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control structures effectively directed stormwater from the waste material during the first quarter <br /> 2010. <br /> 2.0 Groundwater Monitoring Program <br /> During the first quarter 2010 monitoring event, groundwater monitoring was performed at the <br /> French Camp Landfill by Del-Tech. Groundwater samples were collected from two background <br /> monitoring wells (MW-6A and MW-7A) and four detection monitoring wells(MW-8A, MW-9A, <br /> MW-913, and MW-10A) during the first quarter 210 monitoring event. The analytical results <br /> from samples collected at these wells are used to determine potential landfill-related impacts. <br /> During the first quarter 2010 monitoring event, analysis for field parameters (pH, specific <br /> conductance, temperature, and turbidity) and monitoring parameters (bicarbonate, calcium, <br /> carbonate, chloride, magnesium, nitrate, potassium, sodium, sulfate, total dissolved solids [TDS], <br /> and volatile organic compounds [VOCs]) was performed for the background monitoring wells <br /> and detection monitoring wells. <br /> The field results provided by Del-Tech and the laboratory results provided by BC Laboratories, <br /> Inc. (BC Labs) for the first quarter 2010 groundwater monitoring event are summarized on Table <br /> 2.2. The historical groundwater data for the background and detection monitoring wells are <br /> presented in Appendix D. Times series concentration plots of historical groundwater data for the <br /> monitoring wells are presented in Appendix E. For VOCs, only those compounds that exhibited <br /> detections at groundwater monitoring wells during the first quarter 2010 monitoring event were <br /> plotted. The concentration limits presented on Table 2.2 were calculated by Herst & Associates, <br /> Inc. from data collected through the first quarter 2010 monitoring event. The statistical analysis <br /> calculations for groundwater monitoring wells are presented in Appendix E. A copy of the <br /> statistical analysis methodology is presented in Appendix C. <br /> As presented on Table 2.2, the following constituents exceeded their respective concentration <br /> limits during the first quarter 2010: calcium at MW-9A and MW-913; chloride at MW-9B; <br /> potassium at MW-9A and MW-913; and field temperature at MW-8A, MW-9A, MW-913, and <br /> MW-10A. Elevated chloride concentrations (with elevated specific conductance values) could <br /> indicate a saltwater intrusion to the groundwater. The French Camp Landfill is within the central <br /> Stockton area impacted by saltwater intrusion (Fourth Quarter/Annual 1999 Monitoring Report, <br /> French Camp Landfill, CH2M HILL,January 2000). <br /> Historical data from the groundwater monitoring wells were analyzed for temporal trends using <br /> Mann-Kendall / Sen's Slope trend analysis. Graphs and summary tables of the Mann-Kendall / <br /> Sen's Slope analyses for groundwater monitoring wells are presented in Appendix E. <br /> Chloride at MW-10A, potassium at MW-913, and sulfate at MW-913 exhibited increasing trends. <br /> Of these constituents, only potassium at MW-9B exceeded its concentration limit. Mann-Kendall <br /> / Sen's Slope analysis identified decreasing trends in the following constituents: bicarbonate <br /> alkalinity at MW-8A, calcium at MW-6A and MW-8A, chloride at MW-7A, magnesium at MW- <br /> 6A and MW-8A, nitrate at MW-8A and MW-10A, field pH at MW-6A and MW-913, sodium at <br /> MW-8A, field specific conductance at MW-7A, sulfate at MW-7A,total dissolved solids at MW- <br /> 7A, and field turbidity at MW-7A, MW-9A, and MW-10A. As noted above, MW-6A and MW- <br /> 7A are background monitoring wells, and trends in the groundwater quality at these wells are not <br /> indicative of an impact from the facility. <br /> Potassium at MW-913 is the only constituent that exceeded its concentration limit and also <br /> exhibited a significant increasing statistical trend. The first quarter 2010 concentration of <br />