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Atlantic Richfield Company 2 <br /> ARCO 595,6100 North Highway 99,Stockton,CA December 11,2001 <br /> Ethyl tert-but 1 ether ( tBE)� tert-amyl methyl ether(TAME), 1> <br /> 2-dichloroethane (1,2- <br /> DCA), <br /> and ethylene dibromide (EDB) were reported as nondetectable in the samples <br /> Approximately 189 tons of soil generated during the removal of the underground <br /> facilities and the trenching for new piping were disposed of at BFI Landfill in Livermore, <br />' California Mstoncal maps and soil analysis data are included in Attachment B <br /> From June 1 to June 6, 2000, four groundwater monitoring wells (MW-1 through Mw- <br /> 4) and three soil borings (B-1, B-2, and B-3) were completed at the site by West Hazmat <br /> Drilling of Rancho Cordova, California, under the direction of SECOR staff Site <br /> assessment activities showed that petroleum hydrocarbons had impacted the soil and <br />' groundwater beneath the site Historical soil sample data is included in Attachment B, <br /> and historical groundwater data in Tables 1 and 2 <br />' Quarterly groundwater monitoring is currently ongoing Groundwater flow direction is <br /> generally to the west and northwest <br />' ASSESSMENT ACTIVITIES AND FINDINGS <br /> Prior to beginning site assessment activities, SECOR secured well permits from SJCEHD <br /> t Caltrans approved an encroachment permit for access to the offsite well MW-6, and San <br /> Joaquin County Public Works approved an encroachment permit for wells MW-5 and MW- <br /> 7 From July 17 to July 24, 2001, three groundwater monitoring wells (MW-5 through <br /> MW-7) and two soil borings (PSB-1 and PSB-2) were completed Groundwater <br /> monitoring wells MW-5, MW-6, and MW-7 were set at 70 feet below ground surface (bgs) <br /> and screened from 50 to 70 feet bgs Borings PSB-1 and PSB-2 were drilled to a total <br /> depth of 100 feet bgs, and backfilled with grout upon completion Well completion details <br /> are included as Table 3 Boring logs are included as Attachment C Field procedures are <br />' described in Attachment D <br /> Subsurface Conditions <br />' Soil encountered during drilling activities generally consisted of interbedded layers of <br /> sands, silts, and clays The most prominent soil types beneath the site appear to be sandy <br /> silts and silty sands First groundwater was encountered at approximately 50 to 64 feet <br />' bgs Groundwater levels stabilized at approximately 60 feet bgs The groundwater <br /> appears to be under unconfined conditions within sand to silty clay Geologic cross- <br /> sections are included as Figures 3 and 4 <br /> Soil Sampling and Analysis <br /> Borings PSB-I and PSB-2 were continuously cored from 50 to 100 feet bgs to evaluate <br /> changes in soil stratigraphy Soil samples from MW-5, MW-6, and MW-7 were <br /> collected at 5-foot intervals Selected samples were analyzed for TPHg by EPA Method <br />' 8015, benzene, toluene, ethylbenzene, xylenes (BTEX), and MtBE by EPA Method <br /> 8020, and fuel oxygenates, including MtBE, TAME,DIPE, ELBE, TBA, 1,2 DCA, and <br />' EDB by EPA Method 8260 <br />' 077 43029 330/well msta112 doe <br />