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CL Properties, VI E37801.02A <br /> December 6, 1999 Page 3 <br /> 4.0 PROPOSED INVESTIGATIVE PROCEDURES <br /> This characterization will consist of a field investigation, a laboratory testing program, and <br /> preparation of a technical report. This work plan and the activities summarized below are intended <br /> to be consistent with the requirements of the SJCEHD. Standard operating procedures (SOPs), <br /> relevant to the field and laboratory activities,are described in Appendix A. Specific procedures and <br /> deviations to the SOPS which will be used in this work are summarized in the following sections. <br /> 4.1 Field Investieation: The field investigation will consist of collecting subsurface soil vapor <br /> samples for chemical analyses. <br /> 4.1.1 Soil Sampling: Twining proposes to collect subsurface soil vapor samples at the project site <br /> from sampling points advanced in two locations: <br /> • five sampling points in the estimated former location of the dry cleaners ; and <br /> a two sampling points adjacent(across West Sonora Street)to the current dry cleaner facility. <br /> The proposed soil sampling points will not be advanced in an easement or right-of-way controlled <br /> by a municipal government. Nor will the sampling points be advanced to less than 15 above the <br /> estimated groundwater depth. Therefore,municipal permits will not be required for this assessment. <br /> An application for a soil boring permit will be submitted to the SJCEHD with this work plan. <br /> The soil vapor assessment includes the collection of five soil vapor samples from the vicinity of the <br /> former dry cleaning facility located at 513 South Center Street and two soil vapor samples adjacent <br /> (across West Sonora Street) from the active dry cleaning facility. The soil vapor sampling points <br /> will placed in the vicinity of most likely areas of contamination, including the exterior sewer and <br /> subsurface utility trenches. A manually operated slide hammer will be used to drive the sampling <br /> rods with a 1 inch expendable sampling tip to the desired depth(three to five feet BSG). The rods <br /> will be partially retracted in preparation for sampling. Prior to applying vacuum to the sampling <br /> system,hydrated bentonite will be placed within the annular space between the outer diameter of the <br /> rods and the sides of the borehole. The purpose of this is to provide additional security against <br /> drawing ambient air into the borehole. <br /> The sampling points will connected to a vacuum pump with clean polyethylene tubing and an in-line <br /> regulator. A maximum gas flow rate of 200 cubic-centimeters per minute will be applied to the <br /> vacuum pump to purge the system of residual gas. A minimum of three tubing volumes will be <br /> purged prior to sample collection to assure that samples are representative of soil vapors. Samples <br /> will then be collected in Tedlar®bags and placed into ice chests containing blue ice for transport to <br /> the off-site laboratory. All reusable sampling equipment will be decontaminated before, and <br /> between uses, in order to minimize the possibility of cross-contamination. The vapor samples will <br /> be analyzed off-site by a state certified and accredited laboratory. <br /> Soil vapor samples will be submitted for laboratory analysis. Sample handling procedures are <br /> summarized in our SOPS. At least one sample per from each boring will be submitted for analysis. <br /> The analytical results for soil vapor samples collected from these sampling points may provide data <br /> on the existence of HVOCs. This data will be evaluated to determine if further assessment of the <br /> extent of HVOC migration in soil and or groundwater is necessary. <br />