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Clayton <br /> ll! 51 IIV,I• <br /> We use the ambient temperature headspace method to screen individual samples ft, "he <br /> presence of various hydrocarbon vapors We gather a soil or water sample and place it in a <br /> sample jar or ziplock plastic bag so that there is a vacant headspace in the container. if a <br /> sample jar is used, the mouth is covered with foil and the lid is screwed on. The sample is <br /> then allowed to reach ambient temperature (usually in 10-15 minutes) causing any <br /> hydrocarbon vapors to volatilize into the headspace. Monitoring of the headspace in the jar <br /> or plastic bag is dons.with an OVM by piercing the foil or bag with the OVM probe. This <br /> method allows for a rough indication of the presence and concentration of hydrocarbon <br /> vapors in a particular sample <br /> SOIL SAW <br /> Soil samples are taken every 5 feet, at arem of obvious contamination, or as otherwise <br /> specified, with a California modified split-spoon sampler that is lined with three six-inch brass <br /> -- tubes. The sample- and rod are inserted into the borehole to the current depth and a <br /> hammer of known weight and height above the sampler are allowed to Free-tall onto the rod, <br /> advancing the assembly 18 inches into undisturbed soil Clayton uses the number of blows <br /> necessary to drive the sampler into the ground to help evaluate the consistency of materials <br /> encountered. The sampler is then pulled from the borehole and disassembled, and the three <br /> brass tubes are separated for inspection and labeling <br /> Clayton uses new brass liners or liners cleaned with a tnsodium phosphate (TSP) solution, <br /> double rinsed with clean tap water, and air dried prior to each sampling The sampler is also <br /> cleaned with TSP and rinsed with tap water between Qamphrig events. <br /> Soil samples selected for laboratory analysis are left in the brass liners, sealed with aluminum <br /> foil and plastic caps, taped for air tightness, labeled, and immediately placed into a pre-cooled <br /> ice chest chilled to less than 4°C Labels contain the following information- site name, date <br /> and time sampled, borehole number and depth, and the sampler's initials The samples are <br /> transported under chain-of-custody to a state-certified laboratory The laboratory analyzes <br /> soil samples within the prescribed holding time, storing them at temperatures below 4°C at all <br /> E times. <br /> I Pending results of laboratory analysis, excess drilling and sampling cuttings are placed into <br /> Department of Transportation (DOT)-approved drums, Icb-led with the name of the site, <br /> address, and well number, and left at the site Uncontaminated soil may be disposed of by <br /> the client. Soil found to conta.n levels of contaminants above local or state action levels will <br /> require that the client dispose of it in accordance with hazardous waste regulations At the <br /> client's request, we will assist with the disposal of contaminated soil. <br /> 5 <br />'Al <br /> h <br /> a <br /> J <br /> RE"CONSMCTION <br /> Boreholes are converted to monitoring wells by placing 2-inch or flinch diamt,es well casing <br /> $ with Flush-threaded joints and slotted screen into the borehole. Construction materials <br /> include polyvinyl chloride (PVC), stainless steel, or low carbon steel. The most suitable <br /> material for a particular installation will depend on the parameters to be monitored. All <br /> 2 <br /> aRv <br />