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1, <br /> 1 <br /> •k Page 2 <br />' Ms Margaret Lagono <br /> February 21, 1997 <br />' The developed portion of the facility consists of approximately seven acres, is relatively <br /> flat lying, and is almost entirely covered with asphalt and concrete The main facility <br />' building covers approximately two acres. An approximately 1,000-foot-long stormwater <br /> drainage ditch extends westerly from the facility to an intermittent, south-flowing <br /> drainage canal This canal flows into the intermittent Duck Creek, which is located <br /> approximately 900 feet south of the plant <br /> 1 The facility previously had four petroleum hydrocarbon underground storage tanks <br /> (USTs) (see Figure 2, Site Plan) The former 10,000-gallon diesel-fuel tank and two <br />' 6,000-gallon gasoline tanks were located near the southwest corner of the main building <br /> A 20,000-gallon diesel-fuel tank, was located beneath the parking lot on the east side of <br /> the facility (see Figure 2) <br />' The gasoline tanks near the southwest building corner were removed in April 1987 The <br /> westernmost gasoline tank failed a tank integrity test in December 1986 The easternmost <br /> gasoline tank had previously been abandoned in place, prior to 1986, by removing the <br /> fuel and filling the tank with sand The two diesel-fuel USTs were removed in September <br /> 1989 <br /> Approximately 450 cubic yards of soil was excavated during removal of the two USTs in <br /> 1987, of which approximately 120 cubic yards were impacted by gasoline The soil was <br /> disposed of onsite with guidance from the San Joaquin Air Pollution Control District <br /> In July and September 1987, Environmental Science and Engineering, Inc installed three <br /> groundwater monitoring wells (MW-1 through MW-3) In January 1988, Anderson <br /> Consulting Group (ACG) installed wells MW-4 and MW-5 ACG installed wells MW-6 <br />' and MW-7 in February 1990, and MW-8 in September 1990 In March 1994, Philip <br /> (formerly Burlington Environmental) installed wells MW-9 through MW-13 in five <br /> boreholes that were drilled at the facility <br />' Soil samples were collected from the Philip boreholes for chemical analysis Soil sample <br /> hydrocarbon concentrations were all below laboratory method detection limits with the <br /> exception of the 60-foot depth sample from borehole MW-13, which contained 10 <br /> micrograms per kilogram (µg/kg) of benzene This sample was collected at a depth dust <br /> below the groundwater table,and was probably contaminated by petroleum-impacted <br /> groundwater at that location <br /> IPhilip submitted a Remediation System Pilot Test Workplan, dated July 1, 1994, to the <br /> San Joaquin County Environmental Health Division describing proposed groundwater <br /> cleanup technologies These technologies include groundwater sparging combined with <br /> I soil venting Several sparge and vent wells have been installed to implement this <br /> remediation However, active cleanup has been postponed due to pending changes in <br /> related California remediation guidelines In Philip's October 28, 1996, quarterly <br /> monitoring report, Philip recommended performing intrinsic biodegradation analysis to <br /> evaluate the option of passive long-term monitoring versus active remediation <br /> E 121382112599714gtr96 doc <br />