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a� <br /> All drill cuttings will be stored temporarily on site on top of and covered by plastic <br /> sheeting pending laboratory analysis of the boring samples. Additional sampling and <br /> testing of the stockpiled soil may be required in order to meet landfill disposal criteria. <br /> Following receipt of the laboratory results, the drill cuttings will be trensported from the <br /> site by a state-licensed hauler to an appropriate disposal facility. <br /> Upon completion of drilling, any bore holes not utilized for monito0n.0 well construction <br /> will be backfilled with a 9-sack slurry. The slurry will not free tall more than ten (10)feet. <br /> The slurry will be placed by tremie to depths greater than ten feet. <br /> GROUNDWATER MONITORING WELL CONSTiRIICTION <br /> For:hs proposed groundwater monitoring wells MW-4 and MW-5, approximately 20-feet <br /> of 4-inch diameter PVC screen with 0.020-inch slots will be installed from the bottom of <br /> the boring to approximately 5 feet above the observed water table. <br /> For the proposed groundwater monitoring well/vapor extraction well MW-113, <br /> approximarnly 20 feet of 6-inch diameter PVC screen with 0.020-inch slots will be installed <br /> from the bottom of the boring to approximately 5 feet above the observed water table. <br /> Figure 4 shows a typical monitoring well construction detail. Solid-walled, 4- or 6-inch <br /> diameter PVC will be installed from the top of the screened interval to the surface. The <br /> filter will consist of No.3 Lone Star sand, and will be placed to an elevation approximately <br /> z-;set above the top of the screen. The approximate volume of sand necessary to <br /> construct the filter will be calculated in order to identify and prevent bridging during filter <br /> placement. Bentonite pellets will be placed on top of the filter pack for an approximate <br /> 24eet interval. A sand-cement grout will be placed from the top of the Bentonite pellets <br /> to the surface. <br /> The monitoring wells will be developed, purged and sempled in accordance with Aegis' <br /> SOP. Groundwater samples will be sent to a state-certified Iauoratory fcr analysis. The <br /> groundwater monitoring wells will then be surveyed and water levels W] be measured. <br /> The water samples will be analyzed for concentrations of: a) total purgeabie petroleum <br /> hydrocarbons, as gasoline (TPPH); b) benzene, toluene, xylenes, and ethylbenzene <br /> (BTX&E) and c) ethylene dibromide and 1-2 dichloroethane (EDB & EDC), by CAL DHS <br /> DRAFT TPH (modified) and EPA Method 8240 (GC/MS). <br /> ANALYTICAL LABORATORY AND PRACTICAL QUANTITATION LIMITS <br /> The laboratory to be used for the analyses discussed above is tentatively identified as <br /> Coast-to-Coast Arafytical services of Napa, California, a state-certified analytical <br /> laboratory. Selected soil and groundwater samples will be collected and submitted to the <br /> laboratory in accordance with Aegis' SOP. <br /> 90a9BA.WPy .4' <br /> E <br />