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sampled at two depths, also based on lithology,but at approximately 5 and 20 feet bgs. <br /> Existing lithologs will be consulted to verify sampling depths. Continuous core borings, <br /> where lithologs are unavailable or where specific contacts are desired (e.g. the interface <br /> between the soil cover and the buried debris at the former ponds), will also be evaluated <br /> in the field to verify sampling depths. To the extent that prior samples in the vicinity <br /> indicate zones with concentrations suggestive of sources, those results will be used to <br /> modify the sample collection depths of subsequent locations from the 5 and 20 ft. <br /> default depths. Step-out sample locations, if needed, will follow the same depth <br /> selection procedure. <br /> The lithology for every soil gas location will be logged, and screen interval will be placed <br /> in the most permeable zone. A photoionization detector(PID) will be used to help <br /> determine the best soil gas sampling depth. <br /> Soil samples will be collected from the 11 soil cores retrieved during installation of the <br /> multi-depth soil gas probes in the former potential source areas. Soil samples will be <br /> collected from depths corresponding to the surface, 2.5 feet, 5 feet, 10 feet, 25 feet and <br /> approximately 40 feet bgs. The surface sample will be collected from immediately below <br /> (or from as close to immediately below as is feasible) the concrete/asphalt paving. <br /> The soil samples for analysis of dioxins and furans to be collected from the vapor borings <br /> at the former trash burning area and two downwind locations will be collected from two <br /> depths at each location: one at the surface, or immediately below pavement if presently <br /> paved, and second at approximately 2.5 feet bgs. <br /> Eight geotechnical soil samples will be collected and analyzed for geotechnical <br /> parameters. The locations and depths of the soil samples for geotechnical analysis will be <br /> determined in the field,based on soil gas results, lithology, and moisture. The cores from <br /> the installation of the soil gas points will be retained in acetate sleeves until the soil <br /> sample locations are selected. The geotechnical soil sample will be collected from the <br /> same location as the soil gas sample. The moisture content of the soil, as it can be <br /> assessed in the field, will also be considered prior to collection. The depth with the lower <br /> moisture content will be selected. The lithology for each soil point will be documented <br /> so that any other smaller layers for which a geotechnical sample is not collected can be <br /> considered in the risk analysis. <br /> Contingencies addressing potential difficulties collecting samples from the target depths <br /> are discussed in Section 5.5.11. <br /> 5.5.Field Methods <br /> 5.5.1. Utility Clearance <br /> Prior to the commencement of field activities, an underground location company will use <br /> a variety of geophysical methods which may include ground penetrating radar, <br /> Soil Gas and Soil Sampling Work Plan—Rev.4 7693-05 <br /> Former Kearney-KPF Facility Dudek <br /> Stockton,CA 13 September 2013 <br />