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Appendix D:Field Investigation Procedures and Boring Logs <br /> SOIL SAMPLING <br /> Soil cores were obtained using an approximately 5-foot-long, 3-inch-diameter core barrel <br /> sampler. The core barrel sampler contained a plastic acetate liner that retained a relatively <br /> undisturbed soil core from which samples were collected. The soil samples selected for analysis <br /> were cut from the plastic liners, sealed with plastic end caps and Teflon sheets, labeled with <br /> identifying information, and stored in a pre-chilled ice chest for transportation to the laboratory. <br /> A chain of custody form designating the samples to be analyzed and other information <br /> accompanied the samples to the laboratory. <br /> One soil sample was collected from each boring between ground surface and 5 feet bgs to obtain <br /> a sample for a human health screening evaluation(HHSE). If affected soil was observed in the <br /> boring, a soil sample was collected from the interval that appeared to be the most affected. If <br /> there appeared to be an interval of unaffected soil beneath the affected soil and above <br /> groundwater, a soil sample was also collected from the unaffected interval to obtain vertical <br /> delineation. If no affected soil was observed in the boring, in addition to the HHSE sample one <br /> soil sample was collected just above the groundwater table.2 <br /> GROUNDWATER SAMPLING <br /> Grab groundwater samples were collected by placing a clean, pre-packed well screen into the <br /> borehole and collecting samples using a check valve with poly tubing. The well screen was <br /> inserted into the outer rods of the Geoprobe Dual Tube sampling system, and a polyvinyl <br /> chloride(PVC)riser was screwed into the well screen and plumbed to the ground surface. The <br /> dual-tube rods were retracted, with the well screen and PVC riser remaining in the borehole. <br /> The tubing end of the pump was placed at the midpoint of the groundwater column to minimize <br /> the entrainment of sediment in the groundwater sample, the presence of which could artificially <br /> bias the analytical results. <br /> After purging the well casing, groundwater samples were decanted into EPA-approved <br /> laboratory-provided bottles, labeled, and placed in an ice-cooled chest pending analysis by <br /> Lancaster. <br /> SAMPLING LOCATIONS/SURVEY METHODS <br /> After completion, soil borings were geo-spatially located using a Global Positioning System <br /> (GPS)unit. The GPS survey methods were consistent with SAIC FTP No. 175, "Field <br /> Measurement of Physical and Topographical Features." <br /> EQUIPMENT DECONTAMINATION <br /> The decontamination of sampling equipment, which did not directly contact the samples, was <br /> performed in accordance with SAIC FTP No. 400, "Equipment Decontamination." Sample <br /> collection devices, which directly contacted the samples, were decontaminated in accordance <br /> with SAIC FTP No. 405, "Cleaning and Decontaminating Sample Containers and Sampling <br /> Equipment." <br /> 2. Geomatrix Consultants,Inc.,2005. Technical Approach to Site Evaluation and Decision-Making,Historical Pipeline <br /> Portfolio, Central Valley Region. February: <br /> D-2 a The Benham Companies,LLC <br /> "ra81 <br /> _,",,f,SW"N"'s <br />