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ATTACHMENT C <br /> FIELD AND LABORATORY PROCEDURES <br /> Drilling and Monitoring Well Installation Procedures <br /> The monitoring wells will be drilled by a licensed drilling contractor using hollow-stem <br /> auger drilling equipment Soil samples for logging and chemical analysis will be <br /> collected at 5-foot depth intervals or at any lrthologic change noted during drilling. <br /> Samples will be collected using a split-spoon sampler with brass liners driven into the <br /> soil beyond the tip of the augers The depth of the monitoring wells will be based on <br /> static water level and geologic conditions on site, but is expected to be approximately 60 <br /> feet below the ground surface Soil samples for chemical analysis will be retained in <br /> brass liners, capped with Teflon sheets and plastic end caps and sealed in clean plastic <br /> bags, and transported on ice to a state-certified laboratory for chemical analysis <br /> Soil samples collected at 5-foot depth intervals will be analyzed in the field for organic <br /> vapors using a photo-ionization detector The test procedure involves measuring <br /> approximately 30 grams from an undisturbed soil sample, placing this subsample in a <br /> clean glass jar, and sealing the jar with aluminum foil secured under a ring-type <br /> threaded lid The jar as warmed for approximately twenty minutes, then the foil is <br /> pierced and the head-space within the lar is tested for total organic vapor, measured in <br /> parts per million as benzene (ppm, volume/volume) Results of these tests will be used <br /> to assist in selection of samples for laboratory analysis <br /> The borings for the wells will penetrate a maximum of 15 feet into the water-bearing <br /> zone taking care not to penetrate any aquntard underlying the first water-bearing zone, <br /> encountered These borings will be converted to groundwater monitoring wells with the <br /> installation of 2-inch diameter, Schedule 40 PVC casing and 0 02-inch factory-slotted <br /> screen Screen will be placed through the entire saturated section, extending approxi- <br /> mately 5 feet above the static water level A 2 X 16 graded sand pack will be placed in <br /> the annular space across the screened interval, and will extend approximately 2 feet <br /> above the screen Screen size and filter pack size have been determined based on <br /> previous well constructions on site. Approxunately two feet of bentonite will be placed <br /> above the sand pack followed by a concrete seal to the ground surface A locking cap <br /> 3104001\WORKPLN C— 1 August 6, 1993 <br />