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7-Eleven Store#14117 <br /> Corrective Action Plan <br /> October 12, 2007 <br /> Page 5 <br /> Oxygen Injection Well Installation <br /> The proposed oxygen injection wells will be installed at the locations depicted on Figure 2 <br /> using a truck-mounted drilling rig equipped with 8-inch-diameter hollow-stem augers. The <br /> injection wells will be installed to approximately 35 feet bgs (Table 1). Soil samples will be <br /> collected as outlined in Table 4 using a split-spoon sampler lined with 2-inch diameter brass <br /> sample tubes. Downhole drilling equipment will be thoroughly cleaned before drilling each <br /> borehole, and sampling equipment will be cleaned between each sampling interval. Each <br /> soil sample will be screened for hydrocarbon vapors using a portable photoionization <br /> detector (PID). Soils encountered during drilling will be logged by a SECOR field geologist <br /> using the Unified Soil Classification System, working under the supervision of a California <br /> registered geologist. <br /> Soil samples retained for analysis will be sealed with Teflon sheets and plastic caps, then <br /> labeled and placed on ice in an insulated container for delivery to Kiff Analytical located in <br /> Davis, California. Selected soil samples will be analyzed for TPHg, benzene, toluene, <br /> ethylbenzene and xylenes (BTEX), MtBE, TBA, ethyl-tert-butyl ether (EtBE), diisopropyl <br /> ether (DIPE), and tert-amyl-methyl ether (TAME) using U.S. Environmental Protection <br /> Agency (EPA) method 8260B. <br /> Proposed injection wells 1-2 through 1-5 will be constructed using 2-inch diameter Schedule <br /> 40 polyvinyl chloride (PVC) blank casing and 0.020-inch slotted screen. The proposed <br /> injection wells will be constructed with 15 feet of screen set at approximately 20 to 35 feet <br /> bgs. The screen depth may be adjusted based on the lithology encountered in order to <br /> ensure that the top 3 feet of screen is set into the target sand unit at approximately 20-25 <br /> feet bgs and the remaining screen into the large clay and silt unit below (see Attachment <br /> C). The larger screen interval will accommodate alternative oxidant injection technologies <br /> (i.e. iSOCO systems) in the future should modifications to the remedial approach be <br /> necessary. <br /> A sand filter pack will be placed within the annulus of the wells from the bottom of the <br /> borings to approximately 2 feet above the top of the well screens. The annulus of each well <br /> will be sealed with 2 feet of bentonite on top of the sand, and a portland cement/bentonite <br /> grout to the surface. An 8-inch-diameter, traffic-rated, watertight street box will be installed <br /> to protect the well from surface traffic. <br /> Waste Disposal <br /> Soil cuttings, debris and rinsate water generated during drilling operations will be <br /> temporarily stored onsite in properly labeled Department of Transportation (DOT) approved <br /> 55-gallon drums pending characterization, transport and disposal by SECOR's disposal <br /> contractor to an appropriate disposal or treatment facility. <br /> IMPLEMENTATION OF REMEDIAL APPROACH <br /> The proposed oxygen injection wells will be plumbed via a common trench to a single <br /> subsurface well vault located on the western boundary of the site (Figures 2 & 7). <br /> 14117 CAP 10-12-07.doc SECOR International, Inc. <br />