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ATTACHMENT A <br /> FIELD PROCEDURES (CONTINUED) <br /> i <br /> Chevron Service Station 9-2033, 508 West Charter Way, Stockton, California <br /> cement from the bentonite seal to ground surface The well casings will be topped with a <br /> locking cap The wellheads will be contained in watertight well boxes, either traffic rated <br /> and flush mounted or in a "stove-pipe" arrangement The boring logs will show well <br /> construction details The wells will be developed after completion by pumping or bailing <br /> water from the wells until the water is visibly clear, the wells go dry, or until a maximum of <br /> ten casing volumes have been removed <br /> After development, water levels will be allowed to partially recover Groundwater samples <br /> will then be collected using a disposable Teflon bailer, placed into appropriate EPA- <br /> approved containers, labeled, placed on ice, and transported to a California State Certified <br /> laboratory accompanied by chain-of-custody documentation The well casings will be <br /> surveyed to the nearest 0 01 feet in elevation to a known benchmark <br /> Organic Vapor Procedures <br /> Soil samples collected continuously during drilling will be analyzed in the field for ionizable <br /> organic compounds using a photo-ionization detector (PID) with a 10 2 eV lamp or a flame <br /> ionization detector(FID) The test procedure will involve measuring approximately 30 <br /> grams from an undisturbed soil sample, placing this sub-sample in a sealed container (either <br /> a zip-lock bag or a mason far) The container will be warmed for approximately 20 minutes <br /> (in the sun), then the head-space within will be tested for total organic vapor, measured in <br /> parts per million as benzene (ppmv, volume/volume) The instrument will be calibrated prior <br /> to drilling using a 100-ppm isobutylene standard (in air) and a sensitivity factor of 55, which <br /> relates the photo-ionization potential of benzene to that of lsobutylene at 100 ppm The <br /> results of the field-testing will be noted on the boring logs PID and FID readings are useful <br /> for indicating relative levels of contamination, but cannot be used to evaluate hydrocarbon <br /> levels with the confidence of laboratory analyses <br /> Soil Sampling for Stockpiled Soil <br /> Soil samples will be collected by advancing a 2-inch diameter brass sample liner into the soil <br /> stockpile, after removing approximately 6-inches to 1-foot of surface material in the sample <br /> location One composite sample will be collected per approximately 100 cubic yards of soil <br /> Soil samples for chemical analysis will be retained in the brass liners, labeled, and capped <br /> 3 <br />