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4.0 Chemical Analysis—GeoProbe Samples <br /> Twelve (12) soil samples and six (6) groundwater samples ftom the GeoProbe. borings were <br /> analyzed at Kiff Analytical LI-C, a State-certified analytical laboratory in Davis, California. All <br /> samples will be tested for the following; Total Petroleum hydrocarbons as Gasoline (TPHG) and <br /> Diesel (TPHD), Benzene (B), Toluene (T), Ethylbenzene (E), Xylene (X), Volatile Organic <br /> Compounds (IOC), Methyl-tert-butyl-ether (MTBE), and fuel. oxygenates tert-Aixiyl-Methyl- <br /> Ether (TAME), Ethyl-cert-Butyl-Eller (ETBE), Di-Isopropyl Ether (DJ11E) and tert-Butyl <br /> Alcohol (TBA), 1-2, Diehloroethane (1-21)CA), Ethylene DiBromide (EDB) and. Ethanol (F_,th) <br /> and Methanol (Meth) using EPA. Methods 35 10/801 S, 8020 and 8260/82608. The analyses were <br /> performed and a"normal"ten-day turnaround (see 'fables 2 and 3). <br /> 5.0 SJC/EHD GeoProbe Data Review <br /> S.ICIEHD performed a data review of the GeoProbe borings and Wright sent a reap of the <br /> proposed groundwater monitoring well locations; an interim report was not prepared. Once these <br /> locations were reviewed and approved by EHD, then the four monitoring wells were installed. <br /> 6.0 Field Methods—Drillingand Sampling Monitoring Well Exploratory Borings <br /> Four (4) exploratory borings were drilled at approved PHS/ET.4D locations following review of <br /> the Limited Phase 11 Investigation data. Drilling and well installation permits were secured from <br /> the S.1C/EHD, and an underground utility clearance was completed prior to doing the fieldwork. <br /> A site safety plan and traffic control plan was prepared for the site work. The boreholes were <br /> drilled with a truck-mounted hollow-stem auger rig. All drilling equipment and sampling tools <br /> were cleaned prior to arriving, and before leaving the site. The decontamination process used a <br /> tri-phosphate soap to wash the soil sampler between each sample run and each borehole. Augers <br /> and drill rods were decontaminated in similar fashion between each borehole using a pressure <br /> washer as needed to remove soiVsediment adhering to the augers, rods and drill bits. The <br /> hollow-stem augers were advanced and discrete soil samples collected at Five-foot intervals of <br /> depth from each borehole_ The augers and drill rod were advanced to the desired sampling depth <br /> interval, and a drive split spoon sampler driver ahead of the drill bit For collecting soil samples. <br /> The boreholes were logged at five-foot intervals using the Unified Soil Classification System. <br /> under the supervision of a professional geologist. Additional lithologic information was <br /> collected as needed to describe the subsurface geology. The soil samples were collected at rive- <br /> foot intervals, and at intervals of obvious contamination and at stratigraphic features of interest if <br /> needed at the discretion of the geologist. Soil samples were field screened with a portable <br /> photoionization detector (PFD) for fuel hydrocarbons vapor and staining. Samples showing <br /> elevated PID readings were selected for chemical analysis. Upon completion of the borehole <br /> drilling and collection of soil samples, the four boreholes were converted to groundwater <br /> monitoring wells using the procedures discussed below. <br /> Page 4 of 14 <br />