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08 September 2009 <br />AGE -NC Project No. 03-1055 <br />Page l I of 19 <br />Adams Street (B 13 through B 14) and from within the sidewalk of the westside of Adams Street (B 10 <br />and B11) for the collection of soil samples; a total of 24 soil samples were analyzed from the <br />borings. TPH-g were reported in all borings, except B10 (located immediately east of the former <br />Chevron's 5,000 -gallon UST area), at concentrations ranging between 2.0 mg/kg (BI t-15) and <br />160 mg/kg (BI1-10); TPH-g were only reported within the saturated zone (between 10 feet and <br />15 feet bsg). The highest concentrations of TPH-g reported during this investigation were from <br />boring B 11, located immediately down -gradient of the former Chevron UST areas, and equi-gradient <br />to the former Tracy Diner UST areas. <br />In April and May 2008, 14 soil samples were analyzed from pilot soil borings MW 11, MW 13, and <br />MW 14. Constituents were only reported in the samples collected from MW 11; TPH-g and TPR -d <br />were reported at maximum concentrations of 71 mg/kg (MW 11-22) and 400 mg/kg (MW 1140), <br />respectively. Pilot boring MW 11 was located immediately down -gradient of the former Chevron <br />UST areas. <br />Historical analytical results of soil samples are summarized in Tables 1. <br />�%W 3.1. DISTRIBUTION OF PETROLEUM HYDROCARBON -IMPACTED SOIL <br />Laboratory analyses of soil samples indicate the source of petroleum hydrocarbon -impacts to soil <br />on-site are the former 500 -gallon UST and northernmost dispenser. Once released to the subsurface, <br />contaminants migrated through fine grained clay and silt mixes, to a vertical depth of approximately <br />15 feet bsg, at which point contaminants encountered a more porous sandy unit and began to migrate <br />laterally. The direction of lateral migration was predominantly toward the northeast, the preferred <br />ground water flow direction (Appendix G). The vertical migration of soil contamination appeared <br />to be slowed by the silty and clayey layers encountered below the sand unit. Geologic cross sections <br />are depicted on Figures 4, 5 and 6. <br />Boring MW I 1 exhibited the only `deep' (beyond 15 feet bsg) soil contamination throughout all <br />subsurface investigations; contamination encountered in this boring is likely from the former <br />Chevron site. Additionally, the impacted area of Adams Street in the vicinity of borings B 13, B 14 <br />and BIS is likely the result of the former Chevron release as evidenced by the following: 1) the <br />borings are located down -gradient of the former Chevron UST areas and significantly impacted <br />boring SB2; 2) the borings are located in an upgradient location to the Tracy Diner former UST <br />areas; and 3) the non -detection of constituents in boring MW14-15, located between the former <br />Tracy Diner UST areas and borings B 13 through B 15. <br />Former Tracy Diner and former Chevron soil sample locations and the estimated extent of TPH-g <br />impacted soil beneath the site and the former Chevron site are depicted in cross sectional view in <br />Advanced GeoEnviromnental, Inc. <br />