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0 <br />;iECEIVED <br />RIVER CITY PETROLEUM (CONNELL MOTOR) - NO FURTHER ACTION REQUIRED FACT SHEETi t 2 0 2012 <br />River City Petroleum (Connell Motor) is location at 2211 North Wilson Way, Stockton, California on the west <br />side of North Wilson Way. The main structure occupying the site is a large warehouse/truck ay AL HEALTH <br />building. The site is currently used as a commercial tire service facility. Historically, a forklift and commercial VICES <br />truck repair company operated throughout the large warehouse building; waste from the repair operation was <br />apparently released through a drain line in the western portion of the site. A Phase I site investigation of the <br />property conducted in 1999-2000, determined that waste water with solvents and oils were present in the soil <br />and shallow ground water, west of the building. A shallow dissolved Stoddard solvent plume was identified; <br />since 1999-2000, the plume has demonstrated a decreasing trend in dissolved concentrations of all suspected <br />released chemicals. <br />The eastern portion of the site was formerly a fuel card-lock fueling station. This commercial diesel and <br />gasoline fueling operation utilized underground storage tanks (USTs) for fuel storage. In October 1986, four <br />10,000-gallon, steel, USTs were removed from the site; it was known at that time an unauthorized release of <br />hydrocarbons had occurred at the site based on the site inspection log. In June 1998, three fiberglass USTs <br />were removed. Hydrocarbon-impacted soil was encountered beneath the dispenser and the UST piping. <br />Subsequently, a limited volume of impacted soil was excavated and removed and the excavation was <br />backfilled. It was determined that a release of petroleum hydrocarbons [TPH-g, TPH-d, and benzene, toluene, <br />ethylbenzene and xylene (BTEX)] had occurred from dispenser lines. The highest TPH-g and BTEX impact to soil <br />in the upper soil zone is present at monitoring well borings throughout the former UST area. The highest TPH- <br />g impact to soil near the water table and below the water table, to a depth of 75 feet bsg, occurred in the UST <br />area. The aerial extent of the shallow soil contamination is limited and surrounding the former UST dispenser <br />area and not likely present in shallow soil off-site. Since the site is fully paved, there are no direct exposure <br />routes to the residual impacted soil. <br />There are forty-eight ground water monitoring wells at the site which will be destroyed following site closure. <br />Relatively significant TPH-g and BTEX compounds concentrations were previously detected in ground water <br />samples collected directly west of the dispenser island. TPH-g and BTEX compounds were detected in ground <br />water samples collected directly east of the former dispenser island, in the shallow ground water and towards <br />the west under the building at the site. The vertical and the lateral extent of TPH and BTEX have been defined <br />by monitoring well samples. Once released to the subsurface, the historical fuel contained 1,2-DCA (former <br />leaded gasoline), which migrated to deeper depths between 100 and 200 feet. The investigations to date <br />suggest that the source of the 1,2-DCA was the former USTs at the site. 1,2-DCA is the most widespread <br />contaminant released at the site and underlies the western side of the building (within the former Stoddard <br />plume area). <br />Beginning in November 2004, a soil-vapor extraction (SVE) unit began operation at the site, to recover and <br />mitigate the hydrocarbon releases. Remediation wells were installed in soil near the former UST and dispenser <br />area and at the western side of the building. In-situ air sparging (IAS) wells were installed near the former UST <br />dispenser area and east within the building. Beginning in April 2007, the IAS system began to inject air beneath <br />the water table to remediate deeper impacted ground water. The mass of hydrocarbons removed by the SVE <br />system demonstrated successful remediation; a total mass of approximately 41,097 pounds (lbs) of TPH-g, <br />equivalent to a total volume of 6,500 gallons of TPHg, were documented to have been removed since <br />remediation began. Dissolved petroleum hydrocarbon concentrations (well samples) have declined near the <br />former UST area and are attenuating, following site remediation.