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MW -6 (Down -gradient): <br />All constituents were within the tolerance limits in 2013, with the exception of chloride, nitrate <br />and nitrogen, sulfate, TDS, and Magnesium which exceeded their respective concentration limits <br />in the 1st Quarter 2013. Trend analysis indicates an increasing trend in TDS. <br />No VOCs were reported in well MW -6 this year. <br />iMW -7 (Up -gradient): <br />F11 <br />fl <br />u <br />H_ <br />All constituents were within the tolerance limits in 2013. <br />No VOCs were reported in well MW -7 this year. <br />Surface Water <br />Surface water samples were not collected this year due to lack of surface water flow. Surface <br />water was last collected on January 27, 2011. All concentrations of field parameters and <br />constituents of concern were below established concentration limits. VOCs were not detected <br />during the 1st Quarter 2011 sampling event. <br />HISTORICAL TIME SERIES PLOTS AND STIFF DIAGRAMS <br />Historical Time Series Plots are presented in Appendix F. Note that constituents not detected are <br />plotted at a value of half their respective detection limits. Outliers were included in the plots as <br />directed by RWQCB staff. <br />Stiff diagrams are submitted annually with the fourth quarter and annual report. The stiff <br />diagrams submitted for the fourth quarter indicate a sodium -sulfate water type for deep zone wells, <br />MW -6 and MW -7. The shallow zone wells exhibit four uniquely different water types; SB -1 and <br />MW -11 A are a sodium -bicarbonate type, MW -4 is a sodium/calcium-sulfate type, MW -5, and <br />MW -8 are calcium -bicarbonate type and MW -9A, and MW -10A are a sodium -chloride type <br />(Appendix F). An interpretation of zonation of water types in the shallow groundwater zone is <br />presented on Figure 2. <br />A comparison of water quality values between upgradient and downgradient wells in both the <br />shallow and deep zone do not indicate a significant increase in mineralization. <br />Although bicarbonate ions are sometimes assumed to indicate the influence by LFG and that LFG <br />is the carrier mechanism for VOC impact to groundwater, relatively high bicarbonate <br />milliequivalent levels are present in well SB -1 where VOCs are generally not detected. In <br />addition, at well MW -8 where many VOCs have been detected, the bicarbonate milliequivalent <br />levels have been relatively low. <br />Corral Hollow Sanitary Landfill 21 Department of Public Works/Solid Waste <br />4th Quarter and Annual 2013 Groundwater Monitoring County of San Joaquin — January 15, 2014 <br />