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S E C 0 R <br /> 7-Eleven Store #32262 <br /> Site Assessment Report <br /> December 12, 2003 <br /> Page 3 <br /> x� <br /> SECOR prepared a site-specific Health and Safety Plan for well installation and sampling activities at <br /> the site as required by the Occupational Health and Safety Administration (OSHA) Standard <br /> "Hazardous Waste Operations and Emergency Response" guidelines (29 CFR 1910 120) The <br /> document was reviewed and signed by all SECOR personnel and subcontractors performing work at <br /> the site <br /> Prior to conducting subsurface work at the site, USA was contacted to delineate subsurface utilities <br /> near the site with surface markings In addition, a private utility locator service was contracted to <br /> clear each of the proposed drilling locations <br /> Soil Borings <br /> On October 15-17, 2003, SECOR supervised Cascade Drilling of Rancho Cordova, California, drill <br /> and install six groundwater monitoring wells at the locations shown on Figure 2 MW-1 through MW- <br /> 5 were drilled to an approximate depth of 17 feet bgs MW-6D was drilled to an approximate depth <br /> of 51 feet bgs. (Table 3) <br /> The five shallow wells were installed to 17 feet bgs using a truck-mounted drilling rig equipped with <br /> 8-inch-diameter hollow-stem augers (HSAs) Deep welt MW-6D was installed to a depth of <br /> approximately 51 feet bgs using 15-inch HSAs from ground surface to 32 feet bgs to allow for <br /> conductor casing installation, which is described below MW-613 was then drilled from 32 to 51 feet <br /> bgs using 8-inch HSAs through the conductor casing <br /> Soil Sampling <br /> Soil samples were collected continuously in borings MW-1, MW-3, MW-4, and MW-6D, and at five- <br /> foot intervals in MW-2 and MW-5, using a split spoon sampler lined with 2-inch diameter by 6-inch- <br /> long brass sample tubes Downhole drilling equipment was steam cleaned before drilling each <br /> borehole, and sampling equipment was cleaned between each sampling interval Each soil sample <br /> was screened for hydrocarbon vapors using a portable photoionization detector (PID) Soils <br /> encountered during drilling were logged using the Unified Sod Classification System by a SECOR <br /> field geologist, working under the supervision of a California Registered Geologist Selected sod <br /> samples were sent to Kiff Analytical in Davis, CA and analyzed for TPHg, BTEX, fuel oxygenates <br /> MtBE, TBA, TAME, ethyl-tert-butyl ether (EtBE), diisopropyl ether (DIPE), 1,2-dichloroethane (1,2- <br /> DCA), and ethylene dibromide (EDB) by EPA Method 82608 <br /> Lithology <br /> Based on the description of the soil samples collected from the six new wells, the lithology <br /> encountered consists mainly of silt, with minor amounts of gravel and clay, from ground surface to 17 <br /> feet bgs In MW-6, silt, with minor amounts of sand and clay, was encountered from ground surface <br /> to total depth (51 feet bgs) Groundwater was observed at approximately 10 feet bgs No obvious ' <br /> low permeability, confining layer of clay or silt was observed in the soil borings Copies of the sod <br /> boring logs are included in Attachment B Copies of the field notes collected during well installation <br /> are provided in Attachment C <br /> T <br /> 32262 Assessment Report SECOR International Incorporated <br /> x <br /> r <br />