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I <br /> I l <br /> S E C 0 R <br /> Attachment 1 <br /> iSite History , <br /> Four spills have been documented at the Site The first spill occurred on June 9, 1984 and consisted <br /> of 13,000 gallons of gasoline, diesel and heating oil Soil was excavated immediately after the spill <br /> in the spill area until no subjective evidence of hydrocarbons remained The second spill was a tank I' <br /> overflow in August 1990 consisting of approximately 300 gallons of gasoline The third spill occurred <br /> in August 1998, when an unknown volume of gasoline was released as a result of overfilling tank T- <br /> 137 In November 1999, an unknown quantity of red dye diesel was released from a tanker overfill <br /> at the loading racks <br /> Since December 1983, 23 monitoring wells (MW-1 through MW-23) and three piezometers (T-1 <br /> through T-3) have been installed at the Site Well T-2 has since been destroyed and well MW-9 has <br /> been inaccessible since 1992 With the exception of four wells, all are constructed to monitor the <br /> shallow water-bearing zones to depths of 25 to 30 feet bgs Four wells (MW-12, MW-13, MW-22, <br /> and MW-23) were constructed to monitor a lower water-bearing zone at an approximate depth of <br /> approximately 48 feet bgs <br /> Geraghty & Miller, Inc (G&M) performed a Site assessment in August 1993 Twenty soil borings <br /> were drilled in the farm field adjacent to the Site Groundwater samples collected from all 20 borings <br /> were reported as non-detect for total petroleum hydrocarbons as diesel (TPHd), total petroleum <br /> hydrocarbons as gasoline (TPHg), benzene and toluene (G&M 1994) ' <br /> A groundwater remediation system was installed at the Site in January 1994 for product recovery <br /> and hydraulic containment Extraction of groundwater from five wells on Site was initiated in <br /> February 1994, and continued until February 1996 Two wells, MW-18 and MW-19, were used for <br /> hydraulic containment of the groundwater plume and three wells, MW-14, MW-15, and MW-16, were <br /> utilized for product recovery <br /> A dual phase extraction system (DPE) began continuous operation on March 25, 1996 The DPE <br /> system was comprised of 14 DE wells (MW-1, MW-2, MW-7, MW-8, MW-14, MW-15, MW-16, and <br /> DE-1 through DE-7), a water knockout tank, an oil/water separator, four granular activated carbon <br /> vessels arranged in series for groundwater treatment, and a thermal oxidizer for vapor treatment In <br /> May 1997, evidence suggested that the separate phase hydrocarbon (SPH) plume on Site had been <br /> substantially diminished by the DPE system In addition, influent water concentrations had declined <br /> significantly and influent vapor concentrations had declined to near non-detect levels since system <br /> startup The DPE system was shut down in June 1997 Temporary shutdown of the DPE system <br /> was approved by Ms Gail Wiggett of the Regional Water Quality Control Board (RWQCB) in a <br /> meeting on June 2, 1997 <br /> An ongoing feasibility study for groundwater treatment has included a six-month in-situ stable oxygen <br /> generator (ISO-GEN) pilot test that concluded in April, 2002 This pilot test included the installation <br /> of six four-inch test wells (TW-1 through TW-6) and nine two-inch ISO-GEN monitoring wells (MW- r' <br /> 24A through MW-32A) <br /> I <br />