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Lead was detected in all groundwater samples at concentrations between 0.008 parts per <br /> million (ppm; MW-10) and 0.013 ppm (MW-13). The analytical results are summarized in <br /> Table 3. The laboratory report and chain-of-custody are included in Appendix A. <br /> 1,2-Dichloroethane was detected in EW-1, MW-13 and MW-14 at concentrations of 33 ppb, <br /> 14 ppb and 93 ppb, respectively. No other volatile balocarbons were detected in any of the <br /> water samples. The analytical results of the volatile halocarbons are summarized in Table <br /> 4. The laboratory report and chain-of-custody are included in Appendix A. <br /> 5.0 CONCLUSIONS AND RECOMMENDATIONS <br /> 5.1 Groundwater Depth and Flow Direction <br /> The depth to groundwater has decreased approximately 2 feet throughout the site area since <br /> measurements were made in September of 1993. This is in accordance with seasonal <br /> variations of groundwater depth in the region. The groundwater flow direction continues to <br /> be to the south-southwest. <br /> 5.2 Petroleum Hydrocarbon Contamination <br /> There have been several changes in the distribution of contaminants since the September <br /> 1993 sampling event. Concentrations of TPH and BTE&X have decreased significantly in <br /> both MW-14 and EW-1. These two wells are nearest the center of the plume of soil <br /> contamination, and groundwater contamination continues to be greater in these wells. <br /> In contrast, three wells that are located beyond the limits of the soil plume exhibited <br /> increases in groundwater contamination in this quarter. These include two down-gradient <br /> wells (MW-7 and MW-11) and one up-gradient well (MW-10). No contamination was <br /> detected in soil samples when these wells were drilled. None of these wells were <br /> contaminated in the September event, although contamination has been detected in all of <br /> these wells in one or more previous monitoring events. It is therefore difficult to discern a <br /> consistent pattern of contamination in the data, but it does not appear that fluctuations in <br /> groundwater contamination are related to seasonal fluctuations in the water table. <br /> 5.3 Volatile Halocarbon Contamination <br /> For the second consecutive quarter, 1,2-Dichloroethane (1,2-DCA) was detected only in <br /> samples from EW-1, MW-13 and MW-14. The concentration in each well has increased <br /> since the previous quarter. <br /> In June of 1993, Sun-Tech Environmental reported several volatile halocarbons in MW-6, <br /> MW-10, MW-11 and MW-12 in addition to EW-1, MW-13 and MW-14. It appears that <br /> although the number of wells containing detectable concentrations of halocarbons has <br /> Cmbpol AedServ:va,Inc. 12 <br /> 13M.0. MM QR <br />