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I <br /> Geological TuhAks Inc. Page 4 <br /> Additional Site Characterization and <br /> 3"t Quarter Groundwater Monitoring <br /> Project No.989.2 <br /> October 31,2002 <br /> 0.020 inch screened interval and was topped by a two foot bentonite pellet transition seal <br /> installed on top of the filter pack. A surface seal was achieved by pumping a neat cement <br /> grout (augmented with <4% bentonite). The wells were surged using a clean surge block to <br /> achieve maximum filter pack density prior to installing the bentonite transition seal. The <br /> well was secured with a locking watertight cap encased in a flush mounted traffic rated well <br /> box. The boring logs (Appendix B) contain the details of construction. <br /> Soil cuttings and drilling decontamination water were placed in DOT-17 55-gallon drums <br /> and stored on site until their disposal can be arranged. <br /> ' 2.2 Soil Investigation <br /> ' 2.2.1 Soil Sampling Procedure <br /> On July 30, 2002, V&W Drilling and Geological Technics personal mobilized to the site. A <br /> GTI geologist collected soil samples and maintained a log from the soil borings. The <br /> samples were gathered in 6.0-inch brass liners using a 2A-inch modified California split <br /> spoon sampler. The middle 6.0-inch brass liner was selected for laboratory analyses. The <br /> ends were covered with Teflon sheets and sealed with plastic caps. The brass liners and <br /> plastic caps were washed with an Alconox solution and double rinsed prior to use. <br /> The sampling technician wore disposable gloves while collecting all samples. <br /> Soil samples from MW-7, MW-9, and MW-101 were submitted for laboratory analysis and <br /> a screening process was used to gather information through field observations. Soil samples <br /> were not collected from MW-8 due to the drilling method discussed in section 2.1. The <br /> field screening included: <br /> ' • Sediment type, especially grain size and clay content <br /> • Moisture content <br /> ' 0 Visible evidence of contamination (i.e., color change due to reduction of iron or <br /> discoloration from hydrocarbons and other pollutants) <br /> • Odor (OVM was not functioning and field observations were noted relating to odor in <br /> soil samples) <br /> Details on the geology encountered during the well installation, as well as the field <br /> observations, are included in Section 3.2, Geology and Field Observations. <br /> See Appendix B, Boring Logs for more information. <br /> ' 2.2.2 Soil Laboratory Analyses <br /> The following summarizes the soil sample testing used for this phase of work. The soil <br /> samples collected on July 30, 2002, were delivered to Sherwood Labs (California ELAP No. <br /> 1400), of Hilmar, California, for the following analyses: <br /> • Benzene, toluene, ethylbcnzene and xylene (BTEX) by EPA method 8020 <br /> ' • Gasoline range petroleum hydrocarbons (TPH-Gasoline)by EPA method 8015(m) <br /> • Volatile Organic Compounds by EPA method 8260 <br /> ❑ MTBE, DIPE, ETBE, TAME, TBA, 1,2 DCA and EDB <br />