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SITE HISTORY <br />A Phase I Preliminary Hazardous Materials Site Assessment (PSA) was prepared by <br />Kleinfelder of Sacramento, California, and dated November 16, 1988 The PSA was <br />prepared for Nomellini 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 at one time Analytical results of soil samples <br />collected beneath the tanks indicated that petroleum hydrocarbons 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 />removed 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 i I feet below ground surface Soil <br />samples were screened for organic vapors using a photoionization 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, Nomellmi Construction decided to backfill <br />the excavation with clean fill and further assess the extent of the contamination with a <br />t soil boring program <br />In May, 1989, Kleinfelder supervised the drilling of nine soil borings (B-1 through <br />1 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 siu-face <br />In February, 1991, Kleinfelder dulled three borings B-10 through B-12 These <br />borings were subsequently converted into monitor wells MW -1 through MW -3 <br />TPH-g was detected in the groundwater in February, 1991 in MW -1 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 in MW -I The groundwater gradient <br />has generally varied between the northeast to southeast <br />