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S E C ® f - - -- - - <br /> ' Cleanup Plan <br /> October 27, 2003 <br /> Page 5 <br /> 20, and MW-21). Wells MW-14 through MW-16 were used for separate phase hydrocarbon <br /> ' (SPH) recovery and wells MW-18 and MW-19 were used for hydraulic containment (PEG, <br /> 1995). <br /> ■ In August of 1993, Geraghty & Miller, Inc. (G&M) performed a site assessment. Twenty soil <br /> ' borings were drilled in the farm field adjacent to the site. The results of groundwater <br /> samples collected from all 20 borings indicated total petroleum hydrocarbons as diesel <br /> (TPHd), total petroleum hydrocarbons as gasoline (TPHg), benzene and toluene <br /> concentrations were all non-detect(PEG, 1995). <br /> ■ In January of 1994, a groundwater remediation system was installed at the site for SPH <br /> recovery and hydraulic containment. The remedial system was initiated in February of 1994 <br /> and continued until February of 1996. During this time period, groundwater was extracted <br /> from wells, MW-18 and MW-19 (for hydraulic containment of groundwater), and SPH was <br /> recovered from wells, MW-14, MW-15, and MW-16 (PEG, 1995). <br /> ■ In June 1994, Touchtone Development observed the removal of one 10,000-gallon double <br /> ' walled fiberglass UST, pump island, and associated piping from the former Keylock Terminal <br /> Area. Two soil samples were collected from the former pump island area. Groundwater was <br /> observed in the tank excavation at approximately 8 feet bgs. (PEG, 1995). <br /> • In May 1995, Pacific Environmental Group submitted a Problem Assessment Report (PEG, <br /> 1995). The principal findings of the PAR are listed below: <br /> ' 1. The lateral and vertical extent of dissolved hydrocarbons in the lower water bearing <br /> zones was adequately defined. <br /> 2. Continued operation of the containment system, including the pumping of <br /> ' groundwater from the extraction wells maintained the shallow groundwater plume on <br /> site. <br /> 3. Continued SPH recovery and extraction of dissolved-phase hydrocarbons from three <br /> I ' wells within the SPH plume on site reduced hydrocarbon mass in groundwater. <br /> • On March 25, 1996, a dual extraction system (DE) system began continuous operation. The <br /> ' DE system was comprised of 14 DE wells (MW-1, MW-2, MW-7, MW-8, MW-14, MW-15, <br /> MW-16, and DE-1 through DE-7), a water knockout tank, an oil/water separator, four <br /> granular activated carbon vessels arranged in series, and a thermal oxidizer. In May of <br /> 1997, site data suggested the onsite SPH plume had been substantially diminished by the <br /> ' DE system. In addition, groundwater influent concentrations of TPHd had declined from <br /> 69,000 micrograms per liter (Ng/L) to 5,300 and influent vapor concentrations had declined <br /> from 300 parts per million by volume (ppmv) to 21 ppmv (SECOR, 1997). The DE system <br /> was shut down in June of 1997. Temporary shutdown of the DE system was approved by <br /> Ms. Gail Wiggett of the RWQCB during a meeting on June 2, 1997. <br /> ' From September of 2001 through April of 2002, SECOR conducted a six-month ISO-GEN TM <br /> pilot test/feasibility study for groundwater treatment. The pilot test included the installation of <br /> . six four-inch test wells (TW-1 through TW-6) and nine two-inch ISO-GEN TM monitoring wells <br /> ' (MW-24A through MW-32A). The groundwater monitoring wells and ISO-GENTm remediation <br /> I:\Chevron\1001621\REPORTS\2003\2003-Cleanup Plan\Cleanup Plan.doc <br />