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3 <br /> 35 Groundwater Sampling <br /> Monitoring wells MW-1, MW-2, and MW-3, were sampled by Blaine Tech Services on <br /> December 19, 1994 following the Wright Groundwater Sampling Protocol (Appendix B) Prior <br /> to sampling, the wells were purged of approximately 4 well volumes The groundwater samples <br /> were collected using a Teflon bailer cleaned with an industrial-strength detergent and distilled <br /> water Each sample was labeled and placed on ice in an insulated container for delivery to a <br /> State-certified laboratory, accompanied by chain-of-custody documents Purge water generated <br /> during the sampling process was placed in Department of Transportation-approved 55-gallon <br /> drums and left onsite pending characterization for disposal <br /> 36 Surveying <br /> The monitoring wells were surveyed in January 1995 The elevation of each wellhead was <br /> surveyed to within 0 01 foot with respect to a known benchmark and Mean Sea Level by a <br /> licensed land surveyor The survey data is presented in Appendix C <br /> 4.0 SITE CONDITIONS <br /> 41 Hydrogeology and Subsurface Conditions <br /> In general, the soils encountered in boreholes B-1 through B-7 were relati%ely consistent (Figure <br /> 3) The soil underlying the site is a typical valley alluvial deposit consisting of interbedded and <br /> intermixed clays, silts, sands and gravels as shown on the Boring logs (Appendix C) A silty <br /> clay and sand,, clay occurs from beneath the pavement to a depth of approximately 14 to 16 5 <br /> feet bgs An approximately 1 5 to 2 0 foot thick: siltylclavey sand was observed in boreholes B- <br /> 2/MW-I <br /> - <br /> 21MW-1 and B-5 to a depth of approximately 15 5 to 18'_5 feet bgs The siltylcla,,ey sand laver <br /> was not obser,,ed in B-6/MW-2, however, a gravelly sand Iaver occurs from a depth of <br /> approximately 16 5 to 18 5 feet bgs Below the silty/clayey sand is a silty/sandy clax Iaver <br /> extending to the bottom of boreholes B-2/MW-1, B-6/MW-2, and B-7/MW-3 <br /> Groundwater was encountered in boreholes B-2/MW-1, B-3, B-5, B-6/MW-2, and B-7/MW-3, at <br /> depths ranging from approximately 13 to 14 feet bgs The water-bearing unit at this depth <br /> consists of the silty/claye% sand layer observed in boreholes B-2/MW-1 and B-5 Static water <br /> levels measured after deNelopment of wells MW-1, MW-2, and MW-3 were approximately 9 to <br /> 10 feet below the top of the PVC casing suggesting a semi-confined condition This is an <br /> increase of approximately 3 to 4 feet from first encountered water levels Wright prepared a <br /> groundwater contour map using groundwater elevation data obtained on December 19, 1994 <br /> (Figure 2) The interpreted gradient was approximately 0 003 and flowed in a northerly <br /> direction <br /> 42 Soil Analytical Results <br /> The soil samples were analyzed by Priority Environmental Labs in Milpitas, California, for total <br /> petroleum hydrocarbons as gasoline (TPHG) and benzene, toluene, ethvlbenzene and total <br /> xylenes (BTEX) by Environmental Protection Agency (EPA) SW-846 Methods 8015/8020 <br /> Concentrations of TPHG and BTEX were detected in soil samples from boreholes B-1 and B-2 at <br /> a depth of approximately 9 feet bgs All other analytical results for the soil «ere belovy the <br /> detection limits Results of all soil sample analyses are summarized in Table 1 The laboratory <br /> reports and chain-of-custody documents are included in Appendix D <br /> • <br />