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discharged. According to the Operations Manager, the LCRS operated effectively during <br /> the fourth quarter 2008. <br /> Leachate samples were collected from the pond on a monthly basis and analyzed in the <br /> field for pH and specific conductance. In addition to monthly monitoring, the leachate is <br /> sampled annually during the fourth quarter monitoring period for the parameters listed in <br /> Table 2-1. Results of monthly field monitoring measurements and analytical results for <br /> the fourth quarter 2008 are presented in Table 3-5. As shown on Table 3-5, nine <br /> dissolved metal constituents were detected with five measured above the PQL; two <br /> VOCS were detected with one measured above the PQL; and one SVOCs (bis[2- <br /> ethylhexyl] phthalate), a confirmed laboratory contaminant,was measured. No <br /> pesticides, or herbicides were detected in the leachate sample collected during the fourth <br /> quarter 2008 monitoring period. Review of the November 2008 leachate sample data <br /> indicates no potential new COCs, and therefore, no retesting is required. <br /> 3.1.9 Groundwater Treatment Facility Operations <br /> The Groundwater Treatment Facility(GTF) at the Austin Unit has been operational since <br /> 1994 to mitigate impacts from landfill releases. At the GTF, contaminated groundwater <br /> is extracted by two wells (EW-1 and EW-2), treated, and discharged to an infiltration <br /> pond. The GTF operated for 2,078 hours between October I and December 31, 2008, at <br /> 94.1 percent uptime, and treated 18.497 million gallons of groundwater at an average <br /> flow rate of 148 gallons per minute, or 0.214 million gallons per day. During this period, <br /> the GTF removed approximately 1.9 pounds of VOCs. (CH2M Hill, 2008). <br /> 3.2 SUMMARY <br /> Groundwater quality conditions beneath the Austin Unit during the fourth quarter 2008 <br /> monitoring period were generally similar to historical results. Excluding suspected <br /> field/laboratory contaminants, CLs were exceeded in DMP wells AMW-6, AMW-7, <br /> AMW-13, and AMW-14. However, none of the CL exceedances exhibited statistically <br /> significant increasing trends. In the CAP wells, trend analyses are performed instead of <br /> comparison to CLs. During the current monitoring period, one or more statistically <br /> significant increasing trends were noted for VOC constituents in CAP wells AMW-1, <br /> AMW-10, and AMW-19, while decreasing VOC trends were noted in CAP wells AMW- <br /> 4,AMW-5/5R, AMW-10, and AMW-11. The increasing vinyl chloride and/or cis-1,2- <br /> DCE trends in wells AMW-I and AMW-10 suggest that active reductive dechlorination <br /> is occurring in the vicinity of these wells. <br /> During the fourth quarter 2008 monitoring period the leachate results are generally <br /> similar to those observed historically. During the fourth quarter 2008 monitoring period, <br /> nine dissolved metal constituents were detected with five measured above the PQL; two <br /> VOLS were detected with one measured above the PQL; and one SVOCs (bis[2- <br /> ethy1hexyl] phthalate), a confirmed laboratory contaminant, was measured. No <br /> pesticides, or herbicides were detected in the leachate sample collected during the fourth <br /> M0008001 0\FA-4Q08.doc <br /> 13 GeoLogic Associates <br />