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GEOMATRIX <br /> Mr. Robert Mihalovich <br /> Chevron Environmental Management Company <br /> April 3, 2002 <br /> Page 5 <br /> A fifth soil boring (SB-13) will be advanced downgradient of petroleum affected soil to approxi- <br /> mately 10 feet below the water table (estimated depth of 35 to 40 feet bgs) and a soil sample will <br /> be collected from the most visually affected soil within the soil column and the terminus of the <br /> boring. If visually affected soil is not observed in the soil column, a soil sample will be collected <br /> from the capillary fringe and the boring terminus instead. The soil samples will be analyzed for <br /> TPHc, BTEX, and PAHs. In addition, a grab groundwater sample will be collected to evaluate <br /> the downgradient extent of organic compounds quantified as TPHd in groundwater. The grab <br /> groundwater sample will be analyzed for TPHg, BTEX, and PAHs. <br /> Groundwater in wells MW-1 through MW-4 will be monitored and sampled to evaluate the con- <br /> sistency of groundwater quality data. It is anticipated that MW-1 will contain separate phase <br /> petroleum; therefore, if evidence of separate phase petroleum is present a groundwater sample <br /> will not be collected and product thickness will be measured, if possible. <br /> Field Procedures and Laboratory Methods <br /> Prior to drilling, Underground Service Alert(USA) will be notified, the soil boring locations will <br /> be cleared by a private underground utility locator, and appropriate permits will be obtained from <br /> the San Joaquin County Public Health Services Environmental Health Division (SJC-EHD). The <br /> borings will be advanced using a hollow stem auger(HSA) drill rig and soil samples collected <br /> using a drive sampler. A nearly continuous core of the soil will be collected, examined, and <br /> logged at each location. Soil samples will be collected in brass sleeves sealed with Teflon sheets, <br /> end caps, and teflon tape. Samples will be labeled and stored in ice-filled coolers and delivered to <br /> a state-certified analytical laboratory under Geomatrix chain-of-custody procedures. <br /> The grab groundwater sample will be collected from boring SB-13 through temporary PVC casing <br /> place through the HSAs within the borehole. Prior to collection, the HSAs will be raised to above <br /> the capillary fringe as to expose the screened section of the casing to the native materials. Fol- <br /> lowing soil and grab groundwater sampling activities, the borings will be backfilled with grout <br /> according to SJC-EHD standards. <br /> Prior to groundwater well sampling activities, groundwater elevations and/or the presence of sepa- <br /> rate phase petroleum will be measure to the 0.01 of a foot using a electronic sounder or interface <br /> probe and wells will be purged until groundwater quality parameters (e.g.,pH, temperature and <br /> specific conductance)have stabilized. Groundwater samples will be collected using a disposable <br /> bailer and will be decanted into 1-liter amber bottles and 40 milliliter(ml) acidified volatile or- <br /> ganic analysis (VOA) vials provided by the laboratory. Samples will be labeled and stored in <br /> ice-filled coolers and delivered to a state-certified analytical laboratory under Geomatrix chain-of- <br /> custody procedures. <br /> The soil samples will be analyzed using the following methods: TPHc (CK to C36 carbon range) <br /> using EPA Method 8015 Modified, BTEX using EPA Method 8021, and PAHs using EPA <br /> Method 8270 SIM. Groundwater samples will be analyzed using the following methods: TPHg <br /> using EPA Method 8015 Modified, BTEX using EPA Method 8021, PAHs using EPA Method <br /> 8270 SIM, and TPHd using EPA Method 8015 Modified. The laboratory will perform the TPHd <br />