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statistical trend. A Wilcoxon rank-sum test comparing the calcium data at background wells <br /> MW-6A and MW-7A to the data at MW-10A(a= 0.05) indicates that the calcium data at MW- <br /> l0A are statistically distinct from those at the background wells. The Wilcoxon rank sum plot is <br /> presented in Appendix E. The presence of stable calcium concentrations at MW-l0A that are <br /> statistically distinct from background indicates that the concentration limit exceedance for <br /> calcium at MW-10A in the first quarter 2012 is likely due to spatial variation in the natural <br /> groundwater geochemistry at the site. <br /> The first quarter 2012 chloride concentration at well MW-9B (150 mg/L) is within the range of <br /> concentrations observed at MW-9B since the beginning of background in May 2005 (109 mg/L - <br /> 180 mg/L). As discussed above, chloride at MW-9B does not exhibit a significant upward <br /> statistical trend. A Wilcoxon rank-sum test comparing the chloride data at background wells <br /> MW-6A and MW-7A to the data at MW-9B (a=0.05) indicates that the chloride data at MW-913 <br /> are statistically distinct from those at the background wells. The Wilcoxon rank sum plot is <br /> presented in Appendix E. The presence of stable chloride concentrations at MW-9B that are <br /> statistically distinct from background indicates that the concentration limit exceedance for <br /> chloride at MW-9B in the first quarter 2012 is likely due to spatial variation in the natural <br /> groundwater geochemistry at the site. <br /> The first quarter 2012 chloride concentration at well MW-10A (170 mg/L) is within the range of <br /> concentrations observed at MW-l0A since the beginning of background in May 2005 (5 3.5 mg/L <br /> - 210 mg/L). As discussed above, chloride at MW-l0A does not exhibit a significant upward <br /> statistical trend. A Wilcoxon rank-sum test comparing the chloride data at background wells <br /> MW-6A and MW-7A to the data at MW-10A (a= 0.05) indicates that the chloride data at MW- <br /> l0A are statistically distinct from those at the background wells. The Wilcoxon rank sum plot is <br /> presented in Appendix E. The presence of stable chloride concentrations at MW-l0A that are <br /> statistically distinct from background indicates that the concentration limit exceedance for <br /> chloride at MW-l0A in the first quarter 2012 is likely due to spatial variation in the natural <br /> groundwater geochemistry at the site. <br /> The first quarter 2012 magnesium concentration at well MW-l0A (94 mg/L) is within the range <br /> of concentrations observed at MW-l0A since the beginning of background in May 2005 (23.8 <br /> mg/L - 120 mg/L). As discussed above, magnesium at MW-l0A does not exhibit a significant <br /> upward statistical trend. A Wilcoxon rank-sum test comparing the magnesium data at <br /> background wells MW-6A and MW-7A to the data at MW-l0A (a = 0.05) indicates that the <br /> magnesium data at MW-l0A are statistically distinct from those at the background wells. The <br /> Wilcoxon rank sum plot is presented in Appendix E. The presence of stable magnesium <br /> concentrations at MW-l0A that are statistically distinct from background indicates that the <br /> concentration limit exceedance for magnesium at MW-10A in the first quarter 2012 is likely due <br /> to spatial variation in the natural groundwater geochemistry at the site. <br /> The first quarter 2012 field temperature value at well MW-9B (24.6 °C) is within the range of <br /> temperatures observed at MW-9B since the beginning of background in March 1997 (20.0 °C - <br /> 28.0°C). As discussed above, field temperature at MW-9B does not exhibit a significant upward <br /> statistical trend. A Wilcoxon rank-sum test comparing the field temperature data at background <br /> wells MW-6A and MW-7A to the data at MW-9B (a= 0.05) indicates that the field temperature <br /> data at MW-9B are statistically distinct from those at the background wells. The Wilcoxon rank <br /> sum plot is presented in Appendix E. The presence of stable field temperatures at MW-9B that <br /> are statistically distinct from background temperatures indicates that the concentration limit <br /> exceedance for field temperature at MW-9B in the first quarter 2012 is likely due to spatial <br /> variation in the natural groundwater temperatures at the site. <br /> The first quarter 2012 field temperature value at well MW-l0A (25.8 °C) is within the range of <br /> temperatures observed at MW-l0A since the beginning of background in March 1997 (13.5 °C - <br />