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I <br />' 19 September 2002 <br /> i AGE-NC Project No 98-0534 <br /> Page 2 of 4 <br /> a <br /> 2 2 COLLECTION AND ANALYSIS OF GROUND WATER SAMPLES <br /> I <br /> After the depth to ground water was measured to ensure that a minimum of 80% well-volume <br /> recharge had been achieved, a water sample was collected from each well using a dedicated and <br /> disposable plastic bailer Immediately upon retrieval, samples were transferred into one-liter amber <br /> bottles and three 40-m1 EPA-approved volatile organic analysis(VOA)vials containing 0 5 ml 18% <br /> hydrochloric acid as a sample preservative The samples were logged on a chain-of-custody form and <br /> stored in a chilled container under ice The samples were later transported under chain-of-custody <br /> to McCampbell Analytical Inc (MAI),a State of California Department of Health Services (DHS)- <br /> certified analytical laboratory for analysis The samples were analyzed for <br /> • Total petroleum hydrocarbons quantified as gasoline (TPH-g) and diesel (TPH-d) in <br /> r accordance with EPA Method 8015 Modified, <br />■ • Benzene, toluene, ethylbenzene and total xylenes (BTEX) and methyl tertiary-butyl ether <br /> (MTBE) in accordance with EPA Method 8020, and <br /> • The oxygenated compounds di-isopropyl ether (DIPE), ethyl tertiary-butyl ether (ETBE), <br /> MTBE,tertiary-amyl methyl ether(TAME),tertiary butanol(TBA),ethanol,methanol, 1,2- <br /> dibromoethane (EDB) and 1,2-dichloroethane(1,2-DCA) in accordance with EPA Method <br /> 8260-Modified <br /> 3.0. FINDINGS <br /> Ground water elevation, flow direction and gradient were determined from field data collected on <br /> 14 June 2002, the contaminant impact to ground water was assessed from the laboratory data <br /> 3 1 GROUND WATER ELEVATION AND GRADIENT <br /> The relative elevation of ground water in each well was calculated by subtracting the depth to ground <br /> water from the relative casing elevation (Table 1) The average depth to ground water on <br /> 14 June 2002 was 10 feet below the tops of the well casings, presently the water table is at the top <br /> of the screened interval of the wells The water table was inferred to be relatively flat in the area of <br /> the former UST area,but was inferred to form a depression at the northern portion of the site, in the <br /> area of well MW-4, the gradient ranged from essentially flat at the former UST area to 0 05 ft/ft at <br /> the northern edge of the site (Figure 3) <br /> 9 <br /> Advanced GeoEnvi ron mental,Inc <br />