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2,2 Corrective Action Monitoring 0 <br />During the second quarter 2011 monitoring event, Del -Tech collected groundwater samples from <br />corrective action monitoring wells (AMW-1, AMW-5R, AMW-10, AMW-11, AMW-18, AMW- <br />19, and AMW-19BR). Corrective action monitoring well AMW-5R is a replacement for <br />corrective action monitoring well AMW-5. Corrective action monitoring well AMW-19BR is a <br />replacement for corrective action monitoring well AMW-19B. The field results provided by Del - <br />Tech and laboratory results provided by BC Labs for the second quarter 2011 corrective action <br />monitoring event are summarized on Table 2.3. The historical groundwater data for the <br />corrective action monitoring wells are presented in Appendix F. Times series concentration plots <br />of historical groundwater data for the detection monitoring wells are presented in Appendix G. <br />For VOCs, only those compounds that exhibited detections at corrective action monitoring wells <br />during the second quarter 2011 monitoring event were plotted. <br />During the second quarter 2011, there were no VOCs detected above the laboratory RL in wells <br />AMW-4, AMW-5R, AMW-11, or AMW-18. 1,1-Dichloroethane, 1,4 -dichlorobenzene, benzene, <br />chlorobenzene, cis -1,2 -dichlorobenzene, diisopropyl ether, tetracholorethene, and trichloroethene <br />were detected at AMW-1 above the laboratory RL. cis-1,2-Dichloroethene and tetrachloroethene <br />were detected at AMW-10 above the laboratory RL. Tetrachioroethene and trichloroethene were <br />detected at AMW-19 above the laboratory RL. 1,1-Dichloroethane, cis-l,2-dichloroethene, <br />dichlorodifluoromethane, tetrachloroethene, and trichloroethene were detected at AMW-19BR <br />above the laboratory RL. <br />Historical data from the corrective action monitoring wells from March 1994 to the present were <br />analyzed for temporal trends using Mann -Kendall / Sen's Slope trend analysis. Graphs and <br />summary tables of the Mann -Kendall / Sen's Slope analyses for corrective action monitoring <br />wells are presented in Appendix G. <br />Table 2.4 summarizes the results of the corrective action monitoring well trend analysis. Mann - <br />Kendall / Sen's Slope analysis identified significant increasing statistical trends in the following <br />inorganic constituents: arsenic at AMW-10, barium at AMW-1, bicarbonate alkalinity at AMW-1 <br />and AMW-5R, chloride at AMW-5R, nitrate at AMW-4 and AMW-5R, field pH at AMW-4, <br />AMW-5R, AMW-11, and AMW-19BR, potassium at AMW-5R, sodium at AMW-5R, field <br />specific conductance at W-1 and AMW-5R, sulfate at AMW-5R and AMW-10, TDS at <br />AMW-5R, and field turbidity at AMW-5R and AMW-10. Carbonate at AMW-5R exhibited an <br />apparent increasing trend according to the Mann -Kendall / Sen's Slope analysis, but this trend is <br />due to a historical increase in the laboratory RL. <br />Mann -Kendall / Sen's Slope analysis identified significant decreasing statistical trends in the <br />following inorganic constituents: barium at AMW-4, AMW-10, and AMW-11, bicarbonate <br />alkalinity at AMW-4, AM -10, and AMW-11, calcium at AMW-4, AMW-10 and AMW-11, <br />chloride at AMW-1, AMW-4, AMW-10, AMW-11, and AMW-18, gasoline -range hydrocarbons <br />at AMW-4, magnesium at AMW-4, AMW-10, and AMW-11, nitrate at AMW-1, AMW-10, <br />AMW-18, AMW-19, and AMW-19BR, field pH at AMW-1, potassium at AMW-4, AMW-10, <br />AMW-11, AMW-18, and AMW-19BR, sodium at AMW-10, AMW-18, AMW-19, and AMW- <br />1913R, field specific conductance at AMW4, and AMW-11, strontium at AMW-4 and AMW-10, <br />sulfate at AMW-1, AMW-19, and AMW-19BR, field temperature at AMW-4 and AMW-11, TDS <br />at AMW-4, AMW-10, AMW-11, and AMW-18, and field turbidity at AMW-1 and AMW-4. <br />Mann -Kendall / Sen's Slope analysis identified significant increasing statistical trends in the <br />following VOCs: 1,1-diehloroethane at AMW-1; chlorobenzene at AMW-1; cis-1,2- <br />