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y + <br /> n <br /> Wi <br /> STANDARD OPEPAT VG PROCEDURES <br /> RE:SOIL SAMPLING <br /> SOP-2 <br /> .fail samples for chemical analysis are collected in thin-walled brass tubes,4-inches long by 2-inches <br /> a outside diameter. Four of these tubes and a spacer tube are set in a 24nch inside diameter 18-inch <br /> split-barrel sampler. <br /> The split-barrel sampler is driven its entire length either hydraulically or using a 144-pound drop <br /> hammer. The sampler is extracted from the borehole and the brass tubes, containing the soil <br /> samples,are removed. Upon removal from the sampler,the selected brass tubes are immediately <br /> �9 trimmed and capped with aluminum foil and plastic caps. They are then hermetically sealed with <br /> duct tape,labeled and refrigerated for delivery,under chain-of-custody,to the analytic laboratory. <br /> Thew procedures minimize the potential for cross-contamination and volatilization of volatile <br /> organic compounds(VOC)prior to chemical analysis. <br /> One soil sample collected at each sampling interval is analyzed in the field using either a <br /> photoionizadan detector(PID),a flame ionization detector(PID),or an explosimeter.The purpose <br /> of this field analysis is to qualitatively determine the presence or absence,of hydrocarbons and to <br /> establish which soil samples will be analyzed at the laboratory. The soil sample is sealed in a <br /> to enhance volatilization of the hydrocarbons 6om the <br /> zEp!:xck plastic bag and placed in the sun <br /> logs at the depth corresponding to the sampling point. <br /> sample. The data is recorded on the drill <br /> Other sail samples are collected to document the stratigraphy and estimate relative permeability of <br /> the subsurface materials. All drilling and sampling equipment are steam-cleaned prior to use at <br /> -contamination. <br /> ,� tib! each site and between boreholes to minimize the potential for cross <br /> i <br /> i� <br /> S <br /> 9y <br /> T� <br /> n� <br /> y <br /> j <br />