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rl n <br /> 14 May 2004 <br /> AGE-NC Project No. 95-0137 <br /> Page 2 of 4 <br /> After recording water level measurements, disposable plastic bailers were used to purge the wells <br /> of standing water. Approximately 3 to 5 gallons of water(a minimum of 3 casing water-volumes per <br /> well)were removed from MW-1 through MW-5;well MW-2 was purged dry after 3 gallons of water <br /> were removed. <br /> Ground water temperature,pH and conductivity were measured at regular intervals during purging <br /> using an Oakton water analyzer. Purged ground water was containerized in properly labeled <br /> Department of Transportation(DOT)-approved model 17H 55-gallon drums and was stored on-site. <br /> Field sheets and data are included in Appendix A. <br /> 2.1.2. Collection and Analysis of Ground Water Samples <br /> Water samples were collected from the purged wells using new disposable plastic bailers after <br /> allowing the wells to achieve a minimum 80%recovery of the pre-purge water volume. Each sample <br /> was transferred into three 40-m1 EPA-approved volatile organic analysis (VOA) vials and into one <br /> 1-liter amber bottle. Samples were properly labeled, stored in a chilled container and transported <br /> under chain-of-custody to Cal Tech Environmental Laboratories (CTEL) a California Department <br /> of Health Services (DHS)-certified laboratory in Paramount. Each sample was analyzed for. <br /> • Total petroleum hydrocarbons quantified as gasoline and diesel (TPH-g and TPH-d) in <br /> accordance with EPA Method 8015 Modified; and <br /> • BTEX compounds and the oxygenating fuel additives: methyl tertiary butyl ether(MTBE), <br /> tertiary butyl alcohol(TBA),di-isopropyl ether(DIPE),ethyl tertiary butyl ether(ETBE)and <br /> tertiary amyl methyl ether(TAME),ethylene dibromide(EDB)and 1,2 dichloroethane(1,2- <br /> DCA) in accordance with EPA Methods 8260. <br /> 3.0. FINDINGS <br /> Ground water elevation, flow direction and gradient were determined from field data collected on <br /> 23 March 2004; the contaminant impact to ground water was quantified from the ground water <br /> laboratory data. <br /> 3.1. GROUND WATER GRADIENT AND FLOW DIRECTION <br /> Depths to ground water during the March 2004 monitoring event ranged from 25.27 to 26.46 feet <br /> below the well casing tops;the depth to ground water remained stable between the November 2003 <br /> .! and March 2004 monitoring events. The calculated ground water elevations ranged from 31.28 feet <br /> (MW-4) to 31.63 feet (MW-3) and 34.72 feet (MW-5), and ground water flow was inferred to be <br /> Advanced G eoEnvi ron menta 1,Inc. <br />