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Ms. Penny Fottrell GEOMATRIX <br /> Chevron Environmental Management Company <br /> September 12, 2002 <br /> Page 4 <br /> I <br /> y' Borings will be advanced using a hollow stem auger rig. Borings M113-1 and M113-2 will be <br /> advanced to the bottom of visually affected soil to assess the vertical extent of petroleum hydro- <br /> carbons in the vicinity of borings GP 96 and GP 120,respectively. The remaining borings (MH3-3 <br /> through MH3-7)will be advanced to depths up to 30 feet bgs to assess the lateral extent of affected <br /> soil and groundwater quality. Additional step-out borings may be advanced if petroleum-stained <br /> soil is observed in borings M113-3 through - . Typica y, step-out borings will be—s—pa-c—eT_ <br /> approximately 50 to 100 feet from borings that contain visually-affected soil. A continuous core of <br /> n� the soil will be collected and examined from each location and the lithology will be logged by a <br /> Geomatrix field geologist. In addition, organic vapor meter(OVM)readings will be taken an <br /> recorded at various depths. <br /> Soil samples will be collected in butyrate sleeves or brass tubes sealed with Teflon sheets, end <br /> caps, and tape. Sample depths will be as follows: <br /> • To assess potential risk posed by petroleum hydrocarbons, soil samples will be collected <br /> from 2 feet bgs and from the most affected soil shallower than 10 feet bgs at all boring <br /> locations. If no affected soil is observed above 10 feet bgs, soils samples will be collected <br /> �_. from depths of 2 and 6 feet bgs. <br /> • In boring M113-1 and MH3-2 a soil sample also will be collected from a depth immedi- <br /> ately beneath observed staining to confirm the vertical extent of affected soil. <br /> To assess lateral extent soil samples will be collected in borings MH3-3 through M113-7 <br /> from the most visibly affected portion of the soil core, regardless of depth. If no petro- <br /> leum hydrocarbon affected soil is observed a soil sample will be collected from the inter- <br /> val in which petroleum hydrocarbon affected soil was encountered in the closest previous <br /> 1, onngs. <br /> z. Grab groundwater samples will be collected from borings M113-1 (anticipated to be within <br /> affected soil)and from upgradient and downgradient borings where stained soil is not observed. <br /> To minimize the amount of affected sediment entrained in the sample from MH3-1, a pre-packed <br /> well will be placed in the borehole and the sample will be collected using a pump set at a low flow <br /> rate. For the remaining grab groundwater samples, a temporary slotted polyvinyl chloride (PVC) <br /> ' well casing will be placed in the borehole and grab groundwater samples will be collected using a <br /> disposable bailer. After collection of the samples, the PVC casing will be removed and the bore- <br /> holes will be grouted to ground surface. <br /> Soil and groundwater samples will be labeled and stored in an ice-cooled chest until transfer to a <br /> California-certified laboratory under Geomatrix chain-of-custody procedures. All borings will be <br /> grouted to ground surface upon completion. <br /> Soil samples will be analyzed for total petroleum hydrocarbons (TPH)quantified as crude oil <br /> (TPHc) using EPA Method 8015M; BTEX using EPA Method 8021; and PAHs using EPA <br /> Method 8270 with a selective ion monitoring system (SIMS). Grab groundwater samples will be <br /> analyzed for TPHg and TPHd using EPA Method 8015M;BTEX using EPA Method 8021; and <br />