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ATTACHMENT A v <br /> FIELD AND LABORATORY PROCEDURES <br /> Chevron Service Station 20-1761, 1103 South Main Street, Manteca, CA <br /> zip-lock bag or a mason jar). The container was warmed for approximately 20 minutes (in the <br /> sun), then the head-space within was tested for total organic vapor, measured in parts per <br /> million as benzene (ppm; volume/volume). The instrument was calibrated prior to drilling <br /> using a 100-ppm isobutylene standard (its air) and a sensitivity factor of 55, which relates the <br /> photo-ionization potential of benzene to that of isobutylene at 100 ppm. The results of the <br /> field testing were noted on the boring logs. PID and FID readings are useful for indicating <br /> relative levels of contamination, but cannot be used to evaluate hydrocarbon levels with the <br /> confidence of laboratory analyses. <br /> Soil Sampling for Stockpiled Soil <br /> Soil samples were collected by advancing a 2-inch diameter brass sample liner into the soil <br /> stockpile, after removing approximately 6-inches to 1-foot of surface material in the sample <br /> location. One composite sample was collected per approximately 100 cubic yards of soil. <br /> Soil samples for chemical analysis were retained in the brass liners, labeled, and capped with <br /> Teflon sheets and plastic end caps. The samples were then sealed in zip-lock bags, placed on <br /> ice, and transported to the laboratory accompanied by the appropriate chain-of-custody <br /> documentation. <br /> Laboratory Procedures for Soil and Groundwater Samples <br /> Selected soil and groundwater samples were analyzed for the presence of total petroleum <br /> hydrocarbons as gasoline (TPHg) using modified EPA Method 8015, benzene, toluene, <br /> ethylbenzene, xylenes (BTEX), and methyl tertiary butyl ether (MtBE) by EPA Method 8260. <br /> Soil Cuttings and Rinsate Water <br /> Soil cuttings generated during drilling operations were temporarily stored onsite and covered <br /> with plastic sheeting pending characterization and disposal. Soil cuttings were then removed <br /> by Chevron's disposal contractor to an appropriate disposal facility. Water generated during <br /> steam cleaning and well development was temporarily stored in DOT-approved 55-gallon <br /> drums pending transport by Chevron's disposal contractor to an appropriate disposal or <br /> treatment facility. Soil cuttings and rinsate water drums were temporarily stored onsite for <br /> approximately 4 to 8 weeks. <br />