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r: <br /> • 01 November 2002 <br /> AGE-NC Project No 97-0312 <br /> Page 2 of 4 <br /> locations The ground water elevation in each well and ground water flow direction for the site were <br /> �' <br /> determined from the data collected (Table 1) <br /> After measuring ground water depths, monitoring wells UST-2 through UST-6 were purged using <br /> new disposable plastic bailers Between 2 5 and 8 0 gallons of water were removed from wells <br /> UST-2 through UST-6 (a minimum of three casing-water volumes per well) Ground water was <br /> purged from near the top of the water column to remove water trapped within the unscreened interval <br /> of the well casings Temperature, pH and conductivity of purged water were measured at regular <br /> Intervals during purging using an Oakton water analyzer The recorded field data and logs are <br /> Included. in Appendix A Purged water was stored on-site in 55-gallon DOT-approved drums <br /> pending laboratory analysis <br /> In addition, the large on-site domestic well was purged and sampled on 29 August 2002 To purge <br /> the large domestic well, a drain valve was opened on the water storage tank and the pump was <br /> allowed to cycle on and off for approximately 15 minutes The small domestic well was found to be <br /> out of service, the electrical service was disconnected and the distribution piping was truncated and <br /> capped <br /> • <br /> 23 COLLECTION OF GROUND WATER SAMPLES <br /> The depth to water in the monitoring wells was re-measured following purging to assure a minimum <br /> of 80%recharge prior to sampling Water samples were retrieved from each purged monitoring well <br /> using new disposable bailers and an equipment blank was collected from the discharge hose of the <br /> 2-inch submersible purge pump following decontamination To sample the domestic wells, a <br /> sampling port was opened at the well head and samples were collected from the sampling port while <br /> the pump was operating to obtain fresh water samples Each sample was transferred into four <br /> laboratory-supplied 40-m1 EPA-approved VOA vials containing 0 5 ml of 18% hydrochloric acid <br /> as a sample preservative and into one 1-liter amber bottle without preservative <br /> The samples were labeled, placed in a chilled container and transported under chain-of-custody to <br /> McCampbell Analytical Inc (MAI), a California Department of Health Services (DHS)-certified <br /> analytical laboratory in Pacheco The samples were analyzed for <br /> • Total petroleum hydrocarbons quantified as gasoline (TPH-g) and diesel (TPH-d) in <br /> accordance with EPA Methods 5030/8015m and 355018015m, respectively, <br /> • Benzene, toluene, ethylbenzene and total xylenes (BTEX) and the fuel additives methyl <br /> tertiary-butyl ether (MTBE), di-isopropyl ether (DIPE), ethyl tertiary-butyl ether (ETBE), <br /> tertiary-amyl methyl ether (TAME) and tertiary-butanol (TBA), 1,2-dibromoethane(EDB) <br /> • and 1,2-dichloroethane (1,2-DCA) in accordance with EPA Method 8260B, and <br /> Advanced GeoEnvironmental,Inc <br />