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' SITE HISTORY <br />' A Phase I Preliminary Hazardous Materials Site Assessment (PSA) was prepared by <br /> Kleinfelder of Sacramento, Califoinra, and dated November 16, 1988 The PSA was <br /> piepared for Nomellinr Construction Company, a construction and tool rental <br />' operator <br /> Three underground storage tanks (USTs) formerly located at the subject site were <br /> removed in August, 1988 The tank numbers, sizes, contents and histories were as <br />' follows two 1,000 gallon fuel tanks (containing regular and unleaded gasoline) were <br /> excavated from southeast of the warehouse building One 550 gallon waste oil tank <br /> was excavated from a separate site The subsurface investigations that followed relate <br />' to the two 1,000 gallon fuel tanks The tanks were reported to store unleaded <br /> gasoline may also have held kerosene atone time Analytical results of soil samples <br /> collected beneath the tanks indicated that pets oleum hydi ocarbons and gasoline related <br /> constituents were present in the soil beneath the two 1,000 gallon tanks Constituents <br />' were detected below levels of concern in the sample collected beneath the waste oil <br /> tank Results of this investigation were presented in a Kleinfelder report dated <br /> September 22, 1988 <br /> According to the Kleinfelder Report dated June 14, 1989, additional soil was <br /> temoved from the fuel tanks excavation on November 9, 1988 to further assess the <br /> extent of petroleum hydrocarbon contamination One section of the former tank pit <br /> was excavated to a depth of 19 feet from about 11 feet below ground surface Soil <br /> samples were screened for organic vapors using a photoronization detector(PID) <br /> Organic vapor readings were detected at 408 parts per million (ppm) from a sample <br />' collected at a depth of 19 feet within the former tank pit and 740 ppm from a sample <br /> collected 10 feet away from the excavation at a depth of 16 feet Based on the <br /> positive organic vapor screening results, Nomellini Construction decided to backfill <br />' the excavation with clean fill and further assess the extent of the contamination with a <br /> soil boring program <br />' In May, 1989, Kleinfelder supervised the drilling of nine soil borings (B-1 through <br /> B-9) in the vicinity of the former tank pit Samples were analyzed from depths of <br /> 10 5 to 26 feet Ten of 15 soil samples contained total petroleum hydrocarbons as <br /> gasoline at levels ranging from nondetect to 450 ppm <br />' High concentrations of TPH as gasoline (TPH-g), benzene, toluene, ethylbenzene, <br /> and xylenes (BTEX) were detected just above and below the groundwater surface in <br />' boring B-1 which was located adjacent to the south edge of the. excavation <br /> Similarly, high TPH-g concentrations were detected just above the groundwater <br /> surface in B-2, approximately 20 feet north of the former tank excavation The <br />' remaining samples had relatively low concentrations detected, but TPHs were <br /> consistently detected just above the groundwater surface Groundwater was <br /> encountered at a depth of about 25 feet below ground surface <br /> In February, 1991, Kleinfelder drilled three boi Ings B-10 through B-12 These <br /> borings were subsequently converted into monitor wells MW-1 thiough MW-3 <br /> TPH-g was detected in the groundwater in February, 1991 in MW-I through MW-3 <br /> at concentrations of 1,700 ppm, 10,000 ppm and 1,500 ppm, respectively In June, <br /> 1991, 15 feet of free product was measured to MW-1 The groundwater gradient <br /> has generally varied between the northeast to southeast <br />