003 8:30 AM 17.0 767 7.7 10.4 12.410/23/2003 1:45 PM 18.8 541 7.8 9.4 28.510/30/2003 12:06 PM 16.9 774 7.7 9.5 17.311/6/2003 1:14 PM 14.3 831 7.9 10.3 33.5
11/13/2003 11:30 AM 14.1 903 7.8 9.1 25.211/20/2003 12:45 PM 14.2 942 7.9 10.0 NA
129
A7: 541STC510 – SJR @ Maze continued…
Date TimeTemp (ºC)
Field SC (umhos) pH
Dissolved Oxygen (mg/L)
Turbidity (ntu)
11/26/2003 11:18 AM 9.6 991 7.8 11.1 16.012/4/2003 11:48 AM 12.5 1040 8.0 11.1
12/11/2003 11:55 AM 11.7 1030 7.8 11.2 NA12/18/2003 11:53 AM 10.1 1060 7.9 11.5 NA12/23/2003 12:08 PM 11.6 1060 7.9 13.4 NA12/30/2003 12:44 PM 9.2 992 7.8 13.0 NA1/8/2004 11:23 AM 10.0 994 7.9 8.7 NA1/15/2004 12:34 PM 10.8 1180 7.9 10.3 NA1/22/2004 12:24 PM 10.2 1210 7.9 16.4 35.81/29/2004 12:35 PM 12.0 1190 7.9 10.4 NA2/5/2004 11:52 AM 11.3 1180 7.8 13.3 21.02/12/2004 11:45 AM 11.6 1270 7.9 12.9 NA2/19/2004 11:43 AM 13.9 1190 7.9 13.6 NA2/26/2004 12:27 PM 13.0 1020 7.9 9.6 NA3/4/2004 11:34 AM 12.8 982 7.9 9.7 82.03/11/2004 12:29 PM 16.8 916 8.0 9.6 NA3/18/2004 10:45 AM 17.3 733 7.9 11.03/25/2004 1:35 PM 16.8 837 8.0 9.5 35.54/1/2004 12:39 PM 16.6 909 8.1 11.04/15/2004 1:48 PM 17.1 515 8.0 10.2 31.24/22/2004 12:42 PM 16.4 436 8.2 11.3 36.24/29/2004 2:39 PM 19.3 585 7.9 NA 37.75/6/2004 1:34 PM 20.7 415 7.9 10.0 54.55/13/2004 1:42 PM 19.5 403 7.9 14.6 41.05/20/2004 12:59 PM 21.3 900 8.1 10.8 36.55/27/2004 12:55 PM 24.0 948 8.6 NA NA6/3/2004 1:32 PM 24.4 990 8.6 12.9 35.26/10/2004 2:01 PM 23.8 1010 8.6 14.0 44.06/17/2004 1:39 PM 26.0 1050 8.6 13.8 54.06/24/2004 1:26 PM 24.6 977 8.7 13.2 NA7/1/2004 12:36 PM 24.9 999 8.7 15.47/8/2004 1:47 PM 26.4 1010 8.9 16.17/15/2004 1:29 PM 25.1 977 8.8 14.67/22/2004 8:00 AM 25.1 976 8.0 8.37/29/2004 12:53 PM 26.0 1010 8.7 12.98/5/2004 12:00 PM 24.6 905 8.3 10.38/12/2004 12:33 PM 26.5 991 8.4 11.38/19/2004 8:13 AM 24.9 925 8.0 7.18/26/2004 1:25 PM 24.4 778 8.2 7.19/2/2004 12:51 PM 24.6 911 8.0 9.79/9/2004 7:51 AM 23.3 879 8.0 7.5
130
A7: 541STC510 – SJR @ Maze continued…
Date TimeTemp (ºC)
Field SC (umhos) pH
Dissolved Oxygen (mg/L)
Turbidity (ntu)
9/16/2004 7:58 AM 21.4 923 7.1 7.59/23/2004 3:19 PM 22.0 831 8.0 10.49/30/2004 1:35 PM 21.0 948 8.0 11.010/7/2004 11:46 AM 20.8 913 7.9 9.3
10/14/2004 11:50 AM 19.0 837 7.7 8.810/21/2004 12:54 PM 15.7 462 NA 9.210/28/2004 12:40 PM 13.8 451 7.9 13.111/4/2004 1:41 PM 13.7 853 7.9 9.2
11/11/2004 11:55 AM 14.8 944 7.8 8.811/18/2004 12:24 PM 14.0 920 7.8 9.411/23/2004 8:06 AM 10.0 1010 7.8 10.212/2/2004 12:57 PM 8.9 1100 7.9 11.812/9/2004 12:18 PM 11.6 1070 7.8 10.7
12/16/2004 12:41 PM 12.1 934 7.8 10.512/22/2004 8:29 AM 9.1 1110 7.9 12.512/29/2004 7:49 AM 9.9 1050 7.9 9.71/6/2005 10:31 AM 9.3 436 7.5 11.91/13/2005 12:31 PM 9.6 331 7.6 10.61/20/2005 1:22 PM 8.8 659 7.5 9.11/27/2005 12:15 PM 11.1 980 7.8 8.32/3/2005 1:06 PM 11.1 817 7.6 8.92/10/2005 11:59 AM 12.2 775 7.9 10.62/17/2005 1:53 PM 12.9 536 7.9 11.82/24/2005 12:28 PM 13.2 520 7.7 9.93/3/2005 12:14 PM 13.5 510 7.8 10.93/10/2005 1:43 PM 15.5 541 7.9 10.43/17/2005 12:28 PM 13.8 603 7.9 16.03/24/2005 1:15 PM 13.3 427 7.9 10.33/31/2005 12:03 PM 12.8 249 7.8 11.24/7/2005 12:49 PM 13.5 271 7.7 10.74/14/2005 12:43 PM 13.1 295 7.9 10.94/21/2005 1:10 PM 14.0 293 8.0 11.44/28/2005 12:02 PM 14.3 288 7.7 12.85/5/2005 12:55 PM 14.8 290 7.8 10.95/12/2005 12:28 PM 15.3 216 7.8 10.55/19/2005 1:11 PM 15.6 147 7.6 10.05/26/2005 12:55 PM 17.6 100 7.8 9.56/2/2005 12:52 PM 18.7 114 7.6 8.76/9/2005 11:10 AM 17.3 145 7.3 4.16/16/2005 1:05 PM 18.1 223 7.5 10.16/23/2005 2:20 PM 18.3 257 NA 10.06/30/2005 1:45 PM 20.5 271 7.6 7.87/7/2005 12:34 PM 19.2 282 7.6 10.57/13/2005 8:07 AM 21.8 422 7.8 8.9
131
A7: 541STC510 – SJR @ Maze continued…
Date TimeTemp (ºC)
Field SC (umhos) pH
Dissolved Oxygen (mg/L)
Turbidity (ntu)
7/21/2005 1:16 PM 23.3 470 7.8 9.87/28/2005 2:13 PM 23.7 546 8.0 10.18/4/2005 12:16 PM 23.2 506 7.9 9.58/11/2005 12:37 PM 23.9 524 8.0 9.38/18/2005 1:35 PM 23.1 506 8.0 9.48/25/2005 12:22 PM 23.0 528 7.7 9.09/1/2005 12:23 PM 23.2 771 7.9 11.79/8/2005 11:54 AM 22.3 710 7.7 8.99/15/2005 12:28 PM 20.1 535 7.6 9.49/21/2005 10:12 AM 20.4 440 7.8 9.29/22/2005 1:55 PM 21.6 494 7.6 8.99/29/2005 12:39 PM 20.5 490 7.7 8.3
Count 260 260 258 213 54Min 7.4 100 6.7 4.1 12Max 27.5 1410 9.0 16.4 82.0Mean 17.8 847 7.9 10.5 39.9Geo Mean 16.8 786 7.9 10.3 37.1Median 17.1 904 7.9 10.3 36.6Quartile 1 13.1 673 7.7 9.3 29.9Quartile 3 23.1 1020 8.0 11.2 47.4NOTE: For values reported as < (less than), half the detection limit was used.
NA = Data not applicableINA = Site was inaccessibleDRY = Site had no flow
132
A7: 541STC510 – SJR @ Maze continued…
DateTSS
(mg/L)TOC
(mg/L)Total Coli
MPNE. coli MPN
10/5/2000 4010/12/2000 44 4.110/19/2000 1.810/26/2000 46 1.811/2/2000 48 3.611/9/2000 36 3.0
11/16/2000 26 2.911/21/2000 1811/30/2000 25 1.712/7/2000 27 <1
12/12/2000 40 1.412/21/2000 NA 3.612/28/2000 16 2.91/4/2001 14 3.41/11/2001 70 2.81/18/2001 30 5.51/25/2001 36 4.52/1/2001 35 5.42/8/2001 28 5.02/15/2001 48 3.52/22/2001 NA 1.23/1/2001 57 4.83/8/2001 88 7.43/15/2001 58 5.83/22/2001 45 2.13/29/2001 49 <14/5/2001 29 NA4/12/2001 42 4.24/19/2001 52 5.34/26/2001 2.85/3/2001 40 3.35/10/2001 44 3.05/17/2001 2.95/24/2001 74 4.85/31/2001 61 6.96/7/2001 66 126/14/2001 INA INA6/21/2001 NA 106/28/2001 88 8.77/5/2001 7.67/11/2001 6.97/19/2001 7.3
133
A7: 541STC510 – SJR @ Maze continued…
DateTSS
(mg/L)TOC
(mg/L)Total Coli
MPNE. coli MPN
10/5/2000 4010/12/2000 44 4.110/19/2000 1.810/26/2000 46 1.811/2/2000 48 3.611/9/2000 36 3.0
11/16/2000 26 2.911/21/2000 1811/30/2000 25 1.712/7/2000 27 <1
12/12/2000 40 1.412/21/2000 NA 3.612/28/2000 16 2.91/4/2001 14 3.41/11/2001 70 2.81/18/2001 30 5.51/25/2001 36 4.52/1/2001 35 5.42/8/2001 28 5.02/15/2001 48 3.52/22/2001 NA 1.23/1/2001 57 4.83/8/2001 88 7.43/15/2001 58 5.83/22/2001 45 2.13/29/2001 49 <14/5/2001 29 NA4/12/2001 42 4.24/19/2001 52 5.34/26/2001 2.85/3/2001 40 3.35/10/2001 44 3.05/17/2001 2.95/24/2001 74 4.85/31/2001 61 6.96/7/2001 66 126/14/2001 INA INA6/21/2001 NA 106/28/2001 88 8.77/5/2001 7.67/11/2001 6.97/19/2001 7.3
134
A7: 541STC510 – SJR @ Maze continued…
DateTSS
(mg/L)TOC
(mg/L)Total Coli
MPNE. coli MPN
7/26/2001 5.98/2/2001 7.78/9/2001 7.48/16/2001 62 9.98/23/2001 51 8.58/30/2001 34 129/6/2001 41 9.79/13/2001 42 9.89/20/2001 NA 109/27/2001 39 1110/4/2001 NA 9.0
10/11/2001 37 1610/18/2001 44 1610/25/2001 7.811/1/2001 3211/8/2001 35
11/15/2001 48 4.511/20/2001 45 NA11/29/2001 27 NA12/6/2001 36 5.0
12/13/2001 23 2.612/20/2001 23 5.112/27/2001 291/3/2002 981/10/2002 591/17/2002 241/24/2002 211/31/2002 16 NA2/7/2002 27 NA2/14/2002 27 NA2/21/2002 482/28/2002 43 6.43/7/2002 42 6.53/14/2002 45 4.33/21/2002 46 3.53/28/2002 35 5.04/4/2002 46 NA4/11/2002 464/18/2002 69 7.94/25/2002 51 NA5/2/2002 46 3.85/16/2002 46 NA5/23/2002 49 NA
135
A7: 541STC510 – SJR @ Maze continued…
DateTSS
(mg/L)TOC
(mg/L)Total Coli
MPNE. coli MPN
5/30/2002 NA 3.26/6/2002 76 2.66/13/2002 NA NA6/20/2002 85 3.96/27/2002 78 8.97/31/2002 >2419.6 608/22/2002 3.68/29/2002 379/5/2002 3.79/12/2002 25 NA9/19/2002 30 NA9/26/2002 36 NA10/3/2002 23 3.7
10/10/2002 36 2.910/17/2002 26 3.310/24/2002 53 2.310/31/2002 35 3.011/7/2002 41 NA
11/14/2002 50 5.111/21/2002 32 4.811/26/2002 27 3.712/5/2002 24 3.2
12/12/2002 31 2.812/19/2002 77 5.712/24/2002 651/2/2003 461/9/2003 351/16/2003 50 >2419.6 751/23/2003 351/30/2003 512/6/2003 322/13/2003 342/20/2003 382/27/2003 603/6/2003 673/13/2003 NA 6.43/20/2003 NA 4.83/27/2003 57 3.74/3/2003 NA NA
136
A7: 541STC510 – SJR @ Maze continued…
DateTSS
(mg/L)TOC
(mg/L)Total Coli
MPNE. coli MPN
4/10/2003 NA 3.04/17/2003 53 3.14/24/2003 44 3.8 >2419.6 1095/1/2003 35 4.75/8/2003 NA 3.55/15/2003 50 3.35/22/2003 44 2.85/29/2003 46 4.26/5/2003 80 6.06/12/2003 77 3.46/19/2003 62 3.86/26/2003 67 4.77/31/2003 >2419.6 648/28/2003 >2419.6 289/25/2003 >2419.6 51
10/30/2003 >2419.6 5411/20/2003 >2419.6 451/29/2004 >2419.6 822/26/2004 >2419.6 >2419.63/11/2004 7.93/18/2004 4.33/25/2004 >2419.6 454/1/2004 5.14/15/2004 3.74/22/2004 2.54/29/2004 3.8 >2419.6 1405/6/2004 3.55/13/2004 3.85/20/2004 5.65/27/2004 >2419.6 806/3/2004 7.46/10/2004 7.36/17/2004 5.4 >2419.6 596/24/2004 >2419.6 667/1/2004 8.37/8/2004 9.8 >2419.6 487/15/2004 8.37/22/2004 5.87/29/2004 6.0 >2419.6 35
137
A7: 541STC510 – SJR @ Maze continued…
DateTSS
(mg/L)TOC
(mg/L)Total Coli
MPNE. coli MPN
8/5/2004 6.68/12/2004 8.5 >2419.6 448/19/2004 5.48/26/2004 >2419.6 559/16/2004 >2419.6 389/23/20049/30/2004 >2419.6 36
10/14/2004 >2419.6 173310/28/2004 50 >2419.6 16711/4/2004 50 5.5 >2419.6 214
11/11/2004 88 6.211/18/2004 38 6.1 >2419.6 4011/23/2004 26 5.212/2/2004 17 4.812/9/2004 32 4.9 >2419.6 172
12/16/2004 47 5.612/22/2004 21 4.9 >2419.6 3612/29/2004 48 4.81/6/2005 120 10 >2419.6 2481/13/2005 130 111/20/2005 66 >2419.6 351/27/2005 64 8.22/3/2005 53 13 >2419.6 1152/10/2005 43 5.82/17/2005 150 7.6 >2419.6 >2419.62/24/2005 110 7.53/3/2005 50 4.83/10/2005 46 NA 961 243/17/2005 43 4.03/24/2005 74 8.7 >2419.6 >2419.63/31/2005 62 3.74/7/2005 29 3.2 1300 504/14/2005 40 NA4/21/2005 27 2.7 >2419.6 534/28/2005 36 NA5/5/2005 NA 2.4 >2419.6 465/12/2005 33 2.65/19/2005 34 3.0 >2419.6 1615/26/2005 38 2.4
138
139
DateTSS
(mg/L)TOC
(mg/L)Total Coli
MPNE. coli MPN
6/2/2005 38 3.26/9/2005 42 NA >2419.6 1846/16/2005 47 2.96/23/2005 45 2.7 >2419.6 916/30/2005 160 2.17/7/2005 62 2.2 >2419.6 847/13/2005 51 2.37/21/2005 53 2.7 >2419.6 667/28/2005 58 2.98/4/2005 50 2.8 >2419.6 598/11/2005 65 2.98/18/2005 49 3.2 >2419.6 798/25/2005 60 3.09/1/2005 51 3.1 >2419.6 549/8/2005 54 3.1 >2419.6 2619/15/2005 62 2.99/29/29/2
Coun
A7: 541STC510 – SJR @ Maze continued…
1/2005 >2419.6 1942/2005 34 NA9/2005 39 2.7
t 158 157 46 4614 0.5 961 24
160 16 2420 2420n 48
Min MaxMea 5 NA NA
Mean 44 4 2340 95ian 45 4.3 2420 6
GeoMed 5QuaQuaNOT
NA =INA =DRY
rtile 1 35 3.0 2420 47rtile 3 54 6.4 2420 156E: For values reported as < (less than), half the detection limit was used For values reported as > (greater than), 2420 was used
Data not applicable Site was inaccessible
= Site had no flow
A7: 541STC510 – SJR @ Maze continued…
DateNitrate (mg/L)
Nitrate-N (mg/L)
TKN (mg/L)
Ammonia-N (mg/L)
Phosphorus (mg/L)
Ortho-phosphate-
P (mg/L)
Potassium (mg/L)
BOD 5-Day (mg/L)
BOD 10-Day (mg/L)
10/12/2000 1.3 2.310/26/2000 5.8 <2 0.2 <1 3.1 0.9 1.711/16/2000 1.3 2.511/30/2000 8.8 <2 0.2 <1 5.1 1 1.812/12/2000 1.5 2.412/28/2000 9.6 <2 <0.1 <1 6 1.3 2.31/11/2001 2 3.11/25/2001 9.3 <2 0.2 <1 6.5 1.7 2.92/8/2001 12 <2 0.1 <1 6.9 1.7 22/22/2001 7.8 <2 0.2 <1 4.5 1.4 2.33/15/2001 13 <2 0.3 <1 7.1 1.7 3.13/29/2001 9.5 <2 0.2 <1 6.3 1.8 3.44/19/2001 12 <2 0.2 <1 5.6 2.2 4.24/26/2001 6.8 <2 <1 0.2 <1 3.3 1.9 3.25/17/2001 6 <2 0.2 <1 3.6 1.6 2.85/31/2001 12 1.2 0.2 NA 6.2 2.8 5.46/7/2001 12 <1.0 0.3 <1 6.2 4.9 7.56/21/2001 11 <2 0.3 <1 6.8 5.5 9.46/28/2001 15 <2 0.3 <1 7.2 3.4 68/16/2001 11 <2 0.4 <1 5.38/30/2001 11 <2 0.3 <1 6.29/27/2001 14 <2 0.3 <1 6.1
10/25/2001 1 2.311/29/2001 NA NA NA 0.1 6.2 1.1 1.912/13/2001 0.9 1.912/27/2001 1.1 2.21/17/2002 1.1 2.21/31/2002 1.7 2.6
140
A7: 541STC510 – SJR @ Maze continued…
DateNitrate (mg/L)
Nitrate-N (mg/L)
TKN (mg/L)
Ammonia-N (mg/L)
Phosphorus (mg/L)
Ortho-phosphate-
P (mg/L)
Potassium (mg/L)
BOD 5-Day (mg/L)
BOD 10-Day (mg/L)
2/14/2002 1.7 2.92/28/2002 1.9 3.13/14/2002 2.4 3.94/25/2002 1.8 3.15/16/2002 1.6 2.85/30/2002 2.7 4.76/13/2002 12 NA 0.3 0.1 6.3 3.6 6.96/20/2002 6.3 12.68/29/2002 5.2 8.59/26/2002 2.1 3.8
10/31/2002 1.3 211/21/2002 1.6 2.912/19/2002 3.2 4.91/30/2003 1.4 2.1
Count 19 NA 18 1 19 19 20 39 39Min 5.8 NA 0.5 0.5 0.1 0.1 3.1 0.9 1.7Max 15.0 NA 1.2 0.5 0.4 0.5 7.2 6.3 12.6Mean 10.5 NA 1.0 0.5 0.2 0.5 5.7 2.1 3.7Geo Mean 10.1 NA 1.0 0.5 0.2 0.4 5.6 1.9 3.2Median 11.0 NA 1.0 0.5 0.2 0.5 6.2 1.7 2.9Quartile 1 9.1 #NUM! 1.0 0.5 0.2 0.5 5.3 1.3 2.3Quartile 3 12.0 #NUM! 1.0 0.5 0.3 0.5 6.4 2.3 4.1NOTE: For values reported as < (less than), half the detection limit was used.
NA = Data not applicableINA = Site was inaccessibleDRY = Site had no flow
141
A7: 541STC510 – SJR @ Maze continued…
DateHardness
(mg/L)
Total Arsenic (ug/L)
Total Cadmium
(ug/L)
Total Chromium
(ug/L)
Total Copper (ug/L)
Total Lead (ug/L)
Total Nickel (ug/L)
Total Zinc (ug/L)
Total Mercury (ug/L)
10/26/2000 2.5 2.6 <5 <511/30/2000 160 1.1 1.4 <5 <5 5.112/28/2000 200 1 1.5 <5 <5 <21/25/2001 220 1.9 2.7 <5 <5 3.22/22/2001 160 1.8 3.3 <5 <5 5.13/29/2001 250 2.1 2.9 <5 <5 4.64/26/2001 110 2.4 3.3 <5 <5 5.75/31/2001 210 3.0 3.6 <5 5.1 5.86/7/2001 240 3.0 <1 3.6 4.4 <5 6.0 7.2 <0.26/21/2001 NA 3.2 <1 2.7 2.9 <5 <5 4.7 <0.26/28/2001 260 3.1 <1 4.8 4.6 <5 7.7 8.0 <0.27/26/2001 NA NA 3.9 3.7 <5 5.8 6.0 NA8/30/2001 210 2.9 <1 1.8 2.0 <5 <5 2.49/27/2001 210 <4 <1 <1 1.5 <5 <5 <2 <0.2
10/25/2001 120 <4 <0.1 <1 2.1 <5 <5 2.1 <0.211/29/2001 190 <4 <0.1 <1 <1 <5 <5 3 <0.212/27/2001 <4 <0.1 3.4 4.1 <5 <5 6.5 <0.21/31/2002 <4.0 <0.1 <1.0 NA <5.0 <5.0 <2.0 <0.22/28/2002 <4.0 <0.1 2.0 3.5 <5.0 <5.0 4.4 <0.23/28/2002 <4.0 <0.1 2.0 2.5 <5.0 8.8 10 <0.24/25/2002 <4.0 <0.1 <1.0 1.6 <5.0 <5.0 <2.0 <0.25/30/2002 <4.0 <0.1 4.0 4.4 <5.0 5.7 6.9 <0.26/20/2002 260 4.8 <0.1 4.0 4.2 <5.0 6.1 5.7 <0.29/26/2002 200 4.5 <0.1 2.0 NA <5.0 <5.0 3.7 <0.2
10/31/2002 160 <4.0 <0.1 2.1 2.0 <5.0 <5.0 3.8 <0.211/21/2002 220 <4.0 <0.1 3.1 3.8 <5.0 6.3 5.1 <0.23/27/2003 280 <4.0 NA 3.2 3.3 <5.0 <5.0 5.2 <0.24/24/2003 110 <4.0 <0.1 NA NA NA <5.0 4.3 <0.25/29/2003 160 <4.0 <0.1 <1.0 3.6 <5.0 <5.0 3.7 <0.26/26/2003 190 <4.0 <0.1 2.9 3.6 <5.0 <5.0 5.3 <0.2
142
A7: 541STC510 – SJR @ Maze continued…
DateHardness
(mg/L)
Total Arsenic (ug/L)
Total Cadmium
(ug/L)
Total Chromium
(ug/L)
Total Copper (ug/L)
Total Lead (ug/L)
Total Nickel (ug/L)
Total Zinc (ug/L)
Total Mercury (ug/L)
Count 21 21 20 29 27 29 30 29 20Min 110.0 2.0 0.1 0.5 0.5 2.5 2.5 1.0 0.1Max 280.0 4.8 0.5 4.8 4.6 2.5 8.8 10.0 0.1Mean 196.2 2.5 0.2 2.2 2.9 2.5 3.6 4.5 0.1Geo Mean 189.8 2.3 0.1 1.8 2.7 2.5 3.2 3.9 0.1Median 200.0 2.0 0.1 2.1 3.3 2.5 2.5 4.7 0.1Quartile 1 160.0 2.0 0.1 1.1 2.1 2.5 2.5 3.2 0.1Quartile 3 220.0 2.9 0.2 3.1 3.7 2.5 4.5 5.7 0.1NOTE: For values reported as < (less than), half the detection limit was used.
NA = Data not applicableINA = Site was inaccessibleDRY = Site had no flow
143
A7: 541STC510 – SJR @ Maze continued…
DateHardness
(mg/L)
Dissolved Arsenic (ug/L)
Dissolved Cadmium
(ug/L)
Dissolved Chromium
(ug/L)
Dissolved Copper (ug/L)
Dissolved Lead (ug/L)
Dissolved Nickel (ug/L)
Dissolved Zinc
(ug/L)
Dissolved Mercury (ug/L)
10/26/2000 <1 <1 <5 <5 <211/30/2000 160 <1 <1 <5 <5 <212/28/2000 200 <1 <1 <5 <5 <21/25/2001 220 <1 <1 <5 <5 <22/22/2001 160 <1 1.1 <5 <5 <23/29/2001 250 <1 1.4 <5 <5 <24/26/2001 110 <1 1.1 <5 <5 <25/31/2001 210 1.1 <1 <5 <5 2.16/7/2001 240 2.2 <1 <1 1.3 <5 <5 <2 <0.26/21/2001 NA 2.7 <1 <1 <1 <5 <5 <2 <0.26/28/2001 260 3.3 <1 <1 <1 <5 <5 <2 <0.27/26/2001 NA NA NA NA NA NA NA NA8/30/2001 210 2.3 <1 <1 1.1 <5 <5 <29/27/2001 210 <4 <1 <1 <1 <5 <5 <2 <0.2
10/25/2001 120 <4 <0.1 <1 1.0 <5 <5 <2 <0.211/29/2001 190 <4 <0.1 <1 <1 <5 <5 2.4 <0.212/27/2001 <4 <0.1 <1 1.1 <5 <5 2.3 <0.21/31/2002 <4.0 <0.1 <1.0 NA <5.0 <5.0 <2.0 <0.22/28/2002 <4.0 <0.1 1.9 <1.0 <5.0 <5.0 <2.0 <0.23/28/2002 <4.0 <0.1 <1.0 1.8 <5.0 <5.0 6.5 <0.24/25/2002 <4.0 <0.1 <1.0 <1.0 <5.0 <5.0 NA <0.25/30/2002 <4.0 <0.1 <1.0 1.6 <5.0 <5.0 <2.0 <0.26/20/2002 260 <4.0 <0.1 <1.0 3.2 <5.0 <5.0 <2.0 <0.29/26/2002 200 <4.0 <0.1 <1.0 1.7 <5.0 <5.0 <2.0 <0.2
10/31/2002 160 <4.0 <0.1 <1.0 1.2 <5.0 <5.0 <2.0 <0.211/21/2002 220 <4.0 <0.1 <1.0 <1.0 <5.0 <5.0 <2.0 <0.2
144
A7: 541STC510 – SJR @ Maze continued…
DateHardness
(mg/L)
Dissolved Arsenic (ug/L)
Dissolved Cadmium
(ug/L)
Dissolved Chromium
(ug/L)
Dissolved Copper (ug/L)
Dissolved Lead (ug/L)
Dissolved Nickel (ug/L)
Dissolved Zinc
(ug/L)
Dissolved Mercury (ug/L)
Count 17 17 17 25 24 25 25 24 16Min 110.0 2.0 0.1 0.5 0.5 2.5 2.5 1.0 0.1Max 260.0 3.3 0.5 1.9 3.2 2.5 2.5 6.5 0.1Mean 198.8 2.1 0.2 0.6 1.0 2.5 2.5 1.4 0.1Geo Mean 193.5 2.1 0.1 0.5 0.8 2.5 2.5 1.2 0.1Median 210.0 2.0 0.1 0.5 0.8 2.5 2.5 1.0 0.1Quartile 1 160.0 2.0 0.1 0.5 0.5 2.5 2.5 1.0 0.1Quartile 3 220.0 2.0 0.5 0.5 1.2 2.5 2.5 1.0 0.1NOTE: For values reported as < (less than), half the detection limit was used.
NA = Data not applicableINA = Site was inaccessibleDRY = Site had no flow
145
146
A7: 541STC510 – SJR @ Maze continued…
DateChloride (mg/L)
Sulfate (mg/L)
Calcium (mg/L)
Magnesium (mg/L)
TDS (mg/L)
Carbonate (mg/L)
Bicarbonate (mg/L)
Total Alkalinity
(mg/L)Sodium (mg/L)
11/30/2000 91 86 35 18 460 <1 120 100 8612/28/2000 120 120 42 23 520 <1 160 130 1101/25/2001 140 150 45 26 520 <1 180 140 1302/22/2001 82 100 34 18 390 <1 110 90 853/29/2001 140 170 53 30 540 <1 170 140 1404/26/2001 64 25 13 310 <1 70 70 475/31/2001 120 110 45 24 540 <1 120 120 1006/7/2001 25 26 51 27 560 <1 160 130 1206/21/2001 150 150 56 30 690 <1 190 160 1306/28/2001 140 150 57 30 620 <1 180 150 1208/30/2001 140 130 46 24 550 <1 170 140 1109/27/2001 NA 100 44 24 540 <1 NA NA 110
10/25/2001 75 65 26 14 320 <1 68 NA 6111/29/2001 130 120 39 23 550 <1 290 240 1103/27/2003 180 200 59 334/24/2003 68 78 25 135/29/2003 97 99 35 186/26/2003 110 120 42 21
Count 16 18 18 18 14 14 13 12 14Min 25 26 25 13 310 0.5 68 70 47Max 180 200 59 33 690 0.5 290 240 140Mean 110 110 42 23 500 0.5 150 130 100Geo Mean 100 100 41 22 500 0.5 140 130 100Median 120 120 43 24 540 0.5 160 140 110Quartile 1 89 89 35 18 480 0.5 120 120 90Quartile 3 140 150 50 27 550 0.5 180 140 120NOTE: For values reported as < (less than), half the detection limit was used.
NA = Data not applicableINA = Site was inaccessibleDRY = Site had no flow
A7: 541STC510 – SJR @ Maze continued…
Date Result Control Result Control
Result (million/m
l)
Control (million/
ml)MDD (%)
10/26/2000 95 100 NA NA
Count 1 1 N/A N/A N/A N/A N/A
* Significantly reduced from the lab control.** Significantly greater than the lab control.^ Fish were from a "forced hatch," duplicate failed QA.1 Duplicate sample for the set was low - 77% recovery.
3 Samples qualified, but duplicate sample recovery for the set was high - 126% (53.8%/42.5%)NA = Data not applicableINA = Site was inaccessibleDRY = Site had no flow
2 Testing for the Fathead minnow was initiated when samples were approx. 48h old due to untimely shipping of fish by fish supplier.
96h Acute Fathead Minnow
(% Survival)
48h Acute Ceriodaphnia Dubia
(% Survival) Algae Cell Growth
147
A8: 541SJC501 – SJR @ Airport Way Station Code:541SJC501
Location: Latitude 37.67556, Longitude -121.264167
Date TimeTemp (ºC)
Field SC (umhos) pH
Dissolved Oxygen (mg/L)
Turbidity (ntu)
10/5/2000 1:45 PM 20.9 428 8.010/12/2000 7:50 AM 15.8 397 7.710/19/2000 12:30 PM 19.0 336 7.810/26/2000 9:20 AM 15.4 298 7.711/2/2000 12:55 PM 15.4 449 7.311/9/2000 1:55 PM 13.6 581 7.7
11/16/2000 7:45 AM 9.7 636 6.911/21/2000 10:50 AM 11.0 638 7.711/30/2000 7:35 AM 9.1 650 7.112/7/2000 1:40 PM 11.8 725 7.8
12/12/2000 2:20 PM 12.7 778 7.912/21/2000 8:55 AM 9.6 789 6.912/28/2000 7:32 AM 7.1 788 6.71/4/2001 1:14 PM 10.1 831 7.81/11/2001 8:18 AM 9.3 771 7.31/18/2001 2:32 PM 9.9 830 7.41/25/2001 7:53 AM 9.3 916 7.42/1/2001 8:37 AM 8.5 895 6.92/8/2001 3:25 PM 12.4 1020 7.82/10/2001 1:15 PM 9.6 968 7.82/11/2001 2:58 AM 8.8 966 7.72/15/2001 8:30 AM 9.6 696 7.02/22/2001 8:50 AM 11.1 660 6.73/1/2001 1:30 PM 13.6 502 7.73/8/2001 2:00 PM 15.4 496 7.83/15/2001 8:30 AM 14.8 931 7.43/22/2001 8:25 AM 18.4 1090 7.03/29/2001 3:13 PM 20.7 940 7.54/5/2001 8:35 AM 15.0 915 6.64/12/2001 1:50 PM 16.2 687 7.64/19/2001 8:55 AM 16.1 778 7.64/26/2001 3:00 PM 21.0 317 8.05/3/2001 2:34 PM 18.5 308 7.45/10/2001 12:25 PM 20.0 289 7.75/17/2001 8:10 AM 18.6 291 7.25/24/2001 3:00 PM 26.6 672 7.95/31/2001 7:50 AM 22.5 657 7.06/7/2001 7:57 AM 21.8 733 8.0 9.46/14/2001 7:35 AM 21.0 794 7.9 8.8
148
A8: 541SJC501 – SJR @ Airport Way continued…
Date TimeTemp (ºC)
Field SC (umhos) pH
Dissolved Oxygen (mg/L)
Turbidity (ntu)
6/21/2001 8:24 AM 24.4 787 7.8 9.96/28/2001 8:10 AM 21.6 683 7.7 7.97/5/2001 1:02 PM 25.9 676 8.3 10.97/11/2001 8:00 AM 22.9 670 8.0 9.47/19/2001 8:09 AM 22.8 703 7.2 10.77/26/2001 1:15 PM 25.9 737 8.6 14.48/2/2001 2:35 PM 26.0 740 8.6 11.98/9/2001 1:35 PM 27.1 774 8.7 11.98/16/2001 2:16 PM 25.2 691 8.7 12.48/23/2001 2:12 PM 23.9 718 8.4 11.58/30/2001 2:20 PM 25.3 725 8.6 11.69/6/2001 1:44 PM 22.8 748 8.7 13.09/13/2001 2:52 PM 23.1 766 8.4 11.89/20/2001 7:26 AM 21.6 710 7.8 7.89/27/2001 7:45 AM 20.6 676 7.9 7.410/4/2001 12:33 PM 22.0 730 8.0 10.3
10/11/2001 1:17 PM 18.7 701 7.9 9.110/18/2001 2:36 PM 19.8 611 7.9 9.610/25/2001 3:31 PM 16.0 400 7.8 9.411/1/2001 2:06 PM 16.7 494 8.0 8.511/8/2001 2:27 PM 15.3 631 8.5 10.5
11/15/2001 11:55 AM 15.7 640 8.0 9.011/20/2001 8:06 AM 14.1 620 7.7 9.011/29/2001 1:20 PM 14.0 730 7.6 NA12/6/2001 1:15 PM 11.1 697 7.8 10.8
12/13/2001 1:34 PM 10.4 822 7.3 10.912/20/2001 7:51 AM 9.7 878 7.7 10.312/27/2001 9:07 AM 10.7 848 7.8 10.61/3/2002 2:00 PM 13.3 404 7.6 7.41/10/2002 2:13 PM 12.4 739 7.5 10.81/17/2002 12:56 PM 9.0 1010 7.8 10.71/24/2002 8:15 AM 8.1 1120 7.4 11.51/31/2002 7:53 AM 7.5 1050 7.9 11.52/7/2002 12:48 PM 11.3 994 8.1 11.72/14/2002 1:51 PM 13.2 987 8.0 10.62/21/2002 7:40 AM 13.9 937 7.7 10.12/28/2002 2:17 PM 15.9 1030 8.0 9.73/7/2002 12:21 PM 15.1 1017 8.0 9.73/7/2002 3:50 PM 15.1 1020 8.0 9.73/14/2002 1:45 PM 14.1 1030 8.2 10.83/21/2002 2:30 PM 16.1 918 8.0 9.03/28/2002 4:21 PM 18.6 988 8.1 8.94/4/2002 12:22 PM 18.7 908 8.3 10.24/11/2002 2:54 PM 19.8 728 8.2 9.94/18/2002 11:38 AM 14.2 386 7.7 10.6
149
A8: 541SJC501 – SJR @ Airport Way continued…
Date TimeTemp (ºC)
Field SC (umhos) pH
Dissolved Oxygen (mg/L)
Turbidity (ntu)
4/25/2002 7:32 AM 16.9 376 7.7 9.35/2/2002 12:24 PM 16.4 380 8.0 9.95/9/2002 2:01 PM 18.8 351 8.5 11.15/16/2002 1:50 PM 21.3 433 7.5 NA NA5/23/2002 10:20 AM 18.2 490 7.6 NA5/30/2002 8:18 AM 21.7 511 7.8 8.86/6/2002 11:42 AM 24.4 672 8.3 8.66/13/2002 8:02 AM 21.2 749 7.5 NA6/20/2002 12:30 PM 24.1 724 8.9 NA6/27/2002 1:24 PM 24.3 690 8.8 13.77/3/2002 7:39 AM 22.9 665 8.6 NA7/11/2002 8:21 AM 25.1 697 8.3 NA7/18/2002 1:32 PM 688 8.8 13.3 44.07/25/2002 12:14 PM 23.9 787 8.6 11.17/31/2002 8:21 AM 23.6 745 8.1 7.8 52.48/1/2002 12:54 PM 25.5 650 8.4 11.58/8/2002 1:58 PM 24.5 870 8.8 16.28/15/2002 12:07 PM 24.8 824 8.6 12.08/22/2002 12:46 PM 23.2 801 8.5 12.38/29/2002 12:06 PM 24.0 838 8.9 NA9/5/2002 12:12 PM 21.6 864 8.8 NA9/12/2002 12:07 PM 23.1 851 8.6 14.19/19/2002 1:06 PM 23.1 882 8.2 12.1 NA9/26/2002 8:21 AM 21.4 737 6.9 8.810/3/2002 12:56 PM 17.1 802 7.9 9.8
10/10/2002 8:20 AM 19.8 744 7.9 9.110/17/2002 12:21 PM 17.3 794 8.1 11.4 23.610/24/2002 7:58 AM 15.1 380 7.1 9.010/31/2002 2:11 PM 14.6 629 7.9 8.7 28.011/7/2002 12:48 PM 13.5 759 7.8 9.5
11/14/2002 1:02 PM 15.0 801 7.8 9.311/21/2002 8:13 AM 13.0 859 7.6 9.1 30.311/26/2002 7:50 AM 12.3 674 7.9 9.912/5/2002 12:17 PM 11.4 938 7.8 11.0 25.1
12/12/2002 12:34 PM 11.8 931 7.7 10.812/19/2002 12:19 PM 9.8 674 8.1 NA 74.512/24/2002 7:58 AM 8.3 687 6.1 11.51/2/2003 8:56 AM 9.8 877 7.6 13.41/9/2003 1:14 PM 10.5 1060 7.8 12.41/16/2003 8:28 AM 11.5 496 7.5 10.6 41.21/23/2003 12:00 PM 11.9 1130 7.7 10.81/30/2003 1:44 PM 12.8 894 7.7 10.9 43.02/6/2003 7:33 AM 9.6 1080 7.8 10.82/13/2003 8:41 AM 11.5 1040 7.6 10.0 21.1
150
A8: 541SJC501 – SJR @ Airport Way continued…
Date TimeTemp (ºC)
Field SC (umhos) pH
Dissolved Oxygen (mg/L)
Turbidity (ntu)
2/20/2003 7:49 AM 11.3 1010 7.5 10.9 32.32/27/2003 12:02 PM 14.0 1050 7.8 9.13/6/2003 3:00 PM 15.8 1160 7.8 12.0 NA3/13/2003 1:06 PM 18.0 1050 7.9 9.7 40.83/20/2003 12:41 PM 16.5 1200 8.0 9.9 43.13/27/2003 12:25 PM 17.1 1150 8.0 9.8 53.34/3/2003 8:33 AM 14.8 917 7.1 1.3 27.04/10/2003 1:10 PM 19.2 899 8.0 11.9 30.74/17/2003 2:00 PM 15.8 471 7.9 10.1 37.24/24/2003 1:39 PM 15.7 441 7.8 9.2 28.45/1/2003 1:13 PM 16.8 358 8.0 10.8 NA5/8/2003 12:15 PM 17.0 908 7.7 9.2 41.25/15/2003 12:48 PM 20.0 506 7.8 10.35/22/2003 2:39 PM 22.7 535 8.6 13.1 24.15/29/2003 1:26 AM 24.3 456 8.1 10.26/5/2003 2:30 PM 23.1 452 8.5 11.9 29.46/12/2003 2:05 PM 21.0 453 8.3 10.7 34.36/19/2003 2:02 PM 21.5 423 8.7 8.9 27.26/26/2003 1:42 PM 22.3 374 8.5 11.2 27.17/3/2003 12:47 PM 23.5 489 8.6 10.77/10/2003 12:57 PM 25.0 651 8.6 11.27/17/2003 12:54 PM 26.6 705 8.6 11.37/24/2003 12:53 PM 26.5 601 8.4 10.3 37.07/31/2003 1:35 PM 26.1 647 8.2 8.8 59.28/7/2003 12:52 PM 23.7 650 8.5 12.3 45.18/14/2003 11:58 AM 23.6 718 9.1 15.38/21/2003 12:27 PM 24.5 662 8.9 13.2 19.28/28/2003 12:51 PM 24.3 678 8.6 12.4 27.99/4/2003 12:05 PM 24.8 706 8.5 10.1 32.69/11/2003 3:31 PM 24.1 742 8.3 11.9 25.09/18/2003 2:09 PM 21.3 712 8.2 10.4 24.49/25/2003 1:57 PM 22.5 727 8.2 10.3 29.410/2/2003 1:22 PM 20.7 702 8.0 10.1 30.010/9/2003 1:04 PM 20.6 676 7.9 9.3 30.6
10/16/2003 8:11 AM 16.7 637 7.5 10.0 12.310/23/2003 2:03 PM 18.4 419 7.9 9.6 42.910/30/2003 12:25 PM 16.2 559 7.6 8.2 25.611/6/2003 1:32 PM 14.2 713 7.9 11.3 28.6
11/13/2003 11:44 AM 14.0 737 7.8 9.5 27.411/20/2003 1:00 PM 14.2 810 8.1 10.7 NA11/26/2003 11:31 AM 9.5 834 7.9 11.4 17.012/4/2003 12:04 PM 12.3 885 8.0 11.4
12/11/2003 12:15 PM 11.6 975 7.9 11.2 NA12/18/2003 12:07 PM 9.9 952 7.9 11.6 NA12/23/2003 12:29 PM 11.5 914 8.0 13.8 NA
151
A8: 541SJC501 – SJR @ Airport Way continued…
Date TimeTemp (ºC)
Field SC (umhos) pH
Dissolved Oxygen (mg/L)
Turbidity (ntu)
12/30/2003 1:02 PM 9.0 966 8.0 13.5 NA1/8/2004 11:37 AM 10.0 898 7.9 8.4 NA1/15/2004 12:48 PM 10.7 1090 7.9 11.1 NA1/22/2004 12:39 PM 10.1 1110 7.9 16.6 28.11/29/2004 12:52 PM 12.0 1060 7.9 10.9 NA2/5/2004 12:06 PM 11.4 1070 7.9 14.0 42.72/12/2004 12:00 PM 11.5 1050 7.9 13.4 NA2/19/2004 11:55 AM 13.5 936 8.0 13.4 NA2/26/2004 12:41 PM 13.1 897 7.8 9.7 NA3/4/2004 11:47 AM 13.0 917 7.8 9.3 86.63/11/2004 12:47 PM 17.2 862 8.0 9.7 NA3/18/2004 11:02 AM 17.8 740 7.9 10.63/25/2004 2:06 PM 16.9 753 7.9 9.5 41.04/1/2004 12:57 PM 17.0 820 8.0 10.74/15/2004 2:16 PM 17.9 484 7.9 10.4 30.84/22/2004 1:00 PM 16.7 382 7.9 11.5 40.24/29/2004 3:03 PM 18.8 368 8.0 NA 43.75/6/2004 1:54 PM 20.5 326 7.9 10.3 42.55/13/2004 2:08 PM 19.1 335 7.9 14.0 52.45/20/2004 1:22 PM 19.3 478 8.2 11.0 25.35/27/2004 1:19 PM 23.4 695 8.8 NA NA6/3/2004 1:52 PM 24.3 794 8.8 12.9 32.86/10/2004 2:22 PM 23.8 834 8.8 15.0 356/17/2004 2:05 PM 24.9 611 8.6 11.5 27.26/24/2004 2:06 PM 21.6 413 8.7 11.6 NA7/1/2004 12:51 PM 23.1 521 8.8 13.7 NA7/8/2004 2:13 PM 25.6 663 9.0 15.9 NA7/15/2004 1:49 PM 25.1 683 9.0 15.8 NA7/22/2004 7:40 AM 23.2 548 8.1 8.4 NA7/29/2004 1:17 PM 25.9 674 8.7 12.3 NA8/5/2004 12:20 PM 24.3 687 8.4 11.0 NA8/12/2004 12:53 PM 26.6 772 8.5 11.0 NA8/19/2004 7:52 AM 24.2 739 8.2 7.2 NA8/26/2004 1:45 PM 24.3 655 8.3 7.2 NA9/2/2004 1:10 PM 24.6 750 8.0 9.6 NA9/9/2004 7:33 AM 22.8 739 8.3 7.7 NA9/16/2004 7:40 AM 21.2 761 6.8 7.5 NA9/23/2004 3:35 PM 22.2 775 8.0 10.4 NA9/30/2004 1:45 PM 21.3 848 8.1 12.0 NA10/7/2004 11:59 AM 20.6 757 8.0 9.6
10/14/2004 12:07 PM 19.3 740 7.8 9.610/21/2004 1:10 PM 15.9 424 NA 8.610/28/2004 1:02 PM 13.8 367 7.8 13.011/4/2004 2:00 PM 13.7 696 7.9 9.7
152
A8: 541SJC501 – SJR @ Airport Way continued…
Date TimeTemp (ºC)
Field SC (umhos) pH
Dissolved Oxygen (mg/L)
Turbidity (ntu)
11/11/2004 12:14 PM 14.7 794 7.8 8.911/18/2004 12:46 PM 13.7 803 7.8 9.311/23/2004 7:45 AM 10.0 930 7.8 10.512/2/2004 1:15 PM 8.9 1020 7.9 12.012/9/2004 12:36 PM 11.6 825 7.8 11.1
12/16/2004 12:59 PM 12.1 822 7.8 10.812/22/2004 8:04 AM 9.0 920 7.8 13.212/29/2004 7:32 AM 9.8 940 8.1 10.01/6/2005 11:11 AM 9.5 418 7.6 12.01/13/2005 12:49 PM 9.6 303 7.6 9.51/20/2005 1:48 PM 8.9 622 7.5 9.31/27/2005 12:31 PM 11.2 884 7.8 8.02/3/2005 1:23 PM 11.1 756 7.7 8.92/10/2005 12:17 PM 12.4 741 7.9 10.62/17/2005 2:13 PM 13.0 517 7.8 10.72/24/2005 12:43 PM 13.4 506 7.7 9.73/3/2005 12:31 PM 13.7 499 7.8 10.63/10/2005 2:00 PM 15.7 531 7.8 10.13/17/2005 12:52 PM 14.2 580 7.9 11.03/24/2005 1:39 PM 14.5 400 7.7 10.13/31/2005 12:19 PM 14.2 270 7.6 10.44/7/2005 1:09 PM 13.7 262 7.6 10.64/14/2005 1:00 PM 13.5 293 7.9 11.04/21/2005 1:31 PM 14.5 284 7.9 11.34/28/2005 12:18 PM 14.8 277 7.7 12.55/5/2005 1:24 PM 15.0 260 7.8 10.55/12/2005 12:46 PM 15.3 197 7.8 10.15/19/2005 1:33 PM 15.6 142 7.5 9.85/26/2005 1:14 PM 18.6 97 7.6 9.16/2/2005 1:16 PM 20.7 123 7.6 9.16/9/2005 11:28 AM 17.8 143 7.4 9.06/16/2005 1:21 PM 18.5 219 7.5 9.96/23/2005 2:42 PM 18.8 266 NA 10.16/30/2005 2:06 PM 21.2 258 7.6 9.87/7/2005 12:54 PM 20.0 277 7.6 11.07/13/2005 7:47 AM 22.2 404 7.9 8.57/21/2005 1:39 PM 24.1 454 7.9 9.97/28/2005 2:35 PM 24.4 513 8.2 10.98/4/2005 12:31 PM 23.8 487 8.0 10.6
153
A8: 541SJC501 – SJR @ Airport Way continued…
Date TimeTemp (ºC)
Field SC (umhos) pH
Dissolved Oxygen (mg/L)
Turbidity (ntu)
8/11/2005 1:56 PM 24.6 491 8.1 9.88/18/2005 1:57 PM 23.7 479 7.9 9.58/25/2005 12:36 PM 23.4 487 7.8 9.29/1/2005 12:45 PM 23.3 698 7.9 12.79/8/2005 12:24 PM 22.3 651 7.8 9.39/15/2005 12:57 PM 20.4 491 7.7 9.59/21/2005 10:50 AM 20.5 424 7.7 9.49/22/2005 2:22 PM 21.9 434 7.5 8.99/29/2005 1:02 PM 20.8 452 7.6 8.4
Count 264 265 263 216 54Min 7.1 97 6.1 1.3 12Max 27.1 1200 9.1 16.6 86.6Mean 17.4 685 7.9 10.6 35.2Geo Mean 16.5 636 7.9 10.4 33.2Median 17.0 705 7.9 10.5 30.8Quartile 1 13.1 496 7.7 9.5 27.2Quartile 3 22.3 848 8.1 11.5 42.2NOTE: For values reported as < (less than), half the detection limit was used.
NA = Data not applicableINA = Site was inaccessibleDRY = Site had no flow
154
A8: 541SJC501 – SJR @ Airport Way continued…
DateTSS
(mg/L)TOC
(mg/L)Total Coli
MPNE. coli MPN
10/5/2000 4010/12/2000 45 3.810/19/2000 1.510/26/2000 39 <111/2/2000 45 4.211/9/2000 35 3.4
11/16/2000 28 3.211/21/2000 1611/30/2000 24 1.512/7/2000 24 <1
12/12/2000 37 2.112/21/2000 NA 3.412/28/2000 16 2.21/4/2001 13 3.01/11/2001 38 3.11/18/2001 26 3.81/25/2001 37 4.52/1/2001 29 5.22/8/2001 23 4.42/10/2001 29 2.12/11/2001 23 3.02/15/2001 42 2.72/22/2001 NA 3.83/1/2001 51 4.43/8/2001 83 7.43/15/2001 56 5.63/22/2001 53 2.13/29/2001 52 <14/5/2001 27 NA4/12/2001 36 6.34/19/2001 49 5.14/26/2001 2.45/3/2001 37 2.45/10/2001 33 2.55/17/2001 2.55/24/2001 66 3.65/31/2001 48 4.46/7/2001 52 3.76/14/2001 52 106/21/2001 NA 6.86/28/2001 60 6.47/5/2001 3.77/11/2001 5.57/19/2001 4.8
155
A8: 541SJC501 – SJR @ Airport Way continued…
DateTSS
(mg/L)TOC
(mg/L)Total Coli
MPNE. coli MPN
7/26/2001 5.28/2/2001 4.68/9/2001 7.78/16/2001 58 5.78/23/2001 54 7.78/30/2001 28 9.99/6/2001 32 109/13/2001 33 8.49/20/2001 NA 7.49/27/2001 45 1010/4/2001 NA 8.6
10/11/2001 41 1310/18/2001 42 1410/25/2001 4.811/1/2001 4211/8/2001 40
11/15/2001 41 6.111/20/2001 39 NA11/29/2001 24 NA12/6/2001 35 3.7
12/13/2001 21 1.912/20/2001 18 3.112/27/2001 241/3/2002 971/10/2002 601/17/2002 261/24/2002 181/31/2002 14 NA2/7/2002 27 NA2/14/2002 25 NA2/21/2002 422/28/2002 47 6.53/7/2002 443/7/2002 46 6.53/14/2002 48 3.83/21/2002 42 3.13/28/2002 34 3.84/4/2002 46 NA4/11/2002 374/18/2002 35 184/25/2002 39 NA
156
A8: 541SJC501 – SJR @ Airport Way continued…
DateTSS
(mg/L)TOC
(mg/L)Total Coli
MPNE. coli MPN
5/2/2002 38 3.85/9/2002 55 NA5/16/2002 39 NA5/23/2002 35 NA5/30/2002 NA 2.66/6/2002 64 1.66/13/2002 NA NA6/20/2002 62 2.96/27/2002 80 5.67/31/2002 >2419.6 338/15/2002 3.78/22/2002 3.88/29/2002 429/5/2002 4.49/12/2002 27 NA9/19/2002 37 NA9/26/2002 36 NA10/3/2002 25 3.1
10/10/2002 36 2.710/17/2002 43 3.210/24/2002 51 2.010/31/2002 37 2.811/7/2002 42 NA
11/14/2002 50 4.311/21/2002 32 3.211/26/2002 37 3.212/5/2002 27 2.8
12/12/2002 37 2.412/19/2002 78 5.912/24/2002 611/2/2003 411/9/2003 291/16/2003 45 866 341/23/2003 321/30/2003 422/6/2003 262/13/2003 302/20/2003 342/27/2003 533/6/2003 653/13/2003 NA 4.93/20/2003 NA 4.5
157
A8: 541SJC501 – SJR @ Airport Way continued…
DateTSS
(mg/L)TOC
(mg/L)Total Coli
MPNE. coli MPN
3/27/2003 62 3.14/3/2003 NA NA4/10/2003 NA 2.44/17/2003 48 2.84/24/2003 43 3.7 >2419.6 2145/1/2003 11 3.95/8/2003 NA 3.05/15/2003 52 2.85/22/2003 32 2.25/29/2003 45 3.86/5/2003 51 4.36/12/2003 54 2.36/19/2003 42 2.76/26/2003 42 3.37/31/2003 >2419.6 468/28/2003 >2419.6 449/25/2003 >2419.6 46
10/30/2003 >2419.6 27611/20/2003 >2419.6 521/29/2004 1986 332/26/2004 >2419.6 13003/11/2004 6.83/18/2004 4.63/25/2004 >2419.6 314/1/2004 5.04/15/2004 3.34/22/2004 3.04/29/2004 3.1 2420 1545/6/2004 2.95/13/2004 3.05/20/2004 3.45/27/2004 6.8 >2419.6 1116/3/2004 6.06/10/2004 6.56/17/2004 5 >2419.6 596/24/2004 >2419.6 667/1/2004 6.87/8/2004 7.1 >2419.6 467/15/2004 4.57/22/2004 3.27/29/2004 4.3 >2419.6 748/5/2004 4.48/12/2004 5.9 >2419.6 388/19/2004 4.1
158
A8: 541SJC501 – SJR @ Airport Way continued…
DateTSS
(mg/L)TOC
(mg/L)Total Coli
MPNE. coli MPN
8/26/2004 >2419.6 369/16/2004 >2419.6 249/30/2004 >2419.6 16
10/14/2004 >2419.6 20110/28/2004 40 3.6 >2419.6 24811/4/2004 41 4.5 >2419.6 96
11/11/2004 41 5.011/18/2004 37 5.2 >2419.6 5211/23/2004 25 4.612/2/2004 14 3.912/9/2004 31 4.9 >2419.6 142
12/16/2004 54 4.812/22/2004 20 4.0 >2419.6 3112/29/2004 50 4.21/6/2005 110 10 1986 3261/13/2005 150 9.41/20/2005 73 >2419.6 391/27/2005 75 6.62/3/2005 49 9.9 >2419.6 622/10/2005 48 5.22/17/2005 160 7.2 >2419.6 >2419.62/24/2005 78 7.83/3/2005 54 6.23/10/2005 54 NA 457 373/17/2005 39 4.13/24/2005 97 8.3 >2419.6 >2419.63/31/2005 43 5.04/7/2005 28 3.1 2420 464/14/2005 46 NA4/21/2005 40 3.0 >2419.6 564/28/2005 39 NA5/5/2005 NA 2.8 >2419.6 615/12/2005 34 2.85/19/2005 46 2.5 >2419.6 1925/26/2005 30 2.66/2/2005 12 4.06/9/2005 37 NA >2419.6 1736/16/2005 55 2.96/23/2005 58 2.9 >2419.6 636/30/2005 61 2.17/7/2005 58 2.4 >2419.6 647/13/2005 58 2.47/21/2005 56 2.7 >2419.6 337/28/2005 54 3.08/4/2005 51 3.1 >2419.6 24
159
160
DateTSS
(mg/L)TOC
(mg/L)Total Coli
MPNE. coli MPN
8/11/2005 65 2.68/18/2005 45 2.8 >2419.6 708/25/2005 44 3.39/1/2005 54 2.8 >2419.6 559/8/2005 42 2.8 >2419.6 17339/15/2005 40 2.89/21/2005 >2419.6 1029/22/2005 27 NA9/29/2005 62 2.7
Count 16
A8: 541SJC501 – SJR @ Airport Way continued…
3 163 46 46Min 11 0.5 457 16Max 160 18 2420 2420Mean 44 4.5 NA NAGeo Mean 40 3.9 2263 86Median 42 3.8 2420 60QuaQua
rtile 1 33 2.8 2420 38rtile 3 52 5.2 2420 151E: For values reported as < (less than), half the detection limit was used For values reported as > (greater than), 2420 was used
Data not applicable Site was inaccessible
= Site had no flow
NOT
NA =INA =DRY
A8: 541SJC501 – SJR @ Airport Way continued…
DateNitrate (mg/L)
Nitrate (mg/L)
TKN (mg/L)
Ammonia-N (mg/L)
Phosphorus (mg/L)
Ortho-phosphate-
P (mg/L)
Potassium (mg/L)
BOD 5-Day (mg/L)
BOD 10-Day (mg/L)
10/12/2000 1.1 2.010/26/2000 4.6 <2 0.2 <1 2.7 0.9 1.511/16/2000 1.1 2.211/30/2000 8.8 <2 0.2 <1 4.4 0.9 1.612/12/2000 1.2 1.912/28/2000 8.3 <2 0.2 <1 5.2 1.1 2.01/11/2001 1.4 2.31/25/2001 7.9 <2 0.2 <1 5.9 1.7 2.82/8/2001 10 <2 0.2 <1 6.3 1.5 1.72/10/2001 10 <2 0.2 <1 5.9 1.1 2.92/11/2001 10 <2 0.2 <1 5.82/22/2001 7.4 <2 0.2 <1 4.3 1.4 2.23/15/2001 12 <2 0.3 <1 6.5 1.5 2.93/29/2001 8.3 <2 0.2 <1 5.5 1.9 3.34/19/2001 9.1 <2 0.2 <1 4.6 1.8 3.44/26/2001 4.5 <2 <1 0.1 <1 2.4 1.4 2.85/17/2001 3.8 <2 0.1 <1 2.5 1.1 1.95/31/2001 7.8 <1.0 0.2 NA 4.5 1.8 3.36/7/2001 8.8 <1.0 0.2 <1 4.4 3.5 5.56/14/2001 10 <2 <1 4.7 2.3 4.66/21/2001 7.1 <2 0.2 <1 4.7 4.3 6.96/28/2001 8.9 <2 0.2 <1 4.6 2.2 3.88/16/2001 7.8 <2 0.3 <1 4.18/30/2001 8.4 <2 0.2 <1 4.99/27/2001 10 <2 0.2 <1 4.8
10/25/2001 0.7 1.811/29/2001 NA NA NA 0.1 5.2 0.8 1.312/13/2001 0.8 1.6
161
A8: 541SJC501 – SJR @ Airport Way continued…
DateNitrate (mg/L)
Nitrate (mg/L)
TKN (mg/L)
Ammonia-N (mg/L)
Phosphorus (mg/L)
Ortho-phosphate-
P (mg/L)
Potassium (mg/L)
BOD 5-Day (mg/L)
BOD 10-Day (mg/L)
12/27/2001 NA 0.5 0.2 0.1 4.3 1.1 2.11/17/2002 1.0 1.81/31/2002 NA NA 0.2 NA NA 1.1 1.92/14/2002 1.4 2.52/28/2002 NA NA NA 0.1 NA 1.5 2.63/14/2002 2.0 3.34/25/2002 NA NA 0.2 NA 3.1 1.1 2.05/16/2002 0.9 1.65/30/2002 NA NA NA 0.1 NA 1.7 2.66/13/2002 7.1 NA 0.2 <1.0 4.2 2.5 4.96/20/2002 NA 0.7 0.2 0.1 4 4.1 7.68/29/2002 NA 0.8 <0.05 <0.03 5 5.1 8.59/26/2002 NA 0.6 NA 0.2 4.7 2.1 3.8
10/31/2002 NA 0.2 0.2 0.2 2.7 1.0 1.611/21/2002 NA 0.9 0.2 0.2 3.7 1.1 1.912/19/2002 NA 1.9 0.4 <0.03 6.7 4.6 6.61/30/2003 NA 0.7 0.2 0.2 2.7 1.1 1.72/27/2003 12 1.9 0.1 <1.0 6.4
Count 23 NA 30 1 31 33 33 41 41Min 3.8 NA 0.2 0.5 0.03 0.0 2.4 0.7 1.3Max 12.0 NA 1.9 0.5 0.4 0.5 6.7 5.1 8.5Mean 8.4 NA 0.9 0.5 0.2 0.4 4.6 1.7 3.0Geo Mean 8.1 NA 0.9 0.5 0.2 0.3 4.4 1.5 2.6Median 8.4 NA 1.0 0.5 0.2 0.5 4.6 1.4 2.3Quartile 1 7.6 NA 0.8 0.5 0.2 0.2 4.1 1.1 1.9Quartile 3 10.0 NA 1.0 0.5 0.2 0.5 5.2 1.9 3.3NOTE: For values reported as < (less than), half the detection limit was used.
NA = Data not applicableINA = Site was inaccessibleDRY = Site had no flow
162
A8: 541SJC501 – SJR @ Airport Way continued…
DateHardness
(mg/L)
Total Arsenic (ug/L)
Total Cadmium
(ug/L)
Total Chromium
(ug/L)
Total Copper (ug/L)
Total Lead (ug/L)
Total Nickel (ug/L)
Total Zinc (ug/L)
Total Mercury (ug/L)
10/26/2000 140 2.1 2.2 <5 <511/30/2000 170 1.2 1.3 <5 <5 4.012/28/2000 190 <1 1.7 <5 <5 <21/25/2001 220 1.6 2.5 <5 <5 3.32/10/2001 210 1.3 2.2 <5 <5 <22/11/2001 140 1.6 2.8 <5 <5 3.02/22/2001 210 1.4 3.2 <5 <5 5.23/29/2001 80 2.1 3.2 <5 <5 5.64/26/2001 150 1.4 9.4 <5 <5 5.35/31/2001 180 2.8 4.1 <5 <5 5.46/7/2001 190 2.2 <1 2.5 3.6 <5 <5 6.3 <0.26/14/2001 NA <2.0 <1 2.5 3.3 <5 <5 5.0 <0.26/21/2001 170 2.1 <1 1.7 2.1 <5 <5 3.0 <0.26/28/2001 160 3.4 <1 3.2 3.4 <5 5.1 6.2 <0.27/26/2001 160 NA NA 2.6 2.8 <5 <5 4.5 NA8/30/2001 2.4 <1 1.3 1.6 <5 <5 2.19/27/2001 <4 <1 <1 4.1 <5 12 22 <0.2
10/25/2001 92 <4 <0.1 1.2 2.2 <5 <5 4.4 <0.211/29/2001 160 <4 <0.1 <1 <1 <5 <5 2.9 <0.212/27/2001 170 <4 <0.1 1.8 2.2 <5 <5 6.0 <0.21/31/2002 <4.0 <0.1 <1.0 NA <5.0 <5.0 <2.0 <0.22/28/2002 230 <4.0 <0.1 2.5 4.9 <5.0 <5.0 5.7 <0.23/28/2002 220 <4.0 <0.1 1.3 2.7 <5.0 <5.0 7.7 <0.24/25/2002 91 <4.0 <0.1 <1.0 1.4 <5.0 <5.0 <2.0 <0.25/30/2002 120 <4.0 <0.1 2.3 3.2 <5.0 <5.0 4.6 <0.26/20/2002 170 <4.0 <0.1 3 3.3 <5.0 <5.0 5.0 <0.29/26/2002 180 4.9 <0.1 1.6 NA <5.0 <5.0 2.5 <0.2
163
A8: 541SJC501 – SJR @ Airport Way continued…
DateHardness
(mg/L)
Total Arsenic (ug/L)
Total Cadmium
(ug/L)
Total Chromium
(ug/L)
Total Copper (ug/L)
Total Lead (ug/L)
Total Nickel (ug/L)
Total Zinc (ug/L)
Total Mercury (ug/L)
10/31/2002 150 <4.0 <0.1 2.0 2.9 <5.0 <5.0 3.0 <0.211/21/2002 190 <4.0 <0.1 1.7 2.0 <5.0 <5.0 2.9 <0.23/27/2003 250 <4.0 NA <1.0 2.6 <5.0 <5.0 2.1 <0.24/24/2003 99 <4.0 <0.1 NA NA NA <5.0 3.9 <0.25/29/2003 110 <4.0 <0.1 <1.0 3.5 <5.0 <5.0 2.6 <0.26/26/2003 93 <4.0 <0.1 1.3 2.4 <5.0 <5.0 3.1 <0.2
Count 29 22 21 32 30 32 33 32 21Min 80.0 1.0 0.1 0.5 0.5 2.5 2.5 1.0 0.1Max 250.0 4.9 0.5 3.2 9.4 2.5 12.0 22.0 0.1Mean 161.9 2.2 0.2 1.6 2.9 2.5 2.9 4.4 0.1Geo Mean 155.1 2.1 0.1 1.4 2.6 2.5 2.7 3.6 0.1Median 170.0 2.0 0.1 1.6 2.8 2.5 2.5 4.0 0.1Quartile 1 140.0 2.0 0.1 1.2 2.2 2.5 2.5 2.8 0.1Quartile 3 190.0 2.0 0.5 2.2 3.3 2.5 2.5 5.3 0.1NOTE: For values reported as < (less than), half the detection limit was used.
NA = Data not applicableINA = Site was inaccessibleDRY = Site had no flow
164
A8: 541SJC501 – SJR @ Airport Way continued…
DateHardness
(mg/L)
Dissolved Arsenic (ug/L)
Dissolved Cadmium
(ug/L)
Dissolved Chromium
(ug/L)
Dissolved Copper (ug/L)
Dissolved Lead (ug/L)
Dissolved Nickel (ug/L)
Dissolved Zinc
(ug/L)
Dissolved Mercury (ug/L)
10/26/2000 140 <1 <1 <5 <5 <211/30/2000 170 <1 <1 <5 <5 <212/28/2000 190 <1 <1 <5 <5 41/25/2001 220 <1 <1 <5 <5 <22/10/2001 210 <1 <1 <5 <5 <22/11/2001 140 <1 1 <5 <5 <22/22/2001 210 <1 <1 <5 <5 <23/29/2001 80 <1 1.4 <5 <5 <24/26/2001 150 <1 <1 <5 <5 2.85/31/2001 180 <1 <1 <5 <5 <26/7/2001 190 <2 <1 <1 1.4 <5 <5 <2 <0.26/14/2001 NA <2.0 <1 <1 1.1 <5 <5 <2 <0.26/21/2001 170 <2.0 <1 <1 <1 <5 <5 <2 <0.26/28/2001 160 3.0 <1 <1 <1 <5 <5 <2 <0.27/26/2001 160 NA NA NA NA NA NA NA NA8/30/2001 2.1 <1 <1 1.2 <5 <5 <29/27/2001 <4 <1 <1 3.4 <5 12 21 <0.2
10/25/2001 92 <4 <0.1 <1 1.1 <5 <5 5.2 <0.211/29/2001 160 <4 <0.1 <1 <1 <5 <5 3.1 <0.212/27/2001 170 <4 <0.1 <1 <1 <5 <5 <2 <0.21/31/2002 <4.0 <0.1 <1.0 NA <5.0 <5.0 <2.0 <0.22/28/2002 230 <4.0 <0.1 <1.0 1.9 <5.0 <5.0 <2.0 <0.23/28/2002 220 <4.0 <0.1 <1.0 1.5 <5.0 <5.0 3.2 <0.24/25/2002 91 <4.0 <0.1 <1.0 <1.0 <5.0 <5.0 NA <0.25/30/2002 120 <4.0 <0.1 <1.0 1.6 <5.0 <5.0 <2.0 <0.26/20/2002 170 <4.0 <0.1 <1.0 2 <5.0 <5.0 <2.0 <0.29/26/2002 180 <4.0 <0.1 <1.0 2.3 <5.0 <5.0 <2.0 <0.2
165
A8: 541SJC501 – SJR @ Airport Way continued…
DateHardness
(mg/L)
Dissolved Arsenic (ug/L)
Dissolved Cadmium
(ug/L)
Dissolved Chromium
(ug/L)
Dissolved Copper (ug/L)
Dissolved Lead (ug/L)
Dissolved Nickel (ug/L)
Dissolved Zinc
(ug/L)
Dissolved Mercury (ug/L)
10/31/2002 150 <4.0 <0.1 <1.0 1.3 <5.0 <5.0 <2.0 <0.211/21/2002 190 <4.0 <0.1 <1.0 <1.0 <5.0 <5.0 <2.0 <0.23/27/2003 2504/24/2003 995/29/2003 1106/26/2003 93
Count 29 18 18 28 27 28 28 27 17Min 80.0 1.0 0.1 0.5 0.5 2.5 2.5 1.0 0.1Max 250.0 3.0 0.5 0.5 3.4 2.5 12.0 21.0 0.1Mean 161.9 1.9 0.2 0.5 1.0 2.5 2.8 2.2 0.1Geo Mean 155.1 1.8 0.1 0.5 0.9 2.5 2.6 1.4 0.1Median 170.0 2.0 0.1 0.5 0.5 2.5 2.5 1.0 0.1Quartile 1 140.0 2.0 0.1 0.5 0.5 2.5 2.5 1.0 0.1Quartile 3 190.0 2.0 0.5 0.5 1.4 2.5 2.5 1.0 0.1NOTE: For values reported as < (less than), half the detection limit was used.
NA = Data not applicableINA = Site was inaccessibleDRY = Site had no flow
166
A8: 541SJC501 – SJR @ Airport Way continued…
DateChloride (mg/L)
Sulfate (mg/L)
Calcium (mg/L)
Magnesium (mg/L)
TDS (mg/L)
Carbonate (mg/L)
Bicarbonate (mg/L)
Total Alkalinity
(mg/L)Sodium (mg/L)
11/30/2000 75 69 31 16 410 <1 120 100 7112/28/2000 99 94 36 19 430 <1 140 120 891/25/2001 120 120 40 22 540 <1 150 120 1102/10/2001 400 470 47 24 550 <1 150 120 1202/11/2001 120 130 45 24 540 <1 150 120 1102/22/2001 81 100 31 16 340 <1 110 87 733/29/2001 110 130 44 24 540 <1 150 120 1104/26/2001 40 18 9 210 4 50 54 305/31/2001 83 77 33 17 350 <1 92 92 676/7/2001 18 19 39 20 380 <1 120 100 816/14/2001 98 100 42 21 460 <1 130 110 906/21/2001 98 95 40 21 440 <1 140 120 866/28/2001 91 91 36 19 390 <1 130 100 738/30/2001 97 84 36 18 410 <1 140 110 799/27/2001 NA 75 35 18 390 <1 NA NA 76
10/25/2001 49 42 20 10 240 <1 83 NA 4211/29/2001 99 89 34 19 440 <1 130 110 8912/27/2001 110 100 35 21 480 <1.0 140 120 992/28/2002 NA 160 49 26 510 <1.0 112 90 1303/28/2002 130 140 45 25 630 <1.0 150 120 1204/25/2002 47 51 20 10 180 <1.0 64 53 405/30/2002 64 63 27 13 270 <1.0 95 78 566/20/2002 96 97 36 19 NA <1.0 130 110 829/26/2002 99 77 39 20 400 <1.0 150 120 85
167
A8: 541SJC501 – SJR @ Airport Way continued…
DateChloride (mg/L)
Sulfate (mg/L)
Calcium (mg/L)
Magnesium (mg/L)
TDS (mg/L)
Carbonate (mg/L)
Bicarbonate (mg/L)
Total Alkalinity
(mg/L)Sodium (mg/L)
10/31/2002 85 69 31 16 370 <1.0 120 100 7211/21/2002 120 100 39 22 520 <1.0 150 130 1003/27/2003 160 170 52 294/24/2003 51 59 22 115/29/2003 58 57 24 126/26/2003 45 47 21 10
Count 27 30 30 30 25 26 25 24 26Min 18 19 18 9 180 0.5 50 53 30Max 400 470 52 29 630 4.0 150 130 130Mean 100 100 35 18 420 0.6 120 100 84Geo Mean 87 85 34 18 400 0.5 120 100 80Median 97 90 36 19 410 0.5 130 110 84Quartile 1 70 65 31 16 370 0.5 112 98 72Quartile 3 110 100 40 22 510 0.5 150 120 100NOTE: For values reported as < (less than), half the detection limit was used.
NA = Data not applicableINA = Site was inaccessibleDRY = Site had no flow
168
169
A8: 541SJC501 – SJR @ Airport Way continued…
Date Result Control Result Control
Result (million/m
l)
Control (million/
ml) MDD(%)10/26/2000 100 100 NA NA01/25/2001 95 100 100 10002/22/2001 95 100 100 10003/29/2001 100 100 100 10004/26/2001 100 100 100 9005/31/2001 85 90 100 10006/28/2001 85 100 100 10010/25/2001 100 100 100 10011/29/2001 NA NA 100 10012/27/2001 95 100 100 10001/31/2002 100 100 100 10002/28/2002 100 100 100 10004/25/2002 100 100 100 10005/30/2002 100 100 100 10006/20/2002 100 100 100 10008/29/2002 100 100 100 10009/26/2002 100 95 100 10010/31/2002 100 100 100 10011/21/2002 100 100 100 10012/19/2002 100 100 100 100 2.19* 2.93 N/A01/30/2003 100 100 100 100 5.32 3.07 N/A03/27/2003 95 100 100 100 2.44** 1.73 N/A05/29/2003 90 100 100 100 3.49** 2.03 1.411/18/2004 3.69** 1.79 24.012/22/2004 5.16** 1.95 N/A01/20/2005 5.53** 1.92 7.202/17/2005 3.93** 1.78 12.003/24/2005 N/A N/A N/A04/21/2005 2.32 1.63 3.105/18/2005 2.58 1.94 13.006/23/2005 N/A N/A N/A07/21/2005 3.57** 1.72 13.008/18/2005 3.76** 1.76 18.009/22/2005 3.98 1.72 N/A
Count 22 22 22 22 13 13 8
* Significantly reduced from the lab control.** Significantly greater than the lab control.^ Fish were from a "forced hatch," duplicate failed QA.1 Duplicate sample for the set was low - 77% recovery.
3 Samples qualified, but duplicate sample recovery for the set was high - 126% (53.8%/42.5%)NA = Data not applicableINA = Site was inaccessibleDRY = Site had no flow
2 Testing for the Fathead minnow was initiated when samples were approx. 48h old due to untimely shipping of fish by fish supplier.
96h Acute Fathead Minnow
(% Survival)
48h Acute Ceriodaphnia Dubia
(% Survival) Algae Cell Growth
170
A8: 541SJC501 – SJR @ Airport Way continued…
DateResult
(% Survival)Control
(% Survival)
Avg Dry Weight Result (mg)
Avg Dry Weight Control
(mg)Growth MDD(%)
Result (% Survival)
Control (% Survival)
Avg # Young / Adult Result
Avg # Young /
Adult Control
Repro MDD(%)
03/11/2004 96.7 97.5 0.59 0.60 12 100.0 100.0 22.0 20 3103/25/2004 93.3 97.5 0.55* 0.68 11 100.0 100.0 25.8 20.9 N/A04/15/2004 66.7* 97.5 0.38* 0.59 20 100.0 100.0 19.7 21.8 1404/29/2004 23.3* 100.0 0.11* 0.62 14 100.0 100.0 24.9 20 1205/13/2004 83.3* 100.0 0.56 0.68 22 100.0 100.0 24.0 17.3 2905/27/2004 N/A N/A N/A N/A N/A N/A N/A N/A N/A N/A06/10/2004 100.0 97.6 0.55 0.58 13 100.0 100.0 28.2 25.2 1506/24/2004 90.0 100.0 0.53 0.67 22 100.0 100.0 33.9 21.1 1811/18/2004 92.9 100.0 0.55 0.46 20 90.0 100.0 16.7 18.4 1612/22/2004 89.1 95.2 0.45* 0.61 N/A 100.0 100.0 19.0* 24.7 n/a01/20/2005 92.3 97.4 0.75* 0.92 6.4 100.0 100.0 23.1 15.9 2402/17/2005 95.0 97.5 0.35 0.38 17 90.0 100.0 21.3* 28.8 8.503/24/2005 85.0 97.5 0.43 0.41 16 100.0 100.0 13.1* 18.3 1704/21/2005 N/A N/A N/A N/A N/A 100.0 100.0 14.6* 19.4 2205/18/2005 62.5* 100.0 0.41* 0.62 13 100.0 100.0 14.7* 20.50 1606/23/2005 N/A N/A N/A N/A N/A 100.0 100.0 22.7 20.9 1307/21/2005 87.5* 100.0 0.59 0.62 7.2 100.0 100.0 30.3 22.1 1308/18/2005 N/A N/A N/A N/A N/A 100.0 100.0 30.6 21.5 1809/22/2005 85.0 97.5 0.28* 0.5 15.0 90.0 90.0 11.9* 19.9 17
Count 15 15 15 15 14 18 18 18 18 16
* Significantly reduced from the lab control.** Significantly greater than the lab control.^ Fish were from a "forced hatch," duplicate failed QA.1 Duplicate sample for the set was low - 77% recovery.
3 Samples qualified, but duplicate sample recovery for the set was high - 126% (53.8%/42.5%)NA = Data not applicableINA = Site was inaccessibleDRY = Site had no flow
2 Testing for the Fathead minnow was initiated when samples were approx. 48h old due to untimely shipping of fish by fish supplier.
Chronic Ceriodaphnia Dubia - 6 dayChronic Fathead Minnow - 7day
171
APPENDIX B
NORTHEAST BASIN
APPENDIX B: NORTHEAST BASIN B1: 531SAC001 – Cosumnes River at Twin Cities Road…………………………….03-11 B2: 531SAC002 – Mokelumne River at New Hope Road……………………………12-23 B3: 531SJC507 – Pixley Slough at Davis Road………………………………………24-32 B4: 544SJC508 – Bear Creek at Thorton Road (J8)………………..………………..33-38 B5: 531SJC515 – Bear Creek at Lower Sacramento Road…………….……………39-46
2
B1: 531SAC001 – Cosumnes River at Twin Cities Road Station Code:531SAC001
Location: Latitude 38.29083, Longitude -121.37583
Date TimeTemp (ºC)
Field SC (umhos) pH
Dissolved Oxygen (mg/L)
Turbidity (ntu)
10/24/2000 7:20 AM 12.6 98 6.211/28/2000 8:00 AM 9.5 125 6.612/27/2000 7:45 AM 5.9 133 6.81/23/2001 7:38 AM 8.0 145 8.92/20/2001 8:01 AM 10.9 135 6.83/27/2001 7:54 AM 15.9 153 6.44/24/2001 8:00 AM 18.9 145 6.75/29/2001 7:40 AM 19.2 113 6.06/26/2001 7:30 AM 20.8 427 7.0 NA7/24/2001 DRY DRY DRY DRY DRY8/28/2001 DRY DRY DRY DRY DRY9/25/2001 8:03 AM DRY DRY DRY DRY
10/23/2001 DRY DRY DRY DRY DRY11/27/2001 7:27 AM 8.6 97 8.5 11.112/26/2001 8:20 AM 9.2 141 6.6 NA1/29/2002 6:59 AM 5.2 161 7.8 13.72/26/2002 6:52 AM 10.4 89 8.1 14.13/26/2002 7:41 AM 10.9 113 7.8 10.84/23/2002 7:42 AM 15.9 74 7.8 9.85/28/2002 6:59 AM 20.2 64 8.1 9.16/18/2002 7:20 AM 22.0 73 7.5 7.97/31/2002 DRY DRY DRY DRY DRY DRY8/27/2002 8:20 AM DRY DRY DRY DRY9/24/2002 7:25 AM DRY DRY DRY DRY
10/29/2002 7:40 AM DRY DRY DRY DRY DRY11/19/2002 6:59 AM DRY DRY DRY DRY12/17/2002 11:30 AM 10.5 89 8.1 11.1 2481/28/2003 7:22 AM 10.8 82 7.9 11.5 13.03/25/2003 7:19 AM 13.6 109 7.6 10.5 31.04/22/2003 7:10 AM 14.3 76 7.9 10.0 18.15/27/2003 7:46 AM 19.3 46 7.7 9.2 14.26/24/2003 1:07 PM 24.8 69 8.1 11.3 3.27/29/2003 12:40 PM DRY DRY DRY DRY DRY8/26/2003 8:07 AM DRY DRY DRY DRY DRY9/23/2003 8:00 AM DRY DRY DRY DRY DRY
10/28/2003 8:15 AM DRY DRY DRY DRY DRY11/18/2003 7:45 AM DRY DRY DRY DRY DRY1/28/2004 7:16 AM 8.1 105 8.1 13.5 8.92/24/2004 8:17 AM 10.7 112 6.8 10.8 14.43/24/2004 7:10 AM 14.0 52 7.5 10.4 13.4
3
B1: 531SAC001 – Cosumnes River at Twin Cities Road continued…
Date TimeTemp (ºC)
Field SC (umhos) pH
Dissolved Oxygen (mg/L)
Turbidity (ntu)
4/28/2004 7:06 AM 19.8 60 7.7 8.9 6.25/26/2004 7:45 AM 19.0 65 7.4 9.3 5.06/23/2004 7:12 AM DRY DRY DRY DRY DRY7/28/2004 7:30 AM DRY DRY DRY DRY DRY8/25/2004 7:15 AM DRY DRY DRY DRY DRY9/29/2004 7:30 AM DRY DRY DRY DRY DRY
10/27/2004 7:08 AM 12.8 98 8.6 12.011/22/2004 8:07 AM 6.7 107 9.3 12.112/28/2004 7:12 AM 8.2 119 8.3 12.01/26/2005 7:47 AM 9.1 99 8.1 11.52/23/2005 7:01 AM 10.6 91 7.9 NA3/29/2005 8:11 AM 11.5 95 6.8 10.64/26/2005 7:52 AM 13.4 67 8.3 11.35/24/2005 7:24 AM 16.7 47 8.2 9.86/28/2005 7:18 AM 21.5 65 7.1 8.57/26/2005 7:11 AM 24.9 88 8.1 7.98/23/2005 7:15 AM DRY DRY DRY DRY9/27/2005 7:47 AM DRY DRY DRY DRY
Count 38 38 38 27 11Min 5.2 46 6.0 7.9 3.2Max 24.9 427 9.3 14.1 248Mean 13.8 106 7.6 10.7 34.1Geo Mean 12.8 96 7.6 10.6 14.1Median 12.7 98 7.8 10.8 13.4Quartile 1 9.7 73 6.9 9.6 7.6Quartile 3 19.0 118 8.1 11.5 16.3NOTE: For values reported as < (less than), half the detection limit was used.
NA = Data not applicableINA = Site was inaccessibleDRY = Site had no flow
4
B1: 531SAC001 – Cosumnes River at Twin Cities Road continued…
DateTSS
(mg/L)TOC
(mg/L)Total Coli
MPNE. coli MPN
10/24/2000 24 1.511/28/2000 9 3.112/27/2000 <5 1.71/23/2001 14 1.82/20/2001 38 1.63/27/2001 49 NA4/24/2001 34 4.75/29/2001 20 6.76/26/2001 11 202/26/2002 NA3/26/2002 2.34/23/2002 NA5/28/2002 2.16/18/2002 <1.07/31/2002 DRY DRY
12/17/2002 4.73/25/2003 2.34/22/2003 2.3 420 375/27/2003 NA6/24/2003 NA7/29/2003 DRY DRY8/26/2003 DRY DRY9/23/2003 DRY DRY
10/28/2003 DRY DRY11/18/2003 DRY DRY1/28/2004 1553 832/24/2004 228 433/24/2004 416 294/28/2004 1553 805/26/2004 >2419.6 1676/23/2004 DRY DRY7/28/2004 DRY DRY8/25/2004 DRY DRY9/29/2004 DRY DRY
10/27/2004 5.0 >2419.6 92111/22/2004 3.3 >2419.6 9312/28/2004 2.0 435 741/26/2005 1.8 130 362/23/2005 3.0 1733 111
5
6
DateTSS
(mg/L)TOC
(mg/L)Total Coli
MPNE. coli MPN
3/29/2005 3.7 >2419.6 10464/26/2005 NA 613 365/24/2005 NA 510 576/28/2005 1.1 1986 1057/26/2005 NA >2419.6 1118/23/2005 DRY DRY DRY9/27/2005 DRY DRY DRY
Count 9 21 16 16Min 3 0.5 130 29Max 49 20 2420 1046Mean 22 3.6 NA NAGeo Mean 17 2.6 956 93Median 20 2.3 155
B1: 531SAC001 – Cosumnes River at Twin Cities Road continued…
3 82Quartile 1 11 1.8 431 42Quartile 3 34 3.7 2420 111NOT
NA =INADRY
E: For values reported as < (less than), half the detection limit was used For values reported as > (greater than), 2420 was used
Data not applicable = Site was inaccessible = Site had no flow
B1: 531SAC001 – Cosumnes River at Twin Cities Road continued…
DateNitrate (mg/L)
Nitrate-N (mg/L)
TKN (mg/L)
Ammonia-N (mg/L)
Phosphorus (mg/L)
Ortho-phosphate-
P (mg/L)
Potassium (mg/L)
BOD 5-Day (mg/L)
BOD 10-Day (mg/L)
10/24/2000 <2 <2 0.1 <1 2.3 0.6 0.911/28/2000 <2 <2 0.3 <1 3.0 0.5 0.912/27/2000 3.6 <2 0.3 1.0 3.1 0.6 1.01/23/2001 6.1 <2 0.4 <1 3.8 0.8 1.62/20/2001 4.2 <2 0.4 0.4 3.8 1.4 2.73/27/2001 <2 <2 0.4 <1 3.6 1.9 3.24/24/2001 2.6 <2 0.3 <1 3.4 1.4 2.75/29/2001 <2 <2 0.3 <1 2.9 3.9 6.16/26/2001 <2 <2 0.4 <1 8.4 3.5 5.5
11/27/2001 NA NA NA <0.03 1.7 0.8 1.212/26/2001 0.5 1.01/29/2002 0.8 1.12/26/2002 0.5 0.53/26/2002 0.4 0.94/23/2002 0.4 0.55/28/2002 0.3 0.46/18/2002 0.4 0.6
12/17/2002 2.5 3.91/28/2003 0.3 0.4
Count 9 NA 9 NA 9 10 10 19 19Min 1.0 NA 1.0 NA 0.1 0.02 1.7 0.3 0.4Max 6.1 NA 1.0 NA 0.4 1.0 8.4 3.9 6.1Mean 2.4 NA 1.0 NA 0.3 0.5 3.6 1.1 1.8Geo Mean 1.8 NA 1.0 NA 0.3 0.4 3.3 0.8 1.3Median 1.0 NA 1.0 NA 0.3 0.5 3.3 0.6 1.0Quartile 1 1.0 NA 1.0 NA 0.3 0.5 2.9 0.5 0.8Quartile 3 3.6 NA 1.0 NA 0.4 0.5 3.8 1.4 2.7NOTE: For values reported as < (less than), half the detection limit was used.
NA = Data not applicableINA = Site was inaccessibleDRY = Site had no flow
7
B1: 531SAC001 – Cosumnes River at Twin Cities Road continued…
DateHardness
(mg/L)
Total Arsenic (ug/L)
Total Cadmium
(ug/L)
Total Chromium
(ug/L)
Total Copper (ug/L)
Total Lead (ug/L)
Total Nickel (ug/L)
Total Zinc (ug/L)
Total Mercury (ug/L)
10/24/2000 33 <1 2.9 <5 <5 <2.511/28/2000 29 <1 1.8 <5 <5 4.812/27/2000 29 <1 2.3 <5 <5 4.41/23/2001 35 <1 3.2 <5 <5 4.52/20/2001 36 2.5 4.2 <5 <5 7.73/27/2001 39 1.4 3.7 <5 5.1 6.94/24/2001 38 <1 4.0 <5 <5 4.75/29/2001 43 <1 1.4 <5 <5 3.06/26/2001 3.9 <1 <1 <1 <5 <5 3.9 <0.2
11/27/2001 39 <4 <0.1 2.6 2.5 <5 <5 5.3 <0.212/26/2001 <4 <0.1 3.6 5.5 <5 <5 8.0 <0.21/29/2002 <4 <0.1 <1 1.5 <5 <5 2.9 <0.23/26/2002 <4.0 <0.1 1.7 3.5 <5.0 <5.0 4.9 <0.24/23/2002 <4.0 <0.1 <1.0 <1.0 <5.0 <5.0 <2.0 <0.25/28/2002 <4.0 <0.1 <1.0 <1.0 <5.0 <5.0 <2.0 <0.26/18/2002 <4.0 <0.1 <1.0 <1.0 <5.0 <5.0 <2.0 <0.23/25/2003 45 <4.0 <0.1 2.6 2.9 <5.0 <5.0 3 <0.24/22/2003 32 <4.0 <0.1 1.5 1.8 <5.0 <5.0 <2.0 <0.25/27/2003 19 <4.0 <0.1 <1.0 1.4 <5.0 <5.0 <2.0 <0.26/24/2003 26 <4.0 <0.1 <1.0 <1.0 <5.0 <5.0 <2.0 <0.2
Count 13 12 12 20 20 20 20 20 12Min 19.0 2.0 0.1 0.5 0.5 2.5 2.5 1.0 0.1Max 45.0 3.9 0.5 3.6 5.5 2.5 5.1 8.0 0.1Mean 34.1 2.2 0.1 1.1 2.3 2.5 2.6 3.6 0.1Geo Mean 33.3 2.1 0.1 0.8 1.7 2.5 2.6 2.8 0.1Median 35.0 2.0 0.1 0.5 2.1 2.5 2.5 3.5 0.1Quartile 1 29.0 2.0 0.1 0.5 1.2 2.5 2.5 1.0 0.1Quartile 3 39.0 2.0 0.1 1.6 3.3 2.5 2.5 4.8 0.1NOTE: For values reported as < (less than), half the detection limit was used.
NA = Data not applicableINA = Site was inaccessibleDRY = Site had no flow
8
B1: 531SAC001 – Cosumnes River at Twin Cities Road continued…
DateHardness
(mg/L)
Dissolved Arsenic (ug/L)
Dissolved Cadmium
(ug/L)
Dissolved Chromium
(ug/L)
Dissolved Copper (ug/L)
Dissolved Lead (ug/L)
Dissolved Nickel (ug/L)
Dissolved Zinc
(ug/L)
Dissolved Mercury (ug/L)
10/24/2000 3311/28/2000 29 <1 1.1 <5 <5 3.212/27/2000 29 <1 1.1 <5 <5 5.31/23/2001 35 <1 <1 <5 <5 3.92/20/2001 36 <1 1.7 <5 <5 3.33/27/2001 39 <1 1.6 <5 <5 3.14/24/2001 38 <1 1.8 <5 <5 5.15/29/2001 43 <1 <1 <5 <5 2.86/26/2001 3.2 <1 <1 <1 <5 <5 2.1 <0.2
11/27/2001 39 <4 <0.1 <1 1.2 <5 <5 5.4 <0.212/26/2001 <4 <0.1 <1 2.9 <5 <5 5.1 <0.21/29/2002 <4 <0.1 <1 <1 <5 <5 <2 <0.23/26/2002 <4.0 <0.1 <1.0 2.0 <5.0 <5.0 6.1 <0.24/23/2002 <4.0 <0.1 <1.0 <1.0 <5.0 <5.0 <2.0 <0.25/28/2002 <4.0 <0.1 <1.0 <1.0 <5.0 <5.0 <2.0 <0.26/18/2002 <4.0 <0.1 <1.0 <1.0 <5.0 <5.0 <2.0 <0.2
Count 9 8 8 15 15 15 15 15 8Min 29.0 2.0 0.1 0.5 0.5 2.5 2.5 1.0 0.1Max 43.0 3.2 0.5 0.5 2.9 2.5 2.5 6.1 0.1Mean 35.7 2.2 0.1 0.5 1.1 2.5 2.5 3.3 0.1Geo Mean 35.4 2.1 0.1 0.5 0.9 2.5 2.5 2.7 0.1Median 36.0 2.0 0.1 0.5 1.1 2.5 2.5 3.2 0.1Quartile 1 33.0 2.0 0.1 0.5 0.5 2.5 2.5 1.6 0.1Quartile 3 39.0 2.0 0.1 0.5 1.7 2.5 2.5 5.1 0.1NOTE: For values reported as < (less than), half the detection limit was used.
NA = Data not applicableINA = Site was inaccessibleDRY = Site had no flow
9
10
B1: 531SAC001 – Cosumnes River at Twin Cities Road continued…
DateChloride (mg/L)
Sulfate (mg/L)
Calcium (mg/L)
Magnesium (mg/L)
TDS (mg/L)
Carbonate (mg/L)
Bicarbonate (mg/L)
Total Alkalinity
(mg/L)Sodium (mg/L)
10/24/2000 5 7 7 4 95 <1 70 60 711/28/2000 9 8 7 3 110 <1 50 40 1312/27/2000 9 9 7 3 80 <1 50 40 131/23/2001 9 10 8 4 110 <1 50 40 142/20/2001 9 12 8 4 120 <1 46 38 123/27/2001 10 10 8 4 NA <1 56 46 154/24/2001 9 8 8 4 110 <1 51 42 125/29/2001 4 4 9 5 61 <1 44 44 7
11/27/2001 4 7 9 4 60 <1 43 35 43/25/2003 4 6 10 54/22/2003 3 3 7 45/27/2003 3 <2.0 5 26/24/2003 2 3 6 3
Count 13 13 13 13 8 9 9 9 9Min 2 1 5 2 60 0.5 43 35 4Max 10 12 10 5 120 0.5 70 60 15Mean 6 7 8 4 93 0.5 51 43 11Geo Mean 5 6 8 4 90 0.5 51 42 10Median 5 7 8 4 100 0.5 50 40 12Quartile 1 4 4 7 3 75 0.5 46 40 7Quartile 3 9 9 8 4 110 0.5 51 44 13NOTE: For values reported as < (less than), half the detection limit was used.
NA = Data not applicableINA = Site was inaccessibleDRY = Site had no flow
B1: 531SAC001 – Cosumnes River at Twin Cities Road continued…
Date Result Control Result Control
Result (million/m
l)
Control (million/m
l) MDD(%)10/24/2000 100 100 NA NA12/26/2001 100 100 100 1001/29/2002 55* 100 100 1004/23/2002 95 95 90 1005/28/2002 100 100 100 1006/18/2002 95 100 90 100
12/17/2002 100 100 100 100 2.11* 2.92 NA1/28/2003 100 100 100 100 1.38* 3.10 NA4/22/2003 70* 100 100 100 1.64* 2.00 75/28/2003 100 100 100 100 1.27* 2.04 4
11/22/2004 100 100 100 10012/28/2004 100 100 100 1001/26/2005 95 97.5 90 1002/23/2005 87.5 100 100 1003/29/2005 90 100 100 1004/26/2005 67.5* 100 85 1005/24/2005 92.5 100 100 1006/28/2005 100 100 100 1007/26/2005 100 100 100 100
Count 19 19 18 18 4 4 2
* Significantly reduced from the lab control.** Significantly greater than the lab control.^ Fish were from a "forced hatch," duplicate failed QA.1 Duplicate sample for the set was low - 77% recovery.
3 Samples qualified, but duplicate sample recovery for the set was high - 126% (53.8%/42.5%)NA = Data not applicableINA = Site was inaccessibleDRY = Site had no flow
2 Testing for the Fathead minnow was initiated when samples were approx. 48h old due to untimely shipping of fish by fish supplier.
96h Acute Fathead Minnow
(% Survival)
48h Acute Ceriodaphnia Dubia
(% Survival) Algae Cell Growth
11
B2: 531SAC002 – Mokelumne River at New Hope Road Station Code:544SAC002
Location: Latitude 38.23611, Longitude -121.41889
Date TimeTemp (ºC)
Field SC (umhos) pH
Dissolved Oxygen (mg/L)
Turbidity (ntu)
10/24/2000 7:50 AM 12.4 49 6.911/28/2000 8:32 AM 11.4 45 7.412/27/2000 8:15 AM 7.4 44 7.31/23/2001 8:10 AM 9.2 44 10.12/20/2001 8:29 AM 11.0 44 7.43/27/2001 8:24 AM 14.1 46 7.24/24/2001 9:10 AM 16.8 48 7.15/29/2001 8:35 AM 18.3 47 6.96/26/2001 8:12 AM 21.5 54 7.7 6.77/24/2001 7:37 AM 24.4 66 7.7 6.68/28/2001 7:36 AM 24.1 53 7.4 6.99/25/2001 8:27 AM 19.4 64 7.0 8.8
10/23/2001 8:05 AM 15.6 52 7.4 9.111/27/2001 7:56 AM 10.2 55 8.2 10.112/26/2001 8:45 AM 10.1 55 7.3 NA1/29/2002 7:24 AM 7.0 53 7.9 12.42/26/2002 7:21 AM 11.8 52 8.6 13.43/26/2002 8:09 AM 12.8 52 8.6 9.54/23/2002 8:13 AM 16.3 52 7.6 8.75/28/2002 7:24 AM 18.4 71 7.9 10.46/18/2002 7:45 AM 19.0 50 7.6 8.17/31/2002 10:57 AM 23.2 63 7.7 7.4 2.68/27/2002 8:30 AM 21.4 62 NA NA9/24/2002 7:50 AM 22.0 62 6.9 6.6
10/29/2002 8:13 AM 13.0 53 7.8 9.6 3.311/19/2002 7:16 AM 12.3 53 8.4 10.012/17/2002 11:10 AM 11.4 56 8.3 10.4 16.01/28/2003 7:50 AM 11.5 48 8.1 11.0 13.03/25/2003 7:43 AM 13.9 47 7.8 9.5 8.14/22/2003 7:39 AM 14.1 46 7.6 8.8 8.15/27/2003 8:20 AM 18.1 44 7.4 8.7 30.06/24/2003 12:43 PM 16.6 44 7.5 13.1 8.07/29/2003 11:58 AM 19.1 45 7.9 9.2 5.88/26/2003 8:31 AM 21.7 48 7.7 7.8 4.49/23/2003 8:29 AM 21.9 54 7.4 7.6 12.3
10/28/2003 8:43 AM 16.1 49 7.4 9.1 4.711/18/2003 7:58 AM 13.8 47 7.5 10.1 14.01/28/2004 7:41 AM 9.6 45 8.2 13.1 42.02/24/2004 8:40 AM 11.5 47 7.7 10.3 13.2
12
B2: 531SAC002 – Mokelumne River at New Hope Road continued…
Date TimeTemp (ºC)
Field SC (umhos) pH
Dissolved Oxygen (mg/L)
Turbidity (ntu)
3/24/2004 7:29 AM 14.2 47 7.5 9.8 11.44/28/2004 7:25 AM 16.9 48 7.6 9.5 8.25/26/2004 8:15 AM 16.2 46 7.4 9.5 7.06/23/2004 7:29 AM 19.2 47 7.6 8.9 NA7/28/2004 7:50 AM 24.1 84 8.7 8.6 NA8/25/2004 7:38 AM 22.1 64 8.3 6.8 NA9/29/2004 7:57 AM 19.1 104 8.0 6.9 NA
10/27/2004 7:36 AM 14.0 50 8.3 11.111/22/2004 8:41 AM 9.7 49 8.8 10.912/28/2004 7:49 AM 9.4 50 8.3 11.41/26/2005 8:15 AM 9.4 49 7.9 10.72/23/2005 7:25 AM 10.1 46 7.9 11.03/29/2005 8:45 AM 11.1 48 7.0 10.44/26/2005 8:22 AM 12.4 49 8.2 11.45/24/2005 7:51 AM 13.7 48 7.8 10.66/28/2005 7:43 AM 15.3 46 7.1 10.37/26/2005 7:39 AM 16.3 43 8.0 11.08/23/2005 7:42 AM 18.1 51 7.8 8.19/27/2005 8:14 AM 17.1 41 8.2 12.9
Count 58 58 57 48 18Min 7.0 41.0 6.9 6.6 2.6Max 24.4 104 10.1 13.4 42.0Mean 15.4 52.1 7.8 9.6 11.8Geo Mean 14.7 51.3 7.8 9.5 9.2Median 14.8 49.0 7.7 9.6 8.2Quartile 1 11.5 46.3 7.4 8.7 6.1Quartile 3 18.9 53.0 8.1 10.8 13.2NOTE: For values reported as < (less than), half the detection limit was used.
NA = Data not applicableINA = Site was inaccessibleDRY = Site had no flow
13
B2: 531SAC002 – Mokelumne River at New Hope Road continued…
DateTSS
(mg/L)TOC
(mg/L)Total Coli
MPNE. coli MPN
10/24/2000 <5 <111/28/2000 <5 2.812/27/2000 <5 1.31/23/2001 5 4.22/20/2001 6 <13/27/2001 <5 NA4/24/2001 <5 1.65/29/2001 <6 1.56/26/2001 8 3.47/24/2001 3.68/28/2001 7 3.19/25/2001 NA 5.2
10/23/2001 3.82/26/2002 NA3/26/2002 1.64/23/2002 NA5/28/2002 5.56/18/2002 1.07/31/2002 >2419.6 538/27/2002 2.29/24/2002 2.9
10/29/2002 1.211/19/2002 1.512/17/2002 2.83/25/2003 1.54/22/2003 2.0 2420 465/27/2003 NA6/24/2003 NA7/29/2003 >2419.6 1578/26/2003 >2419.6 869/23/2003 >2419.6 110
10/28/2003 1203 14011/18/2003 2420 991/28/2004 >2419.6 1222/24/2004 517 373/24/2004 980 364/28/2004 770 555/26/2004 1986 1026/23/2004 >2419.6 >2419.67/28/2004 >2419.6 2728/25/2004 2420 519/29/2004 1553 34
14
15
DateTSS
(mg/L)TOC
(mg/L)Total Coli
MPNE. coli MPN
10/27/2004 1.5 >2419.6 11111/22/2004 NA 461 2812/28/2004 1.7 866 911/26/2005 1.8 231 532/23/2005 1.6 248 643/29/2005 1.7 >2419.6 464/26/2005 NA 1414 695/24/2005 NA 1553 586/28/2005 1.6 >2419.6 467/26/2005 NA >2419.6 1288/23/2005 1.7 2420 379/27/2005 1.6 1986 75
Count 10 30 28 28Min 3 0.5 231 28Max 8 5.5 2420 2420MeaGeo
B2: 531SAC002 – Mokelumne River at New Hope Road continued…
n 4 2.2 NA NA Mean 4 2 1498 79ian 3 1.7 2420 67rtile 1 3 1.5 114
MedQua 7 46
rtile Qua 3 6 2.9 2420 110E: For values reported as < (less than), half the detection limit was used For values reported as > (greater than), 2420 was used
Data not applicable = Site was inaccessible = Site had no flow
NOT
NA =INADRY
B2: 531SAC002 – Mokelumne River at New Hope Road continued…
DateNitrate (mg/L)
Nitrate-N (mg/L)
TKN (mg/L)
Ammonia-N (mg/L)
Phosphorus (mg/L)
Ortho-phosphate-
P (mg/L)
Potassium (mg/L)
BOD 5-Day (mg/L)
BOD 10-Day (mg/L)
10/24/2000 <2 <2 <0.1 <1 <1 0.4 0.411/28/2000 <2 <2 <0.1 <1 <1 0.3 0.412/27/2000 <2 <2 <0.1 <1 <1 0.4 0.41/23/2001 <2 <2 <0.1 <1 <1 0.3 0.52/20/2001 <1.0 <2 <0.1 0.05 <1 0.5 0.93/27/2001 <2 <2 <0.1 <1 <1 0.4 0.44/24/2001 <2 <2 NA <1 <1 0.4 0.55/29/2001 <2 <2 NA <1 <1 0.5 0.56/26/2001 <2 <2 0.1 <1 1.0 0.4 0.58/28/2001 <2 <2 <0.1 <1 <19/25/2001 <2 <2 <0.1 <1 1.5
10/23/2001 <2 <2 <0.1 <1 <1 0.3 0.411/27/2001 NA NA NA <0.03 1.2 0.5 0.712/26/2001 0.4 0.81/29/2002 0.6 1.02/26/2002 0.5 0.53/26/2002 0.3 0.64/23/2002 0.4 0.65/28/2002 0.4 0.56/18/2002 0.5 0.68/27/2002 0.1 0.39/24/2002 0.6 1.1
10/29/2002 0.3 0.511/19/2002 0.5 0.612/17/2002 1.2 1.91/28/2003 0.2 0.2
16
B2: 531SAC002 – Mokelumne River at New Hope Road continued…
DateNitrate (mg/L)
Nitrate-N (mg/L)
TKN (mg/L)
Ammonia-N (mg/L)
Phosphorus (mg/L)
Ortho-phosphate-
P (mg/L)
Potassium (mg/L)
BOD 5-Day (mg/L)
BOD 10-Day (mg/L)
Count 12 NA 12 NA 10 13 13 24 24Min 0.5 NA 1.0 NA 0.1 0.02 0.5 0.1 0.2Max 1.0 NA 1.0 NA 0.1 0.5 1.5 1.2 1.9Mean 1.0 NA 1.0 NA 0.1 0.4 0.7 0.4 0.6Geo Mean 0.9 NA 1.0 NA 0.1 0.3 0.6 0.4 0.6Median 1.0 NA 1.0 NA 0.1 0.5 0.5 0.4 0.5Quartile 1 1.0 NA 1.0 NA 0.1 0.5 0.5 0.3 0.4Quartile 3 1.0 NA 1.0 NA 0.1 0.5 0.5 0.5 0.6NOTE: For values reported as < (less than), half the detection limit was used.
NA = Data not applicableINA = Site was inaccessibleDRY = Site had no flow
17
B2: 531SAC002 – Mokelumne River at New Hope Road continued…
DateHardness
(mg/L)
Total Arsenic (ug/L)
Total Cadmium
(ug/L)
Total Chromium
(ug/L)
Total Copper (ug/L)
Total Lead (ug/L)
Total Nickel (ug/L)
Total Zinc (ug/L)
Total Mercury (ug/L)
10/24/2000 18 <1 1.8 <5 <5 3.411/28/2000 16 2.5 1.7 9.7 <5 4.712/27/2000 16 <1 2.2 <5 <5 4.51/23/2001 16 <1 1.9 <5 <5 3.52/20/2001 16 <1 2.1 <5 <5 5.33/27/2001 16 <1 1.8 <5 <5 3.34/24/2001 17 <1 1.6 <5 <5 2.85/29/2001 17 <1 1.8 <5 <5 6.66/26/2001 <2 <1 <1 1.8 <5 <5 3.9 <0.27/24/2001 NA NA <1 1.8 <5 <5 4.1 NA8/28/2001 17 <2 <1 <1 1.9 <5 <5 2.79/25/2001 21 <4 <0.1 <1 2.7 <5 <5 2.7 <0.2
10/23/2001 18 <4 <0.1 <1 1.6 <5 <5 4.5 NA11/27/2001 19 <4 <0.1 <1 1.8 <5 <5 5.4 <0.212/26/2001 <4 <0.1 <1 1.9 <5 <5 5.6 <0.21/29/2002 <4 <0.1 <1 <1 <5 <5 <2 <0.23/26/2002 <4.0 <0.1 <1.0 2.5 <5.0 <5.0 6.4 <0.24/23/2002 <4.0 <0.1 2.4 1.6 <5.0 <5.0 3.0 <0.25/28/2002 <4.0 <0.1 <1.0 1.8 <5.0 <5.0 2.7 <0.26/18/2002 <4.0 <0.1 <1.0 1.2 <5.0 <5.0 2.6 <0.29/24/2002 <4.0 <0.1 <1.0 2.2 <5.0 <5.0 4.3 <0.2
10/29/2002 21 <4.0 <0.1 <1.0 2.8 <5.0 <5.0 3.4 <0.211/19/2002 20 <4.0 <0.1 <1.0 1.1 <5.0 <5.0 <2.0 <0.23/25/2003 16 <4.0 <0.1 <1.0 1.7 <5.0 <5.0 3.3 <0.24/22/2003 15 <4.0 <0.1 <1.0 1.8 <5.0 <5.0 3.1 <0.25/27/2003 15 <4.0 <0.1 <1.0 2.9 <5.0 <5.0 2.8 <0.26/24/2003 15 <4.0 <0.1 <1.0 1.9 <5.0 <5.0 4.6 0.2
18
B2: 531SAC002 – Mokelumne River at New Hope Road continued…
DateHardness
(mg/L)
Total Arsenic (ug/L)
Total Cadmium
(ug/L)
Total Chromium
(ug/L)
Total Copper (ug/L)
Total Lead (ug/L)
Total Nickel (ug/L)
Total Zinc (ug/L)
Total Mercury (ug/L)
Count 18 18 18 27 27 27 27 27 16Min 15.0 1.0 0.1 0.5 0.5 2.5 2.5 1.0 0.1Max 21.0 2.0 0.5 2.5 2.9 9.7 2.5 6.6 0.2Mean 17.2 1.9 0.1 0.6 1.9 2.8 2.5 3.7 0.1Geo Mean 17.1 1.9 0.1 0.6 1.8 2.6 2.5 3.5 0.1Median 16.5 2.0 0.1 0.5 1.8 2.5 2.5 3.4 0.1Quartile 1 16.0 2.0 0.1 0.5 1.7 2.5 2.5 2.8 0.1Quartile 3 18.0 2.0 0.1 0.5 2.0 2.5 2.5 4.6 0.1NOTE: For values reported as < (less than), half the detection limit was used.
NA = Data not applicableINA = Site was inaccessibleDRY = Site had no flow
19
B2: 531SAC002 – Mokelumne River at New Hope Road continued…
DateHardness
(mg/L)
Dissolved Arsenic (ug/L)
Dissolved Cadmium
(ug/L)
Dissolved Chromium
(ug/L)
Dissolved Copper (ug/L)
Dissolved Lead (ug/L)
Dissolved Nickel (ug/L)
Dissolved Zinc
(ug/L)
Dissolved Mercury (ug/L)
10/24/2000 1811/28/2000 16 <1 <1 <5 <5 2.412/27/2000 16 <1 <1 <5 <5 5.81/23/2001 16 <1 <1 <5 <5 2.22/20/2001 16 <1 <1 <5 <5 2.43/27/2001 16 <1 <1 <5 <5 2.34/24/2001 17 <1 1.0 <5 <5 2.85/29/2001 17 <1 <1 <5 <5 3.76/26/2001 <2 <1 <1 <1 <5 <5 3.5 <0.27/24/2001 NA NA NA NA NA NA NA NA8/28/2001 17 <2 <1 <1 <1 <5 <5 <29/25/2001 21 <4 <0.1 <1 1.6 <5 <5 <2 <0.2
10/23/2001 18 <4 <0.1 <1 <1 <5 <5 <2 NA11/27/2001 19 <4 <0.1 <1 1.5 <5 <5 8.1 <0.212/26/2001 <4 <0.1 <1 1.7 <5 <5 6.3 <0.21/29/2002 <4 <0.1 <1 <1 <5 <5 <2 <0.23/26/2002 <4.0 <0.1 <1.0 1.5 <5.0 <5.0 5.4 <0.24/23/2002 <4.0 <0.1 <1.0 1.2 <5.0 <5.0 <2.0 <0.25/28/2002 <4.0 <0.1 <1.0 2.2 <5.0 <5.0 2.5 <0.26/18/2002 <4.0 <0.1 <1.0 <1.0 <5.0 <5.0 <2.0 <0.29/24/2002 <4.0 <0.1 <1.0 4.8 <5.0 <5.0 <2.0 <0.2
10/29/2002 21 <4.0 <0.1 <1.0 <1.0 <5.0 <5.0 <2.0 <0.211/19/2002 20 <4.0 <0.1 <1.0 <1.0 <5.0 <5.0 2.3 <0.2
Count 14 14 14 21 21 21 21 21 12Min 16.0 1.0 0.1 0.5 0.5 2.5 2.5 1.0 0.1Max 21.0 2.0 0.5 0.5 4.8 2.5 2.5 8.1 0.1Mean 17.7 1.9 0.1 0.5 1.0 2.5 2.5 2.7 0.1Geo Mean 17.6 1.8 0.1 0.5 0.8 2.5 2.5 2.2 0.1Median 17.0 2.0 0.1 0.5 0.5 2.5 2.5 2.3 0.1Quartile 1 16.0 2.0 0.1 0.5 0.5 2.5 2.5 1.0 0.1Quartile 3 18.8 2.0 0.1 0.5 1.5 2.5 2.5 3.5 0.1NOTE: For values reported as < (less than), half the detection limit was used.
NA = Data not applicableINA = Site was inaccessibleDRY = Site had no flow
20
21
B2: 531SAC002 – Mokelumne River at New Hope Road continued…
DateChloride (mg/L)
Sulfate (mg/L)
Calcium (mg/L)
Magnesium (mg/L)
TDS (mg/L)
Carbonate (mg/L)
Bicarbonate (mg/L)
Total Alkalinity
(mg/L)Sodium (mg/L)
10/24/2000 3 3 5 2 33 <1 20 20 311/28/2000 5 2 4 1 45 <1 30 30 212/27/2000 3 2 4 1 25 <1 20 20 21/23/2001 3 2 4 1 30 <1 30 25 22/20/2001 3 3 4 1 45 <1 21 15 33/27/2001 3 3 4 1 NA <1 22 16 24/24/2001 3 3 4 2 24 <1 27 22 35/29/2001 3 2 4 2 33 <1 18 18 38/28/2001 3 3 4 2 47 <1 25 21 39/25/2001 4 3 5 2 NA <1 29 24 4
10/23/2001 3 3 5 2 NA <1 22 18 311/27/2001 3 3 5 2 45 <1 23 19 33/25/2003 3 3 4 14/22/2003 3 2 4 15/27/2003 3 2 4 16/24/2003 3 2 4 1
Count 16 16 16 16 9 12 12 12 12Min 3 2 4 1 24 0.5 18 15 2Max 5 3 5 2 47 0.5 30 30 4Mean 3 3 4 1 36 0.5 24 21 3Geo Mean 3 3 4 1 35 0.5 24 20 3Median 3 3 4 1 33 0.5 23 20 3Quartile 1 3 2 4 1 30 0.5 21 18 2Quartile 3 3 3 4 2 45 0.5 28 23 3NOTE: For values reported as < (less than), half the detection limit was used.
NA = Data not applicableINA = Site was inaccessibleDRY = Site had no flow
B2: 531SAC002 – Mokelumne River at New Hope Road continued…
Date Result Control Result Control
Result (million/m
l)
Control (million/m
l) MDD(%)10/23/2001 100 100 100 100
12/28/2004 100 100 100 100
Count 2 2 2 2 N/A N/A N/A
* Significantly reduced from the lab control.** Significantly greater than the lab control.^ Fish were from a "forced hatch," duplicate failed QA.1 Duplicate sample for the set was low - 77% recovery.
3 Samples qualified, but duplicate sample recovery for the set was high - 126% (53.8%/42.5%)NA = Data not applicableINA = Site was inaccessibleDRY = Site had no flow
2 Testing for the Fathead minnow was initiated when samples were approx. 48h old due to untimely shipping of fish by fish supplier.
96h Acute Fathead Minnow
(% Survival)
48h Acute Ceriodaphnia Dubia
(% Survival) Algae Cell Growth
22
B2: 531SAC002 – Mokelumne River at New Hope Road continued…
Date
Result (%
Survival)
Control (%
Survival)
Avg Dry Weight Result (mg)
Avg Dry Weight Control
(mg)Growth MDD(%)
Result (%
Survival)
Control (%
Survival)
Avg # Young /
Adult Result
Avg # Young /
Adult Control
Repro MDD(%)
11/23/2004 89.7 97.5 0.21* 0.27 201/26/2005 85.0 97.5 0.42 0.46 232/23/2005 65.0* 100.0 0.39* 0.57 20
03/29/2005 2 97.5 100.0 0.51 0.42 144/26/2005 84.6 92.5 0.36 0.39 275/24/2005 66.7* 87.5 0.39 0.49 366/28/2005 N/A N/A N/A N/A N/A7/26/2005 N/A N/A N/A N/A N/A8/23/2005 90.0 100.0 0.54* 0.77 7.89/27/2005 97.5 97.5 0.5 0.45 15
Count 8 8 8 8 8 N/A N/A N/A N/A N/A
* Significantly reduced from the lab control.** Significantly greater than the lab control.^ Fish were from a "forced hatch," duplicate failed QA.1 Duplicate sample for the set was low - 77% recovery.
3 Samples qualified, but duplicate sample recovery for the set was high - 126% (53.8%/42.5%)NA = Data not applicableINA = Site was inaccessibleDRY = Site had no flow
Chronic Ceriodaphnia Dubia - 6 dayChronic Fathead Minnow - 7day
2 Testing for the Fathead minnow was initiated when samples were approx. 48h old due to untimely shipping of fish by fish supplier.
23
B3: 531SJC507 – Pixley Slough at Davis Road Station Code:531SJC507
Location: Latitude 38.05611, Longitude -121.33306
Date TimeTemp (ºC)
Field SC (umhos) pH
Dissolved Oxygen (mg/L)
Turbidity (ntu)
10/24/2000 8:20 AM 12.6 61 7.011/28/2000 DRY DRY DRY DRY12/27/2000 DRY DRY DRY DRY1/23/2001 DRY DRY DRY DRY2/20/2001 9:01 AM 10.6 53 7.43/27/2001 8:55 AM 15.1 73 6.94/24/2001 10:00 AM 19.0 62 6.95/29/2001 9:25 AM 18.7 73 6.76/5/2001 7:24 AM 18.7 125 8.0 6.76/19/2001 7:32 AM 21.7 54 7.9 7.46/26/2001 9:16 AM 19.5 62 7.9 8.97/24/2001 8:06 AM 22.2 98 7.4 6.38/28/2001 8:11 AM 23.5 119 7.3 5.09/25/2001 9:20 AM 18.7 90 7.6 7.3
10/23/2001 8:35 AM 16.4 116 7.4 5.411/27/2001 8:39 AM 7.9 239 7.4 8.612/26/2001 9:33 AM 9.5 103 7.3 NA1/29/2002 8:09 AM 5.0 206 7.6 12.52/26/2002 8:15 AM DRY DRY DRY DRY3/26/2002 8:43 AM 14.1 119 7.8 6.84/23/2002 8:53 AM 17.4 69 7.2 7.05/28/2002 8:15 AM 18.2 82 7.6 10.16/18/2002 8:16 AM 20.1 71 7.2 6.67/31/2002 9:41 AM 21.1 80 7.2 5.6 31.38/27/2002 8:55 AM 20.4 100 NA NA9/24/2002 8:23 AM 20.2 115 6.9 5.0
10/15/2002 11:20 AM 15.6 104 7.4 7.3 47.310/29/2002 9:20 AM 13.1 81 7.3 8.3 39.011/19/2002 DRY DRY DRY DRY DRY12/17/2002 7:41 AM 11.1 72 7.1 8.8 1241/15/2003 1:03 PM 12.9 275 7.6 8.2 29.01/28/2003 8:15 AM DRY DRY DRY DRY DRY3/25/2003 8:06 AM 14.7 50 7.6 8.9 16.14/22/2003 8:07 AM 14.4 58 7.3 8.6 18.65/27/2003 8:51 AM 20.8 97 6.9 0.7 30.06/24/2003 11:39 AM 19.5 78 7.3 8.0 42.97/29/2003 11:30 AM 23.4 65 7.4 7.8 45.68/26/2003 8:58 AM 23.3 70 7.0 4.7 45.59/23/2003 8:59 AM 20.2 54 7.0 7.3 28.2
24
B3: 531SJC507 – Pixley Slough at Davis Road continued…
Date TimeTemp (ºC)
Field SC (umhos) pH
Dissolved Oxygen (mg/L)
Turbidity (ntu)
10/28/2003 9:14 AM 16.2 51 7.3 9.1 16.511/18/2003 8:40 AM 11.4 94 7.3 9.0 91.01/28/2004 8:14 AM 9.7 193 7.4 13.5 57.72/24/2004 9:04 AM 13.0 98 7.5 9.9 70.13/24/2004 7:55 AM DRY DRY DRY DRY DRY4/28/2004 7:53 AM 19.9 66 7.3 5.0 42.55/26/2004 8:58 AM 19.0 70 7.3 7.6 22.16/23/2004 7:58 AM 19.7 88 9.4 7.3 NA7/28/2004 8:20 AM 21.8 68 8.8 6.0 NA8/25/2004 8:10 AM 21.1 60 7.6 4.7 NA9/29/2004 8:28 AM 18.1 55 7.6 7.7 NA
10/27/2004 8:07 AM 13.4 53 7.9 9.811/22/2004 9:14 AM 8.2 67 8.2 10.312/28/2004 8:21 AM 8.8 70 8.0 11.51/26/2005 8:45 AM DRY DRY DRY DRY2/23/2005 8:04 AM 12.6 96 7.4 5.63/29/2005 9:17 AM 14.0 92 6.8 5.04/26/2005 8:59 AM 13.0 51 7.7 10.75/24/2005 8:23 AM 15.0 50 7.6 9.96/28/2005 8:21 AM 16.5 48 7.1 9.47/26/2005 8:15 AM 20.5 50 7.7 8.38/23/2005 8:13 AM 21.2 74 7.6 6.09/27/2005 8:46 AM 18.2 62 7.8 10.4
Count 54 54 53 47 18Min 5.0 48 6.7 0.7 16.1Max 23.5 275 9.4 13.5 124Mean 16.5 88 7.5 7.8 44.3Geo Mean 15.8 80 7.5 7.3 38.0Median 17.8 73 7.4 7.7 40.8Quartile 1 13.0 61 7.2 6.2 28.4Quartile 3 20.2 98 7.6 9.1 46.9NOTE: For values reported as < (less than), half the detection limit was used.
NA = Data not applicableINA = Site was inaccessibleDRY = Site had no flow
25
B3: 531SJC507 – Pixley Slough at Davis Road continued…
DateTSS
(mg/L)TOC
(mg/L)Total Coli
MPNE. coli MPN
10/24/2000 15 1.32/20/2001 57 2.63/27/2001 <5 NA4/24/2001 9 3.35/29/2001 26 1.26/26/2001 25 3.07/24/2001 3.88/28/2001 26 8.09/25/2001 NA
10/23/2001 103/26/2002 3.84/23/2002 NA5/28/2002 106/18/2002 1.07/31/2002 >2419.6 3878/27/2002 2.59/24/2002 3.8
10/15/2002 >2419.6 10910/29/2002 1.71/15/2003 1733 4613/25/2003 1.64/22/2003 3.6 >2419.6 6135/27/2003 NA6/24/2003 NA7/29/2003 >2419.6 2368/26/2003 >2419.6 4889/23/2003 >2419.6 291
10/28/2003 >2419.6 9811/18/2003 >2419.6 1111/28/2004 >2419.6 >2419.62/24/2004 >2419.6 3453/24/2004 DRY DRY4/28/2004 >2419.6 1615/26/2004 >2419.6 14146/23/2004 >2419.6 3877/28/2004 >2419.6 1798/25/2004 >2419.6 519/29/2004 >2419.6 69
10/27/2004 3.9 >2419.6 >2419.611/22/2004 2.2 >2419.6 21012/28/2004 2.0 >2419.6 2761/26/2005 DRY DRY DRY
26
27
DateTSS
(mg/L)TOC
(mg/L)Total Coli
MPNE. coli MPN
2/23/2005 5.4 1203 863/29/2005 7.6 >2419.6 14144/26/2005 NA 1986 1945/24/2005 NA >2419.6 2766/28/2005 2.4 >2419.6 1947/26/2005 NA >2419.6 2918/23/2005 2.2 >2419.6 1319/27/2005 2.3 >2419.6 75
Count 7 24 28 28Min 3 1.0 120
B3: 531SJC507 – Pixley Slough at Davis Road continued…
3 51Max 57 10 2420 2420Mean 23 3.7 NA NAGeo Mean 16 3.0 2316 268Median 25 2.8 2420 256Quartile 1 12 2.2 2420 126Quartile 3 26 3.8 2420 406
E: For values reported as < (less than), half the detection limit was used For values reported as > (greater than), 2420 was used
Data not applicable = Site was inaccessible = Site had no flow
NOT
NA =INADRY
B3: 531SJC507 – Pixley Slough at Davis Road continued…
DateNitrate (mg/L)
Nitrate-N (mg/L)
TKN (mg/L)
Ammonia-N (mg/L)
Phosphorus (mg/L)
Ortho-phosphate-
P (mg/L)Potassium
(mg/L)BOD 5-Day
(mg/L)BOD 10-Day
(mg/L)10/24/2000 <2 <2 <0.1 <1 1.2 0.7 1.02/20/2001 1.8 <2 0.3 0.1 2.6 3.7 7.03/27/2001 <2 <2 0.1 <1 1.6 1.5 2.74/24/2001 <2 <2 0.1 <1 1.6 1.3 2.35/29/2001 2.1 <2 0.1 <1 1.1 0.9 1.26/26/2001 <2 <2 0.1 <1 1.1 0.7 1.08/28/2001 <2 <2 0.3 <1 2.59/25/2001 <2 <2 0.2 <1 2.7
10/23/2001 <2 <2 <0.1 <1 2.9 1.0 1.811/27/2001 NA NA NA 0.1 5.4 1.9 4.012/26/2001 NA NA 0.2 NA 2.6 1.7 4.11/29/2002 NA 1.4 0.2 NA 4.6 4.7 8.53/26/2002 NA 1.0 0.1 0.1 3.1 3.3 6.04/23/2002 NA NA NA NA 1.5 1.5 2.45/28/2002 NA NA NA 0.1 1.8 1.2 2.06/18/2002 NA 0.5 NA NA 1.3 1.0 1.78/27/2002 NA 0.9 0.4 0.4 NA 4.8 7.49/24/2002 NA NA 0.1 0.1 2.3 1.1 2.2
10/29/2002 NA 0.5 0.1 <0.03 1.4 1.0 1.412/17/2002 NA 1.0 0.2 <0.03 2.3 2.8 4.6
Count 9 NA 15 NA 16 16 19 18 18Min 1.0 NA 0.5 NA 0.1 0.02 1.1 0.7 1.0Max 2.1 NA 1.4 NA 0.4 0.5 5.4 4.8 8.5Mean 1.2 NA 1.0 NA 0.2 0.3 2.3 1.9 3.4Geo Mean 1.2 NA 0.9 NA 0.1 0.2 2.1 1.6 2.7Median 1.0 NA 1.0 NA 0.1 0.5 2.3 1.4 2.4Quartile 1 1.0 NA 1.0 NA 0.1 0.1 1.5 1.0 1.7Quartile 3 1.0 NA 1.0 NA 0.2 0.5 2.7 2.6 4.5NOTE: For values reported as < (less than), half the detection limit was used.
NA = Data not applicableINA = Site was inaccessibleDRY = Site had no flow
28
B3: 531SJC507 – Pixley Slough at Davis Road continued…
DateHardness
(mg/L)
Total Arsenic (ug/L)
Total Cadmium
(ug/L)
Total Chromium
(ug/L)
Total Copper (ug/L)
Total Lead (ug/L)
Total Nickel (ug/L)
Total Zinc (ug/L)
Total Mercury (ug/L)
10/24/2000 22 <1 5.3 <5 <5 7.02/20/2001 22 3.5 7.9 5.8 <5 593/27/2001 26 <1 3.0 <5 <5 124/24/2001 22 <1 8.5 <5 <5 155/29/2001 29 <1 4.9 <5 <5 126/26/2001 <2 <1 <1 5.2 <5 <5 10 <0.27/24/2001 NA NA 1.3 4.5 <5 <5 11 NA8/28/2001 36 <2 <1 1.2 3.7 <5 <5 9.49/25/2001 34 <4 <0.1 1.4 5.1 <5 <5 10 <0.2
10/23/2001 41 <4 <0.1 <1 2.3 <5 <5 4.3 NA11/27/2001 63 <4 <0.1 <1 5.0 <5 <5 18 <0.212/26/2001 <4 <0.1 1.5 6.4 <5 <5 39 <0.21/29/2002 61 <4 <0.1 <1 4.9 <5 <5 36 <0.23/26/2002 45 <4.0 <0.1 1.8 7.3 <5.0 <5.0 27 <0.24/23/2002 27 <4.0 <0.1 <1.0 3.3 <5.0 <5.0 5.3 <0.25/28/2002 33 <4.0 <0.1 1.2 6.8 <5.0 <5.0 18 <0.26/18/2002 30 <4.0 <0.1 <1.0 3.9 <5.0 <5.0 12 <0.29/24/2002 45 <4.0 <0.1 1.1 14 <5.0 <5.0 7.2 <0.2
10/29/2002 33 <4.0 <0.1 <1.0 2.3 <5.0 <5.0 4.2 <0.23/25/2003 18 <4.0 <0.1 <1.0 2.8 <5.0 <5.0 10 <0.24/22/2003 21 <4.0 <0.1 <1.0 3.5 <5.0 <5.0 12 <0.25/27/2003 36 <4.0 <0.1 1.0 6.9 <5.0 <5.0 14 <0.26/24/2003 30 <4.0 <0.1 1.3 4.3 <5.0 <5.0 9.5 <0.2
Count 20 17 17 23 23 23 23 23 15Min 18.0 1.0 0.1 0.5 2.3 2.5 2.5 4.2 0.1Max 63.0 2.0 0.5 3.5 14.0 5.8 2.5 59.0 0.1Mean 33.7 1.9 0.1 0.9 5.3 2.6 2.5 15.7 0.1Geo Mean 31.8 1.8 0.1 0.8 4.8 2.6 2.5 12.4 0.1Median 31.5 2.0 0.1 0.5 4.9 2.5 2.5 12.0 0.1Quartile 1 25.0 2.0 0.1 0.5 3.6 2.5 2.5 9.5 0.1Quartile 3 37.3 2.0 0.1 1.3 6.6 2.5 2.5 16.5 0.1NOTE: For values reported as < (less than), half the detection limit was used.
NA = Data not applicableINA = Site was inaccessibleDRY = Site had no flow
29
B3: 531SJC507 – Pixley Slough at Davis Road continued…
DateHardness
(mg/L)
Dissolved Arsenic (ug/L)
Dissolved Cadmium
(ug/L)
Dissolved Chromium
(ug/L)
Dissolved Copper (ug/L)
Dissolved Lead (ug/L)
Dissolved Nickel (ug/L)
Dissolved Zinc
(ug/L)
Dissolved Mercury (ug/L)
10/24/2000 222/20/2001 22 <1 2.7 <5 <5 203/27/2001 26 <1 2.1 <5 <5 9.64/24/2001 22 <1 6.1 <5 <5 125/29/2001 29 <1 2.1 <5 <5 4.66/26/2001 <2 <1 <1 1.3 <5 <5 2.0 <0.27/24/2001 NA NA NA NA NA NA NA NA8/28/2001 36 <2 <1 <1 1.9 <5 <5 3.59/25/2001 34 <4 <0.1 <1 4.2 <5 <5 18 <0.2
10/23/2001 41 <4 <0.1 <1 2.1 <5 <5 2.5 NA11/27/2001 63 <4 <0.1 <1 4.4 <5 <5 19 <0.212/26/2001 <4 <0.1 <1 4.1 <5 <5 26 <0.21/29/2002 61 <4 <0.1 <1 2.5 <5 <5 15 <0.23/26/2002 45 <4.0 <0.1 <1.0 4.1 <5.0 <5.0 10 <0.24/23/2002 27 <4.0 <0.1 <1.0 3.6 <5.0 <5.0 3.5 <0.25/28/2002 33 <4.0 <0.1 <1.0 3.4 <5.0 <5.0 3.5 <0.26/18/2002 30 <4.0 <0.1 <1.0 1.4 <5.0 <5.0 5 <0.29/24/2002 45 <4.0 <0.1 <1.0 4.7 <5.0 <5.0 5.2 <0.2
10/29/2002 33 <4.0 <0.1 <1.0 2.3 <5.0 <5.0 2.7 <0.2
Count 16 13 13 17 17 17 17 17 11Min 22.0 1.0 0.1 0.5 1.3 2.5 2.5 2.0 0.1Max 63.0 2.0 0.5 0.5 6.1 2.5 2.5 26.0 0.1Mean 35.6 1.8 0.1 0.5 3.1 2.5 2.5 9.5 0.1Geo Mean 33.7 1.8 0.1 0.5 2.9 2.5 2.5 7.0 0.1Median 33.0 2.0 0.1 0.5 2.7 2.5 2.5 5.2 0.1Quartile 1 26.8 2.0 0.1 0.5 2.1 2.5 2.5 3.5 0.1Quartile 3 42.0 2.0 0.1 0.5 4.1 2.5 2.5 15.0 0.1NOTE: For values reported as < (less than), half the detection limit was used.
NA = Data not applicableINA = Site was inaccessibleDRY = Site had no flow
30
31
B3: 531SJC507 – Pixley Slough at Davis Road continued…
DateChloride (mg/L)
Sulfate (mg/L)
Calcium (mg/L)
Magnesium (mg/L)
TDS (mg/L)
Carbonate (mg/L)
Bicarbonate (mg/L)
Total Alkalinity
(mg/L)Sodium (mg/L)
10/24/2000 3 3 6 2 70 <1 20 20 32/20/2001 3 3 5 2 64 <1 23 21 33/27/2001 4 4 7 2 NA <1 33 27 44/24/2001 3 3 6 2 35 <1 30 25 35/29/2001 3 3 7 3 57 <1 26 26 48/28/2001 5 5 10 3 120 <1 55 45 69/25/2001 4 4 8 3 NA <1 41 34 5
10/23/2001 6 5 10 4 NA <1 51 42 611/27/2001 40 7 18 4 140 <1 46 38 161/29/2002 25 7 17 5 120 <1 55 45 153/26/2002 6 5 12 4 100 <1.0 50 40 74/23/2002 4 3 7 3 <10 <1.0 29 24 45/28/2002 4 4 8 3 NA <1.0 35 29 46/18/2002 19 22 7 3 NA <1.0 39 NA 49/24/2002 7 5 11 4 NA <1.0 46 38 5
10/29/2002 5 4 8 3 100 <1.0 37 30 53/25/2003 3 3 5 24/22/2003 4 3 5 25/27/2003 4 3 9 36/24/2003 4 4 8 3
Count 20 20 20 20 10 16 16 15 16Min 3 3 5 2 5 0.5 20 20 3Max 40 22 18 5 140 0.5 55 45 16Mean 8 5 9 3 81 0.5 39 32 6Geo Mean 5 4 8 3 62 0.5 37 31 5Median 4 4 8 3 85 0.5 38 30 5Quartile 1 4 3 7 2 59 0.5 30 26 4Quartile 3 6 5 10 3 120 0.5 47 39 6NOTE: For values reported as < (less than), half the detection limit was used.
NA = Data not applicableINA = Site was inaccessibleDRY = Site had no flow
B3: 531SJC507 – Pixley Slough at Davis Road continued…
Date Result Control Result Control
Result (million/m
l)
Control (million/
ml) MDD(%)11/22/2004 100 100 100 10012/28/2004 97.5 100 100 1002/23/2005 100 100 100 1003/29/2005 100 100 100 1004/26/2005 87.5* 100 100 1005/24/2005 87.5* 100 100 1006/28/2005 85* 100 100 1007/26/2005 100 100 100 1008/23/2005 97.5 100 100 1009/27/2005 100 100 100 100
Count 10 10 10 10 N/A N/A N/A
* Significantly reduced from the lab control.** Significantly greater than the lab control.^ Fish were from a "forced hatch," duplicate failed QA.1 Duplicate sample for the set was low - 77% recovery.
3 Samples qualified, but duplicate sample recovery for the set was high - 126% (53.8%/42.5%)NA = Data not applicableINA = Site was inaccessibleDRY = Site had no flow
2 Testing for the Fathead minnow was initiated when samples were approx. 48h old due to untimely shipping of fish by fish supplier.
96h Acute Fathead Minnow
(% Survival)
48h Acute Ceriodaphnia Dubia
(% Survival) Algae Cell Growth
32
B4: 544SJC508 – Bear Creek at Thorton Road (J8) Station Code:544SJC508
Location: Latitude 38.04306, Longitude -121.34861
Date TimeTemp (ºC)
Field SC (umhos) pH
Dissolved Oxygen (mg/L)
Turbidity (ntu)
10/24/2000 8:45 AM 11.7 132 7.011/28/2000 9:20 AM 9.2 210 7.012/27/2000 9:00 AM 5.6 261 7.31/23/2001 9:00 AM 7.6 308 8.82/20/2001 9:19 AM 10.8 93 7.13/27/2001 9:10 AM 16.1 117 6.94/24/2001 10:32 AM 19.9 94 6.85/29/2001 9:00 AM 19.4 85 6.36/5/2001 7:12 AM 19.8 111 7.8 6.46/19/2001 7:50 AM 24.2 57 7.7 7.16/26/2001 8:53 AM 20.3 481 7.7 8.77/24/2001 8:21 AM 22.3 84 7.3 4.98/28/2001 8:29 AM 23.2 76 7.1 4.89/25/2001 9:06 AM 19.0 106 7.4 6.1
10/23/2001 9:02 AM 16.4 148 7.7 8.111/27/2001 8:28 AM 8.5 77 7.7 7.512/26/2001 9:16 AM 9.3 211 7.0 NA1/29/2002 7:55 AM 6.6 198 7.7 11.82/26/2002 7:52 AM 13.2 232 7.8 10.53/26/2002 8:59 AM 14.4 192 7.7 7.94/23/2002 9:19 AM 18.0 71 7.3 8.35/28/2002 8:31 AM 19.5 73 7.5 9.06/18/2002 8:34 AM 20.7 124 7.3 6.77/31/2002 10:11 AM 21.7 94 7.1 6.3 39.18/27/2002 9:10 AM 20.8 116 NA NA1/15/2003 12:44 PM 13.2 239 7.6 9.2 21.6
Count 26 26 25 16 2Min 5.6 57 6.3 4.8 21.6Max 24.2 481 8.8 11.8 39.1Mean 15.8 153 7.4 7.7 30.4Geo Mean 14.7 132 7.4 7.5 29.1Median 17.2 117 7.3 7.7 30.4Quartile 1 11.0 87 7.1 6.4 26.0Quartile 3 20.2 207 7.7 8.8 34.7NOTE: For values reported as < (less than), half the detection limit was used.
NA = Data not applicableINA = Site was inaccessibleDRY = Site had no flow
33
34
DateTSS
(mg/L)TOC
(mg/L)Total Coli
MPNE. coli MPN
10/24/2000 11 3.611/28/2000 <8 9.712/27/2000 <5 6.51/23/2001 6 18.02/20/2001 25 5.83/27/2001 10 NA4/24/2001 19 4.75/29/2001 21 2.46/26/2001 30 237/24/2001 2.88/28/2001 18 4.29/25/2001 NA
10/23/2001 8.62/26/2002 NA3/26/2002 6.84/23/2002 NA5/26/17/38/21/1
Coun
B4: 544SJC508 – Bear Creek at Thorton Road (J8) continued …
8/2002 6.68/2002 4.81/2002 >2419.6 1667/2002 2.95/2003 411 46
t 10 15 2 2MinMaxMeaGeo
3 2.4 411 4630 23 2420 166
n 15 7.4 NA NA Mean 11 5.9 997 87ian 15 5.8 1416 106rtile 1 7 3.9 91
MedQua 3 76
rtile Qua 3 21 7.7 1918 136E: For values reported as < (less than), half the detection limit was used For values reported as > (greater than), 2420 was used
Data not applicable = Site was inaccessible = Site had no flow
NOT
NA =INADRY
B4: 544SJC508 – Bear Creek at Thorton Road (J8) continued …
DateNitrate (mg/L)
Nitrate-N (mg/L)
TKN (mg/L)
Ammonia-N (mg/L)
Phosphorus (mg/L)
Ortho-phosphate-
P (mg/L)
Potassium (mg/L)
BOD 5-Day (mg/L)
BOD 10-Day (mg/L)
10/24/2000 <2 <2 0.2 <1 7.9 0.9 1.811/28/2000 2.8 <2 0.1 <1 5.8 2.4 4.112/27/2000 <2 <2 <0.1 <1 11 1.0 1.61/23/2001 4.6 2.5 0.5 1.1 19 2.0 6.22/20/2001 2.6 <2 0.3 0.2 3.9 4.0 7.43/27/2001 <2 <2 0.2 <1 5.2 2.3 3.94/24/2001 5.4 <2 0.1 <1 2.8 1.8 3.75/29/2001 2.3 <2 0.1 <1 1.4 1.0 1.66/26/2001 2.3 <2 0.2 <1 2.2 8.4 14.58/28/2001 <2 <2 0.2 <1 1.69/25/2001 2.6 <2 <0.1 <1 2.4
10/23/2001 <2 <2 0.3 <1 3.9 2.0 3.611/27/2001 NA NA NA 0.1 3.5 2.3 4.312/26/2001 NA NA 1.0 NA 14 2.7 7.31/29/2002 NA 1.6 0.3 0.2 9.9 4.6 8.32/26/2002 NA NA 0.5 0.3 11 2.9 4.93/26/2002 NA 1.6 0.4 0.4 8.7 3.2 6.04/23/2002 NA NA NA NA 1.7 1.2 2.45/28/2002 NA NA NA 0.1 2.3 0.8 1.36/18/2002 NA 0.7 NA 0.1 18 1.2 2.38/27/2002 NA 0.5 0.1 0.1 NA 0.4 0.9
Count 12 NA 16 NA 17 19 20 19 19Min 1.0 NA 0.5 NA 0.1 0.1 1.4 0.4 0.9Max 5.4 NA 2.5 NA 1.0 1.1 19.0 8.4 14.5Mean 2.3 NA 1.1 NA 0.3 0.4 6.8 2.4 4.5Geo Mean 1.9 NA 1.1 NA 0.2 0.3 5.0 1.9 3.6Median 2.3 NA 1.0 NA 0.2 0.5 4.6 2.0 3.9Quartile 1 1.0 NA 1.0 NA 0.1 0.2 2.4 1.1 2.1Quartile 3 2.7 NA 1.0 NA 0.3 0.5 10.2 2.8 6.1NOTE: For values reported as < (less than), half the detection limit was used.
NA = Data not applicableINA = Site was inaccessibleDRY = Site had no flow
35
B4: 544SJC508 – Bear Creek at Thorton Road (J8) continued …
DateHardness
(mg/L)
Total Arsenic (ug/L)
Total Cadmium
(ug/L)
Total Chromium
(ug/L)
Total Copper (ug/L)
Total Lead (ug/L)
Total Nickel (ug/L)
Total Zinc (ug/L)
Total Mercury (ug/L)
10/24/2000 39 <1 6.2 <5 <5 6.411/28/2000 66 <1 4.8 <5 <5 1312/27/2000 82 <1 3.6 <5 <5 6.31/23/2001 96 <1 7.3 <5 <5 6.82/20/2001 31 1.8 6.2 <5 <5 353/27/2001 38 <1 4.3 <5 <5 104/24/2001 34 <1 8.6 <5 <5 135/29/2001 33 <1 4.2 <5 <5 7.26/26/2001 <2 <1 1.6 6.8 <5 <5 18 <0.27/24/2001 NA NA <1 3.3 <5 <5 9.7 NA8/28/2001 22 <2 <1 1.0 2.6 <5 <5 6.49/25/2001 39 <4 <0.1 <1 2.8 <5 <5 5.2 <0.2
10/23/2001 58 <4 <0.1 <1 4.2 <5 <5 11 NA11/27/2001 23 <4 <0.1 1.2 5.0 <5 <5 14 <0.212/26/2001 <4 <0.1 1.7 10 <5 <5 16 <0.21/29/2002 64 <4 <0.1 <1 5.1 <5 <5 11 <0.23/26/2002 63 <4.0 <0.1 <1.0 6.6 <5.0 <5.0 11 <0.24/23/2002 26 <4.0 <0.1 <1.0 2.7 <5.0 <5.0 4.5 <0.25/28/2002 25 <4.0 <0.1 1.0 4.2 <5.0 <5.0 6.0 <0.26/18/2002 45 <4.0 <0.1 <1.0 3.0 <5.0 <5.0 5.0 <0.2
Count 17 11 11 20 20 20 20 20 9Min 22.0 1.0 0.1 0.5 2.6 2.5 2.5 4.5 0.1Max 96.0 2.0 0.5 1.8 10.0 2.5 2.5 35.0 0.1Mean 46.1 1.8 0.1 0.8 5.1 2.5 2.5 10.8 0.1Geo Mean 41.8 1.8 0.1 0.7 4.7 2.5 2.5 9.4 0.1Median 39.0 2.0 0.1 0.5 4.6 2.5 2.5 9.9 0.1Quartile 1 31.0 2.0 0.1 0.5 3.5 2.5 2.5 6.4 0.1Quartile 3 63.0 2.0 0.1 1.0 6.3 2.5 2.5 13.0 0.1NOTE: For values reported as < (less than), half the detection limit was used.
NA = Data not applicableINA = Site was inaccessibleDRY = Site had no flow
36
B4: 544SJC508 – Bear Creek at Thorton Road (J8) continued …
DateHardness
(mg/L)
Dissolved Arsenic (ug/L)
Dissolved Cadmium
(ug/L)
Dissolved Chromium
(ug/L)
Dissolved Copper (ug/L)
Dissolved Lead (ug/L)
Dissolved Nickel (ug/L)
Dissolved Zinc
(ug/L)
Dissolved Mercury (ug/L)
10/24/2000 3911/28/2000 66 <1 4.2 <5 <5 1112/27/2000 82 <1 2.8 <5 <5 5.01/23/2001 96 <1 4.4 <5 <5 4.12/20/2001 31 <1 3.3 <5 <5 183/27/2001 38 <1 3.2 <5 <5 7.64/24/2001 34 <1 6.3 <5 <5 8.45/29/2001 33 <1 2.0 <5 <5 3.66/26/2001 <2 <1 <1 3.8 <5 <5 8.6 <0.27/24/2001 NA NA NA NA NA NA NA NA8/28/2001 22 <2 <1 <1 <1 <5 <5 3.29/25/2001 39 <4 <0.1 <1 1.9 <5 <5 3.8 <0.2
10/23/2001 58 <4 <0.1 <1 2.5 <5 <5 10 NA11/27/2001 23 <4 <0.1 <1 3.6 <5 <5 12 <0.212/26/2001 <4 <0.1 <1 8.2 <5 <5 12 <0.21/29/2002 64 <4 <0.1 <1 2.9 <5 <5 4.6 <0.23/26/2002 63 <4.0 <0.1 <1.0 4.8 <5.0 <5.0 7.9 <0.24/23/2002 26 <4.0 <0.1 <1.0 3.4 <5.0 <5.0 5.4 <0.25/28/2002 25 <4.0 <0.1 <1.0 2.6 <5.0 <5.0 4.1 <0.26/18/2002 45 <4.0 <0.1 <1.0 1.9 <5.0 <5.0 3.4 <0.2
Count 17 11 11 18 18 18 18 18 9Min 22.0 1.0 0.1 0.5 0.5 2.5 2.5 3.2 0.1Max 96.0 2.0 0.5 0.5 8.2 2.5 2.5 18.0 0.1Mean 46.1 1.8 0.1 0.5 3.5 2.5 2.5 7.4 0.1Geo Mean 41.8 1.8 0.1 0.5 3.0 2.5 2.5 6.5 0.1Median 39.0 2.0 0.1 0.5 3.3 2.5 2.5 6.5 0.1Quartile 1 31.0 2.0 0.1 0.5 2.5 2.5 2.5 4.1 0.1Quartile 3 63.0 2.0 0.1 0.5 4.1 2.5 2.5 9.7 0.1NOTE: For values reported as < (less than), half the detection limit was used.
NA = Data not applicableINA = Site was inaccessibleDRY = Site had no flow
37
38
B4: 544SJC508 – Bear Creek at Thorton Road (J8) continued …
DateChloride (mg/L)
Sulfate (mg/L)
Calcium (mg/L)
Magnesium (mg/L)
TDS (mg/L)
Carbonate (mg/L)
Bicarbonate (mg/L)
Total Alkalinity
(mg/L)Sodium (mg/L)
10/24/2000 8 5 9 4 87 <1 60 50 711/28/2000 16 10 17 6 140 <1 80 70 1312/27/2000 17 9 19 9 170 <1 110 90 161/23/2001 16 14 21 10 190 <1 130 110 172/20/2001 6 5 8 3 95 <1 37 30 53/27/2001 7 5 9 4 NA <1 51 42 74/24/2001 4 4 9 3 56 <1 46 38 45/29/2001 4 3 8 3 48 <1 30 30 48/28/2001 4 3 6 2 58 <1 32 27 49/25/2001 5 5 10 4 NA <1 45 37 5
10/23/2001 6 6 14 6 NA <1 72 59 811/27/2001 6 4 6 2 76 <1 26 21 41/29/2002 11 9 15 6 130 <1 79 65 123/26/2002 11 6 15 6 150 <1.0 80 70 124/23/2002 4 3 6 2 45 <1.0 28 23 45/28/2002 5 3 6 3 NA <1.0 27 22 46/18/2002 9 7 10 5 NA <1.0 53 NA 7
Count 17 17 17 17 12 17 17 16 17Min 4 3 6 2 45 0.5 26 21 4Max 17 14 21 10 190 0.5 130 110 17Mean 8 6 11 5 104 0.5 58 49 8Geo Mean 7 5 10 4 92 0.5 51 43 7Median 6 5 9 4 91 0.5 51 40 7Quartile 1 5 4 8 3 58 0.5 32 29 4Quartile 3 11 7 15 6 140 0.5 79 66 12NOTE: For values reported as < (less than), half the detection limit was used.
NA = Data not applicableINA = Site was inaccessibleDRY = Site had no flow
B5: 531SJC515 – Bear Creek at Lower Sacramento Road Station Code:531SJC515
Location: Latitude 38.04278, Longitude -121.32139
Date TimeTemp (ºC)
Field SC (umhos) pH
Dissolved Oxygen (mg/L)
Turbidity (ntu)
9/24/2002 8:48 AM 21.4 71 7.8 4.610/15/2002 11:35 AM 15.6 105 7.0 6.1 16.210/29/2002 8:57 AM 11.2 231 7.6 7.4 22.711/19/2002 8:01 AM 8.5 229 7.5 5.912/17/2002 7:24 AM 10.7 210 7.2 7.9 1911/28/2003 8:25 AM 11.3 241 7.5 7.2 14.33/25/2003 8:17 AM 13.7 231 7.1 6.2 35.44/22/2003 8:21 AM 14.7 94 7.1 7.6 24.35/27/2003 9:05 AM 21.6 63 7.1 5.6 45.06/24/2003 12:06 PM 23.1 78 7.0 5.3 1287/29/2003 11:15 AM 25.9 76 7.5 6.3 71.28/26/2003 9:12 AM 24.6 82 6.9 3.9 68.69/23/2003 9:12 AM 21.5 56 6.9 6.2 49.9
10/28/2003 9:32 AM 16.3 77 7.3 7.9 12.911/18/2003 8:54 AM 10.5 108 7.5 11.7 37.31/28/2004 8:28 AM 9.0 236 7.6 13.9 11.62/24/2004 9:15 AM 12.7 258 7.4 9.0 77.03/24/2004 8:05 AM 16.5 228 7.3 5.8 14.94/28/2004 8:04 AM 18.6 184 7.1 4.1 27.45/26/2004 9:11 AM 21.1 78 7.2 6.3 27.06/23/2004 8:08 AM 21.7 55 7.2 6.1 NA7/28/2004 8:35 AM 23.6 95 7.8 4.1 NA8/25/2004 8:28 AM 20.6 69 6.9 2.4 NA9/29/2004 8:45 AM 17.7 68 7.2 3.7 NA
10/27/2004 8:32 AM 13.2 297 7.3 5.811/22/2004 9:31 AM 7.2 295 7.5 5.812/28/2004 8:42 AM 8.8 378 7.3 4.11/26/2005 8:53 AM 9.9 250 7.5 8.12/23/2005 8:18 AM 13.8 211 7.5 8.33/29/2005 9:33 AM 13.9 196 7.2 8.54/26/2005 9:17 AM 16.0 69 7.5 9.55/24/2005 8:37 AM 19.0 57 7.5 8.36/28/2005 8:40 AM 19.9 59 7.1 7.77/26/2005 8:33 AM 21.5 68 7.3 5.48/23/2005 8:34 AM 21.9 162 7.3 6.79/27/2005 9:11 AM 18.4 153 7.6 11.7
39
B5: 531SJC515 – Bear Creek at Lower Sacramento Road continued…
Date TimeTemp (ºC)
Field SC (umhos) pH
Dissolved Oxygen (mg/L)
Turbidity (ntu)
Count 36 36 36 36 18Min 7.2 55 6.9 2.4 11.6Max 25.9 378 7.8 13.9 191Mean 16.5 151 7.3 6.8 48.6Geo Mean 15.7 126 7.3 6.4 34.8Median 16.4 107 7.3 6.3 31.4Quartile 1 12.4 71 7.1 5.6 17.8Quartile 3 21.4 230 7.5 8.0 63.9NOTE: For values reported as < (less than), half the detection limit was used.
NA = Data not applicableINA = Site was inaccessibleDRY = Site had no flow
40
41
DateTSS
(mg/L)TOC
(mg/L)Total Coli
MPNE. coli MPN
9/24/2002 3.710/15/2002 >2419.6 5810/29/2002 6.711/19/2002 7.03/25/2003 9.94/22/2003 4.9 >2419.6 505/27/2003 NA6/24/2003 NA7/29/2003 >2419.6 1058/26/2003 >2419.6 1679/23/2003 >2419.6 1203
10/28/2003 >2419.6 8611/18/2003 >2419.6 >2419.61/28/2004 1733 152/24/2004 >2419.6 7273/24/2004 >2419.6 164/28/2004 >2419.6 545/26/2004 >2419.6 316/23/2004 >2419.6 967/28/2004 >2419.6 >2419.68/259/29
10/11/12/1/262/233/294/265/246/287/268/239/27
Coun
B5: 531SJC515 – Bear Creek at Lower Sacramento Road continued…
/2004 >2419.6 18/2004 >2419.6 20
27/2004 15 >2419.6 10222/2004 14 >2419.6 6828/2004 10 >2419.6 15
/2005 13 1733 76/2005 16 1553 37/2005 13 >2419.6 145/2005 NA >2419.6 96/2005 NA >2419.6 548/2005 2.9 >2419.6 102/2005 NA >2419.6 2420/2005 4.3 >2419.6 126/2005 4.1 >2419.6 133
t NA 14 28 28NA 2.9 1553 15N
Min Max A 16 2420 2420
n NMea A 8.9 NA NA Mean NA 7.7 2326 113ian N
GeoMed A 8.5 2420 96
rtile 1 NQua A 4.5 2420 47rtile 3 NA 13 2420 151E: For values reported as < (less than), half the detection limit was used For values reported as > (greater than), 2420 was used
Data not applicable = Site was inaccessibleY = Site had no flow
QuaNOT
NA =INADR
B5: 531SJC515 – Bear Creek at Lower Sacramento Road continued…
DateNitrate (mg/L)
Nitrate-N (mg/L)
TKN (mg/L)
Ammonia-N (mg/L)
Phosphorus (mg/L)
Ortho-phosphate-
P (mg/L)
Potassium (mg/L)
BOD 5-Day (mg/L)
BOD 10-Day (mg/L)
9/24/2002 NA NA 0.8 NA 1.9 1.3 2.210/29/2002 NA 0.8 0.1 NA 9.9 0.9 1.511/19/2002 NA 0.8 0.1 0.1 10 1.5 2.712/17/2002 NA 3.7 1.4 <0.03 17 8 16.41/28/2003 NA 1.5 0.4 0.3 12 1.3 2.5
Count NA NA 4 NA 5 3 5 5 5Min NA NA 0.8 NA 0.1 0.02 1.9 0.9 1.5Max NA NA 3.7 NA 1.4 0.3 17.0 8.0 16.4Mean NA NA 1.7 NA 0.6 0.1 10.2 2.6 5.1Geo Mean NA NA 1.4 NA 0.3 0.1 8.3 1.8 3.3Median NA NA 1.2 NA 0.4 0.1 10.0 1.3 2.5Quartile 1 NA NA 0.8 NA 0.1 0.1 9.9 1.3 2.2Quartile 3 NA NA 2.1 NA 0.8 0.2 12.0 1.5 2.7NOTE: For values reported as < (less than), half the detection limit was used.
NA = Data not applicableINA = Site was inaccessibleDRY = Site had no flow
42
B5: 531SJC515 – Bear Creek at Lower Sacramento Road continued…
DateHardness
(mg/L)
Total Arsenic (ug/L)
Total Cadmium
(ug/L)
Total Chromium
(ug/L)
Total Copper (ug/L)
Total Lead (ug/L)
Total Nickel (ug/L)
Total Zinc (ug/L)
Total Mercury (ug/L)
9/24/2002 25 <4.0 <0.1 1.1 14 <5.0 <5.0 7.2 <0.210/29/2002 73 <4.0 <0.1 <1.0 3.8 <5.0 <5.0 3.7 <0.211/19/2002 69 <4.0 <0.1 <1.0 2.5 <5.0 <5.0 5.4 <0.2
3/25/2003 74 <4.0 <0.1 1.1 4.0 <5.0 <5.0 3.7 <0.24/22/2003 32 <4.0 <0.1 <1.0 3.5 <5.0 <5.0 5.5 <0.25/27/2003 23 <4.0 <0.1 2.1 5.2 <5.0 <5.0 8.8 <0.26/24/2003 28 <4.0 <0.1 4.1 6.8 <5.0 <5.0 14 <0.2
Count 7 7 7 7 7 7 7 7 7Min 23.0 2.0 0.1 0.5 2.5 2.5 2.5 3.7 0.1Max 74.0 2.0 0.1 4.1 14.0 2.5 2.5 14.0 0.1Mean 46.3 2.0 0.1 1.4 5.7 2.5 2.5 6.9 0.1Geo Mean 40.9 2.0 0.1 1.0 4.9 2.5 2.5 6.2 0.1Median 32.0 2.0 0.1 1.1 4.0 2.5 2.5 5.5 0.1Quartile 1 26.5 2.0 0.1 0.5 3.7 2.5 2.5 4.6 0.1Quartile 3 71.0 2.0 0.1 1.6 6.0 2.5 2.5 8.0 0.1NOTE: For values reported as < (less than), half the detection limit was used.
NA = Data not applicableINA = Site was inaccessibleDRY = Site had no flow
43
B5: 531SJC515 – Bear Creek at Lower Sacramento Road continued…
DateHardness
(mg/L)
Dissolved Arsenic (ug/L)
Dissolved Cadmium
(ug/L)
Dissolved Chromium
(ug/L)
Dissolved Copper (ug/L)
Dissolved Lead (ug/L)
Dissolved Nickel (ug/L)
Dissolved Zinc
(ug/L)
Dissolved Mercury (ug/L)
9/24/2002 25 <4.0 <0.1 <1.0 3.3 <5.0 <5.0 4.4 <0.210/29/2002 73 <4.0 <0.1 <1.0 3 <5.0 <5.0 2.2 <0.211/19/2002 69 <4.0 <0.1 <1.0 1.8 <5.0 <5.0 2.9 <0.2
Count 3 3 3 3 3 3 3 3 3Min 25.0 2.0 0.1 0.5 1.8 2.5 2.5 2.2 0.1Max 73.0 2.0 0.1 0.5 3.3 2.5 2.5 4.4 0.1Mean 55.7 2.0 0.1 0.5 2.7 2.5 2.5 3.2 0.1Geo Mean 50.1 2.0 0.1 0.5 2.6 2.5 2.5 3.0 0.1Median 69.0 2.0 0.1 0.5 3.0 2.5 2.5 2.9 0.1Quartile 1 47.0 2.0 0.1 0.5 2.4 2.5 2.5 2.6 0.1Quartile 3 71.0 2.0 0.1 0.5 3.2 2.5 2.5 3.7 0.1NOTE: For values reported as < (less than), half the detection limit was used.
NA = Data not applicableINA = Site was inaccessibleDRY = Site had no flow
44
45
B5: 531SJC515 – Bear Creek at Lower Sacramento Road continued…
DateChloride (mg/L)
Sulfate (mg/L)
Calcium (mg/L)
Magnesium (mg/L)
TDS (mg/L)
Carbonate (mg/L)
Bicarbonate (mg/L)
Total Alkalinity
(mg/L)Sodium (mg/L)
9/24/2002 4 3 6 3 NA <1.0 29 24 410/29/2002 15 6 16 8 190 <1.0 100 84 1611/19/2002 19 8 15 8 160 <1.0 87 71 163/25/2003 12 6 16 84/22/2003 5 3 7 35/27/2003 4 3 5 26/24/2003 4 3 6 3
Count 7 7 7 7 2 3 3 3 3Min 4 3 5 2 160 0.5 29 24 4Max 19 8 16 8 190 0.5 100 84 16Mean 9 5 10 5 180 0.5 72 60 12Geo Mean 7 4 9 4 170 0.5 63 52 10Median 5 3 7 3 180 0.5 87 71 16Quartile 1 4 3 6 3 170 0.5 58 48 10Quartile 3 14 6 16 8 180 0.5 94 78 16NOTE: For values reported as < (less than), half the detection limit was used.
NA = Data not applicableINA = Site was inaccessibleDRY = Site had no flow
B5: 531SJC515 – Bear Creek at Lower Sacramento Road continued…
Date Result Control Result Control
Result (million/m
l)
Control (million/
ml)MDD (%)
11/22/2004 100 100 100 1001/26/2005 95 97.5 100 1002/23/2005 95 100 100 1003/29/2005 100 100 95 1004/26/2005 72.5* 100 100 1005/24/2005 95 100 100 1006/28/2005 100 100 100 1008/23/2005 95 100 100 1009/27/2005 100 100 100 100
Count 9 9 9 9 N/A N/A N/A
* Significantly reduced from the lab control.** Significantly greater than the lab control.^ Fish were from a "forced hatch," duplicate failed QA.1 Duplicate sample for the set was low - 77% recovery.
3 Samples qualified, but duplicate sample recovery for the set was high - 126% (53.8%/42.5%)NA = Data not applicableINA = Site was inaccessibleDRY = Site had no flow
2 Testing for the Fathead minnow was initiated when samples were approx. 48h old due to untimely shipping of fish by fish supplier.
96h Acute Fathead Minnow
(% Survival)
48h Acute Ceriodaphnia Dubia
(% Survival) Algae Cell Growth
46
APPENDIX C
EASTSIDE BASIN
APPENDIX C: EASTSIDE BASIN C1: 535MER546 – Merced River @ River Road ………………………………………..03-13 C2: 535MER576 – Turner Slough at Fourth Ave………………………………………..14-26 C3: 535STC501 – TID 5 Harding Drain @ Carpenter Road…………………………….27-39 C4: 535STC513 – Tuolumne River at Shiloh Fishing Access……………………………40-52 C5: 535STC514 – Stanislaus river at Caswell Park………………………………………53-63 C6: 531SJC503 – Lone Tree Creek at Austin Road………………………………………64-75 C7: 531SJC504 – French Camp Slough at Airport Way………………………………….76-86
2
C1: 535MER546 – Merced River @ River Road Station Code:541MER546
Location: Latitude 37.84972, Longitude -120.95778
Date TimeTemp (ºC)
Field SC (umhos) pH
Dissolved Oxygen (mg/L)
Turbidity (ntu)
11/30/2000 10:10 AM 10.1 93 8.212/28/2000 11:50 AM 9.7 155 8.71/25/2001 1:50 PM 10.2 129 8.22/22/2001 1:27 PM 15.8 173 9.23/29/2001 12:00 PM 19.7 155 8.24/26/2001 8:57 AM 17.7 74 7.15/30/2001 1:50 PM 26.4 170 7.96/27/2001 12:45 PM 23.8 292 8.4 8.47/25/2001 1:05 PM 26.7 346 7.9 9.78/29/2001 1:39 PM 26.6 396 7.9 9.69/26/2001 12:20 PM 21.9 233 7.9 9.8
10/24/2001 1:46 PM 15.8 41 7.9 9.611/28/2001 12:14 PM 11.0 90 8.6 10.712/26/2001 12:05 PM 10.7 107 7.7 10.71/30/2002 12:44 PM 8.4 162 7.8 12.22/27/2002 11:38 AM 15.3 191 7.8 9.63/27/2002 11:12 AM 16.5 166 7.9 9.24/30/2002 12:08 PM 16.2 115 8.5 11.65/29/2002 12:13 PM 24.3 197 8.1 8.36/19/2002 11:52 AM 25.1 262 7.8 8.17/30/2002 8:45 AM 23.1 310 8.1 7.1 9.38/28/2002 1:30 PM 26.8 302 8.5 NA9/25/2002 1:48 PM 24.5 359 7.8 10.0
10/30/2002 NA 14.9 97 7.8 9.811/20/2002 12:19 PM 13.5 129 8.1 10.412/18/2002 11:42 AM 10.9 115 7.7 9.9 45.31/29/2003 12:25 PM 13.2 177 7.8 10.6 25.03/25/2003 10:44 AM 16.8 135 8.0 10.2 15.97/31/2003 10:58 AM 24.3 416 7.6 8.3 5.68/28/2003 10:41 AM 22.5 409 7.7 8.3 6.39/25/2003 11:31 AM 21.5 358 7.8 8.7 4.3
10/30/2003 10:09 AM 15.7 118 7.8 9.6 4.311/20/2003 10:35 AM 13.1 124 8.2 10.9 NA1/29/2004 11:07 AM 10.7 131 8.3 11.6 NA2/26/2004 10:45 AM 12.3 124 7.9 10.1 NA3/24/2004 11:42 AM 19.0 143 7.6 8.9 NA4/29/2004 11:34 AM 17.5 60 7.9 9.0 9.65/27/2004 11:43 AM 23.0 172 7.5 8.0 14.1
3
C1: 535MER546 – Merced River @ River Road continued …
Date TimeTemp (ºC)
Field SC (umhos) pH
Dissolved Oxygen (mg/L)
Turbidity (ntu)
6/24/2004 11:40 AM 24.6 243 7.7 8.0 NA7/29/2004 10:53 AM 24.3 454 7.9 11.1 NA8/26/2004 11:28 AM 23.9 404 7.8 8.5 NA9/30/2004 10:44 AM 19.1 395 7.7 9.5 NA
10/28/2004 11:19 AM 13.5 95 8.1 10.011/23/2004 11:34 AM 10.9 177 7.6 11.512/29/2004 10:46 AM 9.6 116 7.7 11.51/27/2005 12:53 PM 11.4 168 7.6 12.02/24/2005 11:02 AM 13.8 156 7.6 8.83/29/2005 12:56 PM 11.8 70 7.6 10.44/28/2005 11:18 AM 13.7 66 8.0 10.25/26/2005 12:18 PM 15.8 48 7.6 9.66/30/2005 11:54 AM 19.7 71 7.3 8.57/28/2005 11:21 AM 23.3 96 7.3 6.78/25/2005 11:46 AM 20.2 49 7.6 8.79/29/2005 11:45 AM 18.3 57 6.9 7.2
Count 54 54 54 46 10Min 8.4 41 6.9 6.7 4.3Max 26.8 454 9.2 12.2 45.3Mean 17.6 183 7.9 9.6 14.0Geo Mean 16.7 152 7.9 9.5 10.4Median 16.7 155 7.8 9.6 9.5Quartile 1 13.1 100 7.7 8.6 5.8Quartile 3 23.1 241 8.1 10.4 15.5NOTE: For values reported as < (less than), half the detection limit was used.
NA = Data not applicableINA = Site was inaccessibleDRY = Site had no flow
4
C1: 535MER546 – Merced River @ River Road continued …
DateTSS
(mg/L)TOC
(mg/L)Total Coli
MPNE. coli MPN
11/30/2000 <6 1.612/28/2000 NA 2.01/25/2001 <5 1.92/22/2001 14 2.53/29/2001 NA <14/26/2001 2.85/30/2001 <6 2.76/27/2001 <6 6.27/25/2001 2.58/29/2001 NA 9.39/26/2001 NA 6.2
11/28/2001 NA12/26/2001 2.23/27/2002 NA4/30/2002 NA5/29/2002 1.96/19/2002 NA7/30/2002 >2419.6 4118/28/2002 NA9/25/2002 NA
10/30/2002 1.611/20/2002 1.812/18/2002 4.17/31/2003 >2419.6 1388/28/2003 >2419.6 4619/25/2003 >2419.6 115
10/30/2003 NA NA11/20/2003 1120 311/29/2004 344 192/26/2004 2420 833/24/2004 >2419.6 454/29/2004 >2419.6 935/27/2004 >2419.6 1796/24/2004 >2419.6 3877/29/2004 >2419.6 19868/26/2004 >2419.6 1219/30/2004 >2419.6 113
10/28/2004 1.6 >2419.6 8111/23/2004 1.8 816 2512/29/2004 1.5 1733 501/27/2005 3.2 2420 25
5
6
DateTSS
(mg/L)TOC
(mg/L)Total Coli
MPNE. coli MPN
2/24/2005 5.0 921 3083/29/2005 3.5 >2419.6 6134/28/2005 2.4 1986 865/26/2005 2.6 >2419.6 806/30/2005 NA >2419.6 707/28/2005 NA >2419.6 938/25/2005 2.0 >2419.6 999/29/2005 2.2 >2419.6 488
Count 5 26 26 26Min 3 0.5 344 19Max 14 9.3 2420 1986Mean 5 2.9 NA NAGeo Mean 4 2.5 197
C1: 535MER546 – Merced River @ River Road continued …
3 120Median 3 2.3 2420 96Quartile 1 3 1.8 2420 73Quartile 3 3 3.1 2420 276
E: For values reported as < (less than), half the detection limit was used For values reported as > (greater than), 2420 was used
Data not applicable Site was inaccessible
= Site had no flow
NOT
NA =INA =DRY
C1: 535MER546 – Merced River @ River Road continued …
DateNitrate (mg/L)
Nitrate-N (mg/L)
TKN (mg/L)
Ammonia-N (mg/L)
Phosphorus (mg/L)
Ortho-phosphate-
P (mg/L)
Potassium (mg/L)
BOD 5-Day (mg/L)
BOD 10-Day (mg/L)
11/30/2000 4.9 <2 <0.1 <1 <1 0.3 0.612/28/2000 7.6 <2 <0.1 <1 1.3 0.2 0.31/25/2001 NA NA <0.1 <1 1.3 0.7 0.92/22/2001 8.1 2.4 NA <1 1.7 0.4 0.63/29/2001 6.3 NA <0.1 <1 1.7 0.6 1.14/26/2001 2.0 <2 NA <1 <1 0.5 1.15/30/2001 7.0 <2 NA <1 1.6 0.6 0.76/27/2001 11 <2 <0.1 <1 2.5 0.6 0.88/29/2001 15 <2 <0.1 <1 NA9/26/2001 13 <2 <0.1 <1 1.9
10/24/2001 <2 <2 <0.1 <1 <1 0.5 0.711/28/2001 0.2 0.512/26/2001 0.3 0.71/30/2002 0.1 0.52/27/2002 0.4 0.73/27/2002 1.6 3.84/30/2002 0.5 0.95/29/2002 0.4 0.46/19/2002 0.7 0.88/28/2002 0.1 0.69/25/2002 0.6 0.9
10/30/2002 0.3 0.311/20/200212/18/2002 3.3 7.31/29/2003 0.4 0.6
C1: 535MER546 – Merced River @ River Road continued …
DateNitrate (mg/L)
Nitrate-N (mg/L)
TKN (mg/L)
Ammonia-N (mg/L)
Phosphorus (mg/L)
Ortho-phosphate-
P (mg/L)
Potassium (mg/L)
BOD 5-Day (mg/L)
BOD 10-Day (mg/L)
Count 10 NA 9 NA 8 11 10 22 22Min 1.0 NA 1.0 NA 0.05 0.5 0.5 0.1 0.3Max 15 NA 2.4 NA 0.05 0.5 2.5 3.3 7.3Mean 7.6 NA 1.2 NA 0.05 0.5 1.4 0.6 1.1Geo Mean 6.0 NA 1.1 NA 0.05 0.5 1.2 0.4 0.8Median 7.3 NA 1.0 NA 0.05 0.5 1.5 0.5 0.7Quartile 1 5.3 NA 1.0 NA 0.05 0.5 0.7 0.3 0.6Quartile 3 10.3 NA 1.0 NA 0.05 0.5 1.7 0.6 0.9NOTE: For values reported as < (less than), half the detection limit was used.
NA = Data not applicableINA = Site was inaccessibleDRY = Site had no flow
8
C1: 535MER546 – Merced River @ River Road continued …
DateHardness
(mg/L)
Total Arsenic (ug/L)
Total Cadmium
(ug/L)
Total Chromium
(ug/L)
Total Copper (ug/L)
Total Lead (ug/L)
Total Nickel (ug/L)
Total Zinc (ug/L)
Total Mercury (ug/L)
11/30/2000 29 <1 <1 <5 <5 7.812/28/2000 46 <1 1.3 <5 <5 <21/25/2001 40 <1 1.7 <5 <5 2.52/22/2001 55 <1 2.1 <5 <5 <23/29/2001 48 <1 1.7 <5 <5 2.54/26/2001 26 <1 1.8 <5 <5 2.25/30/2001 50 <1 <1 <5 <5 <27/25/2001 <1 1.2 <5 <5 <28/29/2001 NA <2 <1 <1 <1 <5 <5 <29/26/2001 67 <4 <0.1 <1 1.4 <5 <5 <2 <0.2
10/24/2001 15 <4.0 <0.1 <1.0 <1.0 <5.0 <5.0 <2.0 <0.211/28/2001 28 <4.0 <0.1 <1.0 <1.0 <5.0 <5.0 3.7 <0.212/26/2001 <4 <0.1 <1 1.5 <5 <5 3.4 <0.21/30/2002 <4 <0.1 <1 <1 <5 <5 <2 <0.23/27/2002 <4.0 <0.1 <1.0 5.0 <5.0 <5.0 10 <0.24/30/2002 <4.0 <0.1 <1.0 1.2 <5.0 <5.0 <2.0 <0.25/29/2002 <4.0 <0.1 <1.0 NA <5.0 <5.0 <2.0 <0.26/19/2002 <4.0 <0.1 <1.0 1.0 <5.0 <5.0 <2.0 <0.29/25/2002 98 <4.0 <0.1 <1.0 NA <5.0 <5.0 <2.0 <0.2
10/30/2002 27 <4.0 <0.1 <1.0 NA <5.0 <5.0 <2.0 <0.211/20/2002 41 <4.0 <0.1 <1.0 1.3 <5.0 NA NA <0.2
Count 13 13 13 21 18 21 20 20 12Min 15 1.0 0.1 0.5 0.5 2.5 2.5 1.0 0.1Max 98 2.0 0.5 0.5 5.0 2.5 2.5 10.0 0.1Mean 44 1.9 0.1 0.5 1.3 2.5 2.5 2.3 0.1Geo Mean 39 1.9 0.1 0.5 1.1 2.5 2.5 1.6 0.1Median 41 2.0 0.1 0.5 1.3 2.5 2.5 1.0 0.1Quartile 1 28 2.0 0.1 0.5 0.5 2.5 2.5 1.0 0.1Quartile 3 50 2.0 0.1 0.5 1.7 2.5 2.5 2.5 0.1NOTE: For values reported as < (less than), half the detection limit was used.
NA = Data not applicableINA = Site was inaccessibleDRY = Site had no flow
9
C1: 535MER546 – Merced River @ River Road continued …
DateHardness
(mg/L)
Dissolved Arsenic (ug/L)
Dissolved Cadmium
(ug/L)
Dissolved Chromium
(ug/L)
Dissolved Copper (ug/L)
Dissolved Lead (ug/L)
Dissolved Nickel (ug/L)
Dissolved Zinc
(ug/L)
Dissolved Mercury (ug/L)
11/30/2000 29 <1 <1 <5 <5 <212/28/2000 46 <1 <1 <5 <5 <21/25/2001 40 <1 <1 <5 <5 <22/22/2001 55 <1 <1 <5 <5 2.43/29/2001 48 <1 1.3 <5 <5 <24/26/2001 26 <1 <1 <5 <5 2.45/30/2001 50 <1 <1 <5 <5 4.07/25/20018/29/2001 NA <2 <1 <1 <1 <5 <5 <29/26/2001 67 <4 <0.1 <1 1.4 <5 <5 2.9 <0.2
10/24/2001 15 <4.0 <0.1 <1.0 <1.0 <5.0 <5.0 <2.0 <0.211/28/2001 28 <4.0 <0.1 <1.0 <1.0 <5.0 <5.0 NA <0.212/26/2001 <4 <0.1 <1 1.0 <5 <5 4.5 <0.21/30/2002 <4 <0.1 <1 <1 <5 <5 <2 <0.23/27/2002 <4.0 <0.1 <1.0 2.0 <5.0 <5.0 5.5 <0.24/30/2002 <4.0 <0.1 <1.0 <1.0 <5.0 <5.0 <2.0 <0.25/29/2002 <4.0 <0.1 <1.0 <1.0 <5.0 <5.0 <2.0 <0.26/19/2002 <4.0 <0.1 <1.0 <1.0 <5.0 <5.0 <2.0 <0.29/25/2002 98 <4.0 <0.1 <1.0 NA <5.0 <5.0 <2.0 <0.2
10/30/2002 27 <4.0 <0.1 <1.0 1.2 <5.0 <5.0 <2.0 <0.211/20/2002 41 <4.0 <0.1 <1.0 1.1 <5.0 <5.0 <2.0 <0.2
Count 13 13 13 20 19 20 20 19 12Min 15 1.0 0.1 0.5 0.5 2.5 2.5 1.0 0.1Max 98 2.0 0.5 0.5 2.0 2.5 2.5 5.5 0.1Mean 44 1.9 0.1 0.5 0.8 2.5 2.5 1.8 0.1Geo Mean 39 1.9 0.1 0.5 0.7 2.5 2.5 1.5 0.1Median 41 2.0 0.1 0.5 0.5 2.5 2.5 1.0 0.1Quartile 1 28 2.0 0.1 0.5 0.5 2.5 2.5 1.0 0.1Quartile 3 50 2.0 0.1 0.5 1.1 2.5 2.5 2.4 0.1NOTE: For values reported as < (less than), half the detection limit was used.
NA = Data not applicableINA = Site was inaccessibleDRY = Site had no flow
10
11
C1: 535MER546 – Merced River @ River Road continued …
DateChloride (mg/L)
Sulfate (mg/L)
Calcium (mg/L)
Magnesium (mg/L)
TDS (mg/L)
Carbonate (mg/L)
Bicarbonate (mg/L)
Total Alkalinity
(mg/L)Sodium (mg/L)
11/30/2000 6 4 8 3 99 <1 30 30 612/28/2000 11 9 12 4 76 <1 50 40 121/25/2001 8 8 10 4 57 <1 50 40 92/22/2001 11 11 14 5 130 <1 60 49 133/29/2001 9 9 12 4 110 <1 67 55 104/26/2001 4 4 7 2 65 <1 26 26 55/30/2001 12 10 13 4 NA <1 44 44 136/27/2001 26 17 20 7 140 <1 87 72 258/29/2001 35 NA NA NA 220 <1.0 120 96 359/26/2001 NA NA 17 6 NA <1 72 59 20
10/24/2001 3 3 4 1 59 <1 18 15 311/28/2001 5 5 7 2 59 <1 33 27 6
Count 11 10 11 11 10 12 12 12 12Min 3 3 4 1 57 0.5 18 15 3Max 35 17 20 7 220 0.5 120 96 35Mean 12 8 11 4 100 0.5 55 46 13Geo Mean 9 7 10 3 92 0.5 48 41 10Median 9 9 12 4 88 0.5 50 42 11Quartile 1 6 4 8 3 61 0.5 32 29 6Quartile 3 12 10 14 5 130 0.5 68 56 15NOTE: For values reported as < (less than), half the detection limit was used.
NA = Data not applicableINA = Site was inaccessibleDRY = Site had no flow
C1: 535MER546 – Merced River @ River Road continued …
Date Result Control Result Control
Result (million/m
l)
Control (million/m
l) MDD(%)10/26/2000 100 100 NA NA10/24/2001 100 100 100 10011/28/2001 NA NA 100 10012/26/2001 100 100 100 1001/30/2002 100 100 90 902/27/2002 100 100 100 1004/30/2002 100 100 100 1005/29/2002 100 100 100 1006/19/2002 100 100 100 1008/28/2002 90 100 NA NA9/25/2002 100 100 100 100
10/30/2002 100 100 100 10011/20/2002 100 100 100 10012/18/2002 95 90 100 100 3.35 3.03 NA1/29/2003 95 100 100 100 4.86** 3.28 NA4/17/2003 100 100 100 100 1.73 1.84 45/22/2003 85 100 100 100 4.24** 2.08 59
Count 16 16 15 15 4 4 2
* Significantly reduced from the lab control.** Significantly greater than the lab control.^ Fish were from a "forced hatch," duplicate failed QA.1 Duplicate sample for the set was low - 77% recovery.
3 Samples qualified, but duplicate sample recovery for the set was high - 126% (53.8%/42.5%)NA = Data not applicableINA = Site was inaccessibleDRY = Site had no flow
2 Testing for the Fathead minnow was initiated when samples were approx. 48h old due to untimely shipping of fish by fish supplier.
96h Acute Fathead Minnow
(% Survival)
48h Acute Ceriodaphnia Dubia
(% Survival) Algae Cell Growth
C1: 535MER546 – Merced River @ River Road continued …
Date
Result (%
Survival)
Control (%
Survival)
Avg Dry Weight Result (mg)
Avg Dry Weight Control
(mg)Growth MDD(%)
Result (%
Survival)
Control (%
Survival)
Avg # Young /
Adult Result
Avg # Young /
Adult Control
Repro MDD(%)
11/23/2004 90.0 95.0 0.22* 0.29 2412/29/2004 97.4 97.5 0.63 0.54 12
01/27/2005 1 97.5 100.0 0.48 0.53 202/24/2005 100.0 100.0 0.67 0.57 13
03/29/2005 2 62.5* 100.0 0.31 0.42 424/28/2005 N/A N/A N/A N/A N/A5/26/2005 65.0* 97.5 0.30* 0.51 8.96/30/2005 92.5 97.5 0.42 0.45 117/28/2005 N/A N/A N/A N/A N/A8/25/2005 87.2* 100.0 .47* 0.63 219/29/2005 89.7 100.0 0.41 0.43 24
Count 9 9 9 9 9 N/A N/A N/A N/A N/A
* Significantly reduced from the lab control.** Significantly greater than the lab control.^ Fish were from a "forced hatch," duplicate failed QA.1 Duplicate sample for the set was low - 77% recovery.
3 Samples qualified, but duplicate sample recovery for the set was high - 126% (53.8%/42.5%)NA = Data not applicableINA = Site was inaccessibleDRY = Site had no flow
2 Testing for the Fathead minnow was initiated when samples were approx. 48h old due to untimely shipping of fish by fish supplier.
Chronic Ceriodaphnia Dubia - 6 dayChronic Fathead Minnow - 7day
13
C2: 535MER576 – Turner Slough at Fourth Ave Station Code:535MER576
Location: Latitude 37.32056, Longitude -120.88917
Date TimeTemp (ºC)
Field SC (umhos) pH
Dissolved Oxygen (mg/L)
Turbidity (ntu)
4/26/2001 8:20 AM 20.5 158 6.45/31/2001 8:25 AM 24.1 175 7.96/28/2001 1:06 PM 26.7 232 8.0 7.67/26/2001 2:40 PM 29.6 238 8.1 NA8/30/2001 NA 26.9 196 8.5 NA9/27/2001 12:23 PM 23.2 212 8.3 9.5
10/25/2001 12:04 PM 16.7 301 8.0 11.511/29/2001 9:01 AM 7.9 189 8.0 10.712/27/2001 12:44 PM 9.6 313 7.7 10.01/31/2002 12:10 PM 5.0 342 9.1 13.32/28/2002 2:43 PM 14.5 339 8.3 12.33/28/2002 1:37 PM 20.4 307 8.5 11.34/24/2002 11:54 AM 19.0 192 7.9 7.55/30/2002 12:12 PM 26.2 166 7.8 8.36/20/2002 INA INA INA INA INA INA7/30/2002 11:28 AM 24.2 230 7.4 5.4 97.98/29/2002 12:05 PM 23.3 225 7.5 6.2 1279/26/2002 12:08 PM 21.4 203 7.7 6.4
10/17/2002 12:42 PM 16.7 238 8.2 8.6 91.710/31/2002 12:20 PM 12.9 194 8.6 11.3 10711/21/2002 11:55 AM 11.8 253 7.7 6.2 14212/19/2002 12:11 PM 7.2 234 7.9 10.7 1821/14/2003 11:06 AM 11.5 300 7.6 7.7 1841/30/2003 11:51 AM 11.9 474 7.7 12.1 1323/27/2003 2:12 PM 17.5 385 8.3 13.2 1024/24/2003 12:00 PM 17.7 175 7.6 6.5 1135/29/2003 11:02 AM 24.5 145 7.4 6.6 89.46/26/2003 10:44 AM 24.0 185 7.4 3.2 83.97/31/2003 11:27 AM 25.3 351 7.2 4.1 1658/28/2003 11:13 AM 22.9 290 7.4 5.2 77.89/25/2003 11:25 AM 20.7 212 7.2 5.0 515
10/30/2003 11:22 AM 14.0 185 7.1 3.3 97.711/20/2003 11:48 AM 9.7 203 7.1 6.1 2901/29/2004 11:09 AM DRY DRY DRY DRY DRY2/26/2004 11:10 AM 11.7 251 7.6 8.2 NA3/24/2004 11:24 AM DRY DRY DRY DRY DRY4/29/2004 11:10 AM 17.3 375 7.7 6.0 62.4
14
C2: 535MER576 – Turner Slough at Fourth Ave continued…
Date TimeTemp (ºC)
Field SC (umhos) pH
Dissolved Oxygen (mg/L)
Turbidity (ntu)
5/27/2004 11:23 AM 22.7 139 7.4 5.6 1176/24/2004 11:14 AM 25.1 184 7.7 8.2 NA7/29/2004 10:36 AM 23.2 468 7.7 6.8 NA8/26/2004 11:08 AM 24.7 232 8.0 7.0 NA9/30/2004 10:29 AM 19.0 254 7.8 7.9 NA
10/28/2004 11:01 AM 12.5 68 8.1 9.711/23/2004 11:10 AM 7.1 181 7.6 10.212/29/2004 10:27 AM 9.1 154 7.6 4.51/27/2005 12:10 PM 10.4 216 7.8 12.02/24/2005 10:37 AM 14.1 284 7.8 9.33/29/2005 12:29 PM 15.8 186 7.5 8.74/28/2005 10:56 AM 19.3 154 8.1 9.15/26/2005 11:52 AM 24.3 140 7.5 6.76/30/2005 11:29 AM 27.8 148 7.2 6.17/28/2005 11:00 AM 27.7 161 7.7 8.88/25/2005 11:14 AM 24.9 142 7.6 7.89/29/2005 11:18 AM 21.4 140 6.8 7.4
Count 51 51 51 47 19Min 5.0 68 6.4 3.2 62.4Max 29.6 474 9.1 13.3 515Mean 18.5 230 7.7 8.1 146Geo Mean 17.2 216 7.7 7.7 127Median 19.3 212 7.7 7.8 113Quartile 1 12.7 175 7.5 6.2 94.7Quartile 3 24.2 269 8.0 9.9 154NOTE: For values reported as < (less than), half the detection limit was used.
NA = Data not applicableINA = Site was inaccessibleDRY = Site had no flow
15
C2: 535MER576 – Turner Slough at Fourth Ave continued…
DateTSS
(mg/L)TOC
(mg/L)Total Coli
MPNE. coli MPN
12/28/2000 NA 531/25/2001 30 372/22/2001 40 313/29/2001 NA 204/26/2001 5.45/31/2001 88 5.96/28/2001 61 7.97/26/2001 6.58/30/2001 30 79/27/2001 28
10/25/2001 9.611/29/2001 <11/31/2002 73/28/2002 NA4/24/2002 125/30/2002 4.16/20/2002 INA7/30/2002 >2419.6 5489/26/2002 5.8
10/17/2002 >2419.6 >2419.610/31/2002 NA11/21/2002 4.11/14/2003 >2419.6 8663/27/2003 64/24/2003 NA >2419.6 6495/29/2003 126/26/2003 4.87/31/2003 >2419.6 2608/28/2003 >2419.6 8169/25/2003 >2419.6 166
10/30/2003 >2419.6 >2419.611/20/2003 >2419.6 17331/29/2004 DRY DRY2/26/2004 >2419.6 >2419.63/24/2004 DRY DRY4/29/2004 >2419.6 6875/27/2004 >2419.6 9806/24/2004 >2419.6 17337/29/2004 >2419.6 8168/26/2004 >2419.6 4359/30/2004 >2419.6 186
10/28/2004 7.6 >2419.6 411
16
17
DateTSS
(mg/L)TOC
(mg/L)Total Coli
MPNE. coli MPN
11/23/2004 16 >2419.6 29112/29/2004 7.8 >2419.6 7701/27/2005 13 >2419.6 1622/24/2005 13 1414 1153/29/2005 15 >2419.6 7274/28/2005 6.4 >2419.6 >2419.65/26/2005 8.1 >2419.6 15536/30/2005 NA >2419.6 4577/28/2005 NA >2419.6 13008/25/2005 4.2 >2419.6 8169/29/2005 3.3 >2419.6 146
Count 6 29 28 28Min 28 0.5 1414 115Max 88 53 2420 2420Mean 46 12 NA NAGeoMedQuaQua
C2: 535MER576 – Turner Slough at Fourth Ave continued…
Mean 42 8.2 2374 654ian 35 7.6 2420 749rtile 1 30 5.8 2420 381rtile 3 56 13 2420 1363E: For values reported as < (less than), half the detection limit was used For values reported as > (greater than), 2420 was used
Data not applicable Site was inaccessible
= Site had no flow
NOT
NA =INA =DRY
C2: 535MER576 – Turner Slough at Fourth Ave continued…
DateNitrate (mg/L)
Nitrate-N (mg/L)
TKN (mg/L)
Ammonia-N (mg/L)
Phosphorus (mg/L)
Ortho-phosphate-
P (mg/L)
Potassium (mg/L)
BOD 5-Day (mg/L)
BOD 10-Day (mg/L)
12/28/2000 <2 32 0.3 11.0 100 7.7 16.01/25/2001 NA NA 5.9 4.7 68 8.3 16.42/22/2001 3.9 9.2 NA 2.9 56 8.7 17.23/29/2001 <2 NA 12.0 5.1 66 7.7 15.94/26/2001 4.2 <2 0.2 <1 3.9 2.1 3.85/31/2001 3.9 <2 0.2 <1 4.0 2.9 5.16/28/2001 5.7 <2 0.2 <1 4.3 2.3 4.48/30/2001 5.0 <2 0.2 <1 3.09/27/2001 9.9 <2 <0.1 <1 2.7
10/25/2001 9.4 <2 0.2 <1 6.011/29/2001 NA NA NA 0.1 NA 3.4 5.212/27/2001 NA NA 0.3 0.1 3.6 2.8 4.81/31/2002 NA 1.3 0.2 0.1 NA 3.1 5.22/28/2002 NA NA 0.2 NA 5.5 4.9 7.93/28/2002 NA 1.1 0.4 0.3 5.6 2.8 4.84/24/2002 NA NA 0.3 0.2 4.0 6.3 10.05/30/2002 NA NA NA 0.2 3.3 3.6 6.16/20/2002 INA INA INA INA INA8/29/2002 NA 0.8 NA 0.1 3.1 2.3 3.69/26/2002 NA 0.9 0.2 0.1 4.2 3.5 5.1
10/31/2002 NA 1.0 0.1 <0.03 2.4 7.5 11.411/21/2002 NA 0.8 0.1 0.1 5.0 4.1 6.112/19/2002 NA 1.6 0.2 0.1 4.4 5.0 6.91/30/2003 NA 2.0 NA 0.1 3.4 8.6 17.0
C2: 535MER576 – Turner Slough at Fourth Ave continued…
DateNitrate (mg/L)
Nitrate-N (mg/L)
TKN (mg/L)
Ammonia-N (mg/L)
Phosphorus (mg/L)
Ortho-phosphate-
P (mg/L)
Potassium (mg/L)
BOD 5-Day (mg/L)
BOD 10-Day (mg/L)
Count 9 NA 16 NA 18 22 21 20 20Min 1.0 NA 0.8 NA 0.1 0.02 2.4 2.1 3.6Max 9.9 NA 32 NA 12.0 11.0 100 8.7 17.2Mean 4.9 NA 3.5 NA 1.2 1.3 17 4.9 8.6Geo Mean 3.8 NA 1.5 NA 0.3 0.3 6.8 4.3 7.4Median 4.2 NA 1.0 NA 0.2 0.3 4.2 3.9 6.1Quartile 1 3.9 NA 1.0 NA 0.2 0.1 3.4 2.9 5.0Quartile 3 5.7 NA 1.4 NA 0.3 0.5 5.6 7.6 12.5NOTE: For values reported as < (less than), half the detection limit was used.
NA = Data not applicableINA = Site was inaccessibleDRY = Site had no flow
19
C2: 535MER576 – Turner Slough at Fourth Ave continued…
DateHardness
(mg/L)
Total Arsenic (ug/L)
Total Cadmium
(ug/L)
Total Chromium
(ug/L)
Total Copper (ug/L)
Total Lead (ug/L)
Total Nickel (ug/L)
Total Zinc (ug/L)
Total Mercury (ug/L)
12/28/2000 190 <1 5.9 <5 5.5 201/25/2001 140 <1 6.2 <5 <5 122/22/2001 160 <1 4.2 <5 <5 103/29/2001 130 1.1 3.3 <5 <5 164/26/2001 55 1.4 5.1 <5 <5 4.95/31/2001 60 5.4 7.4 <5 5.2 116/28/2001 74 2.6 <1 4.1 6.1 <5 <5 9.1 <0.27/26/2001 NA NA 4.6 4.9 <5 <5 NA NA8/30/2001 64 <2 <1 2.1 3.1 <5 <5 5.59/27/2001 65 <4 <0.1 2.1 4 <5 <5 4.5 <0.2
10/25/2001 97 <4 <0.1 <1 1.9 <5 <5 <2 NA11/29/2001 59 5.1 <0.1 5.2 5.8 <5 <5 12 <0.212/27/2001 86 4.5 <0.1 7.8 10 <5 6.8 16 <0.22/28/2002 85 <4.0 <0.1 2.4 5.1 <5.0 <5.0 9 <0.23/28/2002 87 <4.0 <0.1 3.6 5.1 <5.0 NA 14 <0.24/24/2002 66 <4.0 <0.1 <1.0 2.2 <5.0 <5.0 <2.0 <0.25/30/2002 58 <4.0 <0.1 2.6 5.6 <5.0 <5.0 6.2 <0.26/20/2002 INA INA INA INA INA INA INA INA9/26/2002 72 <4.0 <0.1 6.1 8.1 <5.0 5.9 15 <0.2
10/31/2002 63 <4.0 <0.1 4.6 6.1 <5.0 <5.0 9.3 <0.211/21/2002 84 <4.0 <0.1 9.0 12 <5.0 7.4 19 <0.23/27/2003 94 4.3 <0.1 6.3 7.5 <5.0 5.7 13 <0.24/24/2003 67 <4.0 <0.1 5.7 7.8 <5.0 5.4 11 <0.25/29/2003 49 <4.0 <0.1 3.7 6.9 <5.0 <5.0 9.9 <0.26/26/2003 51 <4.0 <0.1 3.7 4.9 <5.0 <5.0 8.9 NA
20
C2: 535MER576 – Turner Slough at Fourth Ave continued…
DateHardness
(mg/L)
Total Arsenic (ug/L)
Total Cadmium
(ug/L)
Total Chromium
(ug/L)
Total Copper (ug/L)
Total Lead (ug/L)
Total Nickel (ug/L)
Total Zinc (ug/L)
Total Mercury (ug/L)
Count 23 17 17 24 24 24 23 23 14Min 49 1.0 0.1 0.5 1.9 2.5 2.5 1.0 0.1Max 190 5.1 0.5 9.0 12 2.5 7.4 20.0 0.1Mean 85 2.4 0.1 3.5 5.8 2.5 3.6 10.4 0.1Geo Mean 79 2.3 0.1 2.5 5.3 2.5 3.3 8.5 0.1Median 72 2.0 0.1 3.7 5.7 2.5 2.5 10.0 0.1Quartile 1 62 2.0 0.1 1.3 4.7 2.5 2.5 7.6 0.1Quartile 3 91 2.0 0.1 5.3 7.0 2.5 5.3 13.5 0.1NOTE: For values reported as < (less than), half the detection limit was used.
NA = Data not applicableINA = Site was inaccessibleDRY = Site had no flow
21
C2: 535MER576 – Turner Slough at Fourth Ave continued…
DateHardness
(mg/L)
Dissolved Arsenic (ug/L)
Dissolved Cadmium
(ug/L)
Dissolved Chromium
(ug/L)
Dissolved Copper (ug/L)
Dissolved Lead (ug/L)
Dissolved Nickel (ug/L)
Dissolved Zinc
(ug/L)
Dissolved Mercury (ug/L)
12/28/2000 190 <1 2.5 <5 5.1 9.41/25/2001 140 <1 3.4 <5 5.1 7.02/22/2001 160 <1 2.3 <5 <5 5.63/29/2001 130 <1 2.6 <5 <5 124/26/2001 55 <1 2.2 <5 <5 3.75/31/2001 60 <1 1.9 <5 <5 <26/28/2001 74 <2 <1 <1 <1 <5 <5 2.1 <0.27/26/2001 NA NA NA NA NA NA NA NA8/30/2001 64 <2 <1 <1 1.2 <5 <5 <29/27/2001 65 <4 <0.1 <1 1.6 <5 <5 <2 <0.2
10/25/2001 97 <4 <0.1 <1 1.8 <5 <5 <2 NA11/29/2001 59 <4 <0.1 <1 1.8 <5 <5 5.1 <0.212/27/2001 86 <4 <0.1 <1 2.5 <5 <5 2.9 <0.22/28/2002 85 <4.0 <0.1 <1.0 3.1 <5.0 <5.0 5.5 <0.23/28/2002 87 <4.0 <0.1 <1.0 2.5 <5.0 <5.0 7.6 <0.24/24/2002 66 <4.0 <0.1 <1.0 2.4 <5.0 <5.0 <2.0 <0.25/30/2002 58 <4.0 <0.1 <1.0 2.8 <5.0 <5.0 2.8 <0.26/20/2002 INA INA INA INA INA INA INA INA9/26/2002 72 <4.0 <0.1 <1.0 2.3 <5.0 <5.0 2.3 <0.2
10/31/2002 63 <4.0 <0.1 <1.0 1.3 <5.0 <5.0 <2.0 <0.211/21/2002 84 <4.0 <0.1 <1.0 1.7 <5.0 <5.0 2.2 <0.2
22
C2: 535MER576 – Turner Slough at Fourth Ave continued…
DateHardness
(mg/L)
Dissolved Arsenic (ug/L)
Dissolved Cadmium
(ug/L)
Dissolved Chromium
(ug/L)
Dissolved Copper (ug/L)
Dissolved Lead (ug/L)
Dissolved Nickel (ug/L)
Dissolved Zinc
(ug/L)
Dissolved Mercury (ug/L)
Count 19 13 13 19 19 19 19 19 11Min 55 1.0 0.1 0.5 0.5 2.5 2.5 1.0 0.1Max 190 2.0 0.5 0.5 3.4 2.5 5.1 12.0 0.1Mean 89 1.8 0.1 0.5 2.1 2.5 2.8 3.9 0.1Geo Mean 83 1.8 0.1 0.5 2 2.5 2.7 2.8 0.1Median 74 2.0 0.1 0.5 2.3 2.5 2.5 2.8 0.1Quartile 1 64 2.0 0.1 0.5 1.8 2.5 2.5 1.0 0.1Quartile 3 92 2.0 0.1 0.5 2.5 2.5 2.5 5.6 0.1NOTE: For values reported as < (less than), half the detection limit was used.
NA = Data not applicableINA = Site was inaccessibleDRY = Site had no flow
23
C2: 535MER576 – Turner Slough at Fourth Ave continued…
DateChloride (mg/L)
Sulfate (mg/L)
Calcium (mg/L)
Magnesium (mg/L)
TDS (mg/L)
Carbonate (mg/L)
Bicarbonate (mg/L)
Total Alkalinity
(mg/L)Sodium (mg/L)
12/28/2000 260 89 41 21 2000 <1 1290 1100 5001/25/2001 200 82 31 14 1400 23 970 830 4802/22/2001 140 47 38 15 870 7 450 370 2003/29/2001 140 34 30 13 840 <1 460 380 2004/26/2001 7 8 13 6 160 <1 56 56 115/31/2001 5 11 14 6 130 <1 60 60 136/28/2001 7 11 17 8 150 <1.0 110 89 218/30/2001 5 10 15 6 120 <1 93 76 149/27/2001 12 12 16 6 140 <1 74 61 16
10/25/2001 10 14 23 9 NA <1 140 110 2311/29/2001 6 8 14 6 200 <1 94 77 1612/27/2001 10 13 21 8 190 <1 150 120 321/31/2002 13 20 20 8 NA <1 NA NA 442/28/2002 85 110 20 9 180 <1.0 150 120 423/28/2002 18 21 19 9 NA <1.0 110 89 264/24/2002 7 13 16 7 NA <1.0 83 68 135/30/2002 5 10 14 6 92 <1.0 73 60 119/26/2002 8 13 16 8 NA <1.0 84 69 16
10/31/2002 8 14 15 6 130 <1.0 85 70 1811/21/2002 9 12 20 9 170 <1.0 120 100 223/27/2003 23 94/24/2003 6 8 15 75/29/2003 6 6 12 96/26/2003 14 9 12 5
24
25
C2: 535MER576 – Turner Slough at Fourth Ave continued…
DateChloride (mg/L)
Sulfate (mg/L)
Calcium (mg/L)
Magnesium (mg/L)
TDS (mg/L)
Carbonate (mg/L)
Bicarbonate (mg/L)
Total Alkalinity
(mg/L)Sodium (mg/L)
Count 23 23 24 24 15 20 19 19 20Min 5 6 12 5 92 0.5 56 56 11Max 260 110 41 21 2000 23 1290 1100 500Mean 43 25 20 9 450 2.0 250 210 86Geo Mean 15 17 19 8 260 0.7 150 120 34Median 9 13 17 8 170 0.5 110 89 22Quartile 1 7 10 15 6 140 0.5 84 69 16Quartile 3 16 21 22 9 520 0.5 150 120 43NOTE: For values reported as < (less than), half the detection limit was used.
NA = Data not applicableINA = Site was inaccessibleDRY = Site had no flow
C2: 535MER576 – Turner Slough at Fourth Ave continued…
Date Result Control Result Control
Result (million/m
l)
Control (million/
ml) MDD(%)11/23/2004 100 100 100 10012/29/2004 100 97.5 100 1001/27/2005 90 100 100 1002/24/2005 85 100 100 1003/29/2005 100 100 100 1004/28/2005 N/A N/A 95 1005/26/2005 95 97.5 100 1006/30/2005 92.5 100 100 1007/28/2005 100 97.5 100 1008/25/2005 97.5 100 90 1009/29/2005 97.5 100 100 100
Count 10 10 11 11 N/A N/A N/A
* Significantly reduced from the lab control.** Significantly greater than the lab control.^ Fish were from a "forced hatch," duplicate failed QA.1 Duplicate sample for the set was low - 77% recovery.
3 Samples qualified, but duplicate sample recovery for the set was high - 126% (53.8%/42.5%)NA = Data not applicableINA = Site was inaccessibleDRY = Site had no flow
2 Testing for the Fathead minnow was initiated when samples were approx. 48h old due to untimely shipping of fish by fish supplier.
96h Acute Fathead Minnow
(% Survival)
48h Acute Ceriodaphnia Dubia
(% Survival) Algae Cell Growth
26
C3: 535STC501 – TID 5 Harding Drain @ Carpenter Road Station Code:535STC501
Location: Latitude 37.46444, Longitude -121.03028
Date TimeTemp (ºC)
Field SC (umhos) pH
Dissolved Oxygen (mg/L)
Turbidity (ntu)
10/26/2000 2:05 PM 15.9 258 7.311/29/2000 11:10 AM 12.6 1100 7.012/27/2000 10:00 AM 10.5 921 7.21/24/2001 9:20 AM 12.0 1200 7.32/10/2001 10:40 AM 11.4 1030 7.22/11/2001 1:30 AM 10.8 1020 7.72/11/2001 1:30 AM 10.8 1020 7.72/21/2001 10:20 AM 15.7 875 7.53/28/2001 1:10 PM 21.1 517 7.74/25/2001 10:44 AM 22.0 518 7.65/30/2001 1:00 PM 26.2 819 7.16/5/2001 9:46 AM 20.0 624 7.6 6.16/19/2001 10:55 AM 22.5 557 7.8 7.96/27/2001 11:29 AM 21.4 486 7.7 8.77/25/2001 12:24 PM 23.6 536 7.7 8.98/29/2001 12:46 PM 23.0 487 7.8 9.99/26/2001 11:13 AM 20.4 789 7.5 5.2
10/24/2001 12:49 PM 16.3 552 7.6 8.011/28/2001 11:30 AM 10.6 1460 7.8 9.112/26/2001 11:05 AM 14.2 1160 7.7 9.41/30/2002 11:51 AM 12.3 1180 7.8 10.72/27/2002 10:50 AM 17.4 1150 7.7 9.53/27/2002 10:27 AM 16.8 582 7.5 8.44/30/2002 11:27 AM 18.1 649 7.6 8.85/29/2002 11:20 AM 23.3 605 7.7 8.56/19/2002 11:04 AM 22.7 649 7.8 9.37/30/2002 10:07 AM 22.0 713 7.8 7.4 0.78/28/2002 12:00 PM 25.4 647 8.1 NA9/25/2002 12:31 PM 22.8 806 7.8 9.7
10/15/2002 9:34 AM 18.2 378 7.5 8.9 NA10/30/2002 10:57 AM 17.4 1090 7.6 10.711/20/2002 10:48 AM 17.7 999 7.5 8.112/18/2002 11:02 AM 12.8 693 7.3 8.0 16.21/14/2003 1:52 PM 16.7 1130 7.6 9.4 7.31/22/2003 2:25 PM 15.6 1100 7.8 11.5 14.61/29/2003 11:32 AM 16.2 1080 7.5 8.8 5.12/4/2003 10:04 AM 14.3 1070 7.7 9.6 3.42/20/2003 8:54 AM 13.6 902 7.6 9.4 5.03/6/2003 1:49 PM 19.4 930 7.8 15.3 3.1
27
C3: 535STC501 – TID 5 Harding Drain @ Carpenter Road continued…
Date TimeTemp (ºC)
Field SC (umhos) pH
Dissolved Oxygen (mg/L)
Turbidity (ntu)
3/20/2003 11:27 AM 18.4 851 7.6 8.7 5.73/25/2003 10:04 AM 17.3 585 7.5 8.3 6984/3/2003 9:57 AM 16.7 520 7.3 9.6 29.14/17/2003 12:15 PM 19.1 532 8.0 10.6 9.05/8/2003 10:57 AM 19.3 886 7.3 7.9 16.15/22/2003 1:02 PM 24.6 447 8.5 12.1 10.26/5/2003 12:53 PM 24.7 740 8.4 12.8 6.86/19/2003 12:40 PM 23.2 555 8.0 9.8 5.06/30/2003 12:06 PM 22.5 404 8.3 10.5 7.07/24/2003 11:39 AM 26.4 766 7.6 9.7 70.37/31/2003 12:03 PM 24.9 717 7.6 8.4 6.68/7/2003 11:30 AM 22.2 420 7.7 8.3 3968/21/2003 11:07 AM 23.3 456 7.6 7.6 76.08/28/2003 11:27 AM 24.0 805 7.6 8.5 28.59/11/2003 1:49 PM 26.1 843 8.2 11.3 3.09/25/2003 12:40 PM 22.6 527 8.5 13.5 6.310/9/2003 11:33 AM 20.3 508 8.0 11.0 3.8
10/23/2003 12:42 PM 18.8 430 7.9 11.7 19.611/6/2003 11:50 AM 18.1 1190 7.9 11.2 3.1
11/20/2003 11:30 AM 17.9 974 7.6 9.3 NA1/8/2004 10:17 AM 15.0 1190 7.7 7.7 NA7/29/2004 11:38 AM INA INA INA INA INA8/26/2004 11:55 AM 23.5 583 8.1 9.9 NA9/30/2004 11:55 AM 20.4 581 7.9 10.8 NA
10/28/2004 11:14 AM 14.2 457 7.8 13.711/23/2004 12:10 PM 15.1 1130 7.7 12.412/29/2004 11:29 AM 13.9 816 7.7 10.71/27/2005 1:32 PM 16.1 1190 7.8 13.22/24/2005 11:38 AM 16.9 1140 7.6 8.03/29/2005 2:04 PM 16.6 543 7.6 10.74/28/2005 12:01 PM 18.3 361 7.8 8.75/26/2005 12:57 PM 24.4 588 7.7 10.66/30/2005 12:33 PM 25.8 550 8.0 10.27/28/2005 11:55 AM 25.3 639 7.5 8.68/25/2005 12:19 PM 23.4 454 7.9 10.19/29/2005 12:23 PM 22.1 493 7.6 10.2
28
C3: 535STC501 – TID 5 Harding Drain @ Carpenter Road continued…
Date TimeTemp (ºC)
Field SC (umhos) pH
Dissolved Oxygen (mg/L)
Turbidity (ntu)
Count 74 74 74 62 27Min 10.5 258 7.0 5.2 0.7Max 26.4 1460 8.5 15.3 698Mean 19.0 759 7.7 9.7 53.9Geo Mean 18.4 710 7.7 9.5 11.2Median 18.6 703 7.7 9.5 7.0Quartile 1 16.0 533 7.6 8.5 5.0Quartile 3 22.8 1015 7.8 10.7 17.9NOTE: For values reported as < (less than), half the detection limit was used.
NA = Data not applicableINA = Site was inaccessibleDRY = Site had no flow
29
C3: 535STC501 – TID 5 Harding Drain @ Carpenter Road continued…
DateTSS
(mg/L)TOC
(mg/L)Total Coli
MPNE. coli MPN
10/26/2000 49 3.311/29/2000 NA 2.312/27/2000 <6 2.71/24/2001 13 9.42/10/2001 10 9.92/11/2001 18 9.22/21/2001 11 NA3/28/2001 26 NA4/25/2001 5 3.95/30/2001 8 126/27/2001 8 8.47/25/2001 5.18/29/2001 NA 129/26/2001 NA 16
11/28/2001 NA12/26/2001 9.03/27/2002 NA4/30/2002 NA5/29/2002 4.06/19/2002 NA7/30/2002 >2419.6 169/25/2002 NA
10/15/2002 >2419.6 32810/30/2002 4.211/20/2002 5.81/14/2003 1733 4881/22/2003 >2419.6 2612/4/2003 >2419.6 2382/20/2003 >2419.6 4613/6/2003 >2419.6 4353/20/2003 NA 5.4 >2419.6 1533/25/2003 2.84/3/2003 NA NA >2419.6 4354/17/2003 10 4.3 >2419.6 1795/8/2003 NA 12 >2419.6 11205/22/2003 7 3.1 >2419.6 1966/5/2003 5 8.3 >2419.6 6496/19/2003 7 4.8 >2419.6 3456/30/2003 NA 3.6 >2419.6 2917/31/2003 >2419.6 3658/7/2003 >2419.6 517
30
31
DateTSS
(mg/L)TOC
(mg/L)Total Coli
MPNE. coli MPN
8/21/2003 >2419.6 12038/28/2003 >2419.6 13009/11/2003 >2419.6 8669/25/2003 >2419.6 98010/9/2003 >2419.6 108
10/23/2003 >2419.6 41111/6/2003 >2419.6 345
11/20/2003 >2419.6 931/8/2004 >2419.6 8167/29/2004 INA INA8/26/2004 >2419.6 2859/30/2004 >2419.6 238
10/28/2004 3.9 >2419.6 21411/23/2004 6.3 >2419.6 120312/29/2004 7.4 >2419.6 >2419.61/27/2005 8.0 >2419.6 3612/23/24/25/26/37/28/29/2
CounMin
C3: 535STC501 – TID 5 Harding Drain @ Carpenter Road continued…
4/2005 24 >2419.6 >2419.69/2005 3.6 >2419.6 3658/2005 3.4 >2419.6 3876/2005 5.8 >2419.6 15530/2005 NA >2419.6 2488/2005 NA >2419.6 5485/2005 5.4 >2419.6 11209/2005 5.2 >2419.6 517
t 14 34 40 403 2.3 1733 1649 24 2420 2420
n 13 6.9 NA NA Mean 10 5.9 2400 422ian 9 5.4 2420 399rtile 1 7 3.9 2420 258rtile
MaxMeaGeoMedQuaQua 3 13 8.9 2420 829
E: For values reported as < (less than), half the detection limit was used For values reported as > (greater than), 2420 was used
Data not applicable Site was inaccessible
= Site had no flow
NOT
NA =INA =DRY
C3: 535STC501 – TID 5 Harding Drain @ Carpenter Road continued…
DateNitrate (mg/L)
Nitrate-N (mg/L)
TKN (mg/L)
Ammonia-N (mg/L)
Phosphorus (mg/L)
Ortho-phosphate-
P (mg/L)
Potassium (mg/L)
BOD 5-Day (mg/L)
BOD 10-Day (mg/L)
10/26/2000 14 <2 NA <1 3.6 4.4 5.511/29/2000 41 NA 0.3 2.2 14 7.3 15.612/27/2000 9.9 13 0.2 3.2 18 8.1 16.51/24/2001 15 16 1.7 4.4 21 8.2 16.62/10/2001 27 <2 0.4 1.2 15 7.5 14.82/11/2001 24 7.0 1.0 <1 162/21/2001 19 10 1.5 2.7 15 8.0 16.43/28/2001 15 3.7 1.1 <1 9.1 7.7 15.94/25/2001 25 2.6 1.6 1.4 6.9 5.4 8.55/30/2001 19 9.5 1.9 2.3 16 7.8 16.26/27/2001 15 2.9 1.6 1.8 7.7 4.6 8.48/29/2001 23 <2 0.8 <1 NA9/26/2001 44 7.9 1.4 <1 14
10/24/2001 32 <2 0.8 <1 6.6 5.1 8.511/28/2001 NA 0.1 NA <0.03 1.2 3.6 8.812/26/2001 NA 8.8 2.1 2.0 11 7.3 15.51/30/2002 NA 5.2 0.8 0.6 14 7.4 15.92/27/2002 NA 11 1.6 1.4 NA 6.1 14.63/27/2002 NA 4.2 NA 0.5 4.7 7.0 15.54/30/2002 NA NA 2.3 2.0 NA 7.6 14.25/29/2002 NA 2.4 NA 1.6 7.3 4.6 8.26/19/2002 NA 2.5 1.8 NA 9.9 6.3 12.28/28/2002 NA 2.2 0.8 0.7 8.5 4.9 8.09/25/2002 NA NA 1.3 1.3 6.8 1.7 3.5
10/30/2002 NA NA 3.2 0.1 8.7 1.0 3.311/20/2002 NA 6.6 4.2 2.6 1512/18/2002 NA 4.0 3.2 3.2 9.7 6.4 8.71/29/2003 NA NA 7.5 3.7 11 3.6 7.2
32
C3: 535STC501 – TID 5 Harding Drain @ Carpenter Road continued…
DateNitrate (mg/L)
Nitrate-N (mg/L)
TKN (mg/L)
Ammonia-N (mg/L)
Phosphorus (mg/L)
Ortho-phosphate-
P (mg/L)
Potassium (mg/L)
BOD 5-Day (mg/L)
BOD 10-Day (mg/L)
Count 14 NA 23 NA 24 27 25 24 24Min 9.9 NA 0.1 NA 0.2 0.02 1.2 1.0 3.3Max 44 NA 16 NA 7.5 4.4 21 8.2 16.6Mean 23 NA 5.4 NA 1.8 1.6 10.8 5.9 11.6Geo Mean 21 NA 3.4 NA 1.3 1.0 9.5 5.4 11Median 21 NA 4.0 NA 1.6 1.4 9.9 6.4 13.2Quartile 1 15 NA 2.3 NA 0.8 0.5 7.3 4.6 8.4Quartile 3 27 NA 8.4 NA 2.0 2.3 15.0 7.5 15.7NOTE: For values reported as < (less than), half the detection limit was used.
NA = Data not applicableINA = Site was inaccessibleDRY = Site had no flow
33
C3: 535STC501 – TID 5 Harding Drain @ Carpenter Road continued…
DateHardness
(mg/L)
Total Arsenic (ug/L)
Total Cadmium
(ug/L)
Total Chromium
(ug/L)
Total Copper (ug/L)
Total Lead (ug/L)
Total Nickel (ug/L)
Total Zinc (ug/L)
Total Mercury (ug/L)
10/26/2000 64 1.3 2.5 <5 <5 1411/29/2000 220 1.3 1.9 <5 <5 1812/27/2000 130 2.1 2.8 <5 <5 191/24/2001 160 2.0 4.0 <5 <5 222/10/2001 180 1.8 4.7 <5 <5 172/11/2001 180 1.9 5.1 <5 <5 232/21/2001 160 1.8 3.8 <5 <5 193/28/2001 99 1.3 3.9 <5 <5 114/25/2001 120 <1 1.8 <5 <5 5.65/30/2001 150 <1 2.0 <5 <5 137/25/2001 100 6.7 1.7 <5 <5 6.78/29/2001 NA 2.6 <1 <1 1.5 <5 <5 5.59/26/2001 200 5.7 0.2 13 26 10 12 88 <0.2
10/24/2001 130 <4.0 <0.1 NA <1.0 <5.0 <5.0 9.4 <0.211/28/2001 240 8.8 <0.1 <1.0 2.2 <5.0 <5.0 18 <0.212/26/2001 210 8.0 <0.1 1.5 <1 <5 <5 21 <0.21/30/2002 270 5.3 <0.1 <1 2.5 <5 <5 11 <0.23/27/2002 130 <4.0 <0.1 1.0 3.4 <5.0 <5.0 13 <0.24/30/2002 130 4.4 <0.1 <1.0 2.0 <5.0 <5.0 12 <0.25/29/2002 140 4.4 <0.1 2.3 NA <5.0 <5.0 22 <0.26/19/2002 160 4.4 <0.1 <1.0 2.6 <5.0 <5.0 8.9 <0.29/25/2002 210 8.1 <0.1 1.2 NA <5.0 <5.0 10 <0.2
11/20/2002 200 5.5 <0.1 1.8 3.7 <5.0 NA NA <0.23/20/2003 NA 5.6 <0.1 1.6 2.8 <5.0 <5.0 24 <0.23/25/2003 140 7.5 0.2 16 30 14 13 140 <0.24/17/2003 100 <4.0 <0.1 <1.0 1.9 <5.0 <5.0 13 <0.25/22/2003 110 <4.0 <0.1 <1.0 2.2 <5.0 <5.0 9.1 <0.26/19/2003 120 4.2 <0.1 <1.0 2.7 <5.0 <5.0 13 <0.26/30/2003 90 <4.0 <0.1 <1.0 2.2 <5.0 <5.0 6.9 <0.2
34
C3: 535STC501 – TID 5 Harding Drain @ Carpenter Road continued…
DateHardness
(mg/L)
Total Arsenic (ug/L)
Total Cadmium
(ug/L)
Total Chromium
(ug/L)
Total Copper (ug/L)
Total Lead (ug/L)
Total Nickel (ug/L)
Total Zinc (ug/L)
Total Mercury (ug/L)
Count 27 18 18 28 27 29 28 28 17Min 64 2.0 0.1 0.5 0.5 2.5 2.5 5.5 0.1Max 270 8.8 0.5 16.0 30 14.0 13 140 0.1Mean 150 4.7 0.1 2.3 4.5 3.2 3.2 21.2 0.1Geo Mean 150 4.1 0.1 1.2 2.8 2.8 2.8 15.0 0.1Median 140 4.4 0.1 1.3 2.5 2.5 2.5 13.0 0.1Quartile 1 120 2.2 0.1 0.5 2.0 2.5 2.5 9.9 0.1Quartile 3 190 5.7 0.1 1.8 3.8 2.5 2.5 19.5 0.1NOTE: For values reported as < (less than), half the detection limit was used.
NA = Data not applicableINA = Site was inaccessibleDRY = Site had no flow
35
C3: 535STC501 – TID 5 Harding Drain @ Carpenter Road continued…
DateHardness
(mg/L)
Dissolved Arsenic (ug/L)
Dissolved Cadmium
(ug/L)
Dissolved Chromium
(ug/L)
Dissolved Copper (ug/L)
Dissolved Lead (ug/L)
Dissolved Nickel (ug/L)
Dissolved Zinc
(ug/L)
Dissolved Mercury (ug/L)
10/26/2000 64 <1 <1 <5 <5 2.511/29/2000 220 <1 1.6 <5 <5 1212/27/2000 130 2.0 2.7 <5 <5 191/24/2001 160 1.7 2.4 <5 <5 202/10/2001 180 1.2 3.3 <5 <5 142/11/2001 180 1.3 2.8 <5 <5 182/21/2001 160 1.4 2.7 <5 <5 153/28/2001 99 <1 1.9 <5 <5 6.64/25/2001 120 <1 1.2 <5 <5 6.85/30/2001 150 <1 1.3 <5 <5 148/29/2001 NA 2.6 <1 <1 <1 <5 <5 3.99/26/2001 200 <4 <0.1 <1 1.9 <5 <5 9.4 <0.2
10/24/2001 130 <4.0 <0.1 NA 1.4 <5.0 <5.0 8.0 <0.211/28/2001 240 7.7 <0.1 <1.0 2.1 <5.0 <5.0 NA <0.212/26/2001 210 8.1 <0.1 <1 2.6 <5 <5 17 <0.21/30/2002 270 <4 <0.1 <1 1.4 <5 <5 6.4 <0.23/27/2002 130 4.8 <0.1 <1.0 1.5 <5.0 <5.0 8.9 <0.24/30/2002 130 5.0 <0.1 <1.0 1.2 <5.0 <5.0 13 <0.25/29/2002 140 <4.0 <0.1 <1.0 <1.0 <5.0 <5.0 6.0 <0.26/19/2002 160 <4.0 <0.1 <1.0 1.5 <5.0 <5.0 5.2 <0.29/25/2002 210 6.9 <0.1 <1.0 NA <5.0 <5.0 5.2 <0.2
11/20/2002 200 6.9 <0.1 1.4 2.5 <5.0 <5.0 19 <0.2
Count 21 12 12 21 21 22 22 21 11Min 64 2.0 0.1 0.5 0.5 2.5 2.5 2.5 0.1Max 270 8.1 0.5 2.0 3.3 2.5 2.5 20.0 0.1Mean 166 4.3 0.1 0.8 1.8 2.5 2.5 10.9 0.1Geo Mean 158 3.7 0.1 0.7 1.6 2.5 2.5 9.5 0.1Median 160 3.7 0.1 0.5 1.6 2.5 2.5 9.4 0.1Quartile 1 130 2.0 0.1 0.5 1.3 2.5 2.5 6.4 0.1Quartile 3 200 6.9 0.1 1.2 2.5 2.5 2.5 15.0 0.1NOTE: For values reported as < (less than), half the detection limit was used.
NA = Data not applicableINA = Site was inaccessibleDRY = Site had no flow
36
C3: 535STC501 – TID 5 Harding Drain @ Carpenter Road continued…
DateChloride (mg/L)
Sulfate (mg/L)
Calcium (mg/L)
Magnesium (mg/L)
TDS (mg/L)
Carbonate (mg/L)
Bicarbonate (mg/L)
Total Alkalinity
(mg/L)Sodium (mg/L)
10/26/2000 20 12 17 5 160 <1 80 60 2211/29/2000 140 45 63 15 660 <1 290 230 13012/27/2000 93 60 38 9 520 <1 280 230 1101/24/2001 130 74 47 11 670 <1 350 290 1602/10/2001 110 56 52 13 530 <1 300 250 1302/11/2001 120 61 51 12 580 <1 290 240 1302/21/2001 83 52 44 11 490 <1 260 220 1103/28/2001 67 22 27 8 290 <1 130 110 564/25/2001 43 NA 33 10 NA <1 130 130 495/30/2001 83 50 42 10 NA <1 200 200 916/27/2001 57 24 29 8 280 <1 140 120 538/29/2001 47 NA NA NA 280 <1.0 140 120 509/26/2001 NA NA 53 17 NA <1 240 200 89
10/24/2001 51 26 35 10 340 <1 180 140 6411/28/2001 250 59 68 17 760 <1 560 460 21012/26/2001 160 51 59 15 630 <1 300 240 1501/30/2002 140 49 76 18 700 <1 320 260 1402/27/2002 130 81 52 14 NA <1.0 317 260 1703/27/2002 64 29 36 9 330 <1.0 150 130 634/30/2002 74 35 35 10 NA <1.0 160 130 795/29/2002 65 29 38 11 NA <1.0 160 140 736/19/2002 71 30 43 12 NA <1.0 200 160 789/25/2002 70 40 56 16 NA <1.0 250 200 92
10/30/2002 120 50 69 18 690 <1.0 290 240 14011/20/2002 99 61 52 17 610 <1.0 280 230 1203/20/2003 NA NA NA NA3/25/2003 64 45 34 144/17/2003 59 32 28 85/22/2003 40 26 28 96/19/2003 50 38 32 96/30/2003 46 18 25 7
37
38
C3: 535STC501 – TID 5 Harding Drain @ Carpenter Road continued…
DateChloride (mg/L)
Sulfate (mg/L)
Calcium (mg/L)
Magnesium (mg/L)
TDS (mg/L)
Carbonate (mg/L)
Bicarbonate (mg/L)
Total Alkalinity
(mg/L)Sodium (mg/L)
Count 29 27 29 29 17 25 25 25 25Min 20 12 17 5 160 0.5 80 60 22Max 250 81 76 18 760 0.5 560 460 210Mean 88 43 44 12 500 0.5 240 200 102Geo Mean 77 39 41 11 460 0.5 221 184 92Median 71 45 42 11 530 0.5 250 200 92Quartile 1 57 29 33 9 330 0.5 160 130 64Quartile 3 120 54 52 15 660 0.5 290 240 130NOTE: For values reported as < (less than), half the detection limit was used.
NA = Data not applicableINA = Site was inaccessibleDRY = Site had no flow
C3: 535STC501 – TID 5 Harding Drain @ Carpenter Road continued…
Date Result Control Result Control
Result (million/m
l)
Control (million/
ml)MDD (%)
10/26/2000 100 100 NA NA06/19/2001 100 100 100 9010/24/2001 100 100 100 10011/28/2001 NA NA 100 10012/26/2001 95 100 90 10001/30/2002 100 100 100 9002/27/2002 95 100 100 10004/30/2002 100 100 100 10005/29/2002 100 100 100 10006/19/2002 100 100 100 10008/28/2002 100 100 NA NA09/25/2002 85 100 100 10010/30/2002 95 100 100 10011/20/2002 95 100 100 10012/18/2002 95 90 100 100 0.794* 3.03 NA01/29/2003 100 100 100 100 0.368* 3.28 NA04/17/2003 100 100 100 100 3.61** 1.84 4705/22/2003 90 100 100 100 4.22** 2.08 91
11/23/2004 100 100 90 10012/29/2005 100 97.5 100 10001/27/2005 92.5 100 92.5 10002/24/2005 97.5 100 100 10003/29/2005 97.5 100 100 10004/28/2005 N/A N/A 100 10005/26/2005 97.5 97.5 100 10006/30/2005 100 100 100 10007/28/2005 100 97.5 100 10008/25/2005 100 100 100 10009/29/2005 100 100 100 100
Count 27 27 27 27 4 4 2
* Significantly reduced from the lab control.** Significantly greater than the lab control.^ Fish were from a "forced hatch," duplicate failed QA.1 Duplicate sample for the set was low - 77% recovery.
3 Samples qualified, but duplicate sample recovery for the set was high - 126% (53.8%/42.5%)NA = Data not applicableINA = Site was inaccessibleDRY = Site had no flow
2 Testing for the Fathead minnow was initiated when samples were approx. 48h old due to untimely shipping of fish by fish supplier.
96h Acute Fathead Minnow
(% Survival)
48h Acute Ceriodaphnia Dubia
(% Survival) Algae Cell Growth
39
C4: 535STC513 – Tuolumne River at Shiloh Fishing Access Station Code:535STC513
Location: Latitude 37.60306, Longitude -121.13167
Date TimeTemp (ºC)
Field SC (umhos) pH
Dissolved Oxygen (mg/L)
Turbidity (ntu)
10/26/2000 10:55 AM 16.0 175 7.611/29/2000 9:45 AM 10.7 197 7.812/27/2000 11:40 AM 9.1 196 8.21/24/2001 11:00 AM 10.3 207 8.02/7/2001 12:30 PM 11.3 208 8.22/10/2001 12:20 PM 10.0 190 8.02/11/2001 2:20 AM 9.3 160 7.72/21/2001 12:45 PM 13.8 86 9.03/13/2001 12:45 PM 16.2 107 8.23/28/2001 11:15 AM 20.0 197 6.74/18/2001 1:09 PM 20.9 215 8.24/25/2001 9:18 AM 20.4 121 7.25/15/2001 1:05 PM 20.7 95 8.05/30/2001 10:40 AM 23.6 283 7.56/6/2001 9:05 AM 21.1 278 6.7 6.86/13/2001 11:10 AM 22.2 345 8.2 8.16/20/2001 8:50 AM 24.8 396 7.4 7.86/27/2001 9:50 AM 22.8 313 7.9 7.37/25/2001 10:24 AM 25.6 282 8.0 10.18/14/2001 12:20 PM 24.5 236 8.1 9.48/29/2001 10:40 AM 24.5 259 7.5 9.09/26/2001 9:50 AM 20.6 240 7.5 9.6
10/24/2001 10:42 AM 15.6 182 7.9 9.711/28/2001 9:50 AM 10.7 253 8.6 10.712/26/2001 10:08 AM 11.0 266 7.8 10.21/30/2002 10:09 AM 7.7 198 8.0 12.32/27/2002 9:35 AM 15.0 278 7.7 11.03/27/2002 9:15 AM 15.9 235 8.3 9.74/30/2002 10:09 AM 13.5 62 7.4 11.15/29/2002 9:38 AM 22.6 234 7.5 8.46/19/2002 9:20 AM 23.4 300 7.7 7.67/31/2002 8:04 AM 23.9 288 7.0 6.9 2.18/28/2002 10:20 AM 24.1 264 8.1 NA9/25/2002 10:32 AM 22.1 260 7.7 8.4
10/15/2002 10:58 AM 17.6 199 7.8 8.8 NA10/30/2002 9:21 AM 13.9 184 7.5 9.411/20/2002 9:39 AM 12.8 248 7.6 10.312/18/2002 9:11 AM 10.3 217 7.6 8.4 94.5
40
C4: 535STC513 – Tuolumne River at Shiloh Fishing Access continued…
Date TimeTemp (ºC)
Field SC (umhos) pH
Dissolved Oxygen (mg/L)
Turbidity (ntu)
1/14/2003 1:19 PM 12.7 229 7.6 10.0 9.81/22/2003 3:06 PM 11.8 260 8.2 11.2 5.81/29/2003 9:59 AM 12.7 228 7.7 10.2 9.92/4/2003 9:30 AM 10.7 240 8.1 11.1 3.22/19/2003 10:40 AM 12.4 236 7.9 10.5 7.03/5/2003 10:12 AM 13.2 240 7.7 11.0 2.63/18/2003 11:38 AM 15.4 216 7.9 9.0 46.83/25/2003 9:06 AM 16.2 217 8.0 10.1 5.74/2/2003 11:40 AM 16.5 205 8.2 9.7 18.54/16/2003 11:16 AM 13.9 58 7.5 10.1 15.85/6/2003 11:59 AM 17.3 114 8.2 9.8 8.85/21/2003 11:42 AM 22.0 207 7.6 9.2 5.66/4/2003 11:05 AM 24.0 168 7.6 8.1 26.36/17/2003 11:08 AM 24.4 182 7.6 9.1 7.26/30/2003 12:49 PM 25.8 158 7.9 8.1 6.97/23/2003 10:03 AM 26.4 163 7.6 7.8 4.18/5/2003 9:54 AM 23.1 151 7.6 9.6 4.28/20/2003 10:13 AM 23.8 164 7.7 8.1 5.09/9/2003 10:02 AM 20.5 173 7.7 8.3 6.09/22/2003 10:17 AM 21.5 165 7.6 8.5 4.910/7/2003 10:43 AM 19.6 173 8.0 8.9 12.4
10/21/2003 11:58 AM 17.3 106 7.7 8.7 4.811/4/2003 10:53 AM 12.5 185 7.8 10.9 10.0
11/17/2003 10:47 AM 14.1 205 7.9 10.5 3.81/6/2004 9:47 AM 8.1 200 7.7 12.4 13.61/29/2004 12:54 PM 12.3 199 8.0 12.4 12.42/26/2004 12:43 PM 13.0 149 7.9 10.0 NA3/24/2004 1:15 PM 15.2 67 7.8 10.1 NA4/29/2004 1:46 PM 19.1 97 8.2 9.9 8.05/27/2004 1:36 PM 24.5 206 8.3 9.2 7.36/24/2004 1:58 PM 25.9 247 8.2 11.2 NA7/29/2004 12:34 PM 26.4 222 8.5 10.2 NA8/26/2004 1:41 PM 25.7 256 8.2 9.4 NA9/30/2004 12:35 PM 20.9 255 8.2 10.3 NA
10/28/2004 1:15 PM 13.8 76 8.5 9.811/23/2004 12:45 PM 11.5 235 7.9 12.512/29/2004 12:28 PM 11.2 186 7.9 11.51/27/2005 2:51 PM 12.2 289 8.1 11.82/24/2005 12:33 PM 11.9 56 8.3 11.03/29/2005 2:41 PM 12.5 54 7.9 10.44/28/2005 12:38 PM 12.4 51 8.3 11.35/26/2005 1:45 PM 14.9 45 7.8 10.36/30/2005 1:42 PM 16.6 53 7.8 9.77/28/2005 12:26 PM 20.0 81 7.7 9.48/25/2005 1:07 PM 21.8 150 7.7 8.59/29/2005 12:56 PM 20.7 172 7.4 8.3
41
C4: 535STC513 – Tuolumne River at Shiloh Fishing Access continued…
Date TimeTemp (ºC)
Field SC (umhos) pH
Dissolved Oxygen (mg/L)
Turbidity (ntu)
Count 84 84 84 69 30Min 7.7 45 6.7 6.8 2.1Max 26.4 396 9.0 12.5 94.5Mean 17.3 193 7.9 9.7 12.4Geo Mean 16.5 175 7.8 9.6 8.1Median 16.4 200 7.9 9.7 7.1Quartile 1 12.5 160 7.6 8.7 4.9Quartile 3 22.1 240 8.1 10.5 11.8NOTE: For values reported as < (less than), half the detection limit was used.
NA = Data not applicableINA = Site was inaccessibleDRY = Site had no flow
42
C4: 535STC513 – Tuolumne River at Shiloh Fishing Access continued…
DateTSS
(mg/L)TOC
(mg/L)Total Coli
MPNE. coli MPN
10/26/2000 <5 <111/29/2000 NA <112/27/2000 <6 1.01/24/2001 6 1.42/10/2001 6 2.22/11/2001 13 2.12/21/2001 8 NA3/28/2001 <5 NA4/25/2001 14 1.55/30/2001 10 5.36/27/2001 <6 7.07/25/2001 2.38/29/2001 NA 6.59/26/2001 NA 6.6
11/28/2001 NA12/26/2001 2.83/27/2002 NA4/30/2002 NA5/29/2002 2.46/19/2002 NA7/31/2002 >2419.6 158/28/2002 NA9/25/2002 NA
10/15/2002 >2419.6 12210/30/2002 1.411/20/2002 1.212/18/2002 8.71/14/2003 1046 1781/22/2003 602 312/4/2003 291 192/19/2003 921 393/5/2003 285 303/18/2003 9 NA >2419.6 1044/2/2003 7 2.4 >2419.6 6494/16/2003 14 2.7 >2419.6 3455/6/2003 NA 2.4 1011 965/21/2003 NA 2.2 >2419.6 1076/4/2003 32 3.7 >2419.6 5176/17/2003 8 2.5 >2419.6 536/30/2003 6 3.0 >2419.6 787/23/2003 >2419.6 69
43
44
DateTSS
(mg/L)TOC
(mg/L)Total Coli
MPNE. coli MPN
8/5/2003 >2419.6 1798/20/2003 >2419.6 599/9/2003 >2419.6 799/22/2003 >2419.6 14710/7/2003 >2419.6 43
10/21/2003 >2419.6 7111/4/2003 >2419.6 70
11/17/2003 >2419.6 251/6/2004 >2419.6 2061/29/2004 179 82/26/2004 >2419.6 4883/24/2004 1733 544/29/2004 1986 555/27/2004 >2419.6 1026/24/2004 >2419.6 867/29/2004 >2419.6 1058/29/3
10/11/12/1/22/23/24/25/26/37/28/29/2
CounMin
C4: 535STC513 – Tuolumne River at Shiloh Fishing Access continued…
6/2004 >2419.6 230/2004 >2419.6 3928/2004 1.6 >2419.6 48823/2004 1.3 1553 4329/2004 2.0 >2419.6 6137/2005 2.6 >2419.6 4884/2005 2.4 1300 939/2005 2.2 >2419.6 1378/2005 1.9 >2419.6 916/2005 2.0 >2419.6 680/2005 NA 2420 388/2005 NA >2419.6 555/2005 2.1 >2419.6 399/2005 2.2 >2419.6 60
t 16 34 46 463 0.5 179 8
MaxMeaGeo
32 8.7 2420 649n 9 2.7 NA NA Mean 7 2 1843 83ian 8 2.2 2420 75rtile 1 5 1.7 2420 43rtile
MedQuaQua 3 11 2.7 2420 133
E: For values reported as < (less than), half the detection limit was used For values reported as > (greater than), 2420 was used
Data not applicable Site was inaccessible
= Site had no flow
NOT
NA =INA =DRY
C4: 535STC513 – Tuolumne River at Shiloh Fishing Access continued…
DateNitrate (mg/L)
Nitrate-N (mg/L)
TKN (mg/L)
Ammonia-N (mg/L)
Phosphorus (mg/L)
Ortho-phosphate-
P (mg/L)
Potassium (mg/L)
BOD 5-Day (mg/L)
BOD 10-Day (mg/L)
10/26/2000 6.5 <2 <0.1 <1 1.7 0.8 1.011/29/2000 6.8 NA <0.1 <1 1.6 0.2 0.212/27/2000 6.8 2.2 <0.1 <1 1.7 0.3 0.31/24/2001 7.2 <2 <0.1 <1 1.8 0.7 0.92/10/2001 5.9 <2 <0.1 <1 1.8 <0.1 0.82/11/2001 4.7 <2 <0.1 <1 1.62/21/2001 2.5 <2 <0.1 <1 1.1 0.4 0.73/28/2001 6.2 <2 <0.1 <1 1.8 0.8 1.24/25/2001 3.8 <2 0.1 <1 1.6 0.5 0.95/30/2001 8.7 <2 0.2 <1 3.2 0.8 1.26/27/2001 9.3 <2 0.2 <1 4.1 0.6 1.28/29/2001 8.5 <2 0.4 <1 NA9/26/2001 7.6 <2 0.2 <1 3.3
10/24/2001 6.6 <2 <0.1 <1 1.6 0.5 0.611/28/2001 NA 0.3 NA 0.1 6.2 0.3 0.412/26/2001 0.7 1.51/30/2002 0.4 0.82/27/2002 0.5 0.83/27/2002 0.4 0.84/30/2002 0.5 0.95/29/2002 0.5 0.86/19/2002 0.9 1.48/28/2002 0.2 0.89/25/2002 0.8 1.2
10/30/2002 0.3 0.412/18/2002 5.6 8.41/29/2003 0.3 0.6
45
C4: 535STC513 – Tuolumne River at Shiloh Fishing Access continued…
DateNitrate (mg/L)
Nitrate-N (mg/L)
TKN (mg/L)
Ammonia-N (mg/L)
Phosphorus (mg/L)
Ortho-phosphate-
P (mg/L)
Potassium (mg/L)
BOD 5-Day (mg/L)
BOD 10-Day (mg/L)
Count 14 NA 14 NA 14 15 14 24 24Min 2.5 NA 0.3 NA 0.1 0.1 1.1 0.1 0.2Max 9.3 NA 2.2 NA 0.4 0.5 6.2 5.6 8.4Mean 6.5 NA 1 NA 0.1 0.5 2.4 0.7 1.2Geo Mean 6.2 NA 1 NA 0.1 0.4 2.1 0.5 0.8Median 6.7 NA 1 NA 0.1 0.5 1.8 0.5 0.8Quartile 1 6.0 NA 1 NA 0.1 0.5 1.6 0.3 0.7Quartile 3 7.5 NA 1 NA 0.2 0.5 2.9 0.7 1.2NOTE: For values reported as < (less than), half the detection limit was used.
NA = Data not applicableINA = Site was inaccessibleDRY = Site had no flow
46
C4: 535STC513 – Tuolumne River at Shiloh Fishing Access continued…
DateHardness
(mg/L)
Total Arsenic (ug/L)
Total Cadmium
(ug/L)
Total Chromium
(ug/L)
Total Copper (ug/L)
Total Lead (ug/L)
Total Nickel (ug/L)
Total Zinc (ug/L)
Total Mercury (ug/L)
10/26/2000 <1 <1 <5 <511/29/2000 61 <1 <1 <5 <5 <212/27/2000 62 <1 <1 <5 <5 2.11/24/2001 64 <1 1.3 <5 <5 <22/10/2001 63 <1 1.4 <5 <5 22/11/2001 54 <1 1.7 <5 <5 2.72/21/2001 5 <1 1.2 <5 <5 3.13/28/2001 60 <1 1.7 <5 <5 <24/25/2001 39 <1 1.9 <5 <5 25/30/2001 83 <1 1.5 <5 <5 <27/25/2001 <1 1.1 <5 <5 <28/29/2001 76 2.1 <1 <1 1.1 <5 <5 <29/26/2001 73 <4 <0.1 <1 2.2 <5 <5 2.4 <0.2
10/24/2001 58 <4.0 <0.1 NA <1.0 <5.0 <5.0 <2.0 <0.211/28/2001 77 <4.0 <0.1 <1.0 <1.0 <5.0 <5.0 3.1 <0.212/26/2001 <4 <0.1 1 2.2 <5 <5 6.9 <0.21/30/2002 <4 <0.1 <1 <1 <5 <5 <2 <0.23/27/2002 <4.0 <0.1 1.1 1.7 <5.0 5.6 5 <0.24/30/2002 <4.0 <0.1 <1.0 <1.0 <5.0 <5.0 2.1 <0.25/29/2002 <4.0 <0.1 <1.0 NA <5.0 <5.0 3.1 <0.26/19/2002 <4.0 <0.1 <1.0 1.1 <5.0 <5.0 <2.0 <0.29/25/2002 78 <4.0 <0.1 <1.0 NA <5.0 <5.0 <2.0 <0.2
10/30/2002 60 <4.0 <0.1 <1.0 NA <5.0 <5.0 <2.0 <0.211/20/2002 82 <4.0 <0.1 <1.0 1.2 <5.0 NA NA <0.23/18/2003 71 <4.0 <0.1 <1.0 2.5 <5.0 <5.0 3.3 <0.24/16/2003 21 <4.0 <0.1 <1.0 2.1 <5.0 <5.0 3.1 <0.25/21/2003 66 <4.0 <0.1 <1.0 2.1 <5.0 <5.0 <2.0 <0.26/17/2003 56 <4.0 <0.1 <1.0 1.5 <5.0 <5.0 <2.0 <0.26/30/2003 50 <4.0 <0.1 <1.0 1.8 <5.0 <5.0 <2.0 <0.2
47
C4: 535STC513 – Tuolumne River at Shiloh Fishing Access continued…
DateHardness
(mg/L)
Total Arsenic (ug/L)
Total Cadmium
(ug/L)
Total Chromium
(ug/L)
Total Copper (ug/L)
Total Lead (ug/L)
Total Nickel (ug/L)
Total Zinc (ug/L)
Total Mercury (ug/L)
Count 21 18 18 28 26 29 28 27 17Min 5 2.0 0.1 0.5 0.5 2.5 2.5 1.0 0.1Max 83 2.1 0.5 1.1 2.5 2.5 5.6 6.9 0.1Mean 60 2.0 0.1 0.5 1.3 2.5 2.6 2.0 0.1Geo Mean 54 2.0 0.1 0.5 1.2 2.5 2.6 1.7 0.1Median 62 2.0 0.1 0.5 1.4 2.5 2.5 1.0 0.1Quartile 1 56 2.0 0.1 0.5 0.7 2.5 2.5 1.0 0.1Quartile 3 73 2.0 0.1 0.5 1.8 2.5 2.5 2.9 0.1NOTE: For values reported as < (less than), half the detection limit was used.
NA = Data not applicableINA = Site was inaccessibleDRY = Site had no flow
48
C4: 535STC513 – Tuolumne River at Shiloh Fishing Access continued…
DateHardness
(mg/L)
Dissolved Arsenic (ug/L)
Dissolved Cadmium
(ug/L)
Dissolved Chromium
(ug/L)
Dissolved Copper (ug/L)
Dissolved Lead (ug/L)
Dissolved Nickel (ug/L)
Dissolved Zinc
(ug/L)
Dissolved Mercury (ug/L)
10/26/2000 <1 <1 <5 <5 <211/29/2000 61 <1 <1 <5 <5 <212/27/2000 62 <1 <1 <5 <5 <21/24/2001 64 <1 <1 <5 <5 <22/10/2001 63 <1 1.1 <5 <5 <22/11/2001 54 <1 <1 <5 <5 <22/21/2001 5 <1 <1 <5 <5 <23/28/2001 60 <1 <1 <5 <5 <24/25/2001 39 <1 <1 <5 <5 <25/30/2001 83 <1 <1 <5 <5 2.47/25/20018/29/2001 76 2 <1 <1 1.5 <5 <5 <29/26/2001 73 <4 <0.1 <1 1.5 <5 <5 <2 <0.2
10/24/2001 58 <4.0 <0.1 NA <1.0 <5.0 <5.0 <2.0 <0.211/28/2001 77 <4.0 <0.1 <1.0 <1.0 <5.0 <5.0 NA <0.212/26/2001 <4 <0.1 <1 1.3 <5 <5 4.7 <0.21/30/2002 <4 <0.1 <1 <1 <5 <5 <2 <0.23/27/2002 <4.0 <0.1 <1.0 <1.0 <5.0 <5.0 2.4 <0.24/30/2002 <4.0 <0.1 <1.0 1.6 <5.0 <5.0 <2.0 <0.25/29/2002 <4.0 <0.1 <1.0 <1.0 <5.0 <5.0 <2.0 <0.26/19/2002 <4.0 <0.1 <1.0 <1.0 <5.0 <5.0 <2.0 <0.29/25/2002 78 <4.0 <0.1 <1.0 NA <5.0 <5.0 <2.0 <0.2
10/30/2002 60 <4.0 <0.1 <1.0 1.1 <5.0 <5.0 <2.0 <0.211/20/2002 82 <4.0 <0.1 <1.0 <1.0 <5.0 <5.0 <2.0 <0.2
Count 16 13 13 22 22 23 23 22 12Min 5.0 2.0 0.1 0.5 0.5 2.5 2.5 1.0 0.1Max 83.0 2.0 0.5 0.5 1.6 2.5 2.5 4.7 0.1Mean 62.2 2.0 0.1 0.5 0.7 2.5 2.5 1.3 0.1Geo Mean 55.3 2.0 0.1 0.5 0.7 2.5 2.5 1.2 0.1Median 62.5 2.0 0.1 0.5 0.5 2.5 2.5 1.0 0.1Quartile 1 59.5 2.0 0.1 0.5 0.5 2.5 2.5 1.0 0.1Quartile 3 76.3 2.0 0.1 0.5 1.0 2.5 2.5 1.0 0.1NOTE: For values reported as < (less than), half the detection limit was used.
NA = Data not applicableINA = Site was inaccessibleDRY = Site had no flow
49
50
C4: 535STC513 – Tuolumne River at Shiloh Fishing Access continued…
DateChloride (mg/L)
Sulfate (mg/L)
Calcium (mg/L)
Magnesium (mg/L)
TDS (mg/L)
Carbonate (mg/L)
Bicarbonate (mg/L)
Total Alkalinity
(mg/L)Sodium (mg/L)
11/29/2000 15 8 14 6 140 <1 70 60 1412/27/2000 15 8 15 6 110 <1 70 60 141/24/2001 16 9 15 6 100 <1 70 60 152/10/2001 15 8 15 6 97 <1 90 70 142/11/2001 12 6 13 5 79 <1 60 50 112/21/2001 6 4 7 3 68 <1 37 30 53/28/2001 15 8 14 6 120 <1 73 60 134/25/2001 8 NA 9 4 NA <1 38 38 85/30/2001 24 12 20 8 NA <1 78 78 226/27/2001 28 14 22 9 190 <1 110 93 258/29/2001 20 10 18 8 140 <1.0 93 76 209/26/2001 NA NA 17 7 NA <1 86 71 18
10/24/2001 13 8 14 6 120 <1 67 55 1411/28/2001 20 10 18 8 170 <1 90 74 193/18/2003 15 8 17 74/16/2003 3 3 5 25/21/2003 15 9 15 76/17/2003 13 7 13 66/30/2003 10 6 12 5
Count 18 17 19 19 11 14 14 14 14Min 3 3 5 2 68 0.5 37 30 5Max 28 14 22 9 190 0.5 110 93 25Mean 15 8 14 6 121 0.5 74 63 15Geo Mean 13 8 14 6 116 0.5 71 60 14Median 15 8 15 6 120 0.5 72 60 14Quartile 1 12 7 13 6 99 0.5 68 56 13Quartile 3 16 9 17 7 140 0.5 89 73 19NOTE: For values reported as < (less than), half the detection limit was used.
NA = Data not applicableINA = Site was inaccessibleDRY = Site had no flow
C4: 535STC513 – Tuolumne River at Shiloh Fishing Access continued…
Date Result Control Result Control
Result (million/m
l)
Control (million/
ml)MDD (%)
10/26/2000 100 100 NA NA10/24/2001 100 100 100 10011/28/2001 NA NA 100 10012/26/2001 90 100 100 1001/30/2002 75 100 100 902/27/2002 95 100 100 1004/30/2002 100 100 100 1005/29/2002 100 100 100 1006/19/2002 100 100 100 1008/28/2002 100 100 NA NA9/25/2002 100 100 100 10010/30/2002 100 100 100 10011/20/2002 100 100 100 10012/18/2002 100 90 100 100 1.03* 3.03 NA1/29/2003 100 100 100 100 4.44** 3.28 NA4/16/2003 100 100 100 100 1.72 1.90 35/21/2003 100 100 100 100 4.50** 2.01 20
Count 16 16 15 15 4 4 2
* Significantly reduced from the lab control.** Significantly greater than the lab control.^ Fish were from a "forced hatch," duplicate failed QA.1 Duplicate sample for the set was low - 77% recovery.
3 Samples qualified, but duplicate sample recovery for the set was high - 126% (53.8%/42.5%)NA = Data not applicableINA = Site was inaccessibleDRY = Site had no flow
2 Testing for the Fathead minnow was initiated when samples were approx. 48h old due to untimely shipping of fish by fish supplier.
96h Acute Fathead Minnow
(% Survival)
48h Acute Ceriodaphnia Dubia
(% Survival) Algae Cell Growth
51
C4: 535STC513 – Tuolumne River at Shiloh Fishing Access continued…
DateResult
(% Survival)
Control (%
Survival)
Avg Dry Weight Result (mg)
Avg Dry Weight Control
(mg)
Growth MDD (%)
Result (% Survival)
Control (%
Survival)
Avg # Young /
Adult Result
Avg # Young / Adult
Control
Repro MDD (%)
11/23/2004 90.0 95.0 0.22* 0.29 2512/29/2004 67.5* 97.5 0.41 0.54 29
01/27/2005 1 97.5 100.0 0.55 0.53 192/24/2005 55.3* 100.0 0.31* 0.57 28
03/29/2005 2 50.0* 100.0 0.21* 0.42 264/28/2005 N/A N/A N/A N/A N/A5/26/2005 77.5* 97.5 0.37* 0.51 136/30/2005 76.9* 97.5 0.29* 0.45 187/28/2005 N/A N/A N/A N/A N/A8/25/2005 89.7 100.0 0.52* 0.63 9.49/29/2005 77.5* 100.0 0.34 0.43 33
Count 9 9 9 9 9 N/A N/A N/A N/A N/A
* Significantly reduced from the lab control.** Significantly greater than the lab control.^ Fish were from a "forced hatch," duplicate failed QA.1 Duplicate sample for the set was low - 77% recovery.
3 Samples qualified, but duplicate sample recovery for the set was high - 126% (53.8%/42.5%)NA = Data not applicableINA = Site was inaccessibleDRY = Site had no flow
Chronic Ceriodaphnia Dubia - 6 dayChronic Fathead Minnow - 7day
2 Testing for the Fathead minnow was initiated when samples were approx. 48h old due to untimely shipping of fish by fish supplier.
52
C5: 535STC514 – Stanislaus River at Caswell Park Station Code:535STC514
Location: Latitude 37.70250, Longitude -121.17722
Date TimeTemp (ºC)
Field SC (umhos) pH
Dissolved Oxygen (mg/L)
Turbidity (ntu)
11/29/2000 8:10 AM 10.2 122 7.412/27/2000 1:00 PM 9.1 130 9.01/24/2001 12:35 PM 10.4 144 7.32/21/2001 2:00 PM 13.8 143 8.83/28/2001 8:55 AM 16.6 145 7.14/25/2001 7:38 AM 14.7 68 7.25/30/2001 8:20 AM 18.6 78 7.16/27/2001 8:03 AM 19.7 79 8.2 9.17/25/2001 8:22 AM 21.9 88 7.8 8.38/29/2001 8:32 AM 21.4 88 7.7 NA9/26/2001 8:09 AM 18.8 91 7.5 8.8
10/24/2001 8:53 AM 13.8 64 7.1 9.911/28/2001 8:20 AM 9.9 108 7.7 10.312/26/2001 9:05 AM 10.3 141 7.6 10.11/30/2002 8:59 AM 7.3 152 7.8 11.42/27/2002 8:02 AM 13.0 119 8.3 9.73/27/2002 7:51 AM 13.6 102 8.2 10.04/30/2002 8:55 AM 12.7 105 7.3 11.15/29/2002 8:04 AM 17.1 71 7.7 9.76/19/2002 8:10 AM 20.4 82 7.6 7.97/31/2002 7:57 AM 21.7 98 7.7 7.8 5.08/28/2002 8:45 AM 21.1 99 7.7 NA9/25/2002 8:36 AM 20.2 113 7.5 8.1
10/30/2002 8:07 AM 12.8 88 6.6 9.711/20/2002 8:25 AM 11.7 111 7.6 10.512/18/2002 8:10 AM 10.8 164 7.5 9.1 52.31/29/2003 8:31 AM 11.3 91 7.6 10.8 14.33/25/2003 8:00 AM 14.1 100 7.5 10.3 6.21/28/2004 11:13 AM 10.5 140 8.1 15.1 5.12/24/2004 11:53 AM 12.5 112 7.9 10.8 0.83/24/2004 10:07 AM 16.6 125 7.8 9.1 17.54/28/2004 10:11 AM 15.9 68 7.8 11.4 9.05/26/2004 12:11 PM 18.9 84 7.8 9.3 5.36/23/2004 10:58 AM 17.4 60 7.9 10.0 NA7/28/2004 11:45 AM 22.7 84 8.1 9.8 NA8/25/2004 11:59 AM 21.6 91 8.1 8.1 NA9/29/2004 12:15 PM 18.7 116 8.2 9.1 NA
10/27/2004 11:47 AM 13.3 65 8.6 12.1
53
C5: 535STC514 – Stanislaus River at Caswell Park continued…
Date TimeTemp (ºC)
Field SC (umhos) pH
Dissolved Oxygen (mg/L)
Turbidity (ntu)
11/22/2004 12:16 PM 10.1 119 8.2 11.212/28/2004 10:35 AM 9.8 124 8.0 11.51/26/2005 11:12 AM 11.2 166 7.9 9.92/23/2005 10:25 AM 13.5 183 7.9 9.63/29/2005 11:46 AM 13.6 144 7.9 11.24/26/2005 11:40 AM 16.7 118 7.9 10.45/24/2005 10:42 AM 15.5 78 7.9 10.06/28/2005 10:56 AM 21.1 106 7.7 8.47/26/2005 10:53 AM 23.8 101 7.8 8.58/23/2005 10:55 AM 21.9 103 7.6 8.09/27/2005 11:46 AM 18.2 138 8.1 13.1
Count 49 49 49 40 9Min 7.3 60 6.6 7.8 0.8Max 23.8 183 9.0 15.1 52.3Mean 15.5 108 7.8 10.0 12.8Geo Mean 14.9 104 7.8 9.9 8Median 14.7 105 7.8 9.9 6.2Quartile 1 11.7 88 7.6 9.1 5.1Quartile 3 18.9 125 8.0 10.8 14.3NOTE: For values reported as < (less than), half the detection limit was used.
NA = Data not applicableINA = Site was inaccessibleDRY = Site had no flow
54
C5: 535STC514 – Stanislaus River at Caswell Park continued…
DateTSS
(mg/L)TOC
(mg/L)Total Coli
MPNE. coli MPN
11/29/2000 NA <112/27/2000 <6 1.21/24/2001 <6 <12/21/2001 <5.5 NA3/28/2001 16 NA4/25/2001 15 1.35/30/2001 11 3.36/27/2001 11 4.37/25/2001 1.28/29/2001 NA 3.09/26/2001 NA 6.1
11/28/2001 NA12/26/2001 3.03/27/2002 NA4/30/2002 NA5/29/2002 1.76/19/2002 NA7/31/2002 2420 658/28/2002 NA9/25/2002 NA
10/30/2002 1.211/20/2002 2.012/18/2002 7.01/28/2004 411 882/24/2004 866 303/24/2004 >2419.6 694/28/2004 1986 1085/26/2004 1986 1016/23/2004 >2419.6 2187/28/2004 >2419.6 628/25/2004 2420 369/29/2004 >2419.6 51
10/27/2004 1.9 >2419.6 29911/22/2004 1.6 1203 4112/28/2004 2.0 >2419.6 3081/26/2005 2.9 1300 352/23/2005 5.5 629 883/29/2005 3.4 >2419.6 1354/26/2005 NA >2419.6 825/24/2005 NA 1203 77
55
56
DateTSS
(mg/L)TOC
(mg/L)Total Coli
MPNE. coli MPN
6/28/2005 2.1 >2419.6 417/26/2005 NA >2419.6 758/23/2005 2.3 >2419.6 509/27/2005 3.1 >2419.6 99
Count 7 23 22 2
C5: 535STC514 – Stanislaus River at Caswell Park continued…
2Min 2.8 0.5 411 30Max 16 7.0 2420 308Mean 9 2.7 NA NAGeo Mean 7 2.2 1796 78Median 11 2.1 2420 76Quartile 1 3 1.5 1472 50Quartile 3 13 3.2 2420 101NOTE: For values reported as < (less than), half the detection limit was used
For values reported as > (greater than), 2420 was used
NA =INA =DRY
Data not applicable Site was inaccessible
= Site had no flow
C5: 535STC514 – Stanislaus River at Caswell Park continued…
DateNitrate (mg/L)
Nitrate-N (mg/L)
TKN (mg/L)
Ammonia-N (mg/L)
Phosphorus (mg/L)
Ortho-phosphate-
P (mg/L)
Potassium (mg/L)
BOD 5-Day (mg/L)
BOD 10-Day (mg/L)
11/29/2000 3.2 NA <0.1 <1 1.4 0.2 0.612/27/2000 3.3 <2 <0.1 <1 1.81/24/2001 3.7 <2 <0.1 <1 1.9 0.8 1.22/21/2001 3.7 <2 0.1 <1 2.3 0.9 1.73/28/2001 3.2 <2 <0.1 <1 1.7 1 1.44/25/2001 <2 <2 0.1 <1 1 0.4 0.85/30/2001 <2 <2 0.1 <1 1.2 0.7 0.96/27/2001 <2 <2 <0.1 <1 1.2 0.4 0.48/29/2001 <2 <2 <0.1 <1 NA9/26/2001 <2 <2 <0.1 <1 1.8
10/24/2001 <2 <2 <0.1 <1 <1 0.5 0.711/28/2001 NA 0.1 NA <0.03 1.8 0.4 0.812/26/2001 1.1 2.31/30/2002 0.5 0.92/27/2002 0.5 0.83/27/2002 0.6 0.94/30/2002 0.5 0.95/29/2002 0.3 0.86/19/2002 0.6 0.98/28/2002 0.2 0.79/25/2002 0.6 1
10/30/2002 0.3 0.412/18/2002 6.2 8.81/29/2003 0.7 1
57
C5: 535STC514 – Stanislaus River at Caswell Park continued…
DateNitrate (mg/L)
Nitrate-N (mg/L)
TKN (mg/L)
Ammonia-N (mg/L)
Phosphorus (mg/L)
Ortho-phosphate-
P (mg/L)
Potassium (mg/L)
BOD 5-Day (mg/L)
BOD 10-Day (mg/L)
Count 11 NA 11 NA 11 12 11 21 21Min 1 NA 0.1 NA 0.1 0.0 0.5 0.2 0.4Max 3.7 NA 1.0 NA 0.1 0.5 2.3 6.2 8.8Mean 2.1 NA 0.9 NA 0.1 0.5 1.5 0.8 1.3Geo Mean 1.7 NA 0.8 NA 0.1 0.4 1.4 0.6 1.0Median 1.0 NA 1.0 NA 0.1 0.5 1.7 0.5 0.9Quartile 1 1.0 NA 1.0 NA 0.1 0.5 1.2 0.4 0.8Quartile 3 3.3 NA 1.0 NA 0.1 0.5 1.8 0.7 1.0NOTE: For values reported as < (less than), half the detection limit was used.
NA = Data not applicableINA = Site was inaccessibleDRY = Site had no flow
58
C5: 535STC514 – Stanislaus River at Caswell Park continued…
DateHardness
(mg/L)
Total Arsenic (ug/L)
Total Cadmium
(ug/L)
Total Chromium
(ug/L)
Total Copper (ug/L)
Total Lead (ug/L)
Total Nickel (ug/L)
Total Zinc (ug/L)
Total Mercury (ug/L)
11/29/2000 47 <1 1.1 <5 <5 2.112/27/2000 50 <1 3.0 <5 <5 2.61/24/2001 54 <1 1.3 <5 <5 <22/21/2001 55 <1 2.0 <5 <5 4.33/28/2001 55 <1 2.8 <5 <5 3.64/25/2001 29 <1 1.7 <5 <5 <25/30/2001 31 <1 1.7 <5 <5 <27/25/2001 <1 1.2 <5 <5 <28/29/2001 NA <2 <1 <1 <1 <5 <5 <29/26/2001 35 <4 <0.1 <1 2.4 <5 <5 <2 <0.2
10/24/2001 26 <4.0 <0.1 NA <1.0 <5.0 <5.0 2.1 <0.211/28/2001 41 <4.0 <0.1 <1.0 <1.0 <5.0 <5.0 3.1 <0.212/26/2001 <4 <0.1 <1 2.2 <5 <5 6.5 <0.21/30/2002 <4 <0.1 <1 <1 <5 <5 <2 <0.23/27/2002 <4.0 <0.1 <1.0 2.3 <5.0 <5.0 5.0 <0.24/30/2002 <4.0 <0.1 <1.0 <1.0 <5.0 <5.0 <2.0 <0.25/29/2002 <4.0 <0.1 <1.0 NA <5.0 <5.0 <2.0 <0.26/19/2002 <4.0 <0.1 <1.0 1.3 <5.0 <5.0 <2.0 <0.29/25/2002 41 <4.0 <0.1 <1.0 NA <5.0 <5.0 2.3 <0.2
10/30/2002 36 <4.0 <0.1 <1.0 NA <5.0 <5.0 <2.0 <0.211/20/2002 46 <4.0 <0.1 <1.0 1.4 <5.0 NA NA <0.2
Count 13 13 13 20 18 21 20 20 12Min 26.0 1.0 0.1 0.5 0.5 2.5 2.5 1.0 0.1Max 55.0 2.0 0.5 0.5 3.0 2.5 2.5 6.5 0.1Mean 42.0 1.9 0.1 0.5 1.5 2.5 2.5 2.1 0.1Geo Mean 40.8 1.9 0.1 0.5 1.3 2.5 2.5 1.7 0.1Median 41.0 2.0 0.1 0.5 1.4 2.5 2.5 1.0 0.1Quartile 1 35.0 2.0 0.1 0.5 0.7 2.5 2.5 1.0 0.1Quartile 3 50.0 2.0 0.1 0.5 2.2 2.5 2.5 2.7 0.1NOTE: For values reported as < (less than), half the detection limit was used.
NA = Data not applicableINA = Site was inaccessibleDRY = Site had no flow
59
C5: 535STC514 – Stanislaus River at Caswell Park continued…
DateHardness
(mg/L)
Dissolved Arsenic (ug/L)
Dissolved Cadmium
(ug/L)
Dissolved Chromium
(ug/L)
Dissolved Copper (ug/L)
Dissolved Lead (ug/L)
Dissolved Nickel (ug/L)
Dissolved Zinc
(ug/L)
Dissolved Mercury (ug/L)
11/29/2000 47 <1 <1 <5 <5 5.912/27/2000 50 <1 <1 <5 <5 <21/24/2001 54 <1 <1 <5 <5 <22/21/2001 55 <1 1.3 <5 <5 2.43/28/2001 55 <1 1.2 <5 <5 2.04/25/2001 29 <1 <1 <5 <5 2.25/30/2001 31 <1 <1 <5 <5 3.98/29/2001 NA <2 <1 <1 <1 <5 <5 <29/26/2001 35 <4 <0.1 <1 1.4 <5 <5 <2 <0.2
10/24/2001 26 <4.0 <0.1 NA <1.0 <5.0 <5.0 <2.0 <0.211/28/2001 41 <4.0 <0.1 <1.0 <1.0 <5.0 <5.0 NA <0.212/26/2001 <4 <0.1 <1 1.4 <5 <5 6.1 <0.21/30/2002 <4 <0.1 <1 <1 <5 <5 <2 <0.23/27/2002 <4.0 <0.1 <1.0 <1.0 <5.0 <5.0 3.7 <0.24/30/2002 <4.0 <0.1 <1.0 <1.0 <5.0 <5.0 <2.0 <0.25/29/2002 <4.0 <0.1 <1.0 <1.0 <5.0 <5.0 <2.0 <0.26/19/2002 <4.0 <0.1 <1.0 <1.0 <5.0 <5.0 <2.0 <0.29/25/2002 41 <4.0 <0.1 <1.0 NA <5.0 <5.0 <2.0 <0.2
10/30/2002 36 <4.0 <0.1 <1.0 2.1 <5.0 <5.0 <2.0 <0.211/20/2002 46 <4.0 <0.1 <1.0 <1.0 <5.0 <5.0 <2.0 <0.2
Count 13 13 13 19 19 20 20 19 12Min 26.0 1.0 0.1 0.5 0.5 2.5 2.5 1.0 0.1Max 55.0 2.0 0.5 0.5 2.1 2.5 2.5 6.1 0.1Mean 42.0 1.9 0.1 0.5 0.8 2.5 2.5 2.0 0.1Geo Mean 40.8 1.9 0.1 0.5 0.7 2.5 2.5 1.6 0.1Median 41.0 2.0 0.1 0.5 0.5 2.5 2.5 1.0 0.1Quartile 1 35.0 2.0 0.1 0.5 0.5 2.5 2.5 1.0 0.1Quartile 3 50.0 2.0 0.1 0.5 0.9 2.5 2.5 2.3 0.1NOTE: For values reported as < (less than), half the detection limit was used.
NA = Data not applicableINA = Site was inaccessibleDRY = Site had no flow
60
61
C5: 535STC514 – Stanislaus River at Caswell Park continued…
DateChloride (mg/L)
Sulfate (mg/L)
Calcium (mg/L)
Magnesium (mg/L)
TDS (mg/L)
Carbonate (mg/L)
Bicarbonate (mg/L)
Total Alkalinity
(mg/L)Sodium (mg/L)
11/29/2000 5 6 11 5 100 <1 60 50 612/27/2000 6 7 12 5 75 <1 60 50 61/24/2001 7 7 13 5 75 <1 70 55 82/21/2001 6 7 13 6 120 <1 66 54 73/28/2001 6 7 12 6 87 <1 67 55 74/25/2001 2 NA 7 3 NA <1 30 30 35/30/2001 2 3 8 3 NA <1 32 32 36/27/2001 3 3 8 3 59 <1 41 34 48/29/2001 3 NA NA NA 48 <1.0 110 86 49/26/2001 NA NA 9 3 NA <1 43 35 4
10/24/2001 2 3 7 2 42 <1 33 27 311/28/2001 4 4 10 4 52 <1 51 42 5
Count 11 9 11 11 9 12 12 12 12Min 2 3 7 2 42 0.5 30 27 3Max 7 7 13 6 120 0.5 110 86 8Mean 4 5 10 4 73 0.5 55 46 5Geo Mean 4 5 10 4 69 0.5 52 43 5Median 4 6 10 4 75 0.5 56 46 5Quartile 1 3 3 8 3 52 0.5 39 34 4Quartile 3 6 7 12 5 87 0.5 66 54 6NOTE: For values reported as < (less than), half the detection limit was used.
NA = Data not applicableINA = Site was inaccessibleDRY = Site had no flow
C5: 535STC514 – Stanislaus River at Caswell Park continued…
Date Result Control Result Control
Result (million/m
l)
Control (million/m
l)MDD (%)
10/26/2000 100 100 NA NA1/24/2001 100 100 NA NA
10/24/2001 100 100 100 10011/28/2001 NA NA 100 10012/26/2001 100 100 100 1001/30/2002 100 100 100 902/27/2002 100 100 100 1004/30/2002 100 100 100 1005/29/2002 100 100 100 1006/19/2002 100 100 100 1008/28/2002 100 100 NA NA9/25/2002 100 100 100 100
10/30/2002 100 100 100 10011/20/2002 100 100 100 10012/18/2002 100 90 100 100 3.19** 3.03 N/A1/19/2002 100 100 100 100 1.69* 3.28 N/A4/16/2003 100 100 100 100 1.68 1.90 45/21/2003 100 100 100 100 1.51* 2.01 6
Count 17 17 15 15 4 4 N/A
* Significantly reduced from the lab control.** Significantly greater than the lab control.^ Fish were from a "forced hatch," duplicate failed QA.1 Duplicate sample for the set was low - 77% recovery.
3 Samples qualified, but duplicate sample recovery for the set was high - 126% (53.8%/42.5%)NA = Data not applicableINA = Site was inaccessibleDRY = Site had no flow
2 Testing for the Fathead minnow was initiated when samples were approx. 48h old due to untimely shipping of fish by fish supplier.
96h Acute Fathead Minnow
(% Survival)
48h Acute Ceriodaphnia Dubia
(% Survival) Algae Cell Growth
62
C5: 535STC514 – Stanislaus River at Caswell Park continued…
Date
Result (%
Survival)
Control (%
Survival)
Avg Dry Weight Result (mg)
Avg Dry Weight Control
(mg)
Growth MDD (%)
Result (%
Survival)
Control (%
Survival)
Avg # Young /
Adult Result
Avg # Young /
Adult Control
Repro MDD (%)
11/22/2004 60.0* 97.5 0.14* 0.27 2112/28/2004 97.5 100.0 0.6 0.6 N/A1/26/2005 87.5 97.5 0.49 0.46 302/23/2005 89.7 100.0 0.59 0.57 30
03/29/2005 2 97.5 100.0 0.49 0.42 154/26/2005 50.0* 92.5 0.21* 0.39 285/24/2005 85.4 87.5 0.55 0.49 266/28/2005 N/A N/A N/A N/A N/A7/26/2005 N/A N/A N/A N/A N/A8/23/2005 82.5* 100.0 0.49* 0.77 119/27/2005 97.5 97.5 0.42 0.45 16
Count 9 9 9 9 8 N/A N/A N/A N/A N/A
* Significantly reduced from the lab control.** Significantly greater than the lab control.^ Fish were from a "forced hatch," duplicate failed QA.1 Duplicate sample for the set was low - 77% recovery.
3 Samples qualified, but duplicate sample recovery for the set was high - 126% (53.8%/42.5%)NA = Data not applicableINA = Site was inaccessibleDRY = Site had no flow
Chronic Ceriodaphnia Dubia - 6 dayChronic Fathead Minnow - 7day
2 Testing for the Fathead minnow was initiated when samples were approx. 48h old due to untimely shipping of fish by fish supplier.
63
C6: 531SJC503 – Lone Tree Creek at Austin Road Station Code:531SJC503
Location: Latitude 37.85556, Longitude -121.18500
Date TimeTemp (ºC)
Field SC (umhos) pH
Dissolved Oxygen (mg/L)
Turbidity (ntu)
10/24/2000 10:00 AM 11.2 293 7.211/29/2000 7:15 AM 8.3 295 5.412/27/2000 8:45 AM 5.5 340 7.71/24/2001 8:15 AM 7.6 302 8.82/10/2001 3:15 PM 11.2 275 8.62/11/2001 3:45 AM 7.0 331 7.82/21/2001 9:00 AM 10.6 304 8.83/28/2001 8:05 AM 14.5 69 6.64/25/2001 7:10 AM 17.2 90 7.35/30/2001 7:30 AM 19.0 113 7.46/27/2001 7:30 AM 20.6 174 7.4 7.67/25/2001 7:52 AM 22.5 149 7.7 5.68/29/2001 7:35 AM 20.8 105 7.5 NA9/26/2001 7:34 AM 18.2 225 6.5 8.2
10/24/2001 8:11 AM 11.1 321 6.9 8.111/28/2001 7:40 AM 7.7 266 7.6 9.412/26/2001 8:32 AM 8.9 287 7.5 9.21/30/2002 8:14 AM 1.9 605 7.9 10.42/27/2002 7:30 AM 11.0 518 8.9 4.63/27/2002 7:24 AM 12.5 324 8.1 9.14/30/2002 8:27 AM 13.5 124 6.9 10.35/29/2002 7:32 AM 18.9 143 7.4 7.36/19/2002 7:38 AM 20.7 155 7.5 6.97/31/2002 8:52 AM 20.8 129 7.6 6.6 38.88/28/2002 8:15 AM 20.8 140 7.1 NA9/25/2002 8:02 AM 18.0 119 7.3 7.6
10/30/2002 7:27 AM DRY DRY DRY DRY11/20/2002 7:45 AM 9.1 379 7.4 6.312/18/2002 7:39 AM 9.4 392 7.4 7.9 2881/29/2003 7:56 AM 8.9 404 7.4 6.1 52.51/28/2004 11:44 AM DRY DRY DRY DRY DRY2/24/2004 12:30 PM 16.0 461 7.8 9.8 NA3/24/2004 10:31 AM 15.5 119 7.6 9.9 50.14/28/2004 10:39 AM 18.8 113 7.6 10.8 50.25/26/2004 12:41 PM 21.0 174 7.9 10.0 63.06/23/2004 12:13 PM 23.8 128 8.4 10.9 NA7/28/2004 12:10 PM 24.2 139 7.8 8.7 NA8/25/2004 12:33 PM 21.2 92 7.6 8.1 NA9/29/2004 12:48 PM 19.0 138 7.8 8.5 NA
64
C6: 531SJC503 – Lone Tree Creek at Austin Road continued…
Date TimeTemp (ºC)
Field SC (umhos) pH
Dissolved Oxygen (mg/L)
Turbidity (ntu)
10/27/2004 12:22 PM 13.3 592 7.5 0.411/22/2004 1:08 PM 8.5 500 7.8 10.112/28/2004 11:10 AM 9.3 411 7.5 8.11/26/2005 11:45 AM 11.0 313 7.8 8.92/23/2005 10:58 AM 13.6 520 7.7 7.43/29/2005 12:40 PM 14.7 375 7.7 8.84/26/2005 12:49 PM 17.8 260 7.7 9.55/24/2005 11:18 AM 20.2 127 7.6 9.16/28/2005 11:38 AM 21.0 146 7.6 8.17/26/2005 11:31 AM 23.3 214 7.5 7.78/23/2005 11:37 AM 21.9 156 7.3 7.69/27/2005 12:29 PM 18.6 113 7.7 11.4
Count 49 49 49 37 6Min 1.9 69 5.4 0.4 38.8Max 24.2 605 8.9 11.4 288Mean 15.1 254 7.6 8.2 90.4Geo Mean 13.8 217 7.6 7.7 67.3Median 15.5 225 7.6 8.2 51.4Quartile 1 10.6 129 7.4 7.6 50.1Quartile 3 20.6 331 7.8 9.5 60.4NOTE: For values reported as < (less than), half the detection limit was used.
NA = Data not applicableINA = Site was inaccessibleDRY = Site had no flow
65
C6: 531SJC503 – Lone Tree Creek at Austin Road continued…
DateTSS
(mg/L)TOC
(mg/L)Total Coli
MPNE. coli MPN
10/24/2000 9 1211/29/2000 NA 1212/27/2000 61/24/2001 17 232/10/2001 52 232/11/2001 22 212/21/2001 130 NA3/28/2001 31 NA4/25/2001 20 2.85/30/2001 24 6.06/27/2001 58 6.27/25/2001 8.88/29/2001 NA 6.79/26/2001 NA 17
11/28/2001 NA12/26/2001 283/27/2002 NA4/30/2002 NA5/29/2002 6.46/19/2002 NA7/31/2002 >2419.6 4119/25/2002 NA
11/20/2002 171/28/2004 DRY DRY2/24/2004 >2419.6 4353/24/2004 >2419.6 8164/28/2004 >2419.6 6135/26/2004 >2419.6 2726/23/2004 >2419.6 1537/28/2004 >2419.6 1448/25/2004 >2419.6 1619/29/2004 >2419.6 1733
10/27/2004 52 >2419.6 >2419.611/22/2004 40 >2419.6 98012/28/2004 19 >2419.6 821/26/2005 22 >2419.6 2382/23/2005 67 >2419.6 2193/29/2005 30 >2419.6 8164/26/2005 NA >2419.6 5795/24/2005 NA 1011 525
66
67
DateTSS
(mg/L)TOC
(mg/L)Total Coli
MPNE. coli MPN
6/28/2005 5.3 >2419.6 24207/26/2005 NA >2419.6 9808/23/2005 7.3 >2419.6 3089/27/2005 5.6 >2419.6 435
Count 10 23 21 21Min 6 2.8 1011 82Max 130 67 2420 2420Mean 37 19 NA NAGeo Mean 26 14 2321 468Median 23 17 2420 435Quartile 1 18 6.6 2420 238Quartile 3 47 23 2420 816NOTE: For values reported as < (less than), half the detection limit was used
For values reported as > (greater than), 2420 was used
NA =INA =DRY
C6: 531SJC503 – Lone Tree Creek at Austin Road continued…
Data not applicable Site was inaccessible
= Site had no flow
C6: 531SJC503 – Lone Tree Creek at Austin Road continued…
DateNitrate (mg/L)
Nitrate-N (mg/L)
TKN (mg/L)
Ammonia-N (mg/L)
Phosphorus (mg/L)
Ortho-phosphate-
P (mg/L)
Potassium (mg/L)
BOD 5-Day (mg/L)
BOD 10-Day (mg/L)
10/24/2000 3.6 2.1 1.1 1.3 16 2.4 5.411/29/2000 3.9 NA 0.5 1.2 23 7.1 13.512/27/2000 2.1 <2 1.0 1.8 21 3.0 6.21/24/2001 10 3.3 0.7 1.4 25 6.0 11.72/10/2001 7.3 <2 0.3 <1 24 7.9 15.02/11/2001 10 3.2 1.0 1 282/21/2001 6.3 8.7 1.1 2.1 31 8.3 16.83/28/2001 <2 <2 0.2 <1 2.4 1.5 2.24/25/2001 <2 <2 0.3 <1 3.7 2.0 3.55/30/2001 3.4 <2 0.3 <1 3.4 2.4 3.56/27/2001 7.4 <2 0.5 <1 6.0 2.8 4.88/29/2001 2.8 <2 0.6 <1 NA9/26/2001 3.4 5.5 0.8 <1 13
10/24/2001 4.6 <2 0.9 <1 14 2.3 5.511/28/2001 NA 4.3 NA 1.3 30 7.9 16.112/26/2001 NA 4.4 2.0 1.5 33 8.1 16.31/30/2002 NA 12 4.5 2.7 53 8.2 16.42/27/2002 NA 5.2 2.0 1.2 NA 8.2 16.53/27/2002 NA 1.2 NA 0.2 5.6 1.8 2.84/30/2002 NA NA 0.6 0.5 NA 8.2 13.35/29/2002 NA 1.5 NA 0.6 6.8 5.6 8.06/19/2002 NA 1.1 0.5 NA 5.9 3.3 5.28/28/2002 NA 0.7 0.9 0.8 4.8 1.3 2.49/25/2002 NA NA 0.4 0.4 4.9 2.6 3.9
11/20/2002 NA 5.6 1.8 1.2 2912/18/2002 NA 17 4.4 <0.03 42 8.1 16.51/29/2003 NA NA 4.8 2.8 36 7.7 16.1
68
C6: 531SJC503 – Lone Tree Creek at Austin Road continued…
DateNitrate (mg/L)
Nitrate-N (mg/L)
TKN (mg/L)
Ammonia-N (mg/L)
Phosphorus (mg/L)
Ortho-phosphate-
P (mg/L)
Potassium (mg/L)
BOD 5-Day (mg/L)
BOD 10-Day (mg/L)
Count 14 NA 23 NA 24 26 24 23 23Min 1.0 NA 0.7 NA 0.2 0.02 2.4 1.3 2.2Max 10.0 NA 17.0 NA 4.8 2.8 53.0 8.3 16.8Mean 4.8 NA 3.6 NA 1.3 1.0 19.2 5.1 9.6Geo Mean 3.8 NA 2.3 NA 0.9 0.7 13.6 4.2 7.7Median 3.8 NA 1.5 NA 0.9 0.7 18.5 5.6 8.0Quartile 1 3.0 NA 1.0 NA 0.5 0.5 5.8 2.4 4.4Quartile 3 7.1 NA 4.8 NA 1.3 1.3 29.3 8.0 16.1NOTE: For values reported as < (less than), half the detection limit was used.
NA = Data not applicableINA = Site was inaccessibleDRY = Site had no flow
69
C6: 531SJC503 – Lone Tree Creek at Austin Road continued…
DateHardness
(mg/L)
Total Arsenic (ug/L)
Total Cadmium
(ug/L)
Total Chromium
(ug/L)
Total Copper (ug/L)
Total Lead (ug/L)
Total Nickel (ug/L)
Total Zinc (ug/L)
Total Mercury (ug/L)
10/24/2000 110 2.1 7.9 <5 <5 6.811/29/2000 84 1.6 29 <5 <5 8.312/27/2000 110 <1 11 <5 <5 5.51/24/2001 76 2.0 22 <5 5.7 112/10/2001 79 3.8 24 <5 8 162/11/2001 100 1.6 19 <5 5.5 9.62/21/2001 82 4.4 37 <5 7.1 443/28/2001 28 1.2 4.2 <5 <5 7.54/25/2001 36 <1 4.2 <5 <5 5.85/30/2001 44 <1 3.2 <5 <5 6.77/25/2001 <1 5.8 <5 <5 4.38/29/2001 45 <2 <1 2.8 6.2 <5 <5 139/26/2001 61 <4 <0.1 3.1 35 <5 <5 23 <0.2
10/24/2001 120 <4.0 <0.1 NA 7.6 <5.0 <5.0 2.5 <0.211/28/2001 71 <4.0 <0.1 4.5 16 <5.0 8.3 21 <0.212/26/2001 72 <4 <0.1 3.4 27 <5 6.7 24 <0.21/30/2002 160 <4 0.1 <1 31 <5 7.9 24 <0.23/27/2002 130 <4.0 <0.1 2.4 4.4 <5.0 9.5 12 <0.24/30/2002 47 <4.0 <0.1 <1.0 3.4 <5.0 <5.0 5.6 <0.25/29/2002 54 <4.0 <0.1 2.0 NA <5.0 <5.0 13 <0.26/19/2002 63 <4.0 <0.1 1.7 5.6 <5.0 <5.0 8.4 <0.29/25/2002 44 <4.0 <0.1 1.7 NA <5.0 <5.0 8.1 <0.2
11/20/2002 120 <4.0 <0.1 1.9 11 <5.0 NA NA <0.2
70
C6: 531SJC503 – Lone Tree Creek at Austin Road continued…
DateHardness
(mg/L)
Total Arsenic (ug/L)
Total Cadmium
(ug/L)
Total Chromium
(ug/L)
Total Copper (ug/L)
Total Lead (ug/L)
Total Nickel (ug/L)
Total Zinc (ug/L)
Total Mercury (ug/L)
Count 22 12 12 22 21 23 22 22 11Min 28 1.0 0.1 0.5 3.2 2.5 2.5 2.5 0.1Max 160 2.0 0.5 4.5 37.0 2.5 9.5 44.0 0.1Mean 79 1.9 0.1 2.0 15.0 2.5 4.3 12.7 0.1Geo Mean 72 1.9 0.1 1.5 10.9 2.5 3.7 10.2 0.1Median 74 2.0 0.1 1.8 11.0 2.5 2.5 9.0 0.1Quartile 1 49 2.0 0.1 0.7 5.6 2.5 2.5 6.7 0.1Quartile 3 108 2.0 0.1 2.7 24.0 2.5 6.5 15.3 0.1NOTE: For values reported as < (less than), half the detection limit was used.
NA = Data not applicableINA = Site was inaccessibleDRY = Site had no flow
71
C6: 531SJC503 – Lone Tree Creek at Austin Road continued…
DateHardness
(mg/L)
Dissolved Arsenic (ug/L)
Dissolved Cadmium
(ug/L)
Dissolved Chromium
(ug/L)
Dissolved Copper (ug/L)
Dissolved Lead (ug/L)
Dissolved Nickel (ug/L)
Dissolved Zinc
(ug/L)
Dissolved Mercury (ug/L)
10/24/2000 11011/29/2000 84 <1 24 <5 <5 2.512/27/2000 110 <1 9.9 <5 <5 2.51/24/2001 76 <1 17 <5 5.1 4.92/10/2001 79 <1 18 <5 5.4 5.32/11/2001 100 <1 16 <5 <5 4.42/21/2001 82 1.3 15 <5 <5 143/28/2001 28 <1 2.0 <5 <5 2.54/25/2001 36 <1 2.1 <5 <5 3.85/30/2001 44 <1 2.0 <5 <5 3.87/25/20018/29/2001 45 <2 <1 <1 4.1 <5 <5 6.99/26/2001 61 <4 <0.1 <1 13 <5 <5 22
10/24/2001 120 <4.0 <0.1 NA 6.9 <5.0 <5.0 <2.0 <0.211/28/2001 71 <4.0 <0.1 <1.0 9.4 <5.0 5.6 NA <0.212/26/2001 72 <4 <0.1 <1 15 <5 <5 13 <0.21/30/2002 160 <4 <0.1 <1 16 <5 <5 8.8 <0.23/27/2002 130 <4.0 <0.1 <1.0 2.6 <5.0 <5.0 4.8 <0.24/30/2002 47 <4.0 <0.1 <1.0 2.1 <5.0 <5.0 3.9 <0.25/29/2002 54 <4.0 <0.1 <1.0 3.5 <5.0 <5.0 4.1 <0.26/19/2002 63 <4.0 <0.1 <1.0 2.7 <5.0 <5.0 4.4 <0.29/25/2002 44 <4.0 <0.1 <1.0 NA <5.0 <5.0 <2.0 <0.2
11/20/2002 120 <4.0 <0.1 <1.0 7.5 <5.0 6.2 7.0 <0.2
Count 22 12 12 20 20 21 21 20 10Min 28 1.0 0.1 0.5 2.0 2.5 2.5 1.0 0.1Max 160 2.0 0.5 1.3 24.0 2.5 6.2 22.0 0.1Mean 79 1.9 0.1 0.5 9.4 2.5 3.086 6.0 0.1Geo Mean 72 1.9 0.1 0.5 6.8 2.5 2.911 4.6 0.1Median 74 2.0 0.1 0.5 8.5 2.5 2.5 4.4 0.1Quartile 1 49 2.0 0.1 0.5 2.7 2.5 2.5 3.5 0.1Quartile 3 108 2.0 0.1 0.5 15.3 2.5 2.5 6.9 0.1NOTE: For values reported as < (less than), half the detection limit was used.
NA = Data not applicableINA = Site was inaccessibleDRY = Site had no flow
72
C6: 531SJC503 – Lone Tree Creek at Austin Road continued…
DateChloride (mg/L)
Sulfate (mg/L)
Calcium (mg/L)
Magnesium (mg/L)
TDS (mg/L)
Carbonate (mg/L)
Bicarbonate (mg/L)
Total Alkalinity
(mg/L)Sodium (mg/L)
10/24/2000 16 7 24 12 200 <1 140 110 1211/29/2000 20 11 18 9 240 <1 120 100 1512/27/2000 25 6 25 11 230 <1 150 120 161/24/2001 17 20 17 8 230 <1 300 250 132/10/2001 20 12 18 9 380 <1 90 80 142/11/2001 17 16 24 11 160 <1 130 110 142/21/2001 17 9 18 9 270 <1 120 100 123/28/2001 3 4 6 3 54 <1 34 28 34/25/2001 4 NA 8 4 NA <1 38 38 35/30/2001 3 4 11 4 NA <1 44 44 56/27/2001 7 6 16 7 120 <1 78 64 78/29/2001 3 4 9 5 77 <1.0 50 41 49/26/2001 NA NA 14 6 NA <1 93 77 7
10/24/2001 15 13 27 13 220 <1 140 120 1511/28/2001 18 13 15 8 320 <1 84 69 1112/26/2001 18 12 15 8 270 <1 100 84 131/30/2002 38 14 34 17 410 <1 250 200 252/27/2002 41 12 37 16 NA <1.0 228 187 273/27/2002 8 21 30 14 190 <1.0 120 100 114/30/2002 4 4 11 5 NA <1.0 55 45 55/29/2002 4 4 13 5 NA <1.0 61 50 66/19/2002 5 6 15 6 NA <1.0 67 55 79/25/2002 4 5 11 4 NA <1.0 39 32 5
11/20/2002 28 15 26 12 280 <1.0 140 110 17
73
74
C6: 531SJC503 – Lone Tree Creek at Austin Road continued…
DateChloride (mg/L)
Sulfate (mg/L)
Calcium (mg/L)
Magnesium (mg/L)
TDS (mg/L)
Carbonate (mg/L)
Bicarbonate (mg/L)
Total Alkalinity
(mg/L)Sodium (mg/L)
Count 23 22 24 24 16 24 24 24 24Min 3 4 6 3 54 0.5 34 28 3Max 41 21 37 17 410 0.5 300 250 27Mean 15 10 18 9 220 0.5 110 92 11Geo Mean 11 9 17 8 200 0.5 94 79 9Median 16 10 17 8 230 0.5 97 82 12Quartile 1 4 5 13 5 190 0.5 60 49 6Quartile 3 19 13 24 11 273 0.5 140 110 14NOTE: For values reported as < (less than), half the detection limit was used.
NA = Data not applicableINA = Site was inaccessibleDRY = Site had no flow
C6: 531SJC503 – Lone Tree Creek at Austin Road continued…
Date Result Control Result Control
Result (million/m
l)
Control (million/m
l) MDD(%)06/19/2001 100 100 100 9011/22/2004 100 100 100 10012/28/2004 100 100 100 10001/26/2005 95 97.5 0* 10002/23/2005 100 100 100 10003/29/2005 100 100 100 10004/26/2005 90 10005/24/2005 85* 100 100 10006/28/2005 95 100 100 10007/26/2005 100 100 100 10008/23/2005 97.5 100 100 10009/27/2005 100 100 100 100
Count 12 12 11 11 N/A N/A N/A
* Significantly reduced from the lab control.** Significantly greater than the lab control.^ Fish were from a "forced hatch," duplicate failed QA.1 Duplicate sample for the set was low - 77% recovery.
3 Samples qualified, but duplicate sample recovery for the set was high - 126% (53.8%/42.5%)NA = Data not applicableINA = Site was inaccessibleDRY = Site had no flow
2 Testing for the Fathead minnow was initiated when samples were approx. 48h old due to untimely shipping of fish by fish supplier.
96h Acute Fathead Minnow
(% Survival)
48h Acute Ceriodaphnia Dubia
(% Survival) Algae Cell Growth
75
C7: 531SJC504 – French Camp Slough at Airport Way Station Code:531SJC504
Location: Latitude 37.88167, Longitude -121.24944
Date TimeTemp (ºC)
Field SC (umhos) pH
Dissolved Oxygen (mg/L)
Turbidity (ntu)
10/24/2000 9:35 AM 12.0 289 7.211/28/2000 9:55 AM 9.0 738 8.412/27/2000 9:40 AM 5.8 714 8.71/23/2001 9:30 AM 7.7 402 8.02/20/2001 9:51 AM 11.4 239 7.23/27/2001 9:49 AM 14.6 84 7.24/24/2001 2:51 PM DRY DRY DRY5/29/2001 10:10 AM 19.5 104 6.66/26/2001 9:59 AM 19.4 201 7.8 8.57/24/2001 8:59 AM 22.3 133 7.4 6.98/28/2001 9:11 AM 21.6 138 7.6 8.19/25/2001 10:00 AM 18.2 107 7.6 8.9
10/23/2001 9:31 AM 16.0 296 7.7 7.911/27/2001 9:27 AM 8.0 323 7.4 6.812/26/2001 10:13 AM 9.6 255 7.0 NA1/29/2002 8:46 AM 6.3 187 8.0 13.22/26/2002 8:39 AM 13.1 255 8.0 12.93/26/2002 9:53 AM 13.3 146 7.2 10.34/23/2002 9:59 AM 18.4 149 7.5 8.35/28/2002 9:12 AM 19.7 167 7.1 0.46/18/2002 9:11 AM 21.6 162 7.5 6.77/31/2002 9:08 AM 22.5 172 7.6 6.3 45.78/27/2002 9:50 AM 20.6 131 NA NA9/24/2002 9:30 AM 18.9 107 7.6 8.0
10/29/2002 9:59 AM 13.4 343 7.5 11.0 7.011/19/2002 8:55 AM 9.9 317 7.0 6.312/17/2002 8:22 AM 11.4 182 7.4 8.1 3351/28/2003 9:04 AM 11.9 390 7.8 9.9 13.01/28/2004 12:04 PM 10.9 260 8.6 NA 16.82/24/2004 12:48 PM 13.4 203 7.9 10.1 NA3/24/2004 10:42 AM 15.6 127 7.7 9.8 57.04/28/2004 10:52 AM 20.8 144 7.6 9.2 50.25/26/2004 1:00 PM 22.6 139 7.7 9.0 46.46/23/2004 11:59 AM 23.2 144 7.7 8.8 NA7/28/2004 12:32 PM 25.7 181 7.7 6.7 NA8/25/2004 12:50 PM 23.2 95 7.3 5.2 NA9/29/2004 1:03 PM 18.7 155 7.7 8.2 NA
10/27/2004 12:44 PM 13.3 257 7.8 10.711/22/2004 1:39 PM 9.8 281 7.9 9.1
76
C7: 531SJC504 – French Camp Slough at Airport Way continued…
Date TimeTemp (ºC)
Field SC (umhos) pH
Dissolved Oxygen (mg/L)
Turbidity (ntu)
12/28/2004 11:44 AM 9.6 158 7.7 10.11/26/2005 12:04 PM 10.3 218 7.9 10.32/23/2005 11:23 AM 14.4 170 7.9 10.23/29/2005 1:00 PM 15.1 153 7.9 10.64/26/2005 1:14 PM 18.4 215 7.8 11.05/24/2005 11:37 AM 21.0 122 7.6 8.66/28/2005 11:58 AM 20.8 161 7.6 8.27/26/2005 11:49 AM 24.4 138 7.5 6.28/23/2005 11:56 AM 22.9 171 7.4 7.39/27/2005 12:53 PM 18.7 107 7.6 9.4
Count 48 48 47 38 8Min 5.8 84 6.6 0.4 7.0Max 25.7 738 8.7 13.2 335Mean 16.0 215 7.6 8.6 71.4Geo Mean 15.0 190 7.6 8.0 36.4Median 15.8 171 7.6 8.7 46.1Quartile 1 11.4 139 7.4 7.5 15.9Quartile 3 20.8 256 7.8 10.1 51.9NOTE: For values reported as < (less than), half the detection limit was used.
NA = Data not applicableINA = Site was inaccessibleDRY = Site had no flow
77
C7: 531SJC504 – French Camp Slough at Airport Way continued…
DateTSS
(mg/L)TOC
(mg/L)Total Coli
MPNE. coli MPN
10/24/2000 10 2.311/28/2000 17 <112/27/2000 <6 <11/23/2001 15 212/20/2001 34 113/27/2001 24 NA5/29/2001 80 5.66/26/2001 50 7.77/24/2001 7.38/28/2001 66 7.99/25/2001 NA 8.6
10/23/2001 152/26/2002 NA3/26/2002 3.74/23/2002 NA5/28/2002 346/18/2002 7.67/31/2002 >2419.6 2728/27/2002 3.59/24/2002 5.3
10/29/2002 4.111/19/2002 1112/17/2002 121/28/2004 >2419.6 292/24/2004 >2419.6 763/24/2004 727 3084/28/2004 >2419.6 2615/26/2004 >2419.6 2916/23/2004 >2419.6 1357/28/2004 >2419.6 1538/25/2004 >2419.6 969/29/2004 >2419.6 1203
10/27/2004 13 >2419.6 198611/22/2004 26 >2419.6 1712/28/2004 4.5 >2419.6 621/26/2005 6.0 >2419.6 502/23/2005 7.5 >2419.6 2013/29/2005 7.7 >2419.6 1624/26/2005 NA >2419.6 4115/24/2005 NA >2419.6 770
78
79
DateTSS
(mg/L)TOC
(mg/L)Total Coli
MPNE. coli MPN
6/28/2005 4.5 >2419.6 9807/26/2005 NA >2419.6 1088/23/2005 4.9 >2419.6 609/27/2005 5.2 >2419.6 236
Count 9 28 22 2
C7: 531SJC504 – French Camp Slough at Airport Way continued…
2Min 3 0.5 727 17Max 80 34 2420 1986Mean 33 8.9 NA NAGeo Mean 23 6.3 2291 182Median 24 7.4 2420 182Quartile 1 15 4.5 2420 81Quartile 3 50 11 2420 304NOTE: For values reported as < (less than), half the detection limit was used
For values reported as > (greater than), 2420 was used
NA =INA =DRY
Data not applicable Site was inaccessible
= Site had no flow
C7: 531SJC504 – French Camp Slough at Airport Way continued…
DateNitrate (mg/L)
Nitrate-N (mg/L)
TKN (mg/L)
Ammonia-N (mg/L)
Phosphorus (mg/L)
Ortho-phosphate-
P (mg/L)
Potassium (mg/L)
BOD 5-Day (mg/L)
BOD 10-Day (mg/L)
10/24/2000 7.6 <2 0.2 <1 5 1.0 1.811/28/2000 29 <2 0.2 <1 12 2.1 3.512/27/2000 24 <2 <0.1 <1 10 1.3 2.31/23/2001 15 3.5 0.9 1.3 25 5.2 11.32/20/2001 6.0 <2 0.5 0.7 14 3.1 5.83/27/2001 3.3 <2 0.2 <1 3.5 1.4 2.15/29/2001 2.6 <2 0.5 <1 4.8 3.0 4.46/26/2001 7.3 <2 0.5 <1 4.6 2.2 3.58/28/2001 3.9 <2 0.3 <1 4.09/25/2001 3.0 <2 0.3 <1 4.6
10/23/2001 9.2 <2 0.6 <1 11 3.0 4.811/27/2001 NA NA NA 1.5 37 16.4 33.512/26/2001 NA NA 0.6 NA 11 3.7 6.51/29/2002 NA 1.0 0.2 0.1 5.0 2.0 3.02/26/2002 NA NA 0.1 <0.03 1.9 1.8 2.93/26/2002 NA 0.7 0.1 0.1 2.3 2.1 3.74/23/2002 NA NA NA NA 5.6 3.3 5.35/28/2002 NA NA NA 1.3 10 8.7 17.06/18/2002 NA 1.1 NA 0.5 7.5 3.5 5.58/27/2002 NA 0.8 0.4 0.3 NA 1.0 1.89/24/2002 NA NA 0.5 0.3 4.1 1.8 3.1
10/29/2002 NA 0.6 0.3 0.3 7.6 1.4 2.811/19/2002 NA 3.1 1.2 0.8 21 4.7 8.512/17/2002 NA 4.1 1.5 <0.03 17 8.3 16.81/28/2003 NA 1.3 0.3 0.2 6.8 1.3 2.3
80
C7: 531SJC504 – French Camp Slough at Airport Way continued…
DateNitrate (mg/L)
Nitrate-N (mg/L)
TKN (mg/L)
Ammonia-N (mg/L)
Phosphorus (mg/L)
Ortho-phosphate-
P (mg/L)
Potassium (mg/L)
BOD 5-Day (mg/L)
BOD 10-Day (mg/L)
Count 11 NA 19 NA 21 23 24 23 23Min 2.6 NA 0.6 NA 0.1 0.02 1.9 1.0 1.8Max 29.0 NA 4.1 NA 1.5 1.5 37.0 16.4 33.5Mean 10.1 NA 1.4 NA 0.5 0.5 9.8 3.6 6.6Geo Mean 7.3 NA 1.2 NA 0.3 0.3 7.5 2.7 4.7Median 7.3 NA 1.0 NA 0.3 0.5 7.2 2.2 3.7Quartile 1 3.6 NA 1.0 NA 0.2 0.3 4.6 1.6 2.9Quartile 3 12.1 NA 1.1 NA 0.5 0.5 11.3 3.6 6.2NOTE: For values reported as < (less than), half the detection limit was used.
NA = Data not applicableINA = Site was inaccessibleDRY = Site had no flow
81
C7: 531SJC504 – French Camp Slough at Airport Way continued…
DateHardness
(mg/L)
Total Arsenic (ug/L)
Total Cadmium
(ug/L)
Total Chromium
(ug/L)
Total Copper (ug/L)
Total Lead (ug/L)
Total Nickel (ug/L)
Total Zinc (ug/L)
Total Mercury (ug/L)
10/24/2000 110 1.4 4.0 <5 <5 6.211/28/2000 290 2.0 3.0 <5 <5 <212/27/2000 280 2.0 3.5 <5 <5 2.11/23/2001 130 1.6 17 <5 <5 8.22/20/2001 83 2.8 13 <5 <5 113/27/2001 31 1.7 5.0 <5 <5 7.05/29/2001 44 2.5 7.4 <5 <5 126/26/2001 <2 <1 2.7 4.8 <5 <5 10 <0.27/24/2001 NA NA 1.8 5.4 <5 <5 8.0 NA8/28/2001 42 <2 <1 2.8 6.0 <5 <5 119/25/2001 43 <4 <0.1 2.5 5.7 <5 <5 11 <0.2
10/23/2001 100 <4 <0.1 <1 5.1 <5 <5 8.7 NA11/27/2001 85 <4 <0.1 3.3 16 <5 6.2 20 <0.212/26/2001 84 <4 <0.1 3.6 14 <5 5.0 18 <0.21/29/2002 73 <4 <0.1 <1 3.7 <5 <5 2.7 <0.23/26/2002 58 <4.0 <0.1 2.5 7.4 <5.0 10 11 <0.24/23/2002 61 <4.0 <0.1 <1.0 4.7 <5.0 <5.0 4.3 <0.25/28/2002 59 <4.0 <0.1 2.3 13 <5.0 <5.0 17 <0.26/18/2002 67 <4.0 <0.1 <1.0 4.4 <5.0 <5.0 7.3 <0.29/24/2002 43 <4.0 <0.1 1.4 7.0 <5.0 <5.0 6.6 <0.2
10/29/2002 130 <4.0 <0.1 <1.0 3.6 <5.0 <5.0 <2.0 <0.211/19/2002 110 <4.0 <0.1 1.4 7.9 <5.0 <5.0 8.3 <0.2
82
C7: 531SJC504 – French Camp Slough at Airport Way continued…
DateHardness
(mg/L)
Total Arsenic (ug/L)
Total Cadmium
(ug/L)
Total Chromium
(ug/L)
Total Copper (ug/L)
Total Lead (ug/L)
Total Nickel (ug/L)
Total Zinc (ug/L)
Total Mercury (ug/L)
Count 20 14 14 22 22 22 22 22 12Min 31.0 1.0 0.1 0.5 3.0 2.5 2.5 1.0 0.1Max 290.0 2.0 0.5 3.6 17.0 2.5 10.0 20.0 0.1Mean 96.2 1.9 0.1 1.9 7.3 2.5 3.1 8.7 0.1Geo Mean 79.7 1.8 0.1 1.5 6.4 2.5 2.9 6.9 0.1Median 78.0 2.0 0.1 1.9 5.6 2.5 2.5 8.3 0.1Quartile 1 54.5 2.0 0.1 1.4 4.5 2.5 2.5 6.3 0.1Quartile 3 110.0 2.0 0.1 2.5 7.8 2.5 2.5 11.0 0.1NOTE: For values reported as < (less than), half the detection limit was used.
NA = Data not applicableINA = Site was inaccessibleDRY = Site had no flow
83
C7: 531SJC504 – French Camp Slough at Airport Way continued…
DateHardness
(mg/L)
Dissolved Arsenic (ug/L)
Dissolved Cadmium
(ug/L)
Dissolved Chromium
(ug/L)
Dissolved Copper (ug/L)
Dissolved Lead (ug/L)
Dissolved Nickel (ug/L)
Dissolved Zinc
(ug/L)
Dissolved Mercury (ug/L)
10/24/2000 11011/28/2000 290 1.3 2.0 <5 <5 <212/27/2000 280 1.0 2.5 <5 <5 <21/23/2001 130 <1 14 <5 <5 4.22/20/2001 83 <1 9.5 <5 <5 3.83/27/2001 31 <1 2.2 <5 <5 2.85/29/2001 44 <1 3.4 <5 <5 3.66/26/2001 <2 <1 <1 1.2 <5 <5 <2 <0.27/24/2001 NA NA NA NA NA NA NA NA8/28/2001 42 <2 <1 <1 4.2 <5 <5 9.09/25/2001 43 <4 <0.1 <1 2.8 <5 <5 2.8 <0.2
10/23/2001 100 <4 <0.1 <1 5.0 <5 <5 4.4 NA11/27/2001 85 <4 <0.1 <1 11 <5 <5 13 <0.212/26/2001 84 <4 <0.1 <1 7.2 <5 <5 6.5 <0.21/29/2002 73 <4 <0.1 <1 2.1 <5 <5 <2 <0.23/26/2002 58 <4.0 <0.1 <1.0 4.3 <5.0 <5.0 5.3 <0.24/23/2002 61 <4.0 <0.1 <1.0 4.4 <5.0 <5.0 4.9 <0.25/28/2002 59 <4.0 <0.1 <1.0 6.7 <5.0 <5.0 5.8 <0.26/18/2002 67 <4.0 <0.1 <1.0 3.1 <5.0 <5.0 5.1 <0.29/24/2002 43 <4.0 <0.1 <1.0 2.7 <5.0 <5.0 2.0 <0.2
10/29/2002 130 <4.0 <0.1 <1.0 2.5 <5.0 <5.0 <2.0 <0.211/19/2002 110 <4.0 <0.1 <1.0 6.2 <5.0 <5.0 4.5 <0.2
Count 20 14 14 20 20 20 20 20 12Min 31.0 1.0 0.1 0.5 1.2 2.5 2.5 1.0 0.1Max 290.0 2.0 0.5 1.3 14.0 2.5 2.5 13.0 0.1Mean 96.2 1.9 0.1 0.6 4.9 2.5 2.5 4.1 0.1Geo Mean 79.7 1.8 0.1 0.5 4.0 2.5 2.5 3.2 0.1Median 78.0 2.0 0.1 0.5 3.8 2.5 2.5 4.0 0.1Quartile 1 54.5 2.0 0.1 0.5 2.5 2.5 2.5 1.8 0.1Quartile 3 110.0 2.0 0.1 0.5 6.3 2.5 2.5 5.2 0.1NOTE: For values reported as < (less than), half the detection limit was used.
NA = Data not applicableINA = Site was inaccessibleDRY = Site had no flow
84
85
C7: 531SJC504 – French Camp Slough at Airport Way continued…
DateChloride (mg/L)
Sulfate (mg/L)
Calcium (mg/L)
Magnesium (mg/L)
TDS (mg/L)
Carbonate (mg/L)
Bicarbonate (mg/L)
Total Alkalinity
(mg/L)Sodium (mg/L)
10/24/2000 14 15 24 12 160 <1 130 100 1411/28/2000 54 50 52 39 460 10 270 240 4312/27/2000 55 53 45 40 410 30 350 230 451/23/2001 23 25 27 15 280 <1 150 120 192/20/2001 13 18 18 9 210 <1 90 73 123/27/2001 3 4 7 3 NA <1 39 32 35/29/2001 4 4 10 5 110 <1 40 40 48/28/2001 5 5 11 3 110 <1 63 52 69/25/2001 4 4 10 4 NA <1 51 42 5
10/23/2001 18 14 20 12 NA <1 110 92 1611/27/2001 22 12 18 9 240 <1 120 98 1212/26/2001 15 28 18 10 200 <1 76 62 141/29/2002 8 13 15 8 120 <1 62 76 93/26/2002 6 12 12 7 84 <1.0 60 50 84/23/2002 4 6 14 6 100 <1.0 68 56 75/28/2002 5 5 14 6 NA <1.0 78 64 66/18/2002 5 7 16 7 NA <1.0 79 NA 79/24/2002 4 4 10 4 NA <1.0 45 37 4
10/29/2002 20 12 29 14 240 <1.0 160 130 1911/19/2002 20 20 24 11 230 <1.0 120 96 13
Count 20 20 20 20 14 20 20 19 20Min 3 4 7 3 84 0.5 39 32 3Max 55 53 52 40 460 30 350 240 45Mean 15 16 20 11 210 2 110 89 13Geo Mean 10 11 17 9 190 0.7 90 75 10Median 11 12 17 9 200 0.5 79 73 11Quartile 1 5 5 12 6 110 0.5 62 51 6Quartile 3 20 19 24 12 240 0.5 120 99 15NOTE: For values reported as < (less than), half the detection limit was used.
NA = Data not applicableINA = Site was inaccessibleDRY = Site had no flow
C7: 531SJC504 – French Camp Slough at Airport Way continued…
Date Result Control Result Control
Result (million/m
l)
Control (million/m
l) MDD(%)11/22/2004 100 100 100 10012/28/2004 100 100 100 1001/26/2005 95 97.5 100 1002/23/2005 77.5* 100 100 1003/29/2005 100 100 100 1004/26/2005 62.5* 100 100 1005/24/2005 85* 100 100 1006/28/2005 75* 100 95 1007/26/2005 100 100 100 1008/23/2005 97.5 100 100 1009/27/2005 100 100 100 100
Count 11 11 11 11 N/A N/A N/A
* Significantly reduced from the lab control.** Significantly greater than the lab control.^ Fish were from a "forced hatch," duplicate failed QA.1 Duplicate sample for the set was low - 77% recovery.
3 Samples qualified, but duplicate sample recovery for the set was high - 126% (53.8%/42.5%)NA = Data not applicableINA = Site was inaccessibleDRY = Site had no flow
2 Testing for the Fathead minnow was initiated when samples were approx. 48h old due to untimely shipping of fish by fish supplier.
96h Acute Fathead Minnow
(% Survival)
48h Acute Ceriodaphnia Dubia
(% Survival) Algae Cell Growth
86
APPENDIX D
SOUTHEAST BASIN
APPENDIX D: SOUTHEAST BASIN D1: 545MAD006 – Lone Willow Slough at Road No. 9 ……………………………………...03 D2: 541MER015 – Santa Rita Slough at HWY 152………………………………………...04-09 D3: 535MER577 – Deep Slough at Green House Road…………………………………….10-20 D4: 535MER007 – Bear Creek near Bert Crane Road………………………………………21-32
2
D1: 545MAD006 – Lone Willow Slough at Road No. 9 Station Code: 545MAD006
Location: Latitude 36.86694444, Longitude -120.38194444
Date TimeTemp (ºC)
Field SC (umhos) pH
Dissolved Oxygen (mg/L)
Turbidity (ntu)
10/26/2000 NA DRY DRY DRY DRY11/30/2000 5:30 DRY DRY DRY DRY12/28/2000 7:30 DRY DRY DRY DRY1/25/2001 8:10 DRY DRY DRY DRY2/22/2001 7:40 DRY DRY DRY DRY3/29/2001 7:40 DRY DRY DRY DRY4/26/2001 14:30 DRY DRY DRY DRY5/31/2001 11:00 DRY DRY DRY DRY6/28/2001 9:00 NA NA NA NA7/26/2001 9:30 DRY DRY DRY DRY8/30/2001 10:00 DRY DRY DRY DRY9/27/2001 9:06 DRY DRY DRY DRY
10/25/2001 8:43 DRY DRY DRY DRY1/31/2002 9:00 DRY DRY DRY DRY4/24/2002 8:34 DRY DRY DRY DRY
10/31/2002 9:30 DRY DRY DRY DRY1/30/2003 9:17 DRY DRY DRY DRY4/24/2003 9:30 DRY DRY DRY DRY7/31/2003 9:05 DRY DRY DRY DRY8/28/2003 0:00 DRY DRY DRY DRY
Count NA NA NA NA NAMin NA NA NA NA NAMax NA NA NA NA NAMean NA NA NA NA NAGeo Mean NA NA NA NA NAMedian NA NA NA NA NAQuartile 1 NA NA NA NA NAQuartile 3 NA NA NA NA NANOTE: For values reported as < (less than), half the detection limit was used.
NA = Data not applicableINA = Site was inaccessibleDRY = Site had no flow
3
D2: 541MER015 – Santa Rita Slough at HWY 152 Station Code:541MER015
Location: Latitude 37.04750, Longitude -120.59361
Date TimeTemp (ºC)
Field SC (umhos) pH
Dissolved Oxygen (mg/L)
Turbidity (ntu)
10/26/2000 DRY DRY DRY DRY DRY11/30/2000 6:52 AM DRY DRY DRY DRY12/28/2000 8:20 AM DRY DRY DRY DRY1/25/2001 9:23 AM 5.7 731 7.12/22/2001 8:45 AM 9.6 820 8.23/29/2001 9:00 AM 16.3 830 7.74/26/2001 12:40 PM DRY DRY DRY DRY5/31/2001 12:00 PM DRY DRY DRY DRY6/28/2001 10:34 AM 21.2 615 7.0 6.27/26/2001 DRY DRY DRY DRY DRY8/30/2001 9:00 AM 21.7 643 7.4 NA9/27/2001 10:00 AM DRY DRY DRY DRY
Count 5 5 5 1 NAMin 5.7 615 7.0 6.2 NAMax 21.7 830 8.2 6.2 NAMean 14.9 728 7.5 6.2 NAGeo Mean 13.3 722 7.5 6.2 NAMedian 16.3 731 7.4 6.2 NAQuartile 1 9.6 643 7.1 6.2 NAQuartile 3 21.2 820 7.7 6.2 NANOTE: For values reported as < (less than), half the detection limit was used.
NA = Data not applicableINA = Site was inaccessibleDRY = Site had no flow
4
5
DateTSS
(mg/L)TOC
(mg/L)Total Coli
MPNE. coli MPN
1/25/2001 42 242/22/2001 21 4.33/29/2001 NA <16/28/2001 10 8.48/30/2001 <5 12
Count 4 5 NA NAMin 3 0.5 NA NAMax 42 24 NA NAMean 19 10 NA NAGeo Mean 12 6 NA NAMedian 16 8.4 NA NAQuartile 1 8 4.3 NA NAQuartile
D2: 541MER015 – Santa Rita Slough at HWY 152 continued…
3 26 12 NA NANOTE: For values reported as < (less than), half the detection limit was used
For values reported as > (greater than), 2420 was used
NA =INA =DRY
Data not applicable Site was inaccessible
= Site had no flow
D2: 541MER015 – Santa Rita Slough at HWY 152 continued…
DateNitrate (mg/L)
Nitrate-N (mg/L)
TKN (mg/L)
Ammonia-N (mg/L)
Phosphorus (mg/L)
Ortho-phosphate-
P (mg/L)
Potassium (mg/L)
BOD 5-Day (mg/L)
BOD 10-Day (mg/L)
1/25/2001 NA NA 0.5 <1 23 8.4 16.92/22/2001 10 <2 NA <1 8.4 2.4 4.03/29/2001 6.9 NA 1 1.5 8.9 2.6 5.96/28/2001 <2 <2 0.3 <1 6 1.6 2.98/30/2001 <2 <2 0.2 <1 5
Count 4 NA 3 NA 4 5 5 4 4Min 1.0 NA 1.0 NA 0.2 0.5 5.0 1.6 2.9Max 10.0 NA 1.0 NA 1.0 1.5 23.0 8.4 16.9Mean 4.7 NA 1.0 NA 0.5 0.7 10.3 3.8 7.4Geo Mean 2.9 NA 1.0 NA 0.4 0.6 8.8 3.0 5.8Median 4.0 NA 1.0 NA 0.4 0.5 8.4 2.5 5.0Quartile 1 1.0 NA 1.0 NA 0.3 0.5 6.0 2.2 3.7Quartile 3 7.7 NA 1.0 NA 0.6 0.5 8.9 4.1 8.7NOTE: For values reported as < (less than), half the detection limit was used.
NA = Data not applicableINA = Site was inaccessibleDRY = Site had no flow
D2: 541MER015 – Santa Rita Slough at HWY 152 continued…
DateHardness
(mg/L)
Total Arsenic (ug/L)
Total Cadmium
(ug/L)
Total Chromium
(ug/L)
Total Copper (ug/L)
Total Lead (ug/L)
Total Nickel (ug/L)
Total Zinc (ug/L)
Total Mercury (ug/L)
1/25/2001 260 2.4 5.4 <5 6.1 102/22/2001 230 <1 2.4 <5 <5 6.73/29/2001 200 <1 2.5 <5 <5 4.46/28/2001 150 6.4 <1 <1 <1 <5 <5 <2 <0.28/30/2001 120 4.6 <1 <1 <1 <5 <5 <2
Count 5 2 2 5 5 5 5 5 1Min 120.0 4.6 0.5 0.5 0.5 2.5 2.5 1.0 0.1Max 260.0 6.4 0.5 2.4 5.4 2.5 6.1 10.0 0.1Mean 192.0 5.5 0.5 0.9 2.3 2.5 3.2 4.6 0.1Geo Mean 184.8 5.4 0.5 0.7 1.5 2.5 3.0 3.1 0.1Median 200.0 5.5 0.5 0.5 2.4 2.5 2.5 4.4 0.1Quartile 1 150.0 5.1 0.5 0.5 0.5 2.5 2.5 1.0Quartile 3 230.0 6.0 0.5 0.5 2.5 2.5 2.5 6.7NOTE: For values reported as < (less than), half the detection limit was used.
NA = Data not applicableINA = Site was inaccessibleDRY = Site had no flow
7
D2: 541MER015 – Santa Rita Slough at HWY 152 continued…
DateHardness
(mg/L)
Dissolved Arsenic (ug/L)
Dissolved Cadmium
(ug/L)
Dissolved Chromium
(ug/L)
Dissolved Copper (ug/L)
Dissolved Lead (ug/L)
Dissolved Nickel (ug/L)
Dissolved Zinc
(ug/L)
Dissolved Mercury (ug/L)
1/25/2001 260 <1 2.3 <5 <5 3.42/22/2001 230 <1 1.1 <5 <5 43/29/2001 200 <1 2.5 <5 <5 2.76/28/2001 150 5.9 <1 <1 <1 <5 <5 <2 <0.28/30/2001 120 4.6 <1 <1 <1 <5 <5 <2
Count 5 2 2 5 5 5 5 5 1Min 120.0 4.6 0.5 0.5 0.5 2.5 2.5 1.0 0.1Max 260.0 5.9 0.5 0.5 2.5 2.5 2.5 4.0 0.1Mean 192.0 5.3 0.5 0.5 1.4 2.5 2.5 2.4 0.1Geo Mean 184.8 5.2 0.5 0.5 1.1 2.5 2.5 2.1 0.1Median 200.0 5.3 0.5 0.5 1.1 2.5 2.5 2.7 0.1Quartile 1 150.0 4.9 0.5 0.5 0.5 2.5 2.5 1.0 0.1Quartile 3 230.0 5.6 0.5 0.5 2.3 2.5 2.5 3.4 0.1NOTE: For values reported as < (less than), half the detection limit was used.
NA = Data not applicableINA = Site was inaccessibleDRY = Site had no flow
8
9
D2: 541MER015 – Santa Rita Slough at HWY 152 continued…
DateChloride (mg/L)
Sulfate (mg/L)
Calcium (mg/L)
Magnesium (mg/L)
TDS (mg/L)
Carbonate (mg/L)
Bicarbonate (mg/L)
Total Alkalinity
(mg/L)Sodium (mg/L)
1/25/2001 61 130 67 23 470 <1 100 80 322/22/2001 81 150 59 21 510 <1 120 98 733/29/2001 92 120 46 21 440 <1 130 110 876/28/2001 84 71 38 14 370 <1.0 140 120 718/30/2001 100 49 26 15 360 <1 120 97 76
Count 5 5 5 5 5 5 5 5 5Min 61 49 26 14 360 0.5 100 80 32Max 100 150 67 23 510 0.5 140 120 87Mean 84 104 47 19 430 0.5 122 101 68Geo Mean 82 96 45 18 430 0.5 121 100 64Median 84 120 46 21 440 0.5 120 98 73Quartile 1 81 71 38 15 370 0.5 120 97 71Quartile 3 92 130 59 21 470 0.5 130 110 76NOTE: For values reported as < (less than), half the detection limit was used.
NA = Data not applicableINA = Site was inaccessibleDRY = Site had no flow
D3: 535MER577 – Deep Slough at Green House Road Station Code:535MER577
Location: Latitude 37.22972, Longitude -120.72833
Date TimeTemp (ºC)
Field SC (umhos) pH
Dissolved Oxygen (mg/L)
Turbidity (ntu)
10/26/2000 10:15 AM 13.1 292 7.611/30/2000 7:40 AM 9.0 507 7.412/28/2000 9:15 AM 7.3 597 7.41/25/2001 10:16 AM 9.7 544 7.32/22/2001 10:00 AM 15.6 658 7.83/29/2001 9:40 AM 19.0 698 8.44/26/2001 12:01 PM 24.1 298 7.25/31/2001 12:51 PM 29.5 862 8.96/28/2001 11:17 AM 22.5 671 8.2 5.37/26/2001 12:45 PM 28.9 597 8.6 NA8/30/2001 11:50 AM 24.1 311 8.6 NA9/27/2001 10:39 AM 20.9 480 8.3 7.6
10/25/2001 10:16 AM 15.9 399 8.5 9.311/29/2001 12:49 PM 10.0 459 8.3 11.912/27/2001 11:47 AM 8.9 330 7.9 9.91/31/2002 10:28 AM 5.6 414 8.2 13.42/28/2002 12:47 PM 16.3 752 8.6 15.83/28/2002 11:24 AM 17.5 401 8.2 10.24/24/2002 10:11 AM 19.3 566 8.6 7.85/30/2002 9:15 AM 23.5 509 7.8 NA6/20/2002 10:01 AM 24.0 591 8.1 6.6 1867/30/2002 10:12 AM 23.8 782 8.8 7.4 3198/29/2002 10:01 AM 21.3 966 8.5 7.5 4809/26/2002 DRY DRY DRY DRY DRY
10/17/2002 10:54 AM 17.3 515 7.8 6.7 80.210/31/2002 10:50 AM 13.9 640 8.0 8.7 79.311/21/2002 10:36 AM 12.0 325 7.8 9.8 68.312/19/2002 10:07 AM 8.4 184 7.5 9.8 1131/14/2003 10:05 AM 11.2 290 7.8 9.9 76.51/30/2003 10:46 AM 13.0 385 7.3 10.3 48.63/27/2003 12:20 PM 16.3 862 8.1 12.2 2114/24/2003 11:05 AM 17.0 602 7.8 7.4 57.85/29/2003 10:10 AM 25.7 871 7.7 5.1 91.46/26/2003 9:46 AM 24.3 628 8.3 7.9 50.07/31/2003 10:27 AM DRY DRY DRY DRY DRY8/28/2003 10:10 AM DRY DRY DRY DRY DRY9/25/2003 10:00 AM DRY DRY DRY DRY DRY
10/30/2003 10:22 AM DRY DRY DRY DRY DRY
D3: 535MER577 – Deep Slough at Green House Road continued…
Date TimeTemp (ºC)
Field SC (umhos) pH
Dissolved Oxygen (mg/L)
Turbidity (ntu)
11/20/2003 10:51 AM 12.0 144 7.8 8.9 59.61/29/2004 10:28 AM 10.1 506 8.0 13.0 95.02/26/2004 10:23 AM 11.5 421 7.9 10.3 NA3/24/2004 10:43 AM 19.3 488 8.3 8.9 NA4/29/2004 10:05 AM 18.5 983 8.4 7.1 70.45/27/2004 10:26 AM 22.2 742 7.7 4.2 71.16/24/2004 10:25 AM 23.5 598 7.7 7.8 NA7/29/2004 9:54 AM 23.7 526 7.7 6.6 NA8/26/2004 10:08 AM 22.7 409 8.0 5.8 NA9/30/2004 9:46 AM DRY DRY DRY DRY DRY
10/28/2004 10:05 AM 12.8 358 8.2 8.711/23/2004 10:04 AM 8.9 436 7.7 11.912/29/2004 9:30 AM 9.3 401 7.9 10.31/27/2005 9:59 AM 10.6 313 8.0 11.92/24/2005 8:45 AM 13.7 208 7.8 8.03/29/2005 11:37 AM 13.7 166 7.9 8.04/28/2005 9:55 AM 18.1 427 7.9 7.35/26/2005 11:04 AM 19.6 60 7.5 8.76/30/2005 10:14 AM 26.5 48 7.9 7.27/28/2005 10:03 AM 26.6 375 8.1 6.08/25/2005 10:15 AM 23.8 271 7.9 5.99/29/2005 10:14 AM 20.9 272 6.6 6.8
Count 54 54 54 43 17Min 5.6 48 6.6 4.2 48.6Max 29.5 983 8.9 15.8 480Mean 17.4 484 8.0 8.7 127Geo Mean 16.1 423 8.0 8.4 98.8Median 17.4 470 7.9 8.0 79.3Quartile 1 12.0 326 7.7 7.2 68.3Quartile 3 23.3 601 8.3 10.1 113NOTE: For values reported as < (less than), half the detection limit was used.
NA = Data not applicableINA = Site was inaccessibleDRY = Site had no flow
11
D3: 535MER577 – Deep Slough at Green House Road continued…
DateTSS
(mg/L)TOC
(mg/L)Total Coli
MPNE. coli MPN
10/26/2000 80 3.911/30/2000 34 5.612/28/2000 NA 6.41/25/2001 91 9.52/22/2001 68 3.53/29/2001 NA <14/26/2001 6.95/31/2001 100 116/28/2001 220 127/26/2001 108/30/2001 95 129/27/2001 110
10/25/2001 1411/29/2001 <11/31/2002 3.23/28/2002 NA4/24/2002 145/30/2002 5.16/20/2002 6.27/30/2002 >2419.6 9
10/17/2002 >2419.6 86610/31/2002 NA11/21/2002 4.712/19/20021/14/2003 >2419.6 1841/30/20033/27/2003 4.44/24/2003 NA >2419.6 >2419.65/29/2003 116/26/2003 117/31/2003 DRY DRY8/28/2003 DRY DRY9/25/2003 DRY DRY
10/30/2003 DRY DRY11/20/2003 >2419.6 1991/29/2004 866 1092/26/2004 2420 4883/24/2004 >2419.6 4614/29/2004 >2419.6 24205/27/2004 >2419.6 12036/24/2004 >2419.6 111
12
13
DateTSS
(mg/L)TOC
(mg/L)Total Coli
MPNE. coli MPN
7/29/2004 >2419.6 168/26/2004 >2419.6 109/30/2004 DRY DRY
10/28/2004 9.3 >2419.6 173311/23/2004 7.2 >2419.6 112012/29/2004 7.2 >2419.6 14141/27/2005 10 >2419.6 9802/24/2005 8.6 2420 933/29/2005 10 >2419.6 5174/28/2005 6.9 >2419.6 9215/26/2005 3.6 >2419.6 1086/30/2005 NA >2419.6 857/28/2005 NA >2419.6 198/25/2005 4.4 >2419.6 969/29/2005 4.2 >2419.6 153
Coun
D3: 535MER577 – Deep Slough at Green House Road continued…
t 8 31 25 25Min 34 0.5 866 9MaxMeaGeo
220 14 2420 2420n 100 7.3 NA NA Mean 89 6.0 2323 238ian 93 6.9 2420 199rtile 1 77 4.4 2420 96rtile
MedQuaQua 3 100 10 2420 980
E: For values reported as < (less than), half the detection limit was used For values reported as > (greater than), 2420 was used
Data not applicable Site was inaccessible
= Site had no flow
NOT
NA =INA =DRY
D3: 535MER577 – Deep Slough at Green House Road continued…
DateNitrate (mg/L)
Nitrate-N (mg/L)
TKN (mg/L)
Ammonia-N (mg/L)
Phosphorus (mg/L)
Ortho-phosphate-
P (mg/L)
Potassium (mg/L)
BOD 5-Day (mg/L)
BOD 10-Day (mg/L)
10/26/2000 4.1 <2 NA <1 5.4 2.9 4.911/30/2000 3.2 <2 0.3 <1 7.2 5.4 8.212/28/2000 11 <2 0.4 1.1 12 3.8 6.61/25/2001 NA NA 1.1 1.7 16 7.3 15.72/22/2001 23 2.2 NA 1.3 13 4.4 7.93/29/2001 <2 NA 0.6 <1 10 7.5 14.34/26/2001 5.4 <2 0.6 <1 10 4.3 8.45/31/2001 <2 3.7 1.0 <1 9.8 8.3 16.66/28/2001 <2 2.2 0.6 <1 12 6.3 11.68/30/2001 <2 <2 0.3 <1 5.89/27/2001 <2 <2 0.4 <1 7.4
10/25/2001 <2 <2 0.2 <1 7.4 4.6 7.811/29/2001 NA NA NA 0.2 NA 5.2 8.512/27/2001 NA NA 1.3 1.0 9.7 3.1 6.51/31/2002 NA 2.6 0.5 0.4 NA 3.2 8.02/28/2002 NA NA 0.4 0.2 6.9 8.0 14.13/28/2002 NA 1.7 0.8 0.8 7.7 3.2 5.44/24/2002 NA NA 0.3 0.1 6.1 6.0 10.25/30/2002 NA NA NA 0.2 6.3 2.9 5.06/20/2002 NA 1.3 NA 0.2 6.8 4.6 7.88/29/2002 NA 6.2 NA NA 9.1 8.5 17.1
10/31/2002 NA 1.3 0.2 0.1 4.7 4.4 7.011/21/2002 NA 1.2 0.4 0.2 4.4 5.5 9.012/19/2002 NA 1.9 0.3 <0.03 4.4 5.9 8.61/30/2003 NA 1.2 NA 0.5 5.3 2.4 4.0
D3: 535MER577 – Deep Slough at Green House Road continued…
DateNitrate (mg/L)
Nitrate-N (mg/L)
TKN (mg/L)
Ammonia-N (mg/L)
Phosphorus (mg/L)
Ortho-phosphate-
P (mg/L)
Potassium (mg/L)
BOD 5-Day (mg/L)
BOD 10-Day (mg/L)
Count 11 NA 18 NA 18 24 23 23 23Min 1.0 NA 1.0 NA 0.2 0.02 4.4 2.4 4.0Max 23.0 NA 6.2 NA 1.3 1.7 16.0 8.5 17.1Mean 4.8 NA 1.8 NA 0.5 0.5 8.1 5.1 9.3Geo Mean 2.4 NA 1.5 NA 0.5 0.4 7.7 4.8 8.6Median 1.0 NA 1.3 NA 0.4 0.5 7.4 4.6 8.2Quartile 1 1.0 NA 1.0 NA 0.3 0.2 6.0 3.5 6.8Quartile 3 4.8 NA 2.1 NA 0.6 0.5 9.9 6.2 10.9NOTE: For values reported as < (less than), half the detection limit was used.
NA = Data not applicableINA = Site was inaccessibleDRY = Site had no flow
15
D3: 535MER577 – Deep Slough at Green House Road continued…
DateHardness
(mg/L)
Total Arsenic (ug/L)
Total Cadmium
(ug/L)
Total Chromium
(ug/L)
Total Copper (ug/L)
Total Lead (ug/L)
Total Nickel (ug/L)
Total Zinc (ug/L)
Total Mercury (ug/L)
10/26/2000 88 4.8 4.9 <5 6.0 9.711/30/2000 130 2.2 4.0 <5 <5 6.112/28/2000 150 3.0 5.3 <5 5.7 111/25/2001 130 5.2 10 <5 6.4 242/22/2001 170 4.7 6.9 <5 6.1 173/29/2001 200 7.7 7.9 <5 8.8 144/26/2001 92 3.2 5.7 <5 <5 105/31/2001 240 4.2 5.7 <5 7.8 8.26/28/2001 220 14 <1 14 12 <5 15 23 <0.27/26/2001 NA NA 9.0 8.5 <5 9.8 NA NA8/30/2001 110 5.5 <1 8.3 7.0 <5 8.7 139/27/2001 140 5.8 <0.1 6.1 12 <5 8.4 15 <0.2
10/25/2001 130 7.1 <0.1 <1 2.5 <5 <5 <2 NA11/29/2001 140 6.0 <0.1 5.9 5.9 <5 8.0 14 <0.212/27/2001 120 5.5 <0.1 7.9 9.0 <5 8.8 21 <0.22/28/2002 220 5.8 <0.1 3.7 6.9 <5.0 5.6 11 <0.23/28/2002 120 <4.0 <0.1 5.4 5.8 <5.0 NA 18 <0.24/24/2002 170 9.2 <0.1 <1.0 2.6 <5.0 <5.0 <2.0 <0.25/30/2002 160 7.8 <0.1 4.6 4.9 <5.0 6.6 6.8 <0.26/20/2002 190 11 <0.1 8.2 6.7 <5.0 9.0 13 <0.2
10/31/2002 180 8.2 <0.1 3.8 4.9 <5.0 6.9 6.8 <0.211/21/2002 110 <4.0 <0.1 4.5 5.0 <5.0 5.8 7.1 <0.23/27/2003 220 6.6 <0.1 4.6 7.1 <5.0 7.2 9.1 <0.24/24/2003 180 7.3 <0.1 4.4 5.8 <5.0 6.6 6.1 <0.25/29/2003 240 16 <0.1 2.8 4.8 <5.0 6.1 4.7 <0.26/26/2003 190 14 <0.1 <1.0 2.4 <5.0 <5.0 <2.0 NA
16
D3: 535MER577 – Deep Slough at Green House Road continued…
DateHardness
(mg/L)
Total Arsenic (ug/L)
Total Cadmium
(ug/L)
Total Chromium
(ug/L)
Total Copper (ug/L)
Total Lead (ug/L)
Total Nickel (ug/L)
Total Zinc (ug/L)
Total Mercury (ug/L)
Count 25 17 17 26 26 26 25 25 14Min 88.0 2.0 0.1 0.5 2.4 2.5 2.5 1.0 0.1Max 240.0 16.0 0.5 14.0 12.0 2.5 15.0 24.0 0.1Mean 161.6 7.9 0.1 5.0 6.3 2.5 6.6 10.9 0.1Geo Mean 155.3 6.9 0.1 3.9 5.8 2.5 6.0 8.3 0.1Median 160.0 7.1 0.1 4.6 5.8 2.5 6.6 10.0 0.1Quartile 1 130.0 5.8 0.1 3.3 4.9 2.5 5.7 6.8 0.1Quartile 3 190.0 9.2 0.1 6.1 7.1 2.5 8.4 14.0 0.1NOTE: For values reported as < (less than), half the detection limit was used.
NA = Data not applicableINA = Site was inaccessibleDRY = Site had no flow
17
D3: 535MER577 – Deep Slough at Green House Road continued…
DateHardness
(mg/L)
Dissolved Arsenic (ug/L)
Dissolved Cadmium
(ug/L)
Dissolved Chromium
(ug/L)
Dissolved Copper (ug/L)
Dissolved Lead (ug/L)
Dissolved Nickel (ug/L)
Dissolved Zinc
(ug/L)
Dissolved Mercury (ug/L)
10/26/2000 88 <1 1.7 <5 <5 <211/30/2000 130 <1 2.5 <5 <5 2.412/28/2000 150 <1 2.6 <5 <5 5.01/25/2001 130 <1 3.8 <5 <5 122/22/2001 170 <1 2.5 <5 <5 6.63/29/2001 200 <1 3.2 <5 <5 <24/26/2001 92 <1 2.6 <5 <5 5.95/31/2001 240 <1 2.0 <5 <5 <26/28/2001 220 13 <1 <1 1.2 <5 <5 <2 <0.27/26/2001 NA NA NA NA NA NA NA NA8/30/2001 110 5.9 <1 <1 2.4 <5 <5 <29/27/2001 140 <4 <0.1 <1 2.4 <5 <5 5.8 <0.2
10/25/2001 130 5.6 <0.1 <1 2.2 <5 <5 <2 NA11/29/2001 140 <4 <0.1 <1 1.1 <5 <5 8.7 <0.212/27/2001 120 <4 <0.1 <1 3.5 <5 <5 9.6 <0.22/28/2002 220 6.0 <0.1 <1.0 2.9 <5.0 <5.0 5.3 <0.23/28/2002 120 <4.0 <0.1 <1.0 2.4 <5.0 6.1 10 <0.24/24/2002 170 10 <0.1 <1.0 2.4 <5.0 <5.0 <2.0 <0.25/30/2002 160 7.5 <0.1 <1.0 2.1 <5.0 <5.0 2.6 <0.26/20/2002 190 4.5 <0.1 3.3 2.8 <5.0 <5.0 9.3 <0.2
10/31/2002 180 7.5 <0.1 <1.0 1.4 <5.0 <5.0 3.9 <0.211/21/2002 110 4.6 <0.1 <1.0 1.9 <5.0 <5.0 <2.0 <0.2
Count 21 13 13 21 21 21 21 21 11Min 88.0 2.0 0.1 0.5 1.1 2.5 2.5 1.0 0.1Max 240.0 13.0 0.5 3.3 3.8 2.5 6.1 12.0 0.1Mean 152.9 5.6 0.1 0.6 2.4 2.5 2.7 4.5 0.1Geo Mean 147.2 4.7 0.1 0.5 2.3 2.5 2.6 3.0 0.1Median 140.0 5.6 0.1 0.5 2.4 2.5 2.5 3.9 0.1Quartile 1 120.0 2.0 0.1 0.5 2.0 2.5 2.5 1.0 0.1Quartile 3 180.0 7.5 0.1 0.5 2.6 2.5 2.5 6.6 0.1NOTE: For values reported as < (less than), half the detection limit was used.
NA = Data not applicableINA = Site was inaccessibleDRY = Site had no flow
18
D3: 535MER577 – Deep Slough at Green House Road continued…
DateChloride (mg/L)
Sulfate (mg/L)
Calcium (mg/L)
Magnesium (mg/L)
TDS (mg/L)
Carbonate (mg/L)
Bicarbonate (mg/L)
Total Alkalinity
(mg/L)Sodium (mg/L)
10/26/2000 18 17 20 9 190 <1 120 100 2511/30/2000 44 44 30 14 330 1 180 150 5512/28/2000 54 45 32 16 360 <1 200 160 671/25/2001 46 33 29 14 320 <1 170 140 532/22/2001 57 49 37 19 420 <1 210 180 733/29/2001 65 59 43 23 430 7 240 210 754/26/2001 18 16 20 10 200 <1 96 96 235/31/2001 98 48 52 27 530 52 204 256 946/28/2001 58 49 44 25 440 <1.0 260 220 698/30/2001 15 21 23 12 230 <1 140 110 269/27/2001 29 45 30 16 310 <1 180 150 46
10/25/2001 19 21 28 13 NA <1 270 220 3611/29/2001 30 32 30 15 300 <1 140 150 4412/27/2001 47 36 26 13 310 <1 150 120 541/31/2002 23 27 28 15 NA <1 NA NA 322/28/2002 7 64 47 24 440 10 260 230 913/28/2002 26 32 26 12 NA <1.0 120 100 354/24/2002 53 38 35 19 NA <1.0 210 170 555/30/2002 17 20 35 19 290 <1.0 200 160 486/20/2002 37 48 40 22 NA <1.0 260 220 63
10/31/2002 29 47 38 20 360 <1.0 240 200 5411/21/2002 16 19 24 12 210 <1.0 140 120 263/27/2003 47 264/24/2003 42 33 38 225/29/2003 80 41 49 306/26/2003 32 36 40 22
19
D3: 535MER577 – Deep Slough at Green House Road continued…
DateChloride (mg/L)
Sulfate (mg/L)
Calcium (mg/L)
Magnesium (mg/L)
TDS (mg/L)
Carbonate (mg/L)
Bicarbonate (mg/L)
Total Alkalinity
(mg/L)Sodium (mg/L)
Count 25 25 26 26 17 22 21 21 22Min 7 16 20 9 190 0.5 96 96 23Max 98 64 52 30 530 52 270 260 94Mean 38 37 34 18 330 3.6 190 170 52Geo Mean 32 34 33 17 320 0.8 180 160 48Median 32 36 34 18 320 0.5 200 160 54Quartile 1 19 27 28 13 290 0.5 140 120 35Quartile 3 53 47 40 22 420 0.5 240 210 66NOTE: For values reported as < (less than), half the detection limit was used.
NA = Data not applicableINA = Site was inaccessibleDRY = Site had no flow
20
D4: 535MER007 – Bear Creek near Bert Crane Road Station Code:535MER007
Location: Latitude 37.25556, Longitude -120.65194
Date TimeTemp (ºC)
Field SC (umhos) pH
Dissolved Oxygen (mg/L)
Turbidity (ntu)
10/26/2000 10:50 AM 13.2 238 7.511/30/2000 8:25 AM 8.0 111 7.912/28/2000 9:40 AM 6.7 88 8.41/25/2001 10:44 AM 9.2 156 7.62/22/2001 10:50 AM 14.1 212 8.23/29/2001 10:00 AM 18.0 78 8.74/26/2001 11:34 AM 22.7 107 7.85/31/2001 1:20 PM 25.2 91 8.16/28/2001 11:43 AM 22.7 90 7.8 7.47/26/2001 1:10 PM 27.7 90 8.4 NA8/30/2001 12:15 PM 24.0 102 8.7 NA9/27/2001 11:11 AM 20.8 193 7.9 8.1
10/25/2001 10:43 AM 15.3 101 8.1 9.811/29/2001 1:17 PM 9.9 106 7.7 10.412/27/2001 12:06 PM 8.6 143 8.0 12.31/31/2002 10:52 AM 5.2 213 8.3 13.82/28/2002 1:11 PM 16.4 174 8.7 13.13/28/2002 11:55 AM 17.9 138 8.2 10.74/24/2002 10:39 AM 18.2 105 7.9 8.15/30/2002 8:46 AM 22.5 109 7.4 NA6/20/2002 10:27 AM 22.6 101 7.7 7.6 57.27/30/2002 10:31 AM 22.8 188 7.7 7.2 49.58/29/2002 10:32 AM 22.1 117 7.7 7.9 42.09/26/2002 10:32 AM 20.7 89 7.9 8.5
10/17/2002 11:12 AM 15.9 90 7.7 9.1 20.110/31/2002 11:12 AM 13.0 92 7.6 10.3 17.111/21/2002 11:03 AM 12.0 128 7.8 10.7 16.812/19/2002 10:31 AM 8.6 136 7.7 11.1 53.41/14/2003 10:33 AM 10.8 133 7.8 10.6 36.11/30/2003 11:18 AM 12.0 179 7.5 12.4 10.13/27/2003 12:39 PM 16.8 81 8.2 13 53.44/24/2003 11:29 AM 15.9 64 8.0 9.4 37.45/29/2003 10:30 AM 22.8 78 8.0 8.1 44.26/26/2003 10:08 AM 21.0 74 8.0 8.4 84.57/31/2003 10:52 AM 23.8 100 7.3 6.6 1108/28/2003 10:36 AM 22.4 60 7.7 8 73.69/25/2003 10:36 AM 20.1 85 7.4 7.4 34.9
10/30/2003 10:53 AM 14.3 89 7.7 9.8 20.111/20/2003 11:09 AM 11.8 57 7.6 11.4 37.4
D4: 535MER007 – Bear Creek near Bert Crane Road continued…
Date TimeTemp (ºC)
Field SC (umhos) pH
Dissolved Oxygen (mg/L)
Turbidity (ntu)
1/29/2004 10:44 AM 9.3 108 8.2 13 18.72/26/2004 10:42 AM 11.6 142 8.0 10.2 NA3/24/2004 11:02 AM 18.8 229 8.1 8.6 NA4/29/2004 10:29 AM 17.6 76 8.5 9.5 56.65/27/2004 10:50 AM 21.8 109 7.9 8.5 49.46/24/2004 10:47 AM 22.1 61 8.0 9 NA7/29/2004 10:09 AM 22.5 115 8.0 8.5 NA8/26/2004 10:32 AM 22.2 64 8.4 7.6 NA9/30/2004 10:01 AM 18.0 54 8.2 8.4 NA
10/28/2004 10:29 AM 12.4 183 8.1 9.711/23/2004 10:36 AM 7.7 137 7.8 11.612/29/2004 9:53 AM 9.6 91 7.9 10.41/27/2005 11:08 AM 11.1 130 7.9 12.72/24/2005 8:23 AM 13.3 160 8.0 10.23/29/2005 11:49 AM 15.2 208 7.9 9.94/28/2005 10:17 AM 17.0 132 8.2 95/26/2005 10:34 AM 21.1 77 7.6 8.46/30/2005 10:38 AM 22.3 78 7.5 6.87/28/2005 10:27 AM 22.1 110 7.6 7.78/25/2005 10:44 AM 22.0 74 7.7 8.29/29/2005 10:43 AM 19.3 54 6.8 8.3
Count 60 60 60 49 21Min 5.2 54 6.8 6.6 10.1Max 27.7 238 8.7 13.8 110Mean 16.9 116 7.9 9.5 43.9Geo Mean 15.8 108 7.9 9.4 37.5Median 17.8 106 7.9 9.1 42.0Quartile 1 12.0 84 7.7 8.1 20.1Quartile 3 22.1 137 8.1 10.6 53.4NOTE: For values reported as < (less than), half the detection limit was used.
NA = Data not applicableINA = Site was inaccessibleDRY = Site had no flow
22
D4: 535MER007 – Bear Creek near Bert Crane Road continued…
DateTSS
(mg/L)TOC
(mg/L)Total Coli
MPNE. coli MPN
10/26/2000 55 1511/30/2000 16 1.812/28/2000 NA 3.31/25/2001 170 6.32/22/2001 28 6.03/29/2001 NA <14/26/2001 3.35/31/2001 54 3.36/28/2001 48 5.07/26/2001 3.68/30/2001 51 5.59/27/2001 34
10/25/2001 7.211/29/2001 <11/31/2002 2.13/28/2002 NA4/24/2002 6.56/20/2002 3.27/30/2002 >2419.6 >2419.69/26/2002 3.3
10/17/2002 >2419.6 13310/31/2002 NA11/21/2002 6.81/14/2003 >2419.6 5793/27/2003 2.54/24/2003 NA >2419.6 3085/29/2003 4.06/26/2003 3.77/31/2003 >2419.6 3878/28/2003 >2419.6 2999/25/2003 >2419.6 276
10/30/2003 >2419.6 41111/20/2003 >2419.6 931/29/2004 1553 442/26/2004 >2419.6 13003/24/2004 >2419.6 17334/29/2004 >2419.6 2385/27/2004 >2419.6 2616/24/2004 >2419.6 9217/29/2004 >2419.6 5798/26/2004 >2419.6 1059/30/2004 >2419.6 461
23
24
DateTSS
(mg/L)TOC
(mg/L)Total Coli
MPNE. coli MPN
10/28/2004 13 >2419.6 >2419.611/23/2004 9.6 >2419.6 6912/29/2004 21 >2419.6 >2419.61/27/2005 14 >2419.6 >2419.62/24/2005 7.3 2420 2853/29/2005 6.0 >2419.6 13004/28/2005 7.7 >2419.6 12035/26/2005 4.8 >2419.6 12036/30/2005 NA >2419.6 4357/28/2005 NA >2419.6 >2419.68/25/2005 2.7 >2419.6 2289/29/2005 3.0 >2419.6 770
Count 8 31 30 30Min 16 0.5 155
D4: 535MER007 – Bear Creek near Bert Crane Road continued…
3 44Max 170 21 2420 2420MeaGeoMedQuaQua
n 57 5.9 NA NA Mean 46 4.4 2384 502ian 50 4.8 2420 448rtile 1 33 3.3 2420 265rtile 3 54 7.0 2420 1276E: For values reported as < (less than), half the detection limit was used For values reported as > (greater than), 2420 was used
Data not applicable Site was inaccessible
= Site had no flow
NOT
NA =INA =DRY
D4: 535MER007 – Bear Creek near Bert Crane Road continued…
DateNitrate (mg/L)
Nitrate-N (mg/L)
TKN (mg/L)
Ammonia-N (mg/L)
Phosphorus (mg/L)
Ortho-phosphate-
P (mg/L)
Potassium (mg/L)
BOD 5-Day (mg/L)
BOD 10-Day (mg/L)
10/26/2000 3.4 9.8 NA 2 11 7.6 1611/30/2000 3.5 <2 0.2 <1 1.9 1.9 412/28/2000 3 <2 0.2 <1 1.6 2.9 5.21/25/2001 NA NA 0.3 <1 4.7 7 10.42/22/2001 <2 <2 NA <1 3.2 1.7 3.43/29/2001 <2 NA <0.1 <1 1.8 1.1 2.14/26/2001 <2 <2 0.1 <1 1.9 1.5 2.85/31/2001 2.6 <2 0.3 <1 3 2 4.36/28/2001 31 <2 0.2 <1 2.3 1.7 3.18/30/2001 4.3 <2 0.1 <1 29/27/2001 6.2 <2 0.2 <1 4.4
10/25/2001 3 <2 0.2 <1 1.9 1.1 2.311/29/2001 NA NA NA 0.2 NA 7.6 13.512/27/2001 NA NA 0.1 <0.03 2 0.7 1.41/31/2002 NA 0.5 <0.05 <0.03 NA 1 22/28/2002 NA NA 0.1 <0.03 1.3 1.0 1.93/28/2002 NA 0.7 0.1 0.1 2.6 1.7 3.44/24/2002 NA NA 0.2 0.1 1.8 1.6 2.75/30/2002 NA NA NA 0.1 1.9 1.6 2.56/20/2002 NA 0.7 NA 0.1 1.8 1.8 3.18/29/2002 NA 0.9 NA 0.1 2.8 1.5 2.89/26/2002 NA 0.4 0.2 0.1 1.8 1.3 2.4
10/31/2002 NA 0.2 0.1 0.1 1.4 1.4 2.111/21/2002 NA 0.9 0.1 0.1 4 1.0 2.012/19/2002 NA 1.4 0.1 NA 2.5 3.6 5.21/30/2003 NA 0.6 NA <0.03 2.2 1.0 1.6
D4: 535MER007 – Bear Creek near Bert Crane Road continued…
DateNitrate (mg/L)
Nitrate-N (mg/L)
TKN (mg/L)
Ammonia-N (mg/L)
Phosphorus (mg/L)
Ortho-phosphate-
P (mg/L)
Potassium (mg/L)
BOD 5-Day (mg/L)
BOD 10-Day (mg/L)
Count 11 NA 19 NA 19 25 24 24 24Min 1.0 NA 0.2 NA 0.03 0.02 1.3 0.7 1.4Max 31.0 NA 9.8 NA 0.3 2.0 11.0 7.6 16.0Mean 5.5 NA 1.3 NA 0.2 0.3 2.7 2.3 4.2Geo Mean 3.1 NA 0.9 NA 0.1 0.2 2.4 1.8 3.3Median 3.0 NA 1.0 NA 0.1 0.2 2.0 1.6 2.8Quartile 1 1.8 NA 0.7 NA 0.1 0.1 1.8 1.1 2.1Quartile 3 3.9 NA 1.0 NA 0.2 0.5 2.9 1.9 4.1NOTE: For values reported as < (less than), half the detection limit was used.
NA = Data not applicableINA = Site was inaccessibleDRY = Site had no flow
26
D4: 535MER007 – Bear Creek near Bert Crane Road continued…
DateHardness
(mg/L)
Total Arsenic (ug/L)
Total Cadmium
(ug/L)
Total Chromium
(ug/L)
Total Copper (ug/L)
Total Lead (ug/L)
Total Nickel (ug/L)
Total Zinc (ug/L)
Total Mercury (ug/L)
10/26/2000 63 1.6 6.6 <5 <5 2011/30/2000 41 <1 2.3 <5 <5 5.112/28/2000 34 <1 2.1 <5 <5 4.51/25/2001 68 7.6 13 <5 7 272/22/2001 91 1.4 4.9 <5 <5 113/29/2001 29 <1 3 <5 <5 4.44/26/2001 41 <1 3.1 <5 <5 45/31/2001 40 2.5 4.5 <5 <5 8.36/28/2001 53 <2 <1 2.6 4.6 <5 <5 7.5 <0.27/26/2001 NA NA 2 4.2 <5 <5 NA NA8/30/2001 40 <2 <1 2.5 6.1 <5 <5 6.19/27/2001 71 <4 <0.1 2.5 6.2 <5 <5 5.5 <0.2
10/25/2001 39 <4 <0.1 <1 2.1 <5 <5 <2 NA11/29/2001 35 <4 <0.1 1.2 4.9 <5 <5 9.2 <0.212/27/2001 73 <4 <0.1 1.1 2.6 <5 <5 3.2 <0.22/28/2002 75 <4.0 <0.1 <1.0 3.7 <5.0 <5.0 6.1 <0.23/28/2002 56 <4.0 <0.1 2.1 4.1 <5.0 NA 8.1 <0.24/24/2002 44 <4.0 <0.1 <1.0 1.7 <5.0 <5.0 <2.0 <0.25/30/2002 44 <4.0 <0.1 3.8 2.2 <5.0 <5.0 4.5 <0.26/20/2002 43 <4.0 <0.1 3.2 5.6 <5.0 <5.0 7.6 <0.29/26/2002 37 <4.0 <0.1 2.3 4.8 <5.0 <5.0 4.7 <0.2
10/31/2002 38 <4.0 <0.1 <1.0 2 <5.0 <5.0 2.1 <0.211/21/2002 50 <4.0 <0.1 <1.0 7.8 <5.0 <5.0 5.2 <0.23/27/2003 32 <4.0 <0.1 1.3 4 <5.0 <5.0 4.2 <0.24/24/2003 27 <4.0 <0.1 1 2.8 <5.0 <5.0 3.8 <0.25/29/2003 31 <4.0 <0.1 2.2 4.1 <5.0 <5.0 5.3 <0.26/26/2003 28 <4.0 <0.1 3.4 4.6 <5.0 <5.0 8.6 NA
27
D4: 535MER007 – Bear Creek near Bert Crane Road continued…
DateHardness
(mg/L)
Total Arsenic (ug/L)
Total Cadmium
(ug/L)
Total Chromium
(ug/L)
Total Copper (ug/L)
Total Lead (ug/L)
Total Nickel (ug/L)
Total Zinc (ug/L)
Total Mercury (ug/L)
Count 26 18 18 27 27 27 26 26 15Min 27.0 1.0 0.1 0.5 1.7 2.5 2.5 1.0 0.1Max 91.0 2.0 0.5 7.6 13.0 2.5 7.0 27.0 0.1Mean 47.0 1.9 0.1 1.8 4.4 2.5 2.7 6.8 0.1Geo Mean 44.5 1.9 0.1 1.3 3.9 2.5 2.6 5.4 0.1Median 41.0 2.0 0.1 1.4 4.1 2.5 2.5 5.3 0.1Quartile 1 35.5 2.0 0.1 0.5 2.7 2.5 2.5 4.3 0.1Quartile 3 55.3 2.0 0.1 2.5 4.9 2.5 2.5 8.0 0.1NOTE: For values reported as < (less than), half the detection limit was used.
NA = Data not applicableINA = Site was inaccessibleDRY = Site had no flow
28
D4: 535MER007 – Bear Creek near Bert Crane Road continued…
DateHardness
(mg/L)
Dissolved Arsenic (ug/L)
Dissolved Cadmium
(ug/L)
Dissolved Chromium
(ug/L)
Dissolved Copper (ug/L)
Dissolved Lead (ug/L)
Dissolved Nickel (ug/L)
Dissolved Zinc
(ug/L)
Dissolved Mercury (ug/L)
10/26/2000 63 <1 1.9 <5 <5 3.311/30/2000 41 <1 <1 <5 <5 2.912/28/2000 34 <1 <1 <5 <5 <21/25/2001 68 <1 2.2 <5 <5 <22/22/2001 91 <1 2.3 <5 <5 2.73/29/2001 29 <1 2.4 <5 <5 2.24/26/2001 41 <1 1.1 <5 <5 <25/31/2001 40 <1 1.4 <5 <5 2.26/28/2001 53 <2 <1 <1 <1 <5 <5 <2 <0.27/26/2001 NA NA NA NA NA NA NA NA8/30/2001 40 <2 <1 <1 2.2 <5 <5 <29/27/2001 71 <4 <0.1 <1 3.4 <5 <5 <2 <0.2
10/25/2001 39 <4 <0.1 <1 1.6 <5 <5 <2 NA11/29/2001 35 <4 <0.1 <1 2.1 <5 <5 13 <0.212/27/2001 73 <4 <0.1 <1 1.6 <5 <5 <2 <0.22/28/2002 75 <4.0 <0.1 <1.0 2.5 <5.0 <5.0 4.4 <0.23/28/2002 56 <4.0 <0.1 <1.0 1.8 <5.0 <5.0 4.1 <0.24/24/2002 44 <4.0 <0.1 <1.0 1.7 <5.0 <5.0 <2.0 <0.25/30/2002 44 <4.0 <0.1 <1.0 2.1 <5.0 <5.0 5.6 <0.26/20/2002 43 <4.0 <0.1 1.8 3.4 <5.0 <5.0 5.4 <0.29/26/2002 37 <4.0 <0.1 <1.0 2.5 <5.0 <5.0 <2.0 <0.2
10/31/2002 38 <4.0 <0.1 <1.0 1.3 <5.0 <5.0 3.1 <0.211/21/2002 50 <4.0 <0.1 <1.0 3.6 <5.0 <5.0 <2.0 <0.2
Count 22 14 14 22 22 22 22 22 12Min 29.0 1.0 0.1 0.5 0.5 2.5 2.5 1.0 0.1Max 91.0 2.0 0.5 1.8 3.6 2.5 2.5 13.0 0.1Mean 50.2 1.9 0.1 0.6 1.9 2.5 2.5 2.7 0.1Geo Mean 48.0 1.8 0.1 0.5 1.7 2.5 2.5 2.0 0.1Median 43.5 2.0 0.1 0.5 2.0 2.5 2.5 1.6 0.1Quartile 1 39.3 2.0 0.1 0.5 1.5 2.5 2.5 1.0 0.1Quartile 3 61.3 2.0 0.1 0.5 2.4 2.5 2.5 3.3 0.1NOTE: For values reported as < (less than), half the detection limit was used.
NA = Data not applicableINA = Site was inaccessibleDRY = Site had no flow
29
D4: 535MER007 – Bear Creek near Bert Crane Road continued…
DateChloride (mg/L)
Sulfate (mg/L)
Calcium (mg/L)
Magnesium (mg/L)
TDS (mg/L)
Carbonate (mg/L)
Bicarbonate (mg/L)
Total Alkalinity
(mg/L)Sodium (mg/L)
10/26/2000 8 5 14 7 140 <1 120 100 1011/30/2000 6 NA 10 4 99 <1 50 40 512/28/2000 4 4 9 3 50 <1 40 30 31/25/2001 7 8 14 8 110 <1 70 60 72/22/2001 7 11 18 11 120 <1 100 86 93/29/2001 3 5 7 3 90 <1 44 36 34/26/2001 3 5 10 4 93 <1 40 40 55/31/2001 3 4 9 4 72 <1 34 34 46/28/2001 3 6 13 5 90 <1.0 60 49 58/30/2001 3 5 10 4 84 <1 46 38 59/27/2001 5 7 17 7 150 <1 95 78 10
10/25/2001 3 5 9 4 NA <1 54 44 511/29/2001 4 4 9 3 98 <1 46 38 412/27/2001 7 12 15 9 91 <1 78 64 701/31/2002 8 13 17 11 NA <1 NA NA 102/28/2002 6 10 15 9 92 <1.0 85 70 83/28/2002 5 8 12 6 NA <1.0 60 50 64/24/2002 3 5 11 4 NA <1.0 46 38 45/30/2002 3 6 11 4 73 <1.0 48 39 56/20/2002 3 5 10 4 NA <1.0 44 36 49/26/2002 3 5 9 4 NA <1.0 37 30 4
10/31/2002 3 5 9 4 70 <1.0 44 36 411/21/2002 5 6 12 5 130 <1.0 54 44 53/27/2003 7 34/24/2003 3 4 7 35/29/2003 3 4 8 36/26/2003 3 4 7 3
30
31
D4: 535MER007 – Bear Creek near Bert Crane Road continued…
DateChloride (mg/L)
Sulfate (mg/L)
Calcium (mg/L)
Magnesium (mg/L)
TDS (mg/L)
Carbonate (mg/L)
Bicarbonate (mg/L)
Total Alkalinity
(mg/L)Sodium (mg/L)
Count 26 25 27 27 17 23 22 22 23Min 3 4 7 3 50 0.5 34 30 3Max 8 13 18 11 150 0.5 120 100 70Mean 4 6 11 5 97 0.5 59 49 8Geo Mean 4 6 11 5 94 0.5 55 46 6Median 3 5 10 4 92 0.5 49 40 5Quartile 1 3 5 9 4 84 0.5 44 37 4Quartile 3 6 7 14 7 110 0.5 68 58 8NOTE: For values reported as < (less than), half the detection limit was used.
NA = Data not applicableINA = Site was inaccessibleDRY = Site had no flow
D4: 535MER007 – Bear Creek near Bert Crane Road continued…
Date Result Control Result Control
Result (million/m
l)
Control (million/
ml) MDD(%)6/18/2001 95 100 90 90
11/23/2004 100 100 100 10012/29/2004 97.5 97.5 100 1001/27/2005 55* 100 100 1002/24/2005 70.0* 100 100 1003/29/2005 97.5 100 100 1004/28/2005 N/A N/A 100 1005/26/2005 77.5* 97.5 100 1006/30/2005 100 100 100 1007/28/2005 100 97.5 100 1008/25/2005 100 100 100 1009/29/2005 100 100 100 100
Count 11 11 12 12 N/A N/A N/A
* Significantly reduced from the lab control.** Significantly greater than the lab control.^ Fish were from a "forced hatch," duplicate failed QA.1 Duplicate sample for the set was low - 77% recovery.
3 Samples qualified, but duplicate sample recovery for the set was high - 126% (53.8%/42.5%)NA = Data not applicableINA = Site was inaccessibleDRY = Site had no flow
2 Testing for the Fathead minnow was initiated when samples were approx. 48h old due to untimely shipping of fish by fish supplier.
96h Acute Fathead Minnow
(% Survival)
48h Acute Ceriodaphnia Dubia
(% Survival) Algae Cell Growth
APPENDIX E
GRASSLANDS BASIN
APPENDIX E: GRASSLANDS BASIN E1: 541MER531 – Salt Slough @ Lander Avenue ……………………………………......03-19 E2: 541MER536 – Mud Slough Upstream of SLD Terminus……………………………...20-38 E3: 541MER535 – San Luis Drain @ Terminus……………………………………………39-64 E4: 541MER542 – Mud Slough @ San Luis Drain…………………………………………66-83
2
E1: 541MER531 – Salt Slough @ Lander Avenue Station Code:541MER531
Location: Latitude 37.24861, Longitude -120.85111
Date TimeTemp (ºC)
Field SC (umhos) pH
Dissolved Oxygen (mg/L)
Turbidity (ntu)
10/5/2000 10:12 AM 19.1 1330 7.210/12/2000 10:05 AM 16.1 905 8.010/19/2000 9:47 AM 17.2 1390 7.810/26/2000 2:05 PM 14.7 1600 7.211/2/2000 9:52 AM 14.3 1300 6.311/9/2000 9:35 AM 12.5 1390 7.7
11/16/2000 10:15 AM 10.9 1570 6.911/21/2000 7:45 AM 9.3 1590 7.911/30/2000 9:20 AM 9.6 1660 7.112/7/2000 9:10 AM 9.8 1480 7.6
12/12/2000 9:10 AM 11.2 1460 7.412/21/2000 11:10 AM 9.4 1650 7.712/28/2000 10:50 AM 7.9 1810 7.21/4/2001 9:06 AM 7.6 1920 7.81/11/2001 10:56 AM 9.2 1310 7.71/18/2001 9:15 AM 6.7 1830 7.31/25/2001 11:45 AM 10.5 1790 6.62/1/2001 10:30 AM 8.5 1920 6.82/8/2001 10:00 AM 8.6 1670 7.82/15/2001 11:00 AM 10.5 1560 7.52/22/2001 12:15 PM 17.0 1600 7.63/1/2001 8:55 AM 11.3 1560 7.33/8/2001 9:40 AM 14.9 1340 7.03/15/2001 11:15 AM 16.6 1610 7.43/22/2001 11:36 AM 19.2 1910 7.63/29/2001 11:10 AM 19.4 1540 8.14/5/2001 12:00 PM 15.8 1740 7.74/12/2001 9:42 AM 13.2 1610 7.24/19/2001 11:50 AM 16.8 1890 7.84/26/2001 10:51 AM 22.8 1400 6.85/3/2001 10:20 AM 15.4 1900 7.85/10/2001 8:26 AM 22.9 1240 7.85/17/2001 11:52 AM 23.1 990 7.85/24/2001 9:05 AM 23.5 1300 6.65/31/2001 9:30 AM 24.7 1310 7.86/7/2001 11:15 AM 25.1 1280 7.8 7.56/14/2001 10:08 AM 20.8 1240 7.8 6.8
3
E1: 541MER531 – Salt Slough @ Lander Avenue continued…
Date TimeTemp (ºC)
Field SC (umhos) pH
Dissolved Oxygen (mg/L)
Turbidity (ntu)
6/21/2001 11:38 AM 26.8 1090 7.3 7.16/28/2001 12:45 PM 24.0 1040 7.8 6.17/5/2001 8:47 AM 24.5 1340 7.8 6.17/11/2001 11:05 AM 23.9 975 7.8 7.37/19/2001 11:14 AM 24.2 1100 7.9 8.47/26/2001 1:37 PM 27.6 1000 7.1 NA8/2/2001 9:19 AM 23.9 999 7.9 5.98/9/2001 8:54 AM 25.9 1210 7.6 5.88/16/2001 10:03 AM 24.1 1080 7.5 NA8/23/2001 9:00 AM 22.1 1030 7.7 6.88/30/2001 1:14 PM 25.8 1430 8.3 NA9/6/2001 8:26 AM 20.8 1560 7.8 6.69/13/2001 8:48 AM 20.1 1530 7.7 6.69/20/2001 10:37 AM 21.5 1690 7.9 3.09/27/2001 12:03 PM 22.5 1480 8.0 9.010/4/2001 8:34 AM 19.9 1460 7.8 7.6
10/11/2001 9:14 AM 17.8 1200 7.9 7.110/18/2001 9:09 AM 18.3 1170 7.8 7.610/25/2001 11:36 AM 15.8 1700 7.2 11.411/1/2001 9:30 AM 16.0 1680 7.7 8.311/8/2001 9:11 AM 14.6 1440 8.6 9.8
11/15/2001 9:11 AM 18.3 1280 7.7 7.311/20/2001 11:14 AM 14.4 1570 7.6 9.311/29/2001 10:20 AM 9.9 1710 7.7 9.912/6/2001 8:50 AM 9.9 1480 7.7 11.0
12/13/2001 9:13 AM 9.4 2020 7.7 10.112/20/2001 10:14 AM 10.8 2420 7.8 11.012/27/2001 10:04 AM 10.7 2470 7.7 9.01/3/2002 9:09 AM 12.9 2020 7.6 9.01/10/2002 9:06 AM 12.2 2010 7.5 9.11/17/2002 8:20 AM 7.8 2200 7.6 10.51/24/2002 12:15 PM 8.8 2010 7.5 10.41/31/2002 11:48 AM 8.2 1870 7.8 9.82/7/2002 8:44 AM 10.5 1550 7.8 10.12/14/2002 8:40 AM 11.3 1670 7.5 8.82/21/2002 10:27 AM 14.6 1330 7.7 8.92/28/2002 2:08 PM 17.1 1550 7.9 11.9
4
E1: 541MER531 – Salt Slough @ Lander Avenue continued…
Date TimeTemp (ºC)
Field SC (umhos) pH
Dissolved Oxygen (mg/L)
Turbidity (ntu)
3/7/2002 8:40 AM 14.4 1620 7.7 7.23/14/2002 11:33 AM 13.3 1820 7.9 9.83/21/2002 11:31 AM 15.5 1830 7.6 8.23/28/2002 1:14 PM 18.6 2030 7.8 10.44/4/2002 8:38 AM 17.9 1780 7.7 6.84/11/2002 9:11 AM 18.4 1660 7.7 6.74/18/2002 7:14 AM 14.6 1640 7.8 7.64/24/2002 11:33 AM 20.0 1790 7.7 6.35/2/2002 8:07 AM 16.4 1560 8.1 9.85/9/2002 9:13 AM 18.3 1670 7.7 7.75/16/2002 9:15 AM 20.5 1570 7.7 6.3 54.05/23/2002 6:55 AM 17.5 1120 7.6 NA5/30/2002 11:12 AM 25.9 1340 7.6 6.66/6/2002 7:50 AM 24.4 1220 7.7 NA6/13/2002 11:01 AM 23.1 1230 8.0 NA6/20/2002 11:29 AM 24.7 1240 7.7 5.2 NA6/27/2002 9:36 AM 23.5 1020 7.7 5.97/3/2002 9:55 AM 24.9 1100 8.2 NA7/11/2002 11:51 AM 27.4 1340 7.7 NA7/18/2002 8:55 AM 23.8 1100 7.6 3.1 1487/25/2002 8:25 AM 23.4 960 7.6 6.57/30/2002 11:10 AM 24.2 784 7.7 6.4 1408/1/2002 8:39 AM 24.1 923 7.8 6.38/8/2002 9:56 AM 22.3 896 7.8 6.58/15/2002 8:23 AM 24.1 948 7.7 6.48/22/2002 8:46 AM 21.1 1110 7.7 7.38/29/2002 11:41 AM 23.2 1270 7.7 8.4 68.09/5/2002 8:27 AM 21.5 1110 7.8 7.29/12/2002 8:12 AM 21.4 1280 7.9 7.19/19/2002 8:51 AM 20.5 1320 7.6 7.4 84.09/26/2002 11:34 AM 22.4 1260 8.0 8.810/3/2002 9:05 AM 14.0 1260 8.0 9.5
10/10/2002 11:14 AM 20.1 1360 7.8 5.910/17/2002 11:58 AM 16.8 958 7.8 9.1 79.610/24/2002 9:48 AM 14.7 1110 7.9 9.010/31/2002 12:05 PM 14.5 1390 7.7 8.8 71.211/7/2002 9:02 AM 13.3 1260 7.9 9.7
11/14/2002 9:39 AM 14.2 1300 7.5 8.411/21/2002 8:47 AM 12.4 1440 7.3 8.5 62.111/26/2002 11:22 AM 12.3 1590 7.9 10.3
5
E1: 541MER531 – Salt Slough @ Lander Avenue continued…
Date TimeTemp (ºC)
Field SC (umhos) pH
Dissolved Oxygen (mg/L)
Turbidity (ntu)
12/5/2002 8:57 AM 10.6 1510 7.7 10.8 NA12/12/2002 8:59 AM 11.5 1590 7.6 10.712/19/2002 11:48 AM 9.5 1360 7.4 8.9 55.012/24/2002 9:59 AM 8.0 1460 7.3 10.51/2/2003 11:17 AM 9.9 1630 7.6 13.71/9/2003 10:04 AM 10.2 1850 7.6 11.51/16/2003 10:41 AM 11.7 1730 7.6 9.3 56.41/23/2003 8:28 AM 11.2 1700 7.0 11.41/30/2003 9:20 AM 12.8 1910 7.6 9.0 49.82/6/2003 9:54 AM 9.7 2230 7.7 11.92/13/2003 11:08 AM 13.0 2080 7.7 9.7 35.72/20/2003 10:57 AM 11.3 1340 7.8 10.9 89.22/27/2003 8:25 AM 12.6 1440 7.6 8.33/6/2003 8:53 AM 13.4 1590 7.9 9.0 NA3/13/2003 8:48 AM 17.4 1620 7.7 7.9 44.23/20/2003 8:24 AM 14.6 1820 7.7 8.7 51.53/27/2003 1:35 PM 17.5 1540 7.9 12.4 1504/3/2003 12:30 PM 18.7 1780 7.3 8.3 61.44/10/2003 8:29 AM 18.2 1840 7.8 7.7 83.64/17/2003 8:41 AM 16.0 1590 7.7 7.4 82.84/24/2003 9:19 AM 16.5 1850 7.6 7.3 64.35/1/2003 8:53 AM 17.2 1650 7.7 8.1 NA5/8/2003 8:18 AM 15.8 1770 7.7 8.5 64.35/15/2003 8:35 AM 17.1 1820 7.7 9.65/22/2003 9:05 AM 22.6 1270 7.7 6.5 61.25/29/2003 9:00 AM 24.8 1250 7.6 5.06/5/2003 8:48 AM 23.4 1140 7.6 6.0 1186/12/2003 9:35 AM 19.8 1240 8.0 8.0 1706/19/2003 8:46 AM 21.1 1220 7.7 6.4 1376/26/2003 9:04 AM 23.8 1050 7.7 6.1 1007/3/2003 8:37 AM 23.4 921 7.7 7.27/10/2003 9:03 AM 24.3 990 7.7 7.27/17/2003 8:58 AM 25.6 906 7.8 5.57/24/2003 8:49 AM 26.2 1080 7.8 6.7 1297/31/2003 8:49 AM 25.9 936 7.6 5.0 1238/7/2003 8:45 AM 23.0 824 7.7 6.3 1468/14/2003 8:33 AM 22.8 1030 7.8 6.8
6
E1: 541MER531 – Salt Slough @ Lander Avenue continued…
Date TimeTemp (ºC)
Field SC (umhos) pH
Dissolved Oxygen (mg/L)
Turbidity (ntu)
8/21/2003 8:44 AM 23.9 839 7.7 6.3 1338/28/2003 8:48 AM 23.3 772 7.7 NA 1359/4/2003 8:45 AM 24.2 1060 7.9 6.6 1039/11/2003 9:36 AM 20.8 1180 8.0 8.5 75.69/18/2003 8:45 AM 18.3 1290 7.8 1.2 3309/25/2003 8:59 AM 19.9 1260 8.0 7.6 66.410/2/2003 9:14 AM 19.2 1070 7.8 7.9 11310/9/2003 8:32 AM 19.3 1040 7.8 5.5 209
10/16/2003 10:58 AM 17.1 1250 7.8 10.2 70.010/23/2003 9:10 AM 18.4 1240 7.7 7.6 10410/30/2003 8:50 AM 14.4 1240 7.8 8.9 73.611/6/2003 8:41 AM 12.8 1200 7.7 9.6 73.0
11/13/2003 8:19 AM 12.8 1390 7.7 9.1 51.611/20/2003 8:40 AM 12.6 1380 7.6 8.9 56.211/26/2003 8:21 AM 8.2 1540 7.7 11.0 50.912/4/2003 8:27 AM 12.2 1670 7.9 10.0
12/11/2003 8:24 AM 11.2 2020 7.5 10.2 NA12/18/2003 8:50 AM 8.6 1920 7.6 11.2 NA12/23/2003 8:36 AM 11.4 1740 7.4 10.3 NA12/30/2003 8:38 AM 8.3 1600 7.7 12.0 NA1/8/2004 8:07 AM 8.5 1560 7.7 10.0 NA1/15/2004 8:44 AM 9.8 1690 7.7 9.8 NA1/22/2004 8:47 AM 9.4 1680 7.7 14.9 44.41/29/2004 8:54 AM 10.3 1630 7.6 11.5 49.02/5/2004 8:41 AM 10.1 1510 7.7 11.3 76.12/12/2004 8:30 AM 10.6 1860 7.4 10.8 NA2/19/2004 8:38 AM 12.1 1400 7.5 9.6 NA2/26/2004 8:37 AM 11.9 1500 7.5 8.0 NA3/4/2004 8:40 AM 12.2 1420 7.6 8.8 1253/11/2004 8:46 AM 17.1 1720 7.6 6.6 NA3/18/2004 8:04 AM 19.0 1950 7.9 8.13/25/2004 8:45 AM 17.4 1670 7.7 7.1 62.04/1/2004 8:43 AM 15.7 1980 7.6 8.84/8/2004 8:40 AM 17.2 1700 7.8 7.3 85.14/15/2004 8:57 AM 17.5 1690 7.9 7.8 91.34/22/2004 8:50 AM 16.2 1480 7.8 9.1 1204/29/2004 10:02 AM 17.2 1800 7.9 NA 79.45/6/2004 8:54 AM 21.2 1360 7.8 10.8 84.55/13/2004 9:20 AM 18.8 1330 7.8 12.9 1065/20/2004 8:49 AM 19.9 1320 7.6 7.4 96.75/27/2004 8:35 AM 21.1 1460 7.8 NA NA6/3/2004 9:25 AM 23.0 1190 8.0 6.9 1136/10/2004 9:18 AM 19.4 1010 7.8 7.8 1596/17/2004 9:10 AM 22.9 1100 7.7 6.3 1166/24/2004 9:01 AM 22.4 1130 7.8 6.6 18.8
7
E1: 541MER531 – Salt Slough @ Lander Avenue continued…
Date TimeTemp (ºC)
Field SC (umhos) pH
Dissolved Oxygen (mg/L)
Turbidity (ntu)
7/1/2004 8:53 AM 21.4 1220 7.9 7.5 NA7/8/2004 8:51 AM 22.0 1110 7.8 6.9 NA7/15/2004 9:04 AM 23.7 1090 7.9 6.2 NA7/22/2004 10:43 AM 26.1 966 8.1 8.3 NA7/29/2004 8:32 AM 23.4 1150 7.8 6.6 NA8/5/2004 8:18 AM 23.2 1000 7.4 6.7 NA8/12/2004 8:36 AM 24.9 1100 7.9 5.6 NA8/19/2004 10:49 AM 25.3 955 7.9 7.3 NA8/26/2004 8:43 AM 22.7 1160 8.1 6.8 NA9/2/2004 8:26 AM 23.1 1480 7.8 6.3 NA9/9/2004 9:50 AM 23.5 1130 7.9 7.7 NA9/16/2004 10:27 AM 21.5 1170 8.0 7.8 NA9/23/2004 8:57 AM 18.4 1110 8.1 8.6 NA9/30/2004 8:37 AM 17.3 1190 7.7 4.6 NA10/7/2004 8:09 AM 18.8 1280 8.0 12.1
10/14/2004 8:28 AM 17.6 1210 8.0 8.610/21/2004 9:20 AM 14.8 957 NA 9.510/28/2004 8:29 AM 12.8 1060 7.6 10.911/4/2004 9:08 AM 12.3 1340 7.8 9.3
11/11/2004 8:17 AM 14.0 1400 7.0 8.911/18/2004 8:28 AM 13.5 1250 7.5 9.411/23/2004 11:10 AM 9.5 1330 7.5 10.212/2/2004 8:43 AM 7.2 1590 7.9 11.712/9/2004 8:25 AM 11.2 1660 7.9 10.5
12/16/2004 8:17 AM 11.1 1770 7.8 10.712/22/2004 11:23 AM 9.1 1750 7.7 13.612/29/2004 9:43 AM 10.1 1720 7.7 9.21/6/2005 7:53 AM 9.7 1500 7.8 11.41/13/2005 8:40 AM 9.4 1590 7.7 11.21/20/2005 8:45 AM 9.4 2040 7.4 9.41/27/2005 8:20 AM 11.6 2340 7.6 7.82/3/2005 8:39 AM 10.9 2060 7.6 9.12/10/2005 8:08 AM 12.1 2040 7.7 10.02/17/2005 8:54 AM 14.0 1350 7.6 7.52/24/2005 8:20 AM 14.5 1670 7.6 6.03/3/2005 8:25 AM 15.0 1550 7.6 8.53/10/2005 9:11 AM 18.2 1690 7.6 10.33/17/2005 8:20 AM 16.1 1860 7.8 11.13/24/2005 8:26 AM 14.3 1500 7.4 7.43/31/2005 8:29 AM 14.3 1840 7.6 8.14/7/2005 8:34 AM 17.5 1997 7.6 7.64/14/2005 8:27 AM 14.7 1580 7.8 9.54/21/2005 8:24 AM 16.8 1430 7.9 7.74/28/2005 8:23 AM 17.6 1220 7.8 9.15/5/2005 8:47 AM 19.6 1400 7.5 6.85/12/2005 8:23 AM 18.8 1400 7.5 7.95/19/2005 8:48 AM 20.0 1610 7.4 7.15/26/2005 8:53 AM 24.5 1180 7.1 5.06/2/2005 8:35 AM 21.6 769 7.5 7.36/9/2005 8:07 AM 19.9 808 7.4 5.86/16/2005 8:23 AM 22.2 807 7.5 7.0
8
E1: 541MER531 – Salt Slough @ Lander Avenue continued…
Date TimeTemp (ºC)
Field SC (umhos) pH
Dissolved Oxygen (mg/L)
Turbidity (ntu)
6/23/2005 9:10 AM 22.6 1070 NA 7.66/30/2005 8:36 AM 24.5 886 7.5 6.07/7/2005 8:39 AM 24.1 801 7.6 7.17/13/2005 11:46 AM 28.1 779 7.2 8.67/21/2005 8:24 AM 26.7 911 7.9 5.77/28/2005 8:39 AM 25.8 1010 7.8 6.88/4/2005 8:35 AM 25.6 945 7.7 6.08/11/2005 8:57 AM 24.8 866 7.6 7.18/18/2005 9:04 AM 23.8 940 7.4 6.38/25/2005 8:38 AM 23.3 970 7.7 5.99/1/2005 8:35 AM 22.8 962 7.7 9.19/8/2005 8:42 AM 21.3 1020 7.9 8.79/15/2005 8:25 AM 19.1 925 7.9 8.99/22/2005 9:04 AM 21.3 833 7.8 8.39/29/2005 8:28 AM 19.9 1100 7.7 7.5
Count 262 262 260 216 60Min 6.7 769 6.3 1.2 18.8Max 28.1 2470 8.6 14.9 330Mean 17.3 1420 7.7 8.3 94Geo Mean 16.4 1370 7.7 8.0 84.3Median 17.5 1400 7.7 8.1 83.2Quartile 1 12.4 1130 7.6 6.8 61.9Quartile 3 22.6 1670 7.8 9.6 119NOTE: For values reported as < (less than), half the detection limit was used.
NA = Data not applicableINA = Site was inaccessibleDRY = Site had no flow
9
E1: 541MER531 – Salt Slough @ Lander Avenue continued…
DateTSS
(mg/L)TOC
(mg/L)Total Coli
MPNE. coli MPN
10/26/2000 60 4.011/30/2000 34 1.412/21/2000 NA12/28/2000 NA 4.91/25/2001 73 6.42/22/2001 75 7.93/29/2001 NA <14/26/2001 6.65/31/2001 94 7.76/7/2001 120 116/14/2001 170 106/21/2001 NA 116/28/2001 160 8.07/26/2001 6.18/30/2001 60 149/20/2001 219/27/2001 39
10/25/2001 2111/29/2001 <11/31/2002 3.43/28/2002 NA4/24/2002 115/30/2002 4.36/20/2002 5.87/30/2002 >2419.6 4889/26/2002 4.7
10/17/2002 >2419.6 41110/31/2002 NA11/21/2002 6.412/19/2002 7.01/16/2003 613 843/27/2003 4.84/24/2003 8.6 >2419.6 1525/29/2003 7.16/26/2003 7.27/31/2003 >2419.6 478/28/2003 >2419.6 849/25/2003 >2419.6 56
10/30/2003 >2419.6 14011/20/2003 >2419.6 2041/29/2004 1414 632/26/2004 >2419.6 152
10
11
DateTSS
(mg/L)TOC
(mg/L)Total Coli
MPNE. coli MPN
3/25/2004 >2419.6 624/29/2004 >2419.6 1115/27/2004 >2419.6 1226/24/2004 >2419.6 427/29/2004 >2419.6 498/26/2004 >2419.6 689/30/2004 >2419.6 161
10/28/2004 >2419.6 61311/23/2004 8.3 >2419.6 17212/29/2004 7.5 >2419.6 9211/27/2005 9.1 2420 1452/24/2005 10 >2419.6 1083/31/2005 8.9 >2419.6 594/28/2005 NA >2419.6 785/26/2005 6.8 >2419.6 8666/30/2005 4.8 >2419.6 867/28/29/2
CounMin MaxMeaGeoMedQuaQuaNOT
NA =INA =DRY
E1: 541MER531 – Salt Slough @ Lander Avenue continued…
8/2005 5.8 >2419.6 585/2005 4.6 >2419.6 939/2005 5.2 >2419.6 86
t 10 38 30 3034 0.5 613 42
170 21 2420 921n 89 7.5 NA NA Mean 78 6 2271 124ian 74 6.9 2420 101rtile 1 60 4.8 2420 64rtile 3 114 8.8 2420 159E: For values reported as < (less than), half the detection limit was used For values reported as > (greater than), 2420 was used
Data not applicable Site was inaccessible
= Site had no flow
E1: 541MER531 – Salt Slough @ Lander Avenue continued…
DateNitrate (mg/L)
Nitrate-N (mg/L)
TKN (mg/L)
Ammonia-N (mg/L)
Phosphorus (mg/L)
Ortho-phosphate-
P (mg/L)
Potassium (mg/L)
BOD 5-Day (mg/L)
BOD 10-Day (mg/L)
10/26/2000 <2 <2 0.2 <1 8.6 1.6 2.811/30/2000 2.4 <2 0.2 <1 8.2 1.4 2.812/28/2000 2.5 <2 0.2 <1 8.7 1.6 2.81/25/2001 NA NA 0.2 <1 9.1 2.2 3.92/22/2001 15 <2 NA <1 9.4 2.4 4.43/29/2001 7.2 NA 0.4 <1 10 2.6 4.74/26/2001 7.8 <2 0.4 <1 8.8 1.9 3.35/31/2001 3.2 <2 0.3 <1 9 2.3 4.26/7/2001 10 <1.0 0.4 <1 9.2 3.1 4.76/14/2001 13 <2 <1 9.7 4.2 7.16/21/2001 7.1 <2 0.4 <1 8.6 3.1 4.96/28/2001 7.9 <2 0.4 <1 8.2 2.2 4.18/30/2001 3.6 <2 0.3 <1 8.69/27/2001 2.0 <2 0.2 <1 9
10/25/2001 <2 <2 0.2 <1 9 1.4 2.611/29/2001 NA NA NA 0.1 NA 1.2 2.312/27/2001 1.0 2.01/31/2002 1.7 2.72/28/2002 1.5 2.73/28/2002 2.4 4.04/24/2002 2.3 3.65/30/2002 2.0 2.96/20/2002 2.9 5.18/29/2002 2.8 5.19/26/2002 1.7 3.1
10/31/2002 2.0 3.211/21/2002 1.7 3.112/19/2002 2.7 4.01/30/2003 1.5 2.2
E1: 541MER531 – Salt Slough @ Lander Avenue continued…
DateNitrate (mg/L)
Nitrate-N (mg/L)
TKN (mg/L)
Ammonia-N (mg/L)
Phosphorus (mg/L)
Ortho-phosphate-
P (mg/L)
Potassium (mg/L)
BOD 5-Day (mg/L)
BOD 10-Day (mg/L)
Count 14 NA 13 NA 13 16 15 27 27Min 1.0 NA 0.5 NA 0.2 0.1 8.2 1.0 2.0Max 15.0 NA 1.0 NA 0.4 0.5 10.0 4.2 7.1Mean 6.0 NA 1.0 NA 0.3 0.5 8.9 2.1 3.6Geo Mean 4.3 NA 0.9 NA 0.3 0.5 8.9 2.0 3.5Median 5.4 NA 1.0 NA 0.3 0.5 9.0 2.0 3.3Quartile 1 2.4 NA 1.0 NA 0.2 0.5 8.6 1.6 2.8Quartile 3 7.9 NA 1.0 NA 0.4 0.5 9.2 2.5 4.3NOTE: For values reported as < (less than), half the detection limit was used.
NA = Data not applicableINA = Site was inaccessibleDRY = Site had no flow
13
E1: 541MER531 – Salt Slough @ Lander Avenue continued…
DateHardness
(mg/L)
Total Arsenic (ug/L)
Total Cadmium
(ug/L)
Total Chromium
(ug/L)
Total Copper (ug/L)
Total Lead (ug/L)
Total Nickel (ug/L)
Total Zinc (ug/L)
Total Mercury (ug/L)
10/26/2000 300 2.5 2.5 <5 <511/30/2000 320 1.3 1.6 <5 <5 2712/28/2000 340 1.7 2.3 <5 <5 4.71/25/2001 360 2.8 4 <5 5.5 6.22/22/2001 350 2.1 5.4 <5 5.6 103/29/2001 340 3.1 4.9 <5 6.5 114/26/2001 300 2.6 4.4 <5 5.6 9.65/31/2001 270 3.8 4.6 <5 6.6 126/7/2001 290 6.3 <1 3.7 6 <5 6.9 14 <0.26/14/2001 290 7.2 <1 5.4 6.9 <5 8.9 18 <0.26/21/2001 NA 6.6 <1 4.7 5.3 <5 8.1 15 <0.26/28/2001 NA 6.8 <1 5.5 6.5 <5 8.5 18 <0.27/26/2001 NA NA 5.5 5.4 <5 7.6 NA NA8/30/2001 280 5.6 <1 1.7 2.2 <5 <5 5.79/27/2001 280 6.2 <0.1 2.7 4.6 <5 5.1 8.7 <0.2
10/25/2001 310 4.4 <0.1 <1 1.9 <5 <5 <2 NA11/29/2001 320 4.9 <0.1 <1 <1 <5 <5 4.6 <0.212/27/2001 4.9 <0.1 3.1 2.7 <5 5.4 7.5 <0.22/28/2002 5.6 <0.1 3.5 5.3 <5.0 6.2 14 <0.23/28/2002 <4.0 <0.1 2.9 2.5 <5.0 NA 7.2 <0.24/24/2002 6.9 <0.1 2.6 3.9 <5.0 6.3 12 <0.25/30/2002 6.3 <0.1 4.2 4.2 <5.0 6.4 9.6 <0.26/20/2002 270 8.4 <0.1 5.6 5.5 <5.0 7.6 15 <0.29/26/2002 240 4.4 <0.1 2.3 2.7 <5.0 <5.0 6.5 <0.2
10/31/2002 280 6.7 <0.1 3.3 3.4 <5.0 5.6 7.3 <0.211/21/2002 300 4.2 <0.1 4.2 3.9 <5.0 6.8 11 <0.23/27/2003 360 6.4 <0.1 2.8 3.2 <5.0 <5.0 5.8 <0.24/24/2003 380 5.3 NA NA NA <5.0 5.6 12 <0.25/29/2003 270 7.3 <0.1 1.8 5.5 <5.0 <5.0 7.2 <0.26/26/2003 240 8.2 <0.1 6.2 6.6 <5.0 8.7 16 <0.2
14
E1: 541MER531 – Salt Slough @ Lander Avenue continued…
DateHardness
(mg/L)
Total Arsenic (ug/L)
Total Cadmium
(ug/L)
Total Chromium
(ug/L)
Total Copper (ug/L)
Total Lead (ug/L)
Total Nickel (ug/L)
Total Zinc (ug/L)
Total Mercury (ug/L)
Count 22 21 20 29 29 30 29 28 19Min 240.0 2.0 0.1 0.5 0.5 2.5 2.5 1.0 0.1Max 380.0 8.4 0.5 6.2 6.9 2.5 8.9 27.0 0.1Mean 304.1 5.9 0.2 3.2 4.1 2.5 5.4 10.6 0.1Geo Mean 301.8 5.7 0.1 2.8 3.6 2.5 4.9 9.2 0.1Median 300.0 6.3 0.1 2.9 4.2 2.5 5.6 9.8 0.1Quartile 1 280.0 4.9 0.1 2.3 2.7 2.5 2.5 7.0 0.1Quartile 3 335.0 6.8 0.2 4.2 5.4 2.5 6.8 14.0 0.1NOTE: For values reported as < (less than), half the detection limit was used.
NA = Data not applicableINA = Site was inaccessibleDRY = Site had no flow
15
E1: 541MER531 – Salt Slough @ Lander Avenue continued…
DateHardness
(mg/L)
Dissolved Arsenic (ug/L)
Dissolved Cadmium
(ug/L)
Dissolved Chromium
(ug/L)
Dissolved Copper (ug/L)
Dissolved Lead (ug/L)
Dissolved Nickel (ug/L)
Dissolved Zinc
(ug/L)
Dissolved Mercury (ug/L)
10/26/2000 300 <1 <1 <5 <5 <211/30/2000 320 <1 <1 <5 <5 <212/28/2000 340 <1 <1 <5 <5 <21/25/2001 360 <1 <1 <5 <5 <22/22/2001 350 <1 1.3 <5 <5 <23/29/2001 340 <1 2.4 <5 <5 <24/26/2001 300 <1 <1 <5 <5 <25/31/2001 270 <1 1.1 <5 <5 2.46/7/2001 290 3.4 <1 <1 1.9 <5 <5 <2 <0.26/14/2001 290 4.3 <1 <1 1.9 <5 <5 <2 <0.26/21/2001 NA 4.4 <1 <1 <1 <5 <5 <2 <0.26/28/2001 NA 4.4 <1 <1 <1 <5 <5 <2 <0.27/26/2001 NA NA NA NA NA NA NA NA8/30/2001 280 4.6 <1 <1 2.2 <5 <5 <29/27/2001 280 <4 <0.1 <1 1.7 <5 <5 <2 <0.2
10/25/2001 310 <4 <0.1 <1 1.4 <5 <5 <2 NA11/29/2001 320 <4 <0.1 <1 <1 <5 <5 7 <0.212/27/2001 <4 <0.1 <1 <1 <5 <5 <2 <22/28/2002 <4.0 <0.1 <1.0 2.1 <5.0 <5.0 4.1 <0.23/28/2002 <4.0 <0.1 <1.0 <1.0 <5.0 <5.0 2.5 <0.24/24/2002 4.2 <0.1 <1.0 2.3 <5.0 <5.0 5.1 <0.25/30/2002 4 <0.1 <1.0 1.4 <5.0 <5.0 <2.0 <0.26/20/2002 270 4.9 <0.1 <1.0 2.1 <5.0 <5.0 <2.0 <0.29/26/2002 240 4.6 <0.1 <1.0 1.9 <5.0 <5.0 <2.0 <0.2
10/31/2002 280 <4.0 <0.1 <1.0 1.2 <5.0 <5.0 <2.0 <0.211/21/2002 300 <4.0 <0.1 <1.0 <1.0 <5.0 <5.0 <2.0 <0.23/27/2003 3604/24/2003 3805/29/2003 2706/26/2003 240
16
E1: 541MER531 – Salt Slough @ Lander Avenue continued…
DateHardness
(mg/L)
Dissolved Arsenic (ug/L)
Dissolved Cadmium
(ug/L)
Dissolved Chromium
(ug/L)
Dissolved Copper (ug/L)
Dissolved Lead (ug/L)
Dissolved Nickel (ug/L)
Dissolved Zinc
(ug/L)
Dissolved Mercury (ug/L)
Count 22 17 17 25 25 25 25 25 15Min 240.0 2.0 0.1 0.5 0.5 2.5 2.5 1.0 0.1Max 380.0 4.9 0.5 0.5 2.4 2.5 2.5 7.0 1.0Mean 304.1 3.2 0.2 0.5 1.2 2.5 2.5 1.6 0.2Geo Mean 301.8 3.0 0.1 0.5 1.0 2.5 2.5 1.3 0.1Median 300.0 3.4 0.1 0.5 1.2 2.5 2.5 1.0 0.1Quartile 1 280.0 2.0 0.1 0.5 0.5 2.5 2.5 1.0 0.1Quartile 3 335.0 4.4 0.5 0.5 1.9 2.5 2.5 1.0 0.1NOTE: For values reported as < (less than), half the detection limit was used.
NA = Data not applicableINA = Site was inaccessibleDRY = Site had no flow
17
18
E1: 541MER531 – Salt Slough @ Lander Avenue continued…
DateChloride (mg/L)
Sulfate (mg/L)
Calcium (mg/L)
Magnesium (mg/L)
TDS (mg/L)
Carbonate (mg/L)
Bicarbonate (mg/L)
Total Alkalinity
(mg/L)Sodium (mg/L)
10/26/2000 240 210 62 36 950 <1 250 200 21011/30/2000 NA 210 64 38 1000 <1 240 200 22012/28/2000 270 250 68 42 1100 <1 250 210 2501/25/2001 260 290 73 42 1100 <1 240 200 2402/22/2001 250 250 75 39 1000 <1 230 190 2103/29/2001 210 240 73 39 960 <1 220 180 2004/26/2001 210 200 66 34 850 <1 170 170 1705/31/2001 200 150 56 31 760 <1 150 150 1606/7/2001 200 170 61 33 730 <1 180 150 1606/14/2001 180 160 64 33 740 <1 190 160 1606/21/2001 150 140 54 28 670 <1 170 140 1306/28/2001 170 150 NA NA 550 <1.0 160 130 NA8/30/2001 220 160 59 32 850 <1 220 180 1809/27/2001 240 170 56 34 880 <1 210 170 210
10/25/2001 280 220 62 39 NA <1 240 200 24011/29/2001 260 240 65 39 1000 <1 250 200 2303/27/2003 79 414/24/2003 310 260 79 445/29/2003 190 150 58 306/26/2003 270 260 55 25
Count 18 19 19 19 15 16 16 16 15Min 150 140 54 25 550 0.5 150 130 130Max 310 290 79 44 1100 0.5 250 210 250Mean 230 200 65 36 880 0.5 210 180 200Geo Mean 220 200 64 35 860 0.5 210 180 200Median 230 210 64 36 880 0.5 220 180 210Quartile 1 200 160 59 33 750 0.5 180 160 170Quartile 3 260 250 71 39 1000 0.5 240 200 230NOTE: For values reported as < (less than), half the detection limit was used.
NA = Data not applicableINA = Site was inaccessibleDRY = Site had no flow
E1: 541MER531 – Salt Slough @ Lander Avenue continued…
Date Result Control Result Control
Result (million/m
l)
Control (million/
ml) MDD(%)10/26/2000 100 100 NA NA6/18/2001 100 100 100 90
10/25/2001 100 100 100 10011/29/2001 NA NA 100 10012/27/2001 100 100 100 1001/31/2002 100 100 100 1002/28/2002 85 100 100 1004/24/2002 100 100 100 905/30/2002 100 100 100 1006/20/2002 100 100 100 1008/29/2002 100 100 100 1009/26/2002 100 95 100 1009/26/2002 100 95 100 100
10/31/2002 100 100 100 10011/21/2002 100 100 100 10012/19/2002 100 100 100 100 2.39* 2.93 N/A3/31/2003 100 100 100 100 4.36** 1.73 N/A5/29/2003 100 100 100 100 4.23** 2.03 1.0
Count 17 17 17 17 3 3 1
* Significantly reduced from the lab control.** Significantly greater than the lab control.^ Fish were from a "forced hatch," duplicate failed QA.1 Duplicate sample for the set was low - 77% recovery.
3 Samples qualified, but duplicate sample recovery for the set was high - 126% (53.8%/42.5%)NA = Data not applicableINA = Site was inaccessibleDRY = Site had no flow
2 Testing for the Fathead minnow was initiated when samples were approx. 48h old due to untimely shipping of fish by fish supplier.
96h Acute Fathead Minnow
(% Survival)
48h Acute Ceriodaphnia Dubia
(% Survival) Algae Cell Growth
19
E2: 541MER536 – Mud Slough Upstream of SLD Terminus Station Code:541MER536
Location: Latitude 37.25417, Longitude -120.90694
Date TimeTemp (ºC)
Field SC (umhos) pH
Dissolved Oxygen (mg/L)
Turbidity (ntu)
10/5/2000 11:01 AM 20.9 738 7.710/12/2000 12:45 PM 17.9 718 7.810/19/2000 9:30 AM 17.9 796 7.710/26/2000 4:10 PM 14.5 901 7.511/2/2000 10:35 AM 15.0 978 7.611/9/2000 11:35 AM 13.3 1110 7.7
11/16/2000 10:55 AM 10.7 1290 7.511/21/2000 8:50 AM 9.9 1340 7.911/30/2000 12:35 PM 11.6 1320 7.812/7/2000 10:50 AM 9.6 1430 7.9
12/12/2000 10:15 AM 11.6 1440 7.612/21/2000 12:25 PM 10.3 1490 7.812/28/2000 10:27 AM 7.8 1590 7.71/4/2001 10:30 AM 8.0 1750 7.91/11/2001 12:01 PM 8.9 1640 6.91/18/2001 11:40 AM 7.6 1630 7.61/25/2001 11:47 AM 9.7 1690 7.92/1/2001 12:04 PM 8.6 1750 7.32/8/2001 11:35 AM 8.4 1890 8.02/15/2001 12:25 PM 11.6 1840 8.22/22/2001 1:20 PM 12.7 1960 7.93/1/2001 10:15 AM 12.1 1940 7.83/8/2001 10:55 AM 16.6 1750 7.73/15/2001 12:40 PM 17.5 1960 7.93/22/2001 12:55 PM 20.8 2140 7.93/29/2001 11:48 AM 20.4 2700 8.14/5/2001 1:00 PM 18.0 2330 8.54/12/2001 11:07 AM 14.8 1890 8.04/19/2001 12:40 PM 18.3 2460 8.34/26/2001 11:20 AM 23.8 3400 8.05/3/2001 11:10 AM 16.6 1880 8.05/10/2001 10:03 AM 23.3 1460 7.85/17/2001 1:07 PM 26.5 1450 7.45/24/2001 11:37 AM 26.6 1910 7.65/31/2001 11:30 AM 29.1 1580 8.16/6/2001 NA 25.0 2590 8.0 9.46/7/2001 1:32 PM 28.1 1710 8.3 6.86/13/2001 8:34 AM 18.0 2960 6.5 7.7
20
E2: 541MER536 – Mud Slough Upstream of SLD Terminus continued…
Date TimeTemp (ºC)
Field SC (umhos) pH
Dissolved Oxygen (mg/L)
Turbidity (ntu)
6/14/2001 11:21 AM 23.1 3240 8.1 13.16/20/2001 11:08 AM 27.5 2290 8.1 13.16/21/2001 2:35 PM 32.8 2660 8.4 15.76/28/2001 1:58 PM 29.3 2570 8.5 16.67/5/2001 10:18 AM 25.7 1670 7.8 NA7/11/2001 1:05 PM 28.1 2350 8.2 17.07/19/2001 1:40 PM 29.2 2790 8.3 13.27/26/2001 9:18 AM 23.1 2200 7.9 10.78/2/2001 11:00 AM 24.4 2000 8.3 11.38/9/2001 9:51 AM 23.2 3170 7.9 8.08/16/2001 11:32 AM 25.6 1390 8.0 7.88/23/2001 9:54 AM 22.7 812 8.1 8.28/30/2001 10:56 AM 23.3 1430 7.7 6.49/6/2001 9:31 AM 21.9 1200 7.8 4.99/13/2001 10:53 AM 23.4 1230 7.8 7.79/20/2001 9:56 AM 22.4 1120 7.8 5.39/27/2001 10:30 AM 21.5 1020 7.6 4.310/4/2001 9:17 AM 22.0 1130 7.5 2.1
10/11/2001 10:41 AM 18.3 1130 7.6 4.210/18/2001 10:30 AM 18.7 1230 7.5 4.410/25/2001 11:19 AM 15.8 1420 7.7 6.311/1/2001 11:17 AM 17.1 1330 7.8 7.011/8/2001 11:19 AM 15.4 1450 8.1 7.3
11/15/2001 9:51 AM 15.5 1250 7.8 6.011/20/2001 1:52 PM 15.0 1420 7.9 8.711/29/2001 9:55 AM 10.9 1540 NA NA12/6/2001 10:29 AM 9.9 1590 7.9 9.9
12/13/2001 10:13 AM 8.8 2110 8.0 10.612/20/2001 11:37 AM 9.7 1960 8.1 12.112/27/2001 2:10 PM 10.3 1920 7.9 11.71/3/2002 10:57 AM 12.9 1700 7.7 8.41/10/2002 10:14 AM 11.7 1880 7.9 9.51/17/2002 10:05 AM 6.6 2090 7.9 11.11/24/2002 12:41 PM 8.2 2300 7.9 12.11/31/2002 12:20 PM 7.0 2240 8.2 13.52/7/2002 9:48 AM 10.6 2080 8.1 10.82/14/2002 10:08 AM 11.5 2250 7.9 8.42/21/2002 11:12 AM 14.7 2240 7.8 9.02/28/2002 10:46 AM 15.9 2160 7.9 7.43/7/2002 9:17 AM 14.6 2290 8.1 9.1
21
E2: 541MER536 – Mud Slough Upstream of SLD Terminus continued…
Date TimeTemp (ºC)
Field SC (umhos) pH
Dissolved Oxygen (mg/L)
Turbidity (ntu)
3/14/2002 10:31 AM 11.8 2820 7.9 11.03/21/2002 10:27 AM 15.6 2870 8.4 8.73/28/2002 12:30 PM 19.1 3200 8.4 9.54/4/2002 9:28 AM 17.8 3290 8.1 7.94/11/2002 10:17 AM 18.9 3820 8.1 10.44/18/2002 8:56 AM 14.9 2080 8.0 9.14/25/2002 10:39 AM 20.5 1410 7.8 8.05/2/2002 9:07 AM 15.6 3050 8.2 12.35/9/2002 10:59 AM 20.5 1260 8.2 11.25/16/2002 10:30 AM 21.7 1530 7.1 NA NA5/23/2002 8:10 AM 16.6 1660 8.0 NA5/30/2002 1:24 PM 31.4 2580 8.3 14.06/6/2002 9:14 AM 23.9 1590 8.0 NA6/13/2002 11:49 AM 25.2 1940 8.3 NA6/20/2002 9:20 AM 23.8 1190 8.5 NA6/27/2002 10:37 AM 24.6 2890 8.2 11.07/3/2002 11:25 AM 26.4 2420 8.6 NA7/11/2002 12:58 PM 29.8 1620 8.3 NA7/18/2002 10:42 AM 25.3 1710 8.3 10.9 68.97/25/2002 9:12 AM 24.0 853 7.9 7.88/1/2002 10:17 AM 26.3 1150 8.3 9.48/8/2002 10:45 AM 23.8 1250 8.7 11.28/15/2002 9:30 AM 23.3 1350 8.1 9.58/22/2002 9:28 AM 21.9 785 7.8 7.58/29/2002 9:22 AM 21.4 1310 8.3 NA9/5/2002 9:10 AM 21.2 1270 8.0 7.89/12/2002 9:37 AM 21.8 1290 8.0 8.99/19/2002 9:43 AM 21.7 1120 8.1 9.1 NA9/26/2002 12:22 PM 25.0 972 7.8 9.310/3/2002 9:58 AM 15.1 1190 7.9 12.0
10/10/2002 1:10 PM 23.4 1360 8.3 9.810/17/2002 9:30 AM 16.6 937 8.1 8.7 68.210/24/2002 10:57 AM 15.9 989 7.7 7.210/31/2002 10:30 AM 14.3 1200 7.7 4.8 15.311/7/2002 10:13 AM 14.0 1330 7.7 5.7
11/14/2002 10:18 AM 14.2 1300 7.7 7.011/21/2002 12:56 PM 13.4 1510 7.6 7.1 18.011/26/2002 12:15 PM 12.4 1800 7.9 8.812/5/2002 10:15 AM 10.9 1830 7.8 9.4 35.0
12/12/2002 9:33 AM 11.2 1640 7.7 9.712/19/2002 8:39 AM 8.8 1560 7.8 9.0 23.7
22
E2: 541MER536 – Mud Slough Upstream of SLD Terminus continued…
Date TimeTemp (ºC)
Field SC (umhos) pH
Dissolved Oxygen (mg/L)
Turbidity (ntu)
12/24/2002 INA INA INA INA INA1/2/2003 1:02 PM 10.4 1310 7.8 14.31/9/2003 10:43 AM 9.6 1990 7.7 11.41/16/2003 12:17 PM 11.6 1570 7.8 9.0 64.61/23/2003 9:05 AM 10.6 1960 7.5 13.11/30/2003 10:58 AM 12.7 2030 7.7 8.1 37.12/6/2003 10:31 AM 9.1 2310 7.9 12.52/13/2003 12:25 PM 13.1 1890 7.9 9.8 31.62/20/2003 11:38 AM 12.1 1960 8.0 11.4 44.62/27/2003 9:20 AM 12.6 1930 7.9 7.83/6/2003 11:12 AM 14.9 2150 7.8 11.6 NA3/13/2003 10:36 AM 18.4 1970 8.0 8.1 142.03/20/2003 9:05 AM 14.7 2180 8.0 8.8 113.03/27/2003 9:57 AM 15.7 1940 8.3 9.2 123.04/3/2003 1:22 PM 17.5 2180 7.7 10.8 82.84/10/2003 10:32 AM 19.7 2790 8.2 10.6 52.84/17/2003 9:27 AM 16.5 3300 8.0 9.7 34.24/24/2003 10:27 AM 16.5 1880 8.4 10.2 66.05/1/2003 9:46 AM 17.4 2020 8.2 9.8 NA5/8/2003 9:13 AM 16.0 2820 7.9 NA 25.95/15/2003 9:26 AM 18.3 2220 7.9 10.75/22/2003 10:30 AM 23.9 2190 8.1 10.6 43.65/29/2003 10:05 AM 25.4 1650 7.9 8.36/5/2003 10:18 AM 25.0 1130 8.1 7.6 110.06/12/2003 10:35 AM 21.6 1210 8.2 9.3 126.06/19/2003 10:30 AM 23.9 1650 8.4 7.8 78.26/26/2003 9:51 AM 24.5 1210 8.1 9.2 114.07/3/2003 9:57 AM 24.7 1260 8.2 13.67/10/2003 9:49 AM 24.5 1560 8.4 11.97/17/2003 10:03 AM 26.1 711 8.0 6.67/24/2003 9:36 AM 26.0 1260 8.4 9.8 92.97/31/2003 10:05 AM 24.7 1360 8.5 7.7 41.08/7/2003 9:29 AM 23.6 1010 8.2 9.0 102.08/14/2003 9:45 AM 21.8 930 8.4 NA8/21/2003 9:20 AM 22.5 1260 8.1 8.8 65.08/28/2003 9:45 AM 22.9 795 7.7 NA 33.29/4/2003 9:25 AM 24.6 783 7.7 5.5 22.09/11/2003 11:50 AM INA INA INA INA INA9/18/2003 9:46 AM 20.1 679 7.8 7.7 12.39/25/2003 10:33 AM 21.9 722 7.5 4.2 49.510/2/2003 10:15 AM 20.8 774 7.4 4.4 28.8
23
E2: 541MER536 – Mud Slough Upstream of SLD Terminus continued…
Date TimeTemp (ºC)
Field SC (umhos) pH
Dissolved Oxygen (mg/L)
Turbidity (ntu)
10/9/2003 9:43 AM 20.6 808 7.4 3.9 24.310/16/2003 11:49 AM 18.2 989 7.5 6.1 23.710/23/2003 10:58 AM 19.4 986 7.5 4.9 33.110/30/2003 9:17 AM 15.3 1150 7.7 6.2 15.911/6/2003 10:08 AM 13.8 1130 7.7 8.3 32.0
11/13/2003 8:57 AM 13.1 1190 7.7 7.8 19.211/20/2003 9:41 AM 13.3 1230 7.7 7.9 NA11/26/2003 8:56 AM 7.9 1410 7.9 10.1 12.212/4/2003 9:36 AM 12.0 1500 7.8 9.6
12/11/2003 9:07 AM 10.7 1500 7.9 10.8 NA12/18/2003 9:58 AM 8.6 1560 8.0 12.6 NA12/23/2003 9:28 AM 10.8 1640 7.7 13.5 NA12/30/2003 10:05 AM 8.1 1530 7.9 12.2 NA1/8/2004 8:42 AM 8.9 1740 7.8 9.8 NA1/15/2004 10:00 AM 9.6 1980 7.8 9.3 NA1/22/2004 9:27 AM 8.6 2010 7.8 14.3 24.21/29/2004 10:20 AM 10.5 2140 7.9 9.8 NA2/5/2004 9:20 AM 9.6 2150 8.0 11.4 35.62/12/2004 9:35 AM 10.5 2350 8.0 11.4 NA2/19/2004 9:14 AM 12.0 2230 7.9 11.0 NA2/26/2004 9:54 AM 11.2 1970 7.9 8.8 NA3/4/2004 9:26 AM 11.8 1780 8.1 10.3 100.03/11/2004 10:06 AM 17.1 2180 7.9 8.3 NA3/18/2004 8:41 AM 19.2 2370 8.0 8.33/25/2004 10:19 AM 18.1 2390 8.1 7.4 85.64/1/2004 9:41 AM 15.5 2360 8.3 10.24/8/2004 9:58 AM 17.8 3720 8.2 9.9 40.04/15/2004 9:52 AM 17.6 2420 8.2 10.5 57.54/22/2004 10:09 AM 16.0 3210 8.4 13.7 54.94/29/2004 11:16 AM 19.4 1720 8.2 NA 58.05/6/2004 10:44 AM 22.6 2090 8.0 18.9 39.45/13/2004 10:26 AM 20.1 1110 8.1 19.0 92.25/20/2004 10:12 AM 21.4 NA 8.0 8.9 46.65/27/2004 9:36 AM 22.4 1550 7.9 NA NA6/3/2004 10:34 AM 24.0 2290 8.3 12.1 51.56/10/2004 10:17 AM 21.4 2300 8.5 11.6 26.96/17/2004 10:55 AM 25.2 1630 8.1 11.3 30.86/24/2004 10:01 AM 22.9 1730 8.0 8.9 51.37/1/2004 10:08 AM 22.5 1530 8.1 10.8 NA7/8/2004 9:46 AM 24.7 1250 7.9 7.9 NA7/15/2004 10:17 AM 25.5 1150 7.9 10.8 NA
24
E2: 541MER536 – Mud Slough Upstream of SLD Terminus continued…
Date TimeTemp (ºC)
Field SC (umhos) pH
Dissolved Oxygen (mg/L)
Turbidity (ntu)
7/22/2004 11:45 AM 29.1 1280 8.2 12.5 NA7/29/2004 9:45 AM 25.8 1200 8.0 10.6 NA8/5/2004 9:14 AM 22.9 979 8.0 9.3 NA8/12/2004 9:55 AM INA INA INA INA INA8/19/2004 11:30 AM 27.7 2460 8.2 11.4 NA8/26/2004 10:15 AM 23.1 1520 8.0 6.2 NA9/2/2004 9:31 AM 23.2 755 7.8 5.5 NA9/9/2004 11:35 AM 25.9 807 7.7 7.4 NA9/16/2004 11:15 AM 22.7 847 7.7 5.5 NA9/23/2004 12:58 PM 22.3 981 7.7 8.0 NA9/30/2004 9:46 AM 18.2 899 7.8 5.9 NA10/7/2004 9:33 AM 20.1 829 7.6 4.3
10/14/2004 9:09 AM 18.9 789 7.5 6.810/21/2004 10:43 AM 15.1 830 NA 8.910/28/2004 9:29 AM INA INA INA INA11/4/2004 11:09 AM 12.8 1230 8.0 9.7
11/11/2004 9:06 AM 14.5 1170 7.6 6.811/18/2004 9:28 AM 13.3 1210 7.7 7.311/23/2004 12:31 PM 10.0 1330 7.8 9.412/2/2004 10:34 AM 7.4 1580 8.0 11.712/9/2004 9:15 AM 10.6 1370 8.0 10.3
12/16/2004 10:14 AM 10.9 1440 7.8 9.712/22/2004 12:09 PM 8.6 1480 7.9 14.012/29/2004 10:55 AM 9.5 1390 7.8 9.61/6/2005 8:31 AM 9.5 1430 7.7 11.81/13/2005 10:24 AM 9.0 1280 7.8 9.71/20/2005 9:40 AM 9.0 1280 7.7 11.41/27/2005 9:39 AM 10.7 1950 7.9 11.52/3/2005 9:43 AM 10.8 1930 7.8 9.92/10/2005 9:40 AM 12.3 2110 7.9 9.62/17/2005 9:56 AM 14.0 1660 7.8 10.92/24/2005 9:59 AM 14.1 1360 7.9 8.63/3/2005 9:04 AM 14.7 1660 7.9 9.53/10/2005 11:08 AM 19.2 1740 8.0 11.03/17/2005 9:04 AM 16.2 2250 7.9 12.03/24/2005 9:50 AM 14.4 1870 8.0 9.83/31/2005 9:29 AM 14.2 2270 8.1 9.34/7/2005 10:08 AM 17.5 1410 8.3 8.64/14/2005 9:09 AM 14.0 2500 8.5 10.64/21/2005 9:56 AM 17.6 2540 8.2 8.64/28/2005 9:21 AM 18.2 1490 8.0 12.2
25
E2: 541MER536 – Mud Slough Upstream of SLD Terminus continued…
Date TimeTemp (ºC)
Field SC (umhos) pH
Dissolved Oxygen (mg/L)
Turbidity (ntu)
5/5/2005 10:16 AM 20.2 1070 8.1 9.75/12/2005 9:21 AM 19.2 1690 8.5 9.45/19/2005 10:06 AM 21.6 2590 8.1 8.65/26/2005 10:20 AM 24.2 981 7.9 5.36/2/2005 10:13 AM 21.0 1340 8.1 8.76/9/2005 8:50 AM 20.2 1080 8.0 7.46/16/2005 9:48 AM 23.0 1230 8.0 8.76/23/2005 10:39 AM 23.5 949 NA 8.66/30/2005 10:53 AM 26.5 1110 8.2 10.37/7/2005 9:29 AM 25.9 1070 8.0 11.57/13/2005 10:05 AM 28.1 970 7.3 11.27/21/2005 9:14 AM 27.0 1140 8.2 8.07/28/2005 11:09 AM 29.3 1270 8.7 13.18/4/2005 9:27 AM 25.7 1130 8.5 9.88/11/2005 11:08 AM 27.3 1110 8.4 11.38/18/2005 9:57 AM 23.2 1170 8.3 10.78/25/2005 10:05 AM 22.2 1110 8.0 7.79/1/2005 9:24 AM 21.9 874 8.0 9.79/8/2005 10:00 AM 21.8 784 8.1 10.39/15/2005 9:34 AM 19.3 652 7.9 8.29/22/2005 10:33 AM 22.4 854 8.0 9.69/29/2005 9:35 AM 20.1 872 7.8 9.2
Count 260 259 257 210 54Min 6.6 652 6.5 2.1 12.2Max 32.8 3820 8.7 19.0 142.0Mean 18.0 1660 7.9 9.5 54.1Geo Mean 16.8 1540 7.9 9.1 44.8Median 18.1 1550 7.9 9.4 44.1Quartile 1 12.7 1200 7.8 7.9 29.3Quartile 3 23.1 2030 8.1 11.0 68.7NOTE: For values reported as < (less than), half the detection limit was used.
NA = Data not applicableINA = Site was inaccessibleDRY = Site had no flow
26
E2: 541MER536 – Mud Slough Upstream of SLD Terminus continued…
DateTSS
(mg/L)TOC
(mg/L)Total Coli
MPNE. coli MPN
10/26/2000 20 1411/30/2000 14 6.912/28/2000 11 131/25/2001 22 9.92/22/2001 NA 2.53/29/2001 150 <14/26/2001 115/31/2001 31 116/7/2001 35 136/14/2001 14 176/21/2001 NA 196/28/2001 12 127/26/2001 8.48/30/2001 27 279/20/2001 159/27/2001 28 24
10/25/2001 2511/29/2001 NA1/31/2002 NA2/28/2002 9.63/28/2002 9.64/25/2002 NA5/30/2002 9.56/20/2002 5.68/1/2002 >2419.6 1999/26/2002 NA
10/17/2002 >2419.6 19710/31/2002 2.111/21/2002 1112/19/2002 9.01/16/2003 1733 963/27/2003 8.94/24/2003 7.7 >2419.6 24205/29/2003 106/26/2003 5.87/31/2003 >2419.6 4618/28/2003 >2419.6 2859/25/2003 >2419.6 173
10/30/2003 >2419.6 4811/20/2003 >2419.6 551/29/2004 727 1522/26/2004 >2419.6 326
27
28
DateTSS
(mg/L)TOC
(mg/L)Total Coli
MPNE. coli MPN
3/25/2004 >2419.6 1484/29/2004 >2419.6 5175/27/2004 >2419.6 2616/24/2004 >2419.6 9217/29/2004 >2419.6 3458/26/2004 >2419.6 1019/30/2004 >2419.6 38
11/23/2004 14 >2419.6 3312/29/2004 10 >2419.6 5171/27/2005 13 >2419.6 912/24/2005 13 >2419.6 1143/31/2005 16 >2419.6 934/28/2005 NA >2419.6 1355/26/2005 9.8 >2419.6 13006/30/2005 5.1 >2419.6 1077/28/2005 6.0 >2419.6 498/29/29/2
CounMin MaxMeaGeoMedQuaQuaNOT
NA =INA =DRY
E2: 541MER536 – Mud Slough Upstream of SLD Terminus continued…
5/2005 8.3 >2419.6 1962/2005 NA9/2005 13 >2419.6 107
t 11 38 29 2911 0.5 727 33
150 27 2420 2420n 33 11 NA NA Mean 24 9 2295 179ian 22 10 2420 152rtile 1 14 8.3 2420 96rtile 3 30 13 2420 326E: For values reported as < (less than), half the detection limit was used For values reported as > (greater than), 2420 was used
Data not applicable Site was inaccessible
= Site had no flow
E2: 541MER536 – Mud Slough Upstream of SLD Terminus continued…
DateNitrate (mg/L)
Nitrate-N (mg/L)
TKN (mg/L)
Ammonia-N (mg/L)
Phosphorus (mg/L)
Ortho-phosphate-
P (mg/L)
Potassium (mg/L)
BOD 5-Day (mg/L)
BOD 10-Day (mg/L)
10/26/2000 <2 <2 0.4 <1 11 2.9 6.111/30/2000 <2 <2 0.2 <1 11 1.2 2.712/28/2000 <2 <2 0.2 <1 11 1.2 2.41/25/2001 <2 <2 0.2 <1 10 2.4 42/22/2001 2.5 <2 0.3 <1 12 3.3 6.53/29/2001 2.9 2.3 0.3 <1 15 5.7 10.24/26/2001 <2 <2 <1 0.2 <1 12 3.3 5.45/31/2001 <2 <2 0.2 NA 9.4 3.8 76/7/2001 3.9 <1.0 0.2 <1 8.5 4 5.66/14/2001 <2 <2 <1 8.5 2.4 3.96/21/2001 <2 <2 0.3 <1 9.6 4.2 66/28/2001 <2 <2 0.2 <1 11 2.1 3.38/30/2001 <2 <2 0.4 <1 129/27/2001 <2 <2 0.4 <1 11
10/25/2001 2.5 6.511/29/2001 NA NA NA 0.2 12 1.5 3.312/27/2001 NA 0.8 0.2 0.1 7.2 1.2 31/31/2002 NA NA 0.2 NA NA 2.2 3.92/28/2002 NA NA NA 0.3 NA 2.5 54/25/2002 NA NA 0.3 NA 8.2 3.3 5.45/30/2002 NA NA NA 0.2 NA 2.5 3.96/20/2002 NA 1 0.3 0.1 7.4 2.4 4.37/18/2002 <2.0 <2.0 NA <1.0 8.87/25/2002 4.1 <2.0 0.2 <1.0 6.38/15/2002 <2.0 <2.0 0.3 <1.0 7.28/29/2002 NA 1.4 0.3 0.1 9 4.7 89/26/2002 NA 0.8 NA 0.1 7.4 2.6 5
10/31/2002 NA 1.2 0.3 0.3 6.4 3.3 6.5
29
E2: 541MER536 – Mud Slough Upstream of SLD Terminus continued…
DateNitrate (mg/L)
Nitrate-N (mg/L)
TKN (mg/L)
Ammonia-N (mg/L)
Phosphorus (mg/L)
Ortho-phosphate-
P (mg/L)
Potassium (mg/L)
BOD 5-Day (mg/L)
BOD 10-Day (mg/L)
11/21/2002 NA 1.2 0.3 0.2 7 1.9 412/19/2002 NA 1.3 0.3 <0.03 6 2.2 3.61/30/2003 NA 1.3 0.3 0.3 5.9 2.3 42/27/2003 4 1.4 0.2 <1.0 113/27/2003 NA NA 0.5 <1.0 114/10/2003 <2.0 2.6 0.5 <1.0 135/15/2003 <2.0 <2.0 0.2 <1.0 105/29/2003 <2.0 <2.0 NA <1.0 106/12/2003 4.7 <2.0 0.2 <1.0 76/26/2003 5.1 <2.0 NA <1.0 6.77/17/2003 4.1 1.6 0.3 <1.0 6.77/31/2003 2.2 NA 0.2 <1.0 5.88/14/2003 2.6 <1.0 0.1 <1.0 5.78/28/2003 <2.0 2.2 0.5 <1.0 109/25/2003 <2.0 1.8 0.6 <1.0 8.4
10/30/2003 <2.0 1.9 0.6 <1.0 1111/20/2003 <2.0 <1.0 0.2 <1.0 9.81/29/2004 0.3 1.2 0.2 0.3 0.22/26/2004 0.9 1.6 NA 0.4 0.33/11/2004 2.9 1.4 0.1 0.4 0.43/25/2004 0.9 1.9 0.3 0.8 0.64/15/2004 0.8 1.2 0.1 0.4 0.24/29/2004 <0.05 1.6 0.1 0.3 0.15/13/2004 0.5 1 0.2 0.4 0.16/10/2004 0.1 0.9 0.1 0.2 0.26/24/2004 <0.05 0.8 0 0.2 0.1
30
E2: 541MER536 – Mud Slough Upstream of SLD Terminus continued…
DateNitrate (mg/L)
Nitrate-N (mg/L)
TKN (mg/L)
Ammonia-N (mg/L)
Phosphorus (mg/L)
Ortho-phosphate-
P (mg/L)
Potassium (mg/L)
BOD 5-Day (mg/L)
BOD 10-Day (mg/L)
7/15/2004 0.6 0.5 0.1 NA NA7/29/2004 1.6 1 NA 0.2 NA8/26/2004 <0.16 1.4 NA 0.4 0.39/16/2004 <0.16 1.7 0.2 0.4 0.19/30/2004 0.1 1.1 0.2 NA 0.1
11/23/2004 0.1 1.3 NA 0.3 0.212/29/2004 0.4 1 0.1 0.2 0.21/27/2005 0.5 1.4 0.4 0.4 0.32/24/2005 0.3 1.3 0.3 0.5 0.33/31/2005 0.4 1.8 0.2 0.6 0.44/28/2005 0.5 1.3 0.4 NA 0.25/12/2005 0.1 NA NA 0.3 NA5/26/2005 0.1 1.1 0.1 0.3 0.16/16/2005 NA 0.8 NA NA NA6/30/2005 1.4 1 0.1 0.3 0.17/13/2005 0.5 0.8 NA NA NA9/29/2005 <0.05 1.2 NA NA 0.1
Count 30 25 62 18 56 62 41 26 26Min 1.0 0.03 0.5 0.1 0.1 0.02 5.7 1.2 2.4Max 5.1 2.9 2.6 0.5 0.8 0.6 15.0 5.7 10.2Mean 1.9 0.5 1.2 0.2 0.3 0.3 9.2 2.8 5.0Geo Mean 1.5 0.3 1.1 0.2 0.3 0.3 8.9 2.6 4.7Median 1.0 0.4 1.0 0.2 0.3 0.5 9.4 2.5 4.7Quartile 1 1.0 0.1 1.0 0.1 0.2 0.2 7.2 2.2 3.9Quartile 3 2.6 0.6 1.4 0.3 0.4 0.5 11.0 3.3 6.1NOTE: For values reported as < (less than), half the detection limit was used.
NA = Data not applicableINA = Site was inaccessibleDRY = Site had no flow
31
E2: 541MER536 – Mud Slough Upstream of SLD Terminus continued…
DateHardness
(mg/L)
Total Arsenic (ug/L)
Total Cadmium
(ug/L)
Total Chromium
(ug/L)
Total Copper (ug/L)
Total Lead (ug/L)
Total Nickel (ug/L)
Total Zinc (ug/L)
Total Mercury (ug/L)
10/26/2000 200 3.7 2.1 <5 5.811/30/2000 260 <1 1.2 <5 <5 <212/28/2000 310 1.1 1.8 <5 <5 <21/25/2001 320 1.9 2.2 <5 5 <22/22/2001 370 3.4 3.3 <5 8.5 4.23/29/2001 500 11 7 <5 20 144/26/2001 580 1.4 2.1 <5 5.2 <25/31/2001 310 2.7 2.8 <5 6.5 6.16/7/2001 350 3.6 <1 2.3 2.9 <5 5.5 3.8 <0.26/14/2001 590 3.5 <1 <1 1.2 <5 <5 <2 <0.26/21/2001 NA 4.9 <1 <1 1.3 <5 <5 <2 <0.26/28/2001 470 3.4 <1 <1 1.1 <5 <5 <2 <0.27/26/2001 NA NA 1.1 1.2 <5 <5 <2 NA8/30/2001 260 4.7 <1 1.4 1.3 <5 5.2 <29/27/2001 200 5.5 <1 <1 1.6 <5 5 2 <0.2
10/25/2001 270 4 <0.1 <1 1.3 <5 <5 <2 <0.211/29/2001 280 4.6 <0.1 2 <1 <5 <5 3 <0.212/27/2001 320 <4 <0.1 1.4 2.2 <5 <5 2.1 <0.21/31/2002 <4.0 <0.1 <1.0 NA <5.0 <5.0 <2.0 <0.22/28/2002 410 6.5 <0.1 2.8 3.2 <5.0 7.8 4.3 <0.23/28/2002 740 6 <0.1 6.7 3.9 <5.0 12 6.2 <0.24/25/2002 300 6 <0.1 <1.0 2.5 <5.0 <5.0 <2.0 <0.25/30/2002 460 7.6 <0.1 2.3 2.6 <5.0 6.2 <2.0 <0.26/20/2002 240 5.2 <0.1 5.4 3.7 <5.0 8.8 5.2 <0.29/26/2002 200 6.1 <0.1 2.1 NA <5.0 <5.0 2.2 <0.2
10/31/2002 240 <4.0 <0.1 1 1.5 <5.0 <5.0 <2.0 <0.211/21/2002 300 <4.0 <0.1 1.1 1.2 <5.0 <5.0 <2.0 <0.2
32
E2: 541MER536 – Mud Slough Upstream of SLD Terminus continued…
DateHardness
(mg/L)
Total Arsenic (ug/L)
Total Cadmium
(ug/L)
Total Chromium
(ug/L)
Total Copper (ug/L)
Total Lead (ug/L)
Total Nickel (ug/L)
Total Zinc (ug/L)
Total Mercury (ug/L)
3/27/2003 370 7.5 NA 7.9 6 <5.0 12 9.5 <0.24/24/2003 370 5.7 <0.1 NA NA NA 8.9 5.1 <0.25/29/2003 330 5.5 <0.1 6.2 4.9 <5.0 8.2 8.3 <0.26/26/2003 250 4.3 <0.1 14 5.4 <5.0 12 9.2 <0.2
Count 28 22 21 30 28 30 31 30 21Min 200.0 2.0 0.1 0.5 0.5 2.5 2.5 1.0 0.1Max 740.0 7.6 0.5 14.0 7.0 2.5 20.0 14.0 0.1Mean 350.0 4.7 0.2 2.9 2.6 2.5 5.7 3.3 0.1Geo Mean 330.4 4.3 0.1 1.7 2.2 2.5 4.6 2.2 0.1Median 315.0 4.8 0.1 1.7 2.2 2.5 5.0 1.5 0.1Quartile 1 260.0 3.5 0.1 0.6 1.3 2.5 2.5 1.0 0.1Quartile 3 380.0 5.9 0.5 3.3 3.2 2.5 8.0 4.9 0.1NOTE: For values reported as < (less than), half the detection limit was used.
NA = Data not applicableINA = Site was inaccessibleDRY = Site had no flow
33
E2: 541MER536 – Mud Slough Upstream of SLD Terminus continued…
DateHardness
(mg/L)
Dissolved Arsenic (ug/L)
Dissolved Cadmium
(ug/L)
Dissolved Chromium
(ug/L)
Dissolved Copper (ug/L)
Dissolved Lead (ug/L)
Dissolved Nickel (ug/L)
Dissolved Zinc
(ug/L)
Dissolved Mercury (ug/L)
10/26/2000 200 <1 <1 <5 <5 <211/30/2000 260 <1 1.5 <5 <5 <212/28/2000 310 <1 <1 <5 <5 <21/25/2001 320 <1 <1 <5 <5 <22/22/2001 370 <1 <1 <5 <5 <23/29/2001 500 <1 2.6 <5 <5 <24/26/2001 580 <1 <1 <5 <5 <25/31/2001 310 <1 <1 <5 <5 4.16/7/2001 350 3 <1 <1 1.5 <5 <5 <2 <0.26/14/2001 590 2.9 <1 <1 <1 <5 <5 <2 <0.26/21/2001 NA 4.2 <1 <1 <1 <5 <5 <2 <0.26/28/2001 470 3.5 <1 <1 <1 <5 <5 <2 <0.27/26/2001 NA NA NA NA NA NA NA NA8/30/2001 260 4.2 <1 <1 <1 <5 <5 <29/27/2001 200 4.8 <1 <1 <1 <5 <5 <2 <0.2
10/25/2001 270 4.4 <0.1 <1 1.3 <5 <5 <2 <0.211/29/2001 280 4.2 <0.1 <1 1.6 <5 <5 4.7 <0.212/27/2001 320 <4 <0.1 <1 1.1 <5 <5 <2 <0.21/31/2002 <4.0 <0.1 <1.0 NA <5.0 <5.0 <2.0 <0.22/28/2002 410 5.5 <0.1 <1.0 1.3 <5.0 <5.0 2.1 <0.23/28/2002 740 5.3 <0.1 2.4 2.1 <5.0 6.0 2.1 <0.24/25/2002 300 6.2 <0.1 <1.0 1.9 <5.0 <5.0 NA <0.25/30/2002 460 5.6 <0.1 <1.0 1.4 <5.0 <5.0 <2.0 <0.26/20/2002 240 4.2 <0.1 <1.0 2.2 <5.0 <5.0 2.2 <0.29/26/2002 200 5.3 <0.1 <1.0 1.8 <5.0 <5.0 <2.0 <0.2
10/31/2002 240 <4.0 <0.1 <1.0 1.2 <5.0 <5.0 <2.0 <0.211/21/2002 300 4.7 <0.1 1.3 1.6 <5.0 <5.0 <2.0 <0.2
34
E2: 541MER536 – Mud Slough Upstream of SLD Terminus continued…
DateHardness
(mg/L)
Dissolved Arsenic (ug/L)
Dissolved Cadmium
(ug/L)
Dissolved Chromium
(ug/L)
Dissolved Copper (ug/L)
Dissolved Lead (ug/L)
Dissolved Nickel (ug/L)
Dissolved Zinc
(ug/L)
Dissolved Mercury (ug/L)
Count 24 18 18 26 25 26 26 25 17Min 200.0 2.0 0.1 0.5 0.5 2.5 2.5 1.0 0.1Max 740.0 6.2 0.5 2.4 2.6 2.5 6.0 4.7 0.1Mean 353.3 4.1 0.2 0.6 1.1 2.5 2.6 1.4 0.1Geo Mean 331.2 3.9 0.1 0.6 1.0 2.5 2.6 1.2 0.1Median 310.0 4.2 0.1 0.5 1.2 2.5 2.5 1.0 0.1Quartile 1 260.0 3.1 0.1 0.5 0.5 2.5 2.5 1.0 0.1Quartile 3 422.5 5.2 0.5 0.5 1.6 2.5 2.5 1.0 0.1NOTE: For values reported as < (less than), half the detection limit was used.
NA = Data not applicableINA = Site was inaccessibleDRY = Site had no flow
35
E2: 541MER536 – Mud Slough Upstream of SLD Terminus continued…
DateChloride (mg/L)
Sulfate (mg/L)
Calcium (mg/L)
Magnesium (mg/L)
TDS (mg/L)
Carbonate (mg/L)
Bicarbonate (mg/L)
Total Alkalinity
(mg/L)Sodium (mg/L)
10/26/2000 53 40 39 25 530 <1 240 200 10011/30/2000 170 170 48 34 810 <1 250 200 18012/28/2000 210 240 56 42 980 <1 280 230 2301/25/2001 220 270 58 42 1000 <1 280 230 2402/22/2001 250 310 66 50 1200 <1 330 270 2903/29/2001 350 480 81 72 1700 <1 400 330 4304/26/2001 670 90 87 160 8 318 326 5305/31/2001 190 260 54 43 1000 <1 180 180 2206/7/2001 210 440 65 46 1100 <1 200 170 2406/14/2001 470 660 86 90 2200 <1 350 280 5206/21/2001 360 580 70 70 1700 <1 370 260 4106/28/2001 360 550 71 72 1700 10 280 250 4208/30/2001 190 180 45 36 880 <1 250 200 1909/27/2001 NA 88 36 28 610 <1 NA NA 140
10/25/2001 230 130 48 37 860 <1 280 NA 20011/29/2001 230 200 50 38 930 <1 270 230 22012/27/2001 270 270 55 45 1100 <1.0 300 250 2602/28/2002 NA 360 71 56 1300 <1.0 345 283 3403/28/2002 490 910 160 84 2700 <1.0 370 300 6304/25/2002 190 330 55 41 870 <1.0 200 160 2005/30/2002 330 500 76 65 1700 <1.0 310 260 4106/20/2002 150 180 43 31 NA <1.0 180 150 1609/26/2002 150 79 39 26 430 <1.0 190 160 130
10/31/2002 190 97 45 31 700 <1.0 250 200 16011/21/2002 220 170 53 40 930 <1.0 280 230 2103/27/2003 250 320 65 504/24/2003 260 370 63 515/29/2003 200 300 64 436/26/2003 150 240 48 33
36
37
E2: 541MER536 – Mud Slough Upstream of SLD Terminus continued…
DateChloride (mg/L)
Sulfate (mg/L)
Calcium (mg/L)
Magnesium (mg/L)
TDS (mg/L)
Carbonate (mg/L)
Bicarbonate (mg/L)
Total Alkalinity
(mg/L)Sodium (mg/L)
Count 26 29 29 29 24 25 24 23 25Min 53 40 36 25 160 0.5 180 150 100Max 490 910 160 90 2700 10 400 330 630Mean 240 320 62 49 1100 1.2 280 230 280Geo Mean 220 260 59 46 980 0.6 270 230 250Median 220 270 56 43 990 0.5 280 230 230Quartile 1 190 180 48 36 850 0.5 250 200 190Quartile 3 270 440 70 56 1400 0.5 320 265 410NOTE: For values reported as < (less than), half the detection limit was used.
NA = Data not applicableINA = Site was inaccessibleDRY = Site had no flow
E2: 541MER536 – Mud Slough Upstream of SLD Terminus continued…
Date Result Control Result Control
Result (million/m
l)
Control (million/
ml) MDD(%)6/18/2001 100 100 100 90
Count 1 1 1 1 N/A N/A N/A
* Significantly reduced from the lab control.** Significantly greater than the lab control.^ Fish were from a "forced hatch," duplicate failed QA.1 Duplicate sample for the set was low - 77% recovery.
3 Samples qualified, but duplicate sample recovery for the set was high - 126% (53.8%/42.5%)NA = Data not applicableINA = Site was inaccessibleDRY = Site had no flow
96h Acute Fathead Minnow
(% Survival)
48h Acute Ceriodaphnia Dubia
(% Survival) Algae Cell Growth
2 Testing for the Fathead minnow was initiated when samples were approx. 48h old due to untimely shipping of fish by fish supplier.
38
E3: 541MER535 – San Luis Drain @ Terminus Station Code:541MER535
Location: Latitude 37.25944, Longitude -120.90389
Date TimeTemp (ºC)
Field SC (umhos) pH
Dissolved Oxygen (mg/L)
Turbidity (ntu)
10/5/2000 10:30 AM 21.1 4600 7.110/12/2000 11:30 AM 17.5 3340 8.010/19/2000 9:05 AM 18.2 3390 7.810/26/2000 3:00 PM 14.6 4320 6.811/2/2000 10:10 AM 15.6 3990 6.911/9/2000 10:00 AM 13.1 4520 8.2
11/16/2000 10:40 AM 10.9 4530 6.711/21/2000 8:10 AM 9.5 4450 7.711/30/2000 11:30 AM 11.9 4240 7.512/7/2000 9:35 AM 9.7 3840 7.4
12/12/2000 9:35 AM 12.1 4280 7.212/21/2000 11:40 AM 11.2 3890 7.912/28/2000 11:16 AM 9.7 4330 7.81/4/2001 9:40 AM 7.8 4510 7.11/11/2001 11:30 AM 8.9 4080 5.51/18/2001 9:45 AM 7.7 4420 5.91/25/2001 11:12 AM 9.9 4390 7.82/1/2001 10:53 AM 8.4 4380 7.32/8/2001 10:50 AM 12.2 4170 8.12/15/2001 11:30 AM 10.8 4360 8.12/22/2001 12:33 PM 12.9 4710 7.83/1/2001 9:25 AM 12.1 4710 7.43/8/2001 10:20 AM 16.1 4520 7.13/15/2001 11:45 AM 17.2 5430 8.33/22/2001 12:18 PM 20.4 5730 8.53/29/2001 10:21 AM 20.3 5250 8.34/5/2001 12:30 PM 17.0 5680 8.14/12/2001 10:03 AM 14.0 4890 7.44/19/2001 12:10 PM 17.5 5710 8.34/26/2001 9:00 AM 21.3 5230 8.35/3/2001 10:45 AM 18.1 5190 7.75/10/2001 9:25 AM 24.3 4460 8.15/17/2001 12:14 PM 25.1 4280 7.85/24/2001 10:03 AM 26.5 4130 7.85/31/2001 10:40 AM 26.1 4470 7.66/6/2001 11:25 AM 22.8 4550 7.6 3.26/7/2001 12:15 PM 27.8 4810 8.5 11.1
39
E3: 541MER535 – San Luis Drain @ Terminus continued…
Date TimeTemp (ºC)
Field SC (umhos) pH
Dissolved Oxygen (mg/L)
Turbidity (ntu)
6/13/2001 9:05 AM 21.1 4540 8.6 10.16/14/2001 10:32 AM 21.1 4440 8.4 11.96/20/2001 10:32 AM 27.2 4520 8.3 11.86/21/2001 12:42 PM 28.0 4680 8.4 13.56/28/2001 12:43 PM 24.1 4280 8.4 11.97/5/2001 9:17 AM 26.4 4200 8.2 9.27/11/2001 11:32 AM 25.4 3770 8.3 15.17/19/2001 1:04 PM 24.7 4420 8.4 13.07/26/2001 8:45 AM 24.9 4440 8.2 11.58/2/2001 10:31 AM 24.8 3830 8.3 13.38/9/2001 9:22 AM 26.7 3550 8.3 12.28/16/2001 10:57 AM 24.8 3770 8.4 12.78/23/2001 9:19 AM 22.7 3650 8.4 11.98/30/2001 9:29 AM 24.0 4260 8.4 12.59/6/2001 8:57 AM 24.2 3810 8.0 9.79/13/2001 9:27 AM 22.5 4260 8.6 12.59/20/2001 10:16 AM 23.7 4570 8.4 10.99/27/2001 11:24 AM 23.2 5100 8.2 8.810/4/2001 8:51 AM 22.9 4090 8.1 10.3
10/11/2001 9:43 AM 18.9 4340 8.6 12.810/18/2001 9:40 AM 19.4 3940 8.2 16.110/25/2001 9:39 AM 16.4 4250 8.3 13.411/1/2001 10:50 AM 17.6 4000 8.2 13.311/8/2001 9:35 AM 15.7 4090 8.8 14.1
11/15/2001 9:25 AM 16.0 3610 7.9 10.411/20/2001 11:41 AM 14.9 3510 7.5 8.911/29/2001 8:30 AM 9.3 4350 NA NA12/6/2001 9:15 AM 10.2 4320 7.8 12.4
12/13/2001 9:34 AM 9.3 4710 8.1 12.912/20/2001 10:53 AM 9.1 4590 8.1 12.512/27/2001 1:15 PM 10.1 4170 7.9 13.81/3/2002 10:16 AM 12.9 4210 7.9 12.11/10/2002 9:45 AM 12.0 4260 7.7 11.81/17/2002 8:44 AM 8.3 4550 8.0 13.01/24/2002 1:05 PM 8.2 4970 8.1 13.51/31/2002 11:26 AM 7.7 4680 8.1 14.12/7/2002 9:02 AM 10.3 4290 8.1 13.32/14/2002 9:30 AM 12.0 4580 8.3 11.9
40
E3: 541MER535 – San Luis Drain @ Terminus continued…
Date TimeTemp (ºC)
Field SC (umhos) pH
Dissolved Oxygen (mg/L)
Turbidity (ntu)
2/21/2002 10:52 AM 14.4 4950 7.8 10.62/28/2002 8:40 AM 15.6 5090 8.3 12.83/7/2002 8:58 AM 14.9 4500 8.4 13.43/14/2002 9:51 AM 13.6 4770 8.6 12.93/21/2002 10:01 AM 14.2 4140 7.8 12.13/28/2002 11:12 AM 17.6 5350 8.5 14.84/4/2002 9:03 AM 19.7 5530 8.7 13.84/11/2002 10:50 AM 19.6 5540 8.8 12.64/18/2002 7:28 AM 16.4 5210 8.7 12.64/25/2002 11:21 AM 20.6 5250 8.5 13.15/2/2002 8:28 AM 17.1 4960 8.4 15.75/9/2002 9:52 AM 19.6 4920 8.5 14.55/16/2002 9:41 AM 21.5 5100 8.5 11.1 15.65/23/2002 7:20 AM 18.0 3860 8.4 NA5/30/2002 2:19 PM 27.2 4060 8.2 12.56/6/2002 8:22 AM 24.9 4500 8.3 NA6/13/2002 11:25 AM 24.1 4430 8.2 NA6/20/2002 8:30 AM 25.1 4010 8.5 NA6/27/2002 9:55 AM 24.7 4340 8.4 15.97/3/2002 10:15 AM 26.7 4310 8.1 NA7/11/2002 12:19 PM 27.3 4370 8.7 NA7/18/2002 9:26 AM 24.9 4260 8.6 15.3 16.57/25/2002 8:42 AM 24.3 3730 8.4 13.78/1/2002 9:32 AM 25.1 3610 8.6 13.18/8/2002 10:17 AM 23.2 3960 8.4 8.48/15/2002 8:47 AM 25.3 3600 8.3 10.58/22/2002 9:08 AM 22.3 3660 8.3 11.58/29/2002 8:45 AM 22.4 3420 7.3 NA9/5/2002 8:48 AM 23.6 3570 8.3 11.59/12/2002 8:37 AM 23.0 3620 8.1 11.89/19/2002 9:08 AM 22.4 4940 8.5 9.8 NA9/26/2002 11:42 AM 23.4 4460 7.8 10.310/3/2002 9:30 AM 15.5 4970 8.4 10.6
10/10/2002 11:47 AM 21.2 5010 8.4 10.810/17/2002 8:54 AM 17.7 3860 8.3 12.0 29.210/24/2002 10:11 AM 16.5 3990 8.1 14.110/31/2002 9:50 AM 15.0 4820 8.1 14.3 23.1
41
E3: 541MER535 – San Luis Drain @ Terminus continued…
Date TimeTemp (ºC)
Field SC (umhos) pH
Dissolved Oxygen (mg/L)
Turbidity (ntu)
11/7/2002 9:36 AM 14.1 4720 8.3 12.211/14/2002 9:57 AM 14.9 4510 8.0 10.811/21/2002 11:27 AM 13.8 4390 8.3 17.3 31.211/26/2002 11:48 AM 13.3 4240 8.3 17.512/5/2002 9:35 AM 11.2 4880 8.1 13.6 40.1
12/12/2002 9:15 AM 11.5 4830 7.7 13.712/19/2002 8:40 AM 9.8 4540 7.8 11.9 35.512/24/2002 10:17 AM 8.6 4240 7.1 18.71/2/2003 11:40 AM 10.4 4510 7.3 15.01/9/2003 10:26 AM 10.2 4830 7.8 12.41/16/2003 11:08 AM 11.5 4850 7.8 11.5 37.81/23/2003 8:45 AM 11.0 4510 7.3 11.91/30/2003 10:19 AM 12.9 4520 7.9 11.8 44.82/6/2003 10:12 AM 10.4 4610 7.9 13.02/13/2003 11:39 AM 11.8 4510 8.0 11.7 45.62/20/2003 11:17 AM 12.4 4280 8.1 14.3 62.52/27/2003 8:57 AM 13.4 4920 8.0 11.23/6/2003 10:50 AM 15.0 5080 7.7 14.7 NA3/13/2003 10:01 AM 18.1 5520 8.3 13.1 26.53/20/2003 8:44 AM 14.9 5580 8.1 12.3 20.93/27/2003 9:23 AM 16.6 5590 8.4 13.8 22.24/3/2003 12:47 PM 16.6 5430 8.3 17.6 28.44/10/2003 9:01 AM 18.7 5190 8.2 14.1 45.04/17/2003 9:04 AM 16.4 5250 8.1 13.3 44.44/24/2003 9:54 AM 17.1 5130 8.3 12.0 48.25/1/2003 9:21 AM 18.5 5110 8.1 12.4 NA5/8/2003 8:40 AM 17.5 4300 8.3 10.9 65.05/15/2003 8:57 AM 19.8 5190 8.7 15.55/22/2003 9:50 AM 22.8 4810 8.2 15.7 46.85/29/2003 9:35 AM 25.3 4740 8.2 12.86/5/2003 9:22 AM 25.1 4660 8.3 11.2 22.96/12/2003 10:00 AM 21.5 4330 8.3 12.9 35.76/19/2003 9:15 AM 22.7 4510 8.5 6.9 38.26/26/2003 9:25 AM 24.2 4400 8.6 15.2 26.47/3/2003 9:24 AM 24.9 4630 8.5 30.07/10/2003 9:21 AM 24.9 4500 8.5 18.27/17/2003 9:24 AM 26.6 4260 8.9 12.67/24/2003 9:06 AM 27.8 4020 8.4 10.2 22.87/31/2003 9:28 AM 26.7 3610 8.2 11.1 26.3
42
E3: 541MER535 – San Luis Drain @ Terminus continued…
Date TimeTemp (ºC)
Field SC (umhos) pH
Dissolved Oxygen (mg/L)
Turbidity (ntu)
8/7/2003 9:00 AM 24.5 3700 8.4 11.9 25.88/14/2003 8:49 AM 24.4 3950 8.5 12.38/21/2003 9:01 AM 25.6 4400 8.9 9.4 18.48/28/2003 9:10 AM 25.0 3570 8.4 NA 24.09/4/2003 9:04 AM 25.8 3610 8.3 9.0 20.69/11/2003 10:00 AM 22.7 4020 8.4 10.8 12.79/18/2003 9:19 AM 21.2 4480 8.5 8.3 26.39/25/2003 10:01 AM 22.7 4690 8.7 10.8 28.610/2/2003 9:40 AM 21.8 3990 8.4 14.4 17.310/9/2003 9:22 AM 21.3 4140 8.3 19.9 19.4
10/16/2003 11:22 AM 18.5 4640 8.5 17.3 14.610/23/2003 9:41 AM 20.1 4140 8.3 10.6 15.110/30/2003 8:35 AM 16.7 4410 8.1 9.7 21.911/6/2003 9:07 AM 14.1 4460 8.4 14.5 22.2
11/13/2003 8:36 AM 13.7 4380 8.3 10.0 44.511/20/2003 8:50 AM 13.8 3900 8.2 12.0 NA11/26/2003 8:36 AM 8.9 3970 8.3 13.5 23.412/4/2003 9:02 AM 11.9 4350 7.7 12.2
12/11/2003 8:45 AM 11.1 4030 8.0 14.0 NA12/18/2003 9:17 AM 9.5 4430 8.1 14.3 NA12/23/2003 8:58 AM 10.9 4460 7.9 12.7 NA12/30/2003 9:36 AM 8.5 4020 7.8 13.8 NA1/8/2004 8:21 AM 9.0 4450 7.9 11.0 NA1/15/2004 9:11 AM 10.1 4560 8.0 12.1 NA1/22/2004 9:02 AM 9.5 4410 8.0 20.3 23.41/29/2004 9:04 AM 10.2 4550 7.9 13.4 NA2/5/2004 9:01 AM 10.2 4550 8.1 12.3 25.62/12/2004 8:58 AM 11.1 4290 8.2 14.1 NA2/19/2004 8:58 AM 13.0 3660 7.9 12.0 NA2/26/2004 9:14 AM 12.5 4580 8.0 11.5 NA3/4/2004 9:05 AM 12.7 4810 8.2 11.8 41.23/11/2004 9:27 AM 18.2 5150 8.3 11.7 NA3/18/2004 8:22 AM 20.2 5190 8.0 13.23/25/2004 9:14 AM 18.8 5480 8.5 13.7 21.74/1/2004 9:02 AM 16.8 4660 8.5 12.64/8/2004 8:58 AM 17.9 5470 8.4 11.6 43.04/15/2004 9:17 AM 19.0 5150 8.3 11.5 33.94/22/2004 9:25 AM 17.0 5350 8.5 12.2 70.6
43
E3: 541MER535 – San Luis Drain @ Terminus continued…
Date TimeTemp (ºC)
Field SC (umhos) pH
Dissolved Oxygen (mg/L)
Turbidity (ntu)
4/29/2004 10:30 AM 19.3 4640 8.6 NA 23.65/6/2004 9:20 AM 23.1 4740 8.2 26.2 30.85/13/2004 9:50 AM 19.5 4160 8.4 25.7 38.95/20/2004 9:20 AM 20.9 4560 8.2 12.0 36.85/27/2004 8:57 AM 21.6 3870 8.2 NA NA6/3/2004 10:00 AM 24.4 4680 8.3 13.9 61.96/10/2004 9:42 AM 20.8 4340 8.6 14.0 52.46/17/2004 9:50 AM 24.0 3620 8.5 13.9 25.66/24/2004 9:30 AM 23.4 4080 8.3 12.9 NA7/1/2004 9:27 AM 22.8 3750 8.0 13.5 NA7/8/2004 9:17 AM 24.9 4380 7.8 12.7 NA7/15/2004 9:25 AM 25.2 4160 7.9 11.2 NA7/22/2004 11:24 AM 27.4 3980 8.3 16.9 NA7/29/2004 9:15 AM 23.4 3490 8.4 12.1 NA8/5/2004 8:46 AM 24.1 3900 8.3 10.6 NA8/12/2004 9:11 AM 26.4 3510 8.4 10.2 NA8/19/2004 11:08 AM 26.4 3250 8.2 13.5 NA8/26/2004 9:48 AM 23.9 3800 8.5 11.8 NA9/2/2004 8:55 AM 25.0 4570 8.1 10.5 NA9/9/2004 10:17 AM 24.7 3870 7.8 11.8 NA9/16/2004 10:48 AM 21.7 4690 8.2 12.1 NA9/23/2004 11:22 AM 20.0 3580 8.4 14.2 NA9/30/2004 9:00 AM 19.7 3760 8.1 10.1 NA10/7/2004 8:37 AM 20.6 3480 7.7 18.5
10/14/2004 8:48 AM 18.8 3630 7.5 13.110/21/2004 10:25 AM 15.9 3510 NA 11.610/28/2004 8:54 AM 13.8 3700 7.7 15.111/4/2004 9:35 AM 13.2 4100 8.4 14.8
11/11/2004 8:41 AM 14.3 4310 7.3 10.411/18/2004 9:01 AM 14.0 4410 7.6 10.111/23/2004 11:36 AM 9.9 4510 7.7 11.812/2/2004 9:12 AM 7.6 4390 8.0 13.512/9/2004 8:47 AM 10.3 4400 8.0 11.7
12/16/2004 8:41 AM 11.7 4170 7.4 11.312/22/2004 11:46 AM 9.1 4610 8.0 14.312/29/2004 10:21 AM 9.2 4070 7.6 12.01/6/2005 8:14 AM 10.1 4150 7.3 12.51/13/2005 10:01 AM 10.1 3390 7.6 6.2
44
E3: 541MER535 – San Luis Drain @ Terminus continued…
Date TimeTemp (ºC)
Field SC (umhos) pH
Dissolved Oxygen (mg/L)
Turbidity (ntu)
1/20/2005 9:07 AM 9.3 4860 7.5 11.71/27/2005 9:09 AM 10.9 4690 7.9 12.22/3/2005 9:03 AM 11.7 4710 8.1 11.72/10/2005 8:38 AM 13.2 4950 7.9 12.32/17/2005 9:25 AM 14.6 4570 7.4 10.82/24/2005 9:03 AM 15.3 4620 7.8 11.33/3/2005 8:44 AM 15.9 5230 7.8 12.23/10/2005 9:42 AM 18.9 5540 8.0 16.83/17/2005 8:41 AM 16.9 5960 7.8 17.83/24/2005 8:48 AM 14.8 5060 7.8 14.03/31/2005 8:49 AM 14.5 5570 7.9 14.64/7/2005 9:03 AM 18.1 5720 8.4 12.94/14/2005 8:49 AM 15.2 5770 8.3 12.94/21/2005 8:54 AM 18.2 5610 8.3 13.04/28/2005 8:46 AM 18.6 4730 7.7 15.35/5/2005 9:17 AM 20.8 4620 7.5 11.85/12/2005 8:41 AM 20.1 5350 7.9 12.05/19/2005 9:16 AM 21.7 5410 8.0 12.65/26/2005 9:41 AM 25.1 4080 8.2 11.56/2/2005 9:08 AM 21.4 4670 8.4 10.56/9/2005 8:26 AM 20.5 3970 7.9 13.96/16/2005 8:34 AM 24.1 4310 8.1 13.76/23/2005 9:34 AM 23.9 4430 NA 14.16/30/2005 9:18 AM 25.7 3930 8.5 14.97/7/2005 8:56 AM 25.5 4980 8.5 15.57/13/2005 10:40 AM 28.7 4530 8.7 16.57/21/2005 8:50 AM 27.7 4210 8.1 10.67/28/2005 9:16 AM 27.3 4130 8.5 10.98/4/2005 8:58 AM 27.0 3940 8.2 10.88/11/2005 9:20 AM 26.7 4670 8.4 11.88/18/2005 9:27 AM 24.4 3790 8.0 12.88/25/2005 9:08 AM 25.0 3490 8.4 12.19/1/2005 8:56 AM 24.0 4600 7.6 14.79/8/2005 9:12 AM 23.1 4910 8.4 11.89/15/2005 8:54 AM 20.5 3850 7.6 13.49/22/2005 9:39 AM 22.6 4130 8.3 13.99/29/2005 8:53 AM 21.2 4250 7.9 13.1
45
E3: 541MER535 – San Luis Drain @ Terminus continued…
Date TimeTemp (ºC)
Field SC (umhos) pH
Dissolved Oxygen (mg/L)
Turbidity (ntu)
Count 264 264 261 218 55Min 7.6 3250 5.5 3.2 12.7Max 28.7 5960 8.9 30.0 70.6Mean 18.2 4450 8.1 12.9 32.1Geo Mean 17.2 4410 8.1 12.6 29.5Median 18.5 4430 8.2 12.5 26.5Quartile 1 13.1 4080 7.9 11.5 22.5Quartile 3 23.6 4720 8.4 13.9 40.7NOTE: For values reported as < (less than), half the detection limit was used.
NA = Data not applicableINA = Site was inaccessibleDRY = Site had no flow
46
E3: 541MER535 – San Luis Drain @ Terminus continued…
DateTSS
(mg/L)TOC
(mg/L)Total Coli
MPNE. coli MPN
10/5/2000 5510/12/2000 4910/19/2000 4910/26/2000 NA11/2/2000 5011/9/2000 52
11/16/2000 4811/21/2000 3211/30/2000 36 1.812/7/2000 51
12/12/2000 5512/21/2000 3812/28/2000 38 4.11/4/2001 221/11/2001 531/18/2001 321/25/2001 522/1/2001 432/8/2001 262/15/2001 322/22/2001 31 1.93/1/2001 373/8/2001 353/15/2001 333/22/2001 543/29/2001 47 <14/5/2001 334/12/2001 384/19/2001 565/3/2001 385/10/2001 495/17/2001 555/24/2001 425/31/2001 44 9.96/7/2001 40 106/14/2001 51 146/21/2001 NA 136/28/2001 35 137/5/2001 347/11/2001 417/19/2001 447/26/2001 44 9.4
47
E3: 541MER535 – San Luis Drain @ Terminus continued…
DateTSS
(mg/L)TOC
(mg/L)Total Coli
MPNE. coli MPN
8/2/2001 508/9/2001 418/16/2001 398/23/2001 328/30/2001 58 139/6/2001 339/13/2001 309/20/2001 NA9/27/2001 14 1610/4/2001 NA
10/11/2001 4210/18/2001 3610/25/2001 39 1511/1/2001 4111/8/2001 35
11/15/2001 3811/20/2001 3311/29/2001 39 NA12/6/2001 37
12/13/2001 5012/20/2001 4312/27/2001 361/3/2002 501/10/2002 521/17/2002 381/24/2002 261/31/2002 22 NA2/7/2002 452/14/2002 352/21/2002 232/28/2002 39 6.43/7/2002 NA3/14/2002 423/21/2002 NA3/28/2002 41 5.54/4/2002 39 NA4/11/2002 224/18/2002 264/25/2002 34 NA5/2/2002 705/9/2002 NA5/16/2002 NA
48
E3: 541MER535 – San Luis Drain @ Terminus continued…
DateTSS
(mg/L)TOC
(mg/L)Total Coli
MPNE. coli MPN
5/23/2002 725/30/2002 6.36/6/2002 NA6/13/2002 386/20/2002 54 5.96/27/2002 747/3/2002 537/11/2002 NA7/18/2002 497/25/2002 NA8/1/2002 59 >2419.6 68/8/2002 448/15/2002 428/22/2002 NA8/29/2002 NA9/5/2002 509/12/2002 NA9/19/2002 599/26/200210/3/2002 40
10/10/2002 5910/17/2002 47 >2419.6 <110/24/2002 NA10/31/2002 NA 5.611/7/2002 42
11/14/2002 3511/21/2002 58 5.511/26/2002 4312/5/2002 42
12/12/2002 3712/19/2002 4212/24/2002 331/2/2003 351/9/2003 361/16/2003 40 308 61/23/2003 401/30/2003 402/6/2003 442/13/2003 462/20/2003 542/27/2003 543/6/2003 39
49
E3: 541MER535 – San Luis Drain @ Terminus continued…
DateTSS
(mg/L)TOC
(mg/L)Total Coli
MPNE. coli MPN
3/13/2003 NA3/20/2003 NA3/27/2003 54 4.74/3/2003 414/10/2003 NA4/17/2003 534/24/2003 60 9.5 921 1055/1/2003 535/8/2003 645/15/2003 465/22/2003 375/29/2003 40 106/5/2003 376/12/2003 546/19/2003 576/26/2003 85 7.97/3/2003 537/10/2003 487/17/2003 547/24/2003 447/31/2003 47 >2419.6 <18/7/2003 518/14/2003 638/21/2003 398/28/2003 NA >2419.6 <19/4/2003 279/11/2003 329/18/2003 339/25/2003 39 >2419.6 <110/2/2003 3410/9/2003 33
10/16/2003 3310/23/2003 2810/30/2003 22 >2419.6 111/6/2003 32
11/13/2003 3111/20/2003 30 >2419.6 3611/26/2003 2812/4/2003 38
12/11/2003 NA12/18/2003 26
50
E3: 541MER535 – San Luis Drain @ Terminus continued…
DateTSS
(mg/L)TOC
(mg/L)Total Coli
MPNE. coli MPN
12/23/2003 2412/30/2003 211/8/2004 271/15/2004 241/22/2004 241/29/2004 NA 1733 72/5/2004 242/12/2004 262/19/2004 362/26/2004 45 >2419.6 143/4/2004 453/11/2004 493/18/2004 503/25/2004 40 1414 104/1/2004 624/8/2004 514/15/2004 444/22/2004 964/29/2004 35 >2419.6 445/6/2004 495/13/2004 485/20/2004 665/27/2004 56 >2419.6 46/3/2004 676/10/2004 646/17/2004 516/24/2004 48 >2419.6 97/1/2004 437/8/2004 547/15/2004 427/22/2004 537/29/2004 56 >2419.6 18/5/2004 378/12/2004 468/19/2004 538/26/2004 60 >2419.6 19/2/2004 469/9/2004 399/16/2004 46
51
E3: 541MER535 – San Luis Drain @ Terminus continued…
DateTSS
(mg/L)TOC
(mg/L)Total Coli
MPNE. coli MPN
9/23/2004 459/30/2004 46 >2419.6 <110/7/2004 54
10/14/2004 5010/21/2004 4610/28/2004 43 >2419.6 77011/4/2004 48
11/11/2004 3511/18/2004 5211/23/2004 24 6.5 >2419.6 1212/2/2004 2712/9/2004 40
12/16/2004 NA12/22/2004 3512/29/2004 38 5.9 387 51/6/2005 631/13/2005 901/20/2005 NA1/27/2005 57 6.4 >2419.6 92/3/2005 662/10/2005 622/17/2005 832/24/2005 50 13 1300 83/3/2005 643/10/2005 483/17/2005 463/24/2005 393/31/2005 38 7.5 272 164/7/2005 704/14/2005 414/21/2005 404/28/2005 54 NA 1733 775/5/2005 625/12/2005 585/19/2005 545/26/2005 34 8.8 >2419.6 236/2/2005 766/9/2005 666/16/2005 446/23/2005 646/30/2005 58 9.3 >2419.6 <17/7/2005 61
52
53
DateTSS
(mg/L)TOC
(mg/L)Total Coli
MPNE. coli MPN
7/13/2005 497/21/2005 447/28/2005 39 12 >2419.6 <18/4/2005 428/11/2005 468/18/2005 428/25/2005 33 10 >2419.6 <19/1/2005 349/8/2005 439/15/2005 479/22/2005 399/29/2005 40 11 >2419.6 <1
Count 234 33 30 21Min 14 0.5 27
E3: 541MER535 – San Luis Drain @ Terminus continued…
2 1Max 96 16 2420 770MeaGeo
n 45 8.5 NA NA Mean 43 7 1800 12
MedQua
ian 43 8.8 2420 9rtile 1 36 5.9 1905 6
Quartile 3 52 11 2420 23E: For values reported as < (less than), half the detection limit was used For values reported as > (greater than), 2420 was used
Data not applicable Site was inaccessible
= Site had no flow
NOT
NA =INA =DRY
E3: 541MER535 – San Luis Drain @ Terminus continued…
DateNitrate (mg/L)
Nitrate-N (mg/L)
TKN (mg/L)
Ammonia-N (mg/L)
Phosphorus (mg/L)
Ortho-phosphate-
P (mg/L)
Potassium (mg/L)
BOD 5-Day (mg/L)
BOD 10-Day (mg/L)
10/26/2000 44 <2 <0.1 <1 1311/30/2000 79 <2 <0.1 <1 12 1.3 2.312/28/2000 87 <2 <0.1 <1 8.6 0.9 1.61/25/2001 95 <2 <0.1 <1 82/22/2001 110 <2 <0.1 <1 8.5 1.7 3.13/29/2001 91 <2 <0.1 <1 8.6 5.1 9.64/26/2001 97 <2 <1 <0.02 <1 8.35/31/2001 81 <1.0 0.4 NA 8.9 2.2 4.16/7/2001 88 <1.0 0.1 <1 8 3.3 4.96/14/2001 91 <2 <1 8.2 3.3 5.76/21/2001 73 <2 <0.1 <1 8.2 5.8 10.96/28/2001 58 <2 <0.1 <1 8 3.6 5.78/16/2001 11 <2 0.4 <1 5.48/30/2001 56 <2 <0.1 <1 8.49/27/2001 45 <2 <0.1 <1 11
10/25/2001 4.2 8.311/29/2001 NA NA NA <0.03 11 1.3 2.512/27/2001 1.3 2.41/31/2002 1.5 2.32/28/2002 2.6 4.24/25/2002 5.8 9.85/30/2002 3.2 56/20/2002 5.6 10.18/29/2002 4.5 8
10/31/2002 5.6 8.611/21/2002 4.4 8.412/19/2002 1.6 2.2
54
E3: 541MER535 – San Luis Drain @ Terminus continued…
DateNitrate (mg/L)
Nitrate-N (mg/L)
TKN (mg/L)
Ammonia-N (mg/L)
Phosphorus (mg/L)
Ortho-phosphate-
P (mg/L)
Potassium (mg/L)
BOD 5-Day (mg/L)
BOD 10-Day (mg/L)
1/30/2003 1.9 2.98/28/2003 22 2.2 <0.1 <1.0 119/25/2003 27 2.1 0.1 <1.0 10
10/30/2003 46 1.5 <0.1 <1.0 9.711/20/2003 58 <1.0 <0.1 <1.0 9.11/29/2004 29 0.7 0.1 0.1 NA2/26/2004 22 0.8 NA 0.1 NA3/11/2004 19 1.2 0.1 0.1 <0.013/25/2004 22 1.2 0 0.1 <0.014/15/2004 19 1.2 0.1 0.1 NA4/29/2004 18 1.6 0.1 0.1 NA5/13/2004 14 1.7 0.1 0.1 <0.016/10/2004 16 1.7 0.1 0.1 <0.016/24/2004 11 2 0.1 0.1 <0.017/15/2004 14 1.6 0.1 <0.02 <0.017/29/2004 7.1 2.1 NA 0.1 <0.038/12/2004 6.3 1.8 0.1 0.1 <0.038/26/2004 6.9 2 NA 0.1 NA9/16/2004 8.4 1.9 0.1 0.1 <0.039/30/2004 5.3 1.8 0.2 NA <0.03
10/28/2004 8.9 1.4 NA 0.1 0.111/23/2004 8.3 1.2 NA 0.1 NA12/29/2004 9.7 0.8 0.1 0.1 NA1/27/2005 24 0.8 0.1 0.2 NA2/24/2005 29 2.3 1 0.3 0.13/31/2005 33 1 0.1 0.1 NA4/28/2005 16 2.1 0.1 NA NA5/12/2005 23 NA NA 0.1 <0.035/26/2005 15 1.6 0.1 0.1 <0.036/16/2005 NA 1.3 NA NA NA6/30/2005 12 2 0.1 0.1 NA7/13/2005 12 2 NA NA <0.039/29/2005 7.3 2.5 NA NA <0.03
55
E3: 541MER535 – San Luis Drain @ Terminus continued…
DateNitrate (mg/L)
Nitrate-N (mg/L)
TKN (mg/L)
Ammonia-N (mg/L)
Phosphorus (mg/L)
Ortho-phosphate-
P (mg/L)
Potassium (mg/L)
BOD 5-Day (mg/L)
BOD 10-Day (mg/L)
Count 19 27 46 19 41 35 20 22 22Min 11.0 5.3 0.5 0.1 0.01 0.01 5.4 0.9 1.6Max 110.0 33.0 2.5 1.0 0.4 0.5 13.0 5.8 10.9Mean 66.3 15.4 1.4 0.2 0.1 0.3 9.2 3.2 5.6Geo Mean 58.2 13.6 1.3 0.1 0.1 0.1 9.0 2.8 4.7Median 73.0 14.0 1.2 0.1 0.1 0.5 8.6 3.3 5.0Quartile 1 45.5 8.7 1.0 0.1 0.1 0.02 8.2 1.6 2.6Quartile 3 89.5 20.5 1.8 0.1 0.1 0.5 10.3 4.5 8.4NOTE: For values reported as < (less than), half the detection limit was used.
NA = Data not applicableINA = Site was inaccessibleDRY = Site had no flow
56
E3: 541MER535 – San Luis Drain @ Terminus continued…
DateHardness
(mg/L)
Total Arsenic (ug/L)
Total Cadmium
(ug/L)
Total Chromium
(ug/L)
Total Copper (ug/L)
Total Lead (ug/L)
Total Nickel (ug/L)
Total Zinc (ug/L)
Total Mercury (ug/L)
11/30/2000 7.2 2.8 <5 5.812/28/2000 9.8 2.7 <5 6.8 <21/25/2001 1100 14 2.8 <5 5.9 <22/22/2001 1100 11 2.9 <5 5.8 <23/29/2001 1300 7.2 2.5 <5 <5 <24/26/2001 1300 6 3 <5 <5 <25/31/2001 1000 3.2 1.8 <5 5 <26/7/2001 1200 2.3 <1 6.1 2.6 <5 5.5 <2 <0.26/14/2001 1000 <2.0 <1 5.3 2.1 <5 <5 <2 <0.26/21/2001 NA <2.0 <1 2.1 1.3 <5 <5 <2 <0.26/28/2001 1000 2.1 <1 2.7 1.7 <5 <5 <2 <0.27/26/2001 NA NA 4.3 2.1 <5 <5 <2 NA8/30/2001 930 <2 <1 2 1.9 <5 <5 <29/27/2001 1200 7.9 <1 <1 <1 <5 <5 <2 <0.2
10/25/2001 1100 <4 <0.1 <1 1 <5 <5 <2 <0.211/29/2001 1100 <4 <0.1 2.3 1.6 <5 <5 <2 <0.212/27/2001 <4 <0.1 7.8 2.1 <5 5.3 2.4 <0.21/31/2002 <4.0 <0.1 7.6 NA <5.0 <5.0 <2.0 <0.22/28/2002 <4.0 <0.1 12 3.1 <5.0 <5.0 <2.0 <0.23/28/2002 <4.0 <0.1 8.3 1.4 <5.0 <5.0 <2.0 <0.24/25/2002 <4.0 <0.1 <1.0 <1.0 <5.0 <5.0 <2.0 <0.25/30/2002 <4.0 <0.1 2.1 1.9 <5.0 <5.0 2.8 <0.26/20/2002 950 4.2 <0.1 2.9 1.8 <5.0 5.1 <2.0 <0.2
10/31/2002 1100 <4.0 <0.1 2.1 <1.0 <5.0 <5.0 <2.0 <0.211/21/2002 1200 <4.0 <0.1 3.3 1.1 <5.0 <5.0 4.1 <0.23/27/2003 1300 7.8 NA 6.6 1.3 <5.0 <5.0 <2.0 <0.2
57
E3: 541MER535 – San Luis Drain @ Terminus continued…
DateHardness
(mg/L)
Total Arsenic (ug/L)
Total Cadmium
(ug/L)
Total Chromium
(ug/L)
Total Copper (ug/L)
Total Lead (ug/L)
Total Nickel (ug/L)
Total Zinc (ug/L)
Total Mercury (ug/L)
4/24/2003 1300 <4.0 <0.1 NA NA NA 6.2 <2.0 <0.25/22/2003 <4.0 0.1 2.3 <1.0 <5.0 <5.0 <2.0 0.25/29/2003 1100 <4.0 <0.1 1.9 3.2 <5.0 <5.0 <2.0 <0.26/26/2003 970 <4.0 <0.1 4.2 2.2 <5.0 <5.0 <2.0 <0.2
Count 19 22 21 29 28 29 30 29 21Min 930.0 1.0 0.1 0.5 0.5 2.5 2.5 1.0 0.1Max 1300.0 7.9 0.5 14.0 3.2 2.5 6.8 4.1 0.2Mean 1118.4 2.5 0.2 5.0 1.9 2.5 3.5 1.2 0.1Geo Mean 1111.8 2.1 0.1 3.7 1.7 2.5 3.2 1.1 0.1Median 1100.0 2.0 0.1 4.2 1.9 2.5 2.5 1.0 0.1Quartile 1 1000.0 2.0 0.1 2.1 1.3 2.5 2.5 1.0 0.1Quartile 3 1200.0 2.0 0.5 7.2 2.6 2.5 5.1 1.0 0.1NOTE: For values reported as < (less than), half the detection limit was used.
NA = Data not applicableINA = Site was inaccessibleDRY = Site had no flow
58
E3: 541MER535 – San Luis Drain @ Terminus continued…
DateHardness
(mg/L)
Dissolved Arsenic (ug/L)
Dissolved Cadmium
(ug/L)
Dissolved Chromium
(ug/L)
Dissolved Copper (ug/L)
Dissolved Lead (ug/L)
Dissolved Nickel (ug/L)
Dissolved Zinc
(ug/L)
Dissolved Mercury (ug/L)
11/30/2000 4 1.9 <5 <5 <212/28/2000 6.1 <1 <5 <5 <21/25/2001 1100 8.8 <1 <5 <5 <22/22/2001 1100 8.3 1.3 <5 <5 <23/29/2001 1300 6.2 2.1 <5 <5 <24/26/2001 1300 4.9 2 <5 <5 <25/31/2001 1000 1.5 1.1 <5 <5 <26/7/2001 1200 <2 <1 3.5 1.3 <5 <5 <2 <0.26/14/2001 1000 <2.0 <1 3.5 1.2 <5 <5 <2 <0.26/21/2001 NA <2.0 <1 1.2 <1 <5 <5 <2 <0.26/28/2001 1000 2.3 <1 <1 <1 <5 <5 <2 <0.27/26/2001 NA NA NA NA NA NA NA NA8/30/2001 930 <2 <1 <1 1.1 <5 <5 <29/27/2001 1200 7.7 <1 <1 <1 <5 <5 <2 <0.2
10/25/2001 1100 <4 <0.1 <1 <1 <5 <5 <2 <0.211/29/2001 1100 <4 <0.1 1.5 <1 <5 <5 <2 <0.212/27/2001 <4 <0.1 4.2 <1 <5 <5 <2 <0.21/31/2002 <4.0 <0.1 5 NA <5.0 <5.0 <2.0 <0.22/28/2002 <4.0 <0.1 9.7 1.6 <5.0 <5.0 <2.0 <0.23/28/2002 <4.0 <0.1 6.4 <1.0 <5.0 5 <2.0 <0.24/25/2002 5 <0.1 1.7 <1.0 <5.0 <5.0 NA <0.25/30/2002 <4.0 <0.1 <1.0 1.6 <5.0 <5.0 <2.0 <0.26/20/2002 950 <4.0 <0.1 <1.0 <1.0 <5.0 <5.0 <2.0 <0.2
10/31/2002 1100 <4.0 <0.1 1.8 <1.0 <5.0 <5.0 <2.0 <0.211/21/2002 1200 <4.0 <0.1 <1.0 <1.0 <5.0 <5.0 <2.0 <0.2
59
E3: 541MER535 – San Luis Drain @ Terminus continued…
DateHardness
(mg/L)
Dissolved Arsenic (ug/L)
Dissolved Cadmium
(ug/L)
Dissolved Chromium
(ug/L)
Dissolved Copper (ug/L)
Dissolved Lead (ug/L)
Dissolved Nickel (ug/L)
Dissolved Zinc
(ug/L)
Dissolved Mercury (ug/L)
Count 15 17 17 24 23 24 24 23 16Min 930.0 1.0 0.1 0.5 0.5 2.5 2.5 1.0 0.1Max 1300.0 7.7 0.5 9.7 2.1 2.5 5.0 1.0 0.1Mean 1105.3 2.3 0.2 3.4 0.9 2.5 2.6 1.0 0.1Geo Mean 1099.6 2.0 0.1 2.1 0.8 2.5 2.6 1.0 0.1Median 1100.0 2.0 0.1 2.7 0.5 2.5 2.5 1.0 0.1Quartile 1 1000.0 2.0 0.1 0.5 0.5 2.5 2.5 1.0 0.1Quartile 3 1200.0 2.0 0.5 5.3 1.3 2.5 2.5 1.0 0.1NOTE: For values reported as < (less than), half the detection limit was used.
NA = Data not applicableINA = Site was inaccessibleDRY = Site had no flow
60
E3: 541MER535 – San Luis Drain @ Terminus continued…
DateChloride (mg/L)
Sulfate (mg/L)
Calcium (mg/L)
Magnesium (mg/L)
TDS (mg/L)
Carbonate (mg/L)
Bicarbonate (mg/L)
Total Alkalinity
(mg/L)Sodium (mg/L)
10/5/2000 340010/12/2000 250010/19/2000 250010/26/2000 450 1400 270 85 3300 <1 200 170 56011/2/2000 290011/9/2000 3300
11/16/2000 370011/21/2000 330011/30/2000 430 1300 280 83 3200 <1 260 210 62012/7/2000 2800
12/12/2000 320012/21/2000 280012/28/2000 490 1300 320 86 3200 <1 260 210 5801/4/2001 34001/11/2001 30001/18/2001 32001/25/2001 470 1300 310 82 3300 <1 240 200 5902/1/2001 32002/8/2001 30002/15/2001 33002/22/2001 520 1500 300 91 3600 <1 220 180 6903/1/2001 35003/8/2001 34003/15/2001 42003/22/2001 44003/29/2001 570 1600 320 110 3900 10 140 130 8004/5/2001 4300
61
E3: 541MER535 – San Luis Drain @ Terminus continued…
DateChloride (mg/L)
Sulfate (mg/L)
Calcium (mg/L)
Magnesium (mg/L)
TDS (mg/L)
Carbonate (mg/L)
Bicarbonate (mg/L)
Total Alkalinity
(mg/L)Sodium (mg/L)
4/12/2001 36004/19/2001 43004/26/2001 1800 330 110 4000 20 76 96 7305/3/2001 40005/10/2001 36005/17/2001 32005/24/2001 31005/31/2001 490 1400 260 88 3300 <1 130 130 6706/7/2001 560 1500 300 100 3500 <1 190 160 7306/14/2001 520 1300 270 89 3300 7 160 140 6606/21/2001 540 1600 260 95 3500 <1 150 120 6806/28/2001 510 1300 260 94 3000 <1 180 160 7008/16/2001 27008/23/2001 26008/30/2001 480 1400 230 87 3100 <1 130 110 6009/6/2001 28009/13/2001 32009/20/2001 34009/27/2001 NA 1700 310 110 3900 <1 NA NA 74010/4/2001 3000
10/11/2001 330010/18/2001 280010/25/2001 470 1400 290 85 3200 <1 190 NA 60011/1/2001 310011/8/2001 3000
11/15/2001 2700
62
E3: 541MER535 – San Luis Drain @ Terminus continued…
DateChloride (mg/L)
Sulfate (mg/L)
Calcium (mg/L)
Magnesium (mg/L)
TDS (mg/L)
Carbonate (mg/L)
Bicarbonate (mg/L)
Total Alkalinity
(mg/L)Sodium (mg/L)
11/20/2001 260011/29/2001 460 1400 290 84 3300 <1 260 210 60012/6/2001 3300
12/13/2001 330012/20/2001 34001/3/2002 31001/10/2002 32001/17/2002 34001/24/2002 37001/31/2002 38002/7/2002 31002/14/2002 35002/21/2002 37003/7/2002 34003/14/2002 35003/21/2002 31004/4/2002 41004/11/2002 41004/18/2002 39004/25/2002 39005/2/2002 36005/9/2002 NA5/23/2002 28005/30/2002 30006/6/2002 33006/13/2002 3300
63
E3: 541MER535 – San Luis Drain @ Terminus continued…
DateChloride (mg/L)
Sulfate (mg/L)
Calcium (mg/L)
Magnesium (mg/L)
TDS (mg/L)
Carbonate (mg/L)
Bicarbonate (mg/L)
Total Alkalinity
(mg/L)Sodium (mg/L)
6/20/2002 30006/27/2002 32009/19/2002 350010/3/2002 3700
10/10/2002 380010/17/2002 280010/24/2002 300010/31/2002 360011/7/2002 3500
11/14/2002 350011/26/2002 32003/27/2003 690 1900 340 1104/24/2003 640 1700 350 1005/29/2003 550 1500 280 946/26/2003 540 1500 250 86
Count 18 20 20 20 89 16 15 14 16Min 430 1300 230 82 2500 0.5 76 96 560Max 690 1900 350 110 4400 20 260 210 800Mean 520 1490 290 93 3300 2.7 190 160 660Geo Mean 520 1480 290 93 3300 0.9 180 150 660Median 520 1450 290 90 3300 0.5 190 160 670Quartile 1 470 1380 270 86 3100 0.5 150 130 600Quartile 3 550 1600 310 100 3600 0.5 230 200 708NOTE: For values reported as < (less than), half the detection limit was used.
NA = Data not applicableINA = Site was inaccessibleDRY = Site had no flow
64
65
E4: 541MER542 – Mud Slough @ San Luis Drain Station Code:541MER542
Location: Latitude 37.26389, Longitude -120.90611
Date TimeTemp (ºC)
Field SC (umhos) pH
Dissolved Oxygen (mg/L)
Turbidity (ntu)
10/5/2000 10:45 AM 20.9 1610 7.610/12/2000 12:35 PM 19.0 1240 7.910/19/2000 9:20 AM 17.9 1200 8.010/26/2000 3:50 PM 14.6 1270 7.311/2/2000 10:24 AM 14.9 1370 7.511/9/2000 11:30 AM 13.1 1640 7.8
11/16/2000 10:45 AM 10.6 1890 7.311/21/2000 8:40 AM 9.6 1960 8.111/30/2000 12:05 PM 12.2 1920 7.812/7/2000 10:40 AM 9.6 2010 7.9
12/12/2000 10:00 AM 11.8 2020 7.512/21/2000 12:10 PM 10.5 1960 7.912/28/2000 10:47 AM 7.6 2220 6.91/4/2001 10:13 AM 8.2 2370 7.71/11/2001 11:49 AM 8.7 2080 6.61/18/2001 11:20 AM 8.2 2100 7.51/25/2001 11:30 AM 9.6 2240 7.92/1/2001 11:52 AM 8.5 2310 7.82/8/2001 11:20 AM 9.1 2660 8.12/15/2001 12:15 PM 11.8 2660 8.22/22/2001 12:55 PM 12.3 2870 8.03/1/2001 10:05 AM 12.4 2930 7.33/8/2001 10:40 AM 16.5 2370 7.63/15/2001 12:30 PM 17.1 2740 7.93/22/2001 12:40 PM 20.6 3580 8.13/29/2001 11:25 AM 20.0 4140 8.34/5/2001 12:50 PM 17.5 3740 8.44/12/2001 10:50 AM 15.8 3340 8.04/19/2001 12:25 PM 17.8 4460 8.34/26/2001 10:45 AM 23.4 4910 8.25/3/2001 11:00 AM 17.0 3940 8.15/10/2001 9:45 AM 23.2 3080 7.85/17/2001 12:51 PM 24.4 3110 7.15/24/2001 11:25 AM 28.3 3410 6.95/31/2001 11:00 AM 26.0 3390 8.06/6/2001 11:47 AM 22.7 4400 8.2 7.06/7/2001 1:20 PM 27.0 3860 8.4 11.0
66
E4: 541MER542 – Mud Slough @ San Luis Drain continued…
Date TimeTemp (ºC)
Field SC (umhos) pH
Dissolved Oxygen (mg/L)
Turbidity (ntu)
6/13/2001 8:50 AM 21.1 4470 8.4 9.66/14/2001 10:55 AM 21.6 4520 8.3 10.86/20/2001 10:52 AM 26.9 4310 8.3 9.36/21/2001 2:05 PM 29.3 4450 8.3 9.56/28/2001 1:23 PM 24.8 4190 8.4 9.57/5/2001 9:48 AM 26.0 3550 8.0 8.27/11/2001 11:52 AM 25.6 3750 8.3 13.17/19/2001 1:28 PM 25.7 4190 8.3 10.67/26/2001 9:06 AM 24.7 4160 8.2 10.48/2/2001 10:48 AM 25.0 2170 8.4 10.28/9/2001 9:40 AM 26.5 3370 8.4 10.18/16/2001 11:25 AM 25.0 3420 8.4 9.78/23/2001 9:42 AM 22.5 3100 8.3 10.18/30/2001 10:35 AM 24.3 3820 8.3 10.19/6/2001 9:20 AM 22.9 2970 8.0 7.69/13/2001 10:42 AM 22.3 2470 8.0 7.39/20/2001 10:06 AM 22.5 2540 7.7 6.19/27/2001 10:47 AM 21.7 1870 7.5 5.110/4/2001 9:11 AM 22.1 1610 7.4 2.6
10/11/2001 10:24 AM 18.2 1870 7.6 5.110/18/2001 10:14 AM 18.8 1680 7.6 5.510/25/2001 10:47 AM 15.5 1950 7.7 6.811/1/2001 11:10 AM 17.0 1800 7.8 7.011/8/2001 11:06 AM 15.4 1850 8.1 8.8
11/15/2001 9:45 AM 15.5 1540 7.8 6.511/20/2001 1:43 PM 14.9 1720 7.8 7.611/29/2001 9:30 AM 10.9 2040 NA NA12/6/2001 10:18 AM 9.8 1920 7.8 10.3
12/13/2001 9:57 AM 8.9 2740 8.0 10.612/20/2001 11:26 AM 9.4 2520 8.0 11.612/27/2001 1:51 PM 10.3 2270 7.9 12.11/3/2002 10:45 AM 12.8 2080 7.8 8.91/10/2002 10:05 AM 11.7 2260 7.8 9.81/17/2002 9:46 AM 6.9 2650 7.9 11.61/24/2002 12:55 PM 8.2 3030 8.0 11.91/31/2002 11:59 AM 6.9 2870 8.0 13.42/7/2002 9:12 AM 10.5 2690 8.1 11.22/14/2002 10:00 AM 11.6 3040 8.0 9.02/21/2002 11:01 AM 14.6 3210 7.6 9.22/28/2002 10:18 AM 15.6 3260 8.0 8.6
67
E4: 541MER542 – Mud Slough @ San Luis Drain continued…
Date TimeTemp (ºC)
Field SC (umhos) pH
Dissolved Oxygen (mg/L)
Turbidity (ntu)
3/7/2002 9:10 AM 14.8 3220 8.2 9.93/14/2002 10:22 AM 12.3 3750 8.3 10.53/21/2002 10:14 AM 14.8 3440 8.2 9.23/28/2002 12:17 PM 18.5 3890 8.4 10.04/4/2002 9:19 AM 18.7 4720 8.4 8.54/11/2002 10:43 AM 19.0 5140 8.4 11.04/18/2002 7:43 AM 15.7 4130 8.4 10.54/25/2002 10:52 AM 20.5 3650 8.2 9.05/2/2002 8:56 AM 16.6 4770 8.3 12.55/9/2002 10:46 AM 19.6 4260 8.3 10.95/16/2002 10:03 AM 20.9 3550 8.3 8.7 35.75/23/2002 7:56 AM 17.2 3390 8.1 NA5/30/2002 1:38 PM 27.3 3310 8.1 9.16/6/2002 9:05 AM 24.2 3570 8.1 NA6/13/2002 11:35 AM 24.5 4030 8.4 NA6/20/2002 9:04 AM 23.8 1400 8.5 NA6/27/2002 10:25 AM 25.2 4220 8.6 11.07/3/2002 11:15 AM 26.8 4220 8.6 NA7/11/2002 12:44 PM 27.5 3840 8.6 NA7/18/2002 10:23 AM 25.0 3920 8.6 10.0 23.87/25/2002 9:03 AM 24.2 2540 8.3 9.08/1/2002 9:57 AM 25.4 2840 8.5 8.98/8/2002 10:35 AM 22.3 3290 8.6 10.78/15/2002 9:19 AM 25.1 3330 8.3 9.28/22/2002 9:18 AM 22.2 2460 8.2 8.98/29/2002 9:09 AM 22.3 3140 8.3 NA9/5/2002 9:00 AM 22.9 3130 8.3 9.69/12/2002 9:28 AM 22.4 3400 8.1 9.29/19/2002 9:31 AM 21.6 3210 8.2 7.7 NA9/26/2002 12:05 PM 23.6 2180 7.7 7.810/3/2002 9:51 AM 14.4 2510 8.0 11.3
10/10/2002 1:02 PM 22.0 3040 8.2 7.710/17/2002 9:15 AM 16.7 1430 8.1 7.9 48.810/24/2002 10:49 AM 16.0 1420 7.7 7.310/31/2002 10:10 AM 14.3 1740 7.8 5.9 14.811/7/2002 10:05 AM 14.0 1900 7.7 7.6
11/14/2002 10:10 AM 14.3 1680 7.8 8.311/21/2002 12:27 PM 13.2 1900 7.8 8.7 21.311/26/2002 12:02 PM 12.3 2200 8.0 10.412/5/2002 10:07 AM 10.9 2530 7.9 10.4 17.3
12/12/2002 9:26 AM 11.3 2220 7.7 9.612/19/2002 9:17 AM 8.9 1940 7.8 10.0 24.8
68
E4: 541MER542 – Mud Slough @ San Luis Drain continued…
Date TimeTemp (ºC)
Field SC (umhos) pH
Dissolved Oxygen (mg/L)
Turbidity (ntu)
12/24/2002 10:25 AM 8.3 1500 7.6 12.41/2/2003 12:46 PM 10.4 1610 7.7 14.41/9/2003 11:34 AM 9.7 2540 7.7 10.51/16/2003 12:05 PM 11.6 2010 7.8 10.6 52.91/23/2003 8:57 AM 10.7 2450 7.5 13.61/30/2003 10:41 AM 12.7 2500 7.7 8.5 38.62/6/2003 10:22 AM 9.4 2940 7.9 11.42/13/2003 12:16 PM 12.6 2780 7.8 10.1 36.62/20/2003 11:28 AM 12.1 2640 8.0 12.4 48.22/27/2003 9:13 AM 13.3 3100 7.9 9.33/6/2003 11:02 AM 14.8 3070 7.8 12.0 NA3/13/2003 10:25 AM 18.2 3030 8.1 9.1 1013/20/2003 8:55 AM 14.9 2980 8.0 9.1 90.53/27/2003 9:44 AM 15.8 2270 8.3 9.8 82.54/3/2003 1:11 PM 17.2 3640 7.8 11.3 56.44/10/2003 10:15 AM 18.9 4510 8.2 10.6 45.64/17/2003 9:15 AM 16.6 4830 8.2 10.1 33.54/24/2003 10:11 AM 17.7 3680 8.3 9.8 51.75/1/2003 9:37 AM 17.8 3930 8.2 10.6 NA5/8/2003 9:04 AM 17.4 4350 8.1 10.4 49.65/15/2003 9:09 AM 18.9 4430 8.5 12.05/22/2003 10:19 AM 22.9 4300 8.2 10.4 33.75/29/2003 9:55 AM 25.0 3360 8.1 8.46/5/2003 10:10 AM 25.0 2520 8.1 8.0 81.76/12/2003 10:25 AM 21.4 2730 8.3 9.9 77.76/19/2003 10:17 AM 23.5 3710 8.5 6.3 50.06/26/2003 9:41 AM 23.8 3500 8.5 10.2 59.67/3/2003 9:50 AM 24.7 3820 8.4 27.67/10/2003 9:40 AM 24.8 4370 8.4 15.87/17/2003 9:55 AM 26.5 2770 8.5 10.17/24/2003 9:17 AM 27.3 3740 8.4 8.9 29.57/31/2003 9:50 AM 26.5 3410 8.3 8.8 30.38/7/2003 9:17 AM 24.1 2810 8.4 9.1 56.58/14/2003 9:30 AM 23.9 3560 8.7 10.08/21/2003 9:10 AM 25.2 4110 8.4 8.9 32.68/28/2003 9:37 AM 24.2 2910 8.2 NA 36.29/4/2003 9:15 AM 25.0 2640 8.0 6.4 21.09/11/2003 11:28 AM 23.5 2340 8.3 9.3 47.99/18/2003 9:34 AM 19.6 1750 8.0 17.7 83.49/25/2003 10:22 AM 21.9 1650 7.7 5.3 37.110/2/2003 10:03 AM 20.8 1430 7.6 6.1 25.310/9/2003 9:34 AM 20.7 1650 7.5 7.2 218
10/16/2003 11:39 AM 18.0 1630 7.6 6.9 19.510/23/2003 10:50 AM 19.4 1360 7.6 7.1 21.2
69
E4: 541MER542 – Mud Slough @ San Luis Drain continued…
Date TimeTemp (ºC)
Field SC (umhos) pH
Dissolved Oxygen (mg/L)
Turbidity (ntu)
10/30/2003 9:04 AM 15.6 1650 7.7 6.7 16.511/6/2003 10:02 AM 13.8 1550 7.8 8.3 20.0
11/13/2003 8:51 AM 13.2 1710 7.7 7.9 18.911/20/2003 9:26 AM 13.3 1590 7.8 8.1 NA11/26/2003 8:48 AM 8.0 1850 8.0 10.5 13.312/4/2003 9:28 AM 12.0 2040 7.7 9.6
12/11/2003 8:59 AM 10.8 1900 7.8 11.0 NA12/18/2003 9:51 AM 8.6 2020 7.9 12.8 NA12/23/2003 9:18 AM 10.9 2010 7.6 13.6 NA12/30/2003 9:51 AM 8.1 1820 7.9 12.1 NA1/8/2004 8:35 AM 8.9 2140 7.7 10.0 NA1/15/2004 9:49 AM 9.6 2470 7.9 9.9 NA1/22/2004 9:18 AM 8.7 2490 7.8 16.6 19.81/29/2004 10:07 AM 10.5 2460 7.9 10.8 NA2/5/2004 9:13 AM 9.8 2780 8.0 11.5 27.42/12/2004 9:26 AM 10.7 3070 8.1 12.2 NA2/19/2004 9:08 AM 12.3 2750 7.9 11.8 NA2/26/2004 9:37 AM 11.5 2140 7.9 9.8 NA3/4/2004 9:18 AM 12.0 2420 8.0 10.4 79.13/11/2004 9:53 AM 17.2 2720 7.8 7.7 NA3/18/2004 8:32 AM 19.5 3260 8.0 9.03/25/2004 10:01 AM 18.1 3460 8.2 8.5 57.64/1/2004 9:30 AM 15.9 3370 8.3 10.64/8/2004 9:45 AM 17.9 4970 8.4 10.3 26.74/15/2004 9:39 AM 18.5 4040 8.2 9.6 46.64/22/2004 10:00 AM 16.1 4570 8.3 15.4 52.54/29/2004 10:59 AM 18.7 3600 8.4 NA 42.05/6/2004 10:34 AM 23.0 4180 8.1 24.0 31.55/13/2004 10:10 AM 19.7 2600 8.4 18.9 60.15/20/2004 10:03 AM 20.9 3030 8.2 9.6 46.55/27/2004 9:19 AM 21.8 2800 8.2 NA NA6/3/2004 10:27 AM 24.6 4400 8.3 10.4 44.16/10/2004 10:06 AM 20.8 4170 8.6 10.9 446/17/2004 10:41 AM 24.3 3530 8.4 10.8 38.56/24/2004 9:49 AM 23.2 3800 8.3 9.5 NA7/1/2004 9:58 AM 22.8 3400 8.4 10.3 NA
70
E4: 541MER542 – Mud Slough @ San Luis Drain continued…
Date TimeTemp (ºC)
Field SC (umhos) pH
Dissolved Oxygen (mg/L)
Turbidity (ntu)
7/8/2004 9:33 AM 24.7 3480 8.1 9.5 NA7/15/2004 10:06 AM 25.0 2940 8.0 9.5 NA7/22/2004 11:34 AM 27.6 3120 8.3 11.2 NA7/29/2004 9:31 AM 25.2 2830 8.2 10.1 NA8/5/2004 9:02 AM 23.5 3280 8.3 9.6 NA8/12/2004 9:45 AM 26.3 3580 8.3 9.5 NA8/19/2004 11:22 AM 26.2 3140 8.4 10.7 NA8/26/2004 9:59 AM 23.6 3660 8.5 9.6 NA9/2/2004 9:19 AM 24.1 3520 8.1 8.1 NA9/9/2004 11:26 AM 24.8 2820 7.5 8.2 NA9/16/2004 11:02 AM 22.3 2960 8.1 8.4 NA9/23/2004 12:47 PM 21.5 2220 7.9 9.8 NA9/30/2004 9:22 AM 18.9 2170 7.8 7.5 NA10/7/2004 9:22 AM 20.3 1500 7.4 8.3
10/14/2004 8:56 AM 18.8 1240 7.4 7.510/21/2004 10:35 AM 15.3 1480 NA 9.010/28/2004 9:09 AM 13.2 1360 7.6 9.911/4/2004 10:56 AM 12.8 1780 7.9 8.6
11/11/2004 8:57 AM 14.5 1800 7.5 7.911/18/2004 9:20 AM 13.5 1750 7.7 7.911/23/2004 12:06 PM 9.8 1940 7.6 10.112/2/2004 10:24 AM 7.4 2280 8.0 11.912/9/2004 9:04 AM 10.6 1960 8.0 11.1
12/16/2004 10:01 AM 11.0 1970 7.7 10.312/22/2004 12:01 PM 8.6 2040 8.0 14.112/29/2004 10:42 AM 9.4 1800 7.8 10.61/6/2005 8:25 AM 9.6 1740 7.6 11.81/13/2005 10:12 AM 9.2 1610 7.8 9.01/20/2005 9:29 AM 9.1 1840 7.6 10.91/27/2005 9:25 AM 10.7 2740 7.9 13.92/3/2005 9:34 AM 10.7 2800 7.7 11.12/10/2005 9:33 AM 12.6 2990 7.9 9.92/17/2005 9:42 AM 14.2 2700 7.7 10.22/24/2005 9:46 AM 14.3 1980 7.8 9.33/3/2005 8:55 AM 15.1 2490 7.9 9.33/10/2005 10:50 AM 19.2 2550 7.9 11.33/17/2005 8:55 AM 16.5 3560 7.9 13.0
71
E4: 541MER542 – Mud Slough @ San Luis Drain continued…
Date TimeTemp (ºC)
Field SC (umhos) pH
Dissolved Oxygen (mg/L)
Turbidity (ntu)
3/24/2005 9:37 AM 14.5 2710 7.9 11.23/31/2005 9:14 AM 14.2 3510 8.2 11.04/7/2005 9:48 AM 17.7 3550 8.3 8.94/14/2005 9:01 AM 14.3 3720 8.4 11.14/21/2005 9:48 AM 17.6 4180 8.3 9.04/28/2005 9:11 AM 18.3 3000 8.1 12.95/5/2005 10:07 AM 20.5 3280 8.1 10.05/12/2005 9:10 AM 19.2 3930 8.2 9.95/19/2005 9:56 AM 21.5 4240 8.2 9.65/26/2005 10:05 AM 24.7 2880 8.2 7.56/2/2005 10:00 AM 21.8 2420 8.3 10.96/9/2005 8:39 AM 20.7 2790 8.1 10.06/16/2005 9:34 AM 23.4 3000 8.1 9.56/23/2005 10:28 AM 23.5 2700 NA 9.66/30/2005 10:39 AM 25.9 2740 8.4 10.27/7/2005 9:17 AM 25.2 3410 7.9 11.17/13/2005 10:16 AM 27.9 2740 7.2 9.47/21/2005 9:05 AM 27.2 2930 8.3 8.97/28/2005 10:51 AM 27.6 3370 8.6 10.38/4/2005 9:15 AM 26.1 3190 8.5 8.68/11/2005 10:53 AM 26.6 3240 8.5 10.08/18/2005 9:44 AM 24.1 3470 8.2 9.78/25/2005 9:54 AM 24.2 3000 7.9 9.29/1/2005 9:10 AM 22.9 3050 7.9 9.99/8/2005 9:59 AM 22.0 2970 8.0 8.89/15/2005 9:20 AM 19.6 1930 7.9 9.29/22/2005 10:19 AM 22.1 2700 8.0 10.29/29/2005 9:21 AM 20.3 2160 8.0 7.5
Count 264 264 261 218 55Min 6.9 1200 6.6 2.6 13.3Max 29.3 5140 8.7 27.6 218Mean 17.9 2854 8.0 9.9 45.8Geo Mean 16.9 2710 8.0 9.7 39.0Median 18.2 2805 8.0 9.8 38.6Quartile 1 12.6 2040 7.8 8.8 26.0Quartile 3 23.4 3503 8.3 10.8 52.7NOTE: For values reported as < (less than), half the detection limit was used.
NA = Data not applicableINA = Site was inaccessibleDRY = Site had no flow
72
E4: 541MER542 – Mud Slough @ San Luis Drain continued…
DateTSS
(mg/L)TOC
(mg/L)Total Coli
MPNE. coli MPN
10/12/2000 3410/26/2000 25 1311/30/2000 15 5.312/28/2000 15 8.81/25/2001 28 8.92/22/2001 NA <13/29/2001 72 <14/26/2001 6.65/31/2001 44 8.76/7/2001 46 116/14/2001 45 136/21/2001 NA 136/28/2001 37 147/26/2001 108/30/2001 55 179/27/2001 54 2210/4/2001 28
10/11/2001 3210/25/2001 2211/29/2001 NA1/31/2002 NA2/28/2002 9.53/28/2002 194/25/2002 NA5/30/2002 7.26/20/2002 6.18/1/2002 >2419.6 319/26/2002 NA
10/17/2002 >2419.6 13510/31/2002 1011/21/2002 1112/19/2002 8.41/16/2003 2420 743/27/2003 7.84/24/2003 8.0 >2419.6 24205/29/2003 9.96/26/2003 117/31/2003 >2419.6 448/28/2003 >2419.6 759/25/2003 >2419.6 86
10/30/2003 >2419.6 37
73
74
DateTSS
(mg/L)TOC
(mg/L)Total Coli
MPNE. coli MPN
11/20/2003 >2419.6 593/25/2004 >2419.6 754/29/2004 >2419.6 885/27/2004 >2419.6 866/24/2004 >2419.6 1017/29/2004 >2419.6 1308/26/2004 >2419.6 69/30/2004 >2419.6 17
10/28/2004 >2419.6 16611/23/2004 13 >2419.6 2412/29/2004 11 >2419.6 2781/27/2005 12 >2419.6 642/24/2005 13 >2419.6 933/31/2005 13 >2419.6 744/28/2005 NA >2419.6 1025/26/2005 9.2 >2419.6 6876/37/28/29/2
CounMin
E4: 541MER542 – Mud Slough @ San Luis Drain continued…
0/2005 7.0 1011 438/2005 10 >2419.6 205/2005 11 >2419.6 509/2005 13 >2419.6 99
t 12 39 28 2815 0.5 1011 6
Max 72 32 2420 2420n 39 12 NA NA Mean 35 10 234
MeaGeo 6 76
ian 41 11 2420 7Med 5QuaQua
rtile 1 27 8.6 2420 44rtile 3 48 13 2420 101E: For values reported as < (less than), half the detection limit was used For values reported as > (greater than), 2420 was used
Data not applicable Site was inaccessible
= Site had no flow
NOT
NA =INA =DRY
E4: 541MER542 – Mud Slough @ San Luis Drain continued…
DateNitrate (mg/L)
Nitrate-N (mg/L)
TKN (mg/L)
Ammonia-N (mg/L)
Phosphorus (mg/L)
Ortho-phosphate-
P (mg/L)
Potassium (mg/L)
BOD 5-Day (mg/L)
BOD 10-Day (mg/L)
10/26/2000 4.2 <2 0.4 <1 11 3.2 5.811/30/2000 14 2.2 0.2 <1 11 1.2 2.412/28/2000 17 <2 0.2 <1 11 1.3 2.31/25/2001 18 <2 0.2 <1 10 2.2 3.82/22/2001 36 <2 0.2 <1 11 3.0 5.63/29/2001 52 2.4 <1 0.3 <1 12 5.2 10.44/26/2001 72 <2 <1 0.1 <1 9.8 4.7 7.35/31/2001 50 <2 0.1 NA 9.5 3.2 6.26/7/2001 59 <1.0 0.1 <1 8.7 4.7 7.06/14/2001 84 <2 <1 8.7 4.3 7.46/21/2001 55 <2 <0.1 <1 8.3 7.3 11.86/28/2001 57 <2 <0.1 <1 10 3.3 5.58/30/2001 49 <2 0.1 <1 9.49/27/2001 7.9 <2 0.4 <1 12
10/25/2001 3.0 6.811/29/2001 NA NA NA 0.2 12 1.4 3.412/27/2001 1.3 2.81/31/2002 2.1 3.52/28/2002 2.8 5.33/28/2002 NA 2.1 0.5 0.2 9.64/25/2002 4.9 7.95/30/2002 3.2 5.16/20/2002 6.2 10.98/29/2002 5.1 8.49/26/2002 3.1 5.4
10/31/2002 4.1 7.411/21/2002 2.3 4.6
75
E4: 541MER542 – Mud Slough @ San Luis Drain continued…
DateNitrate (mg/L)
Nitrate-N (mg/L)
TKN (mg/L)
Ammonia-N (mg/L)
Phosphorus (mg/L)
Ortho-phosphate-
P (mg/L)
Potassium (mg/L)
BOD 5-Day (mg/L)
BOD 10-Day (mg/L)
12/19/2002 2.1 3.41/30/2003 2.2 3.83/13/2003 35 4.5 0.5 <1.0 118/28/2003 17 2.3 0.2 <1.0 119/25/2003 5.9 2.1 0.5 <1.0 10
10/30/2003 7.0 2.1 0.5 <1.0 1111/20/2003 6.9 <1.0 0.2 <1.0 101/29/2004 3.9 1.2 0.2 0.3 0.22/26/2004 6.6 1.4 NA 0.4 0.33/11/2004 4.0 2.1 0.2 0.6 0.33/25/2004 7.7 1.8 0.2 0.6 0.24/15/2004 9.5 1.7 0.1 0.2 NA4/29/2004 11.0 1.9 0.1 0.2 <0.015/13/2004 6.8 1.6 0.1 0.2 <0.016/10/2004 13.0 1.7 0.1 0.1 <0.016/24/2004 8.9 1.8 0.1 0.1 <0.017/15/2004 8.2 1.2 0.1 0.1 <0.017/29/2004 5.1 1.7 NA 0.1 <0.038/12/2004 6.3 1.8 0.1 0.1 <0.038/26/2004 6.1 2.1 NA 0.2 <0.039/16/2004 4.3 1.8 0.2 0.2 <0.039/30/2004 1.8 1.6 0.3 NA <0.03
10/28/2004 1.4 1.5 NA 0.4 0.411/23/2004 1.5 1.5 NA 0.3 0.212/29/2004 1.4 1.1 0.1 0.2 0.11/27/2005 6.0 1.4 0.2 0.4 0.22/24/2005 4.9 1.5 0.1 0.5 0.3
76
E4: 541MER542 – Mud Slough @ San Luis Drain continued…
DateNitrate (mg/L)
Nitrate-N (mg/L)
TKN (mg/L)
Ammonia-N (mg/L)
Phosphorus (mg/L)
Ortho-phosphate-
P (mg/L)
Potassium (mg/L)
BOD 5-Day (mg/L)
BOD 10-Day (mg/L)
3/31/2005 10.0 1.7 0.2 0.4 0.24/28/2005 7.5 1.5 0.2 NA NA5/12/2005 12.0 NA NA 0.3 <0.035/26/2005 4.7 1.5 0.1 0.2 <0.036/16/2005 NA 1.2 NA NA NA6/30/2005 6.8 1.8 0.1 0.2 NA7/13/2005 5.6 1.5 NA NA <0.039/29/2005 2.3 1.6 NA NA <0.03
Count 19 27 47 21 42 44 21 26 26Min 4.2 1.4 0.5 0.1 0.1 0.01 8.3 1.2 2.3Max 84.0 13.0 4.5 0.5 0.6 0.5 12.0 7.3 11.8Mean 34.0 6.2 1.6 0.2 0.3 0.3 10.3 3.4 5.9Geo Mean 23.6 5.2 1.4 0.2 0.2 0.1 10.3 3.0 5.4Median 35.0 6.1 1.5 0.1 0.2 0.3 10.0 3.2 5.6Quartile 1 11.0 4.2 1.0 0.1 0.1 0.02 9.6 2.2 3.8Quartile 3 53.5 8.0 1.8 0.2 0.4 0.5 11.0 4.6 7.4NOTE: For values reported as < (less than), half the detection limit was used
For values reported as > (greater than), 2420 was used
NA = Data not applicableINA = Site was inaccessibleDRY = Site had no flow
77
E4: 541MER542 – Mud Slough @ San Luis Drain continued…
DateHardness
(mg/L)
Total Arsenic (ug/L)
Total Cadmium
(ug/L)
Total Chromium
(ug/L)
Total Copper (ug/L)
Total Lead (ug/L)
Total Nickel (ug/L)
Total Zinc (ug/L)
Total Mercury (ug/L)
10/26/2000 280 1.8 1.7 <5 5.411/30/2000 410 1.7 1.5 <5 <5 <212/28/2000 470 3.1 2.2 <5 <5 3.01/25/2001 470 3.7 2.3 <5 5.3 <22/22/2001 620 5.8 3.2 <5 7.6 <23/29/2001 940 8.6 4.1 <5 10 5.14/26/2001 1100 6.2 2.9 <5 <5 <25/31/2001 760 3.3 2.8 <5 6.5 2.76/7/2001 880 2.4 <1 5.0 3.1 <5 6 2.1 <0.26/14/2001 1000 <2.0 <1 5.1 2.0 <5 <5 4.5 <0.26/21/2001 NA 2.0 <1 2.8 1.8 <5 <5 <2 <0.26/28/2001 950 2.4 <1 2.7 1.7 <5 5.2 <2 <0.27/26/2001 NA NA 3.2 1.9 <5 <5 <2 NA8/30/2001 820 2.1 <1 2.5 1.8 <5 <5 <29/27/2001 1200 5.7 <1 <1 2.2 <5 <5 70 <0.2
10/25/2001 400 4.1 <0.1 <1 1.2 <5 <5 2.1 <0.211/29/2001 420 4.6 <0.1 1.6 <1 <5 <5 2.1 <0.212/27/2001 <4 <0.1 2.3 2.2 <5 <5 <2 <0.21/31/2002 <4.0 <0.1 1.6 NA <5.0 <5.0 <2.0 <0.22/28/2002 4.9 <0.1 7.8 4.2 <5.0 8.4 4.7 <0.23/28/2002 9.4 <0.1 5.3 4.9 <5.0 13 8.9 <0.24/25/2002 4.4 <0.1 <1.0 1.0 <5.0 <5.0 <2.0 <0.25/30/2002 <4.0 <0.1 2.5 2.4 <5.0 6.0 <2.0 <0.26/20/2002 700 4.5 <0.1 3.4 1.9 <5.0 6.1 <2.0 <0.29/26/2002 470 6.3 <0.1 3.6 NA <5.0 6.8 2.5 <0.2
10/31/2002 340 4.0 <0.1 1.4 1.6 <5.0 <5.0 <2.0 <0.211/21/2002 360 <4.0 <0.1 2.0 7.7 <5.0 <5.0 <2.0 <0.2
78
E4: 541MER542 – Mud Slough @ San Luis Drain continued…
DateHardness
(mg/L)
Total Arsenic (ug/L)
Total Cadmium
(ug/L)
Total Chromium
(ug/L)
Total Copper (ug/L)
Total Lead (ug/L)
Total Nickel (ug/L)
Total Zinc (ug/L)
Total Mercury (ug/L)
3/27/2003 550 7.7 NA 6.7 4.4 <5.0 9.1 8.5 <0.24/24/2003 830 4.1 <0.1 NA NA NA 5.4 2.7 <0.25/29/2003 730 <4.0 <0.1 4.5 4.7 <5.0 5.7 3.7 <0.26/26/2003 760 <4.0 <0.1 5.9 6.4 <5.0 8.0 3.4 <0.2
Count 23 22 21 30 28 30 31 30 21Min 280.0 1.0 0.1 0.5 0.5 2.5 2.5 1.0 0.1Max 1200.0 9.4 0.5 8.6 7.7 2.5 13.0 70.0 0.1Mean 672.2 3.7 0.2 3.5 2.8 2.5 4.9 4.7 0.1Geo Mean 621.0 3.2 0.1 2.8 2.4 2.5 4.2 2.1 0.1Median 700.0 3.2 0.1 3.2 2.2 2.5 5.2 1.6 0.1Quartile 1 445.0 2.0 0.1 1.9 1.8 2.5 2.5 1.0 0.1Quartile 3 855.0 4.6 0.5 5.1 3.4 2.5 6.3 3.3 0.1NOTE: For values reported as < (less than), half the detection limit was used
For values reported as > (greater than), 2420 was used
NA = Data not applicableINA = Site was inaccessibleDRY = Site had no flow
79
E4: 541MER542 – Mud Slough @ San Luis Drain continued…
DateHardness
(mg/L)
Dissolved Arsenic (ug/L)
Dissolved Cadmium
(ug/L)
Dissolved Chromium
(ug/L)
Dissolved Copper (ug/L)
Dissolved Lead (ug/L)
Dissolved Nickel (ug/L)
Dissolved Zinc
(ug/L)
Dissolved Mercury (ug/L)
10/26/2000 280 <1 <1 <5 <5 <211/30/2000 410 <1 1.2 <5 <5 <212/28/2000 470 1.4 <1 <5 <5 <21/25/2001 470 1.5 <1 <5 <5 <22/22/2001 620 2.5 1.1 <5 <5 <23/29/2001 940 3.1 2.1 <5 <5 <24/26/2001 1100 4.3 1.8 <5 <5 <25/31/2001 760 <1 <1 <5 <5 <26/7/2001 880 2.0 <1 2.4 1.1 <5 <5 <2 <0.26/14/2001 1000 <2.0 <1 3.6 1.1 <5 <5 <2 <0.26/21/2001 NA <2.0 <1 <1 <1 <5 <5 <2 <0.26/28/2001 950 2.5 <1 1.1 <1 <5 <5 <2 <0.27/26/2001 NA NA NA NA NA NA NA NA8/30/2001 820 <2 <1 1.0 1.2 <5 <5 <29/27/2001 1200 5.2 <1 <1 1.3 <5 <5 52 <0.2
10/25/2001 400 4.3 <0.1 <1 1.1 <5 <5 <2 <0.211/29/2001 420 <4 <0.1 <1 1.3 <5 <5 <2 <0.212/27/2001 <4 <0.1 <1 1.2 <5 <5 <2 <0.21/31/2002 <4.0 <0.1 1.4 NA <5.0 <5.0 <2.0 <0.22/28/2002 5.5 <0.1 2.4 1.1 <5.0 <5.0 <2.0 <0.23/28/2002 6.6 <0.1 <1.0 2.1 <5.0 8.1 <2.0 <0.24/25/2002 5.2 <0.1 1.4 <1.0 <5.0 <5.0 NA <0.25/30/2002 <4.0 <0.1 <1.0 1.2 <5.0 <5.0 <2.0 <0.26/20/2002 700 <4.0 <0.1 <1.0 1.5 <5.0 <5.0 <2.0 <0.29/26/2002 470 6.4 <0.1 <1.0 3.2 <5.0 <5.0 <2.0 <0.2
10/31/2002 340 <4.0 <0.1 <1.0 1.3 <5.0 <5.0 <2.0 <0.2
80
E4: 541MER542 – Mud Slough @ San Luis Drain continued…
DateHardness
(mg/L)
Dissolved Arsenic (ug/L)
Dissolved Cadmium
(ug/L)
Dissolved Chromium
(ug/L)
Dissolved Copper (ug/L)
Dissolved Lead (ug/L)
Dissolved Nickel (ug/L)
Dissolved Zinc
(ug/L)
Dissolved Mercury (ug/L)
11/21/2002 360 <4.0 <0.1 <1.0 1.2 <5.0 <5.0 <2.0 <0.23/27/2003 5504/24/2003 8305/29/2003 7306/26/2003 760
Count 23 18 18 26 25 26 26 25 17Min 280.0 1.0 0.1 0.5 0.5 2.5 2.5 1.0 0.1Max 1200.0 6.6 0.5 4.3 3.2 2.5 8.1 52.0 0.1Mean 672.2 3.0 0.2 1.3 1.2 2.5 2.7 3.0 0.1Geo Mean 621.0 2.5 0.1 0.9 1.0 2.5 2.6 1.2 0.1Median 700.0 2.0 0.1 0.5 1.2 2.5 2.5 1.0 0.1Quartile 1 445.0 2.0 0.1 0.5 0.5 2.5 2.5 1.0 0.1Quartile 3 855.0 5.0 0.5 1.5 1.3 2.5 2.5 1.0 0.1NOTE: For values reported as < (less than), half the detection limit was used
For values reported as > (greater than), 2420 was used
NA = Data not applicableINA = Site was inaccessibleDRY = Site had no flow
81
E4: 541MER542 – Mud Slough @ San Luis Drain continued…
DateChloride (mg/L)
Sulfate (mg/L)
Calcium (mg/L)
Magnesium (mg/L)
TDS (mg/L)
Carbonate (mg/L)
Bicarbonate (mg/L)
Total Alkalinity
(mg/L)Sodium (mg/L)
10/26/2000 140 200 61 31 800 <1 240 200 15011/30/2000 230 380 89 45 1300 <1 250 200 26012/28/2000 270 470 100 52 1400 <1 270 220 3101/25/2001 270 480 100 51 1400 <1 270 220 3202/22/2001 330 660 140 66 2000 <1 290 240 4303/29/2001 490 1100 220 97 3000 2 260 220 6404/26/2001 1500 260 110 3700 20 146 166 7105/31/2001 410 1100 180 73 2500 <1 160 160 4906/7/2001 470 1100 210 84 2800 2 180 160 5706/14/2001 540 1300 250 93 3300 5 150 140 6706/21/2001 490 1400 230 93 3300 <1 170 140 6606/28/2001 560 1500 240 89 3200 <1 220 180 6508/30/2001 410 1100 200 79 2800 <1 140 120 5409/27/2001 NA 1700 310 110 3900 <1 NA NA 740
10/25/2001 270 330 85 46 1200 <1 270 NA 27011/29/2001 270 390 88 47 1300 <1 280 228 2906/20/20029/26/2002
10/31/200211/21/20023/27/2003 360 610 120 634/24/2003 450 1100 200 805/29/2003 430 1500 180 706/26/2003 400 1100 190 71
82
E4: 541MER542 – Mud Slough @ San Luis Drain continued…
DateChloride (mg/L)
Sulfate (mg/L)
Calcium (mg/L)
Magnesium (mg/L)
TDS (mg/L)
Carbonate (mg/L)
Bicarbonate (mg/L)
Total Alkalinity
(mg/L)Sodium (mg/L)
Count 18 20 20 20 16 16 15 14 16Min 140 200 61 31 800 0.5 140 120 150Max 560 1700 310 110 3900 20.0 290 240 740Mean 380 950 170 73 2400 2.2 220 190 480Geo Mean 360 810 160 69 2100 0.9 210 180 440Median 400 1100 190 72 2700 0.5 240 190 520Quartile 1 270 480 100 52 1400 0.5 170 160 300Quartile 3 470 1300 220 90 3200 0.9 270 220 650NOTE: For values reported as < (less than), half the detection limit was used
For values reported as > (greater than), 2420 was used
NA = Data not applicableINA = Site was inaccessibleDRY = Site had no flow
83
APPENDIX F
WESTSIDE BASIN
APPENDIX F: WESTSIDE BASIN F1: 541STC019 – Orestimba Creek @ River Road…………………………………….........03-19 F2: 541STC515 – Salado Creek at HWY 33………………………………………………....20-31 F3: 541STC516 – Del Puerto Creek at Vineyard Avenue……………………………………32-42 F4: 541STC040 – Ingram Creek at River Road…………………………………………...…43-55 F5: 541STC042 – Hospital creek at River Road………………………………………..……56-65 F6: 541STC030 – Grayson Road Drain at Grayson…………………………………...……..66-79
2
F1: 541STC019 – Orestimba Creek @ River Road Station Code:541STC019
Location: Latitude 37.41389, Longitude -121.01417
Date TimeTemp (ºC)
Field SC (umhos) pH
Dissolved Oxygen (mg/L)
Turbidity (ntu)
10/26/2000 1:50 PM 15.2 562 7.811/30/2000 10:20 AM 9.4 583 8.012/28/2000 9:36 AM 5.6 637 8.01/25/2001 10:15 AM 8.2 838 8.42/7/2001 10:41 AM 8.4 769 7.32/22/2001 11:20 AM 11.4 769 8.03/13/2001 11:55 AM 16.4 703 7.93/29/2001 12:50 PM 19.5 848 8.44/18/2001 11:38 AM 17.9 921 7.94/26/2001 12:15 PM 22.6 667 8.05/15/2001 12:13 PM 20.0 607 7.45/31/2001 9:50 AM 23.7 864 7.76/6/2001 9:45 AM 19.8 848 7.4 7.36/13/2001 10:25 AM 19.8 702 8.2 8.36/28/2001 11:24 AM 21.7 720 8.1 7.87/26/2001 10:38 AM 23.3 707 8.0 9.28/2/2001 12:17 PM 22.6 750 7.9 8.28/9/2001 11:03 AM 23.6 775 8.0 7.98/14/2001 11:32 AM 20.1 902 8.1 9.48/16/2001 12:16 PM 22.2 908 8.0 8.98/23/2001 11:29 AM 21.3 895 8.0 9.68/30/2001 12:13 PM 22.0 953 8.1 8.09/6/2001 11:22 AM 20.0 1030 7.9 8.09/13/2001 12:44 PM 19.8 1190 8.4 11.59/20/2001 9:06 AM 18.9 1250 8.0 7.79/27/2001 9:33 AM 18.5 827 7.9 8.010/4/2001 10:13 AM 18.7 946 8.0 9.0
10/11/2001 11:35 AM 17.3 653 8.0 9.410/18/2001 11:23 AM 18.6 716 8.0 9.110/25/2001 12:46 PM 15.1 692 8.0 10.511/1/2001 12:05 PM 16.2 718 8.1 9.311/8/2001 12:52 PM 13.3 792 8.3 11.1
11/15/2001 10:27 AM 15.3 659 8.2 9.911/20/2001 10:03 AM 14.2 638 8.0 9.911/29/2001 10:50 AM 12.2 655 7.6 NA12/6/2001 11:30 AM 9.9 660 7.9 12.1
12/13/2001 11:04 AM 8.1 808 7.6 11.5
3
F1: 541STC019 – Orestimba Creek @ River Road continued…
Date TimeTemp (ºC)
Field SC (umhos) pH
Dissolved Oxygen (mg/L)
Turbidity (ntu)
12/20/2001 9:18 AM 7.9 703 8.1 11.912/27/2001 11:23 AM 9.7 749 8.0 12.01/3/2002 11:54 AM 12.7 578 8.0 11.11/10/2002 11:27 AM 11.0 591 8.2 12.01/17/2002 11:06 AM 5.4 581 7.9 13.31/24/2002 10:58 AM 5.0 634 8.2 6.01/31/2002 9:53 AM 3.6 860 8.6 13.92/7/2002 10:39 AM 9.9 644 8.2 12.52/14/2002 11:13 AM 10.8 748 8.3 11.82/21/2002 9:45 AM 12.6 669 8.3 11.02/28/2002 11:47 AM 13.6 748 8.3 11.13/7/2002 10:10 AM 13.4 717 8.2 10.23/14/2002 12:01 PM 11.6 738 8.0 12.33/21/2002 12:01 PM 14.8 894 8.4 12.33/28/2002 2:17 PM 17.6 805 8.1 12.14/4/2002 10:37 AM 16.7 997 8.3 9.04/11/2002 12:47 PM 17.6 849 7.5 9.94/18/2002 9:52 AM 12.0 1020 8.3 10.84/25/2002 9:32 AM 15.9 710 8.0 9.25/2/2002 9:57 AM 16.1 743 7.8 10.25/9/2002 INA INA INA INA INA5/16/2002 11:20 AM 20.5 696 7.4 NA NA5/23/2002 8:50 AM 15.2 845 7.4 NA5/30/2002 12:29 PM 24.3 767 7.6 7.06/6/2002 10:12 AM 22.6 750 8.2 6.66/13/2002 9:54 AM 21.2 815 7.8 NA6/20/2002 10:02 AM 22.0 753 7.3 NA6/27/2002 11:30 AM 22.6 614 7.9 7.97/3/2002 8:50 AM 22.3 699 8.3 NA7/11/2002 11:03 AM 25.8 572 7.8 NA7/18/2002 11:30 AM 22.4 583 7.9 8.3 4907/25/2002 10:08 AM 20.9 732 7.9 8.08/1/2002 11:15 AM 22.1 800 8.1 8.08/8/2002 11:29 AM 20.2 763 8.0 9.98/15/2002 10:37 AM 22.9 772 8.0 8.38/22/2002 10:28 AM 19.6 808 8.0 8.88/29/2002 10:11 AM 20.9 799 8.0 NA9/5/2002 10:11 AM 19.1 848 8.0 8.79/12/2002 10:29 AM 19.1 913 7.9 9.29/19/2002 10:26 AM 20.2 928 8.0 8.3 NA9/26/2002 10:13 AM 19.5 899 8.0 9.1
4
F1: 541STC019 – Orestimba Creek @ River Road continued…
Date TimeTemp (ºC)
Field SC (umhos) pH
Dissolved Oxygen (mg/L)
Turbidity (ntu)
10/3/2002 10:38 AM 12.8 873 7.9 11.910/10/2002 10:01 AM 17.2 828 8.1 9.110/17/2002 10:27 AM 15.1 742 8.5 10.2 15410/24/2002 9:12 AM 15.1 909 7.8 9.510/31/2002 11:23 AM 12.7 750 8.0 9.3 11311/7/2002 10:57 AM 13.6 671 8.0 10.4
11/14/2002 11:11 AM 13.1 571 7.7 10.411/21/2002 10:38 AM 12.3 516 7.9 10.3 67.611/26/2002 10:29 AM 9.4 801 8.0 10.912/5/2002 10:15 AM DRY DRY DRY DRY DRY
12/12/2002 10:05 AM DRY DRY DRY DRY12/19/2002 10:29 AM 7.8 361 7.7 12.6 49.412/24/2002 9:26 AM 6.8 363 7.8 12.91/2/2003 10:18 AM 8.3 360 8.2 16.21/9/2003 11:18 AM DRY DRY DRY DRY1/16/2003 12:00 PM DRY DRY DRY DRY DRY1/23/2003 DRY DRY DRY DRY DRY1/30/2003 11:41 AM 11.5 515 7.5 11.7 2512/6/2003 9:06 AM 8.1 627 8.1 11.82/13/2003 10:13 AM 11.2 876 8.0 11.0 70.62/20/2003 9:27 AM 9.3 891 8.3 12.5 24.62/27/2003 10:17 AM 13.1 717 8.1 10.33/6/2003 1:06 PM 14.3 547 8.3 14.1 NA3/13/2003 11:35 AM 17.0 879 8.5 13.4 42.33/20/2003 10:49 AM 15.1 1120 8.1 10.6 68.83/27/2003 10:50 AM 14.6 909 8.0 10.6 86.34/3/2003 11:04 AM 13.3 1000 7.8 10.6 44.54/10/2003 11:30 AM 17.1 761 8.7 10.2 1134/17/2003 11:28 AM 15.9 953 7.9 9.5 2364/24/2003 11:35 AM 16.4 791 8.1 9.0 1895/1/2003 11:04 AM 16.2 700 8.0 10.5 NA5/8/2003 10:32 AM 15.7 663 7.6 10.2 1905/15/2003 10:35 AM 18.3 675 8.1 10.35/22/2003 12:22 PM 22.6 660 8.0 8.8 2165/29/2003 10:53 AM 23.5 748 7.9 8.06/5/2003 12:20 PM 24.0 840 8.1 8.4 1986/12/2003 11:15 AM 20.9 8 8.0 7.8 1666/19/2003 12:07 PM 21.2 619 8.0 6.3 3626/26/2003 11:14 AM 22.7 751 8.1 8.5 1467/3/2003 10:53 AM 20.9 591 8.1 9.4
5
F1: 541STC019 – Orestimba Creek @ River Road continued…
Date TimeTemp (ºC)
Field SC (umhos) pH
Dissolved Oxygen (mg/L)
Turbidity (ntu)
7/10/2003 10:44 AM 22.8 421 7.9 7.97/17/2003 10:59 AM 23.4 642 8.0 8.17/24/2003 11:03 AM 24.9 448 7.9 8.0 8107/31/2003 11:35 AM 23.8 684 7.9 8.1 2808/7/2003 10:55 AM 21.3 482 8.1 8.9 4058/14/2003 10:37 AM 21.5 500 7.9 8.68/21/2003 10:29 AM 22.5 532 8.0 8.1 3608/28/2003 11:02 AM 20.8 567 7.9 8.9 2309/4/2003 10:22 AM 22.3 936 8.1 7.7 1169/11/2003 1:22 PM 21.1 773 8.1 9.8 1139/18/2003 11:15 AM 17.3 714 8.1 9.7 1649/25/2003 11:59 AM 18.9 753 8.3 10.1 53.710/2/2003 11:21 AM 17.6 615 8.1 10.0 10110/9/2003 11:09 AM 20.2 556 8.0 9.0 295
10/16/2003 10:14 AM 15.6 591 7.9 10.8 73.710/23/2003 12:20 PM 19.2 602 7.9 9.3 17710/30/2003 10:24 AM 15.8 622 7.9 10.2 91.811/6/2003 11:25 AM 13.4 575 8.2 11.2 85.6
11/13/2003 9:46 AM 11.9 619 8.0 10.4 49.711/20/2003 11:05 AM DRY DRY DRY DRY DRY11/26/2003 9:48 AM 5.2 1200 8.0 11.3 14.112/4/2003 10:28 AM DRY DRY DRY DRY DRY
12/11/2003 9:56 AM 9.6 1290 8.0 12.0 NA12/18/2003 11:00 AM DRY DRY DRY DRY DRY12/23/2003 10:30 AM DRY DRY DRY DRY DRY12/30/2003 11:12 AM 7.5 499 7.9 12.7 NA1/8/2004 9:45 AM 9.3 763 7.9 8.8 NA1/15/2004 11:02 AM 9.3 651 8.1 11.5 NA1/22/2004 10:30 AM 7.6 653 8.1 17.2 80.71/29/2004 11:23 AM 9.9 542 8.1 10.5 NA2/5/2004 10:13 AM 8.0 630 8.0 15.3 32.72/12/2004 10:27 AM 9.1 679 8.0 13.5 NA2/19/2004 10:02 AM 12.2 699 7.8 10.3 NA2/26/2004 10:59 AM 11.0 287 7.3 10.7 NA3/4/2004 10:15 AM 12.1 752 8.1 10.6 1123/11/2004 11:11 AM 15.6 634 8.0 9.7 NA3/18/2004 9:33 AM 17.4 729 7.9 10.53/24/2004 11:58 AM 17.8 717 8.0 9.0 NA4/1/2004 10:36 AM 13.2 824 8.0 10.2
6
F1: 541STC019 – Orestimba Creek @ River Road continued…
Date TimeTemp (ºC)
Field SC (umhos) pH
Dissolved Oxygen (mg/L)
Turbidity (ntu)
4/8/2004 11:04 AM 15.1 683 8.1 9.5 2704/15/2004 11:17 AM 16.1 845 8.3 11.2 2854/22/2004 11:05 AM 13.9 764 8.0 10.9 3294/29/2004 11:56 AM 16.7 711 8.0 9.1 1475/6/2004 11:48 AM 19.1 821 7.9 12.2 2445/13/2004 11:55 AM 18.0 830 8.1 16.3 2165/20/2004 11:07 AM 18.1 815 7.8 9.1 2505/27/2004 12:04 PM 20.5 746 8.0 8.3 3096/3/2004 11:35 AM 20.3 978 8.1 8.5 2566/10/2004 11:33 AM 19.5 716 8.2 9.8 2626/17/2004 11:54 AM 22.7 572 8.1 8.8 4026/24/2004 11:57 AM 21.2 815 8.0 10.3 NA7/1/2004 10:56 AM 21.6 740 8.0 10.1 NA7/8/2004 10:54 AM 23.3 726 7.7 7.7 NA7/15/2004 11:41 AM 21.9 661 8.2 9.7 NA7/22/2004 9:53 AM 23.9 717 7.9 9.2 NA7/29/2004 11:10 AM 22.9 653 8.0 9.2 NA8/5/2004 10:17 AM 21.6 828 8.1 8.4 NA8/12/2004 11:00 AM 23.4 800 8.2 9.0 NA8/19/2004 9:40 AM 22.1 682 8.1 NA NA8/26/2004 11:54 AM 20.7 869 7.9 8.2 NA9/2/2004 10:39 AM 20.7 957 7.9 8.7 NA9/9/2004 8:59 AM 20.7 933 8.0 8.0 NA9/16/2004 9:40 AM 19.2 1050 7.8 7.6 NA9/23/2004 1:50 PM 21.3 869 7.9 9.5 NA9/30/2004 11:03 AM 17.1 663 7.8 8.9 NA
10/28/2004 11:39 AM 12.9 573 8.2 10.611/3/2004 11:35 AM 12.8 568 8.0 10.5
11/17/2004 10:31 AM 12.6 521 7.8 9.512/8/2004 9:23 AM 9.3 667 8.0 12.0
12/21/2004 9:07 AM 7.7 759 8.1 12.81/5/2005 9:42 AM 8.2 374 8.2 12.01/19/2005 9:23 AM 8.4 820 8.0 11.62/2/2005 10:09 AM 10.4 748 8.0 10.62/16/2005 9:50 AM 12.0 290 8.0 9.53/9/2005 9:53 AM 16.4 675 8.3 10.13/22/2005 10:48 AM 14.9 704 8.2 10.04/6/2005 9:33 AM 16.6 380 8.0 9.54/20/2005 11:01 AM 16.1 742 8.9 8.94/21/2005 11:10 AM 17.2 785 8.0 9.75/4/2005 10:05 AM 19.1 741 8.1 8.5
7
F1: 541STC019 – Orestimba Creek @ River Road continued…
Date TimeTemp (ºC)
Field SC (umhos) pH
Dissolved Oxygen (mg/L)
Turbidity (ntu)
5/18/2005 9:31 AM 18.3 602 8.0 8.86/8/2005 11:51 AM 19.2 461 8.0 9.36/22/2005 10:14 AM 19.9 516 8.0 8.27/6/2005 9:32 AM 23.0 513 7.9 7.77/20/2005 9:11 AM 24.9 572 7.9 6.78/3/2005 9:47 AM 22.9 626 7.9 8.58/17/2005 9:08 AM 22.8 582 7.7 7.19/7/2005 10:03 AM 19.5 769 7.8 8.29/21/2005 10:18 AM 19.2 812 7.6 8.9
Count 197 197 197 176 52Min 3.6 8 7.3 6.0 14.1Max 25.8 1290 8.9 17.2 810Mean 16.6 723 8.0 9.9 190Geo Mean 15.6 692 8.0 9.8 143Median 17.3 720 8.0 9.7 165Quartile 1 12.7 627 7.9 8.7 84.4Quartile 3 20.9 820 8.1 10.8 258NOTE: For values reported as < (less than), half the detection limit was used.
NA = Data not applicableINA = Site was inaccessibleDRY = Site had no flow
8
F1: 541STC019 – Orestimba Creek @ River Road continued…
DateTSS
(mg/L)TOC
(mg/L)Total Coli
MPNE. coli MPN
10/26/2000 120 2.611/30/2000 19 1.112/28/2000 36 1.81/25/2001 36 3.62/22/2001 NA 2.13/29/2001 73 <14/26/2001 3.05/31/2001 130 116/28/2001 360 9.57/26/2001 6.98/30/2001 190 109/27/2001 68 14
10/25/2001 7.511/29/2001 NA12/27/2001 411/31/2002 NA2/17/2002 482/17/2002 382/18/2002 492/18/2002 462/28/2002 6.33/7/2002 1703/7/2002 1303/8/2002 1153/8/2002 793/9/2002 103/9/2002 103/11/2002 843/11/2002 533/28/2002 4.84/25/2002 NA5/30/2002 5.76/20/2002 2.58/1/2002 >2419.6 6139/26/2002 NA
10/17/2002 >2419.6 48810/31/2002 2.711/21/2002 2.512/19/2002 8.01/16/2003 NA NA3/27/2003 1.9
9
F1: 541STC019 – Orestimba Creek @ River Road continued…
DateTSS
(mg/L)TOC
(mg/L)Total Coli
MPNE. coli MPN
4/24/2003 4.5 >2419.6 5175/29/2003 4.56/26/2003 3.47/31/2003 >2419.6 9808/28/2003 >2419.6 12039/25/2003 >2419.6 411
10/30/2003 >2419.6 9311/20/2003 DRY DRY1/29/2004 >2419.6 932/26/2004 >2419.6 24203/24/2004 >2419.6 1854/29/2004 >2419.6 5795/27/2004 >2419.6 9216/24/2004 >2419.6 6137/29/2004 >2419.6 3878/26/2004 >2419.6 9219/30/2004 >2419.6 613
10/28/2004 4.5 >2419.6 12411/3/2004 >2419.6 113
11/17/2004 NA 5.8 >2419.6 8812/8/2004 >2419.6 194
12/21/2004 39 4.6 >2419.6 3281/5/2005 >2419.6 3871/19/2005 63 5.0 >2419.6 962/2/2005 >2419.6 19862/16/2005 780 NA 1011 10113/9/2005 1553 403/22/2005 150 5.6 >2419.6 3654/6/2005 >2419.6 964/20/2005 280 5.7 >2419.6 1185/4/2005 >2419.6 9805/18/2005 250 4.2 >2419.6 10466/8/2005 >2419.6 649
10
11
DateTSS
(mg/L)TOC
(mg/L)Total Coli
MPNE. coli MPN
6/22/2005 190 NA >2419.6 8667/6/2005 >2419.6 6497/20/2005 450 2.6 >2419.6 11208/3/2005 >2419.6 3878/17/2005 140 5.1 >2419.6 24209/7/2005 >2419.6 1799/21/2005 28 NA >2419.6 1203
Count 32 33 39 39Min 10 0.5 1011 40Max 780 14 2420 2420Mean 134 5.0 NA NAGeo Mean 81 4.1 2340 418Median 76 4.5 2420 517Quartile 1 41 2.6 2420 182Quartile 3 155 5.8 2420 951NOT
NA =INA =DRY
F1: 541STC019 – Orestimba Creek @ River Road continued…
E: For values reported as < (less than), half the detection limit was used For values reported as > (greater than), 2420 was used
Data not applicable Site was inaccessible
= Site had no flow
F1: 541STC019 – Orestimba Creek @ River Road continued…
DateNitrate (mg/L)
Nitrate-N (mg/L)
TKN (mg/L)
Ammonia-N (mg/L)
Phosphorus (mg/L)
Ortho-phosphate-
P (mg/L)
Potassium (mg/L)
BOD 5-Day (mg/L)
BOD 10-Day (mg/L)
10/26/2000 4.3 <2 NA <1 5.2 1.2 1.811/30/2000 NA <2 0.1 NA NA 0.6 112/28/2000 5.2 <2 <0.1 <1 5.7 0.5 0.91/25/2001 7.1 <2 <0.1 <1 6.3 0.9 1.72/22/2001 11 <2 0.1 <1 6.8 0.9 2.13/29/2001 8.2 <2 0.2 <1 7.8 2.3 44/26/2001 9.2 <2 <1 0.4 <1 6 1.9 2.85/31/2001 19 <1.0 0.3 NA 9.4 4 6.56/28/2001 16 <2 0.4 <1 7.3 1.1 1.78/30/2001 20 <2 0.4 <1 7.99/27/2001 11 <2 0.2 <1 9.2
10/25/2001 0.8 1.611/29/2001 NA NA NA 0.1 6.6 1.3 212/27/2001 1 2.51/31/2002 1.2 1.72/28/2002 1.3 2.14/25/2002 2.2 3.65/30/2002 4 6.26/20/2002 1.1 1.88/29/2002 3 8.49/26/2002 1.6 2.6
10/31/2002 1 1.511/21/2002 1.7 3.212/19/2002 1.3 1.71/30/2003 2.7 4.3
12
F1: 541STC019 – Orestimba Creek @ River Road continued…
DateNitrate (mg/L)
Nitrate-N (mg/L)
TKN (mg/L)
Ammonia-N (mg/L)
Phosphorus (mg/L)
Ortho-phosphate-
P (mg/L)
Potassium (mg/L)
BOD 5-Day (mg/L)
BOD 10-Day (mg/L)
Count 10 NA 11 1 10 10 11 23 23Min 4.3 NA 0.5 0.5 0.1 0.1 5.2 0.5 0.9Max 20.0 NA 1.0 0.5 0.4 0.5 9.4 4.0 8.4Mean 11.1 NA 1.0 0.5 0.2 0.5 7.1 1.6 2.9Geo Mean 9.9 NA 0.9 0.5 0.2 0.4 7.0 1.4 2.4Median 10.1 NA 1.0 0.5 0.2 0.5 6.8 1.3 2.1Quartile 1 7.4 NA 1.0 0.5 0.1 0.5 6.2 1.0 1.7Quartile 3 14.8 NA 1.0 0.5 0.4 0.5 7.9 2.1 3.4NOTE: For values reported as < (less than), half the detection limit was used.
NA = Data not applicableINA = Site was inaccessibleDRY = Site had no flow
13
F1: 541STC019 – Orestimba Creek @ River Road continued…
DateHardness
(mg/L)
Total Arsenic (ug/L)
Total Cadmium
(ug/L)
Total Chromium
(ug/L)
Total Copper (ug/L)
Total Lead (ug/L)
Total Nickel (ug/L)
Total Zinc (ug/L)
Total Mercury (ug/L)
10/26/2000 130 7 6.4 <5 11.0 1211/30/2000 140 2.7 2.5 <5 <5 8.612/28/2000 140 3.4 4.3 <5 6.6 6.41/25/2001 170 3 4.3 <5 <5 4.42/22/2001 180 2.8 6.1 <5 6.8 9.23/29/2001 220 8.2 6.7 <5 14.0 114/26/2001 180 12 10 <5 16.0 195/31/2001 300 10 9.1 <5 14.0 146/28/2001 290 NA <1 21 18 6.5 25.0 42 <0.27/26/2001 NA NA 21 16 6.1 28.0 37 NA8/30/2001 280 4.1 <1 15 11 <5 18.0 219/27/2001 220 <4 <1 1.1 3.2 <5 <5 <2 <0.2
10/25/2001 150 <4 <0.1 4.7 5.4 <5 7.9 8.5 <0.211/29/2001 140 <4 <0.1 4.2 3.8 <5 <5 6.7 <0.212/27/2001 <4 <0.1 6.7 6.9 <5 9.3 11 <0.21/31/2002 <4.0 <0.1 3.7 NA <5.0 <5.0 <2.0 <0.22/28/2002 <4.0 <0.1 5 6.9 <5.0 7.6 7.2 <0.23/28/2002 <4.0 <0.1 4.4 5 <5.0 8.0 6.3 <0.24/25/2002 <4.0 <0.1 <1.0 4.1 <5.0 <5.0 <2.0 <0.25/30/2002 5 <0.1 49 31 12 91.0 65 <0.26/20/2002 290 <4.0 <0.1 17 13 <5.0 21.0 23 <0.29/26/2002 250 4.4 <0.1 13 NA <5.0 18.0 20 <0.2
10/31/2002 160 <4.0 <0.1 6 6.3 <5.0 7.3 8.9 <0.211/21/2002 200 <4.0 <0.1 6.3 6.5 <5.0 9.2 9.1 <0.23/27/2003 310 <4.0 NA 5.9 3.7 <5.0 <5.0 3.0 <0.24/24/2003 240 <4.0 <0.1 NA NA NA 25.0 22 <0.25/29/2003 270 <4.0 0.2 22 16 5.7 28.0 29 <0.26/26/2003 290 <4.0 <0.1 11 7.4 <5.0 12.0 13 <0.2
14
F1: 541STC019 – Orestimba Creek @ River Road continued…
DateHardness
(mg/L)
Total Arsenic (ug/L)
Total Cadmium
(ug/L)
Total Chromium
(ug/L)
Total Copper (ug/L)
Total Lead (ug/L)
Total Nickel (ug/L)
Total Zinc (ug/L)
Total Mercury (ug/L)
Count 21 18 18 27 25 27 28 28 18Min 130.0 2.0 0.1 0.5 2.5 2.5 2.5 1.0 0.1Max 310.0 5.0 0.5 49.0 31.0 12.0 91.0 65.0 0.1Mean 216.7 2.4 0.1 9.9 8.5 3.3 14.3 15.0 0.1Geo Mean 207.8 2.3 0.1 6.6 7.1 2.9 9.2 9.7 0.1Median 220.0 2.0 0.1 6.3 6.5 2.5 9.3 10.1 0.1Quartile 1 160.0 2.0 0.1 4.0 4.3 2.5 5.6 6.6 0.1Quartile 3 280.0 2.0 0.1 12.5 10.0 2.5 18.0 20.3 0.1NOTE: For values reported as < (less than), half the detection limit was used.
NA = Data not applicableINA = Site was inaccessibleDRY = Site had no flow
15
F1: 541STC019 – Orestimba Creek @ River Road continued…
DateHardness
(mg/L)
Dissolved Arsenic (ug/L)
Dissolved Cadmium
(ug/L)
Dissolved Chromium
(ug/L)
Dissolved Copper (ug/L)
Dissolved Lead (ug/L)
Dissolved Nickel (ug/L)
Dissolved Zinc
(ug/L)
Dissolved Mercury (ug/L)
10/26/2000 130 <1 2.1 <5 <5 2.311/30/2000 140 <1 1.6 <5 <5 <212/28/2000 140 <1 1.1 <5 <5 <21/25/2001 170 <1 1.6 <5 <5 <22/22/2001 180 <1 2.8 <5 <5 <23/29/2001 220 <1 3.4 <5 <5 <24/26/2001 180 <1 1.8 <5 <5 <25/31/2001 300 3.1 3 <5 <5 <26/28/2001 290 NA <1 2.9 <1 <5 <5 <2 <0.27/26/2001 NA NA NA NA NA NA NA NA8/30/2001 280 2.2 <1 4.2 4.9 <5 <5 169/27/2001 220 <4 <1 1.3 2.3 <5 <5 <2 <0.2
10/25/2001 150 <4 <0.1 <1 1.9 <5 <5 <2 <0.211/29/2001 140 <4 <0.1 <1 3 <5 <5 4.5 <0.212/27/2001 <4 <0.1 <1 2.1 <5 <5 3.4 <0.21/31/2002 <4.0 <0.1 2.6 NA <5.0 <5.0 <2.0 <0.22/28/2002 <4.0 <0.1 <1.0 3.1 <5.0 <5.0 4.7 <0.23/28/2002 <4.0 <0.1 1.5 2.9 <5.0 <5.0 3.7 <0.24/25/2002 4.1 <0.1 2.6 3 <5.0 <5.0 NA <0.25/30/2002 <4.0 <0.1 1.6 4 <5.0 53 <2.0 <0.26/20/2002 290 <4.0 <0.1 2.3 1.9 <5.0 <5.0 <2.0 <0.29/26/2002 250 <4.0 <0.1 1.2 3.2 <5.0 <5.0 <2.0 <0.2
10/31/2002 160 <4.0 <0.1 1.3 2.3 <5.0 <5.0 <2.0 <0.211/21/2002 200 <4.0 <0.1 <1.0 <1.0 <5.0 <5.0 <2.0 <0.2
16
F1: 541STC019 – Orestimba Creek @ River Road continued…
DateHardness
(mg/L)
Dissolved Arsenic (ug/L)
Dissolved Cadmium
(ug/L)
Dissolved Chromium
(ug/L)
Dissolved Copper (ug/L)
Dissolved Lead (ug/L)
Dissolved Nickel (ug/L)
Dissolved Zinc
(ug/L)
Dissolved Mercury (ug/L)
Count 17 14 15 23 22 23 23 22 14Min 130.0 2.0 0.1 0.5 0.5 2.5 2.5 1.0 0.1Max 300.0 4.1 0.5 4.2 4.9 2.5 53.0 16.0 0.1Mean 202.4 2.2 0.1 1.3 2.4 2.5 4.7 2.3 0.1Geo Mean 194.4 2.1 0.1 1.0 2.1 2.5 2.9 1.5 0.1Median 180.0 2.0 0.1 0.5 2.3 2.5 2.5 1.0 0.1Quartile 1 150.0 2.0 0.1 0.5 1.8 2.5 2.5 1.0 0.1Quartile 3 250.0 2.0 0.1 2.0 3.0 2.5 2.5 2.0 0.1NOTE: For values reported as < (less than), half the detection limit was used.
NA = Data not applicableINA = Site was inaccessibleDRY = Site had no flow
17
18
F1: 541STC019 – Orestimba Creek @ River Road continued…
DateChloride (mg/L)
Sulfate (mg/L)
Calcium (mg/L)
Magnesium (mg/L)
TDS (mg/L)
Carbonate (mg/L)
Bicarbonate (mg/L)
Total Alkalinity
(mg/L)Sodium (mg/L)
10/26/2000 77 54 24 16 320 <1 110 90 6011/30/2000 75 53 28 17 350 <1 110 90 5912/28/2000 97 57 27 17 330 <1 110 90 711/25/2001 120 97 33 21 430 <1 130 110 942/22/2001 96 100 36 20 440 <1 120 97 873/29/2001 86 130 46 26 520 <1 150 120 864/26/2001 89 37 22 410 <1 110 110 625/31/2001 74 120 64 34 550 <1 170 170 646/28/2001 60 150 60 35 420 <1 190 160 568/30/2001 110 91 56 34 550 <1 210 170 859/27/2001 NA 74 42 28 500 <1 NA NA 89
10/25/2001 120 46 27 19 380 <1 120 NA 7911/29/2001 100 59 27 18 380 <1 110 94 753/27/2003 91 120 66 354/24/2003 90 110 50 275/29/2003 70 110 56 316/26/2003 53 120 63 33
Count 15 17 17 17 13 13 12 11 13Min 53 46 24 16 320 0.5 110 90 56Max 120 150 66 35 550 0.5 210 170 94Mean 88 93 44 25 430 0.5 140 120 74Geo Mean 86 88 41 25 420 0.5 130 120 73Median 90 97 42 26 420 0.5 120 110 75Quartile 1 75 59 28 19 380 0.5 110 92 62Quartile 3 99 120 56 33 500 0.5 160 140 86NOTE: For values reported as < (less than), half the detection limit was used.
NA = Data not applicableINA = Site was inaccessibleDRY = Site had no flow
F1: 541STC019 – Orestimba Creek @ River Road continued…
Date Result Control Result Control
Result (million/m
l)
Control (million/
ml)MDD (%)
10/26/2000 100 100 NA NA6/18/2001 100 100 100 90
11/17/2004 100 100 100 10012/21/2004 100 100 100 1001/19/2005 100 100 100 1002/16/2005 100 100 100 1003/22/2005 95 100 100 1004/2/2005 100 97.5 100 100
5/18/2005 97.5 97.5 0* 1006/22/2005 97.5 100 100 1007/20/2005 100 100 100 1008/17/2005 100 97.5 100 1009/21/2005 100 100 100 100
Count 13 13 12 12 N/A N/A N/A
* Significantly reduced from the lab control.** Significantly greater than the lab control.^ Fish were from a "forced hatch," duplicate failed QA.1 Duplicate sample for the set was low - 77% recovery.
3 Samples qualified, but duplicate sample recovery for the set was high - 126% (53.8%/42.5%)NA = Data not applicableINA = Site was inaccessibleDRY = Site had no flow
2 Testing for the Fathead minnow was initiated when samples were approx. 48h old due to untimely shipping of fish by fish supplier.
96h Acute Fathead Minnow
(% Survival)
48h Acute Ceriodaphnia Dubia
(% Survival) Algae Cell Growth
19
F2: 541STC515 – Salado Creek at HWY 33 Station Code:541STC515
Location: Latitude 37.48139, Longitude -121.13556
Date TimeTemp (ºC)
Field SC (umhos) pH
Dissolved Oxygen (mg/L)
Turbidity (ntu)
10/24/2000 2:35 PM 20.0 622 7.711/29/2000 10:30 AM 8.8 1140 6.612/27/2000 10:20 AM 5.1 1420 7.41/24/2001 10:00 AM 10.5 787 7.72/21/2001 10:50 AM 14.0 787 7.83/28/2001 12:25 PM 20.8 969 8.24/25/2001 10:10 AM 21.6 1010 8.05/30/2001 11:45 AM 23.5 843 7.76/27/2001 11:08 AM 20.9 971 8.1 10.07/25/2001 11:27 AM 23.6 922 8.2 8.58/29/2001 12:21 PM 25.3 699 8.0 8.49/26/2001 10:43 AM 19.1 1020 8.2 9.5
10/24/2001 11:46 AM 13.4 1250 8.4 12.911/28/2001 10:30 AM 11.6 830 8.1 11.112/26/2001 10:45 AM 11.7 832 8.5 12.11/30/2002 10:53 AM 7.9 1040 8.3 13.12/27/2002 10:15 AM 14.8 1460 8.1 11.43/27/2002 10:03 AM 13.0 570 7.7 10.24/30/2002 10:47 AM 15.8 841 8.3 11.85/29/2002 10:25 AM 21.7 898 8.0 8.46/19/2002 10:12 AM 20.8 543 7.8 7.77/30/2002 10:35 AM 22.3 824 8.3 8.4 43.58/28/2002 11:00 AM 25.2 762 8.6 NA9/25/2002 11:33 AM 21.7 674 8.3 9.1
10/15/2002 10:05 AM 16.4 811 7.9 9.4 NA10/30/2002 10:23 AM 14.7 714 7.4 10.111/20/2002 10:18 AM 15.1 1030 8.2 11.512/18/2002 9:55 AM 9.7 1250 8.1 11.1 19901/14/2003 12:28 PM 13.0 1450 8.2 11.1 1111/29/2003 10:37 AM 11.3 1320 8.8 14.3 19.13/25/2003 9:40 AM 15.0 741 8.2 11.5 19.24/24/2003 1:19 PM 15.9 454 8.3 10.4 2485/29/2003 12:20 PM 25.4 759 8.1 8.7 33.66/26/2003 11:51 AM 24.5 359 8.4 8.8 27.47/31/2003 12:35 PM INA INA INA INA INA8/28/2003 12:42 PM 22.7 684 8.3 10.6 6309/25/2003 12:40 PM 21.2 732 8.5 9.3 695
10/30/2003 12:32 PM 18.8 1180 8.4 9.1 20011/20/2003 12:41 PM 15.3 1450 8.6 14.9 14.4
20
F2: 541STC515 – Salado Creek at HWY 33 continued…
Date TimeTemp (ºC)
Field SC (umhos) pH
Dissolved Oxygen (mg/L)
Turbidity (ntu)
1/29/2004 12:20 PM 12.5 996 8.4 14.4 24.62/26/2004 11:53 AM 11.4 648 8.2 11.4 NA3/24/2004 12:15 PM 18.6 498 9.0 9.6 NA4/29/2004 12:43 PM 17.3 622 8.3 10.3 325/27/2004 12:41 PM 23.5 994 8.7 9.5 66.46/24/2004 1:11 PM 26.0 736 8.4 10.5 NA7/29/2004 11:57 AM 23.8 496 8.7 9.68/26/2004 12:46 PM 23.3 1020 8.7 9.19/30/2004 12:00 PM 19.5 1220 8.3 9.5
10/28/2004 12:28 PM 17.1 1800 8.0 9.411/3/2004 11:58 AM 16.7 527 8.2 6.0
11/17/2004 11:11 AM 16.7 1440 8.4 11.312/8/2004 9:47 AM 12.4 315 8.2 11.6
12/21/2004 9:34 AM 13.7 1020 8.4 11.61/5/2005 10:03 AM 8.9 1930 8.1 10.71/19/2005 9:48 AM 9.0 1320 8.2 10.92/2/2005 11:02 AM 10.5 3860 8.3 10.82/16/2005 10:18 AM 12.0 398 7.9 9.53/9/2005 10:11 AM 14.1 4160 8.3 11.83/22/2005 11:19 AM 14.3 778 8.2 10.24/6/2005 10:18 AM 15.2 1070 8.2 10.74/20/2005 12:00 PM 17.7 874 8.2 8.75/4/2005 10:46 AM 18.8 734 8.4 9.55/18/2005 11:41 AM 17.4 907 8.3 10.86/8/2005 12:45 PM 20.5 557 8.7 10.16/22/2005 11:40 AM 22.1 798 8.3 8.77/6/2005 10:25 AM 23.0 434 7.9 8.17/20/2005 10:19 AM 23.4 493 7.9 7.28/3/2005 10:40 AM 23.4 607 8.3 8.78/17/2005 10:00 AM 23.4 533 8.4 8.89/7/2005 10:43 AM 20.7 725 8.4 8.89/21/2005 11:25 AM 21.1 123 8.2 10.9
Count 70.0 70 70.0 61.0 15Min 5.1 123 6.6 6.0 14.4Max 26.0 4160 9.0 14.9 1990Mean 17.4 961 8.2 10.2 277Geo Mean 16.6 838 8.2 10.1 82.2Median 17.4 827 8.2 10.1 43.5Quartile 1 13.5 655 8.1 9.1 26.0Quartile 3 21.7 1040 8.4 11.1 224NOTE: For values reported as < (less than), half the detection limit was used.
NA = Data not applicableINA = Site was inaccessibleDRY = Site had no flow
21
F2: 541STC515 – Salado Creek at HWY 33 continued…
DateTSS
(mg/L)TOC
(mg/L)Total Coli
MPNE. coli MPN
10/24/2000 83 3.211/29/2000 NA <112/27/2000 <6 4.11/24/2001 7 202/21/2001 6 NA3/28/2001 210 NA4/25/2001 37 3.85/30/2001 94 6.36/27/2001 11 7.17/25/2001 4.78/29/2001 NA 6.29/26/2001 NA 11
11/28/2001 NA12/26/2001 6.03/27/2002 NA4/30/2002 NA5/29/2002 3.86/19/2002 NA7/30/2002 >2419.6 749/25/2002 NA
10/15/2002 >2419.6 17210/30/2002 2.611/20/2002 1.912/18/2002 32001/14/2003 >2419.6 8163/25/2003 3.44/24/2003 NA >2419.6 14145/29/2003 5.86/26/2003 3.17/31/2003 INA INA8/28/2003 >2419.6 709/25/2003 >2419.6 >2419.6
10/30/2003 >2419.6 >2419.611/20/2003 >2419.6 591/29/2004 >2419.6 2762/26/2004 >2419.6 >2419.63/24/2004 >2419.6 1574/29/2004 >2419.6 585/27/2004 >2419.6 1406/24/2004 >2419.6 2497/29/2004 NA NA >2419.6 4118/26/2004 NA NA >2419.6 488
22
23
DateTSS
(mg/L)TOC
(mg/L)Total Coli
MPNE. coli MPN
9/30/2004 NA NA >2419.6 8410/28/2004 NA 4.1 145 211/3/2004 500 30 >2419.6 >2419.6
11/17/2004 NA 2.2 2420 6212/8/2004 97 12 >2419.6 >2419.6
12/21/2004 5 1.0 1120 201/5/2005 7 9.3 >2419.6 7701/19/2005 3 1.5 411 132/2/2005 28 9.5 >2419.6 5482/16/2005 1500 NA >2419.6 >2419.63/9/2005 2 11 >2419.6 4163/22/2005 100 7.6 >2419.6 >2419.64/6/2005 10 3.1 >2419.6 5794/20/2005 41 6.6 >2419.6 1625/4/2005 76 4.4 >2419.6 1045/18/2005 5 3.6 >2419.6 1626/6/27/67/28/38/19/9/2
CounMin
F2: 541STC515 – Salado Creek at HWY 33 continued…
8/2005 14 NA >2419.6 1052/2005 37 NA >2419.6 140/2005 67 5.2 >2419.6 387
0/2005 35 4.0 >2419.6 387/2005 77 3.5 >2419.6 548
7/2005 42 3.3 >2419.6 6137/2005 100 3.1 >2419.6 6871/2005 36 NA >2419.6 1203
t 30 36 40 402 0.5 145 2
MaxMeaGeo
3200 30 2420 2420n 214 6.1 NA NA Mean 35 4.5 2117 288ian 37 4.1 2420 387rtile 1 8 3.2 2420 105rtile
MedQuaQua 3 91 6.7 2420 782
E: For values reported as < (less than), half the detection limit was used For values reported as > (greater than), 2420 was used
Data not applicable Site was inaccessible
= Site had no flow
NOT
NA =INA =DRY
F2: 541STC515 – Salado Creek at HWY 33 continued…
DateNitrate (mg/L)
Nitrate-N (mg/L)
TKN (mg/L)
Ammonia-N (mg/L)
Phosphorus (mg/L)
Ortho-phosphate-
P (mg/L)
Potassium (mg/L)
BOD 5-Day (mg/L)
BOD 10-Day (mg/L)
10/24/2000 6.9 <2 0.2 <1 6.6 0.8 1.311/29/2000 23 NA 0.4 <1 9 1.3 2.212/27/2000 9.9 <2 0.1 <1 10 1.8 2.91/24/2001 6.8 2.1 0.2 <1 7.9 8.2 14.92/21/2001 2.9 <2 0.2 <1 6.1 1.5 2.93/28/2001 7.9 <2 0.3 <1 7.9 2.2 3.54/25/2001 15 <2 0.1 <1 6.8 1.7 3.55/30/2001 11 <2 0.2 <1 5 1.9 3.16/27/2001 17 <2 0.1 <1 4.8 0.9 1.18/29/2001 4.6 <2 0.4 <1 NA9/26/2001 19 <2 0.4 <1 11
10/24/2001 9.1 <2 0.2 <1 12 1.7 3.111/28/2001 NA 1.4 NA 0.2 12 1.2 1.812/26/2001 2 2.81/30/2002 NA 1.3 0.1 0.1 7.3 1 1.62/27/2002 NA 0.6 0.2 0.2 NA 0.3 1.33/27/2002 NA 0.8 NA 0.1 3.9 1.1 2.24/30/2002 NA NA 0.1 0.1 NA 0.5 0.95/29/2002 NA 0.8 NA 0.1 5.3 1.9 36/19/2002 NA 1 0.2 NA 4.5 4.4 6.88/28/2002 NA 1 0.1 0.1 4.8 0.2 0.69/25/2002 NA NA 0.1 0.1 5.8 1.5 2.6
10/30/2002 NA NA <0.05 0.1 3.3 1 1.311/20/2002 NA 1 0.1 0.1 3.912/18/2002 NA 2.4 0.2 0.1 6.5 8.3 141/29/2003 NA NA 0.1 0.1 6.9 1.1 2.2
24
F2: 541STC515 – Salado Creek at HWY 33 continued…
DateNitrate (mg/L)
Nitrate-N (mg/L)
TKN (mg/L)
Ammonia-N (mg/L)
Phosphorus (mg/L)
Ortho-phosphate-
P (mg/L)
Potassium (mg/L)
BOD 5-Day (mg/L)
BOD 10-Day (mg/L)
Count 12 NA 20 NA 22 24 22 23 23Min 2.9 NA 0.6 NA 0.03 0.1 3.3 0.2 0.6Max 23.0 NA 2.4 NA 0.4 0.5 12.0 8.3 14.9Mean 11.1 NA 1.1 NA 0.2 0.3 6.9 2.0 3.5Geo Mean 9.5 NA 1.1 NA 0.2 0.2 6.4 1.4 2.5Median 9.5 NA 1.0 NA 0.2 0.4 6.6 1.5 2.6Quartile 1 6.9 NA 1.0 NA 0.1 0.1 4.9 1.0 1.5Quartile 3 15.5 NA 1.0 NA 0.2 0.5 7.9 1.9 3.1NOTE: For values reported as < (less than), half the detection limit was used.
NA = Data not applicableINA = Site was inaccessibleDRY = Site had no flow
25
F2: 541STC515 – Salado Creek at HWY 33 continued…
DateHardness
(mg/L)
Total Arsenic (ug/L)
Total Cadmium
(ug/L)
Total Chromium
(ug/L)
Total Copper (ug/L)
Total Lead (ug/L)
Total Nickel (ug/L)
Total Zinc (ug/L)
Total Mercury (ug/L)
10/24/2000 150 5.5 9.8 <5 7.4 1411/29/2000 320 16 16 5.2 18 3912/27/2000 430 9.6 3.7 <5 <5 <21/24/2001 170 13 16 <5 9.2 362/21/2001 220 1.1 3.5 <5 <5 <23/28/2001 230 9.7 13 <5 19 234/25/2001 270 5.9 5.2 <5 5.5 4.85/30/2001 200 6.2 5.2 <5 8.2 8.37/25/2001 NA 17 17 <5 17 328/29/2001 4.2 <1 12 20 5.3 18 299/26/2001 290 6.4 0.1 29 45 12 41 70 <0.2
10/24/2001 390 <4.0 <0.1 NA 6 <5.0 <5.0 4.0 <0.211/28/2001 210 <4.0 <0.1 3.5 1.8 <5.0 <5.0 4.5 <0.212/26/2001 200 <4 <0.1 1.8 2.9 <5 <5 4.0 <0.21/30/2002 290 <4 <0.1 5.7 3.8 <5 <5 <2 <0.23/27/2002 140 <4.0 <0.1 1.3 5.5 <5.0 5.8 6.9 <0.24/30/2002 230 <4.0 <0.1 4.1 1.6 <5.0 <5.0 <2.0 <0.25/29/2002 240 <4.0 <0.1 4.3 NA <5.0 5.8 2.6 <0.26/19/2002 160 <4.0 <0.1 5.9 9 <5.0 8.4 12 <0.29/25/2002 150 4.3 <0.1 13 NA 5.2 35 26 <0.2
10/30/2002 170 <4.0 <0.1 5.4 NA <5.0 13 8.1 <0.211/20/2002 260 <4.0 <0.1 6.2 3.3 <5.0 NA NA <0.23/25/2003 180 <4.0 <0.1 1.3 14 <5.0 <5.0 7.5 <0.24/24/2003 120 <4.0 <0.1 24 15 <5.0 75 27 <0.25/29/2003 190 <4.0 <0.1 2.8 4.1 <5.0 5.8 2.2 <0.26/26/2003 93 <4.0 <0.1 1.9 3.1 <5.0 <5.0 3.6 NA
26
F2: 541STC515 – Salado Creek at HWY 33 continued…
DateHardness
(mg/L)
Total Arsenic (ug/L)
Total Cadmium
(ug/L)
Total Chromium
(ug/L)
Total Copper (ug/L)
Total Lead (ug/L)
Total Nickel (ug/L)
Total Zinc (ug/L)
Total Mercury (ug/L)
Count 24 17 17 25 23 26 25 25 15Min 93.0 2.0 0.1 1.1 1.6 2.5 2.5 1.0 0.1Max 430.0 6.4 0.5 29.0 45.0 12.0 75.0 70.0 0.1Mean 221.0 2.5 0.1 8.2 9.8 3.2 12.6 14.7 0.1Geo Mean 207.7 2.3 0.1 5.7 6.8 2.9 7.2 7.4 0.1Median 205.0 2.0 0.1 5.9 5.5 2.5 5.8 7.5 0.1Quartile 1 167.5 2.0 0.1 3.5 3.6 2.5 2.5 3.6 0.1Quartile 3 262.5 2.0 0.1 12.0 14.5 2.5 17.0 26.0 0.1NOTE: For values reported as < (less than), half the detection limit was used.
NA = Data not applicableINA = Site was inaccessibleDRY = Site had no flow
27
F2: 541STC515 – Salado Creek at HWY 33 continued…
DateHardness
(mg/L)
Dissolved Arsenic (ug/L)
Dissolved Cadmium
(ug/L)
Dissolved Chromium
(ug/L)
Dissolved Copper (ug/L)
Dissolved Lead (ug/L)
Dissolved Nickel (ug/L)
Dissolved Zinc
(ug/L)
Dissolved Mercury (ug/L)
11/29/2000 320 2.8 1.1 <5 <5 <212/27/2000 430 9.3 3.7 <5 <5 <21/24/2001 170 7.1 8.3 <5 <5 3.32/21/2001 220 <1 3.1 <5 <5 <23/28/2001 230 <1 3.2 <5 <5 <24/25/2001 270 4.1 2.4 <5 <5 <25/30/2001 200 2.6 1.6 <5 <5 <28/29/2001 2.1 <1 <1 2.2 <5 <5 7.19/26/2001 290 <4 <0.1 3.7 2.9 <5 <5 <2 <0.2
10/24/2001 390 <4.0 <0.1 NA 5.6 <5.0 <5.0 <2.0 <0.211/28/2001 210 <4.0 <0.1 3.6 2.1 <5.0 <5.0 NA <0.212/26/2001 200 <4 <0.1 1.7 2.6 <5 <5 6.1 <0.21/30/2002 290 <4 <0.1 3.9 2.0 <5 <5 <2 <0.23/27/2002 140 <4.0 <0.1 <1.0 4.1 <5.0 <5.0 5.1 <0.24/30/2002 230 <4.0 <0.1 3.7 <1.0 <5.0 <5.0 <2.0 <0.25/29/2002 240 <4.0 <0.1 2.7 1.5 <5.0 <5.0 <2.0 <0.26/19/2002 160 <4.0 <0.1 2.9 4.7 <5.0 <5.0 6.7 <0.29/25/2002 150 <4.0 <0.1 <1.0 NA 10 18 <2.0 <0.2
10/30/2002 170 <4.0 <0.1 1.2 2.9 <5.0 <5.0 <2.0 <0.211/20/2002 260 <4.0 <0.1 4.1 1.3 <5.0 <5.0 <2.0 <0.2
Count 19 13 13 19 19 20 20 19 12Min 140.0 2.0 0.1 0.5 0.5 2.5 2.5 1.0 0.1Max 430.0 2.1 0.5 9.3 8.3 10.0 18.0 7.1 0.1Mean 240.5 2.0 0.1 2.9 2.9 2.9 3.3 2.2 0.1Geo Mean 229.6 2.0 0.1 2.0 2.5 2.7 2.8 1.6 0.1Median 230.0 2.0 0.1 2.8 2.6 2.5 2.5 1.0 0.1Quartile 1 185.0 2.0 0.1 0.9 1.8 2.5 2.5 1.0 0.1Quartile 3 280.0 2.0 0.1 3.8 3.5 2.5 2.5 2.2 0.1NOTE: For values reported as < (less than), half the detection limit was used.
NA = Data not applicableINA = Site was inaccessibleDRY = Site had no flow
28
F2: 541STC515 – Salado Creek at HWY 33 continued…
DateChloride (mg/L)
Sulfate (mg/L)
Calcium (mg/L)
Magnesium (mg/L)
TDS (mg/L)
Carbonate (mg/L)
Bicarbonate (mg/L)
Total Alkalinity
(mg/L)Sodium (mg/L)
10/24/2000 76 66 29 18 350 <1 120 90 6311/29/2000 150 140 50 47 660 <1 200 160 12012/27/2000 110 380 80 56 940 11 220 180 1501/24/2001 94 120 35 19 450 <1 110 90 932/21/2001 66 160 36 31 490 <1 120 100 763/28/2001 110 130 47 28 510 <1 150 130 1104/25/2001 110 NA 48 36 NA <1 130 130 945/30/2001 91 120 32 29 NA 4 122 126 946/27/2001 110 160 38 32 580 <1 180 150 1108/29/2001 110 NA NA NA 370 <1.0 110 99 809/26/2001 NA NA 46 42 NA <1 170 140 110
10/24/2001 150 250 73 51 870 <1 200 160 14011/28/2001 110 120 41 27 500 <1 150 120 8812/26/2001 100 130 39 25 490 24 140 120 871/30/2002 100 180 51 39 580 <1 200 160 1202/27/2002 150 330 72 69 NA <1.0 192 157 1403/27/2002 67 70 30 16 330 <1.0 120 95 604/30/2002 130 130 39 32 NA <1.0 110 90 815/29/2002 97 140 45 32 NA <1.0 140 110 1006/19/2002 66 71 28 22 NA <1.0 110 88 529/25/2002 120 47 25 21 NA <1.0 100 84 87
10/30/2002 110 67 28 24 410 <1.0 120 100 8411/20/2002 97 82 43 37 620 <1.0 130 100 1003/25/2003 88 110 37 214/24/2003 32 50 22 155/29/2003 96 110 37 236/26/2003 40 40 19 11
29
30
F2: 541STC515 – Salado Creek at HWY 33 continued…
DateChloride (mg/L)
Sulfate (mg/L)
Calcium (mg/L)
Magnesium (mg/L)
TDS (mg/L)
Carbonate (mg/L)
Bicarbonate (mg/L)
Total Alkalinity
(mg/L)Sodium (mg/L)
Count 26 24 26 26 15 23 23 23 23Min 32 40 19 11 330 0.5 100 84 52Max 150 380 80 69 940 24 220 180 150Mean 99 130 41 31 543 2.1 150 120 97Geo Mean 94 110 39 28 520 0.7 140 120 94Median 100 120 39 29 500 0.5 130 120 94Quartile 1 89 71 31 21 430 0.5 120 97 83Quartile 3 110 150 47 37 600 0.5 180 150 110NOTE: For values reported as < (less than), half the detection limit was used.
NA = Data not applicableINA = Site was inaccessibleDRY = Site had no flow
F2: 541STC515 – Salado Creek at HWY 33 continued…
Date Result Control Result Control
Result (million/m
l)
Control (million/
ml)MDD (%)
11/17/2004 100 100 100 10012/21/2004 95 100 100 1001/19/2005 100 100 100 1002/16/2005 100 100 100 1003/22/2005 95 100 100 1004/20/2005 100 97.5 100 1005/18/2005 97.5 97.5 100 1006/22/2005 100 100 100 1007/20/2005 100 100 100 1008/17/2005 97.5 97.5 100 1009/21/2005 100 100 100 100
Count 11 11 11 11 N/A N/A N/A
* Significantly reduced from the lab control.** Significantly greater than the lab control.^ Fish were from a "forced hatch," duplicate failed QA.1 Duplicate sample for the set was low - 77% recovery.
3 Samples qualified, but duplicate sample recovery for the set was high - 126% (53.8%/42.5%)NA = Data not applicableINA = Site was inaccessibleDRY = Site had no flow
2 Testing for the Fathead minnow was initiated when samples were approx. 48h old due to untimely shipping of fish by fish supplier.
96h Acute Fathead Minnow
(% Survival)
48h Acute Ceriodaphnia Dubia
(% Survival) Algae Cell Growth
31
F3: 541STC516 – Del Puerto Creek at Vineyard Avenue Station Code:541STC516
Location: Latitude 37.52139, Longitude -121.14861
Date TimeTemp (ºC)
Field SC (umhos) pH
Dissolved Oxygen (mg/L)
Turbidity (ntu)
10/24/2000 2:15 PM 20.6 594 8.011/29/2000 10:11 AM 9.3 1100 7.612/27/2000 10:30 AM 6.7 819 8.01/24/2001 DRY DRY DRY DRY2/7/2001 12:02 PM 8.5 637 8.12/21/2001 11:28 AM 12.0 1030 8.23/13/2001 12:18 PM 17.4 792 7.63/28/2001 11:50 AM 21.5 1280 7.94/18/2001 12:40 PM 21.3 956 8.34/25/2001 9:54 AM 20.4 669 7.95/15/2001 12:45 PM 23.8 572 7.95/30/2001 11:30 AM 24.7 1190 7.26/5/2001 9:23 AM 19.0 1350 8.1 8.16/19/2001 10:22 AM 24.3 1350 7.9 8.56/27/2001 10:45 AM 21.1 1130 7.8 8.07/25/2001 11:02 AM 25.0 988 8.1 8.38/14/2001 11:57 AM 21.7 1350 7.8 4.58/29/2001 12:05 PM 23.8 1020 7.9 6.49/26/2001 10:28 AM 18.0 690 7.3 7.3
10/24/2001 11:22 AM 12.5 743 8.1 11.111/28/2001 10:10 AM DRY DRY DRY DRY12/26/2001 10:35 AM DRY DRY DRY DRY1/30/2002 DRY DRY DRY DRY DRY2/27/2002 DRY DRY DRY DRY DRY3/27/2002 9:47 AM 13.2 1290 7.8 12.64/30/2002 10:33 AM 18.0 1090 8.2 11.05/29/2002 10:08 AM 21.8 1010 7.9 8.36/19/2002 9:53 AM 20.5 1090 7.8 6.87/30/2002 10:49 AM 21.9 771 8.2 7.1 16.88/28/2002 10:50 AM 23.8 907 7.8 NA9/25/2002 11:09 AM 20.9 1110 7.8 8.6
10/15/2002 10:21 AM 14.8 1430 7.6 8.5 NA10/30/2002 9:42 AM 12.0 801 7.6 10.911/20/2002 DRY DRY DRY DRY DRY12/18/2002 9:38 AM 7.3 835 8.3 11.2 67.61/14/2003 DRY DRY DRY DRY DRY DRY1/29/2003 DRY DRY DRY DRY DRY DRY3/25/2003 9:29 AM 14.0 464 8.1 11.5 1224/24/2003 1:38 PM 15.7 945 8.2 10.5 70.6
32
F3: 541STC516 – Del Puerto Creek at Vineyard Avenue continued…
Date TimeTemp (ºC)
Field SC (umhos) pH
Dissolved Oxygen (mg/L)
Turbidity (ntu)
5/29/2003 12:36 PM 26.2 1160 8.1 8.5 70.46/26/2003 12:06 PM 25.1 1070 8.5 9.1 1067/31/2003 12:52 PM 25.6 727 7.6 5.2 54.68/28/2003 12:50 PM DRY DRY DRY DRY DRY9/25/2003 12:53 PM 21.7 743 8.4 9.3 88.0
10/30/2003 12:44 PM 14.4 605 8.7 12.0 9.811/20/2003 1:03 PM 15.7 1860 8.2 9.9 37.31/29/2004 12:29 PM 12.9 1570 8.6 14.8 5.72/26/2004 12:04 PM 11.0 459 8.4 11.3 NA3/24/2004 12:29 PM 19.0 541 8.9 10.3 NA4/29/2004 1:01 PM 21.3 962 8.3 9.9 89.05/27/2004 12:58 PM 25.9 1210 8.7 9.2 2446/24/2004 1:23 PM 27.6 1160 8.0 6.9 NA7/29/2004 12:07 PM 24.0 930 7.9 7.58/26/2004 1:01 PM 25.4 1490 8.4 8.19/30/2004 12:13 PM 21.3 1440 8.2 9.8
10/28/2004 12:40 PM 12.2 576 8.7 12.011/2/2004 8:29 AM 9.7 563 7.9 14.1
11/16/2004 9:03 AM 13.4 421 7.7 9.212/8/2004 8:57 AM 9.7 1030 7.4 6.6
12/21/2004 7:59 AM 6.8 577 8.0 11.91/4/2005 8:22 AM 8.0 760 8.5 11.21/18/2005 8:28 AM 8.4 853 8.5 17.82/1/2005 8:36 AM DRY DRY DRY DRY2/15/2005 8:10 AM 11.4 207 8.2 13.53/8/2005 8:34 AM 12.3 780 8.5 11.53/23/2005 8:52 AM 12.1 669 8.5 12.64/5/2005 8:32 AM 13.5 356 8.4 10.64/19/2005 8:52 AM 11.6 664 7.7 10.95/3/2005 8:17 AM 16.8 557 7.9 10.05/17/2005 8:49 AM 18.3 471 7.8 9.16/8/2005 8:28 AM 18.2 378 7.7 8.36/21/2005 9:13 AM 19.0 749 8.1 8.97/6/2005 10:35 AM 22.6 917 7.8 7.77/19/2005 9:16 AM 22.9 817 7.9 6.68/2/2005 10:30 AM 23.6 436 7.8 6.88/16/2005 10:50 AM 22.6 726 8.0 8.09/6/2005 11:10 AM 21.7 376 7.9 9.19/20/2005 10:49 AM 19.4 640 8.0 10.3
33
F3: 541STC516 – Del Puerto Creek at Vineyard Avenue continued…
Date TimeTemp (ºC)
Field SC (umhos) pH
Dissolved Oxygen (mg/L)
Turbidity (ntu)
Count 68 68 68 56 13Min 6.7 207 7.2 4.5 5.7Max 27.6 1860 8.9 17.8 244Mean 17.7 874 8.0 9.6 75.5Geo Mean 16.7 808 8.0 9.3 51.0Median 19.0 818 8.0 9.2 70.4Quartile 1 12.5 629 7.8 8.1 37.3Quartile 3 22.1 1090 8.2 11.1 89.0NOTE: For values reported as < (less than), half the detection limit was used.
NA = Data not applicableINA = Site was inaccessibleDRY = Site had no flow
34
F3: 541STC516 – Del Puerto Creek at Vineyard Avenue continued…
DateTSS
(mg/L)TOC
(mg/L)Total Coli
MPNE. coli MPN
10/24/2000 38 3.711/29/2000 NA 2.112/27/2000 73 1.82/21/2001 8 NA3/28/2001 9 NA4/25/2001 38 4.85/30/2001 370 7.86/27/2001 150 9.17/25/2001 7.18/29/2001 NA 199/26/2001 NA 8.73/27/2002 NA4/30/2002 NA5/29/2002 4.66/19/2002 NA7/30/2002 >2419.6 5489/25/2002 NA
10/15/2002 >2419.6 >2419.610/30/2002 3.212/18/2002 7.01/14/2003 DRY DRY3/25/2003 3.04/24/2003 NA >2419.6 6495/29/2003 7.36/26/2003 5.27/31/2003 >2419.6 >2419.68/28/2003 DRY DRY9/25/2003 >2419.6 158
10/30/2003 >2419.6 >2419.611/20/2003 >2419.6 >2419.61/29/2004 1300 932/26/2004 >2419.6 >2419.63/24/2004 >2419.6 12034/29/2004 >2419.6 >2419.65/27/2004 >2419.6 17336/24/2004 >2419.6 24207/29/2004 NA NA >2419.6 >2419.68/26/2004 NA NA >2419.6 1949/30/2004 NA NA >2419.6 127
10/28/2004 NA 9.1 >2419.6 10111/2/2004 22 5.4 >2419.6 1986
11/16/2004 40 4.8 >2419.6 1553
35
F3: 541STC516 – Del Puerto Creek at Vineyard Avenue continued…
DateTSS
(mg/L)TOC
(mg/L)Total Coli
MPNE. coli MPN
12/8/2004 55 12 >2419.6 27612/21/2004 48 5.0 >2419.6 1921/4/2005 20 6.2 >2419.6 6491/18/2005 6 3.7 2420 3872/1/2005 DRY DRY DRY DRY2/15/2005 660 5.2 >2419.6 >2419.63/8/2005 8 3.0 1986 9213/23/2005 43 NA >2419.6 >2419.64/5/2005 60 5.3 >2419.6 24204/19/2005 180 NA >2419.6 >2419.65/3/2005 79 4.9 >2419.6 >2419.65/17/2005 77 NA >2419.6 >2419.66/8/2005 NA NA >2419.6 6496/21/2005 270 3.7 >2419.6 737/6/2005 43 5.0 >2419.6 >2419.67/19/2005 83 3.1 >2419.6 12038/2/2005 37 3.2 >2419.6 5488/16/2005 90 2.7 >2419.6 7279/6/2005 160 2.8 >2419.6 3659/20/2005 26 3.5 >2419.6 105
Count 27 33 38 38Min 6 1.8 1300 73Max 660 19 2420 2420Mean 100 5.5 NA NAGeo Mean 52 4.8 2368 819Median 48 4.9 2420 1203Quartile 1 32 3.2 2420 371Quartile 3 86.5 7 2420 2420NOTE: For values reported as < (less than), half the detection limit was used
For values reported as > (greater than), 2420 was used
NA = Data not applicableINA = Site was inaccessibleDRY = Site had no flow
36
37
F3: 541STC516 – Del Puerto Creek at Vineyard Avenue continued…
DateNitrate (mg/L)
Nitrate-N (mg/L)
TKN (mg/L)
Ammonia-N (mg/L)
Phosphorus (mg/L)
Ortho-phosphate-
P (mg/L)
Potassium (mg/L)
BOD 5-Day (mg/L)
BOD 10-Day (mg/L)
10/24/2000 7.5 <2 0.2 <1 4.5 0.9 1.711/29/2000 12 NA 0.1 <1 5.8 0.7 0.912/27/2000 8.5 <2 0.2 <1 6.0 1.4 2.22/21/2001 <2 <2 <0.1 <1 4.1 0.9 1.43/28/2001 38 <2 <0.1 <1 5.7 1.1 1.54/25/2001 7.4 <2 0.3 <1 9.7 3.4 6.25/30/2001 20 2.4 0.5 <1 11 6.9 12.06/27/2001 73 <2 0.4 <1 8.5 3.2 8.18/29/2001 37 3.8 0.3 <1 NA9/26/2001 4.7 <2 0.2 <1 6.9
10/24/2001 5.0 <2 0.1 <1 5.3 1.1 1.911/28/2001 NA 4.9 NA 3.5 163/27/2002 NA 0.9 NA 0.1 5.6 2.2 3.64/30/2002 NA NA 0.3 0.2 NA 1.5 2.55/29/2002 NA 1.4 NA 0.3 7.4 3.1 4.66/19/2002 NA 2.3 0.6 NA 6.1 6.2 11.58/28/2002 NA 16 0.3 0.2 5.7 1.9 8.29/25/2002 NA NA 0.3 0.3 7.5 1.2 2.0
10/30/2002 NA NA 0.2 0.1 2.8 0.9 1.512/18/2002 NA 0.7 0.1 0.1 2.6 0.9 1.3
Count 11 NA 16 NA 17 19 18 17 17Min 1.0 NA 0.7 NA 0.1 0.1 2.6 0.7 0.9Max 73.0 NA 16.0 NA 0.6 3.5 16.0 6.9 12.0Mean 19.5 NA 2.5 NA 0.2 0.5 6.7 2.2 4.2Geo Mean 11.0 NA 1.6 NA 0.2 0.4 6.1 1.7 3.0Median 8.5 NA 1.0 NA 0.2 0.5 5.9 1.4 2.2Quartile 1 6.2 NA 1.0 NA 0.1 0.3 5.4 0.9 1.5Quartile 3 28.5 NA 2.3 NA 0.3 0.5 7.5 3.1 6.2NOTE: For values reported as < (less than), half the detection limit was used.
NA = Data not applicableINA = Site was inaccessibleDRY = Site had no flow
38
F3: 541STC516 – Del Puerto Creek at Vineyard Avenue continued…
DateHardness
(mg/L)
Total Arsenic (ug/L)
Total Cadmium
(ug/L)
Total Chromium
(ug/L)
Total Copper (ug/L)
Total Lead (ug/L)
Total Nickel (ug/L)
Total Zinc (ug/L)
Total Mercury (ug/L)
10/24/2000 62 2.9 3.5 <5 6.8 4.711/29/2000 140 <1 1.1 <5 <5 <212/27/2000 97 4.2 5.4 <5 9.0 9.12/21/2001 160 1.3 2.8 <5 <5 <23/28/2001 170 7.4 2.4 <5 <5 <24/25/2001 NA 2.5 5.9 <5 7.2 4.75/30/2001 180 24 22 <5 48 337/25/2001 17 15 <5 37 608/29/2001 NA 2.8 <1 6.2 6.6 <5 15 8.59/26/2001 NA <4 <0.1 1.4 2.5 <5 <5 2.5 <0.2
10/24/2001 91 <4.0 <0.1 NA 2.0 <5.0 <5.0 <2.0 <0.23/27/2002 220 <4.0 <0.1 3.5 6.2 <5.0 12 7.7 <0.24/30/2002 170 <4.0 <0.1 1.4 2.0 <5.0 <5.0 <2.0 <0.25/29/2002 130 <4.0 <0.1 6.5 NA <5.0 15 <2.0 <0.26/19/2002 170 <4.0 <0.1 5.9 4.3 <5.0 6.1 <2.0 <0.29/25/2002 130 6.3 <0.1 2.9 NA <5.0 8.0 5.2 <0.2
10/30/2002 99 <4.0 <0.1 2.4 NA <5.0 6.4 2.6 <0.23/25/2003 55 <4.0 <0.1 6.0 6.8 <5.0 13 8.9 <0.24/24/2003 140 <4.0 <0.1 5.9 6.3 <5.0 13 8.6 <0.25/29/2003 170 <4.0 <0.1 5.7 6.4 <5.0 11 5.2 <0.26/26/2003 170 <4.0 <0.1 7.3 7.0 <5.0 15 10 NA
Count 17 13 13 20 18 21 21 21 11Min 55.0 2.0 0.1 0.5 1.1 2.5 2.5 1.0 0.1Max 220.0 6.3 0.5 24.0 22.0 2.5 48.0 60.0 0.1Mean 138.5 2.4 0.1 5.7 6.0 2.5 11.3 8.5 0.1Geo Mean 130.2 2.2 0.1 4.0 4.6 2.5 7.7 4.0 0.1Median 140.0 2.0 0.1 5.0 5.7 2.5 8.0 4.7 0.1Quartile 1 99.0 2.0 0.1 2.5 2.6 2.5 2.5 1.0 0.1Quartile 3 170 2.0 0.1 6.3 6.6 2.5 13 8.6 0.1NOTE: For values reported as < (less than), half the detection limit was used.
NA = Data not applicableINA = Site was inaccessibleDRY = Site had no flow
39
F3: 541STC516 – Del Puerto Creek at Vineyard Avenue continued…
DateHardness
(mg/L)
Dissolved Arsenic (ug/L)
Dissolved Cadmium
(ug/L)
Dissolved Chromium
(ug/L)
Dissolved Copper (ug/L)
Dissolved Lead (ug/L)
Dissolved Nickel (ug/L)
Dissolved Zinc
(ug/L)
Dissolved Mercury (ug/L)
11/29/2000 140 <1 <1 <5 <5 <212/27/2000 97 <1 1.2 <5 <5 <22/21/2001 160 <1 1.5 <5 <5 <23/28/2001 170 6.7 2.3 <5 <5 <24/25/2001 NA <1 3.5 <5 <5 2.65/30/2001 180 3.8 2.1 <5 <5 <28/29/2001 NA 2.2 <1 1.0 2.0 <5 <5 4.29/26/2001 NA <4 <0.1 <1 2.4 <5 <5 4.4 <0.2
10/24/2001 91 <4.0 <0.1 NA 1.4 <5.0 <5.0 <2.0 <0.23/27/2002 220 <4.0 <0.1 <1.0 3.4 <5.0 <5.0 3.0 <0.24/30/2002 170 <4.0 <0.1 1.4 1.4 <5.0 <5.0 <2.0 <0.25/29/2002 130 <4.0 <0.1 <1.0 2.5 <5.0 <5.0 <2.0 <0.26/19/2002 170 <4.0 <0.1 2.6 2.0 <5.0 <5.0 <2.0 <0.29/25/2002 130 5.5 <0.1 <1.0 NA <5.0 <5.0 <2.0 <0.2
10/30/2002 99 <4.0 <0.1 <1.0 2.1 <5.0 <5.0 <2.0 <0.2
Count 12 9 9 14 14 15 15 15 8Min 91.0 2.0 0.1 0.5 0.5 2.5 2.5 1.0 0.1Max 220.0 5.5 0.5 6.7 3.5 2.5 2.5 4.4 0.1Mean 146.4 2.4 0.1 1.4 2.0 2.5 2.5 1.7 0.1Geo Mean 141.5 2.3 0.1 0.9 1.8 2.5 2.5 1.4 0.1Median 150.0 2.0 0.1 0.5 2.1 2.5 2.5 1.0 0.1Quartile 1 122.3 2.0 0.1 0.5 1.4 2.5 2.5 1.0 0.1Quartile 3 170 2 0.05 1.3 2.4 2.5 2.5 1.8 0.1NOTE: For values reported as < (less than), half the detection limit was used.
NA = Data not applicableINA = Site was inaccessibleDRY = Site had no flow
40
41
F3: 541STC516 – Del Puerto Creek at Vineyard Avenue continued…
DateChloride (mg/L)
Sulfate (mg/L)
Calcium (mg/L)
Magnesium (mg/L)
TDS (mg/L)
Carbonate (mg/L)
Bicarbonate (mg/L)
Total Alkalinity
(mg/L)Sodium (mg/L)
10/24/2000 71 140 26 18 340 <1 120 100 6211/29/2000 150 250 47 32 650 2 170 140 13012/27/2000 110 180 38 22 480 <1 150 120 932/21/2001 35 470 33 94 600 28 460 380 723/28/2001 150 360 53 56 710 2 210 170 1204/25/2001 79 150 33 17 NA <1 82 82 675/30/2001 140 340 51 51 NA 4 168 172 1306/27/2001 120 320 59 42 670 <1 190 150 1108/29/2001 140 NA NA NA 520 <1.0 150 130 1009/26/2001 NA 170 22 28 NA <1 120 98 91
10/24/2001 110 170 30 22 440 <1 130 100 913/27/2002 170 290 60 34 770 <1.0 180 150 1604/30/2002 140 260 48 34 NA <1.0 160 130 1305/29/2002 120 260 48 33 NA <1.0 170 140 1206/19/2002 120 330 49 49 NA <1.0 210 170 1109/25/2002 160 230 45 28 NA <1.0 170 140 150
10/30/2002 110 190 34 26 470 <1.0 140 110 903/25/2003 51 130 26 164/24/2003 120 200 41 245/29/2003 140 280 51 386/26/2003 130 240 49 29
Count 20 20 20 20 10 17 17 17 17Min 35 130 22 16 340 0.5 82 82 62Max 170 470 60 94 770 28 460 380 160Mean 120 250 42 35 570 2.5 180 150 110Geo Mean 110 230 41 31 550 0.8 160 140 100Median 120 250 46 31 560 0.5 170 140 110Quartile 1 110 180 33 24 470 0.5 140 110 91Quartile 3 140 300 49.5 39 670 0.5 180 150 130NOTE: For values reported as < (less than), half the detection limit was used.
NA = Data not applicableINA = Site was inaccessibleDRY = Site had no flow
F3: 541STC516 – Del Puerto Creek at Vineyard Avenue continued…
Date Result Control Result Control
Result (million/m
l)
Control (million/
ml)MDD (%)
10/24/2000 100 100 NA NA2/21/2001 95 100 100 1003/28/2001 100 100 100 1004/25/2001 100 100 100 905/30/2001 100 95 100 1006/19/2001 100 100 100 906/27/2001 90 100 100 90
Count 7 7 6 6 N/A N/A N/A* Significantly reduced from the lab control.** Significantly greater than the lab control.^ Fish were from a "forced hatch," duplicate failed QA.1 Duplicate sample for the set was low - 77% recovery.
3 Samples qualified, but duplicate sample recovery for the set was high - 126% (53.8%/42.5%)NA = Data not applicableINA = Site was inaccessibleDRY = Site had no flow
2 Testing for the Fathead minnow was initiated when samples were approx. 48h old due to untimely shipping of fish by fish supplier.
96h Acute Fathead Minnow
(% Survival)
48h Acute Ceriodaphnia Dubia
(% Survival) Algae Cell Growth
42
F4: 541STC040 – Ingram Creek at River Road Station Code:541STC040
Location: Latitude 37.60028, Longitude -121.22417
Date TimeTemp (ºC)
Field SC (umhos) pH
Dissolved Oxygen (mg/L)
Turbidity (ntu)
10/24/2000 1:25 PM 16.9 745 6.511/29/2000 8:50 AM 11.9 1980 6.312/27/2000 12:00 PM 11.1 1940 7.91/24/2001 11:27 AM 13.4 2140 6.92/21/2001 1:30 PM 16.3 1960 7.73/28/2001 10:00 AM 18.7 1230 8.04/25/2001 8:25 AM 16.5 908 7.75/30/2001 9:40 AM 19.7 1000 7.56/5/2001 9:04 AM 18.0 1220 8.1 8.46/19/2001 9:55 AM 20.8 963 7.6 8.56/27/2001 8:59 AM 20.1 951 7.9 8.97/25/2001 9:39 AM 20.9 1060 7.9 8.68/29/2001 9:21 AM 21.4 1350 7.9 7.99/26/2001 9:02 AM 17.7 1370 7.9 9.3
10/24/2001 9:45 AM 15.6 1370 7.9 9.511/28/2001 9:18 AM 11.2 2050 8.0 10.312/26/2001 9:37 AM 11.4 2070 8.0 10.41/30/2002 9:24 AM 4.5 2190 8.1 13.22/27/2002 8:48 AM 11.3 1040 7.9 10.23/27/2002 8:35 AM 11.9 1020 8.3 11.24/30/2002 9:32 AM 13.9 1090 7.8 10.65/29/2002 8:53 AM 19.5 1110 7.9 9.46/19/2002 12:19 PM 25.2 1300 8.1 7.67/30/2002 11:09 AM 23.7 1070 8.0 8.0 8408/28/2002 9:36 AM 21.1 1220 8.0 NA9/25/2002 9:41 AM 18.2 963 7.8 9.0
10/15/2002 11:23 AM 16.3 1550 7.8 9.8 NA10/30/2002 8:45 AM 13.5 771 7.2 10.111/20/2002 8:39 AM 13.0 676 7.7 10.612/18/2002 8:38 AM 10.6 1650 7.4 7.7 1031/15/2003 10:33 AM 13.5 2110 8.0 9.6 57.61/29/2003 9:15 AM 11.9 2100 7.6 10.0 63.53/25/2003 8:34 AM 11.4 1390 7.6 10.7 1394/22/2003 11:22 AM 16.9 868 8.0 9.7 4755/27/2003 12:21 PM 22.4 1520 7.7 8.8 22.16/24/2003 8:43 AM 17.9 1030 8.3 10.8 10907/29/2003 10:06 AM 24.9 924 8.0 8.1 12.98/26/2003 11:31 AM 24.6 1030 8.0 7.7 11509/23/2003 11:15 AM 20.5 1430 7.8 9.5 274
43
F4: 541STC040 – Ingram Creek at River Road continued…
Date TimeTemp (ºC)
Field SC (umhos) pH
Dissolved Oxygen (mg/L)
Turbidity (ntu)
10/28/2003 1:07 PM 17.1 1100 8.1 13.0 3.611/18/2003 12:30 PM 16.0 1970 8.3 14.5 27.91/28/2004 10:30 AM DRY DRY DRY DRY DRY2/24/2004 11:20 AM 14.0 2130 8.0 9.5 24.03/24/2004 9:38 AM 13.4 2040 7.8 8.7 1954/28/2004 9:42 AM 17.9 791 7.8 11.4 5805/26/2004 11:35 AM 22.2 1460 8.0 8.3 19006/23/2004 10:28 AM 21.9 104 8.1 9.0 NA7/28/2004 11:11 AM 24.6 1150 8.1 9.4 NA8/25/2004 11:25 AM 23.0 912 8.0 8.2 NA9/29/2004 11:16 AM 17.3 1350 7.8 7.7 NA
10/27/2004 10:56 AM 13.4 802 7.9 8.711/2/2004 7:49 AM 13.5 823 7.8 12.9
11/16/2004 8:30 AM 14.3 709 7.5 10.012/8/2004 8:04 AM 12.2 1730 7.0 10.2
12/21/2004 7:31 AM 9.7 1760 7.7 9.31/4/2005 7:50 AM 11.5 1240 7.9 9.71/18/2005 7:57 AM 12.9 1810 7.7 13.52/1/2005 7:51 AM 10.9 1950 7.7 8.32/15/2005 7:53 AM 14.0 101 7.5 10.43/8/2005 7:59 AM 13.8 1970 7.8 9.63/23/2005 8:00 AM 12.6 1240 8.1 9.74/5/2005 8:03 AM 12.4 107 8.0 7.04/19/2005 8:05 AM 9.2 531 7.0 11.25/3/2005 7:45 AM 14.1 448 7.8 11.55/17/2005 7:58 AM 14.7 483 7.8 10.06/8/2005 8:12 AM 16.6 348 7.7 9.56/21/2005 8:13 AM 17.9 794 7.4 9.27/6/2005 10:18 AM 21.4 585 7.7 8.07/19/2005 8:53 AM 22.2 712 7.8 7.88/2/2005 10:11 AM 24.5 835 7.9 8.18/16/2005 10:30 AM 22.8 789 7.9 8.79/6/2005 10:47 AM 21.6 699 8.0 10.49/20/2005 9:57 AM 18.9 695 7.6 12.5
Count 72.0 72 72.0 63.0 17Min 4.5 101 6.3 7.0 3.6Max 25.2 2190 8.3 14.5 1900Mean 16.5 1202 7.8 9.7 409Geo Mean 15.8 1037 7.8 9.6 132Median 16.4 1095 7.9 9.5 139Quartile 1 13.0 800 7.7 8.6 27.9Quartile 3 20.6 1575 8.0 10.4 580NOTE: For values reported as < (less than), half the detection limit was used.
NA = Data not applicableINA = Site was inaccessibleDRY = Site had no flow
44
F4: 541STC040 – Ingram Creek at River Road continued…
DateTSS
(mg/L)TOC
(mg/L)Total Coli
MPNE. coli MPN
10/24/2000 1200 2.611/29/2000 NA <112/27/2000 <6 <11/24/2001 22 2.52/21/2001 7 NA3/28/2001 180 NA4/25/2001 570 4.15/30/2001 1000 9.86/27/2001 1600 107/25/2001 4.68/29/2001 NA 139/26/2001 NA 17
11/28/2001 NA12/26/2001 4.43/27/2002 NA4/30/2002 NA5/29/2002 3.26/19/2002 NA7/30/2002 >2419.6 3879/25/2002 NA
10/15/2002 >2419.6 8610/30/2002 2.811/20/2002 2.41/15/2003 >2419.6 383/25/2003 2.04/22/2003 3.9 >2419.6 1945/27/2003 NA6/24/2003 NA7/29/2003 >2419.6 6878/26/2003 >2419.6 5489/23/2003 >2419.6 173
10/28/2003 >2419.6 54811/18/2003 >2419.6 811/28/2004 DRY DRY2/24/2004 1553 663/24/2004 >2419.6 >2419.64/28/2004 >2419.6 1665/26/2004 >2419.6 3266/23/2004 6200 >2419.6 1587/28/2004 >2419.6 3088/25/2004 >2419.6 6919/29/2004 >2419.6 238
10/27/2004 8.4 >2419.6 39
45
46
DateTSS
(mg/L)TOC
(mg/L)Total Coli
MPNE. coli MPN
11/2/2004 >2419.6 11511/16/2004 14 4.8 >2419.6 21012/8/2004 >2419.6 1300
12/21/2004 9 3.7 >2419.6 291/4/2005 >2419.6 4351/18/2005 <1.0 3.6 1986 152/1/2005 >2419.6 92/15/2005 93 6.2 >2419.6 >2419.63/8/2005 >2419.6 1353/23/2005 140 NA 1011 6914/5/2005 >2419.6 1944/19/2005 860 NA >2419.6 1195/3/2005 691 2145/17/2005 1190 NA >2419.6 6136/8/2005 >2419.6 1576/21/2005 1300 5.1 >2419.6 2607/7/18/28/19/9/2
Coun
F4: 541STC040 – Ingram Creek at River Road continued…
6/2005 >2419.6 13009/2005 960 3.5 >2419.6 161/2005 810 >2419.6 135
6/2005 1100 4.6 >2419.6 1586/2005 >2419.6 2760/2005 400 10 >2419.6 435
t 21 25 40 400.5 0.5 691 9
620Min Max 0 17 2420 2420
n 84Mea 0 5.3 NA NA Mean 180 4.0 2258 214ian 57
GeoMed 0 4.1 2420 202
rtile 1 22 2.8 242Qua 0 131rtile 3 1100 6.2 2420 463E: For values reported as < (less than), half the detection limit was used For values reported as > (greater than), 2420 was used
Data not applicable Site was inaccessible
= Site had no flow
QuaNOT
NA =INA =DRY
F4: 541STC040 – Ingram Creek at River Road continued…
DateNitrate (mg/L)
Nitrate-N (mg/L)
TKN (mg/L)
Ammonia-N (mg/L)
Phosphorus (mg/L)
Ortho-phosphate-
P (mg/L)
Potassium (mg/L)
BOD 5-Day (mg/L)
BOD 10-Day (mg/L)
10/24/2000 12 2.2 1 <1 13 1.8 2.911/29/2000 65 NA <0.1 <1 2.9 0.3 0.412/27/2000 61 <2 <0.1 <1 3.1 0.6 0.71/24/2001 74 <2 <0.1 <1 3.1 0.6 0.82/21/2001 69 <2 <0.1 <1 2.7 0.6 1.23/28/2001 14 2.1 0.4 <1 9.1 4.8 7.74/25/2001 20 2.4 0.7 <1 12 3 4.95/30/2001 20 2.4 0.6 <1 14 4.4 76/27/2001 17 2.6 1.4 <1 15 2.4 4.28/29/2001 2.3 <2 0.5 <1 NA9/26/2001 25 <2 0.5 <1 11
10/24/2001 37 <2 0.2 <1 4.3 0.6 111/28/2001 NA 1.9 NA <0.03 4.8 0.2 0.312/26/2001 NA 0.1 <0.05 <0.03 1.3 0.4 0.71/30/2002 NA 3.3 <0.05 <0.03 2.5 0.2 0.32/27/2002 NA 1.1 0.1 <0.03 NA 1.7 3.33/27/2002 NA 1.8 NA 0.4 12 3.1 5.14/30/2002 NA NA 0.3 0.2 NA 2.6 4.35/29/2002 NA 1.4 NA 0.2 6.1 2 3.16/19/2002 NA 5.8 0.5 NA 7.8 7.6 15.88/28/2002 NA 3.5 0.5 0.2 5.2 3.2 6.39/25/2002 NA NA 0.2 0.2 6.2 1.7 3.2
10/30/2002 NA NA 0.1 0.1 2.8 0.7 111/20/2002 NA 0.9 0.1 0.1 3.412/18/2002 NA 4.2 0.5 0.3 8.5 7.4 10.51/29/2003 NA NA <0.05 <0.03 0.9 0.3 0.6
47
F4: 541STC040 – Ingram Creek at River Road continued…
DateNitrate (mg/L)
Nitrate-N (mg/L)
TKN (mg/L)
Ammonia-N (mg/L)
Phosphorus (mg/L)
Ortho-phosphate-
P (mg/L)
Potassium (mg/L)
BOD 5-Day (mg/L)
BOD 10-Day (mg/L)
Count 12 NA 21 NA 23 25 23 23 23Min 2.3 NA 0.1 NA 0.03 0.02 0.9 0.2 0.3Max 74.0 NA 5.8 NA 1.4 0.5 15.0 7.6 15.8Mean 34.7 NA 2.0 NA 0.3 0.3 6.6 2.2 3.7Geo Mean 24.6 NA 1.5 NA 0.2 0.2 5.1 1.3 2.1Median 22.5 NA 1.8 NA 0.2 0.4 5.2 1.7 3.1Quartile 1 16.3 NA 1.0 NA 0.1 0.1 3.0 0.6 0.8Quartile 3 62.0 NA 2.4 NA 0.5 0.5 10.1 3.1 5.0NOTE: For values reported as < (less than), half the detection limit was used.
NA = Data not applicableINA = Site was inaccessibleDRY = Site had no flow
48
F4: 541STC040 – Ingram Creek at River Road continued…
DateHardness
(mg/L)
Total Arsenic (ug/L)
Total Cadmium
(ug/L)
Total Chromium
(ug/L)
Total Copper (ug/L)
Total Lead (ug/L)
Total Nickel (ug/L)
Total Zinc (ug/L)
Total Mercury (ug/L)
10/24/2000 260 61 47 18 90 11011/29/2000 520 15 <1 <5 5.9 <212/27/2000 510 15 <1 <5 5.7 <21/24/2001 580 18 1 <5 7.3 <22/21/2001 520 18 <1 <5 6.4 <23/28/2001 290 12 12 <5 17 224/25/2001 270 38 34 12 62 735/30/2001 310 48 38 16 79 857/25/2001 38 31 13 64 738/29/2001 NA 4.2 <1 18 13 5.2 26 269/26/2001 360 <4 <0.1 10 13 <5 14 13 <0.2
10/24/2001 350 <4.0 <0.1 NA 1.2 <5.0 <5.0 <2.0 <0.211/28/2001 540 <4.0 <0.1 17 <1.0 <5.0 8.3 <2.0 <0.212/26/2001 560 4.3 <0.1 18 <1 <5 8.3 2.3 <0.21/30/2002 600 <4 <0.1 17 <1 <5 7 <2 <0.23/27/2002 260 7 <0.1 12 17 <5.0 21 24 <0.24/30/2002 290 <4.0 <0.1 9.5 2.5 <5.0 14 13 <0.25/29/2002 310 4.4 <0.1 33 NA 10 53 56 <0.26/19/2002 390 6.1 0.2 53 50 19 93 102 <0.29/25/2002 220 4.2 <0.1 7 NA <5.0 10 9.4 <0.2
10/30/2002 190 <4.0 <0.1 3.6 NA <5.0 <5.0 3.2 <0.211/20/2002 140 <4.0 <0.1 3.7 3.5 <5.0 NA NA <0.23/25/2003 380 <4.0 <0.1 14 5.9 <5.0 12 10 <0.24/22/2003 220 <4.0 <0.1 22 16 5.9 28 34 <0.25/27/2003 380 <4.0 <0.1 8.1 2.8 <5.0 53 <2.0 <0.26/24/2003 330 8 0.2 64 58 23 110 120 <0.2
49
F4: 541STC040 – Ingram Creek at River Road continued…
DateHardness
(mg/L)
Total Arsenic (ug/L)
Total Cadmium
(ug/L)
Total Chromium
(ug/L)
Total Copper (ug/L)
Total Lead (ug/L)
Total Nickel (ug/L)
Total Zinc (ug/L)
Total Mercury (ug/L)
Count 24 17 17 25 23 26 25 25 16Min 140.0 2.0 0.1 3.6 0.5 2.5 2.5 1.0 0.1Max 600.0 8.0 0.5 64.0 58.0 23.0 110.0 120.0 0.1Mean 365.8 3.4 0.1 22.9 15.2 6.3 32.0 31.4 0.1Geo Mean 341.8 3.0 0.1 17.4 4.9 4.3 18.0 9.4 0.1Median 340.0 2.0 0.1 17.0 5.9 2.5 14.0 13.0 0.1Quartile 1 267.5 2.0 0.1 12.0 0.8 2.5 7.3 1.0 0.1Quartile 3 512.5 4.3 0.1 33.0 24.0 9.0 53.0 56.0 0.1NOTE: For values reported as < (less than), half the detection limit was used.
NA = Data not applicableINA = Site was inaccessibleDRY = Site had no flow
50
F4: 541STC040 – Ingram Creek at River Road continued…
DateHardness
(mg/L)
Dissolved Arsenic (ug/L)
Dissolved Cadmium
(ug/L)
Dissolved Chromium
(ug/L)
Dissolved Copper (ug/L)
Dissolved Lead (ug/L)
Dissolved Nickel (ug/L)
Dissolved Zinc
(ug/L)
Dissolved Mercury (ug/L)
11/29/2000 520 15 <1 <5 6.2 <212/27/2000 510 15 <1 <5 5.3 <21/24/2001 580 18 <1 <5 7.2 <22/21/2001 520 18 <1 <5 6 <23/28/2001 290 1.2 2.9 <5 <5 2.34/25/2001 270 2.1 3.3 <5 <5 <25/30/2001 310 2.2 3.7 <5 <5 <28/29/2001 NA 2.9 <1 4.6 1.1 <5 <5 <29/26/2001 360 <4 <0.1 3.7 7.2 <5 <5 3.3 <0.2
10/24/2001 350 <4.0 <0.1 NA <1.0 <5.0 <5.0 <2.0 <0.211/28/2001 540 <4.0 <0.1 16 <1.0 <5.0 7.8 NA <0.212/26/2001 560 <4 <0.1 17 <1 <5 7.5 2.4 <0.21/30/2002 600 <4 <0.1 11 <1 <5 <5 <2 <0.23/27/2002 260 5.2 <0.1 1.6 6.8 <5.0 <5.0 2.4 <0.24/30/2002 290 <4.0 <0.1 2.4 1.6 <5.0 <5.0 <2.0 <0.25/29/2002 310 <4.0 <0.1 3.6 1.6 <5.0 <5.0 <2.0 <0.26/19/2002 390 <4.0 <0.1 25 23 8.6 44 47 <0.29/25/2002 220 <4.0 <0.1 1.9 NA <5.0 <5.0 <2.0 <0.2
10/30/2002 190 <4.0 <0.1 1.6 3.4 <5.0 6 <2.0 <0.211/20/2002 140 <4.0 <0.1 1.7 1.9 <5.0 <5.0 <2.0 <0.2
Count 19 13 13 19 19 20 20 19 12Min 140.0 2.0 0.1 1.2 0.5 2.5 2.5 1.0 0.1Max 600.0 5.2 0.5 25.0 23.0 8.6 44.0 47.0 0.1Mean 379.5 2.3 0.1 8.5 3.2 2.8 6.0 3.8 0.1Geo Mean 351.6 2.2 0.1 5.2 1.5 2.7 4.0 1.5 0.1Median 350.0 2.0 0.1 3.7 1.6 2.5 2.5 1.0 0.1Quartile 1 280.0 2.0 0.1 2.0 0.5 2.5 2.5 1.0 0.1Quartile 3 520.0 2.0 0.1 15.5 3.4 2.5 6.1 1.7 0.1NOTE: For values reported as < (less than), half the detection limit was used.
NA = Data not applicableINA = Site was inaccessibleDRY = Site had no flow
51
F4: 541STC040 – Ingram Creek at River Road continued…
DateChloride (mg/L)
Sulfate (mg/L)
Calcium (mg/L)
Magnesium (mg/L)
TDS (mg/L)
Carbonate (mg/L)
Bicarbonate (mg/L)
Total Alkalinity
(mg/L)Sodium (mg/L)
10/24/2000 85 87 43 36 460 <1 140 120 7911/29/2000 260 270 120 52 1300 <1 300 240 22012/27/2000 280 280 120 52 1200 5 280 230 2201/24/2001 290 310 130 59 1300 <1 300 250 2402/21/2001 290 290 120 56 1300 6 230 190 2203/28/2001 160 190 57 37 710 <1 180 150 1404/25/2001 100 NA 55 33 NA <1 110 110 915/30/2001 120 140 57 40 NA <1 120 120 1106/27/2001 120 130 60 38 540 <1 160 130 1008/29/2001 190 NA NA NA 1600 <1.0 220 180 1609/26/2001 NA NA 75 41 NA <1 200 160 150
10/24/2001 180 180 78 38 840 <1 220 180 16011/28/2001 280 290 130 55 1300 <1 310 250 23012/26/2001 300 310 130 55 1400 <1 320 270 2301/30/2002 300 310 150 57 1400 <1 320 260 2402/27/2002 140 130 61 25 NA <1.0 182 149 1003/27/2002 110 180 58 29 1700 <1.0 150 120 1004/30/2002 150 170 61 33 NA <1.0 150 130 1305/29/2002 140 150 66 35 NA <1.0 170 140 1406/19/2002 170 210 79 47 NA <1.0 180 150 1609/25/2002 180 92 43 28 NA <1.0 170 140 120
10/30/2002 110 92 36 24 470 <1.0 140 110 9011/20/2002 110 59 30 17 380 <1.0 110 93 733/25/2003 180 200 88 384/22/2003 110 120 45 265/27/2003 220 230 85 396/24/2003 140 170 58 44
52
F4: 541STC040 – Ingram Creek at River Road continued…
DateChloride (mg/L)
Sulfate (mg/L)
Calcium (mg/L)
Magnesium (mg/L)
TDS (mg/L)
Carbonate (mg/L)
Bicarbonate (mg/L)
Total Alkalinity
(mg/L)Sodium (mg/L)
Count 26 24 26 26 15 23 23 23 23Min 85 59 30 17 380 0.5 110 93 73Max 300 310 150 59 1700 6.0 320 270 240Mean 180 190 78 40 1100 0.9 200 170 150Geo Mean 170 170 71 38 953 0.6 190 160 140Median 170 180 64 38 1300 0.5 180 150 140Quartile 1 120 130 57 33 625 0.5 150 130 100Quartile 3 250 270 110 51 1400 0.5 260 210 220NOTE: For values reported as < (less than), half the detection limit was used.
NA = Data not applicableINA = Site was inaccessibleDRY = Site had no flow
53
54
F4: 541STC040 – Ingram Creek at River Road continued…
Date Result Control Result Control
Result (million/m
l)
Control (million/
ml)MDD (%)
6/19/2001 95 100 100 9011/16/2004 100 100 100 10012/21/2004 100 100 100 1001/18/2005 100 100 100 1002/15/2005 100 97.5 100 1003/23/2005 97.5 97.5 100 1004/19/2005 95 100 100 1005/17/2005 97.5 100 100 1006/21/2005 100 100 90 1007/21/2005 97.5 100 100 1008/16/2005 97.5 100 95 95.29/20/2005 100 100 100 100
Count 12 12 12 12 N/A N/A N/A
* Significantly reduced from the lab control.** Significantly greater than the lab control.^ Fish were from a "forced hatch," duplicate failed QA.1 Duplicate sample for the set was low - 77% recovery.
3 Samples qualified, but duplicate sample recovery for the set was high - 126% (53.8%/42.5%)NA = Data not applicableINA = Site was inaccessibleDRY = Site had no flow
2 Testing for the Fathead minnow was initiated when samples were approx. 48h old due to untimely shipping of fish by fish supplier.
96h Acute Fathead Minnow
(% Survival)
48h Acute Ceriodaphnia Dubia
(% Survival) Algae Cell Growth
55
F5: 541STC042 – Hospital creek at River Road Station Code:541STC042
Location: Latitude 37.61056, Longitude -121.22861
Date TimeTemp (ºC)
Field SC (umhos) pH
Dissolved Oxygen (mg/L)
Turbidity (ntu)
10/24/2000 1:05 PM 16.0 694 8.111/29/2000 DRY DRY DRY DRY12/27/2000 12:20 PM DRY DRY DRY1/24/2001 11:43 AM 8.8 353 7.52/10/2001 12:50 PM DRY DRY DRY2/11/2001 2:35 AM DRY DRY DRY2/21/2001 1:35 PM DRY DRY DRY3/28/2001 9:50 AM 15.1 1080 7.74/25/2001 8:10 AM 17.1 789 7.95/30/2001 9:20 AM 20.3 1150 7.16/5/2001 8:59 AM 17.4 991 8.1 7.76/19/2001 9:45 AM 20.8 1240 7.6 7.96/27/2001 8:52 AM 19.8 946 8.1 9.37/25/2001 9:30 AM 20.5 916 8.2 9.08/29/2001 9:49 AM 21.0 1050 7.7 7.79/26/2001 8:46 AM 16.4 1190 7.7 9.22/27/2002 DRY DRY DRY DRY DRY3/27/2002 8:20 AM 12.6 1220 8.4 10.54/30/2002 9:24 AM 11.8 651 7.6 11.35/29/2002 8:42 AM 19.1 712 8.0 9.56/19/2002 8:44 AM 19.8 208 7.7 8.57/30/2002 11:18 AM 22.1 75 8.3 8.8 3008/28/2002 9:30 AM 19.8 1380 7.2 NA9/25/2002 9:20 AM 19.9 662 8.1 9.3
10/15/2002 11:32 AM 15.7 962 7.9 10.1 NA10/30/2002 8:29 AM DRY DRY DRY DRY1/15/2003 DRY DRY DRY DRY DRY DRY3/25/2003 8:27 AM 12.2 615 7.9 11.5 2084/22/2003 11:10 AM 14.4 511 8.1 9.8 3655/27/2003 12:05 PM 23.8 833 7.9 8.4 53.46/24/2003 8:56 AM 17.5 877 7.6 9.0 80.67/29/2003 10:14 AM 24.4 721 7.9 8.9 6.88/26/2003 11:24 AM 25.3 385 8.2 7.8 1089/23/2003 11:06 AM 22.0 611 7.9 7.9 355
10/28/2003 12:59 PM 17.9 939 8.1 10.7 15.911/18/2003 12:15 PM DRY DRY DRY DRY DRY1/28/2004 10:22 AM 11.6 1980 7.9 15.2 1812/24/2004 DRY DRY DRY DRY DRY DRY3/24/2004 9:32 AM 13.8 339 8.2 10.6 350
56
F5: 541STC042 – Hospital creek at River Road continued…
Date TimeTemp (ºC)
Field SC (umhos) pH
Dissolved Oxygen (mg/L)
Turbidity (ntu)
4/28/2004 9:36 AM 17.4 640 7.9 11.5 3075/26/2004 11:29 AM 21.2 836 7.7 7.7 2646/23/2004 10:18 AM 20.4 1090 8.1 10.1 NA7/28/2004 11:05 AM 23.4 1110 8.0 9.1 NA8/25/2004 11:18 AM 22.7 830 8.1 8.2 NA9/29/2004 11:09 AM 16.7 1290 7.7 9.5 NA
10/27/2004 11:09 AM 15.8 1010 8.0 12.111/2/2004 7:43 AM DRY DRY DRY DRY
11/16/2004 8:42 AM 14.9 507 7.5 4.812/8/2004 7:55 AM 10.8 503 6.7 10.3
12/21/2004 7:26 AM DRY DRY DRY DRY1/4/2005 7:44 AM 9.5 290 8.7 9.81/18/2005 7:41 AM DRY DRY DRY DRY2/1/2005 7:50 AM DRY DRY DRY DRY2/15/2005 7:44 AM 11.1 188 8.1 13.33/8/2005 7:51 AM 11.9 739 8.2 10.53/23/2005 7:40 AM 13.5 523 7.9 7.24/5/2005 7:55 AM DRY DRY DRY DRY4/19/2005 7:55 AM 11.0 453 6.5 10.65/3/2005 7:40 AM 14.4 449 8.0 11.65/17/2005 7:50 AM 13.8 391 7.8 9.96/8/2005 8:08 AM 17.5 190 7.9 9.56/21/2005 8:04 AM 17.8 413 7.0 9.37/6/2005 10:10 AM 22.3 454 7.4 7.27/19/2005 8:44 AM 22.2 402 8.2 8.58/2/2005 10:00 AM 21.3 585 7.8 8.58/16/2005 10:16 AM 22.4 415 8.1 9.59/6/2005 10:40 AM 21.8 649 8.1 10.69/20/2005 9:41 AM 19.5 415 7.6 12.1
Count 53 53 53 47 13Min 8.8 75 6.5 4.8 6.8Max 25.3 1980 8.7 15.2 365Mean 17.6 726 7.8 9.6 200Geo Mean 17.0 626 7.8 9.4 126Median 17.5 662 7.9 9.5 208Quartile 1 14.4 449 7.7 8.5 80.6Quartile 3 21.0 962 8.1 10.6 307NOTE: For values reported as < (less than), half the detection limit was used.
NA = Data not applicableINA = Site was inaccessibleDRY = Site had no flow
57
F5: 541STC042 – Hospital creek at River Road continued…
DateTSS
(mg/L)TOC
(mg/L)Total Coli
MPNE. coli MPN
10/24/2000 2900 2.81/24/2001 34 5.13/28/2001 420 NA4/25/2001 27 3.95/30/2001 59 9.76/27/2001 730 137/25/2001 3.18/29/2001 NA 139/26/2001 NA 173/27/2002 NA4/30/2002 NA5/29/2002 5.46/19/2002 NA7/30/2002 >2419.6 1529/25/2002 NA
10/15/2002 >2419.6 15531/15/2003 NA NA3/25/2003 4.54/22/2003 5.7 >2419.6 1265/27/2003 NA6/24/2003 NA7/29/2003 >2419.6 4888/26/2003 >2419.6 4119/23/2003 >2419.6 >2419.6
10/28/2003 >2419.6 27211/18/2003 DRY DRY1/28/2004 >2419.6 82/24/2004 DRY DRY3/24/2004 >2419.6 2724/28/2004 >2419.6 1075/26/2004 >2419.6 >2419.66/23/2004 >2419.6 3657/28/2004 >2419.6 2228/25/2004 >2419.6 6919/29/2004 >2419.6 167
10/27/2004 4.1 >2419.6 9911/2/2004 DRY DRY DRY
11/16/2004 110 8.1 >2419.6 16212/8/2004 >2419.6 199
12/21/2004 DRY DRY DRY DRY1/4/2005 >2419.6 >2419.61/18/2005 DRY DRY DRY DRY
58
F5: 541STC042 – Hospital creek at River Road continued…
DateTSS
(mg/L)TOC
(mg/L)Total Coli
MPNE. coli MPN
2/1/2005 DRY DRY2/15/2005 490 23 691 1733/8/2005 >2419.6 5793/23/2005 130 NA >2419.6 19864/5/2005 DRY DRY DRY DRY4/19/2005 340 NA >2419.6 2285/3/2005 >2419.6 5795/17/2005 503 NA >2419.6 5796/8/2005 >2419.6 316/21/2005 1500 7.7 >2419.6 19867/6/2005 >2419.6 >2419.67/19/2005 3000 3.2 >2419.6 1428/2/2005 >2419.6 6878/16/2005 3300 4.7 >2419.6 24209/6/2005 >2419.6 619/20/2005 27 3.2 >2419.6 238
Count 15 18 33 33Min 27 2.8 691 8Max 3300 23 2420 2420Mean 900 7.6 NA NAGeo Mean 310 6.2 2330 353Median 420 5.3 2420 272Quartile 1 85 4.0 2420 162Quartile 3 1100 9.3 2420 691NOTE: For values reported as < (less than), half the detection limit was used
For values reported as > (greater than), 2420 was used
NA = Data not applicableINA = Site was inaccessibleDRY = Site had no flow
59
60
F5: 541STC042 – Hospital creek at River Road continued…
DateNitrate (mg/L)
Nitrate-N (mg/L)
TKN (mg/L)
Ammonia-N (mg/L)
Phosphorus (mg/L)
Ortho-phosphate-
P (mg/L)
Potassium (mg/L)
BOD 5-Day (mg/L)
BOD 10-Day (mg/L)
10/24/2000 9.7 3.4 4 <1 4 3.3 51/24/2001 8.7 <2 0.3 <1 6.8 3.6 83/28/2001 11 <2 0.5 <1 11 1.6 2.74/25/2001 7.1 <2 0.1 <1 4.8 1.1 1.95/30/2001 11 <2 0.2 <1 11 4 6.56/27/2001 18 <2 0.6 <1 12 0.5 18/29/2001 12 <2 0.7 <1 NA9/26/2001 25 4.2 0.5 <1 133/27/2002 NA 1.7 NA 0.1 6.4 0.5 14/30/2002 NA NA 0.6 0.5 NA 6.7 125/29/2002 NA 1 NA 0.3 8.3 4 66/19/2002 NA 2.1 0.4 NA 8.1 8.3 13.78/28/2002 NA 2.5 0.4 0.4 5.4 1.3 2.69/25/2002 NA NA 0.4 NA 5.7 0.9 1.4
Count 8 NA 12 NA 12 12 12 12 12Min 7.1 NA 1.0 NA 0.1 0.1 4.0 0.5 1.0Max 25.0 NA 4.2 NA 4.0 0.5 13.0 8.3 13.7Mean 12.8 NA 1.7 NA 0.7 0.4 8.0 3.0 5.2Geo Mean 11.9 NA 1.5 NA 0.5 0.4 7.5 2.0 3.6Median 11.0 NA 1.0 NA 0.5 0.5 7.5 2.5 3.9Quartile 1 9.5 NA 1.0 NA 0.4 0.5 5.6 1.1 1.8Quartile 3 13.5 NA 2.2 NA 0.6 0.5 11.0 4.0 6.9NOTE: For values reported as < (less than), half the detection limit was used.
NA = Data not applicableINA = Site was inaccessibleDRY = Site had no flow
61
F5: 541STC042 – Hospital creek at River Road continued…
DateHardness
(mg/L)
Total Arsenic (ug/L)
Total Cadmium
(ug/L)
Total Chromium
(ug/L)
Total Copper (ug/L)
Total Lead (ug/L)
Total Nickel (ug/L)
Total Zinc (ug/L)
Total Mercury (ug/L)
10/24/2000 110 98 35 180 2111/24/2001 110 3.8 8.3 <5 8.8 8.73/28/2001 270 29 25 7.2 43 484/25/2001 180 2.2 3.6 <5 <5 2.55/30/2001 270 5 7.8 <5 8.1 7.77/25/2001 56 43 15 81 918/29/2001 NA 4.8 <1 23 20 7.6 35 389/26/2001 310 <4 <0.1 13 15 <5 20 20 <0.23/27/2002 340 <4.0 <0.1 5.4 4.1 <5.0 <5.0 7.6 <0.24/30/2002 160 <4.0 <0.1 8.9 9.7 <5.0 16 20 <0.25/29/2002 190 5.2 <0.1 27 NA 8.5 41 46 <0.26/19/2002 370 6.9 0.18 60 55 19 91 100 0.29/25/2002 130 <4.0 <0.1 1.9 NA <5.0 <5.0 3.4 <0.23/25/2003 130 <4.0 <0.1 12 12 <5.0 16 20 <0.24/22/2003 140 <4.0 <0.1 20 17 5.2 28 31 <0.25/27/2003 190 4.2 <0.1 2.6 6.9 <5.0 5.5 5 <0.26/24/2003 210 4.7 <0.1 3.2 8.3 <5.0 7.1 7.4 <0.2
Count 14 11 11 17 15 17 17 17 10Min 110.0 2.0 0.1 1.9 3.6 2.5 2.5 2.5 0.1Max 370.0 6.9 0.5 110.0 98.0 35.0 180.0 211.0 0.2Mean 214.3 3.4 0.1 22.5 22.2 7.2 34.6 39.3 0.1Geo Mean 199.8 3.1 0.1 11.2 14.2 4.7 16.5 19.2 0.1Median 190.0 2.0 0.1 12.0 12.0 2.5 16.0 20.0 0.1Quartile 1 145.0 2.0 0.1 3.8 8.1 2.5 7.1 7.6 0.1Quartile 3 270.0 4.8 0.1 27.0 22.5 7.6 41.0 46.0 0.1
*half of the detection limit used for calculationsNOTE: For values reported as < (less than), half the detection limit was used.
NA = Data not applicableINA = Site was inaccessibleDRY = Site had no flow
62
F5: 541STC042 – Hospital creek at River Road continued…
DateHardness
(mg/L)
Dissolved Arsenic (ug/L)
Dissolved Cadmium
(ug/L)
Dissolved Chromium
(ug/L)
Dissolved Copper (ug/L)
Dissolved Lead (ug/L)
Dissolved Nickel (ug/L)
Dissolved Zinc
(ug/L)
Dissolved Mercury (ug/L)
1/24/2001 110 <1 4.4 <5 <5 2.43/28/2001 270 <1 3.6 <5 <5 <24/25/2001 180 <1 1.9 <5 <5 3.95/30/2001 270 1.1 4.9 <5 <5 <28/29/2001 NA 2.2 <1 1.5 3.4 <5 <5 2.69/26/2001 310 <4 <0.1 2 4.5 <5 <5 <2 <0.23/27/2002 340 <4.0 <0.1 3.5 2.2 <5.0 <5.0 2.8 <0.24/30/2002 160 <4.0 <0.1 <1.0 2.3 <5.0 <5.0 4 <0.25/29/2002 190 <4.0 <0.1 <1.0 2.3 <5.0 <5.0 <2.0 <0.26/19/2002 370 <4.0 <0.1 37 34 12 56 61 <0.29/25/2002 130 <4.0 <0.1 <1.0 NA <5.0 <5.0 2.5 <0.2
Count 10 7 7 11 10 11 11 11 6Min 110.0 2.0 0.1 0.5 1.9 2.5 2.5 1.0 0.1Max 370.0 2.2 0.5 37.0 34.0 12.0 56.0 61.0 0.1Mean 233.0 2.0 0.1 4.4 6.4 3.4 7.4 7.6 0.1Geo Mean 216.1 2.0 0.1 1.2 3.9 2.9 3.3 2.6 0.1Median 230.0 2.0 0.1 0.5 3.5 2.5 2.5 2.5 0.1Quartile 1 165.0 2.0 0.1 0.5 2.3 2.5 2.5 1.0 0.1Quartile 3 300.0 2.0 0.1 1.8 4.5 2.5 2.5 3.4 0.1NOTE: For values reported as < (less than), half the detection limit was used.
NA = Data not applicableINA = Site was inaccessibleDRY = Site had no flow
63
64
F5: 541STC042 – Hospital creek at River Road continued…
DateChloride (mg/L)
Sulfate (mg/L)
Calcium (mg/L)
Magnesium (mg/L)
TDS (mg/L)
Carbonate (mg/L)
Bicarbonate (mg/L)
Total Alkalinity
(mg/L)Sodium (mg/L)
10/24/2000 96 82 49 62 460 <1 150 120 761/24/2001 28 33 28 10 200 <1 100 80 243/28/2001 140 160 55 33 630 <1 160 130 1204/25/2001 110 NA 39 21 NA <1 100 100 805/30/2001 140 160 57 32 NA 4 146 150 1206/27/2001 120 130 54 33 540 <1 160 130 998/29/2001 160 NA NA NA 600 <1.0 160 130 1109/26/2001 NA NA 66 34 NA <1 180 140 1203/27/2002 27 43 79 33 740 <1.0 160 130 1204/30/2002 83 94 33 18 NA <1.0 110 88 715/29/2002 89 89 41 23 NA <1.0 130 110 816/19/2002 140 160 68 48 NA <1.0 170 140 1309/25/2002 130 35 21 18 NA <1.0 100 84 853/25/2003 70 74 28 154/22/2003 58 63 28 185/27/2003 110 120 42 216/24/2003 110 120 46 23
Count 16 14 16 16 6 13 13 13 13Min 27 33 21 10 200 0.5 100 80 24Max 160 160 79 62 740 4.0 180 150 130Mean 100 97 46 28 530 0.8 140 120 95Geo Mean 90 86 43 25 490 0.6 140 120 89Median 110 92 44 23 570 0.5 150 130 99Quartile 1 80 66 32 18 480 0.5 110 100 80Quartile 3 130 130 56 33 620 0.5 160 130 120NOTE: For values reported as < (less than), half the detection limit was used.
NA = Data not applicableINA = Site was inaccessibleDRY = Site had no flow
F5: 541STC042 – Hospital creek at River Road continued…
Date Result Control Result Control
Result (million/m
l)
Control (million/
ml)MDD (%)
1/24/2001 95 100 NA NA3/28/2001 100 100 100 1004/25/2001 100 100 80 905/30/2001 85 95 90 1006/27/2001 95 100 100 90
11/16/2004 100 100 100 1002/15/2005 92.5 97.5 100 1003/23/2005 100 97.5 0* 1004/19/2005 100 100 0* 1005/17/2005 95 100 100 1006/21/2005 97.5 100 100 1007/19/2005 97.5 100 100 1008/16/2005 95 100 0* 95.29/20/2005 100 100 100 100
Count 14 14 13 13 N/A N/A N/A
* Significantly reduced from the lab control.** Significantly greater than the lab control.^ Fish were from a "forced hatch," duplicate failed QA.1 Duplicate sample for the set was low - 77% recovery.
3 Samples qualified, but duplicate sample recovery for the set was high - 126% (53.8%/42.5%)NA = Data not applicableINA = Site was inaccessibleDRY = Site had no flow
2 Testing for the Fathead minnow was initiated when samples were approx. 48h old due to untimely shipping of fish by fish supplier.
96h Acute Fathead Minnow
(% Survival)
48h Acute Ceriodaphnia Dubia
(% Survival) Algae Cell Growth
65
F6: 541STC030 – Grayson Road Drain at Grayson Station Code:541STC030
Location: Latitude 37.56194, Longitude -121.17417
Date TimeTemp (ºC)
Field SC (umhos) pH
Dissolved Oxygen (mg/L)
Turbidity (ntu)
10/24/2000 1:45 PM 20.1 671 7.711/29/2000 9:10 AM 12.3 1140 7.312/27/2000 10:55 AM 7.1 627 8.11/24/2001 DRY DRY DRY DRY2/21/2001 12:10 PM 13.3 1370 8.53/28/2001 10:30 AM 18.2 799 7.94/25/2001 8:47 AM 17.9 728 8.15/30/2001 10:05 AM 20.3 960 7.66/27/2001 9:25 AM 20.7 308 8.0 10.17/25/2001 9:57 AM 21.3 1120 8.2 9.08/29/2001 10:12 AM 22.6 806 8.0 8.69/26/2001 9:22 AM 20.8 947 8.1 9.2
10/24/2001 10:10 AM 13.8 958 8.2 10.311/28/2001 9:31 AM DRY DRY DRY DRY12/26/2001 9:59 AM DRY DRY DRY DRY1/30/2002 9:52 AM 8.6 826 7.7 9.52/27/2002 9:11 AM 14.1 1280 8.0 10.03/27/2002 8:52 AM 14.7 1060 8.2 10.54/30/2002 8:48 AM 13.5 964 7.7 9.85/29/2002 9:11 AM 19.5 946 7.9 9.36/19/2002 9:01 AM 19.6 340 8.1 8.87/31/2002 8:27 AM 21.7 919 7.5 8.6 5158/28/2002 9:55 AM 22.1 1330 8.1 NA9/25/2002 9:58 AM 18.9 1460 7.6 NA
10/15/2002 10:38 AM 16.2 1500 8.2 10.0 NA10/30/2002 9:01 AM 14.7 814 7.6 9.711/20/2002 9:14 AM 12.8 653 7.8 10.612/18/2002 8:53 AM DRY DRY DRY DRY DRY1/14/2003 1:00 PM 11.6 161 7.7 5.4 4771/29/2003 DRY DRY DRY DRY DRY DRY3/25/2003 8:49 AM 14.4 655 8.5 10.6 5.94/24/2003 1:54 PM 15.4 883 8.2 10.3 10.25/29/2003 12:50 PM 30.9 1430 8.5 7.6 7426/26/2003 12:26 PM 22.1 786 8.5 9.1 80.57/31/2003 1:06 PM 25.7 518 7.9 8.0 1398/28/2003 1:04 AM 27.2 1220 8.5 9.1 13409/25/2003 1:10 PM DRY DRY DRY DRY DRY
10/30/2003 12:55 PM DRY DRY DRY DRY DRY11/20/2003 1:23 PM 15.4 1630 8.4 10.3 5.3
66
F6: 541STC030 – Grayson Road Drain at Grayson continued…
Date TimeTemp (ºC)
Field SC (umhos) pH
Dissolved Oxygen (mg/L)
Turbidity (ntu)
1/29/2004 12:35 PM DRY DRY DRY DRY DRY2/26/2004 12:25 PM 12.1 176 8.1 10.8 NA3/24/2004 12:45 PM 16.2 763 8.1 9.9 NA4/29/2004 1:24 PM 20.2 793 8.1 9.3 10705/27/2004 1:17 PM 28.1 1190 8.8 7.9 5606/24/2004 1:40 PM 25.1 1030 8.2 9.4 NA7/29/2004 12:19 PM 27.0 1060 8.2 8.5 NA8/26/2004 1:19 PM 25.0 924 8.1 7.9 NA9/29/2004 11:31 AM 20.1 1450 8.1 9.1 NA
10/28/2004 12:58 PM 17.1 636 8.2 8.411/3/2004 12:24 PM 16.3 699 8.1 9.8
11/17/2004 12:19 PM DRY DRY DRY DRY12/8/2004 10:03 AM 12.4 715 7.9 11.8
12/21/2004 9:53 AM DRY DRY DRY DRY1/5/2005 10:24 AM 11.7 595 8.3 12.01/19/2005 10:00 AM DRY DRY DRY DRY2/2/2005 10:45 AM DRY DRY DRY DRY2/16/2005 10:38 AM 12.4 145 7.9 10.03/9/2005 10:20 AM DRY DRY DRY DRY3/22/2005 11:41 AM 14.1 358 8.0 10.24/6/2005 DRY DRY DRY DRY DRY4/20/2005 11:16 AM DRY DRY DRY DRY5/4/2005 11:01 AM 17.1 583 8.1 9.55/18/2005 12:02 PM 18.0 424 8.3 10.36/8/2005 1:05 PM 21.8 303 7.5 7.16/22/2005 12:01 PM 21.1 808 8.1 9.07/6/2005 10:42 AM 22.4 546 8.0 8.57/20/2005 10:43 AM 24.4 686 8.1 8.68/3/2005 11:01 AM 22.5 758 7.7 3.48/17/2005 10:20 AM 22.7 686 8.2 9.19/7/2005 11:00 AM 22.0 940 8.2 8.89/21/2005 11:51 AM 26.6 715 7.8 11.3
Count 56 56 56 47 11Min 7.1 145 7.3 3.4 5.3Max 30.9 1630 8.8 12.0 1340Mean 18.6 836 8.0 9.3 450Geo Mean 17.9 745 8.0 9.1 143Median 19.2 803 8.1 9.3 477Quartile 1 14.3 649 7.9 8.6 45.4Quartile 3 22.1 1038 8.2 10.2 651NOTE: For values reported as < (less than), half the detection limit was used.
NA = Data not applicableINA = Site was inaccessibleDRY = Site had no flow
67
F6: 541STC030 – Grayson Road Drain at Grayson continued…
DateTSS
(mg/L)TOC
(mg/L)Total Coli
MPNE. coli MPN
10/24/2000 27 4.111/29/2000 NA 2.112/27/2000 400 4.92/21/2001 6 NA3/28/2001 <5 NA4/25/2001 240 2.85/30/2001 1400 8.96/27/2001 970 8.67/25/2001 8.78/29/2001 NA 9.19/26/2001 NA 113/27/2002 NA4/30/2002 NA5/29/2002 9.76/19/2002 NA7/31/2002 >2419.6 369/25/2002 NA
10/15/2002 >2419.6 11510/30/2002 3.511/20/2002 3.11/14/2003 >2419.6 1313/25/2003 4.04/24/2003 NA >2419.6 17335/29/2003 7.86/26/2003 4.17/31/2003 >2419.6 10468/28/2003 >2419.6 749/25/2003 DRY DRY
10/30/2003 DRY DRY11/20/2003 1120 71/29/2004 DRY DRY2/26/2004 >2419.6 >2419.63/24/2004 >2419.6 12034/29/2004 >2419.6 1505/27/2004 >2419.6 2386/24/2004 4200 >2419.6 1617/29/2004 >2419.6 2608/26/2004 >2419.6 3179/29/2004 >2419.6 93
10/28/2004 4.5 >2419.6 2011/3/2004 77 7.7 >2419.6 1414
11/17/2004 DRY DRY DRY DRY12/8/2004 90 21 >2419.6 >2419.6
68
F6: 541STC030 – Grayson Road Drain at Grayson continued…
DateTSS
(mg/L)TOC
(mg/L)Total Coli
MPNE. coli MPN
12/21/2004 DRY DRY DRY DRY1/5/2005 18 5.4 >2419.6 201/19/2005 DRY DRY DRY DRY2/2/2005 DRY DRY DRY DRY2/16/2005 200 NA >2419.6 15533/9/2005 DRY DRY DRY DRY3/22/2005 25 7.2 >2419.6 >2419.64/6/2005 DRY DRY DRY DRY4/20/2005 DRY DRY DRY DRY5/4/2005 120 9.6 >2419.6 15535/18/2005 770 4.3 >2419.6 1156/8/2005 180 NA >2419.6 >2419.66/22/2005 48 NA >2419.6 11207/6/2005 70 4.9 >2419.6 1527/20/2005 3500 3.8 >2419.6 2318/3/2005 28000 10 >2419.6 24208/17/2005 510 5.8 >2419.6 11209/7/2005 140 4.0 >2419.6 1949/21/2005 880 NA >2419.6 727
Count 23 27 31 31Min 2.5 2.1 1120 7Max 28000 21 2420 2420Mean 1821 6.7 NA NAGeo Mean 195 5.9 2361 337Median 180 5.4 2420 260Quartile 1 59 4.1 2420 123Quartile 3 825 8.8 2420 1484NOTE: For values reported as < (less than), half the detection limit was used
For values reported as > (greater than), 2420 was used
NA = Data not applicableINA = Site was inaccessibleDRY = Site had no flow
69
70
F6: 541STC030 – Grayson Road Drain at Grayson continued…
DateNitrate (mg/L)
Nitrate-N (mg/L)
TKN (mg/L)
Ammonia-N (mg/L)
Phosphorus (mg/L)
Ortho-phosphate-
P (mg/L)
Potassium (mg/L)
BOD 5-Day (mg/L)
BOD 10-Day (mg/L)
10/24/2000 8.7 <2 0.2 <1 4.5 0.7 1.211/29/2000 10 NA 0.2 <1 6.4 0.8 1.112/27/2000 7.4 <2 0.6 1 9 5.2 7.32/21/2001 30 <2 0.1 <1 4.4 0.8 2.53/28/2001 6.3 <2 0.2 <1 5.2 1.4 2.54/25/2001 13 <2 0.3 <1 6.8 2 3.65/30/2001 14 3.5 0.5 <1 14 3.5 5.86/27/2001 20 3.2 0.5 <1 14 3.1 7.68/29/2001 6.1 <2 1.9 <1 NA9/26/2001 5.1 <2 0.3 <1 6.8
10/24/2001 <2 <2 0.4 <1 5.5 1.9 3.711/28/2001 NA 0.2 NA <0.03 2.912/26/2001 NA 0.4 <0.05 <0.03 4.51/30/2002 NA 13 2.9 2.5 15 7.5 162/27/2002 NA 0.5 0.1 0.1 NA 0.6 13/27/2002 NA 0.9 NA NA 2.8 0.8 1.54/30/2002 NA NA 2.2 0.9 NA 8.5 16.85/29/2002 NA 2 NA 0.4 8.2 8.4 15.46/19/2002 NA 0.7 0.3 NA 3.3 1.1 1.68/28/2002 NA 2 0.7 0.2 6.1 3.4 6.79/25/2002 NA NA 0.4 0.4 14 8.4 16.9
10/30/2002 NA NA 0.2 0.1 2.7 1.2 1.911/20/2002 NA 0.8 0.2 0.1 3.6
71
F6: 541STC030 – Grayson Road Drain at Grayson continued…
DateNitrate (mg/L)
Nitrate-N (mg/L)
TKN (mg/L)
Ammonia-N (mg/L)
Phosphorus (mg/L)
Ortho-phosphate-
P (mg/L)
Potassium (mg/L)
BOD 5-Day (mg/L)
BOD 10-Day (mg/L)
Count 11 NA 19 NA 20 21 20 18 18Min 1.0 NA 0.2 NA 0.03 0.02 2.7 0.6 1.0Max 30.0 NA 13.0 NA 2.9 2.5 15.0 8.5 16.9Mean 11.1 NA 1.9 NA 0.6 0.5 7.0 3.3 6.3Geo Mean 8.4 NA 1.1 NA 0.3 0.3 6.0 2.2 4.0Median 8.7 NA 1.0 NA 0.3 0.5 5.8 2.0 3.7Quartile 1 6.2 NA 0.9 NA 0.2 0.2 4.2 0.9 1.7Quartile 3 13.5 NA 1.5 NA 0.5 0.5 8.4 4.8 7.5NOTE: For values reported as < (less than), half the detection limit was used.
NA = Data not applicableINA = Site was inaccessibleDRY = Site had no flow
72
F6: 541STC030 – Grayson Road Drain at Grayson continued…
DateHardness
(mg/L)
Total Arsenic (ug/L)
Total Cadmium
(ug/L)
Total Chromium
(ug/L)
Total Copper (ug/L)
Total Lead (ug/L)
Total Nickel (ug/L)
Total Zinc (ug/L)
Total Mercury (ug/L)
10/24/2000 170 1.5 2.4 <5 <5 311/29/2000 260 <1 1.5 <5 <5 <212/27/2000 160 21 52 11 31 702/21/2001 400 16 1.1 <5 <5 <23/28/2001 190 <1 3.6 <5 5.1 <24/25/2001 190 13 13 <5 20 295/30/2001 310 54 50 24 88 1307/25/2001 310 61 52 26 91 1508/29/2001 NA 11 <1 86 93 46 180 2409/26/2001 200 <4 <0.1 <1 2.4 <5 <5 <2 <0.2
10/24/2001 220 5.3 <0.1 NA 1.5 <5.0 <5.0 <2.0 <0.21/30/2002 90 4.3 0.2 1.4 8.1 <5 6.9 28 <0.23/27/2002 370 <4.0 <0.1 14 2.5 <5.0 <5.0 5.4 <0.24/30/2002 310 <4.0 <0.1 2.7 9.3 <5.0 8.8 8.5 <0.25/29/2002 280 11 <0.1 56 NA 39 130 180 <0.26/19/2002 110 4.1 <0.1 10 12 <5.0 18 26 <0.29/25/2002 390 5.4 <0.1 12 NA <5.0 25 24 <0.2
10/30/2002 210 <4.0 <0.1 <1.0 NA <5.0 <5.0 <2.0 <0.211/20/2002 140 <4.0 <0.1 <1.0 1.6 <5.0 NA NA <0.23/25/2003 170 12 <0.1 <1.0 4.3 <5.0 <5.0 <2.0 <0.24/24/2003 190 <4.0 <0.1 <1.0 2.1 <5.0 <5.0 <2.0 <0.25/29/2003 360 7.8 <0.1 41 30 12 70 63 <0.26/26/2003 180 <4.0 <0.1 10 14 5.5 24 24 NA
73
F6: 541STC030 – Grayson Road Drain at Grayson continued…
DateHardness
(mg/L)
Total Arsenic (ug/L)
Total Cadmium
(ug/L)
Total Chromium
(ug/L)
Total Copper (ug/L)
Total Lead (ug/L)
Total Nickel (ug/L)
Total Zinc (ug/L)
Total Mercury (ug/L)
Count 22 15 15 22 20 23 22 22 13Min 90 2.0 0.1 0.5 1.1 2.5 2.5 1.0 0.1Max 400 12 1 86 93 46 180 240 0.1Mean 237 5.0 0.1 18 18 8.8 33 45 0.1Geo Mean 220 3.9 0.1 5.0 7.1 4.6 11.1 9.8 0.1Median 205 4.1 0.1 10.0 6.2 2.5 7.9 16.3 0.1Quartile 1 173 2.0 0.1 0.5 2.3 2.5 2.5 1.0 0.1Quartile 3 310 6.6 0.1 19.8 18 8.3 30 55 0.1NOTE: For values reported as < (less than), half the detection limit was used.
NA = Data not applicableINA = Site was inaccessibleDRY = Site had no flow
74
F6: 541STC030 – Grayson Road Drain at Grayson continued…
DateHardness
(mg/L)
Dissolved Arsenic (ug/L)
Dissolved Cadmium
(ug/L)
Dissolved Chromium
(ug/L)
Dissolved Copper (ug/L)
Dissolved Lead (ug/L)
Dissolved Nickel (ug/L)
Dissolved Zinc
(ug/L)
Dissolved Mercury
(ug/L)11/29/2000 260 <1 1.2 <5 <5 <212/27/2000 160 <1 5.1 <5 <5 <22/21/2001 400 15 <1 <5 <5 <23/28/2001 190 <1 2.6 <5 <5 <24/25/2001 190 <1 1.8 <5 <5 <25/30/2001 310 <1 2.2 <5 <5 <28/29/2001 NA 2.4 <1 <1 1.5 <5 6.2 6.69/26/2001 200 <4 <0.1 <1 2.4 <5 <5 6 <0.2
10/24/2001 220 6.5 <0.1 NA 1.7 <5.0 <5.0 <2.0 <0.21/30/2002 90 <4 0.2 <1 4.9 <5 <5 17 <0.23/27/2002 370 <4 <0.1 12 2.9 <5.0 <5.0 2.5 <0.24/30/2002 310 <4.0 <0.1 <1.0 7 <5.0 5.2 5.9 <0.25/29/2002 280 <4.0 <0.1 <1.0 4.5 <5.0 <5.0 <2.0 <0.26/19/2002 110 <4.0 <0.1 6.1 7.4 <5.0 11 17 <0.29/25/2002 390 <4.0 <0.1 1.3 NA <5.0 6 <2.0 <0.2
10/30/2002 210 <4.0 <0.1 <1.0 3 <5.0 <5.0 <2.0 <0.211/20/2002 140 <4.0 <0.1 <1.0 <1.0 <5.0 <5.0 <2.0 <0.2
Count 16 11 11 16 16 17 17 17 10Min 90 2.0 0.1 0.5 0.5 2.5 2.5 1.0 0.1Max 400 6.5 0.5 15 7.4 2.5 11 17 0.1Mean 239 2.4 0.1 2.5 3.1 2.5 3.6 3.9 0.1Geo Mean 220 2.3 0.1 0.9 2.4 2.5 3.2 2.0 0.1Median 215 2.0 0.1 0.5 2.5 2.5 2.5 1.0 0.1Quartile 1 183 2.0 0.1 0.5 1.7 2.5 2.5 1.0 0.1Quartile 3 310 2.0 0.1 0.7 4.6 2.5 2.5 5.9 0.1NOTE: For values reported as < (less than), half the detection limit was used.
NA = Data not applicableINA = Site was inaccessibleDRY = Site had no flow
75
F6: 541STC030 – Grayson Road Drain at Grayson continued…
DateChloride (mg/L)
Sulfate (mg/L)
Calcium (mg/L)
Magnesium (mg/L)
TDS (mg/L)
Carbonate (mg/L)
Bicarbonate (mg/L)
Total Alkalinity
(mg/L)Sodium (mg/L)
10/24/2000 76 77 31 22 380 <1 140 110 7211/29/2000 150 140 46 35 670 2 200 170 13012/27/2000 95 64 31 20 370 <1 110 90 682/21/2001 210 160 82 48 800 <1 200 160 1203/28/2001 96 110 39 22 470 <1 140 110 854/25/2001 82 NA 39 22 NA <1 92 92 725/30/2001 130 140 54 42 NA <1 110 110 1106/27/2001 130 140 57 41 620 <1 160 130 1108/29/2001 130 NA NA NA 440 <1.0 140 110 969/26/2001 NA NA 36 26 NA <1 170 140 110
10/24/2001 140 110 40 28 560 <1 190 150 1201/30/2002 35 40 17 12 240 <1 44 54 242/27/2002 200 160 73 46 NA <1.0 190 156 1203/27/2002 160 130 58 41 640 <1.0 180 150 1004/30/2002 150 170 54 35 NA <1.0 170 140 1405/29/2002 120 130 60 42 NA <1.0 160 140 1206/19/2002 36 32 22 14 NA <1.0 85 70 349/25/2002 410 360 68 54 NA <1.0 360 290 180
10/30/2002 100 98 38 27 480 <1.0 160 130 9111/20/2002 99 57 28 17 350 <1.0 130 110 713/25/2003 73 83 37 194/24/2003 110 130 42 225/29/2003 200 230 72 446/26/2003 98 120 38 21
76
F6: 541STC030 – Grayson Road Drain at Grayson continued…
DateChloride (mg/L)
Sulfate (mg/L)
Calcium (mg/L)
Magnesium (mg/L)
TDS (mg/L)
Carbonate (mg/L)
Bicarbonate (mg/L)
Total Alkalinity
(mg/L)Sodium (mg/L)
Count 23 21 23 23 12 20 20 20 20Min 35 32 17 12 240 0.5 44 54 24Max 410 360 82 54 800 2.0 360 290 180Mean 130 130 46 30 500 0.6 160 130 99Geo Mean 120 110 43 28 480 0.5 150 120 91Median 120 130 40 27 480 0.5 160 130 110Quartile 1 96 83 37 22 380 0.5 130 110 72Quartile 3 150 140 58 42 630 0.5 180 150 120NOTE: For values reported as < (less than), half the detection limit was used.
NA = Data not applicableINA = Site was inaccessibleDRY = Site had no flow
77
78
F6: 541STC030 – Grayson Road Drain at Grayson continued…
Date Result Control Result Control
Result (million/m
l)
Control (million/
ml)MDD (%)
2/16/2005 100 100 100 1003/22/2005 92.5 100 0* 1005/18/2005 100 97.5 100 1006/22/2005 100 100 100 1007/20/2005 100 100 100 1008/17/2005 97.5 97.5 100 1009/21/2005 100 100 95 100
Count 7 7 7 7 N/A N/A N/A
* Significantly reduced from the lab control.** Significantly greater than the lab control.^ Fish were from a "forced hatch," duplicate failed QA.1 Duplicate sample for the set was low - 77% recovery.
3 Samples qualified, but duplicate sample recovery for the set was high - 126% (53.8%/42.5%)NA = Data not applicableINA = Site was inaccessibleDRY = Site had no flow
2 Testing for the Fathead minnow was initiated when samples were approx. 48h old due to untimely shipping of fish by fish supplier.
96h Acute Fathead Minnow
(% Survival)
48h Acute Ceriodaphnia Dubia
(% Survival) Algae Cell Growth
79
APPENDIX G
SOUTH DELTA BASIN
APPENDIX G: SOUTH DELTA BASIN G1: 544SJC001 – New Jerusalem Tile Drain……………………………………….........03-17 G2: 544SJC505 – Tom Paine Slough at Paradise Road………………………...…..……18-28 G3: 544SJC506 – Old River at Tracy Blvd.………………………………….…..………29-39 G4: 544SJC509 – Mt House Creek @ Mt. House Parkway………………….………….40-47
2
G1: 544SJC001 – New Jerusalem Tile Drain Station Code:544SJC001
Location: Latitude 37.70889, Longitude -121.29861
Date TimeTemp (ºC)
Field SC (umhos) pH
Dissolved Oxygen (mg/L)
Turbidity (ntu)
10/24/2000 12:45 PM 20.0 2380 7.611/28/2000 1:42 PM 16.5 2390 7.912/27/2000 12:00 PM 16.7 2550 7.91/23/2001 11:45 AM 16.1 2480 7.82/20/2001 12:05 PM 16.0 2600 8.03/27/2001 12:21 PM 18.6 2760 7.54/24/2001 2:00 PM 20.7 2420 7.45/29/2001 12:55 PM 19.9 2540 7.26/26/2001 1:39 PM 18.0 2580 7.3 10.37/24/2001 11:08 AM 18.9 2740 7.4 9.48/28/2001 9:55 AM 19.1 2340 7.4 10.69/25/2001 11:47 AM 19.2 2230 7.6 10.8
10/23/2001 11:23 AM 19.5 2440 7.9 9.711/27/2001 11:15 AM 19.0 1340 8.0 9.212/26/2001 1:12 PM 13.6 2670 8.2 NA1/29/2002 10:41 AM 17.3 2790 8.1 11.22/26/2002 10:41 AM 17.5 2590 8.0 9.33/26/2002 12:20 PM 15.0 1730 7.9 10.14/23/2002 1:12 PM 17.1 2570 7.5 10.15/28/2002 11:10 AM 17.7 2390 7.5 11.86/18/2002 11:18 AM 17.9 2560 7.4 9.17/31/2002 9:20 AM 18.5 2560 7.6 8.9 2.48/27/2002 NA 20.3 2370 NA NA9/24/2002 11:41 AM 19.3 2430 7.6 10.1
10/15/2002 8:40 AM 19.2 2280 7.6 9.2 0.210/29/2002 1:15 PM 19.2 2290 7.7 9.2 0.211/19/2002 11:01 AM 19.0 2260 7.7 9.812/17/2002 10:14 AM 18.0 2060 7.9 9.5 2901/15/2003 INA INA INA INA INA INA1/28/2003 10:30 AM INA INA INA INA INA3/25/2003 10:15 AM 17.4 2300 7.7 10.9 2.64/22/2003 10:45 AM 17.2 2660 7.6 11.7 13.95/27/2003 11:29 AM 17.4 2510 7.1 9.6 38.36/24/2003 9:34 AM 17.8 2280 7.4 10.3 35.57/29/2003 9:35 AM 18.8 2410 7.4 8.3 2.58/26/2003 11:01 AM 19.1 2550 7.5 9.7 0.79/23/2003 10:42 AM 19.4 2440 7.7 10.2 0.9
10/28/2003 12:27 PM 19.6 2250 7.9 11.2 5.711/18/2003 11:52 AM 19.4 2320 8.3 12.6 6.61/28/2004 INA INA INA INA INA INA
3
G1: 544SJC001 – New Jerusalem Tile Drain continued…
Date TimeTemp (ºC)
Field SC (umhos) pH
Dissolved Oxygen (mg/L)
Turbidity (ntu)
2/24/2004 10:55 AM 15.6 2240 8.1 10.3 NA5/26/2004 10:55 AM INA INA INA INA INA6/23/2004 9:47 AM 18.2 2530 7.5 11.9 NA7/28/2004 10:27 AM 19.4 2190 7.4 11.0 NA8/25/2004 10:38 AM 19.2 2510 7.4 9.9 NA9/29/2004 10:43 AM 19.4 2240 7.3 11.2 NA
10/27/2004 10:43 AM INA INA INA INA INA11/22/2004 11:24 AM 11.0 2540 8.1 10.112/28/2004 10:10 AM INA INA INA INA INA1/26/2005 10:25 AM 17.5 2650 8.0 9.12/23/2005 9:53 AM 17.4 2620 7.8 10.13/29/2005 11:00 AM INA INA INA INA3/31/2005 12:49 PM 17.1 2550 7.5 10.64/26/2005 10:50 AM 17.2 2770 7.4 11.35/24/2005 10:05 AM 17.4 2550 7.2 9.26/28/2005 10:12 AM 17.9 2450 7.3 9.77/26/2005 10:08 AM 18.6 2320 7.3 9.38/23/2005 10:14 AM 19.1 2340 7.2 9.19/27/2005 10:59 AM 19.1 2290 7.4 14.6
Count 52 52 51 42 13Min 11.0 1340 7.1 8.3 0.2Max 20.7 2790 8.3 14.6 290Mean 18.0 2420 7.6 10.2 30.7Geo Mean 17.9 2410 7.6 10.2 4.1Median 18.4 2440 7.6 10.1 2.6Quartile 1 17.4 2300 7.4 9.3 0.9Quartile 3 19.2 2560 7.9 10.9 13.9NOTE: For values reported as < (less than), half the detection limit was used.
NA = Data not applicableINA = Site was inaccessibleDRY = Site had no flow
4
G1: 544SJC001 – New Jerusalem Tile Drain continued…
DateTSS
(mg/L)TOC
(mg/L)Total Coli
MPNE. coli MPN
10/24/2000 <6 <111/28/2000 <6 <112/27/2000 <5 <11/23/2001 <5 1.52/20/2001 <5.5 <13/27/2001 <5 NA4/24/2001 12 3.25/29/2001 <5 3.16/26/2001 33 7.87/24/2001 4.88/28/2001 <6 219/25/2001 NA 21
10/23/2001 202/26/2002 NA3/26/2002 2.14/23/2002 NA5/28/2002 <1.06/18/2002 2.17/31/2002 >2419.6 48/27/2002 1.79/24/2002 2.2
10/15/2002 548 810/29/2002 1.511/19/2002 1.41/15/2003 INA INA3/25/2003 1.84/22/2003 2.6 1986 95/27/2003 NA6/24/2003 NA7/29/2003 1986 48/26/2003 >2419.6 159/23/2003 1120 16
10/28/2003 236 111/18/2003 548 <11/28/2004 INA INA2/24/2004 135 <15/26/2004 INA INA6/23/2004 >2419.6 67/28/2004 >2419.6 188/25/2004 >2419.6 29/29/2004 1986 4
10/27/2004 INA INA INA11/22/2004 <0.20 365 612/28/2004 INA INA INA
5
6
DateTSS
(mg/L)TOC
(mg/L)Total Coli
MPNE. coli MPN
1/26/2005 <0.20 222 <12/23/2005 <0.20 52 13/29/2005 INA INA INA3/31/2005 2.2 548 54/26/2005 NA >2419.6 125/24/2005 NA >2419.6 156/28/2005 1.9 >2419.6 37/26/2005 NA >2419.6 228/23/2005 2.2 2420 19/27/2005 2.4 >2419.6 27
Count 10 28 23 20Min 3 0.10 52 1Max 33 21 2420 27Mean 7 3.9 NA NAGeo Mean 4 1.6 105
G1: 544SJC001 – New Jerusalem Tile Drain continued…
2 6Median 3 2.0 1986 6QuaQuaNOT
NA =INA =DRY
rtile 1 3 0.5 548 4rtile 3 3 2.7 2420 15E: For values reported as < (less than), half the detection limit was used. For values reported as > (greater than), 2420 was used Data not applicable Site was inaccessible
= Site had no flow
G1: 544SJC001 – New Jerusalem Tile Drain continued…
DateNitrate (mg/L)
Nitrate-N (mg/L)
TKN (mg/L)
Ammonia-N (mg/L)
Phosphorus (mg/L)
Ortho-phosphate-
P (mg/L)
Potassium (mg/L)
BOD 5 Day (mg/L)
BOD 10 Day (mg/L)
10/24/2000 77 <2 <0.1 <1 19 <0.1 <0.111/28/2000 NA <2 <0.1 <1 4.2 0.1 0.112/27/2000 59 <2 <0.1 <1 4.4 <0.1 <0.11/23/2001 61 <2 <0.1 <1 4.1 0.2 0.22/20/2001 69 <2 <0.1 0.1 3.9 <0.1 <0.13/27/2001 53 <2 <0.1 <1 4.1 <0.1 <0.14/24/2001 60 <2 NA <1 4.9 0.2 0.45/29/2001 57 <2 NA <1 4.3 0.2 <0.16/26/2001 NA <2 <0.1 <1 4.3 0.2 0.28/28/2001 49 <2 <0.1 <1 4.59/25/2001 53 <2 0.1 <1 6.0
10/23/2001 53 <2 <0.1 <1 4.1 0.1 0.111/27/2001 NA NA NA NA 6.6 <0.1 <0.112/26/2001 NA NA <0.05 NA 2.4 <0.1 0.31/29/2002 NA 2.8 <0.05 <0.03 5.6 0.1 0.12/26/2002 NA NA 0.1 <0.03 2.9 0.2 0.23/26/2002 NA 1 0.1 0.1 3.5 0.3 0.74/23/2002 NA NA NA NA 4.7 <0.1 <0.15/28/2002 NA NA NA 0.1 5.1 0.1 0.16/18/2002 NA 0.8 NA NA 4.2 0.4 0.68/27/2002 NA 1.1 0.1 0.1 NA <0.1 <0.19/24/2002 NA NA <0.05 0.1 4.1 0.1 0.2
10/29/2002 NA 0.8 <0.05 <0.03 1.8 0.1 0.211/19/2002 NA 4.5 <0.05 <0.03 1.8 0.3 0.312/17/2002 NA 1.3 0.1 <0.03 1.9 0.3 0.3
G1: 544SJC001 – New Jerusalem Tile Drain continued…
DateNitrate (mg/L)
Nitrate-N (mg/L)
TKN (mg/L)
Ammonia-N (mg/L)
Phosphorus (mg/L)
Ortho-phosphate-
P (mg/L)
Potassium (mg/L)
BOD 5 Day (mg/L)
BOD 10 Day (mg/L)
Count 10 NA 19 NA 19 21 24 23 23Min 49 NA 0.8 NA 0.03 0.02 1.8 0.1 0.1Max 77 NA 4.5 NA 0.1 0.5 19 0.4 0.7Mean 59 NA 1.3 NA 0.1 0.3 4.7 0.1 0.2Geo Mean 59 NA 1.1 NA 0.1 0.1 4.1 0.1 0.1Median 58 NA 1.0 NA 0.1 0.5 4.2 0.1 0.1Quartile 1 53 NA 1.0 NA 0.04 0.1 3.8 0.1 0.1Quartile 3 61 NA 1.0 NA 0.1 0.5 4.8 0.2 0.3NOTE: For values reported as < (less than), half the detection limit was used.
NA = Data not applicableINA = Site was inaccessibleDRY = Site had no flow
8
G1: 544SJC001 – New Jerusalem Tile Drain continued…
DateHardness
(mg/L)
Total Arsenic (ug/L)
Total Cadmium
(ug/L)
Total Chromium
(ug/L)
Total Copper (ug/L)
Total Lead (ug/L)
Total Nickel (ug/L)
Total Zinc (ug/L)
Total Mercury (ug/L)
10/24/2000 610 18 <1 <5 <5 <211/28/2000 640 20 <1 <5 <5 <212/27/2000 660 26 <1 <5 <5 <21/23/2001 630 22 <1 <5 <5 <22/20/2001 670 30 <1 <5 <5 <23/27/2001 740 23 <1 <5 <5 <24/24/2001 640 20 1.4 <5 <5 <25/29/2001 660 15 1.4 <5 <5 <26/26/2001 <2 <1 16 <1 <5 <5 <2 <0.27/24/2001 NA NA 20 <1 <5 <5 <2 NA8/28/2001 360 <2 <1 16 <1 <5 <5 <29/25/2001 590 <4 <0.1 17 2.4 <5 <5 <2 <0.2
10/23/2001 620 <4 <0.1 <1 22 <5 <5 <2 NA11/27/2001 610 <4 <0.1 23 1.1 <5 <5 6.4 <0.212/26/2001 660 4.8 <0.1 23 <1 <5 <5 <2 <0.21/29/2002 730 <4 <0.1 25 <1 <5 <5 <2 <0.23/26/2002 450 <4.0 <0.1 14 3.9 <5.0 <5.0 3.8 <0.24/23/2002 720 <4.0 <0.1 24 <1.0 <5.0 <5.0 <2.0 <0.25/28/2002 610 <4.0 <0.1 16 <1.0 <5.0 <5.0 <2.0 <0.26/18/2002 720 <4.0 <0.1 14 <1.0 <5.0 <5.0 <2.0 <0.29/24/2002 660 <4.0 <0.1 13 1.3 <5.0 <5.0 <2.0 <0.2
10/29/2002 590 <4.0 <0.1 16 2.4 <5.0 <5.0 <2.0 <0.211/19/2002 580 <4.0 <0.1 16 <1.0 <5.0 <5.0 <2.0 <0.23/25/2003 590 4.6 <0.1 18 <1.0 <5.0 <5.0 <2.0 <0.24/22/2003 720 4.2 <0.1 26 1.5 <5.0 <5.0 <2.0 <0.25/27/2003 680 <4.0 <0.1 19 2.5 <5.0 <5.0 <2.0 <0.26/24/2003 600 <4.0 <0.1 15 2.1 <5.0 <5.0 <2.0 <0.2
9
G1: 544SJC001 – New Jerusalem Tile Drain continued…
DateHardness
(mg/L)
Total Arsenic (ug/L)
Total Cadmium
(ug/L)
Total Chromium
(ug/L)
Total Copper (ug/L)
Total Lead (ug/L)
Total Nickel (ug/L)
Total Zinc (ug/L)
Total Mercury (ug/L)
Count 25 18 18 27 27 27 27 27 16Min 360 1 0.05 0.5 0.5 2.5 2.5 1.0 0.1Max 740 4.8 0.5 30 22 2.5 2.5 6.4 0.1Mean 630 2.3 0.1 19 1.9 2.5 2.5 1.3 0.1Geo Mean 620 2.1 0.1 17 0.9 2.5 2.5 1.1 0.1Median 640 2.0 0.1 18 0.5 2.5 2.5 1.0 0.1Quartile 1 600 2.0 0.1 16 0.5 2.5 2.5 1.0 0.1Quartile 3 670 2.0 0.1 23 1.5 2.5 2.5 1.0 0.1NOTE: For values reported as < (less than), half the detection limit was used.
NA = Data not applicableINA = Site was inaccessibleDRY = Site had no flow
10
G1: 544SJC001 – New Jerusalem Tile Drain continued…
DateHardness
(mg/L)
Dissolved Arsenic (ug/L)
Dissolved Cadmium
(ug/L)
Dissolved Chromium
(ug/L)
Dissolved Copper (ug/L)
Dissolved Lead (ug/L)
Dissolved Nickel (ug/L)
Dissolved Zinc
(ug/L)
Dissolved Mercury (ug/L)
10/24/2000 61011/28/2000 640 21 <1 <5 <5 <212/27/2000 660 27 <1 <5 <5 <21/23/2001 630 22 <1 <5 <52/20/2001 670 30 <1 <5 <5 <23/27/2001 740 24 <1 <5 <5 <24/24/2001 640 21 <1 <5 <5 <25/29/2001 660 15 <1 <5 <5 <26/26/2001 <2 <1 16 <1 <5 <5 <2 <0.27/24/2001 NA NA NA NA NA NA NA NA8/28/2001 360 <2 <1 17 <1 <5 <5 <29/25/2001 590 <4 <0.1 18 2.6 <5 <5 11 <0.2
10/23/2001 620 <4 <0.1 <1 21 <5 <5 <2 NA11/27/2001 610 <4 <0.1 25 <1 <5 <5 4 <0.212/26/2001 660 4.7 <0.1 23 1.1 <5 <5 2.3 <0.21/29/2002 730 <4 <0.1 18 <1 <5 <5 <2 <0.23/26/2002 450 <4.0 <0.1 12 2.7 <5.0 <5.0 2.6 <0.24/23/2002 720 5.8 <0.1 23 <1.0 <5.0 <5.0 <2.0 <0.25/28/2002 610 <4.0 <0.1 16 1.2 <5.0 <5.0 <2.0 <0.26/18/2002 720 <4.0 <0.1 4.5 <1.0 <5.0 <5.0 <2.0 <0.29/24/2002 660 <4.0 <0.1 14 1.6 <5.0 <5.0 <2.0 <0.2
10/29/2002 590 <4.0 <0.1 16 1.1 <5.0 <5.0 <2.0 <0.211/19/2002 580 <4.0 <0.1 15 <1.0 <5.0 <5.0 <2.0 <0.2
11
G1: 544SJC001 – New Jerusalem Tile Drain continued…
DateHardness
(mg/L)
Dissolved Arsenic (ug/L)
Dissolved Cadmium
(ug/L)
Dissolved Chromium
(ug/L)
Dissolved Copper (ug/L)
Dissolved Lead (ug/L)
Dissolved Nickel (ug/L)
Dissolved Zinc
(ug/L)
Dissolved Mercury (ug/L)
Count 21 14 14 21 21 21 21 20 12Min 360 1 0.05 0.5 0.5 2.5 2.5 1.0 0.1Max 740 5.8 0.5 30 21 2.5 2.5 11 0.1Mean 630 2.3 0.1 18 1.8 2.5 2.5 1.8 0.1Geo Mean 620 2.1 0.1 15 0.8 2.5 2.5 1.3 0.1Median 640 2.0 0.1 18 0.5 2.5 2.5 1.0 0.1Quartile 1 610 2.0 0.1 15 0.5 2.5 2.5 1.0 0.1Quartile 3 660 2.0 0.1 23 1.1 2.5 2.5 1.0 0.1NOTE: For values reported as < (less than), half the detection limit was used.
NA = Data not applicableINA = Site was inaccessibleDRY = Site had no flow
12
G1: 544SJC001 – New Jerusalem Tile Drain continued…
DateChloride (mg/L)
Sulfate (mg/L)
Calcium (mg/L)
Magnesium (mg/L)
TDS (mg/L)
Carbonate (mg/L)
Bicarbonate (mg/L)
Total Alkalinity
(mg/L)Sodium (mg/L)
10/24/2000 280 420 150 60 1600 <1 380 310 29011/28/2000 310 420 150 62 1600 <1 370 300 32012/27/2000 320 500 160 65 1700 <1 370 300 3201/23/2001 280 420 150 61 1600 <1 370 300 3102/20/2001 310 520 160 67 1700 <1 360 300 3203/27/2001 360 520 180 71 NA <1 380 310 3304/24/2001 280 610 150 61 1600 <1 320 270 2805/29/2001 290 500 160 63 1700 <1 300 300 3108/28/2001 280 410 51 56 1600 <1 380 310 2909/25/2001 280 410 140 60 NA <1 350 280 280
10/23/2001 300 490 150 61 NA <1 380 310 32011/27/2001 290 450 150 60 1600 <1 370 300 31012/26/2001 310 570 160 62 1800 <1 360 300 3101/29/2002 350 590 180 71 1900 <1 370 300 3303/26/2002 220 320 110 5 1100 <1.0 260 210 2104/23/2002 300 540 180 69 1700 <1.0 340 280 3205/28/2002 340 470 150 58 NA <1.0 350 290 3106/18/2002 330 470 170 69 NA <1.0 360 NA 3409/24/2002 340 400 150 67 NA <1.0 370 310 310
10/29/2002 310 360 140 57 1500 <1.0 370 310 28011/19/2002 320 430 140 57 1500 <1.0 360 300 2803/25/2003 300 390 140 584/22/2003 350 510 170 725/27/2003 310 480 160 666/24/2003 310 430 140 58
13
14
G1: 544SJC001 – New Jerusalem Tile Drain continued…
DateChloride (mg/L)
Sulfate (mg/L)
Calcium (mg/L)
Magnesium (mg/L)
TDS (mg/L)
Carbonate (mg/L)
Bicarbonate (mg/L)
Total Alkalinity
(mg/L)Sodium (mg/L)
Count 25 25 25 25 15 21 21 20 21Min 220 320 51 5 1100 0.5 260 210 210Max 360 610 180 72 1900 0.5 380 310 340Mean 310 470 150 61 1600 0.5 360 290 300Geo Mean 310 460 150 60 1600 0.5 350 290 300Median 310 470 150 61 1600 0.5 370 300 310Quartile 1 290 420 140 58 1600 0.5 350 300 290Quartile 3 320 510 160 67 1700 0.5 370 310 320NOTE: For values reported as < (less than), half the detection limit was used.
NA = Data not applicableINA = Site was inaccessibleDRY = Site had no flow
G1: 544SJC001 – New Jerusalem Tile Drain continued…
Date Result Control Result Control
Result (million/m
l)
Control (million/
ml)MDD (%)
10/24/2000 100 100 NA NA1/23/2001 100 100 NA NA2/20/2001 70* 90 90 1003/27/2001 100 100 100 1004/24/2001 100 90 100 805/29/2001 85 95 90 1006/27/2001 100 100 100 100
10/23/2001 100 100 90 10012/26/2001 95 100 70* 1001/29/2002 100 100 100 1004/23/2002 95 95 90 1005/28/2002 100 100 100 100
10/29/2002 100 95 100 10011/19/2002 100 100 100 1004/22/2003 100 100 100 100 5.07** 2.00 175/28/2003 100 100 NA NA 5.45** 2.04 48
11/22/2004 100 100 100 1001/26/2005 100 97.5 80* 1002/23/2005 100 100 100 1003/31/2005 100 100 100 1004/26/2005 92.5 100 100 1005/24/2005 100 100 80* 1006/28/2005 100 100 100 1007/26/2005 97.5 100 100 1008/23/2005 100 100 90 1009/27/2005 100 100 100 100
Count 26 26 23 23 2 2 2
* Significantly reduced from the lab control.** Significantly greater than the lab control.^ Fish were from a "forced hatch," duplicate failed QA.1 Duplicate sample for the set was low - 77% recovery.
3 Samples qualified, but duplicate sample recovery for the set was high - 126% (53.8%/42.5%)NA = Data not applicableINA = Site was inaccessibleDRY = Site had no flow
2 Testing for the Fathead minnow was initiated when samples were approx. 48h old due to untimely shipping of fish by fish supplier.
96h Acute Fathead Minnow
(% Survival)
48h Acute Ceriodaphnia Dubia
(% Survival) Algae Cell Growth
15
G2: 544SJC505 – Tom Paine Slough at Paradise Road Station Code:544SJC505
Location: Latitude 37.77417, Longitude -121.38222
Date TimeTemp (ºC)
Field SC (umhos) pH
Dissolved Oxygen (mg/L)
Turbidity (ntu)
10/24/2000 10:40 AM 14.3 2920 7.811/28/2000 12:15 PM 10.0 2100 7.212/27/2000 10:15 AM 7.2 2980 8.11/23/2001 10:10 AM 9.0 2920 6.92/20/2001 10:29 AM 11.5 2200 7.63/27/2001 10:27 AM 16.9 2580 7.44/24/2001 11:30 AM 21.7 955 7.25/29/2001 12:20 PM 21.9 812 7.56/26/2001 10:57 AM 21.9 1010 7.5 4.27/24/2001 9:32 AM 23.4 1090 7.4 3.48/28/2001 10:38 AM 24.4 1060 7.7 6.89/25/2001 11:21 AM 21.0 1150 7.8 10.9
10/23/2001 10:48 AM 17.2 1590 7.6 8.911/27/2001 9:59 AM 10.3 2780 7.5 6.412/26/2001 10:50 AM 10.6 2860 7.3 NA1/29/2002 9:29 AM 7.8 3040 7.9 10.32/26/2002 10:11 AM 15.0 3110 8.0 13.63/26/2002 10:46 AM 15.6 1260 7.3 5.44/23/2002 10:42 AM 18.8 1030 7.5 5.45/28/2002 10:42 AM 20.9 845 7.8 8.36/18/2002 10:50 AM 21.6 1070 7.6 5.57/31/2002 INA INA INA INA INA INA8/27/2002 11:00 AM 22.4 1240 NA NA9/24/2002 11:16 AM 23.9 1210 7.5 4.8
10/15/2002 10:05 AM 18.0 1460 7.7 10.6 16.910/29/2002 10:37 AM 15.4 2220 7.4 10.4 13.411/19/2002 9:33 AM 12.8 2700 7.5 7.212/17/2002 9:50 AM 11.1 1240 7.8 9.5 52.71/15/2003 9:18 AM 13.0 1610 7.5 7.0 17.11/28/2003 10:05 AM 13.3 2570 8.0 14.3 38.13/25/2003 8:53 AM 15.9 1660 7.6 8.3 15.14/22/2003 10:14 AM 15.6 1110 8.0 8.6 13.25/27/2003 9:54 AM 20.5 1090 7.2 5.5 15.26/24/2003 10:56 AM 19.9 1240 7.7 8.1 3.97/29/2003 9:09 AM 25.7 918 7.3 2.2 4.08/26/2003 10:42 AM 25.5 1120 7.5 5.4 12.49/23/2003 10:17 AM 22.6 1430 7.1 4.3 10.5
10/28/2003 10:18 AM 17.6 1530 7.2 6.1 8.711/18/2003 9:45 AM 13.5 2660 7.4 8.0 551/28/2004 9:45 AM INA INA INA INA INA2/24/2004 10:16 AM 13.0 2820 7.5 5.6 110
16
G2: 544SJC505 – Tom Paine Slough at Paradise Road continued…
Date TimeTemp (ºC)
Field SC (umhos) pH
Dissolved Oxygen (mg/L)
Turbidity (ntu)
3/24/2004 9:07 AM 16.2 3060 7.4 3.6 5.94/28/2004 9:04 AM 21.7 1030 7.1 10.5 48.55/26/2004 10:30 AM INA INA INA INA INA6/23/2004 9:06 AM 21.2 1190 7.0 3.5 NA7/28/2004 9:58 AM INA INA INA INA INA8/25/2004 9:19 AM 22.0 1120 6.9 2.7 NA9/29/2004 10:03 AM 19.7 1500 7.3 5.8 NA
10/27/2004 10:05 AM 14.7 2220 7.3 4.711/22/2004 10:47 AM 10.9 2990 7.4 9.612/28/2004 9:42 AM 8.4 2890 7.2 8.31/26/2005 9:54 AM 10.1 3180 7.6 6.82/23/2005 9:25 AM 14.9 2900 8.2 16.23/29/2005 10:36 AM 15.5 2950 7.9 13.94/26/2005 10:20 AM 16.8 762 7.4 7.95/24/2005 9:42 AM 20.9 767 7.7 9.26/28/2005 9:38 AM 19.1 784 7.1 6.57/26/2005 9:39 AM 25.2 894 7.4 5.08/23/2005 9:45 AM 23.5 781 7.5 7.69/27/2005 10:25 AM 19.3 1030 7.8 14.3
Count 56 56 55 46 17Min 7.2 762 6.9 2.2 3.9Max 25.7 3180 8.2 16.2 110Mean 17.2 1770 7.5 7.6 25.9Geo Mean 16.3 1580 7.5 7.0 16.9Median 17.1 1450 7.5 7.1 15.1Quartile 1 13.2 1070 7.3 5.4 10.5Quartile 3 21.6 2720 7.7 9.4 38.1NOTE: For values reported as < (less than), half the detection limit was used.
NA = Data not applicableINA = Site was inaccessibleDRY = Site had no flow
17
G2: 544SJC505 – Tom Paine Slough at Paradise Road continued…
DateTSS
(mg/L)TOC
(mg/L)Total Coli
MPNE. coli MPN
10/24/2000 59 4.211/28/2000 22 <112/27/2000 31 2.41/23/2001 32 5.32/20/2001 28 <13/27/2001 27 NA4/24/2001 26 4.55/29/2001 18 4.56/26/2001 18 8.97/24/2001 6.38/28/2001 27 8.89/25/2001 NA 14
10/23/2001 312/26/2002 NA3/26/2002 1.94/23/2002 NA5/28/2002 <1.06/18/2002 4.27/31/2002 INA INA8/27/2002 4.19/24/2002 4.8
10/15/2002 >2419.6 3810/29/2002 6.011/19/2002 3.91/15/2003 1553 273/25/2003 4.24/22/2003 5.0 1986 335/27/2003 NA6/24/2003 NA7/29/2003 >2419.6 608/26/2003 >2419.6 339/23/2003 >2419.6 12
10/28/2003 >2419.6 23611/18/2003 >2419.6 2191/28/2004 INA INA2/24/2004 629 673/24/2004 >2419.6 8164/28/2004 >2419.6 885/26/2004 INA INA6/23/2004 >2419.6 7277/28/2004 INA INA8/25/2004 >2419.6 939/29/2004 >2419.6 7
10/27/2004 6.0 >2419.6 2011/22/2004 5.3 1203 54
18
19
DateTSS
(mg/L)TOC
(mg/L)Total Coli
MPNE. coli MPN
12/28/2004 5.0 >2419.6 2601/26/2005 6.4 >2419.6 382/23/2005 8.6 313 243/29/2005 15 >2419.6 144/26/2005 NA >2419.6 1075/24/2005 NA >2419.6 386/28/2005 4.8 >2419.6 1847/26/2005 NA >2419.6 898/23/2005 4.2 >2419.6 409/27/2005 5.5 >2419.6 24
Count 10 30 26 26Min 18 0.5 313 7Max 59 31 2420 816Mean 29 6.2 NA NAGeo Mean 27 4.5 2017 61MedQuaQuaNOT
NA =INA =DRY
G2: 544SJC505 – Tom Paine Slough at Paradise Road continued…
ian 27 4.9 2420 47rtile 1 23 4.2 2420 29rtile 3 30 6.2 2420 104E: For values reported as < (less than), half the detection limit was used For values reported as > (greater than), 2420 was used
Data not applicable Site was inaccessible
= Site had no flow
G2: 544SJC505 – Tom Paine Slough at Paradise Road continued…
DateNitrate (mg/L)
Nitrate-N (mg/L)
TKN (mg/L)
Ammonia-N (mg/L)
Phosphorus (mg/L)
Ortho-phosphate-
P (mg/L)
Potassium (mg/L)
BOD 5-Day (mg/L)
BOD 10-Day (mg/L)
10/24/2000 <2 2.1 0.3 <1 8.6 8.4 15.011/28/2000 4.0 <2 0.2 <1 7.3 2.6 4.812/27/2000 2.8 <2 0.1 <1 7.5 4.8 8.11/23/2001 2.4 <2 0.1 <1 7.4 6.8 12.02/20/2001 1.0 <2 0.2 0.2 7.8 6.6 11.53/27/2001 <2 2.0 0.2 <1 9.3 7.9 12.34/24/2001 4.9 <2 0.1 <1 5.4 5.1 8.05/29/2001 5.8 <2 0.3 <1 5.4 1.6 2.56/26/2001 7.6 <2 0.4 <1 8.4 4.3 5.98/28/2001 8.0 <2 0.3 <1 5.99/25/2001 5.7 <2 0.3 <1 6.9
10/23/2001 <2 <2 0.2 <1 7.911/27/2001 NA NA NA 0.1 11 4.4 6.912/26/2001 NA NA 0.2 NA 4.0 3.1 7.21/29/2002 NA 1.1 0.1 0.1 14 5.1 8.02/26/2002 NA NA 0.3 <0.03 7.3 8.6 16.03/26/2002 NA 0.9 0.2 0.1 4.3 2.5 4.24/23/2002 NA NA NA NA 6.3 3.2 4.95/28/2002 NA NA NA 0.2 4.0 1.6 2.56/18/2002 NA 0.6 NA 0.3 6.7 1.3 2.28/27/2002 NA 0.6 0.2 0.2 NA 0.8 1.59/24/2002 NA NA 0.2 0.2 5.8 1.8 3.9
10/29/2002 NA 1.3 0.2 <0.03 4.5 8.6 13.611/19/2002 NA 1.4 0.2 0.1 4.4 4.7 8.212/17/2002 NA 1.5 0.2 0.1 2.0 2.4 4.81/28/2003 NA 1.3 0.2 <0.03 3.2 6.7 12.4
20
G2: 544SJC505 – Tom Paine Slough at Paradise Road continued…
DateNitrate (mg/L)
Nitrate-N (mg/L)
TKN (mg/L)
Ammonia-N (mg/L)
Phosphorus (mg/L)
Ortho-phosphate-
P (mg/L)
Potassium (mg/L)
BOD 5-Day (mg/L)
BOD 10-Day (mg/L)
Count 12 NA 20 NA 22 24 25 23 23Min 1 NA 0.6 NA 0.1 0.02 2.0 0.8 1.5Max 8.0 NA 2.1 NA 0.4 0.5 14 8.6 16.0Mean 3.8 NA 1.1 NA 0.2 0.3 6.6 4.5 7.7Geo Mean 2.8 NA 1.1 NA 0.2 0.2 6.1 3.7 6.4Median 3.4 NA 1.0 NA 0.2 0.3 6.7 4.4 7.2Quartile 1 1.0 NA 1.0 NA 0.2 0.1 4.5 2.5 4.5Quartile 3 5.7 NA 1.3 NA 0.3 0.5 7.8 6.7 11.8NOTE: For values reported as < (less than), half the detection limit was used.
NA = Data not applicableINA = Site was inaccessibleDRY = Site had no flow
21
G2: 544SJC505 – Tom Paine Slough at Paradise Road continued…
DateHardness
(mg/L)
Total Arsenic (ug/L)
Total Cadmium
(ug/L)
Total Chromium
(ug/L)
Total Copper (ug/L)
Total Lead (ug/L)
Total Nickel (ug/L)
Total Zinc (ug/L)
Total Mercury (ug/L)
10/24/2000 700 1.2 1.9 <5 <5 <211/28/2000 770 <1 1.1 <5 <5 <212/27/2000 750 <1 1.0 <5 <5 <21/23/2001 730 <1 1.9 <5 <5 <22/20/2001 530 <1 1.6 <5 <5 <23/27/2001 610 <1 2.2 <5 <5 <24/24/2001 220 <1 2.5 <5 <5 2.75/29/2001 190 <1 3.2 <5 <5 3.46/26/2001 5.7 <1 9.7 11 <5 13 23 <0.27/24/2001 NA NA <1 2.2 <5 <5 4.3 NA8/28/2001 230 3.5 <1 1.3 2.1 <5 <5 3.39/25/2001 270 <4 <0.1 <1 2.2 <5 <5 <2 <0.2
10/23/2001 360 5.9 <0.1 <1 2.1 <5 <5 3.2 NA11/27/2001 740 <4 <0.1 <1 1.3 <5 <5 2.1 <0.212/26/2001 710 5.1 <0.1 2.0 3.1 <5 <5 7.2 <0.21/29/2002 750 <4 <0.1 <1 <1 <5 <5 <2 <0.23/26/2002 300 <4.0 <0.1 1.2 3.1 <5.0 8.2 5.8 <0.24/23/2002 250 <4.0 <0.1 <1.0 2.3 <5.0 <5.0 <2.0 <0.25/28/2002 200 <4.0 <0.1 1.1 4.0 <5.0 <5.0 2.6 <0.26/18/2002 270 4.4 <0.1 <1.0 1.6 <5.0 <5.0 <2.0 <0.29/24/2002 280 5.2 <0.1 <1.0 2.7 <5.0 <5.0 3.3 <0.2
10/29/2002 520 5.9 <0.1 <1.0 2.3 <5.0 <5.0 <2.0 <0.211/19/2002 690 4.9 <0.1 <1.0 <1.0 <5.0 <5.0 <2.0 <0.23/25/2003 390 4.9 <0.1 <1.0 1.7 <5.0 <5.0 <2.0 <0.24/22/2003 250 <4.0 <0.1 <1.0 2.7 <5.0 <5.0 <2.0 <0.25/27/2003 250 4.8 <0.1 <1.0 3.0 <5.0 <5.0 <2.0 <0.26/24/2003 300 4.2 <0.1 <1.0 1.6 <5.0 <5.0 <2.0 <0.2
22
G2: 544SJC505 – Tom Paine Slough at Paradise Road continued…
DateHardness
(mg/L)
Total Arsenic (ug/L)
Total Cadmium
(ug/L)
Total Chromium
(ug/L)
Total Copper (ug/L)
Total Lead (ug/L)
Total Nickel (ug/L)
Total Zinc (ug/L)
Total Mercury (ug/L)
Count 25 18 18 27 27 27 27 27 16Min 190 2.0 0.1 0.5 0.5 2.5 2.5 1.0 0.1Max 770 5.9 0.5 9.7 11 2.5 13 23 0.1Mean 450 3.8 0.1 1.0 2.4 2.5 3.1 2.8 0.1Geo Mean 400 3.5 0.1 0.7 2.0 2.5 2.8 1.8 0.1Median 360 4.3 0.1 0.5 2.2 2.5 2.5 1.0 0.1Quartile 1 250 2.0 0.1 0.5 1.6 2.5 2.5 1.0 0.1Quartile 3 700 5.1 0.1 0.5 2.7 2.5 2.5 3.3 0.1NOTE: For values reported as < (less than), half the detection limit was used.
NA = Data not applicableINA = Site was inaccessibleDRY = Site had no flow
23
G2: 544SJC505 – Tom Paine Slough at Paradise Road continued…
DateHardness
(mg/L)
Dissolved Arsenic (ug/L)
Dissolved Cadmium
(ug/L)
Dissolved Chromium
(ug/L)
Dissolved Copper (ug/L)
Dissolved Lead (ug/L)
Dissolved Nickel (ug/L)
Dissolved Zinc
(ug/L)
Dissolved Mercury (ug/L)
10/24/2000 70011/28/2000 770 <1 <1 <5 <5 <212/27/2000 750 <1 <1 <5 <5 <21/23/2001 730 <1 <1 <5 <5 <22/20/2001 530 <1 <1 <5 <5 <23/27/2001 610 <1 <1 <5 <5 <24/24/2001 220 <1 1.1 <5 <5 <25/29/2001 190 <1 1.4 <5 <5 2.36/26/2001 3.2 <1 <1 <1 <5 <5 2.8 <0.27/24/2001 NA NA NA NA NA NA NA NA8/28/2001 230 3.3 <1 <1 <1 <5 <5 <29/25/2001 270 <4 <0.1 <1 1.8 <5 <5 <2 <0.2
10/23/2001 360 5.2 <0.1 <1 2.1 <5 <5 2.9 NA11/27/2001 740 <4 <0.1 <1 <1 <5 <5 5.4 <0.212/26/2001 710 4.0 <0.1 <1 1.1 <5 <5 <2 <0.21/29/2002 750 <4 <0.1 <1 <1 <5 <5 <2 <0.23/26/2002 300 <4.0 <0.1 <1.0 1.7 <5.0 5.1 4.8 <0.24/23/2002 250 5.6 <0.1 <1.0 2.1 <5.0 <5.0 <2.0 <0.25/28/2002 200 <4.0 <0.1 <1.0 3.1 <5.0 <5.0 2.2 <0.26/18/2002 270 <4.0 <0.1 <1.0 <1.0 <5.0 <5.0 <2.0 <0.29/24/2002 280 4.9 <0.1 <1.0 2.5 <5.0 <5.0 <2.0 <0.2
10/29/2002 520 <4.0 <0.1 <1.0 <1.0 <5.0 <5.0 <2.0 <0.211/19/2002 690 <4.0 <0.1 <1.0 <1.0 <5.0 <5.0 <2.0 <0.2
24
G2: 544SJC505 – Tom Paine Slough at Paradise Road continued…
DateHardness
(mg/L)
Dissolved Arsenic (ug/L)
Dissolved Cadmium
(ug/L)
Dissolved Chromium
(ug/L)
Dissolved Copper (ug/L)
Dissolved Lead (ug/L)
Dissolved Nickel (ug/L)
Dissolved Zinc
(ug/L)
Dissolved Mercury (ug/L)
Count 21 14 14 21 21 21 21 21 12Min 190 2.0 0.1 0.5 0.5 2.5 2.5 1.0 0.1Max 770 5.6 0.5 0.5 3.1 2.5 5.1 5.4 0.1Mean 480 3.0 0.1 0.5 1.1 2.5 2.6 1.7 0.1Geo Mean 420 2.8 0.1 0.5 0.9 2.5 2.6 1.4 0.1Median 520 2.0 0.1 0.5 0.5 2.5 2.5 1.0 0.1Quartile 1 270 2.0 0.1 0.5 0.5 2.5 2.5 1.0 0.1Quartile 3 710 3.8 0.1 0.5 1.7 2.5 2.5 2.2 0.1NOTE: For values reported as < (less than), half the detection limit was used.
NA = Data not applicableINA = Site was inaccessibleDRY = Site had no flow
25
G2: 544SJC505 – Tom Paine Slough at Paradise Road continued…
DateChloride (mg/L)
Sulfate (mg/L)
Calcium (mg/L)
Magnesium (mg/L)
TDS (mg/L)
Carbonate (mg/L)
Bicarbonate (mg/L)
Total Alkalinity
(mg/L)Sodium (mg/L)
10/24/2000 440 460 140 88 1800 <1 390 320 37011/28/2000 470 460 160 89 2000 <1 410 340 38012/27/2000 480 490 150 88 1900 <1 390 320 3601/23/2001 450 460 150 87 1900 <1 370 300 3702/20/2001 340 350 110 64 1300 <1 330 270 2703/27/2001 430 410 120 76 NA <1 360 290 3204/24/2001 130 120 47 25 550 <1 168 138 1005/29/2001 100 95 42 21 450 <1 110 110 858/28/2001 140 130 49 26 630 <1 190 150 1209/25/2001 160 140 58 31 NA <1 210 170 140
10/23/2001 240 220 74 43 NA <1 270 220 21011/27/2001 500 480 150 86 1800 <1 390 320 36012/26/2001 460 450 150 83 1800 <1 290 240 3401/29/2002 470 490 160 87 2000 <1 390 320 3703/26/2002 180 180 66 34 710 <1.0 200 160 1504/23/2002 150 140 55 28 580 <1.0 170 140 1205/28/2002 120 120 45 23 NA <1.0 150 120 966/18/2002 140 130 58 29 NA <1.0 190 NA 1309/24/2002 170 150 58 33 NA <1.0 210 170 160
10/29/2002 340 330 110 62 1400 <1.0 380 320 30011/19/2002 490 450 150 78 1800 <1.0 400 330 3503/25/2003 250 250 84 444/22/2003 150 150 50 305/27/2003 150 140 53 296/24/2003 190 170 63 34
26
27
G2: 544SJC505 – Tom Paine Slough at Paradise Road continued…
DateChloride (mg/L)
Sulfate (mg/L)
Calcium (mg/L)
Magnesium (mg/L)
TDS (mg/L)
Carbonate (mg/L)
Bicarbonate (mg/L)
Total Alkalinity
(mg/L)Sodium (mg/L)
Count 25 25 25 25 15 21 21 20 21Min 100 95 42 21 450 0.5 110 110 85Max 500 490 160 89 2000 0.5 410 340 380Mean 280 280 94 53 1400 0.5 280 240 240Geo Mean 250 240 84 46 1200 0.5 260 220 210Median 240 220 74 43 1800 0.5 290 260 270Quartile 1 150 140 55 29 670 0.5 190 160 130Quartile 3 450 450 150 83 1900 0.5 390 320 360NOTE: For values reported as < (less than), half the detection limit was used.
NA = Data not applicableINA = Site was inaccessibleDRY = Site had no flow
G2: 544SJC505 – Tom Paine Slough at Paradise Road continued…
Date Result Control Result Control
Result (million/m
l)
Control (million/m
l) MDD(%)1/28/2003 95 100 90 100 1.7* 3.10 NA
Count 1 1 1 1 1 1 N/A
* Significantly reduced from the lab control.** Significantly greater than the lab control.^ Fish were from a "forced hatch," duplicate failed QA.1 Duplicate sample for the set was low - 77% recovery.
3 Samples qualified, but duplicate sample recovery for the set was high - 126% (53.8%/42.5%)NA = Data not applicableINA = Site was inaccessibleDRY = Site had no flow
96h Acute Fathead Minnow
(% Survival)
48h Acute Ceriodaphnia Dubia
(% Survival) Algae Cell Growth
2 Testing for the Fathead minnow was initiated when samples were approx. 48h old due to untimely shipping of fish by fish supplier.
28
G3: 544SJC506 – Old River at Tracy Blvd Station Code:544SJC506
Location: Latitude 37.80472, Longitude -121.44944
Date TimeTemp (ºC)
Field SC (umhos) pH
Dissolved Oxygen (mg/L)
Turbidity (ntu)
10/24/2000 11:00 AM 15.8 984 8.211/28/2000 12:40 PM 10.0 802 8.212/27/2000 10:40 AM 8.4 824 6.91/23/2001 10:30 AM 9.3 949 7.72/20/2001 10:49 AM 11.6 718 8.23/27/2001 10:47 AM 18.6 1190 8.04/24/2001 12:15 PM 20.1 498 6.55/29/2001 11:50 AM 22.2 768 7.56/26/2001 11:30 AM 23.0 941 7.6 5.27/24/2001 9:50 AM 23.9 816 7.7 6.78/28/2001 11:10 AM 25.4 875 8.0 8.59/25/2001 10:58 AM 22.6 754 7.8 9.4
10/23/2001 10:22 AM 18.1 852 7.8 8.111/27/2001 10:23 AM 11.8 808 7.3 8.512/26/2001 11:10 AM 10.3 1200 8.0 NA1/29/2002 9:47 AM 8.4 1140 8.0 11.32/26/2002 9:22 AM 14.8 1070 7.8 10.03/26/2002 11:02 AM 15.6 1040 7.8 10.84/23/2002 11:20 AM 19.0 1080 7.9 7.65/28/2002 9:45 AM 20.5 617 8.1 12.06/18/2002 10:26 AM 23.1 827 7.6 5.37/31/2002 10:29 AM 24.4 889 8.3 6.3 55.98/27/2002 10:35 AM 23.8 932 NA NA9/24/2002 10:55 AM 23.9 899 7.5 3.3
10/15/2002 9:45 AM 19.2 1070 8.0 8.9 22.010/29/2002 11:02 AM 16.3 693 7.9 7.2 24.711/19/2002 9:51 AM 13.1 883 7.7 7.712/17/2002 9:29 AM 11.4 952 7.8 9.3 37.21/15/2003 9:36 AM 12.6 1110 7.7 8.9 26.61/28/2003 9:54 AM 13.0 1140 7.6 10.1 33.33/25/2003 9:30 AM 16.0 1230 7.8 12.6 30.24/22/2003 9:06 AM 14.9 793 7.7 9.9 33.95/27/2003 10:14 AM 22.3 617 8.5 10.9 32.06/24/2003 10:22 AM 21.0 694 8.1 9.3 50.97/29/2003 8:00 AM 26.6 727 7.7 6.6 42.88/26/2003 9:57 AM 26.3 771 8.0 5.7 46.59/23/2003 9:55 AM 23.4 785 7.9 9.0 26.8
10/28/2003 10:38 AM 18.9 572 7.8 8.3 20.611/18/2003 10:05 AM 15.6 864 7.8 8.8 19.31/28/2004 9:28 AM 10.1 1090 7.7 14.4 53.0
29
G3: 544SJC506 – Old River at Tracy Blvd continued…
Date TimeTemp (ºC)
Field SC (umhos) pH
Dissolved Oxygen (mg/L)
Turbidity (ntu)
2/24/2004 10:00 AM 13.2 837 7.6 8.7 41.73/24/2004 8:47 AM 16.9 769 8.0 10.2 32.14/28/2004 8:44 AM 20.8 773 7.5 11.0 32.45/26/2004 10:05 AM 19.7 767 8.2 11.4 30.76/23/2004 8:46 AM 21.2 745 7.7 7.2 NA7/28/2004 9:40 AM 25.8 833 8.1 7.3 NA8/25/2004 9:37 AM 23.0 830 7.6 6.2 NA9/29/2004 9:40 AM 20.4 943 7.4 8.3 NA
10/27/2004 9:38 AM 15.4 979 7.5 7.611/22/2004 10:29 AM 11.6 1140 7.6 9.412/28/2004 9:25 AM 8.9 1020 7.6 12.61/26/2005 9:37 AM 9.7 776 7.6 9.12/23/2005 9:07 AM 13.5 650 7.5 8.23/29/2005 10:19 AM 13.9 324 7.4 9.24/26/2005 10:03 AM 15.2 438 7.4 10.65/24/2005 9:21 AM 17.6 150 7.5 8.86/28/2005 9:21 AM 19.6 449 7.1 8.37/26/2005 9:23 AM 25.4 465 7.4 7.28/23/2005 9:24 AM 23.3 628 7.4 6.89/27/2005 10:04 AM 20.1 570 7.5 10.6
Count 60 60 59 50 20Min 8.4 150 6.5 3.3 19.3Max 26.6 1230 8.5 14.4 55.9Mean 17.7 826 7.7 8.8 34.6Geo Mean 16.8 787 7.7 8.5 33.1Median 18.4 826 7.7 8.8 32.3Quartile 1 13.2 725 7.5 7.4 26.8Quartile 3 22.4 959 8.0 10.1 42.0NOTE: For values reported as < (less than), half the detection limit was used.
NA = Data not applicableINA = Site was inaccessibleDRY = Site had no flow
30
G3: 544SJC506 – Old River at Tracy Blvd continued…
DateTSS
(mg/L)TOC
(mg/L)Total Coli
MPNE. coli MPN
10/24/2000 36 1.811/28/2000 21 1.412/27/2000 14 1.61/23/2001 23 3.12/20/2001 22 1.53/27/2001 38 NA4/24/2001 27 3.25/29/2001 44 4.76/26/2001 32 4.57/24/2001 5.78/28/2001 20 8.59/25/2001 NA 9.8
10/23/2001 172/26/2002 NA3/26/2002 3.04/23/2002 NA5/28/2002 8.96/18/2002 3.87/31/2002 >2419.6 598/27/2002 5.09/24/2002 4.3
10/15/2002 >2419.6 4010/29/2002 2.811/19/2002 4.112/17/2002 3.61/15/2003 >2419.6 1203/25/2003 4.04/22/2003 4.3 980 1085/27/2003 NA6/24/2003 NA7/29/2003 >2419.6 1978/26/2003 >2419.6 579/23/2003 >2419.6 50
10/28/2003 >2419.6 7011/18/2003 >2419.6 501/28/2004 >2419.6 502/24/2004 1414 753/24/2004 1203 464/28/2004 >2419.6 595/26/2004 >2419.6 586/23/2004 >2419.6 467/28/2004 >2419.6 298/25/2004 >2419.6 259/29/2004 >2419.6 28
31
32
DateTSS
(mg/L)TOC
(mg/L)Total Coli
MPNE. coli MPN
10/27/2004 4.6 >2419.6 11911/22/2004 5.6 >2419.6 4812/28/2004 4.0 >2419.6 2141/26/2005 8.3 >2419.6 932/23/2005 9.9 770 3453/29/2005 6.5 2420 1674/26/2005 NA >2419.6 695/24/2005 NA >2419.6 2616/28/2005 3.9 >2419.6 597/26/2005 NA >2419.6 888/23/2005 3.5 >2419.6 799/27/2005 3.3 >2419.6 63
Count 10 31 30 30Min 14 1.4 770 2
G3: 544SJC506 – Old River at Tracy Blvd continued…
5Max 44 17 2420 345Mean 28 5.0 NA NAGeo Mean 26 4.3 2169 74Median 25 4.1 2420 61Quartile 1 21 3.3 2420 50Quartile 3 35 5.7 2420 104NOTE: For values reported as < (less than), half the detection limit wa
For values reported as > (greater than), 2420 was used
Data not applicable Site was inaccessible
= Site had no flow
NA =INA =DRY
G3: 544SJC506 – Old River at Tracy Blvd continued…
DateNitrate (mg/L)
Nitrate-N (mg/L)
TKN (mg/L)
Ammonia-N (mg/L)
Phosphorus (mg/L)
Ortho-phosphate-
P (mg/L)
Potassium (mg/L)
BOD 5-Day (mg/L)
BOD 10-Day (mg/L)
Count 12 NA 20 NA 22 24 25 24 24Min 4.8 NA 0.6 NA 0.2 0.1 3.0 1.2 2.5Max 10.0 NA 2.1 NA 0.7 0.5 8.1 6.1 10.4Mean 7.6 NA 1.1 NA 0.3 0.3 5.3 3.0 5.1Geo Mean 7.4 NA 1.1 NA 0.2 0.3 5.1 2.6 4.6Median 7.9 NA 1.0 NA 0.2 0.2 5.3 2.6 4.2Quartile 1 6.8 NA 1.0 NA 0.2 0.2 4.4 1.9 3.3Quartile 3 8.4 NA 1.1 NA 0.3 0.5 5.9 3.7 6.4NOTE: For values reported as < (less than), half the detection limit was used.
NA = Data not applicableINA = Site was inaccessibleDRY = Site had no flow
33
G3: 544SJC506 – Old River at Tracy Blvd continued…
DateHardness
(mg/L)
Total Arsenic (ug/L)
Total Cadmium
(ug/L)
Total Chromium
(ug/L)
Total Copper (ug/L)
Total Lead (ug/L)
Total Nickel (ug/L)
Total Zinc (ug/L)
Total Mercury (ug/L)
10/24/2000 220 1.8 2.8 <5 <5 3.711/28/2000 180 1.8 2.4 <5 <5 3.612/27/2000 180 <1 1.8 <5 <5 2.61/23/2001 200 1.4 2.6 <5 <5 2.92/20/2001 160 1.5 2.6 <5 <5 3.43/27/2001 260 2.5 3.9 <5 5.2 6.44/24/2001 110 1.8 2.7 <5 <5 3.75/29/2001 180 1.7 3.4 <5 <5 4.76/26/2001 3.8 <1 1.9 3.1 <5 <5 4.2 <0.27/24/2001 NA NA 1.4 2.1 <5 <5 4.8 NA8/28/2001 190 3.0 <1 <1 1.9 <5 <5 2.49/25/2001 180 <4 <0.1 <1 2.0 <5 <5 <2 <0.2
10/23/2001 200 <4 <0.1 <1 2.5 <5 <5 3.8 NA11/27/2001 190 <4 <0.1 <1 1.8 <5 <5 10 <0.212/26/2001 280 <4 <0.1 2.7 4.2 <5 <5 9.8 <0.21/29/2002 260 <4 <0.1 <1 <1 <5 <5 4.0 <0.23/26/2002 230 <4.0 <0.1 1.5 2.9 <5.0 13 5.4 <0.24/23/2002 260 4.0 <0.1 <1.0 1.2 <5.0 <5.0 <2.0 <0.25/28/2002 150 <4.0 <0.1 1.6 4.5 <5.0 <5.0 3.7 <0.26/18/2002 220 <4.0 <0.1 <1.0 2.6 <5.0 <5.0 4.3 <0.29/24/2002 210 <4.0 <0.1 <1.0 5.4 <5.0 <5.0 4.1 <0.2
10/29/2002 170 <4.0 <0.1 1.8 3.5 <5.0 <5.0 2.8 <0.211/19/2002 200 <4.0 <0.1 <1.0 1.9 <5.0 <5.0 2.4 <0.23/25/2003 280 4.0 <0.1 1.8 2.7 <5.0 <5.0 3.0 <0.24/22/2003 190 <4.0 <0.1 <1.0 2.4 <5.0 <5.0 <2.0 <0.25/27/2003 140 <4.0 <0.1 1.3 3.3 <5.0 <5.0 2.9 <0.26/24/2003 160 <4.0 <0.1 2.1 3.3 <5.0 <5.0 4.1 <0.2
34
G3: 544SJC506 – Old River at Tracy Blvd continued…
DateHardness
(mg/L)
Total Arsenic (ug/L)
Total Cadmium
(ug/L)
Total Chromium
(ug/L)
Total Copper (ug/L)
Total Lead (ug/L)
Total Nickel (ug/L)
Total Zinc (ug/L)
Total Mercury (ug/L)
Count 25 18 18 27 27 27 27 27 16Min 110 2.0 0.1 0.5 0.5 2.5 2.5 1.0 0.1Max 280 4.0 0.5 2.7 5.4 2.5 13 10 0.1Mean 200 2.4 0.1 1.3 2.7 2.5 3.0 3.9 0.1Geo Mean 190 2.3 0.1 1.1 2.5 2.5 2.7 3.4 0.1Median 190 2.0 0.1 1.4 2.6 2.5 2.5 3.7 0.1Quartile 1 180 2.0 0.1 0.5 2.1 2.5 2.5 2.9 0.1Quartile 3 220 2.0 0.1 1.8 3.3 2.5 2.5 4.3 0.1NOTE: For values reported as < (less than), half the detection limit was used.
NA = Data not applicableINA = Site was inaccessibleDRY = Site had no flow
35
G3: 544SJC506 – Old River at Tracy Blvd continued…
DateHardness
(mg/L)
Dissolved Arsenic (ug/L)
Dissolved Cadmium
(ug/L)
Dissolved Chromium
(ug/L)
Dissolved Copper (ug/L)
Dissolved Lead (ug/L)
Dissolved Nickel (ug/L)
Dissolved Zinc
(ug/L)
Dissolved Mercury (ug/L)
10/24/2000 22011/28/2000 180 <1 <1 <5 <5 <212/27/2000 180 <1 <1 <5 <5 <21/23/2001 200 <1 <1 <5 <5 <22/20/2001 160 <1 1.3 <5 <5 <23/27/2001 260 <1 1.7 <5 <5 <24/24/2001 110 <1 1.0 <5 <5 <25/29/2001 180 <1 1.3 <5 <5 <26/26/2001 3.7 <1 <1 <1 <5 <5 <2 <0.27/24/2001 NA NA NA NA NA NA NA NA8/28/2001 190 2.9 <1 <1 <1 <5 <5 <29/25/2001 180 <4 <0.1 <1 2.2 <5 <5 11 <0.2
10/23/2001 200 <4 <0.1 <1 1.4 <5 <5 <2 NA11/27/2001 190 <4 <0.1 <1 1.3 <5 <5 8.1 <0.212/26/2001 280 <4 <0.1 <1 2.3 <5 <5 6.0 <0.21/29/2002 260 <4 <0.1 <1 <1 <5 <5 <2 <0.23/26/2002 230 <4.0 <0.1 <1.0 2.0 <5.0 <5.0 3.8 <0.24/23/2002 260 5.3 <0.1 <1.0 1.5 <5.0 <5.0 <2.0 <0.25/28/2002 150 <4.0 <0.1 <1.0 3.0 <5.0 <5.0 <2.0 <0.26/18/2002 220 <4.0 <0.1 <1.0 <1.0 <5.0 <5.0 <2.0 <0.29/24/2002 210 4.2 <0.1 <1.0 2.6 <5.0 <5.0 <2.0 <0.2
10/29/2002 170 <4.0 <0.1 <1.0 1.7 <5.0 <5.0 <2.0 <0.211/19/2002 200 <4.0 <0.1 <1.0 <1.0 <5.0 <5.0 <2.0 <0.2
36
G3: 544SJC506 – Old River at Tracy Blvd continued…
DateHardness
(mg/L)
Dissolved Arsenic (ug/L)
Dissolved Cadmium
(ug/L)
Dissolved Chromium
(ug/L)
Dissolved Copper (ug/L)
Dissolved Lead (ug/L)
Dissolved Nickel (ug/L)
Dissolved Zinc
(ug/L)
Dissolved Mercury (ug/L)
Count 21 14 14 21 21 21 21 21 12Min 110 2.0 0.1 0.5 0.5 2.5 2.5 1.0 0.1Max 280 5.3 0.5 0.5 3.0 2.5 2.5 11.0 0.1Mean 200 2.6 0.1 0.5 1.3 2.5 2.5 2.2 0.1Geo Mean 200 2.4 0.1 0.5 1.1 2.5 2.5 1.4 0.1Median 200 2.0 0.1 0.5 1.3 2.5 2.5 1.0 0.1Quartile 1 180 2.0 0.1 0.5 0.5 2.5 2.5 1.0 0.1Quartile 3 220 2.7 0.1 0.5 1.7 2.5 2.5 1.0 0.1NOTE: For values reported as < (less than), half the detection limit was used.
NA = Data not applicableINA = Site was inaccessibleDRY = Site had no flow
37
G3: 544SJC506 – Old River at Tracy Blvd continued…
DateChloride (mg/L)
Sulfate (mg/L)
Calcium (mg/L)
Magnesium (mg/L)
TDS (mg/L)
Carbonate (mg/L)
Bicarbonate (mg/L)
Total Alkalinity
(mg/L)Sodium (mg/L)
10/24/2000 130 110 45 27 580 <1 190 150 11011/28/2000 100 86 39 21 460 <1 140 120 9212/27/2000 100 95 39 21 490 <1 140 120 931/23/2001 120 120 43 23 450 <1 160 130 1102/20/2001 8 100 35 18 420 <1 120 100 813/27/2001 160 180 55 30 NA <1 180 150 1404/24/2001 61 65 25 13 280 <1 84 69 485/29/2001 100 92 38 20 400 16 84 100 798/28/2001 110 100 41 21 510 <1 150 130 979/25/2001 100 84 39 20 NA <1 140 120 84
10/23/2001 120 97 42 22 NA <1 150 130 1011/27/2001 120 94 40 22 490 <1 130 150 10012/26/2001 180 160 57 32 720 <1 190 160 1401/29/2002 160 150 56 30 680 <1 190 150 1403/26/2002 150 150 48 26 590 <1.0 160 130 1204/23/2002 160 150 54 29 610 <1.0 160 130 1305/28/2002 80 76 33 16 NA <1.0 110 87 656/18/2002 120 110 48 24 NA <1.0 160 NA 1109/24/2002 130 100 46 24 NA <1.0 170 140 110
10/29/2002 96 87 36 19 470 <1.0 130 110 8411/19/2002 130 100 42 22 530 <1.0 160 130 1103/25/2003 160 180 59 324/22/2003 110 120 39 225/27/2003 80 76 32 166/24/2003 94 82 36 18
38
39
G3: 544SJC506 – Old River at Tracy Blvd continued…
DateChloride (mg/L)
Sulfate (mg/L)
Calcium (mg/L)
Magnesium (mg/L)
TDS (mg/L)
Carbonate (mg/L)
Bicarbonate (mg/L)
Total Alkalinity
(mg/L)Sodium (mg/L)
Count 25 25 25 25 15 21 21 20 21Min 8 65 25 13 280 0.5 84 69 10Max 180 180 59 32 720 16 190 160 140Mean 120 110 43 23 510 1.2 148 130 98Geo Mean 100 100 42 22 500 0.6 144 120 89Median 120 100 41 22 490 0.5 150 130 100Quartile 1 100 87 38 20 460 0.5 130 120 84Quartile 3 130 120 48 26 590 0.5 160 140 110NOTE: For values reported as < (less than), half the detection limit was used.
NA = Data not applicableINA = Site was inaccessibleDRY = Site had no flow
G4: 544SJC509 – Mt House Creek @ Mt. House Parkway Station Code:544SJC509
Location: Latitude 37.78556, Longitude -121.53472
Date TimeTemp (ºC)
Field SC (umhos) pH
Dissolved Oxygen (mg/L)
Turbidity (ntu)
12/27/2000 11:15 AM 6.9 2840 7.81/23/2001 11:00 AM 8.5 2930 7.62/10/2001 2:10 PM 8.5 2860 7.22/11/2001 4:43 AM 6.8 2900 8.12/20/2001 11:12 AM 9.8 2780 7.93/27/2001 11:10 AM 14.9 531 7.94/24/2001 1:00 PM 22.7 1040 7.35/29/2001 11:00 AM 21.0 467 7.66/26/2001 12:28 PM 23.3 485 7.5 2.97/24/2001 DRY DRY DRY DRY DRY8/28/2001 11:38 AM 23.9 647 7.8 8.89/25/2001 10:39 AM 17.5 737 7.8 11.9
10/23/2001 10:19 AM DRY DRY DRY DRY11/27/2001 DRY DRY DRY DRY DRY12/26/2001 DRY DRY DRY DRY DRY1/29/2002 10:11 AM DRY DRY DRY DRY2/26/2002 10:00 AM DRY DRY DRY DRY3/26/2002 DRY DRY DRY DRY DRY4/23/2002 11:58 AM 17.4 353 7.7 9.75/28/2002 10:10 AM DRY DRY DRY DRY6/18/2002 9:55 AM 17.9 344 7.3 8.17/31/2002 10:04 AM 19.1 551 8.8 7.0 2608/27/2002 10:20 AM DRY DRY DRY DRY9/24/2002 10:30 AM 18.5 715 7.6 9.2
10/15/2002 DRY DRY DRY DRY DRY DRY10/29/2002 11:27 AM 13.4 676 7.8 10.2 12111/19/2002 DRY DRY DRY DRY DRY12/17/2002 9:00 AM 10.1 1660 7.8 10.6 2741/15/2003 DRY DRY DRY DRY DRY DRY1/28/2003 9:30 AM DRY DRY DRY DRY DRY3/25/2003 9:06 AM 11.5 656 7.5 10.8 75.64/22/2003 9:20 AM DRY DRY DRY DRY DRY5/27/2003 10:40 AM 20.0 531 7.8 8.1 41.06/24/2003 10:07 AM DRY DRY DRY DRY DRY7/29/2003 8:35 AM 20.8 246 7.6 9.0 1418/26/2003 10:05 AM DRY DRY DRY DRY DRY9/23/2003 10:22 AM DRY DRY DRY DRY DRY
10/28/2003 10:55 AM DRY DRY DRY DRY DRY11/18/2003 10:40 AM DRY DRY DRY DRY DRY
40
G4: 544SJC509 – Mt House Creek @ Mt. House Parkway continued…
Date TimeTemp (ºC)
Field SC (umhos) pH
Dissolved Oxygen (mg/L)
Turbidity (ntu)
Count 20 20 20 12 6Min 6.8 246 7.2 2.9 41.0Max 23.9 2930 8.8 11.9 274Mean 15.6 1280 7.7 8.9 152Geo Mean 14.5 863 7.7 8.4 125Median 17.5 666 7.8 9.1 131Quartile 1 10.0 520 7.6 8.1 87.0Quartile 3 20.2 1940 7.8 10.3 230NOTE: For values reported as < (less than), half the detection limit was used.
NA = Data not applicableINA = Site was inaccessibleDRY = Site had no flow
41
42
DateTSS
(mg/L)TOC
(mg/L)Total Coli
MPNE. coli MPN
12/27/2000 15 2.61/23/2001 16 6.12/10/2001 25 3.12/11/2001 37 6.62/20/2001 26 4.23/27/2001 49 NA5/29/2001 76 146/26/2001 34 138/28/2001 110 9.89/25/2001 NA 9.24/23/2002 NA6/18/2002 5.87/31/2002 >2419.6 10469/24/2002 4.7
10/15/2002 DRY DRY10/29/2002 2.812/1/13/24/25/27/28/29/2
10/11/
CounMin MaxMeaGeoMedQuaQua
G4: 544SJC509 – Mt House Creek @ Mt. House Parkway continued…
17/2002 145/2003 DRY DRY5/2003 4.62/2003 DRY DRY7/2003 NA9/2003 >2419.6 12036/2003 DRY DRY3/2003 DRY DRY28/2003 DRY DRY18/2003 DRY DRY
t 9 14 2 215 2.6 2420 1046
110 14 2420 1203n 43 7.2 NA NA Mean 35 6.1 2420 1122ian 34 6.0 2420 1125rtile 1 25 4.3 2420 1085rtile 3 49 9.7 2420 1164E: For values reported as < (less than), half the detection limit was used For values reported as > (greater than), 2420 was used
Data not applicable Site was inaccessible
= Site had no flow
NOT
NA =INA =DRY
G4: 544SJC509 – Mt House Creek @ Mt. House Parkway continued…
DateNitrate (mg/L)
Nitrate-N (mg/L)
TKN (mg/L)
Ammonia-N (mg/L)
Phosphorus (mg/L)
Ortho-phosphate-
P (mg/L)
Potassium (mg/L)
BOD 5-Day (mg/L)
BOD 10-Day (mg/L)
12/27/2000 5.2 2.6 0.2 <1 22 2.8 6.61/23/2001 7.6 2.3 0.2 <1 21 2.2 5.22/10/2001 4.9 <2 0.2 <1 19 1.4 3.72/11/2001 5.5 <2 0.2 <1 202/20/2001 5.7 <2 0.2 0.2 19 1.7 3.43/27/2001 5.3 <2 0.3 <1 5.9 2.4 3.95/29/2001 2.2 2.1 0.3 <1 6.5 7.0 11.66/26/2001 2.5 <2 0.4 <1 7.4 8.0 15.38/28/2001 4.8 <2 0.3 <1 6.19/25/2001 <2 <2 0.2 <1 104/23/2002 NA NA NA NA 4.3 1.2 2.16/18/2002 NA 0.9 NA 0.2 5.0 2.7 4.59/24/2002 NA NA 0.1 0.1 6.2 1.9 3.3
10/29/2002 NA 0.6 0.1 <0.03 3.9 1.3 2.012/17/2002 NA 3.4 0.3 0.3 13 7.0 13.2
Count 10 NA 13 NA 13 14 15 12 12Min 1.0 NA 0.6 NA 0.1 0.02 3.9 1.2 2.0Max 7.6 NA 3.4 NA 0.4 0.5 22 8.0 15.3Mean 4.5 NA 1.5 NA 0.2 0.4 11 3.3 6.2Geo Mean 3.9 NA 1.3 NA 0.2 0.3 9.4 2.6 5.0Median 5.1 NA 1.0 NA 0.2 0.5 7.4 2.3 4.2Quartile 1 3.1 NA 1.0 NA 0.2 0.2 6.0 1.6 3.4Quartile 3 5.5 NA 2.1 NA 0.3 0.5 19 3.9 7.9NOTE: For values reported as < (less than), half the detection limit was used.
NA = Data not applicableINA = Site was inaccessibleDRY = Site had no flow
43
G4: 544SJC509 – Mt House Creek @ Mt. House Parkway continued…
DateHardness
(mg/L)
Total Arsenic (ug/L)
Total Cadmium
(ug/L)
Total Chromium
(ug/L)
Total Copper (ug/L)
Total Lead (ug/L)
Total Nickel (ug/L)
Total Zinc (ug/L)
Total Mercury (ug/L)
12/27/2000 410 1.3 3.7 <5 6.3 2.21/23/2001 460 1.0 3.8 <5 5.7 <22/10/2001 470 1.8 4.3 <5 6.0 3.42/11/2001 480 2.2 5.4 <5 6.6 4.72/20/2001 460 1.4 4.6 <5 5.7 <23/27/2001 120 3.2 6.5 <5 7.8 8.65/29/2001 120 2.4 6.8 <5 7.8 7.76/26/2001 2.1 <1 1.5 8.0 <5 7.7 6.9 <0.28/28/2001 90 3.1 <1 7.0 8.6 <5 12 209/25/2001 130 <4 <0.1 2.5 5.5 <5 6.1 6.2 <0.24/23/2002 94 <4.0 <0.1 1.4 5.1 <5.0 <5.0 5.7 <0.26/18/2002 100 <4.0 <0.1 2.9 6.0 <5.0 6.1 8.0 <0.29/24/2002 140 <4.0 <0.1 6.0 8.4 <5.0 9.7 15 <0.2
10/29/2002 130 <4.0 <0.1 3.5 7.8 <5.0 6.6 8.7 <0.23/25/2003 120 <4.0 <0.1 3.7 5.3 <5.0 6.1 7.8 <0.25/27/2003 110 <4.0 <0.1 2.3 10 <5.0 5.3 5.5 <0.2
Count 15 9 9 16 16 16 16 16 8Min 90 2.0 0.1 1.0 3.7 2.5 2.5 1.0 0.1Max 480 3.1 0.5 7.0 10 2.5 12 20 0.1Mean 229 2.1 0.2 2.8 6.2 2.5 6.8 7.0 0.1Geo Mean 181 2.1 0.1 2.4 6.0 2.5 6.4 5.4 0.1Median 130 2.0 0.1 2.4 5.8 2.5 6.2 6.6 0.1Quartile 1 115 2.0 0.1 1.5 5.0 2.5 5.9 4.4 0.1Quartile 3 435 2.0 0.1 3.3 7.9 2.5 7.7 8.2 0.1NOTE: For values reported as < (less than), half the detection limit was used.
NA = Data not applicableINA = Site was inaccessibleDRY = Site had no flow
44
G4: 544SJC509 – Mt House Creek @ Mt. House Parkway continued…
DateHardness
(mg/L)
Dissolved Arsenic (ug/L)
Dissolved Cadmium
(ug/L)
Dissolved Chromium
(ug/L)
Dissolved Copper (ug/L)
Dissolved Lead (ug/L)
Dissolved Nickel (ug/L)
Dissolved Zinc
(ug/L)
Dissolved Mercury (ug/L)
12/27/2000 410 <1 2.1 <5 5.2 <21/23/2001 460 <1 2.2 <5 5.0 <22/10/2001 470 <1 2.7 <5 <5 <22/11/2001 480 <1 2.9 <5 <5 <22/20/2001 460 <1 3.4 <5 <5 <23/27/2001 120 <1 3.3 <5 <5 2.85/29/2001 120 <1 4.3 <5 <5 4.56/26/2001 2.0 <1 <1 6.2 <5 5.6 3.3 <0.28/28/2001 90 2.3 <1 <1 3.9 <5 <5 5.49/25/2001 130 <4 <0.1 <1 3.6 <5 <5 15 <0.24/23/2002 94 <4.0 <0.1 <1.0 4.1 <5.0 <5.0 3.7 <0.26/18/2002 100 <4.0 <0.1 <1.0 1.5 <5.0 <5.0 2.8 <0.29/24/2002 140 <4.0 <0.1 <1.0 3.1 <5.0 <5.0 <2.0 <0.2
10/29/2002 130 <4.0 <0.1 <1.0 3.8 <5.0 <5.0 <2.0 <0.2
Count 13 7 7 14 14 14 14 14 6Min 90 2.0 0.1 0.5 1.5 2.5 2.5 1.0 0.1Max 480 2.3 0.5 0.5 6.2 2.5 5.6 15.0 0.1Mean 246 2.0 0.2 0.5 3.4 2.5 3.1 3.2 0.1Geo Mean 194 2.0 0.1 0.5 3.2 2.5 2.9 2.1 0.1Median 130 2.0 0.1 0.5 3.4 2.5 2.5 1.9 0.1Quartile 1 120 2.0 0.1 0.5 2.8 2.5 2.5 1.0 0.1Quartile 3 460 2.0 0.3 0.5 3.9 2.5 2.5 3.6 0.1NOTE: For values reported as < (less than), half the detection limit was used.
NA = Data not applicableINA = Site was inaccessibleDRY = Site had no flow
45
46
G4: 544SJC509 – Mt House Creek @ Mt. House Parkway continued…
DateChloride (mg/L)
Sulfate (mg/L)
Calcium (mg/L)
Magnesium (mg/L)
TDS (mg/L)
Carbonate (mg/L)
Bicarbonate (mg/L)
Total Alkalinity
(mg/L)Sodium (mg/L)
12/27/2000 410 430 72 57 1800 <1 480 400 4801/23/2001 400 480 82 61 1800 <1 470 380 4802/10/2001 400 470 84 63 1800 <1 460 380 4802/11/2001 410 490 86 64 1900 <1 450 370 4902/20/2001 370 470 85 60 1800 <1 440 360 4503/27/2001 60 60 26 14 NA <1 120 100 575/29/2001 51 45 25 14 250 <1 88 88 458/28/2001 120 31 23 8 390 <1 96 79 779/25/2001 140 42 24 17 NA <1 99 81 934/23/2002 26 23 19 11 240 <1.0 100 83 376/18/2002 35 30 21 11 NA <1.0 82 NA 359/24/2002 150 32 24 19 NA <1.0 100 83 98
10/29/2002 130 35 22 18 430 <1.0 110 89 873/25/2003 80 31 22 155/27/2003 66 63 21 14
Count 15 15 15 15 9 13 13 12 13Min 26 23 19 8 240 0.5 82 79 35Max 410 490 86 64 1900 0.5 480 400 490Mean 190 182 42 30 1157 0.5 238 208 224Geo Mean 129 87 35 23 837 0.5 178 159 135Median 130 45 24 17 1800 0.5 110 95 93Quartile 1 63 32 22 14 390 0.5 99 83 57Quartile 3 385 450 77 59 1800 0.5 450 373 480NOTE: For values reported as < (less than), half the detection limit was used.
NA = Data not applicableINA = Site was inaccessibleDRY = Site had no flow
G4: 544SJC509 – Mt House Creek @ Mt. House Parkway continued…
Date Result Control Result Control
Result (million/m
l)
Control (million/
ml) MDD(%)1/23/2001 100 100 100 NA2/20/2001 80 90 100 1003/27/2001 100 100 100 1005/29/2001 85 95 100 1006/19/2001 100 100 100 906/26/2001 95 100 80 1004/23/2002 100 95 100 1006/18/2002 100 100 100 1009/24/2002 95 100 100 100
10/29/2002 100 95 100 10012/17/2002 100 100 100 100 2.57 2.92 NA5/28/2003 90 100 100 100 3.48** 2.04 8
Count 12 12 12 11 2 2 N/A
* Significantly reduced from the lab control.** Significantly greater than the lab control.^ Fish were from a "forced hatch," duplicate failed QA.
1 Duplicate sample for the set was low - 77% recovery.
3 Samples qualified, but duplicate sample recovery for the set was high - 126% (53.8%/42.5%)NA = Data not applicableINA = Site was inaccessibleDRY = Site had no flow
2 Testing for the Fathead minnow was initiated when samples were approx. 48h old due to
96h Acute Fathead Minnow
(% Survival)
48h Acute Ceriodaphnia Dubia
(% Survival) Algae Cell Growth
47
APPENDIX H
PARAMETERS, DETECTION LEVELS, HOLDING TIMES AND ANALYTICAL RECOVERIES
Appendix H. Parameters, Detection Levels, Holding Times and Acceptable Analytical Recoveries (Revised Aug 2007)
Minimum Field Duplicate Holding Time/
Constituent Laboratory Sample Size Units Method RL RPD/Recovery Preservation Container Completeness
Dissolved Oxygen CVRWQCB 500 mL mg/L a/360.1 0.1 N/A on site 500 mL
Polyethylene 95%
pH CVRWQCB 500 mL None a/150.1 0.1 N/A on site 500 mL Polyethylene 95%
Specific Conductance CVRWQCB 500 mL umhos/cm a/b/120.1 1 RPD<10% 28 days - Cool, 4 °C in the
dark 500 mL
Polyethylene 95%
Temperature CVRWQCB 500 mL oC a/temperature 0.1 N/A on site 500 mL Polyethylene 95%
Turbidity CVRWQCB 500 mL NTU a 1 RPD<10% on site 500 mL Polyethylene 95%
Total Alkalinity SFL 800 mL mg/L SM2320B 5.0 RPD<15% 14 days - Cool, 4 °C in the dark
500 mL/1 L Polyethylene 95%
Appendix H. Parameters, Detection Levels, Holding Times and Acceptable Analytical Recoveries (Revised Aug 2007) continued…
Minimum Field Duplicate Holding Time/
Constituent Laboratory Sample Size Units Method RL RPD/Recovery Preservation Container Completeness
Total Dissolved Solids SFL 300 mL mg/L SM2540C 10 RPD<15% 7 days - Cool, 4 °C in the dark 500 mL/1 L
Polyethylene 95%
Total Hardness SFL 500 mL mg/L EPA 130.2 5.0 RPD<15% 180 days- Cool, 4 °C in the dark
500 mL/1 L Polyethylene 95%
Total Suspended
Solids SFL 1000 mL mg/L SM2540D 1.0 RPD<20% 7 days - Cool, 4 °C in the dark 500 mL/1 L
Polyethylene 95%
Metals in Water
Arsenic, Total & Dissolvedd SFL 500 mL µg/L SM3114B 2
4-20 ±4 At concentrations greater than the ranges shown,
acceptable recovery is 80 - 120%
180 days - When preserved to a pH < 2 using nitric acid within 24 hours of sample
collection
500 mL/1 L Polyethylene 95%
Cadmium, Total &
Dissolvedd SFL 500 mL µg/L SM3113B to
MDL 0.1
0.1-10 ±3 At concentrations greater than the ranges shown,
acceptable recovery is 80 - 120%
180 days - When preserved to a pH < 2 using nitric acid within 24 hours of sample
collection
500 mL/1 L Polyethylene 95%
Appendix H. Parameters, Detection Levels, Holding Times and Acceptable Analytical Recoveries (Revised Aug 2007) continued…
Minimum Field Duplicate Holding Time/
Constituent Laboratory Sample Size Units Method RL RPD/Recovery Preservation Container Completeness
Copper,Total & Dissolvedd SFL 500 mL µg/L SM3113B 1
1-20 ± 5 At concentrations greater than the ranges shown,
acceptable recovery is 70 - 130%
180 days - When preserved to a pH < 2 using nitric acid within 24 hours of sample
collection
500 mL /1 L Polyethylene 95%
Lead, Total & Dissolvedd SFL 500 mL µg/L SM3113B 3
5-25 ± 8 At concentrations greater than the ranges shown,
acceptable recovery is 60 - 140%
180 days - When preserved to a pH < 2 using nitric acid within 24 hours of sample
collection
500 mL/1 L Polyethylene 95%
Mercury, Total & Dissolvedd SFL 500 mL µg/L SM3112B to
MDL 0.1
0.1-10 ±.5 At concentrations greater than the ranges shown,
acceptable recovery is 70 - 130%
28 days- Cool, 4 °C in the dark
500 mL/1 L Polyethylene 95%
Nickel, Total & Dissolvedd SFL 500 mL µg/L EPA 249.2 3
5-25 ± 6 At concentrations greater than the ranges shown,
acceptable recovery is 65-135%
180 days - When preserved to a pH < 2 using nitric acid within 24 hours of sample
collection
500 mL/1 L Polyethylene 95%
Zinc,Total & Dissolvedd SFL 500 mL µg/L SM3111B 2
1-20 ± 6 - At concentrations greater than the ranges shown,
acceptable recovery is 70 - 130%
180 days - When preserved to a pH < 2 using nitric acid within 24 hours of sample
collection
500 mL/1 L Polyethylene 95%
Appendix H. Parameters, Detection Levels, Holding Times and Acceptable Analytical Recoveries (Revised Aug 2007) continued…
Minimum Field Duplicate Holding Time/
Constituent Laboratory Sample Size Units Method RL RPD/Recovery Preservation Container Completeness
Minerals in Water
Bicarbonate SFL 200 mL mg/L SM2320B 5.0 RPD<15% 14 days - Cool, 4 °C in the dark
500 mL/1 L Polyethylene 95%
Calcium SFL 500 mL mg/L SM3111B 0.1 RPD<15% 180 days- Cool, 4 °C in the dark
500 mL/1 L Polyethylene 95%
Chloride SFL 50 mL mg/L EPA 300.0 1.0 RPD<15% 28 days - Cool, 4 °C in the dark
500 mL/1 L Polyethylene 95%
Magnesium SFL 500 mL mg/L EPA 242.1 0.02 RPD<15% 180 days - Cool, 4 °C in the dark
500 mL/1 L Polyethylene 95%
Potassium SFL 500 mL mg/L EPA 258.1 0.10 RPD<15% 180 days - Cool, 4 °C in the dark
500 mL/1 L Polyethylene 95%
Sodium SFL 500 mL mg/L SM3111B 0.10 RPD<15% 180 days - Cool, 4 °C in the dark
500 mL/1 L Polyethylene 95%
Appendix H. Parameters, Detection Levels, Holding Times and Acceptable Analytical Recoveries (Revised Aug 2007) continued…
Minimum Field Duplicate Holding Time/
Constituent Laboratory Sample Size Units Method RL RPD/Recovery Preservation Container Completeness
Sulfate
SFL 100 mL mg/L EPA 300.0 0.5 RPD<15% 28 days - Cool, 4 °C in the dark
500 mL/1 L Polyethylene 95%
Nutrients in Water
Ammonia as Nd Basic 300 mL mg/L 350.1 0.05 80 – 120% Recovery 28 days - Cool, 4 C, H2SO4 to pH <2 Polyethylene 95%
Ammoniad SFL 300 mL mg/L EPA 350.3 0.20 80 – 120% Recovery 28 days - Cool, 4 C, H2SO4 to pH <2 Polyethylene 95%
Nitrate as N Basic 100 mL mg/L 353.2 0.05 80 – 120% Recovery 2 days - Cool, 4 °C in the dark Polyethylene 95%
Nitrate SFL 100 mL mg/L EPA 300.0 0.05 80 – 120% Recovery 2 days - Cool, 4 °C in the dark Polyethylene 95%
Appendix H. Parameters, Detection Levels, Holding Times and Acceptable Analytical Recoveries (Revised Aug 2007) continued…
Minimum Field Duplicate Holding Time/
Constituent Laboratory Sample Size Units Method RL RPD/Recovery Preservation Container Completeness
Total Phosphorousd Basic 150 mL mg/L SM 4500P 0.05 80 – 120% Recovery 28 days - Cool, 4 °C in the
dark Polyethylene 95%
Ortho Phosphated Basic 150 mL mg/L SM 4500P-E 0.05 80 – 120% Recovery 2 days - Cool, 4 °C Polyethylene 95%
Ortho Phosphated SFL 150 mL mg/L EPA 365.3 0.01 80 – 120% Recovery 2 days - Cool, 4 °C in the dark Polyethylene 95%
Total Kjldahl Nitrogend Basic 300 mL mg/L 351.2 0.2 80 – 120% Recovery 28 days - Cool, 4 °C in the
dark, H2SO4 to pH <2 Polyethylene 95%
Total Kjldahl Nitrogend SFL 300 mL mg/L EPA 351.3 0.50 80 – 120% Recovery 28 days - Cool, 4 °C in the
dark, H2SO4 to pH <2 Polyethylene 95%
Appendix H. Parameters, Detection Levels, Holding Times and Acceptable Analytical Recoveries (Revised Aug 2007) continued…
Minimum Field Duplicate Holding Time/
Constituent Laboratory Sample Size Units Method RL RPD/Recovery Preservation Container Completeness
Total Phosphorousd Basic 150 mL mg/L SM 4500P 0.05 80 – 120% Recovery 28 days - Cool, 4 °C in the
dark Polyethylene 95%
Total Phosphorousd SFL 150 mL mg/L EPA 365.2 0.02 80 – 120% Recovery 2 days - Cool, 4 °C in the
darkC Polyethylene 95%
Freshwater Toxicity
48h % Survival,
Ceriodaphnia SFL 1000 mL
Adult Count (% survival)
EPA 821-R-02-012, Table
12
Significant difference, or
RPD<20% 36 Hr - Cool, 4 °C in the dark 1L Glass 95%
96h % Survival, Fathead Minnow
(Pimephales), non-renewal
SFL 1000 mL % Survival
EPA 821-R-02-012, Table
14
Significant difference, or
RPD<20% 36 Hr - Cool, 4 °C in the dark 1L Glass 95%
96h Algae (Selenastrum)
growth SFL 1000 mL
Cell Count (growth or reduction)
cell/mL
EPA 821-R-02-013, 1003.0
Significant
difference, or RPD<20%
36 Hr - Cool, 4 °C in the dark 1L Glass 95%
Appendix H. Parameters, Detection Levels, Holding Times and Acceptable Analytical Recoveries (Revised Aug 2007) continued…
Minimum Field Duplicate Holding Time/
Constituent Laboratory Sample Size Units Method RL RPD/Recovery Preservation Container Completeness
Chronic Toxicity,
Ceriodaphnia SFL 1000 mL
Adult Count (% survival)
EPA 821-R-02-013, 1002.0
Significant
difference, or RPD<20%
36 Hr - Cool, 4 °C in the dark 1L Glass 95%
Chronic Toxicity,
Ceriodaphnia SFL 1000 mL
Larval Count
(num/rep)
EPA 821-R-02-013, 1002.0
Significant
difference, or RPD<20%
36 Hr - Cool, 4 °C in the dark 1L Glass 95%
Chronic Toxicity, Fathead Minnow
(Pimephales)
SFL 1000 mL % Survival
EPA 821-R-02-013, 1000.0
Significant
difference, or RPD<20%
36 Hr - Cool, 4 °C in the dark 1L Glass 95%
Chronic Toxicity, Fathead Minnow
(Pimephales)
SFL 1000 mL Weight (mg/ind)
EPA 821-R-02-013, 1000.0
Significant
difference, or RPD<20%
36 Hr - Cool, 4 °C in the dark 1L Glass 95%
Bacteria in Water
Total & Fecal Coliform, 15 tube Multiple
tube fermentation
SFL 125 mL MPN/100 mL SM9221B, E e 6 Hr to lab, 8h to analysis -
Cool, 4 °C in the dark Sterile Plastic 95%
Total Coliform & E. Coli, MTF
+ MUG SFL 125 mL MPN/100
mL SM9221B +
MUG e 6 Hr to lab, 8h to analysis - Cool, 4 °C in the dark Sterile Plastic 95%
Appendix H. Parameters, Detection Levels, Holding Times and Acceptable Analytical Recoveries (Revised Aug 2007) continued…
Minimum Field Duplicate Holding Time/
Constituent Laboratory Sample Size Units Method RL RPD/Recovery Preservation Container Completeness
Total Coliform CVRWQCB 100 mL MPN Colilert® 18 by Idexx 95% CI 6 Hr - Cool, 4 °C in the dark 100 mL
Polyethylene 95%
E. Coli CVRWQCB 100 mL MPN Colilert® 18 by Idexx 95% CI 6 Hr - Cool, 4 °C in the dark 100 mL
Polyethylene 95%
Organics in Water
Total Organic Carbon SFL 100 mL / 125
mL mg/L, % SM5310C 0.20 RPD<20% 28 days - Cool, 4 °C in the dark, H2SO4 to pH <2
250 mL Glass-Amber 95%
Biological Oxygen Demand
BOD 5-Day SFL 2000 ml mg/L SM 5210 B 1.0 RPD<20% 48 Hr - Cool, 4 °C in the dark Polyethylene 95%
BOD 10-Day SFL 2000 ml mg/L SM 5210 B 1.0 RPD<20% 48 Hr - Cool, 4 °C in the dark Polyethylene 95%
a. A YSI 6600 and a 600XLM Instrument is used to determine field SC, pH, Temp, DO, Turb.
b. A YSI 3200 Bench Top conductivity meter is used to determine lab SC.
c. Laboratory is determined through SWAMP - SJSU Master Contract
d. Samples analyzed as part of the Grassland Bypass Program and are set based on those Waste Discharge Requirements.
e. low range2-2400; mid range 20-2400; high range 200-240000; very high range 2000-2400000 *Carlson, R.M. 1978. Automated separation and conductimetric determination of ammonia and dissolved carbon dioxide.
Analytical Chemistry 50:1528-1531. *Carlson, R.M. 1986. Continuous flow reduction of nitrate to ammonia with granular zinc. Analytical Chemistry 58:1590-1591. **Yu, Z., Northup, R.R. and Dahlgren, R.A. 1994. Determination of dissolved organic nitrogen using persulfate oxidation and conductimetric
quantification of nitrate-nitrogen. Commun. Soil Sci. Plant Anal. 25:3161-3169. *** low range 2-2400; mid range 20-24000; high range 200-240000; very high range 2000-2,400,000
SFL = Sierra Foothill Laboratory Basic = Basic Laboratory CVRWQCB = in house processing in the Central Valley Regional Water Quality Control Board laboratory Eaton, A. D. ed., Clesceri, L. S. ed., Greenberg, A. E. ed. 1995. Standard Methods for the Examination of Water and Wastewater. 19th edition. American Public Health Association, American Water Works Association, Water Environment Federation.
APPENDIX I:
SJR Main Stem Site Information and Photographic Documentation
APPENDIX I: SJR Main Stem Site Information and Photographic Documentation I1: 541MAD007 – SJR at Sack Dam…………………………………………………03-04 I2: 541MER522 – SJR at Lander Avenue……………………………………....……05-06 I3: 541MER538 – SJR at Fremont Ford………………………………………….......07-08 I4: 541STC512 – SJR at Hills Ferry………………………………………………….09-10 I5: 535STC504 – SJR at Crows Landing…………………………………………….11-12 I6: 541STC507 – SJR at Patterson…………………………………………………...13-14 I7: 541STC510 – SJR at Maze……………………………………………………….15-16 I8: 541SJC501 – SJR at Airport Way………………………………………………...17-18
2
I1: 541MAD007 – SJR at Sack Dam
MONITORING SITE INFORMATION Site Description, Location and Access: Exit East onto Highway 152 off of Interstate 5. Exit South onto Highway 33 to Dos Palos. Go East onto Valeria Avenue until it dead-ends. Access is via a dirt road at the end of Valeria Avenue. Latitude/Longitude: Lat. N 36° 59’ 01.2” Long. W 120° 30’ 01.0” County: Madera WATER SOURCE The source of water is primarily from the Mendota Pool. Mendota Pool is supplied with Delta water pumped via the Delta Mendota Canal. During the wet season or during periods of planned releases, high quality San Joaquin River water from Friant Dam also flows to Mendota Pool.
3
Water Year 2004 – Dry Water Year 2005 – Wet Rainy Season
02/26/04 01/27/05
Spring Runoff
04/29/04 04/28/05
Irrigation Season
07/29/04 07/28/05
Dry Season
09/30/04 09/29/05
4
I2: 541MER522 – SJR at Lander Avenue
MONITORING SITE INFORMATION Site Description, Location and Access: The site is located approximately 16.5 miles north of Los Banos on Lander Avenue (Highway 165). The site is 1.2 miles south of the Highway 140 –Lander Avenue intersection. The sample is taken at the northwest corner of the Lander Avenue Bridge over the San Joaquin River. Township/Range/Section: NE ¼, NE ¼, SE ¼, Section 27, T7S, R10E (DWR#7S/10E-27J) Latitude/Longitude: Lat. N 37o 17’ 43” Long. W 120o 51’ 01” County: Merced USGS Quad map: Stevenson, CA WATER SOURCE Surface water in the San Joaquin River. In low flow periods, a significant portion of the river flow will consist of surface runoff from irrigated areas. Water quality at this site is expected to show natural background levels or good quality surface runoff from irrigated agriculture. No tile drainage water enters the river upstream of this site.
5
Water Year 2004 – Dry Water Year 2005 – Wet Rainy Season
02/26/04 02/17/05
Spring Runoff
04/29/04 04/28/05
Irrigation Season
07/29/04 07/28/05
Dry Season
09/30/04 09/22/05
6
I3: 541MER538 – SJR at Fremont Ford
MONITORING SITE INFORMATION Site Description, Location and Access: The monitoring site is located at Fremont Ford on the west bank of the San Joaquin River at Highway 140. The Sample is taken on the southwest side of the bridge. Fremont Ford is located approximately 5.4 miles northeast of Gustine on Highway 140. Township/Range/Section: NW ¼, NW ¼, SE ¼, Section 24, T7S, R9E (DWR#7S/9E-24K) Latitude/Longitude: Lat. N 37° 18’ 34” Long. W 120° 55’ 45” County: Merced USGS Quad Map: Gustine WATER SOURCE This site represents the San Joaquin River downstream of the confluence with Salt Slough. Water quality at this site is usually elevated with respect to salinity.
7
Water Year 2004 – Dry Water Year 2005 – Wet Rainy Season
02/26/04 02/17/05
Spring Runoff
04/29/04 04/28/05
Irrigation Season
07/29/04 07/28/05
Dry Season
09/30/04 09/22/05
8
I4: 541STC512 – SJR at Hills Ferry
MONITORING SITE INFORMATION Site Description, Location and Access: The site is located on the west band of the San Joaquin River approximately 30 yards south of the Merced River confluence. Access to the site is via Hills Ferry Road west of Newman. Hills Ferry Road crosses the San Joaquin River just north (downstream) of the Merced River confluence. To get to the sample point, park vehicle on northwest side of bridge, on shoulder of road and hike down the Merced River confluence to take sample. Township/Range/Section: SE ¼, SW ¼, SW 1/4, Section 3, T7S, R9E (DWR#7S/9E-3N) Latitude/Longitude: Lat. N 37º 20’ 33” Long. W 120º 58’ 38” County: Stanislaus USGS Quad Map: Gustine WATER SOURCE Flows at this site are composed of subsurface agricultural drainage, wetland drainage, and some surface runoff from the Grassland Area, as well as wet season inflows from Merced River flood channels. The quality of these flows will greatly influence quality in the river. Water at this site will likely be elevated with respect to salt, selenium, and boron.
9
Water Year 2004 – Dry Water Year 2005 – Wet Rainy Season
03/25/04 02/17/05
Spring Runoff
04/29/04 05/19/05
Irrigation Season
07/29/04 08/18/05
Dry Season
09/30/04 09/29/05
10
I5: 535STC504 – SJR at Crows Landing
MONITORING SITE INFORMATION Site Description, Location and Access: The sampling site is located on the fishing dock on the East bank at the Turlock Sports Club off of Carpenter road. The entrance to the sports club is 100 ft north of Crows Landing road. Upon entering, drive north on dirt road and take first left to fishing dock. Sample off of the west side of the dock. Township/Range/Section: NW ¼, SE ¼, NE ¼, Section 7, T6S, R9E (DWR#6S/9E-7H) Latitude/Longitude: Lat. N 37° 25’ 55” Long. W 121° 00’ 42” County: Stanislaus USGS Quad Map: Crows Landing, CA WATER SOURCE Water quality at this site will be better than that at upstream stations as the Merced River and Orestimba Creek drain to the San Joaquin River upstream of this station. This station will represent the San Joaquin River as influenced by the Grassland discharges and diluted by the Merced River flow.
11
Water Year 2004 – Dry Water Year 2005 – Wet Rainy Season
01/29/04 01/20/05
Spring Runoff
04/29/04 04/28/05
Irrigation Season
06/24/04 06/09/05
Dry Season
09/30/04 09/22/05
12
I6: 541STC507 – SJR at Patterson
MONITORING SITE INFORMATION Site Description, Location and Access: The monitoring site is located north of the Patterson Bridge at the fishing access off of Poplar Avenue. Access to the site is via Las Palmas Avenue (West Main St.) east from Patterson to Poplar Avenue located on the north side of the road approximately 0.5 miles west of the bridge. Go north on Poplar Avenue and make an immediate right on the road to Las Palmas Fishing Access. The sample is taken at the launch ramp on the southeast corner parking lot. Township/Range/Section: SW ¼, NW ¼, SW ¼, Section 15, T5S, R8E (DWR#5S/8E-15M) Latitude/Longitude: Lat. N 37° 29’ 52” Long. W 121° 04’ 54” County: Stanislaus USGS Quad Map: Crows Landing, CA WATER SOURCE Water quality at this site will be similar to that at Crows Landing Bridge (Site STC 504) with the additional influence of a few agricultural discharges to the river.
13
Water Year 2004 – Dry Water Year 2005 – Wet Rainy Season
02/26/04 02/17/05
Spring Runoff
04/29/04 04/28/05
Irrigation Season
07/29/04 07/28/05
Dry Season
09/30/04 09/22/05
14
I7: 541STC510 – SJR at Maze
MONITORING SITE INFORMATION Site Description, Location and Access: The monitoring site is located on the southwest side of the Highway 132 Bridge approximately 100 yards south of the Bridge. Access to the site is via River road, then turn down the alfalfa farmers’ driveway towards the pump house on the river. Parking is on a gravel turnabout at the pump house, then hike down to the river bank for sampling. Township/Range/Section: SW ¼, NW ¼, SW ¼, Section 29, T3S, R7E (DWR#3S/7E-29M) Latitude/Longitude: Lat. N 37° 38’ 31” Long. W 121° 13’ 40” County: Stanislaus USGS Quad Map: Ripon, CA WATER SOURCE Water quality and water quantity at this site is poor and lower, respectively than that found immediately downstream at Vernalis (site SJC 501). This station is immediately upstream of the inflow of the Stanislaus River and downstream of the inflow of the Tuolumne River.
15
Water Year 2004 – Dry Water Year 2005 – Wet Rainy Season
02/26/04 01/27/05
Spring Runoff
04/29/04 04/28/05
Irrigation Season
07/29/04 07/28/05
Dry Season
09/30/04 09/22/05
16
I8: 541SJC501 – SJR at Airport Way
MONITORING SITE INFORMATION Site Description, Location and Access: The site is located on the west bank of the San Joaquin River on the south side of the Airport Way Bridge. Access to the site is via Kasson Road to Airport Way. Airport Way is located just south of San Joaquin River Club. Township/Range/Section: SE ¼, SW ¼, NW ¼, Section 13, T3S, R6E (DWR#3S/6E-13E) Latitude/Longitude: Lat. N 37° 40’ 32” Long. W 121° 15’ 51” County: San Joaquin USGS Quad Map: Vernalis, CA WATER SOURCE Water at this site is natural surface flow in the San Joaquin River. Water quality at this site is good and shows typical surface flow quality. This site is just downstream of the inflow from the Stanislaus River. Quality is likely to be the best of any of the river sites.
17
Water Year 2004 – Dry Water Year 2005 – Wet Rainy Season
02/26/04 02/17/05
Spring Runoff
04/29/04 04/28/05
Irrigation Season
07/29/04 07/28/05
18
Dry Season
09/30/04 09/22/05
APPENDIX J:
Northeast Basin Site Information and Photographic Documentation
APPENDIX J: Northeast Basin Site Information and Photographic Documentation J1: 531SAC001 – Cosumnes River at Twin Cities Road.……………………………03-04 J2: 544SAC002 – Mokelumne River at New Hope Road……………………....……05-06 J3: 531SJC507 – Pixley Slough at Davis Road.………………………………….......07-08 J4: 544SJC508 – Bear Creek at Thornton Road (J8)...……………………………….09-10 J5: 531SJC515 – Bear Creek at Lower Sacramento Road..………………………….11-12
2
J1: 531SAC001 – Cosumnes River at Twin Cities Road
MONITORING SITE INFORMATION Site Description, Location and Access: Exiting West onto Twin Cities Road (E13) from Highway 99, the site location is at the Eastern most crossing of the River. Access is via the Northeastern side of the first bridge. Latitude/Longitude: Lat. N 38° 17’ 27.1” Long. W 121° 22’ 33.2” County: Sacramento WATER SOURCE The Cosumnes River is a natural stream, which ceases to flow during summer months from July until the first major storm in the fall unless water is diverted to it. Water is diverted, when available, from the Folsom-South Canal by Omochumne-Hartnell Water District. The channel, for about 10.5 miles, is dominated by agricultural supply water when water is diverted from the Folsom-South Canal from April through September.
3
Water Year 2004 – Dry Water Year 2005 – Wet Rainy Season
02/24/04 02/23/05
Spring Runoff
04/28/04 04/26/05
Irrigation Season
06/23/04 06/28/05
Dry Season
08/25/04 08/23/05
J2: 544SAC002 – Mokelumne River at New Hope Road
MONITORING SITE INFORMATION Site Description, Location and Access: Exiting East off of Interstate 5 onto Thornton Road (J8), take Thornton Road North. Make a left hand turn onto New Hope Road. Access is via the Southeast corner where New Hope Road crosses the river. Latitude/Longitude: Lat. N 38° 14’ 10” Long. W 121° 25’ 08” County: Sacramento WATER SOURCE This site is a culmination of the entire watershed and serves as an integrator for the lower watershed. The river is wide and deep and has been channeled between levees, which in turn have been reinforced with concrete riprap in several locations.
Water Year 2004 – Dry Water Year 2005 – Wet Rainy Season
02/24/04 02/23/05
Spring Runoff
04/28/04 04/26/05
Irrigation Season
07/28/04 07/26/05
Dry Season
09/29/04 09/27/05
J3: 531SJC507 – Pixley Slough at Davis Road
MONITORING SITE INFORMATION Site Description, Location and Access: Exit East onto Eight Mile Road off of Interstate 5. Make a right hand turn onto Davis Road. Access is via the northwest side of the bridge at Davis Road and Pixley Slough. Latitude/Longitude: Lat. N 38° 03’ 22.3” Long. W 121° 19’ 59.5” County: San Joaquin WATER SOURCE This slough originates at Bear Creek and carries supply water from Bear Creek to agricultural land in the North San Joaquin W.C.D. It carries agricultural supply water until it is diverted back into Bear Creek, north of Stockton. The total length of the slough is about 9.7 miles. The period that agricultural supply water dominates the flow in Pixley Slough is during the growing season from April through October.
Water Year 2004 – Dry Water Year 2005 – Wet Rainy Season
02/24/04 02/23/05
Spring Runoff
04/28/04 04/26/05
Irrigation Season
07/28/04 07/26/05
Dry Season
09/29/04 09/27/05
J4: 544SJC508 – Bear Creek at Thornton Road (J8)
MONITORING SITE INFORMATION Site Description, Location and Access: Exit East onto Eight Mile Road from Interstate 5. Make a right hand turn onto Thornton Road (J8). Access to the Creek is via the Northwest corner of the bridge. Latitude/Longitude: Lat. N 38° 02’ 35.3” Long. W 121° 20’ 54.8” County: San Joaquin WATER SOURCE The headwater of Bear Creek extends to the foothills. Under natural conditions, it would flow only part of the year. Supply waters which are released form upstream reservoirs are diverted form the Mokelumne River in the North San Joaquin W.C.D. This water supplies agriculture in the district. Operational spill water contributes its flow until it reaches the Delta tidal influence at Interstate 5. The total distance is about 13.6 miles. It has been channeled in a number of locations.
Water Year 2001 Water Year 2002 Rainy Season
02/26/02
Spring Runoff
04/24/01 04/23/02
Irrigation Season
07/24/01
Dry Season
09/26/01
J5: 531SJC515 – Bear Creek at Lower Sacramento Road
MONITORING SITE INFORMATION Site Description, Location and Access: Exit East onto Eight Mile Road from Interstate 5. Make a right hand turn onto Lower Sacramento Road. Access to the Creek is via the Southwest corner of the bridge. Latitude/Longitude: Lat. N 38° 02’ 33.9” Long. W 121° 19’ 16.9” County: San Joaquin WATER SOURCE The headwater of Bear Creek extends to the foothills. Under natural conditions, it would flow only part of the year. Supply waters that are released from upstream reservoirs are diverted from the Mokelumne River in the North San Joaquin W.C.D. This water supplies agriculture in the district. Operational spill water contributes its flow until it reaches the Delta tidal influence at Interstate 5. The total distance is about 13.6 miles. It has been channeled in a number of locations. Note: This site was changed from the Thornton Rd. site (May of 2002) due to the influx of tidal waters from the Delta. The new (Lower Sacramento Rd.) site is upstream of the tidal influence.
Water Year 2004 – Dry Water Year 2005 – Wet Rainy Season
02/24/04 02/23/05
Spring Runoff
04/28/04 04/26/05
Irrigation Season
06/23/04 06/28/05
Dry Season
08/25/04 08/23/05
APPENDIX K:
Eastside Basin Site Information and Photographic Documentation
APPENDIX K: Eastside Basin Site Information and Photographic Documentation K1: 531SJC503 – Lone Tree Creek at Austin Road.…………………………………03-04 K2: 531SJC504 – French Camp Slough at Airport Way..……………………....……05-06 K3: 535MER576 – Turner Slough at Fourth Avenue….…..……………………........07-08 K4: 535MER546 – Merced River at River Road……………………………………….09-10 K5: 535STC501 – TID 5 Harding Drain at Carpenter Road...……………………….11-12 K6: 535STC513 – Tuolumne River at Shiloh Fishing Access..……………………...13-14 K7: 535STC514 – Stanislaus River at Caswell Park...……………………………….15-16
2
K1: 531SJC503 – Lone Tree Creek at Austin Road
MONITORING SITE INFORMATION Site Description, Location and Access: Going East on Camp Road from Highway 99, turn left (north) onto Austin Rd. As the road curves to the right it will cross the Creek. Latitude/Longitude: Lat. N 37° 51’ 20” Long. W 121° 11’ 06” County: San Joaquin WATER SOURCE A 20 mile natural Channel originating south of Woodward Reservoir, this ephemeral stream carries natural runoff for four months of the year, in a westerly direction until its confluence with French Camp Slough and ultimate discharge into the San Joaquin River. Between March and November, flows in the creek are dominated by agricultural return flow beginning south of Woodward and continuing to French Camp Slough. Water is recaptured from irrigation as it moves downstream.
3
Water Year 2004 – Dry Water Year 2005 – Wet Rainy Season
02/24/04 02/23/05
Spring Runoff
04/28/04 04/26/05
Irrigation Season
07/28/04 07/26/05
Dry Season
09/29/04 09/27/05
K2: 531SJC504 – French Camp Slough at Airport Way
MONITORING SITE INFORMATION Site Description, Location and Access: Exit West onto French Camp Road (J9) off of Highway 99 South of Stockton. Make a right hand turn onto Airport Way (J3). Access to this site is via the Northwest side of the Slough where it meets Airport Way, at the Gauging system. Latitude/Longitude: Lat. N 37° 52’ 54.2” Long. W 121° 14’ 57.6” County: San Joaquin WATER SOURCE French Camp Slough originates at the confluence of Lone Tree Creek and Littlejohns Creek. The Slough carries agricultural return flows from March to November and storm runoff the rest of the year (ISWP 1993). As a long term monitoring site, sampling was augmented as part of this project.
Water Year 2004 – Dry Water Year 2005 – Wet Rainy Season
02/24/04 02/23/05
Spring Runoff
03/24/04 03/29/05
Irrigation Season
07/28/04 07/26/05
Dry Season
09/29/04 09/27/05
K3: 535MER576 – Turner Slough at Fourth Avenue
MONITORING SITE INFORMATION Site Description, Location and Access: Going south on Highway 165, turn right (west) onto Fourth Avenue (south Stevenson). Access to the slough is on the south side of Fourth Avenue, 1/8 of a mile east of Edminster Rd. Samples are taken from the south side of the bridge. Latitude/Longitude: Lat. N 37° 19’ 14” Long. W 120° 53’ 21” County: Merced WATER SOURCE Turner Slough is a former flood channel that has no natural flow. The channel has been reconstructed and realigned now to serve as a main drain for areas in the Stevenson Water District. Flow in the reconstructed channel is totally agricultural drainage flows.
Water Year 2004 – Dry Water Year 2005 – Wet Rainy Season
02/26/04 02/24/05
Spring Runoff
04/29/04 04/28/05
Irrigation Season
07/29/04 07/28/05
Dry Season
09/30/04 09/29/05
K4: 535MER546 – Merced River at River Road
MONITORING SITE INFORMATION Site Description, Location and Access: The site is under the historic bridge on the north bank near the mouth of the Merced River. The site is accessed via the parking lot at the intersection of River Road and Kelly Roads. Township/Range/Section: NW ¼, SW ¼, SW ¼, Section 2, T7S, R9E (DWR#7S/9E-2N) Latitude/Longitude: Lat. N 37° 20’ 59” Long. W 120° 57’ 28” County: Merced USGS Quad Map: Gustine, CA WATER SOURCE Water quality at this site is likely to reflect the quality of the major eastside tributaries.
Water Year 2004 – Dry Water Year 2005 – Wet Rainy Season
02/24/05
Spring Runoff
04/29/04 04/28/05
Irrigation Season
07/28/05
Dry Season
09/30/04 09/27/05
K5: 535STC501 – TID 5 Harding Drain at Carpenter Road
MONITORING SITE INFORMATION Site Description, Location and Access: From interstate 5, take Fink Road east for approximately 3.6 miles. Continue northeast on Crows Landing Road for approximately 3.6 miles until Carpenter Road. Travel approximately 2.4 miles northwest until drain. Sample on west side. Township/Range/Section: SE ¼ Section 5, T5S, R9E Latitude/Longitude: Lat. N 37° 27’ 52” Long. W 120° 01’ 49” County: Stanislaus USGS Quad Map: Crows Landing, CA WATER SOURCE Agricultural return flows, sewage disposal, and industrial flows.
Water Year 2004 – Dry Water Year 2005 – Wet Rainy Season
11/20/03 11/23/04
Spring Runoff
04/28/05
Irrigation Season
07/29/04 07/28/05
Dry Season
09/30/04 09/29/05
K6: 535STC513 – Tuolumne River at Shiloh Fishing Access
MONITORING SITE INFORMATION Site Description, Location and Access: The site is on the left bank of the Tuolumne River, under the Shiloh Road Bridge, approximately seven miles upstream of the confluence with the San Joaquin River. The site can be reached following the sign for Shiloh fishing access on the south side of the Shiloh Road Bridge. Sample from the sandy bar under the bridge. Latitude/Longitude: Lat. N 37° 36’ 11” Long. W 121° 07’ 54” County: Stanislaus WATER SOURCE Water quality at this site is representative of drainage from the entire watershed (1,540 square miles) and has an average annual unimpaired runoff of about 1.8 million-acre feet. The area is a daytime recreation area and is adjacent to a Recreational Vehicle park. As a long time monitoring site, sampling was augmented as part of this project.
Water Year 2004 – Dry Water Year 2005 – Wet Rainy Season
02/26/04 02/24/05
Spring Runoff
04/29/04 04/28/05
Irrigation Season
07/29/04 07/28/05
Dry Season
09/30/04 09/29/05
K7: 535STC514 – Stanislaus River at Caswell Park
MONITORING SITE INFORMATION Site Description, Location and Access: This site is on the right bank of the Stanislaus River approximately seven miles upstream of the confluence with the San Joaquin River. The site can be reached by entering Caswell Memorial State Park via Austin Road, then following signs to campsite number 17. Walk down bank and collect sample from riprap. Latitude/Longitude: Lat. N 37° 42’ 09” Long. W 121° 10’ 38” County: Stanislaus WATER SOURCE Water quality at this site is representative of drainage from the entire watershed (1,100 square miles). Caswell Park is a 258-acre park containing examples of riparian forest. The area is a daytime and overnight recreation area supporting activities such as swimming, fishing, camping, and hiking. There are urban influences from nearby communities such as Oakdale and Riverbank. Orchards, cropland, pastureland, and herbaceous rangeland are among the land uses in the Caswell park vicinity. Flow at this site is moderate and the channel is approximately 30 feet wide. As a long term monitoring site, sampling was augmented as part of this project.
Water Year 2004 – Dry Water Year 2005 – Wet Rainy Season
02/24/04 02/23/05
Spring Runoff
03/24/04 04/26/05
Irrigation Season
07/28/04 07/26/05
Dry Season
09/29/04 09/27/05
APPENDIX L:
Southeast Basin Site Information and Photographic Documentation
APPENDIX L: Southeast Basin Site Information and Photographic Documentation L1: 545MAD006 – Lone Willow Slough at Road 9…………………….………………03-04 L2: 541MER015 – Santa Rita Slough at Highway 152…...……….….………....……05-06 L3: 535MER577 – Deep Slough at Green House Road………………………….......07-08 L4: 535MER007 – Bear Creek near Bert Crane Road…………….………………….09-10
2
L1: 545MAD006 – Lone Willow Slough at Road 9
MONITORING SITE INFORMATION Site Description, Location and Access: Exiting West from Highway 99 onto Avenue 7. Following Avenue 7 make a right hand turn onto Rd. 9. Access is via the east side of Rd. 9. Latitude/Longitude: Lat. N 36° 52’ 00.9” Long. W 120° 22’ 54.9” County: Madera WATER SOURCE Lone Willow Slough is an old flood channel of the San Joaquin River extending from near Mendota to the Fresno River. The slough was isolated off from the San Joaquin River with the construction of the Eastside Bypass. With the construction of Friant Dam, the Slough rarely conveys natural flood flows. There are discharges of tailwater into various reaches of the Slough, but these are not sufficient to sustain a continuous flow. The Slough is dominated by these flows as there is no other flow in the Slough. Some of these tailwater flows are diverted for agricultural use.
3
Water Year 2001 Water Year 2002 Rainy Season
12/28/00 01/31/02
Spring Runoff
04/26/01 04/24/02
Irrigation Season
07/25/01
Dry Season
09/27/01
L2: 541MER015 – Santa Rita Slough at Highway 152
MONITORING SITE INFORMATION Site Description, Location and Access: Going East on Highway 152 from Interstate 5. Access to the Slough is via Indiana Avenue on the south side of Highway 152 near the Cotton Gin. Latitude/Longitude: Lat. N 37° 02’ 51.1” Long. W 120° 35’ 36.9” County: Merced WATER SOURCE A former overflow channel of the San Joaquin River, Santa Rita Slough now only conveys flood flows and has been extensively modified to enhance its use as an agricultural supply and drainage channel. The seven-mile channel conveys supply and return flows from approximately the Merced-Fresno County line to its discharge into Salt Slough Ditch during the irrigation season (March to October).
Water Year 2001 Rainy Season
12/28/00
Spring Runoff
04/26/01
Irrigation Season
07/25/01
Dry Season
09/27/01
L3: 535MER577 – Deep Slough at Green House Road
MONITORING SITE INFORMATION Site Description, Location and Access: Exiting South onto Bert Crane Road from Highway 99 follow Bert Crane Road until it makes a left hand turn where it turns into Dan McNamara Road. Make a right hand turn (west) off of Dan McNamara onto Green House Road. Access to the sight is via Green House Road. Latitude/Longitude: Lat. N 37° 13’ 47.3” Long. W 120° 43’ 41.6” County: Merced WATER SOURCE Deep Slough is a small, reconstructed, former overflow channel of the San Joaquin River. The 1.35-mile slough receives agricultural drainage from 432 acres between February and October.
Water Year 2004 – Dry Water Year 2005 – Wet Rainy Season
02/26/04 02/24/05
Spring Runoff
04/29/04 04/28/05
Irrigation Season
07/29/04 06/30/05
Dry Season
08/26/04 08/25/05
L4: 535MER007 – Bear Creek near Bert Crane Road
MONITORING SITE INFORMATION Site Description, Location and Access: From Highway 99, head west on Highway 140 for approximately 7.3 miles to Bert Crane Road. Travel south on Bert Crane Road for Approximately 4.2 miles. Turn west on dirt road on south side of Bear Creek for approximately 300 feet to gauging station. Latitude/Longitude: Lat. N 37° 15’ 20” Long. W 120° 39’ 07” County: Merced WATER SOURCE Agricultural return flows, operational spill from Merced Irrigation District and storm flows.
Water Year 2004 – Dry Water Year 2005 – Wet Rainy Season
02/26/04 02/24/05
Spring Runoff
04/29/04 04/28/05
Irrigation Season
07/29/04 07/28/05
Dry Season
09/30/04 08/25/05
APPENDIX M:
Grasslands Basin Site Information and Photographic Documentation
APPENDIX M: Grasslands Basin Site Information and Photographic Documentation M1: 541MER531 – Salt Slough at Lander Avenue (Highway 165)…………………03-04 M2: 541MER536 – Mud Slough Upstream of SLD Terminus..…….….……....……05-06 M3: 541MER535 – San Luis Drain at Terminus………………………………….......07-08 M4: 541MER542 – Mud Slough (North) at SLD………..…………………………….09-10
2
M1: 541MER531 – Salt Slough at Lander Avenue (Highway 165)
MONITORING SITE INFORMATION Site Description, Location and Access: The site is located on Lander Avenue approximately 13.0 miles north of Los Banos and 5.0 miles south of Highway 140. The samples are taken at the northeast corner of bridge. Township/Range/Section: NW ¼, SE ¼, SE ¼, Section 10, T8S, R10E (DWR#8S/10E-10R) Latitude/Longitude: Lat. N 37o 14’ 55” Long. W 120o 51’ 04” County: Merced USGS Quad Map: San Luis Ranch, CA WATER SOURCE The water at this site is a blend of surface tail water, operational spills, and wetland drainage from the Salt Slough area. This site represents the drainage from the Grassland Watershed entering the San Joaquin River above Highway 140. The water quality and quantity at the site will vary, but the range of variation is dampened by the large amount of area, which drains into the San Joaquin River. Salinity is expected to be elevated.
3
Water Year 2004 – Dry Water Year 2005 – Wet Rainy Season
02/26/04 02/17/05
Spring Runoff
04/29/04 04/28/05
Irrigation Season
07/29/04 07/28/05
Dry Season
09/30/04 09/22/05
M2: 541MER536 – Mud Slough Upstream of SLD Terminus
MONITORING SITE INFORMATION Site Description, Location and Access: Township/Range/Section: SE ¼, SE ¼, Section 6, T8S, R10E Latitude/Longitude: Lat. N 37° 15’ 15” Long. W 120° 54’ 25” County: Merced USGS Quad Map: Gustine, CA WATER SOURCE Mud Slough (north) at this site carries mainly wetland spills and drainage. The flow is highly variable throughout the year, ranging from high flow during the wet season and during periods of wetland releases to very low flow during the summer and early fall. The water is usually elevated with respect to salinity.
Water Year 2004 – Dry Water Year 2005 – Wet Rainy Season
02/26/04 02/17/05
Spring Runoff
04/29/04 04/28/05
Irrigation Season
07/29/04 07/28/05
Dry Season
09/30/04 09/22/05
M3: 541MER535 – San Luis Drain at Terminus
MONITORING SITE INFORMATION Site Description, Location and Access: Township/Range/Section: SE ¼, SE ¼, Section 6, T8S, R10E Latitude/Longitude: Lat. N 37° 14’ 26” Long. W 120° 52’ 55” County: Merced USGS Quad Map: Gustine, CA WATER SOURCE This water at this site consists of subsurface agricultural drainage from the Grassland Watershed. The water is elevated with respect to salinity, selenium, and boron. Flows at this site are highly managed and tend to have the highest concentrations of salt selenium and boron in during the pre-irrigation season, with concentrations decreasing throughout the year to a minimum during the non-irrigation season.
Water Year 2004 – Dry Water Year 2005 – Wet Rainy Season
01/29/04 02/17/05
Spring Runoff
04/29/04 04/28/05
Irrigation Season
07/29/04 07/28/05
Dry Season
09/30/04 09/22/05
M4: 541MER542 – Mud Slough (North) at SLD
MONITORING SITE INFORMATION Site Description, Location and Access: The monitoring site is located approximately 5.2 miles east of Gustine and 2 miles southeast of Highway 140. The site is located at the footbridge 400 ft northwest of the terminus of the San Luis Drain. The site is located in the Kesterson National Wildlife Refuge. The USGS gauge is at the site. The sample is taken at the bridge. Township/Range/Section: SE ¼, SE ¼, Section 6, T8S, R10E Latitude/Longitude: Lat. N 37ο 15’ 50” Long. W 120o 54’ 22” County: Merced USGS Quad Map: Gustine WATER SOURCE Mud Slough (North) at this site carries a blend of subsurface tile drainage water and discharges from surrounding duck clubs. The main flow in Mud Slough (North) is composed of subsurface agricultural drainage flows from the San Luis Drain and seasonal wetland releases. Water quality at this site is elevated with respect to salinity, selenium, and boron.
Water Year 2004 – Dry Water Year 2005 – Wet Rainy Season
01/29/04 02/17/05
Spring Runoff
04/29/04 04/28/05
Irrigation Season
07/29/04 07/28/05
Dry Season
09/30/04 09/22/05
APPENDIX N:
Westside Basin Site Information and Photographic Documentation
APPENDIX N: Westside Basin Site Information and Photographic Documentation N1: 541STC019 – Orestimba Creek at River Road……………..……………………03-04 N2: 541STC515 – Salado Creek at Highway 33……………..…..….….……....……05-06 N3: 541STC516 – Del Puerto Creek at Vineyard Avenue..……….…………….......07-08 N4: 541STC040 – Ingram Creek at River Road…………..………….……………….09-10 N5: 541STC042 – Hospital Creek at River Road………….…………..………….......11-12 N6: 541STC030 – Grayson Road Drain at Grayson……....………..…………….......13-14
2
N1: 541STC019 – Orestimba Creek at River Road
MONITORING SITE INFORMATION Site Description, Location and Access: Orestimba Creek at River Road gives good access to the creek and represents runoff water quality just prior to its entrance to the San Joaquin River at Mile 109.0. Township/Range/Section: SE ¼, SE ¼, NE ¼, Section 18, T6S, R9E (DWR#6S/9E-18H) Latitude/Longitude: Lat. N 37° 24’ 50” Long. W 121° 00’ 51” County: Stanislaus USGS Quad Map: Crows Landing WATER SOURCE The water in Orestimba Creek consists of both natural surface flow from Orestimba Creek, Crow Creek and runoff, tail water and operational spills from the tear depending upon the intensity of irrigation on the area. There are no known discharges of tile drainage water directly into the creek Orestimba Creek carries both natural runoff and agricultural return flows. It is also likely that the deep entrenchment of the creek in its lower reaches near the San Joaquin causes seepage of groundwater into the creek in several reaches.
3
Water Year 2004 – Dry Water Year 2005 – Wet Rainy Season
02/26/04 02/16/05
Spring Runoff
04/29/04 04/20/05
Irrigation Season
07/29/04 07/20/05
Dry Season
09/02/04 09/21/05
N2: 541STC515 – Salado Creek at Highway 33
MONITORING SITE INFORMATION Site Description, Location and Access: Located just before the city of Patterson going South on Highway 33. Access to this Creek is via the east side of Highway 33 where it crosses the Creek. Bridge 38-20 Latitude/Longitude: Lat. N 37° 28’ 53.3” Long. W 121° 08’ 07.9” County: Stanislaus WATER SOURCE Salado Creek is an ephemeral stream originating in the Coast Range whose flows only reach the San Joaquin River during high flood periods. Natural runoff occurs for 2-3 months of the year upstream of power lines which transverse the creek approximately 1.5 miles upstream of Interstate 5. Downstream of the power line, the Creek channel is dominated by agricultural return flows from March to November. Downstream of the Delta Mendota Canal, the flood channel has been extensively reworked; now it can be considered a constructed channel carrying only agricultural return flows that is then piped underground from Highway 33 until it discharges into the San Joaquin River along Olive Avenue.
Water Year 2004 – Dry Water Year 2005 – Wet Rainy Season
02/26/04 02/16/05
Spring Runoff
04/29/04 04/20/05
Irrigation Season
08/26/04 07/20/05
Dry Season
09/02/04 09/21/05
N3: 541STC516 – Del Puerto Creek at Vineyard Avenue
MONITORING SITE INFORMATION Site Description, Location and Access: Del Puerto Creek at the intersection of Vineyard Road and Loquat. The creek is sampled at the bridge. Latitude/Longitude: Lat. N 37° 31’ 17.3” Long. W 121° 08’ 55.3” County: Stanislaus WATER SOURCE Type and source of water being monitored (description): The majority of the water in Del Puerto Creek is tail water from irrigated fields in the adjacent areas. Also in the creek is operational spill water from both West Stanislaus Irrigation District and Patterson Water District. Little if any tile drainage enters the creek. It would be expected that seepage into the creek from high groundwater would also be present but little is found. Comments on factors affecting water quality and quantity at the site: The quality of the creek will be related to the operational spill water quality and the quality of the tail water leaving individual fields.
Water Year 2004 – Dry Water Year 2005 – Wet Rainy Season
02/26/04 02/15/05
Spring Runoff
04/29/04 04/19/05
Irrigation Season
07/29/04 07/19/05
Dry Season
09/30/04 09/20/05
N4: 541STC040 – Ingram Creek at River Road
MONITORING SITE INFORMATION Site Description, Location and Access: Ingram Creek as it passes under River Road. Sample site is on the east side of the road 200 feet downstream of the last pope input to the drain at River Road. Township/Range/Section: SE ¼, NE ¼, SW ¼, Section 8, T4S, R7E (DWR#4S/7E-8L) Latitude/Longitude: Lat. N 37° 36’ 01” Long. W 121° 13’ 27” County: Stanislaus USGS Quad Map: Westley, CA WATER SOURCE The water in Ingram Creek at this site is a combination of tail water and subsurface tile drainage water. The majority of the flow will be tail water. The quality of the flow will be determined by the amount of tail water in the creek. The site is very near the Ingram Creek Drain (site STC041), which enters on the east side of River Road just downstream of the bridge from the south bank.
Water Year 2004 – Dry Water Year 2005 – Wet Rainy Season
02/24/04 02/15/05
Spring Runoff
04/28/04 04/19/05
Irrigation Season
07/28/04 07/19/05
Dry Season
09/29/04 09/20/05
N5: 541STC042 – Hospital Creek at River Road
MONITORING SITE INFORMATION Site Description, Location and Access: Hospital Creek just downstream of its crossing of River Road. Township/Range/Section: SW ¼, SW ¼, SW ¼, Section 5, T4S, R7E (DWR#4S/7E-5N) Latitude/Longitude: Lat. N 37° 36’ 38” Long. W 121° 13’ 43” County: Stanislaus USGS Quad Map: Westley, CA WATER SOURCE Hospital Creek carries storm runoff and tail water from irrigated land upslope. No known tile drainage enters the creek upstream of River Road.
Water Year 2004 – Dry Water Year 2005 – Wet Rainy Season
02/24/04 02/15/05
Spring Runoff
04/28/04 04/19/05
Irrigation Season
06/23/04 06/21/05
Dry Season
09/29/04 09/20/05
N6: 541STC030 – Grayson Road Drain at Grayson
MONITORING SITE INFORMATION Site Description, Location and Access: Sampling point is at the Grayson Road Bridge as it crosses the old river channel (0.15 miles west of the intersection of Grayson Road and Cox Road). Discharged is from a black pipe in the west bank of the old channel under the bridge. This closes pipeline collection system is owned and operated by the West Stanislaus Irrigation District. Township/Range/Section: NW ¼, SW ¼, NW ¼, Section 26, T4S, R7E (DWR#4S/7E-26E) Latitude/Longitude: Lat. N 37° 33’ 43” Long. W 121° 10’ 27” County: Stanislaus USGS Quad Map: Westley, CA WATER SOURCE All water entering this closed pipeline is tail water from the West Stanislaus Irrigation District. During periods of no flow, some seepage does enter the pipeline due to high groundwater in the area, but the flow is small compared to the total discharge volume.
Water Year 2004 – Dry Water Year 2005 – Wet Rainy Season
02/26/04 02/16/05
Spring Runoff
04/29/04 04/20/05
Irrigation Season
07/29/04 07/20/05
Dry Season
09/29/04 09/21/05
APPENDIX O:
Delta Basin Site Information and Photographic Documentation
APPENDIX O: Delta Basin Site Information and Photographic Documentation O1: 544SJC001 – New Jerusalem Tile Drain…………………………………………03-04 O2: 544SJC505 – Tom Paine Slough at Paradise Road……..…….….……....……05-06 O3: 544SJC506 – Old River at Tracy Blvd……………....………….…………….......07-08 O4: 544SJC509 – Mountain House Creek at Mountain House Parkway….……….09-10
2
O1: 544SJC001 – New Jerusalem Tile Drain
MONITORING SITE INFORMATION Site Description, Location and Access: This tile drain system discharges to the SJR at approximately mile 63.5. There is a concrete deep structure on the levee and the sample is taken from the river side of the levee below this structure. The site is accessed via Wright Road northeast off of Kasson Road for approximately 1.25 miles to a barn and farmhouse. Take the dirt road at the farmhouse and go southeast to the levee. Go south on the levee for approximately 0.2 miles to the drop structure and sample site. Alternate access to this site is via the Banta Carbona Canal levee road on the North side of the Banta Carbona Lift Pumps (the pumps are located approximately 1.0 miles south of Wright Rd. on the East side of Kasson Rd). By driving NE on the levee road to a second gate (past the fish screen) the drop structure and site is accessed by foot. Walk NE on the levee road to the site. For access to the levee road from Kasson Rd, contact: Keith Robertson, partner of K&H Farms, cell-- (209) 914-1391 office (209) 836-2068. Latitude/Longitude: Lat. N 37° 42’ 32” Long. W 121° 17’ 55” County: San Joaquin WATER SOURCE: The water source for the drain farm tile drainage.
3
Water Year 2004 – Dry Water Year 2005 – Wet Rainy Season
02/24/04 02/23/05
Spring Runoff
04/26/05
Irrigation Season
07/28/04 07/26/05
Dry Season
09/29/04 09/27/05
O2: 544SJC505 – Tom Paine Slough at Paradise Road
MONITORING SITE INFORMATION Site Description, Location and Access: Exit North onto Macarthur Boulevard off of Interstate 205. Make a right hand turn onto Arbor Road. Follow Arbor Road until it dead ends into Paradise Road. Make a left hand turn onto Paradise Road. Follow Tom Payne Slough along the right side of Paradise Road until you come to the bridge. Access is via the Northeast corner of the bridge. Latitude/Longitude: Lat. N 37° 46’ 27.1” Long. W 121° 22’ 55.8” County: San Joaquin WATER SOURCE Tom Payne Slough is a natural flood channel of the San Joaquin River. River and agricultural development has cut off the Slough from the San Joaquin River. Flow in the Slough is now from the Delta and return flows entering the Slough. The Slough, from its origin near the San Joaquin River to the tide gates at Sugar Cut, is dominated by agricultural activities and return flows. The portion downstream of the tide gates is a natural channel, but flow and quality are affected by NPDES discharges near Sugar Cut. These discharges also affect the quality in Tom Payne Slough during high tide periods as water flows into the Slough.
Water Year 2004 – Dry Water Year 2005 – Wet Rainy Season
02/24/04 02/23/05
Spring Runoff
04/28/04 04/26/05
Irrigation Season
07/28/04 07/26/05
Dry Season
09/29/04 09/27/05
O3: 544SJC506 – Old River at Tracy Blvd
MONITORING SITE INFORMATION Site Description, Location and Access: Exit North onto Tracy Boulevard off of Interstate 205. Follow Tracy Boulevard, North, until it comes to Old River, the first Bridge. Access is via the Northeast side of the Bridge next to the Gauging System. Latitude/Longitude: Lat. N 37° 48’ 17.2” Long. W 121° 26’ 58.3” County: San Joaquin WATER SOURCE A major river that borders the South Delta Basin, influenced heavily by river flow, pumping action, and tides. It is argued that Old River can be designated as a natural water body dominated by agricultural supply, but estuary flow characteristics are considered more dominant.
Water Year 2004 – Dry Water Year 2005 – Wet Rainy Season
02/24/04 02/23/05
Spring Runoff
04/28/04 04/26/05
Irrigation Season
07/28/04 07/26/05
Dry Season
09/29/04 09/27/05
O4: 544SJC509 – Mountain House Creek at Mountain House Parkway
MONITORING SITE INFORMATION Site Description, Location and Access: Going Northwest on Byron Highway (J4) out of Tracy, the Creek can be accessed on your right hand side approx. 2/5 mile after the Mt. House Parkway turn off. Access is via a dirt road that crosses over the Creek itself. Note: As you approach Mt. House Creek driving on Byron Highway, you will notice a row of trees that lines the creek on the left hand side of the Highway. Access is on your right where the creek crosses under the Highway. Latitude/Longitude: Lat. N 37o 47’ 8.88” Long. W -121o 32’ 8.12” County: San Joaquin WATER SOURCE The water type and source being discharged is farm tile drainage. This water discharges directly into Old River.
Water Year 2002 Water Year 2003 Rainy Season
01/29/02 01/28/03
Spring Runoff
04/23/02 04/22/03
Irrigation Season
06/18/02 06/24/03
Dry Season
08/27/02 08/26/03
APPENDIX P
EXCEEDANCE/ELEVATED LEVELS SUMMARY
Appendix P: Exceedance/elevated levels Summary
Temp Counts: Bay-Delta
Authority targets Temp (ºC)
Field SC Counts
Goal Basin PlanBasin Plan
(ref) Goal
San Joaquin River at Vernalis
SJR at Airport Way , Vernalis; Old r iver at tracy Road Bridge MUN
Irrig. Water Supply
Location Site
Bay-Delta Authority
targets (Apr-Jun, Sep-Nov 20ºC)
Basin Plan (700 Apr-Aug)
(1000 Sep-Mar)
California Secondary
MCL (Short Term 2200 umhos/cm)
Water quality for
Agriculture (Ayers and Westcot)
(700umhos/cm)
Main StemSJR @Sack Dam 541MAD007 33 15 65 1 0 10SJR @ Lander 541MER522 132 64 265 189 2 215SJR @ Fremont Ford 541MER538 128 55 256 232 11 244SJR @ Hills Ferry 541STC512 44 25 83 77 15 80SJR @ Crows 535STC504 130 51 261 194 0 219SJR @ Patterson 541STC507 132 63 262 203 0 224SJR @ Maze 541STC510 129 60 260 122 0 191SJR @ Airport Way/Vernalis 541SJC501 131 55 265 56 0 136
Total Main Stem Count 859 388 1717 1074 28 1319Southeast Bas in Deep Slough Green House Rd 535MER577 26 12 54 6 0 8Santa Rita Slough at Highway 152 541MER015 1 1 5 0 0 3 Bear Creek Bert Crane Rd 535MER007 31 14 60 0 0 0
Total Southeast Basin Count 58 27 119 6 0 11Grassland BasinSalt Slough @Lander/Hwy 165 541MER531 131 47 262 256 NA 262Mud Slough (n) (upstream) @ SLD 541MER536 132 66 259 231 NA 257Discharge from SLD 541MER535 134 68 264 264 NA 264Mud Slough (n) (downstream) @ SLD 541MER542 134 65 264 264 NA 264
Total Grassland Basin Count 531 246 1049 1015 NA 1047Eastside BasinTurner Slough at 4th Avenue 535MER576 28 14 51 0 0 0Merced River Hatf ield Park (River Rd) 541MER546 26 9 54 0 0 0Harding Drain discharge @ SJR (TID5) 535STC501 37 19 74 26 0 37French Camp Slough @ Airport 531SJC504 23 6 48 0 0 2
Lone Tree Creek @ Austin Rd 531SJC503 23 6 49 0 0 0 Tuolumne River @ Shiloh 535STC513 43 22 84 0 0 0 Stanislaus River @Caswell 535STC514 23 3 49 0 0 0
Total Eastside Basin Count 203 79 409 26 0 39West Side BasinOres timba Creek @ River Rd. 541STC019 102 26 197 62 0 114Solado Creek @ Hwy 33 541STC515 36 15 70 37 2 49Del Puerto Creek @Vineyard 541STC516 38 18 68 36 0 45Grayson Drain 541STC030 30 14 56 27 0 36Ingram Creek @River Rd. 541STC040 38 8 72 55 0 61Hospital Creek @River Rd. 541STC042 30 7 53 22 0 25
Total West Side Basin Count 274 88 516 239 2 330Northeast BasinCosumnes River @ Twin Cities Rd. 531SAC001 19 5 38 0 0 0Mokelumne River @New Hope Rd. 544SAC002 30 3 58 0 NA 0Pixley Slough @ Davis Rd 531SJC507 31 5 54 0 0 0Bear Creek @ Thorton Road (J8) 544SJC508 13 3 26 0 0 0Bear Creek @Lower Sacramento Rd. 531SJC515 20 6 36 0 0 0
Total Northeast Basin Count 113 22 212 0 0 0Delta BasinNew Jerusalem Drain 544SJC001 28 1 52 52 48 52Tom Payne Slough @Paradise Rd. 544SJC505 30 12 56 56 20 56Old River @Tracy Blvd 544SJC506 31 14 60 28 0 46Mountain House Creek 544SJC509 9 3 20 7 5 9
Total Delta Basin Count 98 30 188 143 73 163
Total Program Count 2136 880 4210 2503 103 2909NA= Not Applicable/Not a designated Benificial Use
Field SC (umhos)
*Note for the Field SC Basin Plan objective for SJR at Airport Way the thirty day running average defined in the basin plan was not applied; looking only at individual grab samples.
Appendix P: Exceedance/elevated levels Summary continued…
pH Counts pH
Dissolved Oxygen Counts
Turbidity Counts
Turbidity (NTU)
Basin Plan Basin Plan Basin Plan Basin Plan
In fresh water w/
designated COLD or WARM
beneficial uses
All other2 Delta waters excluding bodies of water
constructed for special purposes and from which fish have been excluded or
where the fishery is not important as a beneficial
use
Cold/Spawning: Cosumnes, Mokelumne, Calaveras, Stanislaus
from Goodwin Dam to SJR, Tuolumne from New Don Pedro
Dam to SJR, Fr iant Dam to Mendota Pool, McSWAIN
reservoir to SJR, Spawning3: Mendota dam to Vernalis, Mud
Slough North, Salt Slough.
Delta waters6:
except for periods of
storm runoff :Other Delta
waters
LocationBasin Plan (<6.5, >8.5) Basin Plan (5.0mg/L) Basin Plan (7.0mg/L)
Bas in Plan (150 NTU)
Main StemSJR @Sack Dam 65 4 51 NA 7 NA NASJR @ Lander 261 24 217 NA 26 NA NASJR @ Fremont Ford 256 2 214 NA 30 NA NASJR @ Hills Ferry 82 0 67 NA 6 NA NASJR @ Crows 259 0 216 NA 9 NA NASJR @ Patterson 260 10 215 NA 1 NA NASJR @ Maze 258 34 213 NA 3 NA NASJR @ Airport Way/Vernalis 263 42 216 NA 1 NA NA
1704 116 1409 NA 83 NA NASoutheast Bas in Deep Slough Green House Rd 54 8 43 NA 10 NA NASanta Rita Slough at Highway 152 5 0 1 NA 1 NA NA Bear Creek Bert Crane Rd 60 4 49 NA 2 NA NA
119 12 93 NA 13 0 NAGrassland BasinSalt Slough @Lander/Hwy 165 260 2 216 NA 60 NA NAMud Slough (n) (upstream) @ SLD 257 12 210 NA 30 NA NADischarge from SLD 261 43 218 NA 3 NA NAMud Slough (n) (downstream) @ SLD 261 17 218 NA 16 NA NA
1039 74 1005 NA 109 0 NAEastside BasinTurner Slough at 4th Avenue 51 5 47 NA 19 NA NAMerced River Hatf ield Park (River Rd) 54 5 46 NA 1 NA NAHarding Drain discharge @ SJR (TID5) 74 2 62 NA 2 NA NAFrench Camp Slough @ Airport 47 2 38 NA 9 NA NA
Lone Tree Creek @ Austin Rd 49 6 37 NA 7 NA NA Tuolumne River @ Shiloh 84 4 69 NA 2 NA NA Stanislaus River @Caswell 49 3 40 NA 0 NA NA
408 27 339 NA 40 0 NAWest Side BasinOrestimba Creek @ River Rd. 197 5 176 NA 5 NA NASolado Creek @ Hwy 33 70 10 61 NA 1 NA NADel Puerto Creek @Vineyard 68 10 56 NA 8 NA NAGrayson Drain 56 6 47 NA 2 NA NAIngram Creek @River Rd. 72 2 63 NA 1 NA NAHospital Creek @River Rd. 53 2 47 NA 1 NA NA
516 35 450 NA 18 0 NANortheast BasinCosumnes River @ Twin Cities Rd. 38 7 27 NA 0 NA NAMokelumne River @New Hope Rd. 57 5 48 NA 6 18 0Pixley Slough @ Davis Rd 53 2 47 NA 17 NA NABear Creek @ Thorton Road (J8) 25 2 16 2 NA 2 0Bear Creek @Lower Sacramento Rd. 36 0 36 NA 21 NA NA
209 16 174 2 44 20 0Delta BasinNew Jerusalem Drain 51 0 42 0 NA 13 0Tom Payne Slough @Paradise Rd. 55 0 46 10 NA 17 0Old River @Tracy Blvd 59 2 50 1 NA 20 0Mountain House Creek 20 1 12 1 NA 6 1
185 3 150 12 NA 56 1
4180 283 3620 14 307 76 1NA= Not Applicable/Not a designated Benificial Use
Dissolved Oxygen (mg/L)
Appendix P: Exceedance/elevated levels Summary continued…
TOC Sample Counts
TOC (mg/L)
E. coli Sample Counts
E. coli MPN
Target GoalSource water quality for the
Delta Rec. Use
Location Site
Bay-Delta Authority (3.0mg/L)
USEPA Guideline_Designated Beach Area
(235 MPN)
Main StemSJR @Sack Dam 541MAD007 33 17 30 1SJR @ Lander 541MER522 162 154 46 7SJR @ Fremont Ford 541MER538 160 154 46 6SJR @ Hills Ferry 541STC512 30 29 29 10SJR @ Crows 535STC504 162 144 46 8SJR @ Patterson 541STC507 161 150 46 6SJR @ Maze 541STC510 157 116 46 6SJR @ Airport Way/Vernalis 541SJC501 163 110 46 7
Total Main Stem Count 1028 874 335 51Southeast Bas in Deep Slough Green House Rd 535MER577 31 29 25 12Santa Rita Slough at Highway 152 541MER015 5 4 NA 0 Bear Creek Bert Crane Rd 535MER007 31 24 30 24
Total Southeast Basin Count 67 57 55 36Grassland BasinSalt Slough @Lander/Hwy 165 541MER531 38 35 30 5Mud Slough (n) (upstream) @ San Luis Drain 541MER536 38 35 29 10Discharge from SLD 541MER535 33 30 21 1Mud Slough (n) (downstream) @ San Luis Drain 541MER542 39 37 28 3
Total Grassland Basin Count 148 137 108 19Eastside BasinTurner Slough at 4th Avenue 535MER576 29 28 28 23Merced River Hatf ield Park (River Road) 541MER546 26 7 26 7Harding Drain discharge @ San Joaquin River (TID5) 535STC501 34 31 40 33French Camp Slough @ Airport 531SJC504 28 25 22 10Lone Tree Creek @ Austin Rd 531SJC503 23 22 21 16 Tuolumne River @ Shiloh 535STC513 34 6 46 7 Stanislaus River @Caswell 535STC514 23 7 22 2
Total Eastside Basin Count 197 126 205 98West Side BasinOres timba Creek @ River Rd. 541STC019 33 22 39 27Solado Creek @ Hwy 33 541STC515 36 30 40 23Del Puerto Creek @Vineyard 541STC516 33 27 38 30Grayson Drain 541STC030 27 25 31 17Ingram Creek @River Rd. 541STC040 25 18 40 18Hospital Creek @River Rd. 541STC042 18 17 33 19
Total West Side Basin Count 172 139 221 134Northeast BasinCosumnes River @ Twin Cities Rd. 531SAC001 21 8 16 2Mokelumne River @New Hope Rd. 544SAC002 30 7 28 2Pixley Slough @ Davis Rd 531SJC507 24 11 28 15Bear Creek @ Thorton Road (J8) 544SJC508 15 12 2 0Bear Creek @Lower Sacramento Rd. 531SJC515 14 13 28 6
Total Northeast Basin Count 104 51 102 25Delta Basin New Jerusalem Drain 544SJC001 28 7 20 0 Tom Payne Slough @Paradise Rd. 544SJC505 30 25 26 4Old River @Tracy Blvd 544SJC506 31 25 30 2Mountain House Creek 544SJC509 14 12 2 2
Total Delta Basin Count 103 69 78 8
Total Program Count 1819 1453 1104 371NA= Not Applicable/Not a designated Benificial Use
Appendix P: Exceedance/elevated levels Summary continued… Nitrate Sample Counts Nitrate (mg/L)
Nitrate-N Sample Counts
Nitrate-N (mg/L)
Ammonia-N Sample Counts
Ammonia-N (mg/L)
Basin Plan (ref) Basin Plan (ref) GoalMun Mun Aquatic Life
Location SiteCalifornia Primary
MCL (45mg/L)California Primary
MCL (10mg/L)
USEPA National Ambient W Q Criteria/1 hour average (calc)
Main StemSJR @Sack Dam 541MAD007 14 0 NA 0 NA 0SJR @ Lander 541MER522 22 0 NA 0 NA 0SJR @ Fremont Ford 541MER538 37 0 24 0 17 0SJR @ Hills Ferry 541STC512 11 0 NA 0 NA 0SJR @ Crows 535STC504 39 0 27 0 17 0SJR @ Patterson 541STC507 20 0 NA 0 1 0SJR @ Maze 541STC510 19 0 NA 0 1 0SJR @ Airport Way/Vernalis 541SJC501 23 0 NA 0 1 0
Total Main Stem Count 185 0 51 0 37 0Southeast Bas in Deep Slough Green House Rd 535MER577 11 0 NA 0 NA 0Santa Rita Slough at Highway 152 541MER015 4 0 NA 0 NA 0 Bear Creek Bert Crane Rd 535MER007 11 0 NA 0 NA 0
Total Southeast Basin Count 26 0 0 0 0 0Grassland BasinSalt Slough @Lander/Hwy 165 541MER531 14 13 NA 0 NA 0
Mud Slough (n) (upstream) @ San Luis Drain 541MER536 30 0 25 0 18 0Discharge from SLD 541MER535 19 14 27 18 19 0Mud Slough (n) (downstream) @ San Luis Drain 541MER542 19 8 27 3 21 0
Total Grassland Basin Count 82 35 79 21 58 0Eastside BasinTurner Slough at 4th Avenue 535MER576 9 0 NA 0 NA 0Merced River Hatf ield Park (River Road) 541MER546 10 NA NA NA NA 0Harding Drain discharge @ San Joaquin River (TID5) 535STC501 14 0 NA 0 NA 0French Camp Slough @ Airport 531SJC504 11 0 31 0 NA 0Lone Tree Creek @ Austin Rd 531SJC503 14 0 NA 0 NA 0 Tuolumne River @ Shiloh 535STC513 14 0 NA 0 NA 0 Stanislaus River @Caswell 535STC514 11 0 NA 0 NA 0
Total Eastside Basin Count 83 0 31 0 0 0West Side BasinOres timba Creek @ River Rd. 541STC019 10 0 NA 0 1 0Solado Creek @ Hwy 33 541STC515 12 0 NA 0 NA 0Del Puerto Creek @Vineyard 541STC516 11 1 NA 0 NA 0Grayson Drain 541STC030 11 0 NA 0 NA 0Ingram Creek @River Rd. 541STC040 12 4 NA 0 NA 0Hospital Creek @River Rd. 541STC042 8 0 NA 0 NA 0
Total West Side Basin Count 64 5 0 0 1 0Northeast BasinCosumnes River @ Twin Cities Rd. 531SAC001 9 0 NA 0 NA 0Mokelumne River @New Hope Rd. 544SAC002 12 NA NA NA NA 0Pixley Slough @ Davis Rd 531SJC507 9 0 NA 0 NA 0Bear Creek @ Thorton Road (J8) 544SJC508 12 0 NA 0 NA 0Bear Creek @Lower Sacramento Rd. 531SJC515 NA 0 NA 0 NA 0
Total Northeast Basin Count 42 0 0 0 0 0Delta Basin New Jerusalem Drain 544SJC001 10 10 NA 0 NA 0 Tom Payne Slough @Paradise Rd. 544SJC505 12 0 NA 0 NA 0Old River @Tracy Blvd 544SJC506 12 0 NA 0 NA 0Mountain House Creek 544SJC509 10 0 NA 0 NA 0
Total Delta Basin Count 44 10 0 0 0 0
Total Program Count 526 50 161 21 96 0NA= Not Applicable/Not a designated Benificial Use
Appendix P: Exceedance/elevated levels Summary continued… Total
Arsenic Sample Count
Total Cadmium Sample Count
Basin Plan (ref) Goal Goal Basin Plan (ref) Goal Goal
MUNIrrig. Water
Supply Drinking Water Mun Aquatic LifeIrr ig. Water
Supply
Location Site
Basin Plan (ref) (MUN) Cal
Primary MCL (50ug/L)
Water Quality for Agriculture
(Ayers & Westcot) (100ug/L)
USEPA Primary MCL (10ug/L)
Bas in Plan (ref) (MUN) Cal
Primary MCL (5ug/L)
California Toxics rule
(USEPA) (calc)
Water Quality for Agriculture
(Ayers & Westcot) (10ug/L)
Main StemSJR @Sack Dam 541MAD007 18 0 0 0 18 0 0 0SJR @ Lander 541MER522 21 0 0 6 21 0 0 0SJR @ Fremont Ford 541MER538 22 0 0 0 22 0 0 0SJR @ Hills Ferry 541STC512 16 0 0 0 16 0 0 0SJR @ Crows 535STC504 24 0 0 0 23 0 0 0SJR @ Patterson 541STC507 22 0 0 0 21 0 0 0SJR @ Maze 541STC510 21 0 0 0 20 0 0 0SJR @ Airport Way/Vernalis 541SJC501 22 0 0 0 21 0 0 0
Total Main Stem Count 166 0 0 6 162 0 0 0Southeast Bas in Deep Slough Green House Rd 535MER577 17 0 0 4 17 0 0 0Santa Rita Slough at Highway 152 541MER015 2 0 0 0 2 0 0 0 Bear Creek Bert Crane Rd 535MER007 18 0 0 0 18 0 0 0
Total Southeast Basin Count 37 0 0 4 37 0 0 0Grassland BasinSalt Slough @Lander/Hwy 165 541MER531 21 NA 0 0 20 NA 0 0Mud Slough (n) (upstream) @ San Luis Drain 541MER536 22 NA 0 0 21 NA 0 0Discharge from SLD 541MER535 22 NA 0 0 21 NA 0 0Drain 541MER542 22 NA 0 0 21 NA 0 0
Total Grassland Basin Count 87 NA 0 0 83 NA 0 0Eastside BasinTurner Slough at 4th Avenue 535MER576 17 0 0 0 17 0 0 0Merced River Hatf ield Park (River Road) 541MER546 13 0 0 0 13 0 0 0Harding Drain discharge @ San Joaquin River (TID5) 535STC501 18 0 0 0 18 0 0 0French Camp Slough @ Airport 531SJC504 14 0 0 0 14 0 0 0Lone Tree Creek @ Austin Rd 531SJC503 12 0 0 0 12 0 0 0 Tuolumne River @ Shiloh 535STC513 18 0 0 0 18 0 0 0 Stanislaus River @Caswell 535STC514 13 0 0 0 13 0 0 0
Total Eastside Basin Count 105 0 0 0 105 0 0 0West Side BasinOres timba Creek @ River Rd. 541STC019 18 0 0 0 18 0 0 0Solado Creek @ Hwy 33 541STC515 17 0 0 0 17 0 0 0Del Puerto Creek @Vineyard 541STC516 13 0 0 0 13 0 0 0Grayson Drain 541STC030 15 0 0 3 15 0 0 0Ingram Creek @River Rd. 541STC040 17 0 0 0 17 0 0 0Hospital Creek @River Rd. 541STC042 11 0 0 0 11 0 0 0
Total West Side Basin Count 91 0 0 3 91 0 0 0Northeast BasinCosumnes River @ Twin Cities Rd. 531SAC001 12 0 0 0 12 0 0 0Mokelumne River @New Hope Rd. 544SAC002 18 NA 0 NA 18 NA 0 0Pixley Slough @ Davis Rd 531SJC507 17 0 0 0 17 0 0 0Bear Creek @ Thorton Road (J8) 544SJC508 11 0 0 0 11 0 0 0Bear Creek @Lower Sacramento Rd. 531SJC515 17 0 0 0 17 0 0 0
Total Northeast Basin Count 75 0 0 0 75 0 0 0Delta Basin New Jerusalem Drain 544SJC001 18 0 0 0 18 0 0 0 Tom Payne Slough @Paradise Rd. 544SJC505 18 0 0 0 18 0 0 0Old River @Tracy Blvd 544SJC506 18 0 0 0 18 0 0 0Mountain House Creek 544SJC509 9 0 0 0 9 0 0 0
Total Delta Basin Count 63 0 0 0 63 0 0 0
Total Program Count 624 0 0 13 616 0 0 0NA= Not Applicable/Not a designated Benificial Use
Total Arsenic (ug/L) Total Cadmium (ug/L)
Appendix P: Exceedance/elevated levels Summary continued… Total
Chromium Sample Count
Total Chromium
(ug/L)
Total Copper Sample Count
Basin Plan (ref) Basin Plan (ref) Goal Goal Goal
Mun Mun Aquatic LifeIrrig. Water
Supply Drinking Water
Location Site
Basin Plan (ref) (MUN) Cal
Primary MCL (50ug/L)
Basin Plan (ref) (MUN) Cal
Primary MCL (1000ug/L)
California Toxics rule
(USEPA) (calc)
Water Quality for Agriculture
(Ayers & Westcot) (200ug/L)
California Toxics Rule (USEPA) for sources of
drinking water (1300ug/L)
Main StemSJR @Sack Dam 541MAD007 26 0 26 0 0 0 0SJR @ Lander 541MER522 31 0 31 0 0 0 0SJR @ Fremont Ford 541MER538 30 0 29 0 0 0 0SJR @ Hills Ferry 541STC512 24 0 23 0 0 0 0SJR @ Crows 535STC504 32 0 30 0 0 0 0SJR @ Patterson 541STC507 30 0 28 0 0 0 0SJR @ Maze 541STC510 29 0 27 0 0 0 0SJR @ Airport Way/Vernalis 541SJC501 32 0 30 0 0 0 0
Total Main Stem Count 234 0 224 0 0 0 0Southeast Bas in Deep Slough Green House Rd 535MER577 26 0 26 0 0 0 0Santa Rita Slough at Highway 152 541MER015 5 0 5 0 0 0 0 Bear Creek Bert Crane Rd 535MER007 27 0 27 0 4 0 0
Total Southeast Basin Count 58 0 58 0 4 0 0Grassland BasinSalt Slough @Lander/Hwy 165 541MER531 20 NA 29 NA 0 0 0
Mud Slough (n) (upstream) @ San Luis Drain 541MER536 30 NA 28 NA 0 0 0Discharge from SLD 541MER535 29 NA 28 NA 0 0 0Mud Slough (n) (downstream) @ San Luis Drain 541MER542 30 NA 28 NA 0 0 0
Total Grassland Basin Count 109 NA 113 NA 0 0 0Eastside BasinTurner Slough at 4th Avenue 535MER576 24 0 24 0 1 0 0Merced River Hatf ield Park (River Road) 541MER546 21 0 18 0 0 0 0Harding Drain discharge @ San Joaquin River (TID5) 535STC501 28 0 27 0 1 0 0French Camp Slough @ Airport 531SJC504 22 0 22 0 7 0 0Lone Tree Creek @ Austin Rd 531SJC503 22 0 21 0 9 0 0 Tuolumne River @ Shiloh 535STC513 28 0 26 0 1 0 0 Stanislaus River @Caswell 535STC514 20 0 18 0 0 0 0
Total Eastside Basin Count 165 0 156 0 19 0 0West Side BasinOres timba Creek @ River Rd. 541STC019 27 0 25 0 0 0 0Solado Creek @ Hwy 33 541STC515 25 0 23 0 0 0 0Del Puerto Creek @Vineyard 541STC516 20 0 18 0 0 0 0Grayson Drain 541STC030 22 4 20 0 0 0 0Ingram Creek @River Rd. 541STC040 25 3 23 0 2 0 0Hospital Creek @River Rd. 541STC042 17 3 15 0 1 0 0
Total West Side Basin Count 136 10 124 0 3 0 0Northeast BasinCosumnes River @ Twin Cities Rd. 531SAC001 20 0 20 0 0 0 0Mokelumne River @New Hope Rd. 544SAC002 27 NA 27 NA 1 0 NAPixley Slough @ Davis Rd 531SJC507 23 0 23 0 11 0 0Bear Creek @ Thorton Road (J8) 544SJC508 20 0 20 0 5 0 0Bear Creek @Lower Sacramento Rd. 531SJC515 25 0 23 0 1 0 0
Total Northeast Basin Count 115 0 113 0 18 0 0Delta Basin New Jerusalem Drain 544SJC001 27 0 27 0 0 0 0 Tom Payne Slough @Paradise Rd. 544SJC505 27 0 27 0 0 0 0Old River @Tracy Blvd 544SJC506 27 0 27 0 0 0 0Mountain House Creek 544SJC509 16 0 16 0 0 0 0
Total Delta Basin Count 97 0 97 0 0 0 0
Total Program Count 914 10 885 0 44 0 0NA= Not Applicable/Not a designated Benificial Use
Total Copper (ug/L)
Appendix P: Exceedance/elevated levels Summary continued…
Total Lead Sample Count
Total Nickel Sample Count
Basin Plan (ref) Goal Goal Basin Plan (ref) Goal Goal Goal
Mun Aquatic LifeIrrig. Water
Supply Mun Aquatic LifeIrr ig. Water
Supply Drinking Water
Location Site
Basin Plan (ref) (MUN) Cal
Primary MCL (15ug/L)
California Toxics rule
(USEPA) (calc)
Water Quality for Agriculture
(Ayers & Westcot)
(5000ug/L)
Bas in Plan (ref) (MUN) Cal
Primary MCL (100ug/L)
California Toxics rule
(USEPA) (calc)
Water Quality for Agriculture
(Ayers & Westcot) (200ug/L)
California Toxics Rule (USEPA) for sources of
drinking water (610 ug/L)
Main StemSJR @Sack Dam 541MAD007 26 0 0 0 25 0 0 0 0SJR @ Lander 541MER522 31 0 0 0 31 0 0 0 0SJR @ Fremont Ford 541MER538 30 0 0 0 30 0 0 0 0SJR @ Hills Ferry 541STC512 25 0 0 0 24 0 0 0 0SJR @ Crows 535STC504 32 0 0 0 33 0 0 0 0SJR @ Patterson 541STC507 30 0 0 0 31 0 0 0 0SJR @ Maze 541STC510 29 0 0 0 30 0 0 0 0SJR @ Airport Way/Vernalis 541SJC501 32 0 0 0 33 0 0 0 0
Total Main Stem Count 235Southeast Bas in Deep Slough Green House Rd 535MER577 26 0 0 0 25 0 0 0 0Santa Rita Slough at Highway 152 541MER015 5 0 0 0 5 0 0 0 0 Bear Creek Bert Crane Rd 535MER007 27 0 0 0 26 0 0 0 0
Total Southeast Basin Count 58 0 0 0 56 0 0 0 0Grassland BasinSalt Slough @Lander/Hwy 165 541MER531 30 NA 0 0 29 NA 0 0 0
Mud Slough (n) (upstream) @ San Luis Drain 541MER536 30 NA 0 0 31 NA 0 0 0Discharge from SLD 541MER535 29 NA 0 0 30 NA 0 0 0Mud Slough (n) (downstream) @ San Luis Drain 541MER542 30 NA 0 0 31 NA 0 0 0
Total Grassland Basin Count 119 NA 0 0 121 NA 0 0 0Eastside BasinTurner Slough at 4th Avenue 535MER576 24 0 0 0 23 0 0 0 0Merced River Hatf ield Park (River Road) 541MER546 21 0 0 0 20 0 0 0 0Harding Drain discharge @ San Joaquin River (TID5) 535STC501 29 0 0 0 28 0 0 0 0French Camp Slough @ Airport 531SJC504 22 0 0 0 22 0 0 0 0Lone Tree Creek @ Austin Rd 531SJC503 23 0 0 0 22 0 0 0 0 Tuolumne River @ Shiloh 535STC513 29 0 0 0 28 0 0 0 0 Stanislaus River @Caswell 535STC514 21 0 0 0 20 0 0 0 0
Total Eastside Basin Count 169 0 0 0 163 0 0 0 0West Side BasinOres timba Creek @ River Rd. 541STC019 27 0 0 0 28 0 0 0 0Solado Creek @ Hwy 33 541STC515 26 0 0 0 25 0 0 0 0Del Puerto Creek @Vineyard 541STC516 21 0 0 0 21 0 0 0 0Grayson Drain 541STC030 23 4 0 0 22 2 0 0 0Ingram Creek @River Rd. 541STC040 26 4 0 0 25 1 0 0 0Hospital Creek @River Rd. 541STC042 17 3 0 0 17 1 0 0 0
Total West Side Basin Count 140 11 0 0 138 4 0 0 0Northeast BasinCosumnes River @ Twin Cities Rd. 531SAC001 20 0 0 0 20 0 0 0 0Mokelumne River @New Hope Rd. 544SAC002 27 NA 1 0 27 NA 0 0 NAPixley Slough @ Davis Rd 531SJC507 23 0 0 0 23 0 0 0 0Bear Creek @ Thorton Road (J8) 544SJC508 20 0 0 0 20 0 0 0 0Bear Creek @Lower Sacramento Rd. 531SJC515 26 0 0 0 25 0 0 0 0
Total Northeast Basin Count 116 0 1 0 115 0 0 0 0Delta Basin New Jerusalem Drain 544SJC001 27 0 0 0 27 0 0 0 0 Tom Payne Slough @Paradise Rd. 544SJC505 27 0 0 0 27 0 0 0 0Old River @Tracy Blvd 544SJC506 27 0 0 0 27 0 0 0 0Mountain House Creek 544SJC509 16 0 0 0 16 0 0 0 0
Total Delta Basin Count 97 0 0 0 97 0 0 0 0
Total Program Count 934 11 1 0 690 4 0 0 0NA= Not Applicable/Not a designated Benificial Use
Total Nickel (ug/L)Total Lead (ug/L)
Appendix P: Exceedance/elevated levels Summary continued…
Total Zinc Sample Count
Total Mercury Sample Count
Basin Plan (ref) Goal Goal Goal Basin Plan (ref) Goal Goal
Mun Aquatic LifeIrrig. Water
Supply Rec. Use Mun Aquatic Life Drinking Water
Location Site
Basin Plan (ref) (MUN) Cal
Primary MCL (5000ug/L)
California Toxics rule
(USEPA) (calc)
Water Quality for Agriculture
(Ayers & Westcot)
(2000ug/L)
USEPA IRIS Reference Dose
(2100ug/L)
Basin Plan (ref) (MUN) Cal
Primary MCL (2ug/L)
USEPA National Ambient W Q Criteria/1 hour
average (1.4ug/L)
California Toxics Rule (USEPA) for sources of
drinking water (0.05ug/L)
Main StemSJR @Sack Dam 541MAD007 25 0 0 0 0 15 0 0 0SJR @ Lander 541MER522 30 0 0 0 0 19 0 0 0SJR @ Fremont Ford 541MER538 31 0 0 0 0 21 0 0 0SJR @ Hills Ferry 541STC512 24 0 0 0 0 14 0 0 0SJR @ Crows 535STC504 32 0 0 0 0 23 0 0 0SJR @ Patterson 541STC507 30 0 0 0 0 21 0 0 0SJR @ Maze 541STC510 29 0 0 0 0 20 0 0 0SJR @ Airport Way/Vernalis 541SJC501 32 0 0 0 0 21 0 0 0
Total Main Stem CountSoutheast Bas in Deep Slough Green House Rd 535MER577 25 0 0 0 0 14 0 0 0Santa Rita Slough at Highway 152 541MER015 5 0 0 0 0 1 0 0 0 Bear Creek Bert Crane Rd 535MER007 26 0 0 0 0 15 0 0 0
Total Southeast Basin Count 56 0 0 0 0 30 0 0 0Grassland BasinSalt Slough @Lander/Hwy 165 541MER531 28 NA 0 0 0 19 NA 0 NA
Mud Slough (n) (upstream) @ San Luis Drain 541MER536 30 NA 0 0 0 21 NA 0 NADischarge from SLD 541MER535 29 NA 0 0 0 21 NA 0 NAMud Slough (n) (downstream) @ San Luis Drain 541MER542 30 NA 0 0 0 21 NA 0 NA
Total Grassland Basin Count 117 NA 0 0 0 82 NA 0 NAEastside BasinTurner Slough at 4th Avenue 535MER576 23 0 0 0 0 14 0 0 0Merced River Hatf ield Park (River Road) 541MER546 20 0 0 0 0 12 0 0 0Harding Drain discharge @ San Joaquin River (TID5) 535STC501 28 0 0 0 0 17 0 0 0French Camp Slough @ Airport 531SJC504 22 0 0 0 0 12 0 0 0Lone Tree Creek @ Austin Rd 531SJC503 22 0 0 0 0 11 0 0 0 Tuolumne River @ Shiloh 535STC513 27 0 0 0 0 17 0 0 0 Stanislaus River @Caswell 535STC514 20 0 0 0 0 12 0 0 0
Total Eastside Basin Count 162 0 0 0 0 95 0 0 0West Side BasinOres timba Creek @ River Rd. 541STC019 28 0 0 0 0 18 0 0 0Solado Creek @ Hwy 33 541STC515 25 0 0 0 0 15 0 0 0Del Puerto Creek @Vineyard 541STC516 21 0 0 0 0 11 0 0 0Grayson Drain 541STC030 22 0 0 0 0 13 0 0 0Ingram Creek @River Rd. 541STC040 25 0 0 0 0 16 0 0 0Hospital Creek @River Rd. 541STC042 17 0 0 0 0 10 0 0 1
Total West Side Basin Count 138 0 0 0 0 83 0 0 1Northeast BasinCosumnes River @ Twin Cities Rd. 531SAC001 20 0 0 0 0 12 0 0 0Mokelumne River @New Hope Rd. 544SAC002 27 NA 0 0 0 16 NA 0 NAPixley Slough @ Davis Rd 531SJC507 23 0 1 0 0 15 0 0 0Bear Creek @ Thorton Road (J8) 544SJC508 20 0 0 0 0 9 0 0 0Bear Creek @Lower Sacramento Rd. 531SJC515 25 0 0 0 0 15 0 0 0
Total Northeast Basin Count 115 0 1 0 0 67 0 0 0Delta Basin New Jerusalem Drain 544SJC001 27 0 0 0 0 16 0 0 0 Tom Payne Slough @Paradise Rd. 544SJC505 27 0 0 0 0 16 0 0 0Old River @Tracy Blvd 544SJC506 27 0 0 0 0 16 0 0 0Mountain House Creek 544SJC509 16 0 0 0 0 8 0 0 0
Total Delta Basin Count 97 0 0 0 0 56 0 0 0
Total Program Count 685 0 1 0 0 413 0 0 1NA= Not Applicable/Not a designated Benificial Use
Total Mercury (ug/L)Total Zinc (ug/L)
Appendix P: Exceedance/elevated levels Summary continued… Dissolved
Arsenic Sample Count
Dissolved Cadmium Sample Count
Dissolved Cadmium
(ug/L)
Dissolved Copper Sample Count
Basin Plan Goal Goal Basin Plan Goal
Sacramento-San Joaquin
Delta Aquatic Life Aquatic Life
Sacramento-San Joaquin
Delta Aquatic Life
Location SiteBasin Plan (10ug/L)
California Toxics Rule (USEPA)/ 1-hour average
(340 ug/L)
California Toxics rule
(USEPA) (calc)Basin Plan (10ug/L)
California Toxics rule
(USEPA) (calc)
Main StemSJR @Sack Dam 541MAD007 14 NA 0 14 0 21 NA 0SJR @ Lander 541MER522 17 NA 0 17 0 27 NA 0SJR @ Fremont Ford 541MER538 18 NA 0 18 0 25 NA 0SJR @ Hills Ferry 541STC512 12 NA 0 12 0 19 NA 0SJR @ Crows 535STC504 18 NA 0 18 0 25 NA 0SJR @ Patterson 541STC507 18 NA 0 18 0 25 NA 0SJR @ Maze 541STC510 17 NA 0 17 0 24 NA 0SJR @ Airport Way/Vernalis 541SJC501 18 NA 0 18 0 27 NA 0
Total Main Stem Count 132 NA 0 132 0 193 NA 0Southeast Bas in Deep Slough Green House Rd 535MER577 13 NA 0 13 0 21 NA 0Santa Rita Slough at Highway 152 541MER015 2 NA 0 2 0 5 NA 0 Bear Creek Bert Crane Rd 535MER007 14 NA 0 14 0 22 NA 0
Total Southeast Basin Count 29 NA 0 29 0 48 NA 0Grassland BasinSalt Slough @Lander/Hwy 165 541MER531 14 NA 0 14 0 22 NA 0
Mud Slough (n) (upstream) @ San Luis Drain 541MER536 18 NA 0 18 0 25 NA 0Discharge from SLD 541MER535 17 NA 0 17 0 23 NA 0Mud Slough (n) (downstream) @ San Luis Drain 541MER542 18 NA 0 18 0 25 NA 0
Total Grassland Basin Count 67 NA 0 67 0 95 NA 0Eastside BasinTurner Slough at 4th Avenue 535MER576 13 NA 0 13 0 19 NA 0Merced River Hatf ield Park (River Road) 541MER546 13 NA 0 13 0 19 NA 0Harding Drain discharge @ San Joaquin River (TID5) 535STC501 12 NA 0 12 0 21 NA 0French Camp Slough @ Airport 531SJC504 14 NA 0 14 0 20 NA 0Lone Tree Creek @ Austin Rd 531SJC503 12 NA 0 12 0 20 NA 7 Tuolumne River @ Shiloh 535STC513 13 NA 0 13 0 22 NA 0 Stanislaus River @Caswell 535STC514 13 NA 0 13 0 19 NA 0
Total Eastside Basin Count 90 NA 0 90 0 140 NA 7West Side BasinOres timba Creek @ River Rd. 541STC019 14 NA 0 15 0 22 NA 0Solado Creek @ Hwy 33 541STC515 13 NA 0 13 0 19 NA 0Del Puerto Creek @Vineyard 541STC516 9 NA 0 9 0 14 NA 0Grayson Drain 541STC030 11 NA 0 11 0 16 NA 0Ingram Creek @River Rd. 541STC040 13 NA 0 13 0 19 NA 0Hospital Creek @River Rd. 541STC042 7 NA 0 7 0 10 NA 0
Total West Side Basin Count 67 NA 0 68 0 100 NA 0Northeast BasinCosumnes River @ Twin Cities Rd. 531SAC001 8 NA 0 8 0 15 NA 0Mokelumne River @New Hope Rd. 544SAC002 14 0 0 14 0 21 0 0Pixley Slough @ Davis Rd 531SJC507 13 NA 0 13 0 17 NA 1Bear Creek @ Thorton Road (J8) 544SJC508 11 0 0 11 0 18 0 2Bear Creek @Lower Sacramento Rd. 531SJC515 3 0 0 3 0 3 0 0
Total Northeast Basin Count 49 0 0 49 0 74 0 3Delta Basin New Jerusalem Drain 544SJC001 14 0 0 14 0 21 1 0 Tom Payne Slough @Paradise Rd. 544SJC505 14 0 0 14 0 21 0 0Old River @Tracy Blvd 544SJC506 14 0 0 14 0 21 0 0Mountain House Creek 544SJC509 7 0 0 7 0 14 0 0
Total Delta Basin Count 49 0 0 49 0 77 1 0
Total Program Count 483 0 0 484 0 727 1 10NA= Not Applicable/Not a designated Benificial Use
Dissolved Arsenic (ug/L)
Dissolved Copper (ug/L)
Appendix P: Exceedance/elevated levels Summary continued… Dissolved
Lead Sample Count
Dissolved Lead
(ug/L)
Dissolved Nickel
Sample Count
Dissolved Nickel (ug/L)
Dissolved Zinc
Sample Count
Goal Goal Basin Plan Goal
Aquatic Life Aquatic Life
Sacramento-San Joaquin
Delta Aquatic Life
Location Site
California Toxics rule
(USEPA) (calc)
California Toxics rule
(USEPA) (calc)Basin Plan (100ug/L)
California Toxics rule
(USEPA) (calc)
Main StemSJR @Sack Dam 541MAD007 21 0 21 0 21 NA 0SJR @ Lander 541MER522 27 0 27 0 27 NA 0SJR @ Fremont Ford 541MER538 26 0 26 0 25 NA 0SJR @ Hills Ferry 541STC512 20 0 20 0 19 NA 0SJR @ Crows 535STC504 26 0 26 0 25 NA 0SJR @ Patterson 541STC507 26 0 26 0 25 NA 0SJR @ Maze 541STC510 25 0 25 0 24 NA 0SJR @ Airport Way/Vernalis 541SJC501 28 0 28 0 27 NA 0
Total Main Stem Count 199 0 199 0 193 NA 0Southeast Bas in Deep Slough Green House Rd 535MER577 21 0 21 0 21 NA 0Santa Rita Slough at Highway 152 541MER015 5 0 5 0 5 NA 0 Bear Creek Bert Crane Rd 535MER007 22 0 22 0 22 NA 0
Total Southeast Basin Count 48 0 48 0 48 NA 0Grassland BasinSalt Slough @Lander/Hwy 165 541MER531 22 0 22 0 22 NA 0
Mud Slough (n) (upstream) @ San Luis Drain 541MER536 26 0 26 0 25 NA 0Discharge from SLD 541MER535 24 0 24 0 23 NA 0Mud Slough (n) (downstream) @ San Luis Drain 541MER542 26 0 26 0 25 NA 0
Total Grassland Basin Count 98 0 98 0 95 NA 0Eastside BasinTurner Slough at 4th Avenue 535MER576 19 0 19 0 19 NA 0Merced River Hatf ield Park (River Road) 541MER546 20 0 20 0 19 NA 0Harding Drain discharge @ San Joaquin River (TID5) 535STC501 22 0 22 0 21 NA 0French Camp Slough @ Airport 531SJC504 20 0 20 0 20 NA 0Lone Tree Creek @ Austin Rd 531SJC503 21 0 21 0 20 NA 0 Tuolumne River @ Shiloh 535STC513 23 0 23 0 22 NA 0 Stanislaus River @Caswell 535STC514 20 0 20 0 19 NA 0
Total Eastside Basin Count 145 0 145 0 140 NA 0West Side BasinOres timba Creek @ River Rd. 541STC019 23 0 23 0 22 NA 0Solado Creek @ Hwy 33 541STC515 20 0 20 0 19 NA 0Del Puerto Creek @Vineyard 541STC516 15 0 15 0 15 NA 0Grayson Drain 541STC030 17 0 17 0 17 NA 0Ingram Creek @River Rd. 541STC040 20 0 20 0 19 NA 0Hospital Creek @River Rd. 541STC042 11 0 11 0 11 NA 0
Total West Side Basin Count 106 0 106 0 103 NA 0Northeast BasinCosumnes River @ Twin Cities Rd. 531SAC001 15 0 15 0 15 NA 0Mokelumne River @New Hope Rd. 544SAC002 21 0 21 0 21 0 0Pixley Slough @ Davis Rd 531SJC507 17 0 17 0 17 NA 0Bear Creek @ Thorton Road (J8) 544SJC508 18 0 18 0 18 0 0Bear Creek @Lower Sacramento Rd. 531SJC515 3 0 3 0 3 0 0
Total Northeast Basin Count 74 0 74 0 74 0 0Delta Basin New Jerusalem Drain 544SJC001 21 0 21 0 20 0 0 Tom Payne Slough @Paradise Rd. 544SJC505 21 0 21 0 21 0 0Old River @Tracy Blvd 544SJC506 21 0 21 0 21 0 0Mountain House Creek 544SJC509 14 0 14 0 14 0 0
Total Delta Basin Count 77 0 77 0 76 0 0
Total Program Count 747 0 747 0 729 0 0NA= Not Applicable/Not a designated Benificial Use
Dissolved Zinc (ug/L)
Appendix P: Exceedance/elevated levels Summary continued… Chloride Sample Counts
Sulfate Sample Counts
Sulfate (mg/L)
TDS Sample Counts
Basin Plan (ref) Goal Goal
Basin Plan (ref)
Basin Plan (ref) Goal
Mun Aquatic LifeIrrig. Water
Supply Mun MunIrrig. Water
Supply
Location Site
Basin Plan (ref) (MUN) Cal Primary MCL (600
mg/L)
USEPA National
Ambient W Q Criteria / 1-hour average (860 mg/L)
Water Quality for Agriculture (Ayers & Westcot) (106mg/L)
Basin Plan (ref) (MUN)
Cal Secondary
MCL (600mg/L)
Basin Plan (ref) (MUN)
Cal Secondary MCL (1500
mg/L)
Water Quality for Agriculture (Ayers & Westcot) (450mg/L)
Main StemSJR @Sack Dam 541MAD007 26 0 0 6 26 0 17 0 2SJR @ Lander 541MER522 20 0 0 20 20 0 16 0 16SJR @ Fremont Ford 541MER538 26 0 0 26 27 0 21 0 21SJR @ Hills Ferry 541STC512 25 0 0 25 24 0 15 2 14SJR @ Crows 535STC504 26 0 0 23 29 0 24 0 21SJR @ Patterson 541STC507 17 0 0 16 19 0 15 0 13SJR @ Maze 541STC510 16 0 0 10 18 0 14 0 11SJR @ Airport Way/Vernalis 541SJC501 27 0 0 8 30 0 25 0 9
Total Main Stem Count 183 0 0 134 193 0 147 2 107Southeast Basin Deep Slough Green House Rd 535MER577 25 0 0 0 25 0 17 0 1Santa Rita Slough at Highway 152 541MER015 5 0 0 0 5 0 5 0 2 Bear Creek Bert Crane Rd 535MER007 26 0 0 0 25 0 17 0 0
Total Southeast Basin Count 56 0 0 0 55 0 39 0 3Grassland BasinSalt Slough @Lander/Hwy 165 541MER531 18 0 0 18 19 0 15 0 15Mud Slough (n) (upstream) @ San Luis Drain 541MER536 26 0 0 25 29 3 24 6 22Discharge from SLD 541MER535 18 2 0 18 20 20 89 89 89Mud Slough (n) (downstream) @ San Luis Drain 541MER542 18 0 0 18 20 14 16 10 16
Total Grassland Basin Count 80 2 0 79 88 37 144 105 142Eastside BasinTurner Slough at 4th Avenue 535MER576 23 0 0 4 23 0 15 1 4
Merced River Hatfield Park (River Road) 541MER546 11 0 0 0 10 0 10 0 0Harding Drain discharge @ San Joaquin River (TID5) 535STC501 29 0 0 9 27 0 17 0 11French Camp Slough @ Airport 531SJC504 20 0 0 0 20 0 14 0 1Lone Tree Creek @ Austin Rd 531SJC503 23 0 0 0 22 0 16 0 0 Tuolumne River @ Shiloh 535STC513 18 0 0 0 17 0 11 0 0 Stanislaus River @Caswell 535STC514 11 0 0 0 9 0 9 0 0
Total Eastside Basin Count 135 0 0 13 128 0 92 1 16West Side BasinOrestimba Creek @ River Rd. 541STC019 15 0 0 3 17 0 13 0 4Solado Creek @ Hwy 33 541STC515 26 0 0 12 24 0 15 0 10Del Puerto Creek @Vineyard 541STC516 20 0 0 16 20 0 10 0 8Grayson Drain 541STC030 23 0 0 13 21 0 12 0 7Ingram Creek @River Rd. 541STC040 26 0 0 24 24 0 15 2 14Hospital Creek @River Rd. 541STC042 16 0 0 9 14 0 6 0 5
Total West Side Basin Count 126 0 0 77 120 0 71 2 48Northeast BasinCosumnes River @ Twin Cities Rd. 531SAC001 13 0 0 0 13 0 8 0 0Mokelumne River @New Hope Rd. 544SAC002 16 NA 0 0 16 NA 9 NA 0Pixley Slough @ Davis Rd 531SJC507 20 0 0 0 20 0 10 0 0Bear Creek @ Thorton Road (J8) 544SJC508 17 0 0 0 17 0 12 0 0Bear Creek @Lower Sacramento Rd. 531SJC515 7 0 0 0 7 0 2 0 0
Total Northeast Basin Count 73 0 0 0 73 0 41 0 0Delta Basin New Jerusalem Drain 544SJC001 25 0 0 25 25 1 15 12 15 Tom Payne Slough @Paradise Rd. 544SJC505 25 0 0 24 25 0 15 8 14Old River @Tracy Blvd 544SJC506 25 0 0 15 25 0 15 0 11Mountain House Creek 544SJC509 15 0 0 9 15 0 9 5 5
Total Delta Basin Count 90 0 0 73 90 1 54 25 45
Total Program Count 743 2 0 376 747 38 588 135 361NA= Not Applicable/Not a designated Benificial Use
Chloride (mg/L)TDS
(mg/L)
Appendix P: Exceedance/elevated levels Summary continued… Sodium Sample Counts
Goal Goal Goal
Irrig. Water Supply
Drinking Water
Drinking Water
Location Site
Water Quality for Agriculture (Ayers & Westcot) (69mg/L)
USEPA Drinking Water
Advisory: Taste and
odor threshold (30-
60mg/L)
USEPA Drinking Water
Advisory: Persons on restricted
sodium diet (20mg/L)
Main StemSJR @Sack Dam 541MAD007 23 15 17 23SJR @ Lander 541MER522 17 17 17 17SJR @ Fremont Ford 541MER538 24 24 24 24SJR @ Hills Ferry 541STC512 22 22 22 22SJR @ Crows 535STC504 25 23 23 25SJR @ Patterson 541STC507 15 14 15 15SJR @ Maze 541STC510 14 12 13 14SJR @ Airport Way/Vernalis 541SJC501 26 21 22 26
Total Main Stem Count 166 148 153 166Southeast Basin Deep Slough Green House Rd 535MER577 22 4 7 22Santa Rita Slough at Highway 152 541MER015 5 4 4 5 Bear Creek Bert Crane Rd 535MER007 23 1 1 1
Total Southeast Basin Count 50 9 12 28Grassland BasinSalt Slough @Lander/Hwy 165 541MER531 15 15 15 15Mud Slough (n) (upstream) @ San Luis Drain 541MER536 25 25 25 25Discharge from SLD 541MER535 16 16 16 16Mud Slough (n) (downstream) @ San Luis Drain 541MER542 16 16 16 16
Total Grassland Basin Count 72 72 72 72Eastside BasinTurner Slough at 4th Avenue 535MER576 20 4 4 11
Merced River Hatfield Park (River Road) 541MER546 12 0 0 2Harding Drain discharge @ San Joaquin River (TID5) 535STC501 25 18 20 25French Camp Slough @ Airport 531SJC504 20 0 0 2Lone Tree Creek @ Austin Rd 531SJC503 24 0 0 2 Tuolumne River @ Shiloh 535STC513 14 0 0 2 Stanislaus River @Caswell 535STC514 12 0 0 0
Total Eastside Basin Count 127 22 24 44West Side BasinOrestimba Creek @ River Rd. 541STC019 13 8 10 13Solado Creek @ Hwy 33 541STC515 23 20 21 23Del Puerto Creek @Vineyard 541STC516 17 15 17 17Grayson Drain 541STC030 20 17 18 20Ingram Creek @River Rd. 541STC040 23 23 23 23Hospital Creek @River Rd. 541STC042 13 12 12 13
Total West Side Basin Count 109 95 101 109Northeast BasinCosumnes River @ Twin Cities Rd. 531SAC001 9 0 0 0Mokelumne River @New Hope Rd. 544SAC002 12 0 NA NAPixley Slough @ Davis Rd 531SJC507 16 0 0 0Bear Creek @ Thorton Road (J8) 544SJC508 17 0 0 0Bear Creek @Lower Sacramento Rd. 531SJC515 3 0 0 0
Total Northeast Basin Count 57 0 0 0Delta Basin New Jerusalem Drain 544SJC001 21 21 21 21 Tom Payne Slough @Paradise Rd. 544SJC505 21 21 21 21Old River @Tracy Blvd 544SJC506 21 18 19 20Mountain House Creek 544SJC509 13 9 9 13
Total Delta Basin Count 76 69 70 75
Total Program Count 657 415 432 494NA= Not Applicable/Not a designated Benificial Use
Sodium (mg/L)
APPENDIX Q
WATER QUALITY OBJECTIVES/GOALS AND RELATED BENEFICIAL USE TABLES (Q1-Q3)
Appendix Q1: Basin Plan Objectives for the San Joaquin Basin Water Quality Objectives and Targets used to analyze San Joaquin River SWAMP data
Arsenic (Dissolved)
all
Critical Year10
Copper (Dissolved)
all
San Joaquin River between Turner Cut and Stockton. Sept 1- Nov 30All other2 Delta waters, excluding bodies of water constructed for special purposes and from which fish have been excluded or where the fishery is not important as a beneficial use.
all
Cold/Spawning: Cosumnes, Mokelumne, Calaveras, Stanislaus from Goodwin Dam to SJR, Tuolumne from New Don Pedro Dam to SJR, Friant Dam to Mendota Pool, McSWAIN reservoir to SJR, Spawning3: Mendota dam to Vernalis, Mud Slough North, Salt Slough.
all
Merced River from Cressy to New Exchequer Dam allTuolumne River from Waterford to La Grange Oct 15 - Jun 15
Apr 1- Aug 31Sep 1- Mar 31
pH5 all
Temperature5
See Resolution R5-2005-0119
Central Delta all
other Delta waters all
0-5 NTU no >1 NTU5-50 NTU no >20%
50-100 NTU no >10 NTU
>100 NTU no >10%<1 NTU no >5 NTU
1-5 NTU no >5 NTU
>5 NTU General turbidity objectives
Zinc (Dissolved)
all
San Joaquin River at Airport Way Bridge, Vernalis; Old River at Tracy Road Bridge11
8.0 mg/L
all
all
6.5 - 8.5
10 µg/L50 µg/L
Outside Delta (legal
boundaries)4
Electrical Conductivity
50 NTU
Dissolved Oxygen
Deer Creek, source to Cosumnes River. The following applies to daily maximum turbidity. For daily average turbidity see Resolution R5-2002-
0127. (ephemeral water body)
Delta waters6:
except for periods of
storm runoff
Turbidity
In fresh waters with designated COLD or WARM beneficial uses.San Joaquin River, mouth of the Merced River to Vernalis
Salt Slough, Mud Slough (north), San Joaquin River from Sack Dam to the mouth of Merced River
7.0 mg/L
0.1 mg/L
15 µg/LMonthly mean
allSan Joaquin River, mouth of the Merced River to Vernalis
700 µmhos/cm1000 µmhos/cm
Monthly mean
Constituent Location/Comment
Within Delta (legal
boundaries)
5.0 mg/L
Objective
Sacramento-San Joaquin Delta
Dates
SACRAMENTO-SAN JOAQUIN BASIN PLAN OBJECTIVES (CVRWQCB, 1998)
Boron (Total)
Numeric
2.0 mg/L
2.6 mg/L
Mar 15- Sept 15
Sept 16 -Mar 14
Monthly mean 0.8 mg/L
Sacramento-San Joaquin Delta 0.01 mg/L
all
150 NTU
6.0 mg/L
8.0 mg/L
19 µg/L
5 µg/L20 µg/L
4 day Average
Monthly mean
San Joaquin River, mouth of the Merced River to Vernalis
Monthly mean 1.3 mg/L0.01 mg/L
1.0 mg/L
4 day AverageSalt Slough, Mud Slough (north), and the San Joaquin River from Sack
Dam to the mouth of Merced River
Where natural turbidity is between:
all
all
Range 63-81ºF
Sacramento River and San Joaquin River Basins6
Deer Creek, source to Cosumnes River. The following applies to daily maximum temperature. For Monthly average temperature see Resolution
R5-2005-0119 (ephemeral water body).
Where the dilution ratio for discharges is < 20:1 and natural
turbidity is:Where natural
turbidity is:Where the
dilution ratio for discharges is
>20:1 and natural turbidity
is:
5 µg/L
all20 µg/L
Monthly mean 2 µg/L
Molybdenum (Total)
Selenium (Total)
Salt Slough and constructed and re-constructed water supply channels in the Grassland watershed listed in Appendix 40 (See Basin Plan).
Sacramento-San Joaquin Delta
12 µg/L
Appendix Q1: Basin Plan Objectives for the San Joaquin Basin continued…
pH5all
Temperature5all
Toxicity
all
TSS
all
SACRAMENTO-SAN JOAQUIN BASIN PLAN OBJECTIVES*Arsenic (Total)
all
Cadmium (Total)
all
Recommended 250 mg/LUpper 500 mg/L
Short Term 600 mg/LChromium
(Total)all
Copper (Total)
all
Lead (Total)all
Mercury (Total)
all
Nickel (Total)all
Nitrate (as NO3)
all
Nitrate-Nall
Recommended 900 µmhos/cmUpper 1600 µmhos/cm
Short Term 2200 µmhos/cm
Seleniumall
Recommended 250 mg/LUpper 500 mg/L
Short Term 600 mg/LRecommended 500mg/L
Upper 1000mg/LShort Term 1500 mg/L
Turbidityall
Zinc (Total)all
BAY-DELTA AUTHORITY TARGETS (CALFED Water Quality Program plan, 2000)
Temperature7/
8
April 1 - Jun 30 and Sept 1-
Nov 30TOC all
3 Spawning was used in areas designated as WARM and SPAWNING (Applied most limiting)4 Apply most limiting.5 Contains narrative and Numeric. Apply most limiting. 6 Exceptions to the following limit will be considered when a dredging operation can cause an increase in turbidity.7 Daily average temperature in all water-year types.8 Central Valley Regional Water Quality Control Board (CVRWQCB) Water Quality Control Plan
11 Maximum 30-day running average of mean daily, in µmhos/cm
Water Bodies Designated as Municipal and Domestic Supply (MUN)-Drinking Water. California Primary MCL
50 µg/L
Water Bodies Designated as Municipal and Domestic Supply (MUN)-Drinking Water. California Secondary MCL
1000 µg/L
Water Bodies Designated as Municipal and Domestic Supply (MUN)-Drinking Water. California Secondary MCL
5 NTU
Water Bodies Designated as Municipal and Domestic Supply (MUN)-Drinking Water. California Primary MCL
100 µg/L
45 mg/L
Water Bodies Designated as Municipal and Domestic Supply (MUN)-Drinking Water. California Primary MCL
10 mg/L
Water Bodies Designated as Municipal and Domestic Supply (MUN)-Drinking Water. California Primary MCL
2 µg/L
Water Bodies Designated as Municipal and Domestic Supply (MUN)-Drinking Water. California Primary MCL
5 µg/L
Water Bodies Designated as Municipal and Domestic Supply (MUN)-Drinking Water. California Primary MCL
50 µg/L
Water Bodies Designated as Municipal and Domestic Supply (MUN)-Drinking Water. California Secondary MCL
Maximum Contaminant Level Ranges
all
Water Bodies Designated as Municipal and Domestic Supply (MUN)-Drinking Water. California Primary MCL
Electrical Conductivity
Water Bodies Designated as Municipal and Domestic Supply (MUN)-Drinking Water. California Secondary MCL
all Maximum Contaminant Level Ranges
SulfateWater Bodies Designated as Municipal and Domestic Supply (MUN)-
Drinking Water. California Secondary MCL
San Joaquin River at Vernalis <68 ºF
TDSWater Bodies Designated as Municipal and Domestic Supply (MUN)-
Drinking Water. California Secondary MCL all Maximum
Contaminant Level Ranges
Water Bodies Designated as Municipal and Domestic Supply (MUN)-Drinking Water. California Secondary MCL
5000 µg/L
The suspended sediment load and suspended sediment discharge rate of surface waters shall not be altered in such a manner as to cause nuisance
or adversely affect beneficial uses.
Sacramento River and San Joaquin River Basins
Sacramento River and San Joaquin River Basins
Changes in normal ambient pH levels shall not exceed 0.5 in fresh waters with designated COLD
or WARM beneficial uses.
Sacramento River and San Joaquin River BasinsNarrative
At no time or place shall the temperature of intrastate waters be increased more than 5 ºF
above natural receiving water temperature.
Location/Comment Dates Objective
2 Refers to the above cell and the following: Sacramento river (below the I Street Bridge) and in all Delta waters west of the Antioch Bridge.
All waters shall be maintained free of toxic substances in concentrations that produce
detrimental physiological responses in human, plant, animal, or aquatic life.
Sacramento River and San Joaquin River Basins
3.0 mg/LSource water quality for the Delta
50 µg/L
all Maximum Contaminant Level Ranges
Water Bodies Designated as Municipal and Domestic Supply (MUN)-Drinking Water. California Primary MCL
15 µg/L
10 See Table IV-3 in Basin Plan
Water Bodies Designated as Municipal and Domestic Supply (MUN)-Drinking Water. California Primary MCL
*Title 22 of the California code of regulations, which are incorporated by reference into the Sacramento-San Joaquin Basin Plan Objectives: Table 64431-A (Inorganic Chemicals), Table 64449-A (Secondary Maximum contaminant Levels-consumer Acceptance Limits) and Table 64449-B (Secondary Maximum Contaminant Levels-Ranges). Lead is stated in Article 19, Section 64468.1 and also in the Basin plan (III-3). Use the following objectives unless otherwise stated above.
Chloride
Constituent
Appendix Q2: Water Quality Goals for the San Joaquin Basin
UnitsDrinking
WaterAquatic
LifeIrrig. Water
Supply Rec. Use
24.1u1
36.1u2
Arsenic (dissolved) µg/L 340f
0.004m
10t
Boron (total) mg/L 1a 0.7e
Cadmium (dissolved) µg/L 1.6r
Cadmium (total) µg/L 0.07m 1.6r 10 e
Chloride mg/L 860j 106e
Copper (dissolved) µg/L 5.7h
1300g
170m
235 v
298 w
409 x
575 y
Electrical Conductivity µmhos/cm 700e
30-60 c
20 d
Lead (dissolved) µg/L 23.5l
Lead (total) µg/L 2m 25.4l 5000e
0.05g
1.2m
Molybdenum µg/L 10e 35q
Nickel (dissolved) µg/L 215.7n
610g
12m 216.1n 200e
1.4 j
SJR-BENEFICIAL USE(S)
Sodium mg/L 69 e
Indicator(s)Ammonia Nitrogen (NH3-N) mg N/L
200eCopper (total) µg/L 5.9h
Nickel (total)
Mercury (total) µg/L
µg/L
E. coli MPN/100mL
Arsenic (total) µg/L 100e
Appendix Q2: Water Quality Goals for the San Joaquin Basin continued…
UnitsDrinking
WaterAquatic
LifeIrrig. Water
Supply Rec. UseNitrate-nitrogen (NO3-N) mg/L 10m
Selenium µg/L 20b 20e 35q
Total Dissolved Solids mg/L 450e
Zinc (total) µg/L 55.1o 2000e 2100q
Zinc (dissolved) µg/L 53.9o
a California DHS Action Level for drinking waterb National Toxics Rule (USEPA) / 1-hour average (total)c Taste and odor threshold (USEPA Drinking Water Advisory)d USEPA Drinking Water Advisory for persons on restricted sodium diet eWater Quality for Agriculture (Ayers & Westcot)f California Toxics Rule (USEPA)/ 1-hour averageg California Toxics Rule (USEPA) for sources of drinking water j USEPA National Ambient W Q Criteria / 1-hour average
m California Public Health Goal for Drinking Water
Indicator(s)
SJR-BENEFICIAL USE(S)
Maximum concentation (1-hour Average,dissolved) =(e(0.9422*LN(hardness)-1.700))*(0.960)
Maximum concentration (1-hour Average, total recoverable) =(e(1.273*LN(hardness)-1.460))
Maximum concentration (1-hour Average, dissolved) =(e(1.273*LN(hardness)-1.460))*(1.46203-(LN(hardness)*0.145712))
h California Toxics Rule (USEPA): The concluding concentration was determined by using a 40 mg/L hardness. Where deviations from 40 mg/L of water hardness occur, the goals, in mg/L, shall be determined using the following formulas: (As hardness increases copper increases)
l California Toxics Rule (USEPA): The concluding concentration was determined by using a 40 mg/L hardness. Where deviations from 40 mg/L of water hardness occur, the goals, in mg/L, shall be determined using the following formulas: (As hardness increases lead increases)
Maximum concentration(1-hour Average,total recoverable) =(e(0.9422*LN(hardness)-1.700))
Appendix Q2: Water Quality Goals for the San Joaquin Basin continued…
t USEPA P
x USEPAC.L.)
Maximum concentration (1-hour Average, total recoverable)=(e(0.8473*LN(hardness)+0.884))
Maximum concentration(1-hour Average, total recoverable)=e(0.8460*LN(hardness)+2.255)
y USEPA 95% C.L.)
q USEPA Irelative so
r Californdeviationshardness i
v USEPA
w USEPAC.L.)
u1&2 USWhere devmore acidic to
o California Toxics Rule (USEPA): The concluding concentration was determined by using a 40 mg/L hardness. Where deviations from 40 mg/L of water hardness occur, the goals, in mg/L, shall be determined using the following formulas: (As hardness increases zinc increases)
Maximum concentration(1-hour Average, dissolved)=e(0.8460*LN(hardness)+2.255))*(0.998)
n California Toxics Rule (USEPA): The concluding concentration was determined by using a 40 mg/L hardness. Where deviations from 40 mg/L of water hardness occur, the goals, in mg/L, shall be determined using the following formulas: (As hardness increases nickel increases)
rimary MCL
Criteria Maximum concentration 1-hour Average (mg N/L):
Salmonids
Guideline - Single Sample Maximum Allowable Density: lightly used full body contact recreation (upper 90%
2- Absent:
Maximum concentration(1-hour Average, dissolved)=(e(0.8473*LN(hardness)+0.884))*(0.978)
Guideline - Single Sample Maximum Allowable Density: infrequently used full body contact recreation (upper
Maximum concentration (1 hour Average, total recoverable) =(exp(1.128*LN(hardness)-3.6867))
Maximum concentration (1-hour Average, dissolved) =(exp(1.128*LN(hardness)-3.6867))*(1.136672-(LN(hardness)*0.041838))
RIS Reference Dose (Assumes 70 kg body weight, 2 liters per day drinking water consumption, and 20 percent urce contrubution. An additional undertainty factor of 10 is used for Class C carcinogens.)
ia Toxics Rule (USEPA): The concluding concentration was determined by using a 40 mg/L hardness. Where from 40 mg/L of water hardness occur, the goals, in mg/L, shall be determined using the following formulas: (As ncreases cadmium increases)
Guideline - Single Sample Maximum Allowable Density: designated Beach Area (upper 75% C.L.)
Guideline - Single Sample Maximum Allowable Density: moderate full body contact recreation (upper 82%
EPA National Ambient Water Quality Criteria: the concluding concentration was determined by using a pH of 7. iations from pH of 7 occur, the goal, in mg/L, shall be determined using the following formulas: (As pH becomes
tal ammonia Nitrogen increases)
1- Present:
CMC =
0.2751+107.204−pH +
39.01+10pH−7.204
CMC =
0.4111+107.204−pH +
58.41+10pH−7.204
Appendix Q3: Site Specific Representations and Beneficial Use(s) By Sub-Areas (All identified uses are being evaluated whether or not designated in current Basin plan)
Process IND POW REC-2 WARM COLD
Mun
icip
al a
nd D
omes
tic
Supp
ly
Irri
gatio
n
Stoc
k W
ater
ing
Proc
ess
Serv
ice
Supp
ly
Pow
er
Con
tact
Can
oein
g an
d R
aftin
g
Oth
er N
onco
ntac
t
War
m
Col
d
War
m
Col
d
War
m
Col
d
Wild
life
Hab
itat
SJR @Sack Dam541MAD007
P E E E E E E E E E E P E D
SJR @ Lander541MER522
P E E E E E E E E E E P E D
SJR @ Fremont Ford541MER538
P E E E E E E E E E E P E D
SJR @ Hills Ferry541STC512
P E E E E E E E E E E P E D
SJR @ Crows535STC504
P E E E E E E E E E E E D
SJR @ Patterson541STC507
P E E E E E E E E E E E D
SJR @ Maze541STC510
P E E E E E E E E E E E D
SJR @ Airport Way/Vernalis541SJC501
P E E E E E E E E E E E D
North East Basin
Cosumnes River @ Twin Cities Rd.531SAC001
E E E E E E E E E E E E E D
Mokelumne River @ New Hope Rd.544SAC002
E E E E E E E E E E E E D
Pixley Slough @Davis Rd. *544SJC507
E E E E E E E E E E E E E T
Bear Creek @Thornton Rd (J8) *544SJC508
E E E E E E E E E E E E E T
Bear Creek @Lower Sacramento Rd. *531SJC515
E E E E E E E E E E E E E T
DRAINAGE BASIN INFLOWS TO SJR
WILD
Des
igna
ted
(D) o
r T
ribu
tary
(T)AGR REC-1 MIGR SPWN
RECREATION FRESHWATER MIGRATION
MAIN STEM SAN JOAQUIN RIVER
SPAWNING
SITE SPECIFIC MONITORING BY PROGRAM AND SUB-AREA BASIN Site ID A
pplic
able
Bas
in P
lan
Obj
ectiv
e Su
rfac
e W
ater
Bod
y D
esig
natio
n MUNAGRICULTURE INDUSTRY
Appendix Q3: Site Specific Representations and Beneficial Use(s) By Sub-Areas continued…
Process IND POW REC-2 WARM COLD
Mun
icip
al a
nd D
omes
tic
Supp
ly
Irri
gatio
n
Stoc
k W
ater
ing
Proc
ess
Serv
ice
Supp
ly
Pow
er
Con
tact
Can
oein
g an
d R
aftin
g
Oth
er N
onco
ntac
t
War
m
Col
d
War
m
Col
d
War
m
Col
d
Wild
life
Hab
itat
Eastside Basin
Lone Tree Creek *531SJC503
E E E E E E E E E E E E E T
French Camp Slough @ Airport *531SJC504
E E E E E E E E E E E E E T
Merced River Hatfield Park (River Road)541MER546
E E E E E E E E E E E E E E E D
Turner Slough @ 4th Avenue *535MER576
P E E E E E E E E E E P E T
TID 5 (Harding Drain)*535STC501
P E E E E E E E E E E E T
Tuolumne River @ Shiloh535STC513
P E E E E E E E E E E E E D
Stanislaus River @Caswell535STC514
P E E E E E E E E E E E E E E D
Southeast Basin
Lone Willow Slough *545MAD006
P E E E E E E E E E E P E T
Bear Creek @ Bert Crane Rd. *535MER007
P E E E E E E E E E E P E T
Deep Slough Green House Rd. *535MER577
P E E E E E E E E E E P E T
Grassland Basin
Discharge from San Luis Drain (SLD)*541MER535
L E E E E E E T
Mud Slough (upstream of SLD)541MER536
L E E E E E E D
Mud Slough (Downstream of SLD)541MER542
L E E E E E E D
Salt Slough @Lander/Hwy 165 541MER531
E E E E E E E D
AGR REC-1 MIGR SPWNMIGRATION SPAWNING
WILD
Des
igna
ted
(D) o
r T
ribu
tary
(T)
AGRICULTURE INDUSTRY RECREATION FRESHWATER
SITE SPECIFIC MONITORING BY PROGRAM AND SUB-AREA BASIN Site ID A
pplic
able
Bas
in P
lan
Obj
ectiv
e Su
rfac
e W
ater
Bod
y D
esig
natio
n MUN
Appendix Q3: Site Specific Representations and Beneficial Use(s) By Sub-Areas continued…
Process IND POW REC-2 WARM COLD
Mun
icip
al a
nd D
omes
tic
Supp
ly
Irri
gatio
n
Stoc
k W
ater
ing
Proc
ess
Serv
ice
Supp
ly
Pow
er
Con
tact
Can
oein
g an
d R
aftin
g
Oth
er N
onco
ntac
t
War
m
Col
d
War
m
Col
d
War
m
Col
d
Wild
life
Hab
itat
West Side Basin
Orestimba Creek @ River Rd. *541STC019
P E E E E E E E E E E E T
Solado Creek @ Hwy 33 *541STC515
P E E E E E E E E E E E T
Del Puerto Creek @Vineyard *541STC516
P E E E E E E E E E E E T
Grayson Drain *541STC030
P E E E E E E E E E E E T
Ingram Creek @River Rd. *541STC040
P E E E E E E E E E E E T
Hospital Creek @River Rd. *541STC042
P E E E E E E E E E E E T
Delta Basin
New Jerusalem Drain*544SJC501
E E E E E E E E E E E E T
Tom Payne Slough @Paradise Rd.544SJC505
E E E E E E E E E E E E E D
Old River @Tracy Blvd544SJC506
E E E E E E E E E E E E E D
Mt. House Creek @ Mt. House Parkway S544SJC509
E E E E E E E E E E E E E T
* = Beneficial uses not specifically designated, therefore current listing based on downstream beneficial useE = Exisiting beneficial usesP = Potential beneficial usesL=Existing Limited Beneficial Use
AGR REC-1 MIGR SPWNMIGRATION SPAWNING
WILD
Des
igna
ted
(D) o
r Tr
ibut
ary
(T)
AGRICULTURE INDUSTRY RECREATION FRESHWATER
SITE SPECIFIC MONITORING BY PROGRAM AND SUB-AREA BASIN Site ID A
pplic
able
Bas
in P
lan
Obj
ectiv
e Su
rfac
e W
ater
Bod
y D
esig
natio
n MUN
APPENDIX R
GRAPHICAL SUMMARY OF RESULTS
APPENDIX R: GRAPHICAL SUMMARY OF RESULTS R1: San Joaquin River Main Stem………………………………….……….1-53 R2: Northeast Basin………………………………………………………54-103 R3: Eastside Basin………………………………………………………104-153 R4: Southeast Basin……………………………………………….…….154-203 R5: Grassland Basin……………………………………………………..204-255 R6: Westside Basin…………………………………………..………….256-305 R7: South Delta Basin…………………………………………………...306-356
San Joaquin River Main Stem Temperature WY01-WY05
5
10
15
20
25
30
35
Oct
-00
Jan-
01
Apr
-01
Jul-0
1
Oct
-01
Jan-
02
Apr
-02
Jul-0
2
Oct
-02
Jan-
03
Apr
-03
Jul-0
3
Oct
-03
Jan-
04
Apr
-04
Jul-0
4
Oct
-04
Jan-
05
Apr
-05
Jul-0
5
Sample Date
Tem
pera
ture
(ºC
)
SJR @Sack Dam
SJR @ Lander
SJR @ Fremont Ford
SJR @ Hills Ferry
SJR @ Crows
R1-1
1
San Joaquin River Main StemTemperature WY01- WY05
0
5
10
15
20
25
30
35
SJR @SackDam
SJR @ Lander SJR @Fremont Ford
SJR @ HillsFerry
SJR @ Crows SJR @Patterson
SJR @ Maze SJR @ AirportWay/Vernalis
Tem
pera
ture
(ºC
)
Median
R1-2
2
San Joaquin River Main Stem Specific Conductivity WY01-WY05
0
500
1000
1500
2000
2500
3000
3500
4000O
ct-0
0
Jan-
01
Apr
-01
Jul-0
1
Oct
-01
Jan-
02
Apr
-02
Jul-0
2
Oct
-02
Jan-
03
Apr
-03
Jul-0
3
Oct
-03
Jan-
04
Apr
-04
Jul-0
4
Oct
-04
Jan-
05
Apr
-05
Jul-0
5
Oct
-05
Sample Date
SC (μ
mho
s/cm
)
SJR @Sack Dam SJR @ Lander SJR @ Fremont FordSJR @ Hills Ferry SJR @ Crows SJR @ Patterson SJR @ Maze SJR @ Airport Way/Vernalis Basin Plan Objective (Apr 1-Aug 31, 700 μmhos/cm; Sep 1-Mar 31,1000 μmhos/cm)
R1-3
3
San Joaquin River Main StemSpecific Conductivity WY01- WY05
0
500
1000
1500
2000
2500
3000
3500
SJR @SackDam
SJR @ Lander SJR @Fremont Ford
SJR @ HillsFerry
SJR @ Crows SJR @Patterson
SJR @ Maze SJR @ AirportWay/Vernalis
Spec
ific
Con
duct
ivity
(μm
hos/
cm)
Median
R1-4
4
San Joaquin River Main Stem pH WY01-WY05
6.0
6.5
7.0
7.5
8.0
8.5
9.0
9.5
Oct
-00
Jan-
01
Apr
-01
Jul-0
1
Oct
-01
Jan-
02
Apr
-02
Jul-0
2
Oct
-02
Jan-
03
Apr
-03
Jul-0
3
Oct
-03
Jan-
04
Apr
-04
Jul-0
4
Oct
-04
Jan-
05
Apr
-05
Jul-0
5
Sample Date
pH
SJR @Sack Dam SJR @ Lander SJR @ Fremont FordSJR @ Hills Ferry SJR @ Crows SJR @ Patterson SJR @ Maze SJR @ Airport Way/Vernalis Basin Plan Objective (6.5-8.5)
R1-5
5
San Joaquin River Main StempH WY01- WY05
6
6.5
7
7.5
8
8.5
9
9.5
SJR @SackDam
SJR @ Lander SJR @Fremont Ford
SJR @ HillsFerry
SJR @ Crows SJR @Patterson
SJR @ Maze SJR @ AirportWay/Vernalis
pH
MedianBasin Plan Objective (6.5-8.5)
R1-6
6
San Joaquin River Main Stem Dissolved Oxygen WY01-WY05
0
5
10
15
20
25
Apr
-01
Jul-0
1
Oct
-01
Jan-
02
Apr
-02
Jul-0
2
Oct
-02
Jan-
03
Apr
-03
Jul-0
3
Oct
-03
Jan-
04
Apr
-04
Jul-0
4
Oct
-04
Jan-
05
Apr
-05
Jul-0
5
Sample Date
DO
(mg/
L)
SJR @Sack Dam SJR @ Lander SJR @ Fremont FordSJR @ Hills Ferry SJR @ Crows SJR @ Patterson SJR @ Maze SJR @ Airport Way/Vernalis Basin Plan Objective (7.0 mg/L)
R1-7
7
San Joaquin River Main StemDissolved Oxygen WY01- WY05
0
5
10
15
20
25
SJR @SackDam
SJR @ Lander SJR @Fremont Ford
SJR @ HillsFerry
SJR @ Crows SJR @Patterson
SJR @ Maze SJR @ AirportWay/Vernalis
Dis
solv
ed O
xyge
n (m
g/L)
MedianBasin Plan Objective (7.0 mg/L)
R1-8
8
San Joaquin River Main Stem Turbidity WY02-WY04
0
50
100
150
200
250
300
Apr
-02
Jul-0
2
Oct
-02
Jan-
03
Apr
-03
Jul-0
3
Oct
-03
Jan-
04
Sample Date
Turb
idity
(ntu
)
SJR @Sack Dam SJR @ Lander SJR @ Fremont Ford SJR @ Hills Ferry SJR @ Crows SJR @ Patterson SJR @ Maze SJR @ Airport Way/Vernalis
R1-9
9
San Joaquin River Main StemTurbidity WY02- WY04
0
50
100
150
200
250
300
SJR @SackDam
SJR @ Lander SJR @Fremont Ford
SJR @ HillsFerry
SJR @ Crows SJR @Patterson
SJR @ Maze SJR @ AirportWay/Vernalis
Turb
idity
(ntu
)
Median
R1-10
10
San Joaquin River Main Stem Total Suspended Solids WY01-WY05
0
20
40
60
80
100
120
140
160
180
200
Oct
-00
Jan-
01
Apr
-01
Jul-0
1
Oct
-01
Jan-
02
Apr
-02
Jul-0
2
Oct
-02
Jan-
03
Apr
-03
Jul-0
3
Oct
-03
Jan-
04
Apr
-04
Jul-0
4
Oct
-04
Jan-
05
Apr
-05
Jul-0
5
Sample Date
TSS
(mg/
L)
SJR @Sack Dam SJR @ Lander SJR @ Fremont Ford SJR @ Hills Ferry SJR @ Crows SJR @ Patterson SJR @ Maze SJR @ Airport Way/Vernalis
R1-11
11
San Joaquin River Main StemTotal Suspended Solids WY01- WY05
0
20
40
60
80
100
120
140
160
180
200
SJR @SackDam
SJR @ Lander SJR @Fremont Ford
SJR @ HillsFerry
SJR @ Crows SJR @Patterson
SJR @ Maze SJR @ AirportWay/Vernalis
Tota
l Sus
pend
ed S
olid
s (m
g/L)
Median
R1-12
12
San Joaquin River Main Stem Total Organic Carbon WY01-WY05
0
5
10
15
20
25
30
Oct
-00
Jan-
01
Apr
-01
Jul-0
1
Oct
-01
Jan-
02
Apr
-02
Jul-0
2
Oct
-02
Jan-
03
Apr
-03
Jul-0
3
Oct
-03
Jan-
04
Apr
-04
Jul-0
4
Oct
-04
Jan-
05
Apr
-05
Jul-0
5
Sample Date
TOC
(mg/
L)
SJR @Sack Dam SJR @ Lander SJR @ Fremont FordSJR @ Hills Ferry SJR @ Crows SJR @ Patterson SJR @ Maze SJR @ Airport Way/Vernalis Bay-Delta Authority Target (3 mg/L)
R1-13
13
San Joaquin River Main StemTotal Organic Carbon WY01- WY05
0
5
10
15
20
25
30
SJR @SackDam
SJR @ Lander SJR @Fremont Ford
SJR @ HillsFerry
SJR @ Crows SJR @Patterson
SJR @ Maze SJR @ AirportWay/Vernalis
Tota
l Org
anic
Car
bon
(mg/
L)
MedianBay-Delta Authority Target (3 mg/L)
R1-14
14
San Joaquin River Main Stem Total Coliform WY02-WY05
0
500
1000
1500
2000
2500
Jul-0
2
Oct
-02
Jan-
03
Apr
-03
Jul-0
3
Oct
-03
Jan-
04
Apr
-04
Jul-0
4
Oct
-04
Jan-
05
Apr
-05
Jul-0
5
Sample Date
Tota
l Col
iform
(MPN
/100
ml)
SJR @Sack Dam SJR @ Lander SJR @ Fremont Ford SJR @ Hills Ferry SJR @ Crows SJR @ Patterson SJR @ Maze SJR @ Airport Way/Vernalis
R1-15
15
San Joaquin River Main StemTotal Coliform WY02- WY05
0
500
1000
1500
2000
2500
3000
SJR @SackDam
SJR @ Lander SJR @Fremont Ford
SJR @ HillsFerry
SJR @ Crows SJR @Patterson
SJR @ Maze SJR @ AirportWay/Vernalis
Tota
l Col
iform
(MPN
/100
ml)
Median
R1-16
16
San Joaquin River Main Stem Escherichia coli WY02-WY05
0
500
1000
1500
2000
2500
Jul-0
2
Oct
-02
Jan-
03
Apr
-03
Jul-0
3
Oct
-03
Jan-
04
Apr
-04
Jul-0
4
Oct
-04
Jan-
05
Apr
-05
Jul-0
5
Sample Date
E. c
oli
(MPN
/100
ml)
SJR @Sack Dam SJR @ Lander SJR @ Fremont Ford SJR @ Hills Ferry SJR @ Crows SJR @ Patterson SJR @ Maze SJR @ Airport Way/Vernalis USEPA Guideline - Designated beach area. (235 MPN/100 mL)
R1-17
17
San Joaquin River Main StemEscherichia coli WY02-WY05
0
500
1000
1500
2000
2500
3000
SJR @SackDam
SJR @ Lander SJR @Fremont Ford
SJR @ HillsFerry
SJR @ Crows SJR @Patterson
SJR @ Maze SJR @ AirportWay/Vernalis
E. c
oli
(MPN
/100
ml)
MedianUSEPA Guideline - Designated beach area. (235 MPN/100 mL)
R1-18
18
San Joaquin River Main Stem Nitrate WY01-WY04
0
5
10
15
20
25
30
35
40
45
50
Oct
-00
Jan-
01
Apr
-01
Jul-0
1
Oct
-01
Jan-
02
Apr
-02
Jul-0
2
Oct
-02
Jan-
03
Apr
-03
Jul-0
3
Oct
-03
Jan-
04
Sample Date
Nitr
ate
(mg/
L)
SJR @Sack Dam SJR @ Lander SJR @ Fremont FordSJR @ Hills Ferry SJR @ Crows SJR @ Patterson SJR @ Maze SJR @ Airport Way/Vernalis California Primary MCL (45mg/L)
R1-19
19
San Joaquin River Main StemNitrate WY01-WY04
0
5
10
15
20
25
30
35
40
45
50
SJR @SackDam
SJR @ Lander SJR @Fremont Ford
SJR @ HillsFerry
SJR @ Crows SJR @Patterson
SJR @ Maze SJR @ AirportWay/Vernalis
Nitr
ate
(mg/
L)
MedianCalifornia Primary MCL (45mg/L)
R1-20
20
San Joaquin River Main Stem Nitrate-N WY04-WY05
0
1
2
3
4
5
6
7
8
9
10
Jan-
04
Apr
-04
Jul-0
4
Oct
-04
Jan-
05
Apr
-05
Jul-0
5
Sample Date
Nitr
ate-
N (m
g/L)
SJR @ Fremont Ford SJR @ Crows California Primary MCL (10mg/L)
R1-21
21
San Joaquin River Main Stem Total Kjeldahl Nitrogen WY01-WY05
0.0
0.5
1.0
1.5
2.0
2.5
3.0
3.5
4.0
Oct
-00
Jan-
01
Apr
-01
Jul-0
1
Oct
-01
Jan-
02
Apr
-02
Jul-0
2
Oct
-02
Jan-
03
Apr
-03
Jul-0
3
Oct
-03
Jan-
04
Apr
-04
Jul-0
4
Oct
-04
Jan-
05
Apr
-05
Jul-0
5
Sample Date
TKN
(mg/
L)
SJR @Sack Dam SJR @ Lander SJR @ Fremont Ford SJR @ Hills Ferry SJR @ Crows SJR @ Patterson SJR @ Maze SJR @ Airport Way/Vernalis
R1-22
22
San Joaquin River Main StemTotal Kjeldahl Nitrogen WY01-WY05
0
0.5
1
1.5
2
2.5
3
3.5
4
4.5
SJR @SackDam
SJR @ Lander SJR @Fremont Ford
SJR @ HillsFerry
SJR @ Crows SJR @Patterson
SJR @ Maze SJR @ AirportWay/Vernalis
TKN
(mg/
L)
Median
R1-23
23
San Joaquin River Main Stem Ammonia-N WY01-WY05
0
0.1
0.2
0.3
0.4
0.5
0.6
Oct
-00
Jan-
01
Apr
-01
Jul-0
1
Oct
-01
Jan-
02
Apr
-02
Jul-0
2
Oct
-02
Jan-
03
Apr
-03
Jul-0
3
Oct
-03
Jan-
04
Apr
-04
Jul-0
4
Oct
-04
Jan-
05
Apr
-05
Jul-0
5
Sample Date
Am
mon
ia-N
(mg/
L)
SJR @ Fremont Ford SJR @ Crows SJR @ Patterson SJR @ Maze SJR @ Airport Way/Vernalis
R1-24
24
San Joaquin River Main StemAmmonia-N WY04-WY05
0
0.1
0.2
0.3
0.4
0.5
0.6
SJR @ Fremont Ford SJR @ Crows SJR @ Patterson SJR @ Maze SJR @ AirportWay/Vernalis
Am
mon
ia-N
(mg/
L)
Median
R1-25
25
San Joaquin River Main Stem Phosphorus WY01-WY05
0
0.1
0.2
0.3
0.4
0.5
0.6
0.7
Oct
-00
Jan-
01
Apr
-01
Jul-0
1
Oct
-01
Jan-
02
Apr
-02
Jul-0
2
Oct
-02
Jan-
03
Apr
-03
Jul-0
3
Oct
-03
Jan-
04
Apr
-04
Jul-0
4
Oct
-04
Jan-
05
Apr
-05
Jul-0
5
Sample Date
Phos
phor
us (m
g/L)
SJR @Sack Dam SJR @ Lander SJR @ Fremont Ford SJR @ Hills Ferry SJR @ Crows SJR @ Patterson SJR @ Maze
R1-26
26
San Joaquin River Main StemPhosphorus WY01-WY05
0
0.1
0.2
0.3
0.4
0.5
0.6
0.7
0.8
SJR @SackDam
SJR @ Lander SJR @Fremont Ford
SJR @ HillsFerry
SJR @ Crows SJR @Patterson
SJR @ Maze SJR @ AirportWay/Vernalis
Phos
phor
us (m
g/L)
Median
R1-27
27
San Joaquin River Main Stem Orthophosphate-P WY01-WY05
0
0.1
0.2
0.3
0.4
0.5
0.6
Oct
-00
Jan-
01
Apr
-01
Jul-0
1
Oct
-01
Jan-
02
Apr
-02
Jul-0
2
Oct
-02
Jan-
03
Apr
-03
Jul-0
3
Oct
-03
Jan-
04
Apr
-04
Jul-0
4
Oct
-04
Jan-
05
Apr
-05
Jul-0
5
Sample Date
Ort
ho-P
(mg/
L)
SJR @Sack Dam SJR @ Lander SJR @ Fremont Ford SJR @ Hills Ferry SJR @ Crows SJR @ Patterson SJR @ Maze SJR @ Airport Way/Vernalis
R1-28
28
San Joaquin River Main StemOrthophosphate-P WY01-WY05
0
0.1
0.2
0.3
0.4
0.5
0.6
SJR @SackDam
SJR @ Lander SJR @Fremont Ford
SJR @ HillsFerry
SJR @ Crows SJR @Patterson
SJR @ Maze SJR @ AirportWay/Vernalis
Ort
hoph
osph
ate-
P (m
g/L)
Median
R1-29
29
San Joaquin River Main Stem Potassium WY01-WY04
0
2
4
6
8
10
12
14
Oct
-00
Jan-
01
Apr
-01
Jul-0
1
Oct
-01
Jan-
02
Apr
-02
Jul-0
2
Oct
-02
Jan-
03
Apr
-03
Jul-0
3
Oct
-03
Jan-
04
Sample Date
Pota
ssiu
m (m
g/L)
SJR @Sack Dam SJR @ Lander SJR @ Fremont Ford SJR @ Hills Ferry SJR @ Crows SJR @ Patterson SJR @ Maze SJR @ Airport Way/Vernalis
R1-30
30
San Joaquin River Main StemPotassium WY01-WY04
0
2
4
6
8
10
12
14
SJR @SackDam
SJR @ Lander SJR @Fremont Ford
SJR @ HillsFerry
SJR @ Crows SJR @Patterson
SJR @ Maze SJR @ AirportWay/Vernalis
Pota
ssiu
m (m
g/L)
Median
R1-31
31
San Joaquin River Main Stem Biochemical Oxygen Demand 5-Day WY01-WY03
0
1
2
3
4
5
6
7
8
9
10
Oct
-00
Jan-
01
Apr
-01
Jul-0
1
Oct
-01
Jan-
02
Apr
-02
Jul-0
2
Oct
-02
Jan-
03
Sample Date
BO
D 5
-Day
(mg/
L)
SJR @Sack Dam SJR @ Lander SJR @ Fremont Ford SJR @ Hills Ferry SJR @ Crows SJR @ Patterson SJR @ Maze SJR @ Airport Way/Vernalis
R1-32
32
San Joaquin River Main StemBiological Oxygen Demand 5-Day WY01-WY03
0
1
2
3
4
5
6
7
8
9
10
SJR @SackDam
SJR @ Lander SJR @Fremont Ford
SJR @ HillsFerry
SJR @ Crows SJR @Patterson
SJR @ Maze SJR @ AirportWay/Vernalis
BO
D- 5
(mg/
L)
Median
R1-33
33
San Joaquin River Main Stem Biochemical Oxygen Demand 10-Day WY01-WY03
0
2
4
6
8
10
12
14
16
18
Oct
-00
Jan-
01
Apr
-01
Jul-0
1
Oct
-01
Jan-
02
Apr
-02
Jul-0
2
Oct
-02
Jan-
03
Sample Date
BO
D 1
0-D
ay (m
g/L)
SJR @Sack Dam SJR @ Lander SJR @ Fremont Ford SJR @ Hills Ferry SJR @ Crows SJR @ Patterson SJR @ Maze SJR @ Airport Way/Vernalis
R1-34
34
San Joaquin River Main StemBiological Oxygen Demand 10-Day WY01-WY03
0
2
4
6
8
10
12
14
16
18
20
SJR @SackDam
SJR @ Lander SJR @Fremont Ford
SJR @ HillsFerry
SJR @ Crows SJR @Patterson
SJR @ Maze SJR @ AirportWay/Vernalis
BO
D- 1
0 (m
g/L)
Median
R1-35
35
San Joaquin River Main Stem Chloride WY01-WY03
0
50
100
150
200
250
300
350
400
450
500
Oct
-00
Jan-
01
Apr
-01
Jul-0
1
Oct
-01
Jan-
02
Apr
-02
Jul-0
2
Oct
-02
Jan-
03
Apr
-03
Sample Date
Chl
orid
e (m
g/L)
SJR @Sack Dam SJR @ Lander SJR @ Fremont Ford SJR @ Hills Ferry SJR @ Crows SJR @ Patterson SJR @ Maze SJR @ Airport Way/Vernalis California Secondary MCL (recommended level) (250 mg/L)
R1-36
36
San Joaquin River Main StemChloride WY01-WY03
0
50
100
150
200
250
300
350
400
450
500
SJR @SackDam
SJR @ Lander SJR @Fremont Ford
SJR @ HillsFerry
SJR @ Crows SJR @Patterson
SJR @ Maze SJR @ AirportWay/Vernalis
Chl
orid
e (m
g/L)
Median
R1-37
37
San Joaquin River Main Stem Sulfate WY01-WY03
0
100
200
300
400
500
600
Oct
-00
Jan-
01
Apr
-01
Jul-0
1
Oct
-01
Jan-
02
Apr
-02
Jul-0
2
Oct
-02
Jan-
03
Apr
-03
Sample Date
Sulfa
te (m
g/L)
SJR @Sack Dam SJR @ Lander SJR @ Fremont Ford SJR @ Hills Ferry SJR @ Crows SJR @ Patterson SJR @ Maze SJR @ Airport Way/Vernalis California Secondary MCL (recommended level) (250 mg/L)
R1-38
38
San Joaquin River Main StemSulfate WY01-WY03
0
100
200
300
400
500
600
SJR @SackDam
SJR @ Lander SJR @Fremont Ford
SJR @ HillsFerry
SJR @ Crows SJR @Patterson
SJR @ Maze SJR @ AirportWay/Vernalis
Sulfa
te (m
g/L)
MedianCalifornia Secondary MCL (recommended level) (250 mg/L)
R1-39
39
San Joaquin River Main Stem Calcium WY01-WY03
0
20
40
60
80
100
120
140
Oct
-00
Jan-
01
Apr
-01
Jul-0
1
Oct
-01
Jan-
02
Apr
-02
Jul-0
2
Oct
-02
Jan-
03
Apr
-03
Sample Date
Cal
cium
(mg/
L)
SJR @Sack Dam SJR @ Lander SJR @ Fremont Ford SJR @ Hills Ferry SJR @ Crows SJR @ Patterson SJR @ Maze SJR @ Airport Way/Vernalis
R1-40
40
San Joaquin River Main StemCalcium WY01-WY03
0
20
40
60
80
100
120
140
SJR @SackDam
SJR @ Lander SJR @Fremont Ford
SJR @ HillsFerry
SJR @ Crows SJR @Patterson
SJR @ Maze SJR @ AirportWay/Vernalis
Cal
cium
(mg/
L)
Median
R1-41
41
San Joaquin River Main Stem Magnesium WY01-WY03
0
10
20
30
40
50
60
70
Oct
-00
Jan-
01
Apr
-01
Jul-0
1
Oct
-01
Jan-
02
Apr
-02
Jul-0
2
Oct
-02
Jan-
03
Apr
-03
Sample Date
Mag
nesi
um (m
g/L)
SJR @Sack Dam SJR @ Lander SJR @ Fremont Ford SJR @ Hills Ferry SJR @ Crows SJR @ Patterson SJR @ Maze SJR @ Airport Way/Vernalis
R1-42
42
San Joaquin River Main StemMagnesium WY01-WY03
0
10
20
30
40
50
60
70
80
SJR @SackDam
SJR @ Lander SJR @Fremont Ford
SJR @ HillsFerry
SJR @ Crows SJR @Patterson
SJR @ Maze SJR @ AirportWay/Vernalis
Mag
nesi
um (m
g/L)
Median
R1-43
43
San Joaquin River Main Stem Total Dissolved Solids WY01-WY03
0
200
400
600
800
1000
1200
1400
1600
1800
Oct
-00
Jan-
01
Apr
-01
Jul-0
1
Oct
-01
Jan-
02
Apr
-02
Jul-0
2
Oct
-02
Sample Date
TDS
(mg/
L)
SJR @Sack Dam SJR @ Lander SJR @ Fremont Ford SJR @ Hills Ferry SJR @ Crows SJR @ Patterson SJR @ Maze California Secondary MCL (recommended level) (500 mg/L)
R1-44
44
San Joaquin River Main StemTotal Dissolved Solids WY01-WY03
0
200
400
600
800
1000
1200
1400
1600
1800
SJR @SackDam
SJR @ Lander SJR @Fremont Ford
SJR @ HillsFerry
SJR @ Crows SJR @Patterson
SJR @ Maze SJR @ AirportWay/Vernalis
TDS
(mg/
L)
Median
R1-45
45
San Joaquin River Main Stem Carbonate WY01-WY03
0
2
4
6
8
10
12
14
Oct
-00
Jan-
01
Apr
-01
Jul-0
1
Oct
-01
Jan-
02
Apr
-02
Jul-0
2
Oct
-02
Jan-
03
Apr
-03
Jul-0
3
Oct
-03
Sample Date
Car
bona
te (m
g/L)
SJR @Sack Dam SJR @ Lander SJR @ Fremont Ford SJR @ Hills Ferry SJR @ Crows SJR @ Patterson SJR @ Maze SJR @ Airport Way/Vernalis
R1-46
46
San Joaquin River Main StemCarbonate WY01-WY03
0
2
4
6
8
10
12
14
SJR @SackDam
SJR @ Lander SJR @Fremont Ford
SJR @ HillsFerry
SJR @ Crows SJR @Patterson
SJR @ Maze SJR @ AirportWay/Vernalis
Car
bona
te (m
g/L)
Median
R1-47
47
San Joaquin River Main Stem Bicarbonate WY01-WY03
50
100
150
200
250
300
Oct
-00
Jan-
01
Apr
-01
Jul-0
1
Oct
-01
Jan-
02
Apr
-02
Jul-0
2
Oct
-02
Sample Date
Bic
arbo
nate
(mg/
L)
SJR @Sack Dam SJR @ Lander SJR @ Fremont Ford SJR @ Hills Ferry SJR @ Crows SJR @ Patterson SJR @ Maze SJR @ Airport Way/Vernalis
R1-48
48
San Joaquin River Main StemBicarbonate WY01-WY03
0
50
100
150
200
250
300
350
SJR @SackDam
SJR @ Lander SJR @Fremont Ford
SJR @ HillsFerry
SJR @ Crows SJR @Patterson
SJR @ Maze SJR @ AirportWay/Vernalis
Bic
arbo
nate
(mg/
L)
Median
R1-49
49
San Joaquin River Main Stem Total Alkalinity WY01-WY03
50
100
150
200
250
300
Oct
-00
Jan-
01
Apr
-01
Jul-0
1
Oct
-01
Jan-
02
Apr
-02
Jul-0
2
Oct
-02
Sample Date
Tota
l Alk
alin
ity (m
g/L)
SJR @Sack Dam SJR @ Lander SJR @ Fremont Ford SJR @ Hills Ferry SJR @ Crows SJR @ Patterson SJR @ Maze SJR @ Airport Way/Vernalis
R1-50
50
San Joaquin River Main StemTotal Alkalinity WY01-WY03
0
50
100
150
200
250
300
SJR @SackDam
SJR @ Lander SJR @Fremont Ford
SJR @ HillsFerry
SJR @ Crows SJR @Patterson
SJR @ Maze SJR @ AirportWay/Vernalis
Tota
l Alk
alin
ity (m
g/L)
Median
R1-51
51
San Joaquin River Main Stem Sodium WY01-WY03
0
50
100
150
200
250
300
350
400
Oct
-00
Jan-
01
Apr
-01
Jul-0
1
Oct
-01
Jan-
02
Apr
-02
Jul-0
2
Oct
-02
Sample Date
Sodi
um (m
g/L)
SJR @Sack Dam SJR @ Lander SJR @ Fremont Ford SJR @ Hills Ferry SJR @ Crows SJR @ Patterson SJR @ Maze SJR @ Airport Way/Vernalis Water Quality for Agriculture(Ayers & Westcot) (69 mg/L)
R1-52
52
San Joaquin River Main StemSodium WY01-WY03
0
50
100
150
200
250
300
350
400
SJR @SackDam
SJR @ Lander SJR @Fremont Ford
SJR @ HillsFerry
SJR @ Crows SJR @Patterson
SJR @ Maze SJR @ AirportWay/Vernalis
Sodi
um (m
g/L)
MedianWater Quality for Agriculture (Ayers & Westcot) (69 mg/L)
R1-53
53
San Joaquin River Northeast Basin Temperature WY01-WY05
0
5
10
15
20
25
30
Oct
-00
Jan-
01
Apr
-01
Jul-0
1
Oct
-01
Jan-
02
Apr
-02
Jul-0
2
Oct
-02
Jan-
03
Apr
-03
Jul-0
3
Oct
-03
Jan-
04
Apr
-04
Jul-0
4
Oct
-04
Jan-
05
Apr
-05
Jul-0
5
Oct
-05
Jan-
06
Sample Date
Tem
pera
ture
(ºC
)
Cosumnes River @ Twin Cities Rd. Mokelumne River @New Hope Rd. Pixley Slough @ Davis RdBear Creek @ Thorton Road (J8)Bear Creek @Lower Sacramento Rd. Bay-Delta Authority Target, SJR @ Vernalis (Apr 1-Jun 30 & Sept 1- Nov 30, 20ºC)
R2-1
54
San Joaquin River Northeast BasinTemperature WY01- WY05
0
5
10
15
20
25
30
Cosumnes River @ TwinCities Rd.
Mokelumne River @NewHope Rd.
Pixley Slough @ DavisRd
Bear Creek @ ThortonRoad (J8)
Bear Creek @LowerSacramento Rd.
Tem
pera
ture
(ºC
)
Median
R2-2
55
San Joaquin River Northeast Basin Specific Conductivity WY01- WY05
0
200
400
600
800
1000
1200
Oct
-00
Jan-
01
Apr
-01
Jul-0
1
Oct
-01
Jan-
02
Apr
-02
Jul-0
2
Oct
-02
Jan-
03
Apr
-03
Jul-0
3
Oct
-03
Jan-
04
Apr
-04
Jul-0
4
Oct
-04
Jan-
05
Apr
-05
Jul-0
5
Oct
-05
Jan-
06
Sample Date
SC (μ
mho
s/cm
)
Cosumnes River @ Twin Cities Rd. Mokelumne River @New Hope Rd. Pixley Slough @ Davis RdBear Creek @ Thorton Road (J8)Bear Creek @Lower Sacramento Rd. Basin Plan Objective (Apr 1-Aug 31, 700 μmhos/cm; Sep 1-Mar 31,1000 μmhos/cm)
R2-3
56
San Joaquin River Northeast BasinSpecific Conductivity WY01- WY05
0
100
200
300
400
500
600
Cosumnes River @ TwinCities Rd.
Mokelumne River @NewHope Rd.
Pixley Slough @ DavisRd
Bear Creek @ ThortonRoad (J8)
Bear Creek @LowerSacramento Rd.
Spec
ific
Con
duct
ivity
(μm
hos/
cm)
Median
R2-4
57
San Joaquin River Northeast Basin pH WY01-WY05
5
6
7
8
9
10
Oct
-00
Jan-
01
Apr
-01
Jul-0
1
Oct
-01
Jan-
02
Apr
-02
Jul-0
2
Oct
-02
Jan-
03
Apr
-03
Jul-0
3
Oct
-03
Jan-
04
Apr
-04
Jul-0
4
Oct
-04
Jan-
05
Apr
-05
Jul-0
5
Sample Date
pH
Cosumnes River @ Twin Cities Rd. Mokelumne River @New Hope Rd. Pixley Slough @ Davis RdBear Creek @ Thorton Road (J8) Bear Creek @Lower Sacramento Rd. Basin Plan Objective (6.5-8.5)
R2-5
58
San Joaquin River Northeast BasinpH WY01- WY05
5
6
7
8
9
10
Cosumnes River @ TwinCities Rd.
Mokelumne River @NewHope Rd.
Pixley Slough @ DavisRd
Bear Creek @ ThortonRoad (J8)
Bear Creek @LowerSacramento Rd.
pH
MedianBasin Plan Objective (6.5-8.5)
R2-6
59
San Joaquin River Northeast Basin Dissolved Oxygen WY01-WY05
0
2
4
6
8
10
12
14
16
18
Apr
-01
Jul-0
1
Oct
-01
Jan-
02
Apr
-02
Jul-0
2
Oct
-02
Jan-
03
Apr
-03
Jul-0
3
Oct
-03
Jan-
04
Apr
-04
Jul-0
4
Oct
-04
Jan-
05
Apr
-05
Jul-0
5
Oct
-05
Jan-
06
Sample Date
DO
(mg/
L)
Cosumnes River @ Twin Cities Rd. Mokelumne River @New Hope Rd. Pixley Slough @ Davis RdBear Creek @ Thorton Road (J8) Bear Creek @Lower Sacramento Rd. Basin Plan Objective (7.0 mg/L)
R2-7
60
San Joaquin River Northeast BasinDissolved Oxygen WY01- WY05
0
2
4
6
8
10
12
14
16
Cosumnes River @ TwinCities Rd.
Mokelumne River @NewHope Rd.
Pixley Slough @ DavisRd
Bear Creek @ ThortonRoad (J8)
Bear Creek @LowerSacramento Rd.
Dis
solv
ed O
xyge
n (m
g/L)
MedianBasin Plan Objective (7.0 mg/L)
R2-8
61
San Joaquin River Notheast Basin Turbidity WY02-WY04
0
50
100
150
200
250
300
Jul-0
2
Oct
-02
Jan-
03
Apr
-03
Jul-0
3
Oct
-03
Jan-
04
Apr
-04
Sample Date
Turb
idity
(ntu
)
Cosumnes River @ Twin Cities Rd. Mokelumne River @New Hope Rd. Pixley Slough @ Davis RdBear Creek @ Thorton Road (J8) Bear Creek @Lower Sacramento Rd.
R2-9
62
San Joaquin River Northeast BasinTurbidity WY02- WY04
0
50
100
150
200
250
300
Cosumnes River @ TwinCities Rd.
Mokelumne River @NewHope Rd.
Pixley Slough @ DavisRd
Bear Creek @ ThortonRoad (J8)
Bear Creek @LowerSacramento Rd.
Turb
idity
(ntu
)
Median
R2-10
63
San Joaquin River Notheast Basin Total Suspended Solids WY01
0
10
20
30
40
50
60
Oct
-00
Jan-
01
Apr
-01
Jul-0
1
Sample Date
TSS
(mg/
L)
Cosumnes River @ Twin Cities Rd. Mokelumne River @New Hope Rd. Pixley Slough @ Davis Rd Bear Creek @ Thorton Road (J8)
R2-11
64
San Joaquin River Northeast BasinTotal Suspended Solids WY01- WY05
0
10
20
30
40
50
60
Cosumnes River @ Twin CitiesRd.
Mokelumne River @New HopeRd.
Pixley Slough @ Davis Rd Bear Creek @ Thorton Road(J8)
Tota
l Sus
pend
ed S
olid
s (m
g/L)
Median
R2-12
65
San Joaquin River Northeast BasinTotal Organic Carbon WY01-WY05
0
5
10
15
20
25
Oct
-00
Jan-
01
Apr
-01
Jul-0
1
Oct
-01
Jan-
02
Apr
-02
Jul-0
2
Oct
-02
Jan-
03
Apr
-03
Jul-0
3
Oct
-03
Jan-
04
Apr
-04
Jul-0
4
Oct
-04
Jan-
05
Apr
-05
Jul-0
5
Sample Date
TOC
(mg/
L)
Cosumnes River @ Twin Cities Rd. Mokelumne River @New Hope Rd. Pixley Slough @ Davis RdBear Creek @ Thorton Road (J8) Bear Creek @Lower Sacramento Rd. Bay-Delta Authority Target (3 mg/L)
R2-13
66
San Joaquin River Northeast BasinTotal Organic Carbon WY01- WY05
0
5
10
15
20
25
Cosumnes River @ TwinCities Rd.
Mokelumne River @NewHope Rd.
Pixley Slough @ DavisRd
Bear Creek @ ThortonRoad (J8)
Bear Creek @LowerSacramento Rd.
Tota
l Org
anic
Car
bon
(mg/
L)
MedianBay-Delta Authority Target (3 mg/L)
R2-14
67
San Joaquin River Northeast Basin Total Coliform WY02-WY05
0
500
1000
1500
2000
2500
Jul-0
2
Oct
-02
Jan-
03
Apr
-03
Jul-0
3
Oct
-03
Jan-
04
Apr
-04
Jul-0
4
Oct
-04
Jan-
05
Apr
-05
Jul-0
5
Sample Date
Tota
l Col
iform
(MPN
/100
ml)
Cosumnes River @ Twin Cities Rd. Mokelumne River @New Hope Rd. Pixley Slough @ Davis RdBear Creek @ Thorton Road (J8) Bear Creek @Lower Sacramento Rd.
R2-15
68
San Joaquin River Northeast BasinTotal Coliform WY02- WY05
0
500
1000
1500
2000
2500
3000
Cosumnes River @ TwinCities Rd.
Mokelumne River @NewHope Rd.
Pixley Slough @ DavisRd
Bear Creek @ ThortonRoad (J8)
Bear Creek @LowerSacramento Rd.
Tota
l Col
iform
(MPN
/100
ml)
Median
R2-16
69
San Joaquin River Northeast Basin Escherichia coli WY02-WY05
0
500
1000
1500
2000
2500
Jul-0
2
Oct
-02
Jan-
03
Apr
-03
Jul-0
3
Oct
-03
Jan-
04
Apr
-04
Jul-0
4
Oct
-04
Jan-
05
Apr
-05
Jul-0
5
Sample Date
E. c
oli
(MPN
/100
ml)
Cosumnes River @ Twin Cities Rd. Mokelumne River @New Hope Rd. Pixley Slough @ Davis Rd Bear Creek @ Thorton Road (J8)Bear Creek @Lower Sacramento Rd. USEPA Guideline - Designated beach area. (235 MPN/100 mL)
R2-17
70
San Joaquin River Northeast BasinEscherichia coli WY02-WY05
0
500
1000
1500
2000
2500
3000
Cosumnes River @ TwinCities Rd.
Mokelumne River @NewHope Rd.
Pixley Slough @ DavisRd
Bear Creek @ ThortonRoad (J8)
Bear Creek @LowerSacramento Rd.
E. c
oli
(MPN
/100
ml)
MedianUSEPA Guideline - Designated beach area. (235 MPN/100 mL)
R2-18
71
San Joaquin River Northeast Basin Nitrate WY01-WY02
0
5
10
15
20
25
30
35
40
45
Oct
-00
Jan-
01
Apr
-01
Jul-0
1
Oct
-01
Sample Date
Nitr
ate
(mg/
L)
Cosumnes River @ Twin Cities Rd. Mokelumne River @New Hope Rd. Pixley Slough @ Davis RdBear Creek @ Thorton Road (J8) California Primary MCL (45mg/L)
R2-19
72
San Joaquin River Northeast BasinNitrate WY01-WY04
0
5
10
15
20
25
30
35
40
45
Cosumnes River @ Twin CitiesRd.
Mokelumne River @New HopeRd.
Pixley Slough @ Davis Rd Bear Creek @ Thorton Road(J8)
Nitr
ate
(mg/
L)
MedianCalifornia Primary MCL (45mg/L)
R2-20
73
San Joaquin River Northeast Basin Total Kjeldahl Nitrogen WY01-WY03
0.0
0.5
1.0
1.5
2.0
2.5
3.0
3.5
4.0
Oct
-00
Jan-
01
Apr
-01
Jul-0
1
Oct
-01
Jan-
02
Apr
-02
Jul-0
2
Oct
-02
Jan-
03
Apr
-03
Sample Date
TKN
(mg/
L)
Cosumnes River @ Twin Cities Rd. Mokelumne River @New Hope Rd. Pixley Slough @ Davis RdBear Creek @ Thorton Road (J8) Bear Creek @Lower Sacramento Rd.
R2-21
74
San Joaquin River Northeast BasinTotal Kjeldahl Nitrogen WY01-WY05
0
0.5
1
1.5
2
2.5
3
3.5
4
Cosumnes River @ TwinCities Rd.
Mokelumne River @NewHope Rd.
Pixley Slough @ DavisRd
Bear Creek @ ThortonRoad (J8)
Bear Creek @LowerSacramento Rd.
TKN
(mg/
L)
Median
R2-22
75
San Joaquin River Northeast Basin Phosphorus WY01-WY03
0.0
0.2
0.4
0.6
0.8
1.0
1.2
1.4
Oct
-00
Jan-
01
Apr
-01
Jul-0
1
Oct
-01
Jan-
02
Apr
-02
Jul-0
2
Oct
-02
Jan-
03
Apr
-03
Sample Date
Phos
phor
us (m
g/L)
Cosumnes River @ Twin Cities Rd. Mokelumne River @New Hope Rd. Pixley Slough @ Davis RdBear Creek @ Thorton Road (J8) Bear Creek @Lower Sacramento Rd.
R2-23
76
San Joaquin River Northeast BasinPhosphorus WY01-WY05
0
0.2
0.4
0.6
0.8
1
1.2
1.4
1.6
Cosumnes River @ TwinCities Rd.
Mokelumne River @NewHope Rd.
Pixley Slough @ DavisRd
Bear Creek @ ThortonRoad (J8)
Bear Creek @LowerSacramento Rd.
Phos
phor
us (m
g/L)
Median
R2-24
77
San Joaquin River Northeast Basin Orthophosphate-P WY01-WY03
0.0
0.2
0.4
0.6
0.8
1.0
1.2
Oct
-00
Jan-
01
Apr
-01
Jul-0
1
Oct
-01
Jan-
02
Apr
-02
Jul-0
2
Oct
-02
Jan-
03
Apr
-03
Sample Date
Ort
ho-P
(mg/
L)
Cosumnes River @ Twin Cities Rd. Mokelumne River @New Hope Rd. Pixley Slough @ Davis RdBear Creek @ Thorton Road (J8) Bear Creek @Lower Sacramento Rd.
R2-25
78
San Joaquin River Northeast BasinOrthophosphate-P WY01-WY05
0
0.2
0.4
0.6
0.8
1
1.2
Cosumnes River @ TwinCities Rd.
Mokelumne River @NewHope Rd.
Pixley Slough @ DavisRd
Bear Creek @ ThortonRoad (J8)
Bear Creek @LowerSacramento Rd.
Ort
hoph
osph
ate-
P (m
g/L)
Median
R2-26
79
San Joaquin River Northeast Basin Potassium WY01-WY03
0
2
4
6
8
10
12
14
16
18
20
Oct
-00
Jan-
01
Apr
-01
Jul-0
1
Oct
-01
Jan-
02
Apr
-02
Jul-0
2
Oct
-02
Jan-
03
Apr
-03
Sample Date
Pota
ssiu
m (m
g/L)
Cosumnes River @ Twin Cities Rd. Mokelumne River @New Hope Rd. Pixley Slough @ Davis RdBear Creek @ Thorton Road (J8) Bear Creek @Lower Sacramento Rd.
R2-27
80
San Joaquin River Northeast BasinPotassium WY01-WY04
0
2
4
6
8
10
12
14
16
18
20
Cosumnes River @ TwinCities Rd.
Mokelumne River @NewHope Rd.
Pixley Slough @ DavisRd
Bear Creek @ ThortonRoad (J8)
Bear Creek @LowerSacramento Rd.
Pota
ssiu
m (m
g/L)
Median
R2-28
81
San Joaquin River Northeast Basin Biochemical Oxygen Demand 5-Day WY01-WY03
0
1
2
3
4
5
6
7
8
9
Oct
-00
Jan-
01
Apr
-01
Jul-0
1
Oct
-01
Jan-
02
Apr
-02
Jul-0
2
Oct
-02
Jan-
03
Apr
-03
Sample Date
BO
D 5
-Day
(mg/
L)
Cosumnes River @ Twin Cities Rd. Mokelumne River @New Hope Rd. Pixley Slough @ Davis RdBear Creek @ Thorton Road (J8) Bear Creek @Lower Sacramento Rd.
R2-29
82
San Joaquin River Northeast BasinBiological Oxygen Demand 5-Day WY01-WY03
0
1
2
3
4
5
6
7
8
9
Cosumnes River @ TwinCities Rd.
Mokelumne River @NewHope Rd.
Pixley Slough @ DavisRd
Bear Creek @ ThortonRoad (J8)
Bear Creek @LowerSacramento Rd.
BO
D- 5
(mg/
L)
Median
R2-30
83
San Joaquin River Northeast Basin Biochemical Oxygen Demand 10-Day WY01-WY03
0
2
4
6
8
10
12
14
16
18
Oct
-00
Jan-
01
Apr
-01
Jul-0
1
Oct
-01
Jan-
02
Apr
-02
Jul-0
2
Oct
-02
Jan-
03
Apr
-03
Sample Date
BO
D 1
0-D
ay (m
g/L)
Cosumnes River @ Twin Cities Rd. Mokelumne River @New Hope Rd. Pixley Slough @ Davis RdBear Creek @ Thorton Road (J8) Bear Creek @Lower Sacramento Rd.
R2-31
84
San Joaquin River Northeast BasinBiological Oxygen Demand 10-Day WY01-WY03
0
2
4
6
8
10
12
14
16
18
Cosumnes River @ TwinCities Rd.
Mokelumne River @NewHope Rd.
Pixley Slough @ DavisRd
Bear Creek @ ThortonRoad (J8)
Bear Creek @LowerSacramento Rd.
BO
D- 1
0 (m
g/L)
Median
R2-32
85
San Joaquin River Northeast Basin Chloride WY01-WY03
0
50
100
150
200
250
300
Oct
-00
Jan-
01
Apr
-01
Jul-0
1
Oct
-01
Jan-
02
Apr
-02
Jul-0
2
Oct
-02
Jan-
03
Apr
-03
Sample Date
Chl
orid
e (m
g/L)
Cosumnes River @ Twin Cities Rd. Mokelumne River @New Hope Rd. Pixley Slough @ Davis Rd Bear Creek @ Thorton Road (J8)Bear Creek @Lower Sacramento Rd. California Secondary MCL (recommended level) (250 mg/L)
R2-33
86
San Joaquin River Northeast BasinChloride WY01-WY03
0
50
100
150
200
250
300
Cosumnes River @ TwinCities Rd.
Mokelumne River @NewHope Rd.
Pixley Slough @ DavisRd
Bear Creek @ ThortonRoad (J8)
Bear Creek @LowerSacramento Rd.
Chl
orid
e (m
g/L)
MedianCalifornia Secondary MCL (recommended level) (250 mg/L)
R2-34
87
San Joaquin River Northeast Basin Sulfate WY01-WY03 Log Scale
1
10
100
1000
Oct
-00
Jan-
01
Apr
-01
Jul-0
1
Oct
-01
Jan-
02
Apr
-02
Jul-0
2
Oct
-02
Jan-
03
Apr
-03
Sample Date
Sulfa
te L
og s
cale
(mg/
L)
Cosumnes River @ Twin Cities Rd. Mokelumne River @New Hope Rd.
Pixley Slough @ Davis Rd Bear Creek @ Thorton Road (J8)
Bear Creek @Lower Sacramento Rd. California Secondary MCL (recommended level) (250 mg/L)
R2-35
88
San Joaquin River Northeast BasinSulfate WY01-WY03
0
5
10
15
20
25
Cosumnes River @ TwinCities Rd.
Mokelumne River @NewHope Rd.
Pixley Slough @ DavisRd
Bear Creek @ ThortonRoad (J8)
Bear Creek @LowerSacramento Rd.
Sulfa
te (m
g/L)
MedianCalifornia Secondary MCL (recommended level) (250 mg/L)
R2-36
89
San Joaquin River Northeast Basin Calcium WY01-WY03
0
5
10
15
20
25
Oct
-00
Jan-
01
Apr
-01
Jul-0
1
Oct
-01
Jan-
02
Apr
-02
Jul-0
2
Oct
-02
Jan-
03
Apr
-03
Sample Date
Cal
cium
(mg/
L)
Cosumnes River @ Twin Cities Rd. Mokelumne River @New Hope Rd. Pixley Slough @ Davis RdBear Creek @ Thorton Road (J8) Bear Creek @Lower Sacramento Rd.
R2-37
90
San Joaquin River Northeast BasinCalcium WY01-WY03
0
5
10
15
20
25
Cosumnes River @ TwinCities Rd.
Mokelumne River @NewHope Rd.
Pixley Slough @ DavisRd
Bear Creek @ ThortonRoad (J8)
Bear Creek @LowerSacramento Rd.
Cal
cium
(mg/
L)
Median
R2-38
91
San Joaquin River Northeast Basin Magnesium WY01-WY03
0
1
2
3
4
5
6
7
8
9
10
Oct
-00
Jan-
01
Apr
-01
Jul-0
1
Oct
-01
Jan-
02
Apr
-02
Jul-0
2
Oct
-02
Jan-
03
Apr
-03
Sample Date
Mag
nesi
um (m
g/L)
Cosumnes River @ Twin Cities Rd. Mokelumne River @New Hope Rd. Pixley Slough @ Davis RdBear Creek @ Thorton Road (J8) Bear Creek @Lower Sacramento Rd.
R2-39
92
San Joaquin River Northeast BasinMagnesium WY01-WY03
0
2
4
6
8
10
12
Cosumnes River @ TwinCities Rd.
Mokelumne River @NewHope Rd.
Pixley Slough @ DavisRd
Bear Creek @ ThortonRoad (J8)
Bear Creek @LowerSacramento Rd.
Mag
nesi
um (m
g/L)
Median
R2-40
93
San Joaquin River Northeast Basin Total Dissolved Solids WY01-WY03
0
100
200
300
400
500
600
Oct
-00
Jan-
01
Apr
-01
Jul-0
1
Oct
-01
Jan-
02
Apr
-02
Jul-0
2
Oct
-02
Sample Date
TDS
(mg/
L)
Cosumnes River @ Twin Cities Rd. Mokelumne River @New Hope Rd. Pixley Slough @ Davis Rd Bear Creek @ Thorton Road (J8)Bear Creek @Lower Sacramento Rd. California Secondary MCL (recommended level) (500 mg/L)
R2-41
94
San Joaquin River Northeast BasinTotal Dissolved Solids WY01-WY03
0
100
200
300
400
500
600
Cosumnes River @ TwinCities Rd.
Mokelumne River @NewHope Rd.
Pixley Slough @ DavisRd
Bear Creek @ ThortonRoad (J8)
Bear Creek @LowerSacramento Rd.
TDS
(mg/
L)
MedianCalifornia Secondary MCL (recommended level) (250 mg/L)
R2-42
95
San Joaquin River Northeast Basin Carbonate WY01-WY03
0
5
10
15
20
25
30
Oct
-00
Jan-
01
Apr
-01
Jul-0
1
Oct
-01
Jan-
02
Apr
-02
Jul-0
2
Oct
-02
Sample Date
Car
bona
te (m
g/L)
Cosumnes River @ Twin Cities Rd. Mokelumne River @New Hope Rd. Pixley Slough @ Davis RdBear Creek @ Thorton Road (J8) Bear Creek @Lower Sacramento Rd.
R2-43
96
San Joaquin River Northeast BasinCarbonate WY01-WY03
0
0.1
0.2
0.3
0.4
0.5
0.6
Cosumnes River @ TwinCities Rd.
Mokelumne River @NewHope Rd.
Pixley Slough @ DavisRd
Bear Creek @ ThortonRoad (J8)
Bear Creek @LowerSacramento Rd.
Car
bona
te (m
g/L)
Median
R2-44
97
San Joaquin River Northesat Basin Bicarbonate WY01-WY03
0
20
40
60
80
100
120
140
Oct
-00
Jan-
01
Apr
-01
Jul-0
1
Oct
-01
Jan-
02
Apr
-02
Jul-0
2
Oct
-02
Sample Date
Bic
arbo
nate
(mg/
L)
Cosumnes River @ Twin Cities Rd. Mokelumne River @New Hope Rd. Pixley Slough @ Davis RdBear Creek @ Thorton Road (J8) Bear Creek @Lower Sacramento Rd.
R2-45
98
San Joaquin River Northeast BasinBicarbonate WY01-WY03
0
20
40
60
80
100
120
140
Cosumnes River @ TwinCities Rd.
Mokelumne River @NewHope Rd.
Pixley Slough @ DavisRd
Bear Creek @ ThortonRoad (J8)
Bear Creek @LowerSacramento Rd.
Bic
arbo
nate
(mg/
L)
Median
R2-46
99
San Joaquin River Northeast Basin Total Alkalinity WY01-WY03
0
20
40
60
80
100
Oct
-00
Jan-
01
Apr
-01
Jul-0
1
Oct
-01
Jan-
02
Apr
-02
Jul-0
2
Oct
-02
Sample Date
Tota
l Alk
alin
ity (m
g/L)
Cosumnes River @ Twin Cities Rd. Mokelumne River @New Hope Rd. Pixley Slough @ Davis RdBear Creek @ Thorton Road (J8) Bear Creek @Lower Sacramento Rd.
R2-47
100
San Joaquin River Northeast BasinTotal Alkalinity WY01-WY03
0
20
40
60
80
100
120
Cosumnes River @ TwinCities Rd.
Mokelumne River @NewHope Rd.
Pixley Slough @ DavisRd
Bear Creek @ ThortonRoad (J8)
Bear Creek @LowerSacramento Rd.
Tota
l Alk
alin
ity (m
g/L)
Median
R2-48
101
San Joaquin River Northeast Basin Sodium WY01-WY03
0
10
20
30
40
50
60
70
Oct
-00
Jan-
01
Apr
-01
Jul-0
1
Oct
-01
Jan-
02
Apr
-02
Jul-0
2
Oct
-02
Sample Date
Sodi
um (m
g/L)
Cosumnes River @ Twin Cities Rd. Mokelumne River @New Hope Rd. Pixley Slough @ Davis Rd Bear Creek @ Thorton Road (J8)Bear Creek @Lower Sacramento Rd. Water Quality for Agriculture(Ayers & Westcot) (69 mg/L)
R2-49
102
San Joaquin River Northeast BasinSodium WY01-WY03
0
10
20
30
40
50
60
70
Cosumnes River @ TwinCities Rd.
Mokelumne River @NewHope Rd.
Pixley Slough @ DavisRd
Bear Creek @ ThortonRoad (J8)
Bear Creek @LowerSacramento Rd.
Sodi
um (m
g/L)
MedianWater Quality for Agriculture (Ayers & Westcot) (69 mg/L)
R2-50
103
San Joaquin River East Side Basin Temperature WY01-WY05
0
5
10
15
20
25
30
Oct
-00
Jan-
01
Apr
-01
Jul-0
1
Oct
-01
Jan-
02
Apr
-02
Jul-0
2
Oct
-02
Jan-
03
Apr
-03
Jul-0
3
Oct
-03
Jan-
04
Apr
-04
Jul-0
4
Oct
-04
Jan-
05
Apr
-05
Jul-0
5
Sample Date
Tem
p (º
C)
Turner Slough at 4th Avenue Merced River Hatfield Park (River Road) Harding Drain discharge @ San Joaquin River (TID5) Tuolumne River @ Shiloh Stanislaus River @Caswell French Camp Slough @ AirportLone Tree Creek @ Austin RdBay-Delta Authority Target, SJR @ Vernalis (Apr 1-Jun 30 & Sept 1- Nov 30, 20ºC)
R3-1
104
San Joaquin River Eastside BasinTemperature WY01- WY05
0
5
10
15
20
25
30
35
Turner Slough at4th Avenue
Merced RiverHatfield
Park(River Rd)
Lone Tree Creek@ Austin Rd
French CampSlough @ Airport
Harding Drain @SJR (TID5)
Tuolumne River@ Shiloh
Stanislaus River@Caswell
Tem
pera
ture
(ºC
)
Median
R3-2
105
San Joaquin River East Side Basin Specific Conductivity WY01-WY05
0
200
400
600
800
1000
1200
1400
1600
Oct
-00
Jan-
01
Apr
-01
Jul-0
1
Oct
-01
Jan-
02
Apr
-02
Jul-0
2
Oct
-02
Jan-
03
Apr
-03
Jul-0
3
Oct
-03
Jan-
04
Apr
-04
Jul-0
4
Oct
-04
Jan-
05
Apr
-05
Jul-0
5
Sample Date
Spec
ific
Con
duct
ivity
(μm
hos/
cm)
Turner Slough at 4th Avenue Merced River Hatfield Park (River Road) Harding Drain discharge @ San Joaquin River (TID5) Tuolumne River @ Shiloh Stanislaus River @Caswell Basin Plan Objective (Apr 1-Aug 31, 700 μmhos/cm; Sep 1-Mar 31,1000 μmhos/cm)French Camp Slough @ AirportLone Tree Creek @ Austin Rd
R3-3
106
San Joaquin River Eastside BasinSpecific Conductivity WY01- WY05
0
200
400
600
800
1000
1200
1400
1600
Turner Slough at4th Avenue
Merced RiverHatfield
Park(River Rd)
Lone Tree Creek@ Austin Rd
French CampSlough @ Airport
Harding Drain @SJR (TID5)
Tuolumne River@ Shiloh
Stanislaus River@Caswell
Spec
ific
Con
duct
ivity
(μm
hos/
cm)
Median
R3-4
107
San Joaquin River East Side Basin pH WY01-WY05
5.0
5.5
6.0
6.5
7.0
7.5
8.0
8.5
9.0
9.5
Oct
-00
Jan-
01
Apr
-01
Jul-0
1
Oct
-01
Jan-
02
Apr
-02
Jul-0
2
Oct
-02
Jan-
03
Apr
-03
Jul-0
3
Oct
-03
Jan-
04
Apr
-04
Jul-0
4
Oct
-04
Jan-
05
Apr
-05
Jul-0
5
Sample Date
pH
Turner Slough at 4th Avenue Merced River Hatfield Park (River Road) Harding Drain discharge @ San Joaquin River (TID5) Tuolumne River @ Shiloh Stanislaus River @Caswell Basin Plan Objective (6.5-8.5)French Camp Slough @ Airport Lone Tree Creek @ Austin Rd
R3-5
108
San Joaquin River Eastside BasinpH WY01- WY05
5
5.5
6
6.5
7
7.5
8
8.5
9
9.5
10
Turner Slough at4th Avenue
Merced RiverHatfield
Park(River Rd)
Lone Tree Creek@ Austin Rd
French CampSlough @ Airport
Harding Drain @SJR (TID5)
Tuolumne River@ Shiloh
Stanislaus River@Caswell
pH
MedianBasin Plan Objective (6.5-8.5)
R3-6
109
San Joaquin River East Side Basin Dissolved Oxygen WY01-WY05
0
2
4
6
8
10
12
14
16
18
Apr
-01
Jul-0
1
Oct
-01
Jan-
02
Apr
-02
Jul-0
2
Oct
-02
Jan-
03
Apr
-03
Jul-0
3
Oct
-03
Jan-
04
Apr
-04
Jul-0
4
Oct
-04
Jan-
05
Apr
-05
Jul-0
5
Sample Date
DO
(mg/
L)
Turner Slough at 4th Avenue Merced River Hatfield Park (River Road) Harding Drain discharge @ San Joaquin River (TID5) Tuolumne River @ Shiloh Stanislaus River @Caswell Basin Plan Objective (7.0 mg/L)French Camp Slough @ Airport
R3-7
110
San Joaquin River Eastside BasinDissolved Oxygen WY01- WY05
0
2
4
6
8
10
12
14
16
18
Turner Slough at4th Avenue
Merced RiverHatfield
Park(River Rd)
Lone Tree Creek@ Austin Rd
French CampSlough @ Airport
Harding Drain @SJR (TID5)
Tuolumne River@ Shiloh
Stanislaus River@Caswell
Dis
solv
ed O
xyge
n (m
g/L)
MedianBasin Plan Objective (7.0 mg/L)
R3-8
111
San Joaquin River East Side Basin Turbidity WY02-WY04
0
100
200
300
400
500
600
700
Jul-0
2
Oct
-02
Jan-
03
Apr
-03
Jul-0
3
Oct
-03
Jan-
04
Apr
-04
Sample Date
Turb
idity
(ntu
)
Turner Slough at 4th Avenue Merced River Hatfield Park (River Road) Harding Drain discharge @ San Joaquin River (TID5) Tuolumne River @ Shiloh Stanislaus River @Caswell French Camp Slough @ AirportLone Tree Creek @ Austin Rd
R3-9
112
San Joaquin River Eastside BasinTurbidity WY02- WY04
0
100
200
300
400
500
600
700
800
Turner Slough at4th Avenue
Merced RiverHatfield
Park(River Rd)
Lone Tree Creek@ Austin Rd
French CampSlough @ Airport
Harding Drain @SJR (TID5)
Tuolumne River@ Shiloh
Stanislaus River@Caswell
Turb
idity
(ntu
)
Median
R3-10
113
San Joaquin River East Side Basin Total Suspended Solids WY01-WY03
0
20
40
60
80
100
120
Oct
-00
Jan-
01
Apr
-01
Jul-0
1
Oct
-01
Jan-
02
Apr
-02
Jul-0
2
Oct
-02
Jan-
03
Apr
-03
Sample Date
TSS
(mg/
L)
Turner Slough at 4th Avenue Merced River Hatfield Park (River Road) Harding Drain discharge @ San Joaquin River (TID5) Tuolumne River @ Shiloh Stanislaus River @Caswell French Camp Slough @ AirportLone Tree Creek @ Austin Rd
R3-11
114
San Joaquin River Eastside BasinTotal Suspended Solids WY01- WY05
0
20
40
60
80
100
120
140
Turner Slough at4th Avenue
Merced RiverHatfield
Park(River Rd)
Lone Tree Creek@ Austin Rd
French CampSlough @ Airport
Harding Drain @SJR (TID5)
Tuolumne River@ Shiloh
Stanislaus River@Caswell
Tota
l Sus
pend
ed S
olid
s (m
g/L)
Median
R3-12
115
San Joaquin River East Side Basin Total Orgainic Carbon WY01-WY05
0
10
20
30
40
50
60
70
Oct
-00
Jan-
01
Apr
-01
Jul-0
1
Oct
-01
Jan-
02
Apr
-02
Jul-0
2
Oct
-02
Jan-
03
Apr
-03
Jul-0
3
Oct
-03
Jan-
04
Apr
-04
Jul-0
4
Oct
-04
Jan-
05
Apr
-05
Jul-0
5
Sample Date
TOC
(mg/
L)
Turner Slough at 4th Avenue Merced River Hatfield Park (River Road) Harding Drain discharge @ San Joaquin River (TID5) Tuolumne River @ Shiloh Stanislaus River @Caswell Bay-Delta Authority Target (3 mg/L)French Camp Slough @ Airport Lone Tree Creek @ Austin Rd
R3-13
116
San Joaquin River Eastside BasinTotal Organic Carbon WY01- WY05
0
10
20
30
40
50
60
70
80
Turner Slough at4th Avenue
Merced RiverHatfield
Park(River Rd)
Lone Tree Creek@ Austin Rd
French CampSlough @ Airport
Harding Drain @SJR (TID5)
Tuolumne River@ Shiloh
Stanislaus River@Caswell
Tota
l Org
anic
Car
bon
(mg/
L)
MedianBay-Delta Authority Target (3 mg/L)
R3-14
117
San Joaquin River East Side Basin Total Coliform WY02-WY05
0
500
1000
1500
2000
2500
Jul-0
2
Oct
-02
Jan-
03
Apr
-03
Jul-0
3
Oct
-03
Jan-
04
Apr
-04
Jul-0
4
Oct
-04
Jan-
05
Apr
-05
Jul-0
5
Sample Date
Tota
l Col
iform
(MPN
/100
ml)
Turner Slough at 4th Avenue Merced River Hatfield Park (River Road) Harding Drain discharge @ San Joaquin River (TID5) Tuolumne River @ Shiloh Stanislaus River @Caswell French Camp Slough @ AirportLone Tree Creek @ Austin Rd
R3-15
118
San Joaquin River Eastside BasinTotal Coliform WY02- WY05
0
500
1000
1500
2000
2500
3000
Turner Slough at4th Avenue
Merced RiverHatfield
Park(River Rd)
Lone Tree Creek@ Austin Rd
French CampSlough @ Airport
Harding Drain @SJR (TID5)
Tuolumne River@ Shiloh
Stanislaus River@Caswell
Tota
l Col
iform
(MPN
/100
ml)
Median
R3-16
119
San Joaquin River East Side Basin Escherichia coli WY02-WY05
0
500
1000
1500
2000
2500
Jul-0
2
Oct
-02
Jan-
03
Apr
-03
Jul-0
3
Oct
-03
Jan-
04
Apr
-04
Jul-0
4
Oct
-04
Jan-
05
Apr
-05
Jul-0
5
Sample Date
E. c
oli
(MPN
/100
ml)
Turner Slough at 4th Avenue Merced River Hatfield Park (River Road) Harding Drain discharge @ San Joaquin River (TID5) Tuolumne River @ Shiloh Stanislaus River @Caswell USEPA Guideline - Designated beach area. (235 MPN/100 mL)French Camp Slough @ Airport Lone Tree Creek @ Austin Rd
R3-17
120
San Joaquin River Eastside BasinEscherichia coli WY02-WY05
0
500
1000
1500
2000
2500
3000
Turner Slough at4th Avenue
Merced RiverHatfield
Park(River Rd)
Lone Tree Creek@ Austin Rd
French CampSlough @ Airport
Harding Drain @SJR (TID5)
Tuolumne River@ Shiloh
Stanislaus River@Caswell
E. c
oli
(MPN
/100
ml)
MedianUSEPA Guideline - Designated beach area. (235 MPN/100 mL)
R3-18
121
San Joaquin River East Side Basin Nitrate WY01-WY02
0
5
10
15
20
25
30
35
40
45
Oct
-00
Jan-
01
Apr
-01
Jul-0
1
Oct
-01
Sample Date
Nitr
ate
(mg/
L)
Turner Slough at 4th Avenue Merced River Hatfield Park (River Road) Harding Drain discharge @ San Joaquin River (TID5) Tuolumne River @ Shiloh Stanislaus River @Caswell California Primary MCL (45mg/L)French Camp Slough @ Airport Lone Tree Creek @ Austin Rd
R3-19
122
San Joaquin River Eastside BasinNitrate WY01-WY04
0
5
10
15
20
25
30
35
40
45
50
Turner Slough at4th Avenue
Merced RiverHatfield
Park(River Rd)
Lone Tree Creek@ Austin Rd
French CampSlough @ Airport
Harding Drain @SJR (TID5)
Tuolumne River@ Shiloh
Stanislaus River@Caswell
Nitr
ate
(mg/
L)
MedianCalifornia Primary MCL (45mg/L)
R3-20
123
San Joaquin River East Side BasinTotal Kjeldahl Nitrogen WY01-WY03
0
5
10
15
20
25
30
35
Oct
-00
Jan-
01
Apr
-01
Jul-0
1
Oct
-01
Jan-
02
Apr
-02
Jul-0
2
Oct
-02
Jan-
03
Apr
-03
Sample Date
TKN
(mg/
L)
Turner Slough at 4th Avenue Merced River Hatfield Park (River Road) Harding Drain discharge @ San Joaquin River (TID5) Tuolumne River @ Shiloh Stanislaus River @Caswell French Camp Slough @ AirportLone Tree Creek @ Austin Rd
R3-21
124
San Joaquin River Eastside BasinTotal Kjeldahl Nitrogen WY01-WY05
0
5
10
15
20
25
30
35
Turner Slough at4th Avenue
Merced RiverHatfield
Park(River Rd)
Lone Tree Creek@ Austin Rd
French CampSlough @ Airport
Harding Drain @SJR (TID5)
Tuolumne River@ Shiloh
Stanislaus River@Caswell
TKN
(mg/
L)
Median
R3-22
125
San Joaquin River East Side Basin Phosphorus WY01-WY03
0
2
4
6
8
10
12
Oct
-00
Jan-
01
Apr
-01
Jul-0
1
Oct
-01
Jan-
02
Apr
-02
Jul-0
2
Oct
-02
Jan-
03
Apr
-03
Sample Date
Phos
phor
us (m
g/L)
Turner Slough at 4th Avenue Merced River Hatfield Park (River Road) Harding Drain discharge @ San Joaquin River (TID5) Tuolumne River @ Shiloh Stanislaus River @Caswell French Camp Slough @ AirportLone Tree Creek @ Austin Rd
R3-23
126
San Joaquin River Eastside BasinPhosphorus WY01-WY05
0
2
4
6
8
10
12
14
Turner Slough at4th Avenue
Merced RiverHatfield
Park(River Rd)
Lone Tree Creek@ Austin Rd
French CampSlough @ Airport
Harding Drain @SJR (TID5)
Tuolumne River@ Shiloh
Stanislaus River@Caswell
Phos
phor
us (m
g/L)
Median
R3-24
127
San Joaquin River East Side Basin Orthophosphate-P WY01-WY03
0
2
4
6
8
10
12
Oct
-00
Jan-
01
Apr
-01
Jul-0
1
Oct
-01
Jan-
02
Apr
-02
Jul-0
2
Oct
-02
Jan-
03
Apr
-03
Sample Date
Ort
ho-P
(mg/
L)
Turner Slough at 4th Avenue Merced River Hatfield Park (River Road) Harding Drain discharge @ San Joaquin River (TID5) Tuolumne River @ Shiloh Stanislaus River @Caswell French Camp Slough @ AirportLone Tree Creek @ Austin Rd
R3-25
128
San Joaquin River Eastside BasinOrthophosphate-P WY01-WY05
0
2
4
6
8
10
12
Turner Slough at4th Avenue
Merced RiverHatfield
Park(River Rd)
Lone Tree Creek@ Austin Rd
French CampSlough @ Airport
Harding Drain @SJR (TID5)
Tuolumne River@ Shiloh
Stanislaus River@Caswell
Ort
hoph
osph
ate-
P (m
g/L)
Median
R3-26
129
San Joaquin River East Side Basin Potassium WY01-WY03
0
10
20
30
40
50
60
70
80
90
100
Oct
-00
Jan-
01
Apr
-01
Jul-0
1
Oct
-01
Jan-
02
Apr
-02
Jul-0
2
Oct
-02
Jan-
03
Apr
-03
Sample Date
Pota
ssiu
m (m
g/L)
Turner Slough at 4th Avenue Merced River Hatfield Park (River Road) Harding Drain discharge @ San Joaquin River (TID5) Tuolumne River @ Shiloh Stanislaus River @Caswell French Camp Slough @ AirportLone Tree Creek @ Austin Rd
R3-27
130
San Joaquin River Eastside BasinPotassium WY01-WY04
0
20
40
60
80
100
120
Turner Slough at4th Avenue
Merced RiverHatfield
Park(River Rd)
Lone Tree Creek@ Austin Rd
French CampSlough @ Airport
Harding Drain @SJR (TID5)
Tuolumne River@ Shiloh
Stanislaus River@Caswell
Pota
ssiu
m (m
g/L)
Median
R3-28
131
San Joaquin River East Side Basin Biochemical Oxygen Demand 5-Day WY01-WY03
0
1
2
3
4
5
6
7
8
9
Oct
-00
Jan-
01
Apr
-01
Jul-0
1
Oct
-01
Jan-
02
Apr
-02
Jul-0
2
Oct
-02
Jan-
03
Apr
-03
Sample Date
BO
D 5
-Day
(mg/
L)
Turner Slough at 4th Avenue Merced River Hatfield Park (River Road) Harding Drain discharge @ San Joaquin River (TID5) Tuolumne River @ Shiloh Stanislaus River @Caswell French Camp Slough @ AirportLone Tree Creek @ Austin Rd
R3-29
132
San Joaquin River Eastside BasinBiological Oxygen Demand 5-Day WY01-WY03
0
2
4
6
8
10
12
14
16
18
Turner Slough at4th Avenue
Merced RiverHatfield
Park(River Rd)
Lone Tree Creek@ Austin Rd
French CampSlough @ Airport
Harding Drain @SJR (TID5)
Tuolumne River@ Shiloh
Stanislaus River@Caswell
BO
D- 5
(mg/
L)
Median
R3-30
133
San Joaquin River East Side Basin Biochemical Oxygen Demand 10-Day WY01-WY03
0
5
10
15
20
25
30
35
Oct
-00
Jan-
01
Apr
-01
Jul-0
1
Oct
-01
Jan-
02
Apr
-02
Jul-0
2
Oct
-02
Jan-
03
Apr
-03
Sample Date
BO
D 1
0-D
ay (m
g/L)
Turner Slough at 4th Avenue Merced River Hatfield Park (River Road) Harding Drain discharge @ San Joaquin River (TID5) Tuolumne River @ Shiloh Stanislaus River @Caswell French Camp Slough @ AirportLone Tree Creek @ Austin Rd
R3-31
134
San Joaquin River Eastside BasinBiological Oxygen Demand 10-Day WY01-WY03
0
5
10
15
20
25
30
35
40
Turner Slough at4th Avenue
Merced RiverHatfield
Park(River Rd)
Lone Tree Creek@ Austin Rd
French CampSlough @ Airport
Harding Drain @SJR (TID5)
Tuolumne River@ Shiloh
Stanislaus River@Caswell
BO
D- 1
0 (m
g/L)
Median
R3-32
135
San Joaquin River East Side Basin Chloride WY01-WY03
0
50
100
150
200
250
300
Oct
-00
Jan-
01
Apr
-01
Jul-0
1
Oct
-01
Jan-
02
Apr
-02
Jul-0
2
Oct
-02
Jan-
03
Apr
-03
Sample Date
Chl
orid
e (m
g/L)
Turner Slough at 4th Avenue Merced River Hatfield Park (River Road) Harding Drain discharge @ San Joaquin River (TID5) Tuolumne River @ Shiloh Stanislaus River @Caswell California Secondary MCL (recommended level) (250 mg/L)French Camp Slough @ Airport Lone Tree Creek @ Austin Rd
R3-33
136
San Joaquin River Eastside BasinChloride WY01-WY03
0
50
100
150
200
250
300
Turner Slough at4th Avenue
Merced RiverHatfield
Park(River Rd)
Lone Tree Creek@ Austin Rd
French CampSlough @ Airport
Harding Drain @SJR (TID5)
Tuolumne River@ Shiloh
Stanislaus River@Caswell
Chl
orid
e (m
g/L)
MedianCalifornia Secondary MCL (recommended level) (250 mg/L)
R3-34
137
San Joaquin River East Side Basin Sulfate WY01-WY03
0
50
100
150
200
250
300
Oct
-00
Jan-
01
Apr
-01
Jul-0
1
Oct
-01
Jan-
02
Apr
-02
Jul-0
2
Oct
-02
Jan-
03
Apr
-03
Sample Date
Sulfa
te (m
g/L)
Turner Slough at 4th Avenue Merced River Hatfield Park (River Road) Harding Drain discharge @ San Joaquin River (TID5) Tuolumne River @ Shiloh Stanislaus River @Caswell California Secondary MCL (recommended level) (250 mg/L)French Camp Slough @ Airport Lone Tree Creek @ Austin Rd
R3-35
138
San Joaquin River Eastside BasinSulfate WY01-WY03
0
20
40
60
80
100
120
Turner Slough at4th Avenue
Merced RiverHatfield
Park(River Rd)
Lone Tree Creek@ Austin Rd
French CampSlough @ Airport
Harding Drain @SJR (TID5)
Tuolumne River@ Shiloh
Stanislaus River@Caswell
Sulfa
te (m
g/L)
MedianCalifornia Secondary MCL (recommended level) (250 mg/L)
R3-36
139
San Joaquin River East Side Basin Calcium WY01-WY03
0
10
20
30
40
50
60
70
80
Oct
-00
Jan-
01
Apr
-01
Jul-0
1
Oct
-01
Jan-
02
Apr
-02
Jul-0
2
Oct
-02
Jan-
03
Apr
-03
Sample Date
Cal
cium
(mg/
L)
Turner Slough at 4th Avenue Merced River Hatfield Park (River Road) Harding Drain discharge @ San Joaquin River (TID5) Tuolumne River @ Shiloh Stanislaus River @Caswell French Camp Slough @ AirportLone Tree Creek @ Austin Rd
R3-37
140
San Joaquin River Eastside BasinCalcium WY01-WY03
0
10
20
30
40
50
60
70
80
Turner Slough at4th Avenue
Merced RiverHatfield
Park(River Rd)
Lone Tree Creek@ Austin Rd
French CampSlough @ Airport
Harding Drain @SJR (TID5)
Tuolumne River@ Shiloh
Stanislaus River@Caswell
Cal
cium
(mg/
L)
Median
R3-38
141
San Joaquin River East Side Basin Magnesium WY01-WY03
0
5
10
15
20
25
30
35
40
45
Oct
-00
Jan-
01
Apr
-01
Jul-0
1
Oct
-01
Jan-
02
Apr
-02
Jul-0
2
Oct
-02
Jan-
03
Apr
-03
Sample Date
Mag
nesi
um (m
g/L)
Turner Slough at 4th Avenue Merced River Hatfield Park (River Road) Harding Drain discharge @ San Joaquin River (TID5) Tuolumne River @ Shiloh Stanislaus River @Caswell French Camp Slough @ AirportLone Tree Creek @ Austin Rd
R3-39
142
San Joaquin River Eastside BasinMagnesium WY01-WY03
0
5
10
15
20
25
30
35
40
45
Turner Slough at4th Avenue
Merced RiverHatfield
Park(River Rd)
Lone Tree Creek@ Austin Rd
French CampSlough @ Airport
Harding Drain @SJR (TID5)
Tuolumne River@ Shiloh
Stanislaus River@Caswell
Mag
nesi
um (m
g/L)
Median
R3-40
143
San Joaquin River East Side Basin Total Dissolved Solids WY01-WY03
0
200
400
600
800
1000
1200
1400
1600
1800
2000
Oct
-00
Jan-
01
Apr
-01
Jul-0
1
Oct
-01
Jan-
02
Apr
-02
Jul-0
2
Oct
-02
Sample Date
TDS
(mg/
L)
Turner Slough at 4th Avenue Merced River Hatfield Park (River Road) Harding Drain discharge @ San Joaquin River (TID5) Tuolumne River @ Shiloh Stanislaus River @Caswell California Secondary MCL (recommended level) (500 mg/L)French Camp Slough @ Airport Lone Tree Creek @ Austin Rd
R3-41
144
San Joaquin River Eastside BasinTotal Dissolved Solids WY01-WY03
0
500
1000
1500
2000
2500
Turner Slough at4th Avenue
Merced RiverHatfield
Park(River Rd)
Lone Tree Creek@ Austin Rd
French CampSlough @ Airport
Harding Drain @SJR (TID5)
Tuolumne River@ Shiloh
Stanislaus River@Caswell
TDS
(mg/
L)
MedianCalifornia Secondary MCL (recommended level) (500 mg/L)
R3-42
145
San Joaquin River East Side Basin Carbonate WY01-WY03
0
5
10
15
20
25
30
35
Oct
-00
Jan-
01
Apr
-01
Jul-0
1
Oct
-01
Jan-
02
Apr
-02
Jul-0
2
Oct
-02
Jan-
03
Sample Date
Car
bona
te (m
g/L)
Turner Slough at 4th Avenue Merced River Hatfield Park (River Road) Harding Drain discharge @ San Joaquin River (TID5) Tuolumne River @ Shiloh Stanislaus River @Caswell French Camp Slough @ AirportLone Tree Creek @ Austin Rd
R3-43
146
San Joaquin River Eastside BasinCarbonate WY01-WY03
0
5
10
15
20
25
30
35
Turner Slough at4th Avenue
Merced RiverHatfield
Park(River Rd)
Lone Tree Creek@ Austin Rd
French CampSlough @ Airport
Harding Drain @SJR (TID5)
Tuolumne River@ Shiloh
Stanislaus River@Caswell
Car
bona
te (m
g/L)
Median
R3-44
147
San Joaquin River East Side BasinBicarbonate WY01-WY03
0
200
400
600
800
1000
1200
1400
Oct
-00
Jan-
01
Apr
-01
Jul-0
1
Oct
-01
Jan-
02
Apr
-02
Jul-0
2
Oct
-02
Sample Date
Bic
arbo
nate
(mg/
L)
Turner Slough at 4th Avenue Merced River Hatfield Park (River Road) Harding Drain discharge @ San Joaquin River (TID5) Tuolumne River @ Shiloh Stanislaus River @Caswell French Camp Slough @ AirportLone Tree Creek @ Austin Rd
R3-45
148
San Joaquin River Eastside BasinBicarbonate WY01-WY03
0
200
400
600
800
1000
1200
1400
Turner Slough at4th Avenue
Merced RiverHatfield
Park(River Rd)
Lone Tree Creek@ Austin Rd
French CampSlough @ Airport
Harding Drain @SJR (TID5)
Tuolumne River@ Shiloh
Stanislaus River@Caswell
Bic
arbo
nate
(mg/
L)
Median
R3-46
149
San Joaquin River East Side Basin Total Alkalinity WY01-WY03
0
200
400
600
800
1000
1200
Oct
-00
Jan-
01
Apr
-01
Jul-0
1
Oct
-01
Jan-
02
Apr
-02
Jul-0
2
Oct
-02
Sample Date
Tota
l Alk
alin
ity (m
g/L)
Turner Slough at 4th Avenue Merced River Hatfield Park (River Road) Harding Drain discharge @ San Joaquin River (TID5) Tuolumne River @ Shiloh Stanislaus River @Caswell French Camp Slough @ AirportLone Tree Creek @ Austin Rd
R3-47
150
San Joaquin River Eastside BasinTotal Alkalinity WY01-WY03
0
200
400
600
800
1000
1200
Turner Slough at4th Avenue
Merced RiverHatfield
Park(River Rd)
Lone Tree Creek@ Austin Rd
French CampSlough @ Airport
Harding Drain @SJR (TID5)
Tuolumne River@ Shiloh
Stanislaus River@Caswell
Tota
l Alk
alin
ity (m
g/L)
Median
R3-48
151
San Joaquin River East Side Basin Sodium WY01-WY03
0
50
100
150
200
250
300
350
400
450
500
Oct
-00
Jan-
01
Apr
-01
Jul-0
1
Oct
-01
Jan-
02
Apr
-02
Jul-0
2
Oct
-02
Sample Date
Sodi
um (m
g/L)
Turner Slough at 4th Avenue Merced River Hatfield Park (River Road) Harding Drain discharge @ San Joaquin River (TID5) Tuolumne River @ Shiloh Stanislaus River @Caswell French Camp Slough @ AirportLone Tree Creek @ Austin Rd Water Quality for Agriculture(Ayers & Westcot) (69 mg/L)
R3-49
152
San Joaquin River Eastside BasinSodium WY01-WY03
0
50
100
150
200
250
300
350
400
450
500
Turner Slough at4th Avenue
Merced RiverHatfield
Park(River Rd)
Lone Tree Creek@ Austin Rd
French CampSlough @ Airport
Harding Drain @SJR (TID5)
Tuolumne River@ Shiloh
Stanislaus River@Caswell
Sodi
um (m
g/L)
MedianWater Quality for Agriculture (Ayers & Westcot) (69 mg/L)
R3-50
153
San Joaquin River Southeast Basin Temperature WY01-WY05
0
5
10
15
20
25
30
35
Oct
-00
Jan-
01
Apr
-01
Jul-0
1
Oct
-01
Jan-
02
Apr
-02
Jul-0
2
Oct
-02
Jan-
03
Apr
-03
Jul-0
3
Oct
-03
Jan-
04
Apr
-04
Jul-0
4
Oct
-04
Jan-
05
Apr
-05
Jul-0
5
Sample Date
Tem
pera
ture
(ºC
)
Deep Slough Green House RdBear Creek Bert Crane Rd Santa Rita Slough at Highway 152 Bay-Delta Authority Target, SJR @ Vernalis (Apr 1-Jun 30 & Sept 1- Nov 30, 20ºC)
R4-1
154
San Joaquin River Southeast BasinTemperature WY01- WY05
0
5
10
15
20
25
30
35
Santa Rita Slough at Highway 152 Deep Slough Green House Rd Bear Creek Bert Crane Rd
Tem
pera
ture
(ºC
)
Median
R4-2
155
San Joaquin River Southeast Basin Specific Conductivity WY01-WY05
0
200
400
600
800
1000
1200
Oct
-00
Jan-
01
Apr
-01
Jul-0
1
Oct
-01
Jan-
02
Apr
-02
Jul-0
2
Oct
-02
Jan-
03
Apr
-03
Jul-0
3
Oct
-03
Jan-
04
Apr
-04
Jul-0
4
Oct
-04
Jan-
05
Apr
-05
Jul-0
5
Sample Date
SC (μ
mho
s/cm
)
Deep Slough Green House RdBear Creek Bert Crane Rd Basin Plan Objective (Apr 1-Aug 31, 700 μmhos/cm; Sep 1-Mar 31,1000 μmhos/cm)Santa Rita Slough at Highway 152
R4-3
156
San Joaquin River Southeast BasinSpecific Conductivity WY01- WY05
0
200
400
600
800
1000
1200
Santa Rita Slough at Highway 152 Deep Slough Green House Rd Bear Creek Bert Crane Rd
Spec
ific
Con
duct
ivity
(μm
hos/
cm)
Median
R4-4
157
San Joaquin River Southeast Basin pH WY01-WY05
6.0
6.5
7.0
7.5
8.0
8.5
9.0
Oct
-00
Jan-
01
Apr
-01
Jul-0
1
Oct
-01
Jan-
02
Apr
-02
Jul-0
2
Oct
-02
Jan-
03
Apr
-03
Jul-0
3
Oct
-03
Jan-
04
Apr
-04
Jul-0
4
Oct
-04
Jan-
05
Apr
-05
Jul-0
5
Sample Date
pH
Deep Slough Green House Rd Bear Creek Bert Crane Rd Basin Plan Objective (6.5-8.5) Santa Rita Slough at Highway 152
R4-5
158
San Joaquin River Southeast BasinpH WY01- WY05
6
6.5
7
7.5
8
8.5
9
9.5
10
Santa Rita Slough at Highway 152 Deep Slough Green House Rd Bear Creek Bert Crane Rd
pH
MedianBasin Plan Objective (6.5-8.5)
R4-6
159
San Joaquin River Southeast Basin Dissolved Oxygen WY01-WY05
4
6
8
10
12
14
16
Apr
-01
Jul-0
1
Oct
-01
Jan-
02
Apr
-02
Jul-0
2
Oct
-02
Jan-
03
Apr
-03
Jul-0
3
Oct
-03
Jan-
04
Apr
-04
Jul-0
4
Oct
-04
Jan-
05
Apr
-05
Jul-0
5
Sample Date
DO
(mg/
L)
Deep Slough Green House Rd Bear Creek Bert Crane Rd Basin Plan Objective (7.0 mg/L) Santa Rita Slough at Highway 152
R4-7
160
San Joaquin River Southeast BasinDissolved Oxygen WY01- WY05
0
2
4
6
8
10
12
14
16
18
Santa Rita Slough at Highway 152 Deep Slough Green House Rd Bear Creek Bert Crane Rd
Dis
solv
ed O
xyge
n (m
g/L)
MedianBasin Plan Objective (7.0 mg/L)
R4-8
161
San Joaquin River Southeast Basin Turbidity WY02-WY04
0
50
100
150
200
250
300
350
400
450
500
Apr
-02
Jul-0
2
Oct
-02
Jan-
03
Apr
-03
Jul-0
3
Oct
-03
Jan-
04
Apr
-04
Jul-0
4
Sample Date
Turb
idity
(ntu
)
Deep Slough Green House Rd Bear Creek Bert Crane Rd
R4-9
162
San Joaquin River Southeast BasinTurbidity WY02- WY04
0
100
200
300
400
500
600
Deep Slough Green House Rd Bear Creek Bert Crane Rd
Turb
idity
(ntu
)
Median
R4-10
163
San Joaquin River Southeast Basin Total Suspended Solids WY01
0
50
100
150
200
250
Oct
-00
Jan-
01
Apr
-01
Jul-0
1
Oct
-01
Sample Date
TSS
(mg/
L)
Deep Slough Green House Rd Bear Creek Bert Crane Rd Santa Rita Slough at Highway 152
R4-11
164
San Joaquin River Southeast BasinTotal Suspended Solids WY01- WY05
0
50
100
150
200
250
SJR @Sack Dam SJR @ Lander SJR @ Fremont Ford
Tota
l Sus
pend
ed S
olid
s (m
g/L)
Median
R4-12
165
San Joaquin River Southeast Basin Total Organic Carbon WY01-WY05
0
5
10
15
20
25
30
Oct
-00
Jan-
01
Apr
-01
Jul-0
1
Oct
-01
Jan-
02
Apr
-02
Jul-0
2
Oct
-02
Jan-
03
Apr
-03
Jul-0
3
Oct
-03
Jan-
04
Apr
-04
Jul-0
4
Oct
-04
Jan-
05
Apr
-05
Jul-0
5
Sample Date
TOC
(mg/
L)
Deep Slough Green House Rd Bear Creek Bert Crane Rd Santa Rita Slough at Highway 152 Bay-Delta Authority Target (3 mg/L)Bay-Delta Authority Target (3 mg/L)
R4-13
166
San Joaquin River Southeast BasinTotal Organic Carbon WY01- WY05
0
5
10
15
20
25
30
Santa Rita Slough at Highway 152 Deep Slough Green House Rd Bear Creek Bert Crane Rd
Tota
l Org
anic
Car
bon
(mg/
L)
MedianBay-Delta Authority Target (3 mg/L)
R4-14
167
San Joaquin River Southeast Basin Total Coliform WY02-WY05
500
700
900
1100
1300
1500
1700
1900
2100
2300
2500
Jul-0
2
Oct
-02
Jan-
03
Apr
-03
Jul-0
3
Oct
-03
Jan-
04
Apr
-04
Jul-0
4
Oct
-04
Jan-
05
Apr
-05
Jul-0
5
Sample Date
Tota
l Col
iform
(MPN
/100
ml)
Deep Slough Green House Rd Bear Creek Bert Crane Rd
R4-15
168
San Joaquin River Southeast BasinTotal Coliform WY02- WY05
0
500
1000
1500
2000
2500
3000
Deep Slough Green House Rd Bear Creek Bert Crane Rd
Tota
l Col
iform
(MPN
/100
ml)
Median
R4-16
169
San Joaquin River Southeast Basin Escherichia coli WY02-WY05
0
500
1000
1500
2000
2500
3000
Jul-0
2
Oct
-02
Jan-
03
Apr
-03
Jul-0
3
Oct
-03
Jan-
04
Apr
-04
Jul-0
4
Oct
-04
Jan-
05
Apr
-05
Jul-0
5
Sample Date
E. c
oli
(MPN
/100
ml)
Deep Slough Green House Rd Bear Creek Bert Crane Rd USEPA Guideline - Designated beach area. (235 MPN/100 mL)
R4-17
170
San Joaquin River Southeast BasinEscherichia coli WY02-WY05
0
500
1000
1500
2000
2500
3000
Deep Slough Green House Rd Bear Creek Bert Crane Rd
E. c
oli
(MPN
/100
ml)
MedianUSEPA Guideline - Designated beach area. (235 MPN/100 mL)
R4-18
171
San Joaquin River Southeast Basin Nitrate WY01-WY02
0
5
10
15
20
25
30
35
40
45
50
Oct
-00
Jan-
01
Apr
-01
Jul-0
1
Oct
-01
Sample Date
Nitr
ate
(mg/
L)
Deep Slough Green House Rd Bear Creek Bert Crane Rd California Primary MCL (45mg/L) Santa Rita Slough at Highway 152
R4-19
172
San Joaquin River Southeast BasinNitrate WY01-WY04
0
5
10
15
20
25
30
35
40
45
50
Santa Rita Slough at Highway 152 Deep Slough Green House Rd Bear Creek Bert Crane Rd
Nitr
ate
(mg/
L)
MedianCalifornia Primary MCL (45mg/L)
R4-20
173
San Joaquin River Southeast Basin Total Kjeldahl Nitrogen WY01-WY03
0
1
2
3
4
5
6
7
8
9
10
Oct
-00
Jan-
01
Apr
-01
Jul-0
1
Oct
-01
Jan-
02
Apr
-02
Jul-0
2
Oct
-02
Jan-
03
Apr
-03
Sample Date
TKN
(mg/
L)
Deep Slough Green House Rd Bear Creek Bert Crane Rd Santa Rita Slough at Highway 152
R4-21
174
San Joaquin River Southeast BasinTotal Kjeldahl Nitrogen WY01-WY05
0
2
4
6
8
10
12
Santa Rita Slough at Highway 152 Deep Slough Green House Rd Bear Creek Bert Crane Rd
TKN
(mg/
L)
Median
R4-22
175
San Joaquin River Southeast Basin Phosphorus WY01-WY03
0.0
0.2
0.4
0.6
0.8
1.0
1.2
1.4
Oct
-00
Jan-
01
Apr
-01
Jul-0
1
Oct
-01
Jan-
02
Apr
-02
Jul-0
2
Oct
-02
Sample Date
Phos
phor
us (m
g/L)
Deep Slough Green House Rd Bear Creek Bert Crane Rd Santa Rita Slough at Highway 152
R4-23
176
San Joaquin River Southeast BasinPhosphorus WY01-WY05
0
0.2
0.4
0.6
0.8
1
1.2
1.4
Santa Rita Slough at Highway 152 Deep Slough Green House Rd Bear Creek Bert Crane Rd
Phos
phor
us (m
g/L)
Median
R4-24
177
San Joaquin River Southeast Basin Orthophosphate-P WY01-WY03
0.0
0.2
0.4
0.6
0.8
1.0
1.2
1.4
1.6
1.8
2.0
Oct
-00
Jan-
01
Apr
-01
Jul-0
1
Oct
-01
Jan-
02
Apr
-02
Jul-0
2
Oct
-02
Jan-
03
Apr
-03
Sample Date
Ort
hoph
osph
ate-
P (m
g/L)
Deep Slough Green House Rd Bear Creek Bert Crane Rd Santa Rita Slough at Highway 152
R4-25
178
San Joaquin River Southeast BasinOrthophosphate-P WY01-WY05
0
0.5
1
1.5
2
2.5
Santa Rita Slough at Highway 152 Deep Slough Green House Rd Bear Creek Bert Crane Rd
Ort
hoph
osph
ate-
P (m
g/L)
Median
R4-26
179
San Joaquin River Southeast Basin Potassium WY01-WY03
0
5
10
15
20
25
Oct
-00
Jan-
01
Apr
-01
Jul-0
1
Oct
-01
Jan-
02
Apr
-02
Jul-0
2
Oct
-02
Jan-
03
Sample Date
Pota
ssiu
m (m
g/L)
Deep Slough Green House Rd Bear Creek Bert Crane Rd Santa Rita Slough at Highway 152
R4-27
180
San Joaquin River Southeast BasinPotassium WY01-WY04
0
5
10
15
20
25
Santa Rita Slough at Highway 152 Deep Slough Green House Rd Bear Creek Bert Crane Rd
Pota
ssiu
m (m
g/L)
Median
R4-28
181
San Joaquin River Southeast Basin Biochemical Oxygen Demand 5-Day WY01-WY03
0
1
2
3
4
5
6
7
8
9
Oct
-00
Jan-
01
Apr
-01
Jul-0
1
Oct
-01
Jan-
02
Apr
-02
Jul-0
2
Oct
-02
Jan-
03
Apr
-03
Sample Dates
BO
D 5
-Day
(mg/
L)
Deep Slough Green House Rd Bear Creek Bert Crane Rd Santa Rita Slough at Highway 152
R4-29
182
San Joaquin River Southeast BasinBiological Oxygen Demand 5-Day WY01-WY03
0
1
2
3
4
5
6
7
8
9
Santa Rita Slough at Highway 152 Deep Slough Green House Rd Bear Creek Bert Crane Rd
BO
D- 5
(mg/
L)
Median
R4-30
183
San Joaquin River Southeast Basin Biochemical Oxygen Demand 10-Day WY01-WY03
0
2
4
6
8
10
12
14
16
18
Oct
-00
Jan-
01
Apr
-01
Jul-0
1
Oct
-01
Jan-
02
Apr
-02
Jul-0
2
Oct
-02
Jan-
03
Apr
-03
Sample Date
BO
D 1
0-D
ay (m
g/L)
Deep Slough Green House Rd Bear Creek Bert Crane Rd Santa Rita Slough at Highway 152
R4-31
184
San Joaquin River Southeast BasinBiological Oxygen Demand 10-Day WY01-WY03
0
2
4
6
8
10
12
14
16
18
Santa Rita Slough at Highway 152 Deep Slough Green House Rd Bear Creek Bert Crane Rd
BO
D- 1
0 (m
g/L)
Median
R4-32
185
San Joaquin River Southeast Basin Chloride WY01-WY03
0
50
100
150
200
250
Oct
-00
Jan-
01
Apr
-01
Jul-0
1
Oct
-01
Jan-
02
Apr
-02
Jul-0
2
Oct
-02
Jan-
03
Apr
-03
Sample Date
Chl
orid
e (m
g/L)
Deep Slough Green House Rd Bear Creek Bert Crane Rd California Secondary MCL (recommended level) (250 mg/L) Santa Rita Slough at Highway 152
R4-33
186
San Joaquin River Southeast BasinChloride WY01-WY03
0
50
100
150
200
250
Santa Rita Slough at Highway 152 Deep Slough Green House Rd Bear Creek Bert Crane Rd
Chl
orid
e (m
g/L)
MedianCalifornia Secondary MCL (recommended level) (250 mg/L)
R4-34
187
San Joaquin River Southeast Basin Sulfate WY01-WY03
0
50
100
150
200
250
300
Oct
-00
Jan-
01
Apr
-01
Jul-0
1
Oct
-01
Jan-
02
Apr
-02
Jul-0
2
Oct
-02
Jan-
03
Apr
-03
Sample Date
Sulfa
te (m
g/L)
Bear Creek Bert Crane Rd Bear Creek Bert Crane Rd California Secondary MCL (recommended level) (250 mg/L) Santa Rita Slough at Highway 152
R4-35
188
San Joaquin River Southeast BasinSulfate WY01-WY03
0
50
100
150
200
250
300
Santa Rita Slough at Highway 152 Deep Slough Green House Rd Bear Creek Bert Crane Rd
Sulfa
te (m
g/L)
MedianCalifornia Secondary MCL (recommended level) (250 mg/L)
R4-36
189
San Joaquin River Southeast Basin Calcium WY01-WY03
0
10
20
30
40
50
60
70
80
Oct
-00
Jan-
01
Apr
-01
Jul-0
1
Oct
-01
Jan-
02
Apr
-02
Jul-0
2
Oct
-02
Jan-
03
Apr
-03
Sample Dates
Cal
cium
(mg/
L)
Deep Slough Green House Rd Bear Creek Bert Crane Rd Santa Rita Slough at Highway 152
R4-37
190
San Joaquin River Southeast BasinCalcium WY01-WY03
0
10
20
30
40
50
60
70
80
Santa Rita Slough at Highway 152 Deep Slough Green House Rd Bear Creek Bert Crane Rd
Cal
cium
(mg/
L)
Median
R4-38
191
San Joaquin River Southeast Basin Magnesium WY01-WY03
0
5
10
15
20
25
30
Oct
-00
Jan-
01
Apr
-01
Jul-0
1
Oct
-01
Jan-
02
Apr
-02
Jul-0
2
Oct
-02
Jan-
03
Apr
-03
Sample Date
Mag
nesi
um (m
g/L)
Deep Slough Green House Rd Bear Creek Bert Crane Rd Santa Rita Slough at Highway 152
R4-39
192
San Joaquin River Southeast BasinMagnesium WY01-WY03
0
5
10
15
20
25
30
35
Santa Rita Slough at Highway 152 Deep Slough Green House Rd Bear Creek Bert Crane Rd
Mag
nesi
um (m
g/L)
Median
R4-40
193
San Joaquin River Southeast Basin Total Dissolved Solids WY01-WY03
0
100
200
300
400
500
600
Oct
-00
Jan-
01
Apr
-01
Jul-0
1
Oct
-01
Jan-
02
Apr
-02
Jul-0
2
Oct
-02
Sample Date
TDS
(mg/
L)
Deep Slough Green House Rd Bear Creek Bert Crane Rd California Secondary MCL (recommended level) (500 mg/L) Santa Rita Slough at Highway 152
R4-41
194
San Joaquin River Southeast BasinTotal Dissolved Solids WY01-WY03
0
100
200
300
400
500
600
Santa Rita Slough at Highway 152 Deep Slough Green House Rd Bear Creek Bert Crane Rd
TDS
(mg/
L)
MedianCalifornia Secondary MCL (recommended level) (500 mg/L)
R4-42
195
San Joaquin River Southeast Basin Carbonate WY01-WY03
0
10
20
30
40
50
60
Oct
-00
Jan-
01
Apr
-01
Jul-0
1
Oct
-01
Jan-
02
Apr
-02
Jul-0
2
Oct
-02
Sample Date
Car
bona
te (m
g/L)
Deep Slough Green House Rd Bear Creek Bert Crane Rd Santa Rita Slough at Highway 152
R4-43
196
San Joaquin River Southeast BasinCarbonate WY01-WY03
0
10
20
30
40
50
60
Santa Rita Slough at Highway 152 Deep Slough Green House Rd Bear Creek Bert Crane Rd
Car
bona
te (m
g/L)
Median
R4-44
197
San Joaquin River Southeast Basin Bicarbonate WY01-WY03
0
50
100
150
200
250
300
Oct
-00
Jan-
01
Apr
-01
Jul-0
1
Oct
-01
Jan-
02
Apr
-02
Jul-0
2
Oct
-02
Sample Date
Bic
arbo
nate
(mg/
L)
Deep Slough Green House Rd Bear Creek Bert Crane Rd Santa Rita Slough at Highway 152
R4-45
198
San Joaquin River Southeast BasinBicarbonate WY01-WY03
0
50
100
150
200
250
300
Santa Rita Slough at Highway 152 Deep Slough Green House Rd Bear Creek Bert Crane Rd
Bic
arbo
nate
(mg/
L)
Median
R4-46
199
San Joaquin River Southeast Basin Total Alkalinity WY01-WY03
0
50
100
150
200
250
300
Oct
-00
Jan-
01
Apr
-01
Jul-0
1
Oct
-01
Jan-
02
Apr
-02
Jul-0
2
Oct
-02
Sample Date
Tota
l Alk
alin
ity (m
g/L)
Deep Slough Green House Rd Bear Creek Bert Crane Rd Santa Rita Slough at Highway 152
R4-47
200
San Joaquin River Southeast BasinTotal Alkalinity WY01-WY03
0
50
100
150
200
250
300
Santa Rita Slough at Highway 152 Deep Slough Green House Rd Bear Creek Bert Crane Rd
Tota
l Alk
alin
ity (m
g/L)
Median
R4-48
201
San Joaquin River Southeast Basin Sodium WY01-WY03
0
10
20
30
40
50
60
70
80
90
100
Oct
-00
Jan-
01
Apr
-01
Jul-0
1
Oct
-01
Jan-
02
Apr
-02
Jul-0
2
Oct
-02
Sample Date
Sodi
um (m
g/L)
Deep Slough Green House Rd Bear Creek Bert Crane Rd Water Quality for Agriculture(Ayers & Westcot) (69 mg/L) Santa Rita Slough at Highway 152
R4-49
202
San Joaquin River Southeast BasinSodium WY01-WY03
0
10
20
30
40
50
60
70
80
90
100
Santa Rita Slough at Highway 152 Deep Slough Green House Rd Bear Creek Bert Crane Rd
Sodi
um (m
g/L)
MedianWater Quality for Agriculture (Ayers & Westcot) (69 mg/L)
R4-50
203
San Joaquin River Grassland Basin Temperature WY01-WY05
5
10
15
20
25
30
35
Oct
-00
Jan-
01
Apr
-01
Jul-0
1
Oct
-01
Jan-
02
Apr
-02
Jul-0
2
Oct
-02
Jan-
03
Apr
-03
Jul-0
3
Oct
-03
Jan-
04
Apr
-04
Jul-0
4
Oct
-04
Jan-
05
Apr
-05
Jul-0
5
Sample Date
Tem
pera
ture
(ºC
)
Salt Slough @Lander/Hwy 165 Mud Slough (n) (upstream) @ San Luis Drain Discharge from SLD Mud Slough (n) (downstream) @ San Luis Drain Bay-Delta Authority Target, SJR @ Vernalis (Apr 1-Jun 30 & Sept 1- Nov 30, 20ºC)
R5-1
204
San Joaquin River Grassland BasinTemperature WY01- WY05
0
5
10
15
20
25
30
35
Salt Slough @Lander/Hwy 165 Mud Slough (n) (upstream) @SLD
Discharge from SLD Mud Slough (n) (downstream)@ SLD
Tem
pera
ture
(ºC
)
Median
R5-2
205
San Joaquin River Grassland Basin Specific Conductivity WY01-WY05
0
1000
2000
3000
4000
5000
6000
Oct
-00
Jan-
01
Apr
-01
Jul-0
1
Oct
-01
Jan-
02
Apr
-02
Jul-0
2
Oct
-02
Jan-
03
Apr
-03
Jul-0
3
Oct
-03
Jan-
04
Apr
-04
Jul-0
4
Oct
-04
Jan-
05
Apr
-05
Jul-0
5
Sample Date
SC (μ
mho
s/cm
)
Salt Slough @Lander/Hwy 165 Mud Slough (n) (upstream) @ San Luis Drain Discharge from SLD Mud Slough (n) (downstream) @ San Luis Drain Basin Plan Objective (Apr 1-Aug 31, 700 μmhos/cm; Sep 1-Mar 31,1000 μmhos/cm)
R5-3
206
San Joaquin River Grassland BasinSpecific Conductivity WY01- WY05
0
1000
2000
3000
4000
5000
6000
Salt Slough @Lander/Hwy 165 Mud Slough (n) (upstream) @SLD
Discharge from SLD Mud Slough (n) (downstream)@ SLD
Spec
ific
Con
duct
ivity
(μm
hos/
cm)
Median
R5-4
207
San Joaquin River Grassland Basin pH WY01-WY05
5.5
6.0
6.5
7.0
7.5
8.0
8.5
9.0
Oct
-00
Jan-
01
Apr
-01
Jul-0
1
Oct
-01
Jan-
02
Apr
-02
Jul-0
2
Oct
-02
Jan-
03
Apr
-03
Jul-0
3
Oct
-03
Jan-
04
Apr
-04
Jul-0
4
Oct
-04
Jan-
05
Apr
-05
Jul-0
5
Sample Date
pH
Salt Slough @Lander/Hwy 165 Mud Slough (n) (upstream) @ San Luis Drain Discharge from SLD Mud Slough (n) (downstream) @ San Luis Drain Basin Plan Objective (6.5-8.5)
R5-5
208
San Joaquin River Grassland BasinpH WY01- WY05
6
6.5
7
7.5
8
8.5
9
9.5
10
Salt Slough @Lander/Hwy 165 Mud Slough (n) (upstream) @SLD
Discharge from SLD Mud Slough (n) (downstream)@ SLD
pH
MedianBasin Plan Objective (6.5-8.5)
R5-6
209
San Joaquin River Grassland Basin Dissolved Oxygen WY01-WY05
0
5
10
15
20
25
30
Apr
-01
Jul-0
1
Oct
-01
Jan-
02
Apr
-02
Jul-0
2
Oct
-02
Jan-
03
Apr
-03
Jul-0
3
Oct
-03
Jan-
04
Apr
-04
Jul-0
4
Oct
-04
Jan-
05
Apr
-05
Jul-0
5
Sample Date
DO
(mg/
L)
Salt Slough @Lander/Hwy 165 Mud Slough (n) (upstream) @ San Luis Drain Discharge from SLD Mud Slough (n) (downstream) @ San Luis Drain Basin Plan Objective (7.0 mg/L)
R5-7
210
San Joaquin River Grassland BasinDissolved Oxygen WY01- WY05
0
5
10
15
20
25
30
35
Salt Slough @Lander/Hwy 165 Mud Slough (n) (upstream) @SLD
Discharge from SLD Mud Slough (n) (downstream)@ SLD
Dis
solv
ed O
xyge
n (m
g/L)
MedianBasin Plan Objective (7.0 mg/L)
R5-8
211
San Joaquin River Grassland Basin Turbidity WY01-WY05
0
100
200
300
400
500
600
700
800
900
Apr
-02
Jul-0
2
Oct
-02
Jan-
03
Apr
-03
Jul-0
3
Oct
-03
Jan-
04
Apr
-04
Sample Date
Turb
idity
(ntu
)
Salt Slough @Lander/Hwy 165 Mud Slough (n) (upstream) @ San Luis Drain Discharge from SLD Mud Slough (n) (downstream) @ San Luis Drain
R5-9
212
San Joaquin River Grassland BasinTurbidity WY02- WY04
0
50
100
150
200
250
300
350
Salt Slough @Lander/Hwy 165 Mud Slough (n) (upstream) @SLD
Discharge from SLD Mud Slough (n) (downstream)@ SLD
Turb
idity
(ntu
)
Median
R5-10
213
San Joaquin River Grassland Basin Total Suspended Solids WY01-WY05
0
20
40
60
80
100
120
140
160
180
Oct
-00
Jan-
01
Apr
-01
Jul-0
1
Oct
-01
Jan-
02
Apr
-02
Jul-0
2
Oct
-02
Jan-
03
Apr
-03
Jul-0
3
Oct
-03
Jan-
04
Apr
-04
Jul-0
4
Oct
-04
Jan-
05
Apr
-05
Jul-0
5
Sample Date
TSS
(mg/
L)
Salt Slough @Lander/Hwy 165 Mud Slough (n) (upstream) @ San Luis Drain Discharge from SLD Mud Slough (n) (downstream) @ San Luis Drain
R5-11
214
San Joaquin River Grassland BasinTotal Suspended Solids WY01- WY05
0
20
40
60
80
100
120
140
160
180
Salt Slough @Lander/Hwy 165 Mud Slough (n) (upstream) @SLD
Discharge from SLD Mud Slough (n) (downstream)@ SLD
Tota
l Sus
pend
ed S
olid
s (m
g/L)
Median
R5-12
215
San Joaquin River Grassland Basin Total Organic Carbon WY01-WY05
0
5
10
15
20
25
30
35
Oct
-00
Jan-
01
Apr
-01
Jul-0
1
Oct
-01
Jan-
02
Apr
-02
Jul-0
2
Oct
-02
Jan-
03
Apr
-03
Jul-0
3
Oct
-03
Jan-
04
Apr
-04
Jul-0
4
Oct
-04
Jan-
05
Apr
-05
Jul-0
5
Sample Date
TOC
(mg/
L)
Mud Slough (n) (upstream) @ San Luis Drain Mud Slough (n) (upstream) @ San Luis Drain Discharge from SLD Mud Slough (n) (downstream) @ San Luis Drain Bay-Delta Authority Target (3 mg/L)
R5-13
216
San Joaquin River Grassland BasinTotal Organic Carbon WY01- WY05
0
5
10
15
20
25
30
35
Salt Slough @Lander/Hwy 165 Mud Slough (n) (upstream) @SLD
Discharge from SLD Mud Slough (n) (downstream)@ SLD
Tota
l Org
anic
Car
bon
(mg/
L)
MedianBay-Delta Authority Target (3 mg/L)
R5-14
217
San Joaquin River Grassland Basin Total Coliform WY02-WY05
0
500
1000
1500
2000
2500
Jul-0
2
Oct
-02
Jan-
03
Apr
-03
Jul-0
3
Oct
-03
Jan-
04
Apr
-04
Jul-0
4
Oct
-04
Jan-
05
Apr
-05
Jul-0
5
Sample Date
Tota
l Col
iform
(MPN
/100
ml)
Salt Slough @Lander/Hwy 165 Mud Slough (n) (upstream) @ San Luis Drain Discharge from SLD Mud Slough (n) (downstream) @ San Luis Drain
R5-15
218
San Joaquin River Grassland BasinTotal Coliform WY02- WY05
0
500
1000
1500
2000
2500
3000
Salt Slough @Lander/Hwy 165 Mud Slough (n) (upstream) @SLD
Discharge from SLD Mud Slough (n) (downstream)@ SLD
Tota
l Col
iform
(MPN
/100
ml)
Median
R5-16
219
San Joaquin River Grassland Basin Echerichia coli WY02-WY05
0
200
400
600
800
1000
1200
1400
Oct
-00
Jan-
01
Apr
-01
Jul-0
1
Oct
-01
Jan-
02
Apr
-02
Jul-0
2
Oct
-02
Jan-
03
Apr
-03
Jul-0
3
Oct
-03
Jan-
04
Apr
-04
Jul-0
4
Oct
-04
Jan-
05
Apr
-05
Jul-0
5
Sample Date
E. c
oli
(MPN
/100
ml)
Salt Slough @Lander/Hwy 165 Mud Slough (n) (upstream) @ San Luis Drain Discharge from SLD Mud Slough (n) (downstream) @ San Luis Drain USEPA Guideline - Designated beach area. (235 MPN/100 mL)
E. coli
2100
2300
2500
Apr
-03
Jun-
03
Sample Date
E. c
oli
(MPN
/100
ml)
R5-17
220
San Joaquin River Grassland BasinEscherichia coli WY02-WY05
0
500
1000
1500
2000
2500
3000
Salt Slough @Lander/Hwy 165 Mud Slough (n) (upstream) @SLD
Discharge from SLD Mud Slough (n) (downstream)@ SLD
E. c
oli
(MPN
/100
ml)
MedianUSEPA Guideline - Designated beach area. (235 MPN/100
R5-18
221
San Joaquin River Grassland BasinNitrate WY01-WY04
0
20
40
60
80
100
120
Oct
-00
Jan-
01
Apr
-01
Jul-0
1
Oct
-01
Jan-
02
Apr
-02
Jul-0
2
Oct
-02
Jan-
03
Apr
-03
Jul-0
3
Oct
-03
Sample Date
Nitr
ate
(mg/
L)
Salt Slough @Lander/Hwy 165 Mud Slough (n) (upstream) @ San Luis Drain Discharge from SLD Mud Slough (n) (downstream) @ San Luis Drain California Primary MCL (45mg/L)
R5-19
222
San Joaquin River Grassland BasinNitrate WY01-WY04
0
20
40
60
80
100
120
Salt Slough @Lander/Hwy 165 Mud Slough (n) (upstream) @SLD
Discharge from SLD Mud Slough (n) (downstream)@ SLD
Nitr
ate
(mg/
L)
MedianCalifornia Primary MCL (45mg/L)
R5-20
223
San Joaquin River Grassland Basin Nitrate-N WY04-WY05
0
5
10
15
20
25
30
35
Jan-
04
Apr
-04
Jul-0
4
Oct
-04
Jan-
05
Apr
-05
Jul-0
5
Sample Date
Nitr
ate-
N (m
g/L)
Mud Slough (n) (upstream) @ San Luis Drain Discharge from SLD Mud Slough (n) (downstream) @ San Luis Drain California Primary MCL (10mg/L)
R5-21
224
San Joaquin River Grassland Basin Total Kjeldahl Nitrogen WY01-WY05
0.0
0.5
1.0
1.5
2.0
2.5
3.0
3.5
4.0
4.5
5.0
Oct
-00
Jan-
01
Apr
-01
Jul-0
1
Oct
-01
Jan-
02
Apr
-02
Jul-0
2
Oct
-02
Jan-
03
Apr
-03
Jul-0
3
Oct
-03
Jan-
04
Apr
-04
Jul-0
4
Oct
-04
Jan-
05
Apr
-05
Jul-0
5
Sample Date
TKN
(mg/
L)
Salt Slough @Lander/Hwy 165 Mud Slough (n) (upstream) @ San Luis Drain Discharge from SLD Mud Slough (n) (downstream) @ San Luis Drain
R5-22
225
San Joaquin River Grassland BasinTotal Kjeldahl Nitrogen WY01-WY05
0
0.5
1
1.5
2
2.5
3
3.5
4
4.5
5
Salt Slough @Lander/Hwy 165 Mud Slough (n) (upstream) @SLD
Discharge from SLD Mud Slough (n) (downstream)@ SLD
TKN
(mg/
L)
Median
R5-23
226
San Joaquin River Grassland Basin Ammonia-N WY01-WY05
0.0
0.1
0.2
0.3
0.4
0.5
0.6
0.7
0.8
0.9
1.0
Oct
-00
Jan-
01
Apr
-01
Jul-0
1
Oct
-01
Jan-
02
Apr
-02
Jul-0
2
Oct
-02
Jan-
03
Apr
-03
Jul-0
3
Oct
-03
Jan-
04
Apr
-04
Jul-0
4
Oct
-04
Jan-
05
Apr
-05
Jul-0
5
Sample Date
Am
mon
ia-N
(mg/
L)
Mud Slough (n) (upstream) @ San Luis Drain Discharge from SLD Mud Slough (n) (downstream) @ San Luis Drain
R5-24
227
San Joaquin River Grassland BasinAmmonia-N WY04-WY05
0
0.2
0.4
0.6
0.8
1
1.2
Mud Slough (n) (upstream) @ SLD Discharge from SLD Mud Slough (n) (downstream) @ SLD
Am
mon
ia-N
(mg/
L)
Median
R5-25
228
San Joaquin River Grassland Basin Phosphorus WY01-WY05
0.0
0.1
0.2
0.3
0.4
0.5
0.6
0.7
0.8
0.9
Oct
-00
Jan-
01
Apr
-01
Jul-0
1
Oct
-01
Jan-
02
Apr
-02
Jul-0
2
Oct
-02
Jan-
03
Apr
-03
Jul-0
3
Oct
-03
Jan-
04
Apr
-04
Jul-0
4
Oct
-04
Jan-
05
Apr
-05
Jul-0
5
Sample Date
Phos
phor
us (m
g/L)
Salt Slough @Lander/Hwy 165 Mud Slough (n) (upstream) @ San Luis Drain Discharge from SLD Mud Slough (n) (downstream) @ San Luis Drain
R5-26
229
San Joaquin River Grassland BasinPhosphorus WY01-WY05
0
0.1
0.2
0.3
0.4
0.5
0.6
0.7
0.8
0.9
Salt Slough @Lander/Hwy 165 Mud Slough (n) (upstream) @SLD
Discharge from SLD Mud Slough (n) (downstream)@ SLD
Phos
phor
us (m
g/L)
Median
R5-27
230
San Joaquin River Grassland Basin Orthophosphate-P WY01-WY05
0.0
0.1
0.2
0.3
0.4
0.5
0.6
0.7
Oct
-00
Jan-
01
Apr
-01
Jul-0
1
Oct
-01
Jan-
02
Apr
-02
Jul-0
2
Oct
-02
Jan-
03
Apr
-03
Jul-0
3
Oct
-03
Jan-
04
Apr
-04
Jul-0
4
Oct
-04
Jan-
05
Apr
-05
Jul-0
5
Sample Date
Ort
ho-P
(mg/
L)
Salt Slough @Lander/Hwy 165 Mud Slough (n) (upstream) @ San Luis Drain Discharge from SLD Mud Slough (n) (downstream) @ San Luis Drain
R5-28
231
San Joaquin River Grassland BasinOrthophosphate-P WY01-WY05
0
0.1
0.2
0.3
0.4
0.5
0.6
0.7
Salt Slough @Lander/Hwy 165 Mud Slough (n) (upstream) @SLD
Discharge from SLD Mud Slough (n) (downstream)@ SLD
Ort
hoph
osph
ate-
P (m
g/L)
Median
R5-29
232
San Joaquin River Grassland Basin Potassium WY01-WY04
0
2
4
6
8
10
12
14
16
Oct
-00
Jan-
01
Apr
-01
Jul-0
1
Oct
-01
Jan-
02
Apr
-02
Jul-0
2
Oct
-02
Jan-
03
Apr
-03
Jul-0
3
Oct
-03
Jan-
04
Sample Date
Pota
ssiu
m (m
g/L)
Salt Slough @Lander/Hwy 165 Mud Slough (n) (upstream) @ San Luis Drain Discharge from SLD Mud Slough (n) (downstream) @ San Luis Drain
R5-30
233
San Joaquin River Grassland BasinPotassium WY01-WY04
0
2
4
6
8
10
12
14
16
Salt Slough @Lander/Hwy 165 Mud Slough (n) (upstream) @SLD
Discharge from SLD Mud Slough (n) (downstream)@ SLD
Pota
ssiu
m (m
g/L)
Median
R5-31
234
San Joaquin River Grassland Basin Biochemical Oxygen Demand 5-Day WY01-WY03
0
1
2
3
4
5
6
7
8
Oct
-00
Jan-
01
Apr
-01
Jul-0
1
Oct
-01
Jan-
02
Apr
-02
Jul-0
2
Oct
-02
Jan-
03
Sample Date
BO
D 5
-Day
(mg/
L)
Salt Slough @Lander/Hwy 165 Mud Slough (n) (upstream) @ San Luis Drain Discharge from SLD Mud Slough (n) (downstream) @ San Luis Drain
R5-32
235
San Joaquin River Grassland BasinBiological Oxygen Demand 5-Day WY01-WY03
0
1
2
3
4
5
6
7
8
Salt Slough @Lander/Hwy 165 Mud Slough (n) (upstream) @SLD
Discharge from SLD Mud Slough (n) (downstream)@ SLD
BO
D- 5
(mg/
L)
Median
R5-33
236
San Joaquin River Grassland Basin Biochemical Oxygen Demand 10-Day WY01-WY03
0
2
4
6
8
10
12
14
Oct
-00
Jan-
01
Apr
-01
Jul-0
1
Oct
-01
Jan-
02
Apr
-02
Jul-0
2
Oct
-02
Jan-
03
Sample Date
BO
D 1
0-D
ay (m
g/L)
Salt Slough @Lander/Hwy 165 Mud Slough (n) (upstream) @ San Luis Drain Discharge from SLD Mud Slough (n) (downstream) @ San Luis Drain
R5-34
237
San Joaquin River Grassland BasinBiological Oxygen Demand 10-Day WY01-WY03
0
2
4
6
8
10
12
14
Salt Slough @Lander/Hwy 165 Mud Slough (n) (upstream) @SLD
Discharge from SLD Mud Slough (n) (downstream)@ SLD
BO
D- 1
0 (m
g/L)
Median
R5-35
238
San Joaquin River Grassland Basin Chloride WY01-WY03
0
100
200
300
400
500
600
700
Oct
-00
Jan-
01
Apr
-01
Jul-0
1
Oct
-01
Jan-
02
Apr
-02
Jul-0
2
Oct
-02
Jan-
03
Apr
-03
Sample Date
Chl
orid
e (m
g/L)
Salt Slough @Lander/Hwy 165 Mud Slough (n) (upstream) @ San Luis Drain Discharge from SLD Mud Slough (n) (downstream) @ San Luis Drain California Secondary MCL (recommended level) (250 mg/L)
R5-36
239
San Joaquin River Grassland BasinChloride WY01-WY03
0
100
200
300
400
500
600
700
800
Salt Slough @Lander/Hwy 165 Mud Slough (n) (upstream) @SLD
Discharge from SLD Mud Slough (n) (downstream)@ SLD
Chl
orid
e (m
g/L)
Median
R5-37
240
San Joaquin River Grassland Basin Sulfate WY01-WY03
0
200
400
600
800
1000
1200
1400
1600
1800
2000
Oct
-00
Jan-
01
Apr
-01
Jul-0
1
Oct
-01
Jan-
02
Apr
-02
Jul-0
2
Oct
-02
Jan-
03
Apr
-03
Sample Date
Sulfa
te (m
g/L)
Salt Slough @Lander/Hwy 165 Mud Slough (n) (upstream) @ San Luis Drain Discharge from SLD Mud Slough (n) (downstream) @ San Luis Drain California Secondary MCL (recommended level) (250 mg/L)
R5-38
241
San Joaquin River Grassland BasinSulfate WY01-WY03
0
200
400
600
800
1000
1200
1400
1600
1800
2000
Salt Slough @Lander/Hwy 165 Mud Slough (n) (upstream) @SLD
Discharge from SLD Mud Slough (n) (downstream)@ SLD
Sulfa
te (m
g/L)
MedianCalifornia Secondary MCL (recommended level) (250 mg/L)
R5-39
242
San Joaquin River Grassland Basin Calcium WY01-WY03
0
50
100
150
200
250
300
350
400
Oct
-00
Jan-
01
Apr
-01
Jul-0
1
Oct
-01
Jan-
02
Apr
-02
Jul-0
2
Oct
-02
Jan-
03
Apr
-03
Jul-0
3
Oct
-03
Sample Date
Cal
cium
(mg/
L)
Salt Slough @Lander/Hwy 165 Mud Slough (n) (upstream) @ San Luis Drain Discharge from SLD Mud Slough (n) (downstream) @ San Luis Drain
R5-40
243
San Joaquin River Grassland BasinCalcium WY01-WY03
0
50
100
150
200
250
300
350
400
Salt Slough @Lander/Hwy 165 Mud Slough (n) (upstream) @SLD
Discharge from SLD Mud Slough (n) (downstream)@ SLD
Cal
cium
(mg/
L)
Median
R5-41
244
San Joaquin River Grassland BasinMagnesium WY01-WY03
0
20
40
60
80
100
120
Oct
-00
Jan-
01
Apr
-01
Jul-0
1
Oct
-01
Jan-
02
Apr
-02
Jul-0
2
Oct
-02
Jan-
03
Apr
-03
Sample Date
Mag
nesi
um (m
g/L)
Salt Slough @Lander/Hwy 165 Mud Slough (n) (upstream) @ San Luis Drain Discharge from SLD Mud Slough (n) (downstream) @ San Luis Drain
R5-42
245
San Joaquin River Grassland BasinMagnesium WY01-WY03
0
20
40
60
80
100
120
Salt Slough @Lander/Hwy 165 Mud Slough (n) (upstream) @SLD
Discharge from SLD Mud Slough (n) (downstream)@ SLD
Mag
nesi
um (m
g/L)
Median
R5-43
246
San Joaquin River Grassland Basin Total Dissolved Solids WY01-WY03
0
500
1000
1500
2000
2500
3000
3500
4000
4500
Oct
-00
Jan-
01
Apr
-01
Jul-0
1
Oct
-01
Jan-
02
Apr
-02
Jul-0
2
Oct
-02
Sample Date
TDS
(mg/
L)
Salt Slough @Lander/Hwy 165 Mud Slough (n) (upstream) @ San Luis Drain Discharge from SLD Mud Slough (n) (downstream) @ San Luis Drain California Secondary MCL (recommended level) (500 mg/L)
R5-44
247
San Joaquin River Grassland BasinTotal Dissolved Solids WY01-WY03
0
500
1000
1500
2000
2500
3000
3500
4000
4500
5000
Salt Slough @Lander/Hwy 165 Mud Slough (n) (upstream) @SLD
Discharge from SLD Mud Slough (n) (downstream)@ SLD
TDS
(mg/
L)
MedianCalifornia Secondary MCL (recommended level) (500 mg/L)
R5-45
248
San Joaquin River Grassland Basin Carbonate WY01-WY03
0
5
10
15
20
25
Oct
-00
Jan-
01
Apr
-01
Jul-0
1
Oct
-01
Jan-
02
Apr
-02
Jul-0
2
Oct
-02
Jan-
03
Sample Date
Car
bona
te (m
g/L)
Salt Slough @Lander/Hwy 165 Mud Slough (n) (upstream) @ San Luis Drain Discharge from SLD Mud Slough (n) (downstream) @ San Luis Drain
R5-46
249
San Joaquin River Grassland BasinCarbonate WY01-WY03
0
5
10
15
20
25
Salt Slough @Lander/Hwy 165 Mud Slough (n) (upstream) @SLD
Discharge from SLD Mud Slough (n) (downstream)@ SLD
Car
bona
te (m
g/L)
Median
R5-47
250
San Joaquin River Grassland Basin Bicarbonate WY01-WY03
50
100
150
200
250
300
350
400
Oct
-00
Jan-
01
Apr
-01
Jul-0
1
Oct
-01
Jan-
02
Apr
-02
Jul-0
2
Oct
-02
Sample Date
Bic
arbo
nate
(mg/
L)
Salt Slough @Lander/Hwy 165 Mud Slough (n) (upstream) @ San Luis Drain Discharge from SLD Mud Slough (n) (downstream) @ San Luis Drain
R5-48
251
San Joaquin River Grassland BasinBicarbonate WY01-WY03
0
50
100
150
200
250
300
350
400
450
Salt Slough @Lander/Hwy 165 Mud Slough (n) (upstream) @SLD
Discharge from SLD Mud Slough (n) (downstream)@ SLD
Bic
arbo
nate
(mg/
L)
Median
R5-49
252
San Joaquin River Grassland Basin Total Alkalinity WY01-WY03
50
100
150
200
250
300
350
Oct
-00
Jan-
01
Apr
-01
Jul-0
1
Oct
-01
Jan-
02
Apr
-02
Jul-0
2
Oct
-02
Sample Date
Tota
l Alk
alin
ity (m
g/L)
Salt Slough @Lander/Hwy 165 Mud Slough (n) (upstream) @ San Luis Drain Discharge from SLD Mud Slough (n) (downstream) @ San Luis Drain
R5-50
253
San Joaquin River Grassland BasinTotal Alkalinity WY01-WY03
0
50
100
150
200
250
300
350
Salt Slough @Lander/Hwy 165 Mud Slough (n) (upstream) @SLD
Discharge from SLD Mud Slough (n) (downstream)@ SLD
Tota
l Alk
alin
ity (m
g/L)
Median
R5-51
254
San Joaquin River Grassland Basin Sodium WY01-WY03
0
100
200
300
400
500
600
700
800
Oct
-00
Jan-
01
Apr
-01
Jul-0
1
Oct
-01
Jan-
02
Apr
-02
Jul-0
2
Oct
-02
Sample Date
Sodi
um (m
g/L)
Salt Slough @Lander/Hwy 165 Mud Slough (n) (upstream) @ San Luis Drain Discharge from SLD Mud Slough (n) (downstream) @ San Luis Drain Water Quality for Agriculture(Ayers & Westcot) (69 mg/L)
R5-52
255
San Joaquin River Grassland BasinSodium WY01-WY03
0
100
200
300
400
500
600
700
800
900
Salt Slough @Lander/Hwy 165 Mud Slough (n) (upstream) @SLD
Discharge from SLD Mud Slough (n) (downstream)@ SLD
Sodi
um (m
g/L)
MedianWater Quality for Agriculture (Ayers & Westcot) (69 mg/L)
R5-53
256
San Joaquin River West Side Basin Temperature WY01-WY05
0
5
10
15
20
25
30
35
Oct
-00
Jan-
01
Apr
-01
Jul-0
1
Oct
-01
Jan-
02
Apr
-02
Jul-0
2
Oct
-02
Jan-
03
Apr
-03
Jul-0
3
Oct
-03
Jan-
04
Apr
-04
Jul-0
4
Oct
-04
Jan-
05
Apr
-05
Jul-0
5
Sample Date
Tem
pera
ture
(ºC
)
Orestimba Creek @ River Rd. Solado Creek @ Hwy 33 Del Puerto Creek @Vineyard Grayson Drain Ingram Creek @River Rd. Hospital Creek @River Rd. Bay-Delta Authority Target, SJR @ Vernalis (Apr 1-Jun 30 & Sept 1- Nov 30, 20ºC)
R6-1
257
San Joaquin River Westside BasinTemperature WY01- WY05
0
5
10
15
20
25
30
35
Orestimba Creek @River Rd.
Solado Creek @ Hwy33
Del Puerto Creek@Vineyard
Grayson Drain Ingram Creek@River Rd.
Hospital Creek@River Rd.
Tem
pera
ture
(ºC
)
Median
R6-2
258
San Joaquin River West Side Basin Specific Conductivity WY01-WY05
0
500
1000
1500
2000
2500
Oct
-00
Jan-
01
Apr
-01
Jul-0
1
Oct
-01
Jan-
02
Apr
-02
Jul-0
2
Oct
-02
Jan-
03
Apr
-03
Jul-0
3
Oct
-03
Jan-
04
Apr
-04
Jul-0
4
Oct
-04
Jan-
05
Apr
-05
Jul-0
5
Sample Date
SC (μ
mho
s/cm
)
Orestimba Creek @ River Rd. Solado Creek @ Hwy 33 Del Puerto Creek @Vineyard Grayson Drain Ingram Creek @River Rd. H it l C k @Ri Rd
Solado Creek @ Hwy 33
38003900400041004200
Jan- 05 M
ar-
05
Sample Date
EC
(μm
hos/
cm)
R6-3
259
San Joaquin River Westside BasinSpecific Conductivity WY01- WY05
0
500
1000
1500
2000
2500
3000
3500
4000
4500
Orestimba Creek @River Rd.
Solado Creek @Hwy 33
Del Puerto Creek@Vineyard
Grayson Drain Ingram Creek@River Rd.
Hospital Creek@River Rd.
Spec
ific
Con
duct
ivity
(μm
hos/
cm)
Median
R6-4
260
San Joaquin River Northwest Basin pH WY01-WY05
6.0
6.5
7.0
7.5
8.0
8.5
9.0
Oct
-00
Jan-
01
Apr
-01
Jul-0
1
Oct
-01
Jan-
02
Apr
-02
Jul-0
2
Oct
-02
Jan-
03
Apr
-03
Jul-0
3
Oct
-03
Jan-
04
Apr
-04
Jul-0
4
Oct
-04
Jan-
05
Apr
-05
Jul-0
5
Sample Date
pH
Orestimba Creek @ River Rd. Solado Creek @ Hwy 33 Del Puerto Creek @Vineyard Grayson Drain Ingram Creek @River Rd. Hospital Creek @River Rd. Basin Plan Objective (6.5-8.5) Series2
R6-5
261
San Joaquin River Westside BasinpH WY01- WY05
6
6.5
7
7.5
8
8.5
9
9.5
10
Orestimba Creek @River Rd.
Solado Creek @Hwy 33
Del Puerto Creek@Vineyard
Grayson Drain Ingram Creek@River Rd.
Hospital Creek@River Rd.
pH
MedianBasin Plan Objective (6.5-8.5)
R6-6
262
San Joaquin River West Side Basin Dissolved Oxygen WY01-WY05
2
4
6
8
10
12
14
16
18
Apr
-01
Jul-0
1
Oct
-01
Jan-
02
Apr
-02
Jul-0
2
Oct
-02
Jan-
03
Apr
-03
Jul-0
3
Oct
-03
Jan-
04
Apr
-04
Jul-0
4
Oct
-04
Jan-
05
Apr
-05
Jul-0
5
Sample Date
DO
(mg/
L)
Orestimba Creek @ River Rd. Solado Creek @ Hwy 33 Del Puerto Creek @Vineyard Grayson Drain Ingram Creek @River Rd. Hospital Creek @River Rd. Basin Plan Objective (7.0 mg/L)
R6-7
263
San Joaquin River Westside BasinDissolved Oxygen WY01- WY05
0
2
4
6
8
10
12
14
16
18
20
Orestimba Creek @River Rd.
Solado Creek @ Hwy33
Del Puerto Creek@Vineyard
Grayson Drain Ingram Creek@River Rd.
Hospital Creek@River Rd.
Dis
solv
ed O
xyge
n (m
g/L)
MedianBasin Plan Objective (7.0 mg/L)
R6-8
264
San Joaquin River West Side Basin Turbidity WY02-WY04
0
200
400
600
800
1000
1200
1400
1600
1800
2000
Jul-0
2
Oct
-02
Jan-
03
Apr
-03
Jul-0
3
Oct
-03
Jan-
04
Apr
-04
Sample Date
Turb
idity
(ntu
)
Orestimba Creek @ River Rd. Solado Creek @ Hwy 33 Del Puerto Creek @Vineyard Grayson Drain Ingram Creek @River Rd. Hospital Creek @River Rd.
R6-9
265
San Joaquin River Westside BasinTurbidity WY02- WY04
0
500
1000
1500
2000
2500
Orestimba Creek @River Rd.
Solado Creek @Hwy 33
Del Puerto Creek@Vineyard
Grayson Drain Ingram Creek@River Rd.
Hospital Creek@River Rd.
Turb
idity
(ntu
)
Median
R6-10
266
San Joaquin River West Side Basin Total Suspended Solids WY01-WY05
0
1000
2000
3000
4000
5000
6000
7000
Oct
-00
Jan-
01
Apr
-01
Jul-0
1
Oct
-01
Jan-
02
Apr
-02
Jul-0
2
Oct
-02
Jan-
03
Apr
-03
Jul-0
3
Oct
-03
Jan-
04
Apr
-04
Jul-0
4
Oct
-04
Jan-
05
Apr
-05
Jul-0
5
Sample Date
TSS
(mg/
L)
Orestimba Creek @ River Rd. Solado Creek @ Hwy 33 Del Puerto Creek @Vineyard Grayson Drain Ingram Creek @River Rd. Hospital Creek @River Rd.
Grayson Drain
27000
28000
29000
Jul-
05
Sep
-05
Sample Date
TSS
(mg/
L)
R6-11
267
San Joaquin River Westside BasinTotal Suspended Solids WY01- WY05
0
5000
10000
15000
20000
25000
30000
Orestimba Creek @River Rd.
Solado Creek @Hwy 33
Del Puerto Creek@Vineyard
Grayson Drain Ingram Creek@River Rd.
Hospital Creek@River Rd.
Tota
l Sus
pend
ed S
olid
s (m
g/L)
Median
R6-12
268
San Joaquin River West Side Basin Total Organic Carbon WY01-WY05
0
5
10
15
20
25
30
Oct
-00
Jan-
01
Apr
-01
Jul-0
1
Oct
-01
Jan-
02
Apr
-02
Jul-0
2
Oct
-02
Jan-
03
Apr
-03
Jul-0
3
Oct
-03
Jan-
04
Apr
-04
Jul-0
4
Oct
-04
Jan-
05
Apr
-05
Jul-0
5
Sample Date
TOC
(mg/
L)
Orestimba Creek @ River Rd. Solado Creek @ Hwy 33 Del Puerto Creek @Vineyard Grayson Drain Ingram Creek @River Rd. Hospital Creek @River Rd. Bay-Delta Authority Target (3 mg/L)
R6-13
269
San Joaquin River Westside BasinTotal Organic Carbon WY01- WY05
0
5
10
15
20
25
30
35
Orestimba Creek @River Rd.
Solado Creek @ Hwy33
Del Puerto Creek@Vineyard
Grayson Drain Ingram Creek@River Rd.
Hospital Creek@River Rd.
Tota
l Org
anic
Car
bon
(mg/
L)
MedianBay-Delta Authority Target (3 mg/L)
R6-14
270
San Joaquin River West Side Basin Total Coliform WY02-WY05
0
500
1000
1500
2000
2500
Jul-0
2
Oct
-02
Jan-
03
Apr
-03
Jul-0
3
Oct
-03
Jan-
04
Apr
-04
Jul-0
4
Oct
-04
Jan-
05
Apr
-05
Jul-0
5
Sample Date
Tota
l Col
iform
(MPN
)
Orestimba Creek @ River Rd. Solado Creek @ Hwy 33 Del Puerto Creek @Vineyard Grayson Drain Ingram Creek @River Rd. Hospital Creek @River Rd.
R6-15
271
San Joaquin River Westside BasinTotal Coliform WY02- WY05
0
500
1000
1500
2000
2500
3000
Orestimba Creek @River Rd.
Solado Creek @Hwy 33
Del Puerto Creek@Vineyard
Grayson Drain Ingram Creek@River Rd.
Hospital Creek@River Rd.
Tota
l Col
iform
(MPN
/100
ml)
Median
R6-16
272
San Joaquin River West Side Basin Escherichia coli WY02-WY05
0
500
1000
1500
2000
2500
Jul-0
2
Oct
-02
Jan-
03
Apr
-03
Jul-0
3
Oct
-03
Jan-
04
Apr
-04
Jul-0
4
Oct
-04
Jan-
05
Apr
-05
Jul-0
5
Sample Date
E. c
oli
(MPN
)
Orestimba Creek @ River Rd. Solado Creek @ Hwy 33 Del Puerto Creek @Vineyard Grayson Drain Ingram Creek @River Rd. Hospital Creek @River Rd. USEPA Guideline - Designated beach area. (235 MPN/100 mL)
R6-17
273
San Joaquin River Westside BasinEscherichia coli WY02-WY05
0
500
1000
1500
2000
2500
3000
Orestimba Creek @River Rd.
Solado Creek @Hwy 33
Del Puerto Creek@Vineyard
Grayson Drain Ingram Creek@River Rd.
Hospital Creek@River Rd.
E. c
oli
(MPN
/100
ml)
MedianUSEPA Guideline - Designated beach area. (235 MPN/100 mL)
R6-18
274
San Joaquin River West Side Basin Summary Nitrate WY01-WY02
0
10
20
30
40
50
60
70
80
Oct
-00
Jan-
01
Apr
-01
Jul-0
1
Oct
-01
Sample Date
Nitr
ate
(mg/
L)
Orestimba Creek @ River Rd. Solado Creek @ Hwy 33 Del Puerto Creek @Vineyard Grayson Drain Ingram Creek @River Rd. Hospital Creek @River Rd. California Primary MCL (45mg/L)
R6-19
275
San Joaquin River Westside BasinNitrate WY01-WY04
0
10
20
30
40
50
60
70
80
Orestimba Creek @River Rd.
Solado Creek @ Hwy33
Del Puerto Creek@Vineyard
Grayson Drain Ingram Creek@River Rd.
Hospital Creek@River Rd.
Nitr
ate
(mg/
L)
MedianCalifornia Primary MCL (45mg/L)
R6-20
276
San Joaquin River West Side Basin Total Kjeldahl Nitrogen WY01-WY03
0
2
4
6
8
10
12
14
16
Oct
-00
Jan-
01
Apr
-01
Jul-0
1
Oct
-01
Jan-
02
Apr
-02
Jul-0
2
Oct
-02
Sample Date
TKN
(mg/
L)
Orestimba Creek @ River Rd. Solado Creek @ Hwy 33 Del Puerto Creek @Vineyard Grayson Drain Ingram Creek @River Rd. Hospital Creek @River Rd.
R6-21
277
San Joaquin River Westside BasinTotal Kjeldahl Nitrogen WY01-WY05
0
2
4
6
8
10
12
14
16
18
Orestimba Creek @River Rd.
Solado Creek @ Hwy33
Del Puerto Creek@Vineyard
Grayson Drain Ingram Creek@River Rd.
Hospital Creek@River Rd.
TKN
(mg/
L)
Median
R6-22
278
San Joaquin River West SideBasin Phosporus WY01-WY03
0.0
0.5
1.0
1.5
2.0
2.5
3.0
3.5
4.0
Oct
-00
Jan-
01
Apr
-01
Jul-0
1
Oct
-01
Jan-
02
Apr
-02
Jul-0
2
Oct
-02
Jan-
03
Apr
-03
Sample Date
Phos
phor
us (m
g/L)
Orestimba Creek @ River Rd. Solado Creek @ Hwy 33 Del Puerto Creek @Vineyard Grayson Drain Ingram Creek @River Rd. Hospital Creek @River Rd.
R6-23
279
San Joaquin River Westside BasinPhosphorus WY01-WY05
0
0.5
1
1.5
2
2.5
3
3.5
4
4.5
Orestimba Creek @River Rd.
Solado Creek @Hwy 33
Del Puerto Creek@Vineyard
Grayson Drain Ingram Creek@River Rd.
Hospital Creek@River Rd.
Phos
phor
us (m
g/L)
Median
R6-24
280
San Joaquin River West Side Basin Orthophosphate-P WY01-WY03
0.0
1.0
2.0
3.0
4.0
Oct
-00
Jan-
01
Apr
-01
Jul-0
1
Oct
-01
Jan-
02
Apr
-02
Jul-0
2
Oct
-02
Jan-
03
Apr
-03
Sample Date
Ort
hoph
osph
ate-
P (m
g/L)
Orestimba Creek @ River Rd. Grayson Drain Ingram Creek @River Rd. Hospital Creek @River Rd. Solado Creek @ Hwy 33 Del Puerto Creek @Vineyard
R6-25
281
San Joaquin River Westside BasinOrthophosphate-P WY01-WY05
0
0.5
1
1.5
2
2.5
3
3.5
4
Orestimba Creek @River Rd.
Solado Creek @Hwy 33
Del Puerto Creek@Vineyard
Grayson Drain Ingram Creek@River Rd.
Hospital Creek@River Rd.
Ort
hoph
osph
ate-
P (m
g/L)
Median
R6-26
282
San Joaquin River West Side Basin Potassium WY01-WY03
0
2
4
6
8
10
12
14
16
Oct
-00
Jan-
01
Apr
-01
Jul-0
1
Oct
-01
Jan-
02
Apr
-02
Jul-0
2
Oct
-02
Jan-
03
Apr
-03
Sample Date
Pota
ssiu
m (m
g/L)
Orestimba Creek @ River Rd. Solado Creek @ Hwy 33 Del Puerto Creek @Vineyard Grayson Drain Ingram Creek @River Rd. Hospital Creek @River Rd.
R6-27
283
San Joaquin River Westside BasinPotassium WY01-WY04
0
2
4
6
8
10
12
14
16
18
Orestimba Creek @River Rd.
Solado Creek @ Hwy33
Del Puerto Creek@Vineyard
Grayson Drain Ingram Creek@River Rd.
Hospital Creek@River Rd.
Pota
ssiu
m (m
g/L)
Median
R6-28
284
San Joaquin River West Side Basin Biochemical Oxygen Demand 5-day WY01-WY03
0
1
2
3
4
5
6
7
8
9
Oct
-00
Jan-
01
Apr
-01
Jul-0
1
Oct
-01
Jan-
02
Apr
-02
Jul-0
2
Oct
-02
Jan-
03
Apr
-03
Sample Date
BO
D 5
-Day
(mg/
L)
Orestimba Creek @ River Rd. Solado Creek @ Hwy 33 Del Puerto Creek @Vineyard Grayson Drain Ingram Creek @River Rd. Hospital Creek @River Rd.
R6-29
285
San Joaquin River Westside BasinBiological Oxygen Demand 5-Day WY01-WY03
0
1
2
3
4
5
6
7
8
9
Orestimba Creek @River Rd.
Solado Creek @ Hwy33
Del Puerto Creek@Vineyard
Grayson Drain Ingram Creek@River Rd.
Hospital Creek@River Rd.
BO
D- 5
(mg/
L)
Median
R6-30
286
San Joaquin River West Side Basin Biochemical Oygen Demand 10-Day WY01-WY03
0
2
4
6
8
10
12
14
16
18
Oct
-00
Jan-
01
Apr
-01
Jul-0
1
Oct
-01
Jan-
02
Apr
-02
Jul-0
2
Oct
-02
Jan-
03
Apr
-03
Sample Date
BO
D 1
0-D
ay (m
g/L)
Orestimba Creek @ River Rd. Solado Creek @ Hwy 33 Del Puerto Creek @Vineyard Grayson Drain Ingram Creek @River Rd. Hospital Creek @River Rd.
R6-31
287
San Joaquin River Westside BasinBiological Oxygen Demand 10-Day WY01-WY03
0
2
4
6
8
10
12
14
16
18
Orestimba Creek @River Rd.
Solado Creek @Hwy 33
Del Puerto Creek@Vineyard
Grayson Drain Ingram Creek@River Rd.
Hospital Creek@River Rd.
BO
D- 1
0 (m
g/L)
Median
R6-32
288
San Joaquin River West Side Basin Chloride WY01-WY03
0
50
100
150
200
250
300
350
400
450
Oct
-00
Jan-
01
Apr
-01
Jul-0
1
Oct
-01
Jan-
02
Apr
-02
Jul-0
2
Oct
-02
Jan-
03
Apr
-03
Sample Date
Chl
orid
e (m
g/L)
Orestimba Creek @ River Rd. Solado Creek @ Hwy 33 Del Puerto Creek @Vineyard Grayson Drain Ingram Creek @River Rd. Hospital Creek @River Rd. California Secondary MCL (recommended level) (250 mg/L)
R6-33
289
San Joaquin River Westside BasinChloride WY01-WY03
0
50
100
150
200
250
300
350
400
450
Orestimba Creek @River Rd.
Solado Creek @Hwy 33
Del Puerto Creek@Vineyard
Grayson Drain Ingram Creek@River Rd.
Hospital Creek@River Rd.
Chl
orid
e (m
g/L)
MedianCalifornia Secondary MCL (recommended level) (250 mg/L)
R6-34
290
San Joaquin River West Side Basin Sulfate WY01-WY03
0
50
100
150
200
250
300
350
400
450
500
Oct
-00
Jan-
01
Apr
-01
Jul-0
1
Oct
-01
Jan-
02
Apr
-02
Jul-0
2
Oct
-02
Jan-
03
Apr
-03
Jul-0
3
Oct
-03
Sample Date
Sulfa
te (m
g/L)
Orestimba Creek @ River Rd. Solado Creek @ Hwy 33 Del Puerto Creek @Vineyard Grayson Drain Ingram Creek @River Rd. Hospital Creek @River Rd. California Secondary MCL (recommended level) (250 mg/L)
R6-35
291
San Joaquin River Westside BasinSulfate WY01-WY03
0
50
100
150
200
250
300
350
400
450
500
Orestimba Creek @River Rd.
Solado Creek @Hwy 33
Del Puerto Creek@Vineyard
Grayson Drain Ingram Creek@River Rd.
Hospital Creek@River Rd.
Sulfa
te (m
g/L)
MedianCalifornia Secondary MCL (recommended level) (250 mg/L)
R6-36
292
San Joaquin River West Side Basin Calcium WY01-WY03
0
20
40
60
80
100
120
140
160
Oct
-00
Jan-
01
Apr
-01
Jul-0
1
Oct
-01
Jan-
02
Apr
-02
Jul-0
2
Oct
-02
Jan-
03
Apr
-03
Sample Date
Cal
cium
(mg/
L)
Orestimba Creek @ River Rd. Solado Creek @ Hwy 33 Grayson Drain Ingram Creek @River Rd. Hospital Creek @River Rd.
R6-37
293
San Joaquin River Westside BasinCalcium WY01-WY03
0
20
40
60
80
100
120
140
160
Orestimba Creek @River Rd.
Solado Creek @Hwy 33
Del Puerto Creek@Vineyard
Grayson Drain Ingram Creek@River Rd.
Hospital Creek@River Rd.
Cal
cium
(mg/
L)
Median
R6-38
294
San Joaquin River West Side Basin Magnesium WY01- WY03
10
20
30
40
50
60
70
80
90
100
Oct
-00
Jan-
01
Apr
-01
Jul-0
1
Oct
-01
Jan-
02
Apr
-02
Jul-0
2
Oct
-02
Jan-
03
Apr
-03
Sample Date
Mag
nesi
um (m
g/L)
Orestimba Creek @ River Rd. Solado Creek @ Hwy 33 Del Puerto Creek @Vineyard Grayson Drain Ingram Creek @River Rd. Hospital Creek @River Rd.
R6-39
295
San Joaquin River Westside BasinMagnesium WY01-WY03
0
10
20
30
40
50
60
70
80
90
100
Orestimba Creek @River Rd.
Solado Creek @Hwy 33
Del Puerto Creek@Vineyard
Grayson Drain Ingram Creek@River Rd.
Hospital Creek@River Rd.
Mag
nesi
um (m
g/L)
Median
R6-40
296
San Joaquin River West Side Basin Total Dissolved Solids WY01-W03
0
200
400
600
800
1000
1200
1400
1600
1800
Oct
-00
Jan-
01
Apr
-01
Jul-0
1
Oct
-01
Jan-
02
Apr
-02
Jul-0
2
Oct
-02
Sample Date
TDS
(mg/
L)
Orestimba Creek @ River Rd. Solado Creek @ Hwy 33 Del Puerto Creek @Vineyard Grayson Drain Ingram Creek @River Rd. Hospital Creek @River Rd. California Secondary MCL (recommended level) (500 mg/L)
R6-41
297
San Joaquin River Westside BasinTotal Dissolved Solids WY01-WY03
0
200
400
600
800
1000
1200
1400
1600
1800
Orestimba Creek @River Rd.
Solado Creek @Hwy 33
Del Puerto Creek@Vineyard
Grayson Drain Ingram Creek@River Rd.
Hospital Creek@River Rd.
TDS
(mg/
L)
MedianCalifornia Secondary MCL (recommended level) (500 mg/L)
R6-42
298
San Joaquin River West Side Basin Carbonate WY01- WY03
0
5
10
15
20
25
30
Oct
-00
Jan-
01
Apr
-01
Jul-0
1
Oct
-01
Jan-
02
Apr
-02
Jul-0
2
Oct
-02
Sample Date
Car
bona
te (m
g/L)
Orestimba Creek @ River Rd. Solado Creek @ Hwy 33 Del Puerto Creek @Vineyard Grayson Drain Ingram Creek @River Rd. Hospital Creek @River Rd.
R6-43
299
San Joaquin River Westside BasinCarbonate WY01-WY03
0
5
10
15
20
25
30
Orestimba Creek @River Rd.
Solado Creek @ Hwy33
Del Puerto Creek@Vineyard
Grayson Drain Ingram Creek@River Rd.
Hospital Creek@River Rd.
Car
bona
te (m
g/L)
Median
R6-44
300
San Joaquin River West Side Basin Bicarbonate WY01- WY03
0
50
100
150
200
250
300
350
400
450
500
Oct
-00
Jan-
01
Apr
-01
Jul-0
1
Oct
-01
Jan-
02
Apr
-02
Jul-0
2
Oct
-02
Sample Date
Bic
arbo
nate
(mg/
L)
Orestimba Creek @ River Rd. Solado Creek @ Hwy 33 Del Puerto Creek @Vineyard Grayson Drain Ingram Creek @River Rd. Hospital Creek @River Rd.
R6-45
301
San Joaquin River Westside BasinBicarbonate WY01-WY03
0
50
100
150
200
250
300
350
400
450
500
Orestimba Creek @River Rd.
Solado Creek @Hwy 33
Del Puerto Creek@Vineyard
Grayson Drain Ingram Creek@River Rd.
Hospital Creek@River Rd.
Bic
arbo
nate
(mg/
L)
Median
R6-46
302
San Joaquin River West Side Basin Total Alkalinity WY01-WY03
50
100
150
200
250
300
350
400
Oct
-00
Jan-
01
Apr
-01
Jul-0
1
Oct
-01
Jan-
02
Apr
-02
Jul-0
2
Oct
-02
Sample Date
Tota
l Alk
alin
ity (m
g/L)
Orestimba Creek @ River Rd. Solado Creek @ Hwy 33 Del Puerto Creek @Vineyard Grayson Drain Ingram Creek @River Rd. Hospital Creek @River Rd.
R6-47
303
San Joaquin River Westside BasinTotal Alkalinity WY01-WY03
0
50
100
150
200
250
300
350
400
Orestimba Creek @River Rd.
Solado Creek @Hwy 33
Del Puerto Creek@Vineyard
Grayson Drain Ingram Creek@River Rd.
Hospital Creek@River Rd.
Tota
l Alk
alin
ity (m
g/L)
Median
R6-48
304
San Joaquin River West Side Basin Sodium WY01-WY03
0
50
100
150
200
250
Oct
-00
Jan-
01
Apr
-01
Jul-0
1
Oct
-01
Jan-
02
Apr
-02
Jul-0
2
Oct
-02
Sample Date
Sodi
um (m
g/L)
Orestimba Creek @ River Rd. Solado Creek @ Hwy 33 Del Puerto Creek @Vineyard Grayson Drain Ingram Creek @River Rd. Hospital Creek @River Rd. Water Quality for Agriculture(Ayers & Westcot) (69 mg/L)
R6-49
305
San Joaquin River Westside BasinSodium WY01-WY03
0
50
100
150
200
250
300
Orestimba Creek @River Rd.
Solado Creek @Hwy 33
Del Puerto Creek@Vineyard
Grayson Drain Ingram Creek@River Rd.
Hospital Creek@River Rd.
Sodi
um (m
g/L)
MedianWater Quality for Agriculture (Ayers & Westcot) (69 mg/L)
R6-50
306
San Joaquin River Delta Basin Temperature WY01-WY05
5
10
15
20
25
30O
ct-0
0
Jan-
01
Apr-0
1
Jul-0
1
Oct
-01
Jan-
02
Apr-0
2
Jul-0
2
Oct
-02
Jan-
03
Apr-0
3
Jul-0
3
Oct
-03
Jan-
04
Apr-0
4
Jul-0
4
Oct
-04
Jan-
05
Apr-0
5
Jul-0
5
Sample Date
Tem
pera
ture
(ºC
)
New Jerusalem DrainTom Payne Slough @Paradise Rd.Old River @Tracy Blvd Mountain House CreekBay-Delta Authority Target, SJR @ Vernalis (Apr 1-Jun 30 & Sept 1- Nov 30, 20ºC)
R7-1
307
San Joaquin River South Delta BasinTemperature WY01- WY05
5
10
15
20
25
30
New Jerusalem Drain Tom Payne Slough @ ParadiseRd.
Old River @Tracy Blvd Mountain House Creek
Tem
pera
ture
(ºC
)
Median
R7-2
308
San Joaquin River Delta BasinSpecific Conductivity WY01-WY05
0
500
1000
1500
2000
2500
3000
3500
Oct
-00
Jan-
01
Apr-
01
Jul-0
1
Oct
-01
Jan-
02
Apr-
02
Jul-0
2
Oct
-02
Jan-
03
Apr-
03
Jul-0
3
Oct
-03
Jan-
04
Apr-
04
Jul-0
4
Oct
-04
Jan-
05
Apr-
05
Jul-0
5
Sample Date
SC (μ
mho
s/cm
)
New Jerusalem DrainTom Payne Slough @Paradise Rd.Old River @Tracy Blvd Mountain House CreekBasin Plan Objective (Apr 1-Aug 31, 700 μmhos/cm; Sep 1-Mar 31,1000 μmhos/cm)
R7-3
309
San Joaquin River South Delta BasinSpecific Conductivity WY01- WY05
0
500
1000
1500
2000
2500
3000
3500
New Jerusalem Drain Tom Payne Slough @ ParadiseRd.
Old River @Tracy Blvd Mountain House Creek
Spec
ific
Con
duct
ivity
(μm
hos/
cm)
Median
R7-4
310
San Joaquin River Delta BasinpH WY01-WY05
6.0
6.5
7.0
7.5
8.0
8.5
9.0
Oct
-00
Jan-
01
Apr-
01
Jul-0
1
Oct
-01
Jan-
02
Apr-
02
Jul-0
2
Oct
-02
Jan-
03
Apr-
03
Jul-0
3
Oct
-03
Jan-
04
Apr-
04
Jul-0
4
Oct
-04
Jan-
05
Apr-
05
Jul-0
5
Sample Date
pH
New Jerusalem Drain Tom Payne Slough @Paradise Rd. Old River @Tracy Blvd Mountain House Creek Basin Plan Objective (6.5-8.5)
R7-5
311
San Joaquin River South Delta BasinpH WY01- WY05
6
6.5
7
7.5
8
8.5
9
New Jerusalem Drain Tom Payne Slough @ ParadiseRd.
Old River @Tracy Blvd Mountain House Creek
pH
MedianBasin Plan Objective (6.5-8.5)
R7-6
312
San Joaquin River Delta Basin Dissolved Oxygen WY01-WY05
0
2
4
6
8
10
12
14
16
18
Apr-
01
Jul-0
1
Oct
-01
Jan-
02
Apr-
02
Jul-0
2
Oct
-02
Jan-
03
Apr-
03
Jul-0
3
Oct
-03
Jan-
04
Apr-
04
Jul-0
4
Oct
-04
Jan-
05
Apr-
05
Jul-0
5
Sample Date
Dis
solv
ed O
xyge
n (m
g/L)
New Jerusalem Drain Tom Payne Slough @Paradise Rd. Old River @Tracy Blvd Mountain House Creek Basin Plan Objective (5 mg/L)
R7-7
313
San Joaquin River South Delta BasinDissolved Oxygen WY01- WY05
0
2
4
6
8
10
12
14
16
18
New Jerusalem Drain Tom Payne Slough @ ParadiseRd.
Old River @Tracy Blvd Mountain House Creek
Dis
solv
ed O
xyge
n (m
g/L)
MedianBasin Plan Objective (5 mg/L)
R7-8
314
San Joaquin River Delta Basin Turbidity WY02-WY04
0
50
100
150
200
250
300
Jul-0
2
Oct
-02
Jan-
03
Apr-
03
Jul-0
3
Oct
-03
Jan-
04
Apr-
04
Sample Date
Turb
idity
(ntu
)
New Jerusalem Drain Tom Payne Slough @Paradise Rd. Old River @Tracy Blvd Mountain House Creek
R7-9
315
San Joaquin River South Delta BasinTurbidity WY02- WY04
0
50
100
150
200
250
300
350
New Jerusalem Drain Tom Payne Slough @ ParadiseRd.
Old River @Tracy Blvd Mountain House Creek
Turb
idity
(ntu
)
Median
R7-10
316
San Joaquin River Delta Basin Total Suspended Solids WY01
0
20
40
60
80
100
120
Oct
-00
Jan-
01
Apr-
01
Jul-0
1
Sample Date
TSS
(mg/
L)
New Jerusalem Drain Tom Payne Slough @Paradise Rd. Old River @Tracy Blvd Mountain House Creek
R7-11
317
San Joaquin River South Delta BasinTotal Suspended Solids WY01
0
20
40
60
80
100
120
New Jerusalem Drain Tom Payne Slough @ ParadiseRd.
Old River @Tracy Blvd Mountain House Creek
Tota
l Sus
pend
ed S
olid
s (m
g/L)
Median
R7-12
318
San Joaquin River Delta Basin Total Organic Carbon WY01-WY05
0
5
10
15
20
25
30
35
Oct
-00
Jan-
01
Apr-
01
Jul-0
1
Oct
-01
Jan-
02
Apr-
02
Jul-0
2
Oct
-02
Jan-
03
Apr-
03
Jul-0
3
Oct
-03
Jan-
04
Apr-
04
Jul-0
4
Oct
-04
Jan-
05
Apr-
05
Jul-0
5
Sample Date
TOC
(mg/
L)
New Jerusalem Drain Tom Payne Slough @Paradise Rd. Old River @Tracy Blvd Mountain House Creek Bay-Delta Authority Target (3 mg/L)
R7-13
319
San Joaquin River South Delta BasinTotal Organic Carbon WY01- WY05
0
5
10
15
20
25
30
35
New Jerusalem Drain Tom Payne Slough @ ParadiseRd.
Old River @Tracy Blvd Mountain House Creek
Tota
l Org
anic
Car
bon
(mg/
L)
MedianBay-Delta Authority Target (3 mg/L)
R7-14
320
San Joaquin River Delta Basin Total Coliform WY02-WY05
0
500
1000
1500
2000
2500
3000
Jul-0
2
Oct
-02
Jan-
03
Apr-
03
Jul-0
3
Oct
-03
Jan-
04
Apr-
04
Jul-0
4
Oct
-04
Jan-
05
Apr-
05
Jul-0
5
Sample Date
Tota
l Col
iform
(MPN
)
New Jerusalem Drain Tom Payne Slough @Paradise Rd. Old River @Tracy Blvd Mountain House Creek
R7-15
321
San Joaquin River South Delta BasinTotal Coliform WY02- WY05
0
500
1000
1500
2000
2500
3000
New Jerusalem Drain Tom Payne Slough @ ParadiseRd.
Old River @Tracy Blvd Mountain House Creek
Tota
l Col
iform
(MPN
/100
ml)
Median
R7-16
322
San Joaquin River Delta BasinEscherichia coli WY02-WY05
0
200
400
600
800
1000
1200
1400Ju
l-02
Oct
-02
Jan-
03
Apr-
03
Jul-0
3
Oct
-03
Jan-
04
Apr-
04
Jul-0
4
Oct
-04
Jan-
05
Apr-
05
Jul-0
5
Sample Date
E. c
oli
(MPN
)
New Jerusalem DrainTom Payne Slough @Paradise Rd.Old River @Tracy Blvd Mountain House CreekUSEPA Guideline - Designated beach area. (235 MPN/100 mL)
R7-17
323
San Joaquin River South Delta BasinEscherichia coli WY02-WY05
0
200
400
600
800
1000
1200
1400
New Jerusalem Drain Tom Payne Slough @ ParadiseRd.
Old River @Tracy Blvd Mountain House Creek
E. c
oli
(MPN
/100
ml)
MedianUSEPA Guideline - Designated beach area. (235 MPN/100 mL)
R7-18
324
San Joaquin River Delta Basin Nitrate WY01
0
10
20
30
40
50
60
70
80
90
Oct
-00
Jan-
01
Apr-
01
Jul-0
1
Oct
-01
Sample Date
Nitr
ate
(mg/
L)
New Jerusalem Drain Tom Payne Slough @Paradise Rd. Old River @Tracy Blvd Mountain House Creek California Primary MCL (45mg/L)
R7-19
325
San Joaquin River South Delta BasinNitrate WY01-WY04
0
10
20
30
40
50
60
70
80
90
New Jerusalem Drain Tom Payne Slough @ ParadiseRd.
Old River @Tracy Blvd Mountain House Creek
Nitr
ate
(mg/
L)
MedianCalifornia Primary MCL (45mg/L)
R7-20
326
San Joaquin River Delta BasinTotal Kjeldahl Nitrogen WY01-WY03
0.0
0.5
1.0
1.5
2.0
2.5
3.0
3.5
4.0
4.5
5.0
Oct
-00
Jan-
01
Apr-
01
Jul-0
1
Oct
-01
Jan-
02
Apr-
02
Jul-0
2
Oct
-02
Jan-
03
Apr-
03
Sample Date
TKN
(mg/
L)
New Jerusalem Drain Tom Payne Slough @Paradise Rd. Old River @Tracy Blvd Mountain House Creek
R7-21
327
San Joaquin River South Delta BasinTotal Kjeldahl Nitrogen WY01-WY05
0
0.5
1
1.5
2
2.5
3
3.5
4
4.5
5
New Jerusalem Drain Tom Payne Slough @ ParadiseRd.
Old River @Tracy Blvd Mountain House Creek
TKN
(mg/
L)
Median
R7-22
328
San Joaquin River Delta BasinPhosphorus WY01-WY03
0
0.1
0.2
0.3
0.4
0.5
0.6
0.7
0.8
Oct
-00
Jan-
01
Apr-
01
Jul-0
1
Oct
-01
Jan-
02
Apr-
02
Jul-0
2
Oct
-02
Jan-
03
Apr-
03
Sample Date
Phos
phor
us (m
g/L)
New Jerusalem Drain Tom Payne Slough @Paradise Rd. Old River @Tracy Blvd Mountain House Creek
R7-23
329
San Joaquin River South Delta BasinPhosphorus WY01-WY05
0
0.1
0.2
0.3
0.4
0.5
0.6
0.7
0.8
New Jerusalem Drain Tom Payne Slough @ ParadiseRd.
Old River @Tracy Blvd Mountain House Creek
Phos
phor
us (m
g/L)
Median
R7-24
330
San Joaquin River Delta Basin Orthophosphate-P WY01-WY03
0
0.1
0.2
0.3
0.4
0.5
0.6
Oct
-00
Jan-
01
Apr-
01
Jul-0
1
Oct
-01
Jan-
02
Apr-
02
Jul-0
2
Oct
-02
Jan-
03
Apr-
03
Sample Date
Ort
ho-P
(mg/
L)
New Jerusalem Drain Tom Payne Slough @Paradise Rd. Old River @Tracy Blvd Mountain House Creek
R7-25
331
San Joaquin River South Delta BasinOrthophosphate-P WY01-WY05
0
0.1
0.2
0.3
0.4
0.5
0.6
New Jerusalem Drain Tom Payne Slough @ ParadiseRd.
Old River @Tracy Blvd Mountain House Creek
Ort
hoph
osph
ate-
P (m
g/L)
Median
R7-26
332
San Joaquin River Delta Basin Potassium WY01-WY03
0
5
10
15
20
25
Oct
-00
Jan-
01
Apr-
01
Jul-0
1
Oct
-01
Jan-
02
Apr-
02
Jul-0
2
Oct
-02
Jan-
03
Apr-
03
Sample Date
Pota
ssiu
m (m
g/L)
New Jerusalem Drain Tom Payne Slough @Paradise Rd. Old River @Tracy Blvd Mountain House Creek
R7-27
333
San Joaquin River South Delta BasinPotassium WY01-WY04
0
5
10
15
20
25
New Jerusalem Drain Tom Payne Slough @ ParadiseRd.
Old River @Tracy Blvd Mountain House Creek
Pota
ssiu
m (m
g/L)
Median
R7-28
334
San Joaquin River Delta Basin Biological Oxygen Demand 5-Day WY01-WY03
0
1
2
3
4
5
6
7
8
9
10
Oct
-00
Jan-
01
Apr-
01
Jul-0
1
Oct
-01
Jan-
02
Apr-
02
Jul-0
2
Oct
-02
Jan-
03
Sample Date
BO
D 5
-Day
(mg/
L)
New Jerusalem Drain Tom Payne Slough @Paradise Rd. Old River @Tracy Blvd Mountain House Creek
R7-29
335
San Joaquin River South Delta BasinBiological Oxygen Demand 5-Day WY01-WY03
0
1
2
3
4
5
6
7
8
9
10
New Jerusalem Drain Tom Payne Slough @ ParadiseRd.
Old River @Tracy Blvd Mountain House Creek
BO
D- 5
(mg/
L)
Median
R7-30
336
San Joaquin River Delta Basin Biological Oxygen Demand 10-Day WY01-WY03
0
2
4
6
8
10
12
14
16
18
Oct
-00
Jan-
01
Apr-
01
Jul-0
1
Oct
-01
Jan-
02
Apr-
02
Jul-0
2
Oct
-02
Jan-
03
Apr-
03
Sample Date
BO
D 1
0-D
ay (m
g/L)
New Jerusalem Drain Tom Payne Slough @Paradise Rd. Old River @Tracy Blvd Mountain House Creek
R7-31
337
San Joaquin River South Delta BasinBiological Oxygen Demand 10-Day WY01-WY03
0
2
4
6
8
10
12
14
16
18
New Jerusalem Drain Tom Payne Slough @ ParadiseRd.
Old River @Tracy Blvd Mountain House Creek
BO
D- 1
0 (m
g/L)
Median
R7-32
338
San Joaquin River Delta Basin Chloride WY01-WY03
0
100
200
300
400
500
600
Oct
-00
Jan-
01
Apr-
01
Jul-0
1
Oct
-01
Jan-
02
Apr-
02
Jul-0
2
Oct
-02
Jan-
03
Apr-
03
Sample Date
Chl
orid
e (m
g/L)
New Jerusalem Drain Tom Payne Slough @Paradise Rd.Old River @Tracy Blvd Mountain House CreekCalifornia Secondary MCL (recommended level) (250 mg/L)
R7-33
339
San Joaquin River South Delta BasinChloride WY01-WY03
0
100
200
300
400
500
600
New Jerusalem Drain Tom Payne Slough @ ParadiseRd.
Old River @Tracy Blvd Mountain House Creek
Chl
orid
e (m
g/L)
MedianCalifornia Secondary MCL (recommended level) (250 mg/L)
R7-34
340
San Joaquin River Delta Basin Sulfate WY01-WY03
0
100
200
300
400
500
600
700
Oct
-00
Jan-
01
Apr-
01
Jul-0
1
Oct
-01
Jan-
02
Apr-
02
Jul-0
2
Oct
-02
Jan-
03
Apr-
03
Sample Date
Sulfa
te (m
g/L)
New Jerusalem Drain Tom Payne Slough @Paradise Rd.Old River @Tracy Blvd Mountain House CreekCalifornia Secondary MCL (recommended level) (250 mg/L)
R7-35
341
San Joaquin River South Delta BasinSulfate WY01-WY03
0
100
200
300
400
500
600
700
New Jerusalem Drain Tom Payne Slough @ ParadiseRd.
Old River @Tracy Blvd Mountain House Creek
Sulfa
te (m
g/L)
MedianCalifornia Secondary MCL (recommended level) (250 mg/L)
R7-36
342
San Joaquin River Delta Basin Calcium WY01-WY03
0
20
40
60
80
100
120
140
160
180
200
Oct
-00
Jan-
01
Apr-
01
Jul-0
1
Oct
-01
Jan-
02
Apr-
02
Jul-0
2
Oct
-02
Jan-
03
Apr-
03
Sample Date
Cal
cium
(mg/
L)
New Jerusalem Drain Tom Payne Slough @Paradise Rd. Old River @Tracy Blvd Mountain House Creek
R7-37
343
San Joaquin River South Delta BasinCalcium WY01-WY03
0
20
40
60
80
100
120
140
160
180
200
New Jerusalem Drain Tom Payne Slough @ ParadiseRd.
Old River @Tracy Blvd Mountain House Creek
Cal
cium
(mg/
L)
Median
R7-38
344
San Joaquin River Delta BasinMagnesium WY01-WY03
0
10
20
30
40
50
60
70
80
90
100
Oct
-00
Jan-
01
Apr-
01
Jul-0
1
Oct
-01
Jan-
02
Apr-
02
Jul-0
2
Oct
-02
Jan-
03
Apr-
03
Sample Date
Mag
nesi
um (m
g/L)
New Jerusalem Drain Tom Payne Slough @Paradise Rd. Old River @Tracy Blvd Mountain House Creek
R7-39
345
San Joaquin River South Delta BasinMagnesium WY01-WY03
0
10
20
30
40
50
60
70
80
90
100
New Jerusalem Drain Tom Payne Slough @ ParadiseRd.
Old River @Tracy Blvd Mountain House Creek
Mag
nesi
um (m
g/L)
Median
R7-40
346
San Joaquin River Delta BasinTotal Dissolved Solids WY01-WY03
0
500
1000
1500
2000
2500
Oct
-00
Jan-
01
Apr-
01
Jul-0
1
Oct
-01
Jan-
02
Apr-
02
Jul-0
2
Oct
-02
Sample Date
TDS
(mg/
L)
New Jerusalem Drain Tom Payne Slough @Paradise Rd.Old River @Tracy Blvd Mountain House CreekCalifornia Secondary MCL (recommended level) (500 mg/L)
R7-41
347
San Joaquin River South Delta BasinTotal Dissolved Solids WY01-WY03
0
500
1000
1500
2000
2500
New Jerusalem Drain Tom Payne Slough @ ParadiseRd.
Old River @Tracy Blvd Mountain House Creek
TDS
(mg/
L)
MedianCalifornia Secondary MCL (recommended level) (500 mg/L)
R7-42
348
San Joaquin River Delta Basin Carbonate WY01-WY03
0
2
4
6
8
10
12
14
16
18
Oct
-00
Jan-
01
Apr-
01
Jul-0
1
Oct
-01
Jan-
02
Apr-
02
Jul-0
2
Oct
-02
Jan-
03
Sample Date
Car
bona
te (m
g/L)
New Jerusalem Drain Tom Payne Slough @Paradise Rd. Old River @Tracy Blvd Mountain House Creek
R7-43
349
San Joaquin River South Delta BasinCarbonate WY01-WY03
0
2
4
6
8
10
12
14
16
18
New Jerusalem Drain Tom Payne Slough @ ParadiseRd.
Old River @Tracy Blvd Mountain House Creek
Car
bona
te (m
g/L)
Median
R7-44
350
San Joaquin River Delta BasinBicarbonate WY01-WY03
0
50
100
150
200
250
300
350
400
450
500
Oct
-00
Jan-
01
Apr-
01
Jul-0
1
Oct
-01
Jan-
02
Apr-
02
Jul-0
2
Oct
-02
Sample Date
Bic
arbo
nate
(mg/
L)
New Jerusalem Drain Tom Payne Slough @Paradise Rd. Old River @Tracy Blvd Mountain House Creek
R7-45
351
San Joaquin River South Delta BasinBicarbonate WY01-WY03
0
100
200
300
400
500
600
New Jerusalem Drain Tom Payne Slough @ ParadiseRd.
Old River @Tracy Blvd Mountain House Creek
Bic
arbo
nate
(mg/
L)
Median
R7-46
352
San Joaquin River Delta BasinTotal Alkalinity WY01-WY03
0
50
100
150
200
250
300
350
400
450
Oct
-00
Jan-
01
Apr-
01
Jul-0
1
Oct
-01
Jan-
02
Apr-
02
Jul-0
2
Oct
-02
Sample Date
Tota
l Alk
alin
ity (m
g/L)
New Jerusalem Drain Tom Payne Slough @Paradise Rd. Old River @Tracy Blvd Mountain House Creek
R7-47
353
San Joaquin River South Delta BasinTotal Alkalinity WY01-WY03
0
50
100
150
200
250
300
350
400
450
New Jerusalem Drain Tom Payne Slough @ ParadiseRd.
Old River @Tracy Blvd Mountain House Creek
Tota
l Alk
alin
ity (m
g/L)
Median
R7-48
354
San Joaquin River Delta BasinSodium WY01-WY03
0
100
200
300
400
500
600
Oct
-00
Jan-
01
Apr-
01
Jul-0
1
Oct
-01
Jan-
02
Apr-
02
Jul-0
2
Oct
-02
Sample Date
Sodi
um (m
g/L)
New Jerusalem Drain Tom Payne Slough @Paradise Rd.Old River @Tracy Blvd Mountain House CreekWater Quality for Agriculture(Ayers & Westcot) (69 mg/L)
R7-49
355
San Joaquin River South Delta BasinSodium WY01-WY03
0
100
200
300
400
500
600
New Jerusalem Drain Tom Payne Slough @ ParadiseRd.
Old River @Tracy Blvd Mountain House Creek
Sodi
um (m
g/L)
MedianWater Quality for Agriculture (Ayers & Westcot) (69 mg/L)
R7-50
356