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Well Installation and Site Investigation Report <br /> ARCO Facility No.5469 <br /> Stockton,California <br /> Page 5 <br /> method estimates soil lithology by comparing the force (cone bearing pressure) required <br /> to advance the probe (Q) to the friction ratio (Rf) [(Rf equals sleeve friction (FS) divided <br /> by the probe tip load times the penetration pore pressure (Ud)]. A graphical diagram <br /> illustrating CPT interpretations of soil types is included in Appendix C. Computer <br /> generated CPT logs were plotted in the field, providing the field geologist a graphical log <br /> of subsurface soil lithology. The CPT test data report, which includes logs of all CPT <br /> data, graphical geologic logs, and additional information on the CPT technique, is <br /> presented in Appendix C. CPT tests were performed in accordance with American <br /> Society of Testing and Materials (ASTM) Method D3441. The location of boring CPT-1 <br /> is included on Figure 2. <br /> Soil samples were collected by driving a 1.7-inch diameter piston-type sampler, equipped <br /> with two pre-cleaned 1.25-inch diameter by 6-inch long brass sleeves, into undisturbed soil <br /> at the desired sampling interval. Additional sleeves of soil collected at each sampling <br /> interval were field screened for volatile organic compounds using a photoionization detector <br /> (PID). The soil samples were classified onsite using the Unified Soil Classification System. <br /> The lowermost intact sample tube from each interval was retained for analysis. The sample <br /> tube ends were covered with Teflon' sheets and tight fitting plastic caps. Once labeled and <br /> sealed, the samples were placed in an ice-chilled cooler. Each sample was identified on a <br /> chain-of custody form that followed the samples to the analyzing laboratory. Soil sampling <br /> intervals, soil descriptions, and PID readings are included on the borehole sampling log <br /> presented in Appendix B. <br /> Stratus and Gregg returned to the site on November 21, 2002, to collect grab groundwater <br /> samples using the Hydropunch" technique. Groundwater samples were collected by <br /> pushing the HydropunchT" sampler, with 2-inch diameter steel rods, to the desired <br /> sampling interval. The CPT operator subsequently pulled up on the steel rods, exposing a <br /> 4-foot long PVC screen. Samples were collected by lowering a metal bailer within the <br /> steel rods. Groundwater was collected in the bailer and placed in properly preserved <br /> glass sample containers provided by the laboratory. Following collection, the samples <br /> were placed in an ice-chilled cooler. Each sample was appropriately labeled and <br /> identified on a chain-of-custody form. Groundwater sampling intervals are included on <br /> the borehole sampling log presented in Appendix B. <br /> .Analytical Methods <br /> Soil and groundwater samples were forwarded to Sequoia Analytical, Inc., a California <br /> state-certified laboratory (ELAP #1210), for chemical analysis under strict chain-of-custody <br /> procedures. Soil samples were analyzed for TPHG using USEPA Method 8015B Modified, <br /> for benzene, toluene, ethylbenzene, and total xylenes (BTEX) using USEPA Method <br /> 8021B, and for MTBE, TBA, ethyl tertiary butyl ether (ETBE), di-isopropyl ether (DIPE), <br /> tertiary amyl methyl ether (TAME), and 1,2-dichloroethane (1,2-DCA) using USEPA <br /> P:1Bp-Arco for URS154691Reports\S469report2003.doc <br />