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S E C 0 R <br /> r� <br /> �i <br /> Mr Ed Ralston <br /> September 7, 2004 <br /> Page 3 � <br /> impact in soil and groundwater downgradient of the site and to determine the placement of wells that <br /> will complete delineation of the plume <br /> • Health and Safety As required by the Occupational Health and Safety Administration <br /> (OSHA) Standard "Hazardous Waste Operations and Emergency Response" guidelines (29 <br /> CFR 1910120), and by California Occupational Health and Safety Administration <br /> (Cal-OSHA) "Hazardous Waste Operations and Emergency Response" guidelines (CCR Title <br /> 8, Section 5192), SECOR prepared a site-specific Health and Safety Plan (HASP) Prior to <br /> the commencement of fieldwork, the HASP was updated with appropriate field personnel and <br /> subcontractor information The field staff and contractors reviewed the HASP before <br /> beginning field operations at the site <br /> • Permitting Prior to initiating work, SECOR obtained soil boring and well installation permits <br /> form SJCEH, encroachment permits form the City of Lathrop, and obtained an access <br /> agreement to 16200 Cambridge Street SJCEHD soil boring and well installation permits and <br /> City of Lathrop encroachment permits are included as Attachment B <br /> • Geoprobe Soil Borings The off-site exploratory geoprobe soil borings were advanced r� <br /> using standard direct push equipment to an approximate depth of 15 feet bgs Soil samples <br /> were collected at depths of 5, 10, and 15 feet bgs for logging purposes with the 10 and 15 <br /> foot samples submitted for laboratory analysis Temporary casing was installed in each <br /> boring and a groundwater"grab" sample was collected at each geoprobe boring location with <br /> a clean disposable bailer Boring logs are included as Attachment C <br /> • Soil Analytical Results Soil samples at 10 and 15 feet bgs from geoprobe borings GP-10 <br /> through GP-14 were collected and submitted for laboratory analysis Soil samples were <br /> analyzed for TPHg, BTEX, and fuel oxygenates (MtBE, EtBE, DIPE, TAME, TBA, EDB, 1,2- <br /> DCA, and ethanol) by EPA Method 8260B TPHg, xylenes, and ethanol were reported In soil <br /> sample GP-13@10 at concentrations of 1 2 mg/kg, 0 0095 mg/kg, and 0 65 mg/kg, <br /> respectively The laboratory report noted that the TPHg detection did meet the gasoline <br /> standard No detectable concentrations of petroleum hydrocarbons were reported in the soil <br /> samples from GP-10, GP-11, GP-12, and GP-14 Soil analytical results are included in Table <br /> 1 Field and laboratory procedures are presented in Attachment D The certified laboratory <br /> analytical report and chain-of-custody documentation are presented in Attachment E <br /> • Groundwater Analytical Results Groundwater "grab" samples collected from each of the <br /> geoprobe boring locations were analyzed for TPHg, BTEX, and fuel oxygenates (MtBE, <br /> EtBE, DIPE, TAME, TBA, EDB, 1,2-DCA, and ethanol) by EPA Method 8260B L MtBE was <br /> reported at a concentration of 0 88 ug/L In boring location GP-12 and ethanol was reported at <br /> a concentration of 610 ug/L in boring location GP-13 Groundwater analytical results are rl <br /> included in Table 2 and shown on Figure 2 The certified laboratory analytical report and <br /> chain-of-custody documentation are presented in Attachment E iI <br /> • Stockpiled Soil One drum of soil was generated during the assessment activities Filter <br /> Recycling Service removed the drum for proper disposal <br /> w <br /> a <br /> 1ConocoPhdlipslTosco Markelrng1120511Reportslgeoprobe rpt 9-04 doc <br />