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Drinking Water Standard(5 ug/L). The third quarter 2008 concentration of bromoform at AMW- <br /> 7 (1.1 ug/L) is comparable to concentrations observed at that well intermittently since August <br /> 2006. The third quarter 2008 concentration of dibromochloromethane at AMW-7 (0.81 ug/L) is <br /> comparable to concentrations observed at that well intermittently since August 2006. The third <br /> quarter 2008 concentration of tetrachloroethene at AMW-13 (2.7 ug/L) is comparable to <br /> concentrations observed at that well intermittently since March 1994, and is below the National <br /> Primary Drinking Water Standard (5 ug/L). The third quarter 2008 concentration of <br /> dichlorodifluoromethane at AMW-14(0.81)is comparable to concentrations observed at that well <br /> intermittently since May 1996. The third quarter 2008 concentration of tetrachloroethene at <br /> AMW-14 (15 ug/L) is comparable to concentrations observed at that well intermittently since <br /> March 1996, and is above the National Primary Drinking Water Standard (5 ug/L). The third <br /> quarter 2008 concentration of trichloroethene at AMW-14 (1.3 ug/L) is comparable to <br /> concentrations observed at that well intermittently since March 1994, and is below the National <br /> Primary Drinking Water Standard(5 ug/L). <br /> Historical data from the detection monitoring wells were analyzed for temporal trend using Sen's <br /> Slope trend analysis. Graphs of the Sen's Slope analyses for detection monitoring wells are <br /> included in Appendix E. The following inorganic constituents exhibited an increasing trend <br /> according to the Sen's Slope analysis: barium at AMW-6 and AMW-14, bicarbonate at AMW-6, <br /> AMW-7, AMW-12, and AMW-13, calcium at AMW-14, chloride at AMW-6 and AMW-7, <br /> magnesium at AMW-7 and AMW-14, nitrate at AMW-2, AMW-6, and AMW-7, potassium at <br /> AMW-14, sodium at AMW-14, field specific conductance at AMW-2 and AMW-7, strontium at <br /> AMW-6 and AMW-14, sulfate at AMW-7, and TDS at AMW-7. There were no constituents that <br /> exhibited a statistically significant increasing trend during the third quarter 2008 and also <br /> exceeded their concentration limits. <br /> Sen's Slope analysis identified decreasing trends in the following inorganic parameters: calcium <br /> at AMW-12, chloride at AMW-12, magnesium at AMW-12, nitrate at AMW-13, field specific <br /> conductance at AMW-14, strontium at AMW-12, TDS at AMW-14, and field turbidity at AMW- <br /> 2. <br /> Of the organic constituents that were detected in detection monitoring wells during the third <br /> quarter 2008 monitoring event, none exhibited a statistically significant increasing or decreasing <br /> trend according to the Sen's Slope analysis. <br /> 2.2 Corrective Action Monitoring <br /> Groundwater samples were collected by ATC Associates, Inc. from the corrective action <br /> monitoring wells (AMW-1, AMW-4, AMW-5R, AMW-10, AMW-11, AMW-18, and AMW-19) <br /> during the third quarter 2008 monitoring event. Corrective action monitoring well AMW-5R is a <br /> replacement for corrective action monitoring well AMW-5. The field results provided by ATC <br /> Associates, Inc. and laboratory results provided by BC Laboratories, Inc. for the third quarter <br /> 2008 corrective action sampling are summarized on Table 2.3. <br /> VOCs have been consistently detected in samples from corrective action monitoring wells AMW- <br /> 1, AMW-4, AMW-10, and AMW-11. AMW-5/5R, AMW-18, and AMW-19 have previously <br /> exhibited sporadic VOC detections. <br /> The historical groundwater data for the corrective action monitoring wells are presented in <br /> Appendix F. The data are graphed on time series concentration plots, included in Appendix G. <br /> 3 <br />