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with three pre-cleaned 2-inch by 6-inch brass sleeves The samples were collected at five-foot <br /> intervals, using a 140 pound hammer to advance the sampler 18 inches The number of <br /> blows required to advance the sampler in 6-inch increments was recorded on the boring logs <br /> To avoid cross contamination, the sampling equipment was washed in an alconox solution <br /> and rinsed twice with water prior to each sampling run <br /> For each sample, both ends of the lead tube were covered with aluminum sheets, capped <br /> and sealed with tape. The samples were then stored on ice and transported under chain-of- <br /> custody to McCampbell Analytical in Pacheco, CA <br /> 3.2 Logging <br /> Soil was extruded from the second brass tube and screened for the presence of organic <br /> vapors, using a PID, and the readings were recorded on the boring logs The soil was then <br /> described in accordance with the Unified Soil Classification System (see Boring Logs, <br /> Appendix B) <br /> 33 Well Completion <br /> The boring was completed as a groundwater monitoring well using a 2-inch diameter PVC <br /> casing with 0 020 screen from 29 to 49 feet The filter pack (#3 lonestar sand) was installed <br /> from 27 to 49 feet Bentonite chips were used to make a two foot plug and the well was <br /> grouted to the surface with Portland Cement <br /> 3.4 Monitoring Well Sampling <br /> On June 2 1994 theroundwater depths in all wells were measured relative to the top of <br /> g P <br /> the casing using a Sohnst water level meter. The relative piezometric levels and hydraulic <br /> gradient were determined from these data In accordance with an agreement between the <br /> PHS/EHD and Comfort Air, only MW-5 was sampled <br /> After groundwater depths were measured, a PVC bailer was used to surge MW-5 and <br /> remove sediment A two-stage submersible pump was then used to purge standing water <br /> from the well. Approximately 9 gallons of water were removed to stabilize temperature, pH <br /> Iand conductivity (see Table 1) Stabilization parameters were measured at one-gallon <br /> intervals using an ICM water analyzer <br /> After stabilization, additional water was then removed (total 25 gallons) to completely <br /> develop MW-5. All water removed from MW-5 was stored in a 55-gallon drum on-site <br /> Following stabilization and development, a water sample was collected from MW-5 using <br /> a new, disposable plastic bailer The sample was collected in three 40 ml EPA vials <br /> I <br /> Owbrad A.&S./...k I— 5 <br /> ckd.n MW ImuM-sorra...ism <br /> I <br />