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• • • Phase lI ESA Work Plan <br /> San Joaquin Regional Rail Commission <br /> Page 2 <br /> • 1102 E. Weber Ave. (90 feet east of the Site)is the former location of a bulk fuel storage facility <br /> that operated for several decades around the 1950s. According to file review at the San Joaquin <br /> County Environmental Health Department(SJCEHD), 15 USTs were recently removed from this <br /> property. Groundwater at this location may be impacted by petroleum hydrocarbons. <br /> • 936 E. Weber Ave. (200 feet west of the Site) is the location of a former leaking gasoline UST. <br /> According to SJCEHD files, petroleum hydrocarbon-impacted soil and groundwater remains at <br /> this location. <br /> • 931 E. Weber Ave. (350 feet west of the Site) is the location of the nearest groundwater boring <br /> conducted during a Phase II ESA in 2003. Groundwater contained tetrachloroethylene (PCE), a <br /> chlorinated solvent and several SVOCs. <br /> • 800 E. Main St. (700 feet west of the Site) is the location of a former service station. <br /> Groundwater is impacted by petroleum hydrocarbons at this location. <br /> An assumed easterly groundwater gradient direction was utilized when assessing the potential risk posed <br /> to the Site from off-site locations. This assumed groundwater gradient is based upon previous <br /> groundwater monitoring reports for nearby properties. It should be noted, however, that groundwater <br /> gradients in this area have fluctuated significantly over time, and current gradient directions may not <br /> represent historic gradients. <br /> 3.0 FIELD PROCEDURES <br /> 3.1 SOIL SAMPLING PROCEDURES <br /> Two soil sampling locations are planned near the former Western Pacific railroad tracks on the east side <br /> of the property, six sample locations around the perimeter of the train depot, and four sample locations <br /> from the former rail spur areas on the western portion of the Site (Figure 3, Appendix A). Soil samples <br /> will be collected from the surface [0 to 6 inches below ground surface (bgs)] and from the subsurface <br /> (2.0 to 2.5 feet bgs). <br /> Surface soil samples will be collected by removing surface debris; loosening the soil with a stainless steel <br /> shovel,and transferring the soil into 9-ounce (oz.)laboratory-supplied glass jars. Subsurface samples will <br /> either be transferred into 9 oz. laboratory-supplied glass jars, or collected in brass tubes using a slide- <br /> hammer (AST locations). Samples collected in brass tubes will be capped and sealed with Teflon tape <br /> and end caps. Each sample container will be labeled for sample identification and placed in a cooler <br /> chilled with ice. The sampling equipment will be decontaminated by washing with a solution of <br /> laboratory-grade, non-phosphate detergent and double-rinsed with distilled water prior to use at each <br /> sample location. The samples will be shipped under chain-of-custody procedures via courier to <br /> McCampbell Analytical, Inc. a California-certified laboratory (DHS #1644) located in Pittsburgh, <br /> California for analysis. <br /> 3.2 DIRECT PUSH BORING FIELD PROCEDURES <br /> This section includes a description of the site preparation and groundwater sampling procedures. <br /> 3.2.1 Site Preparation <br /> Condor will complete the boring permit applications and obtain the required permits prior to initiating <br /> field work. The proposed boring locations will be marked with white paint and underground services <br /> alert (USA) will be notified at least 48 hours in advance to identify utilities in and near the work area. <br />