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Work Plan for Additional Assessment <br /> ARCO Service Station 2130 <br /> Stockton, California <br /> Page 3 o 15 <br /> SENSITIVE RECEPTORS <br /> Two active water supply wells are located within 2,000 feet of ARCO Station 2130. The <br /> wells are operated by the City of Stockton Municipal Utilities Department (CSMUD) . City <br /> Well #4 is located approximately 1 ,200 feet south southeast of the site on Segovia Lane. It <br /> is 600 feet deep and has a production capacity of 1 .5 million gallons per day (MGD) . City <br /> Well #12 is located approximately 1 ,600 feet south of the site at 341 Leslie Avenue. It is <br /> 410 feet deep and has a production capacity of 0.82 MGD. No other wells were located <br /> within 2,000 feet of the site (URS, 2004) . <br /> URS performed a sensitive receptor survey of the site in 2004. No surface water bodies, <br /> schools or wildlife habitats were identified within 500 feet of the site. The nearest school <br /> identified is Pulliam Elementary located approximately 1 ,300 feet southeast of the site. <br /> CHARACTERIZATION STATUS <br /> Hydrocarbons in the unsaturated zone appear to be confined primarily to the former UST <br /> area . The lateral extent of impacted soil generally increases with depth , particularly in the <br /> area beneath the pump islands. However, because the water table has risen to <br /> approximately 40 feet bgs, the impacted soil locations are now below the water table. <br /> The mass of TPHg in soil prior to remedial action at the site was calculated to be 10,782 <br /> pounds of TPHg . The operation of the SVE system removed approximately 9, 109 pounds <br /> of TPHg . Therefore , a net of 1 ,673 pounds of TPHg remain at the site (URS, 2004) . The <br /> remaining contamination may be present in either the soil or groundwater. <br /> The historical direction of groundwater flow beneath the site has been variable (reported <br /> toward the southeast, northeast, and east) . Review of historical groundwater monitoring <br /> data (since mid-2001 ) indicates that flow has predominantly been toward the southeast. <br /> TPHg impacted groundwater is generally confined to the vicinity of the dispenser islands <br /> and the UST complex. The historic maximum dissolved concentration of GRO was 340,000 <br /> micrograms per liter (Ng/L) in vapor well VW- 1 in May 1997. During the third quarter 2006, <br /> the maximum dissolved GRO concentration was 21 , 000 pg/L in VW- 10. Historically, <br /> downgradient well MW-6 has contained relatively low concentrations of GRO. However, <br /> the highest concentration detected was in second quarter 2006 at 2,800 pg/L. Fourth <br /> quarter 2006 GRO concentrations in MW-6 were 98 pg/L. <br /> Benzene concentrations in groundwater are primarily located in the former UST and <br /> dispenser island areas. The maximum benzene concentrations reported in groundwater <br /> have been in vapor extraction wells VW-8 and VW- 10, which are located approximately 20 <br /> feet south-southeast of the dispenser islands. The maximum benzene concentration <br /> detected during the fourth quarter 2006 was 1 ,300 pg/L in VW- 10. <br /> The lateral extent of methyl tert butyl ether (MtBE) in the shallow water bearing zone is <br /> delineated by the existing monitoring well network. Concentrations up to 14. 1 pg/L (9/2/99) <br /> have been reported in off- site well MW-6, which is located downgradient from the pump <br /> islands and UST complex. However, MtBE has not been detected in MW-6 since <br /> December 2003, suggesting that MW-6 currently delineates the downgradient extent of the <br /> dissolved MtBE. <br /> 1 ,2- DCA concentrations in groundwater are primarily located in the dispenser island areas <br /> and east of the USTs. The maximum 1 ,2-DCA concentration reported in groundwater was <br /> in vapor extraction well VW-5 (660 pg/L) in March 2003. The maximum 1 ,2- DCA <br /> concentration detected during the fourth quarter 2006 was 270 pg/L in VW-5. <br />