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cement seal will extend from the bentonite transition seal to the ground surface The Portland <br /> cement seal will be emplaced by tremie pipe or through the center of the hollow-stem augers <br /> in one continuous operation from the bottom of the interval to be filled to the top <br /> Emplacement of the Portland cement grout specifically shall not be accomplished by "free <br /> fall" from the ground surface The boring logs will show well construction details The <br /> groundwater monitoring wells will be developed after completion The development proce- <br /> dure for each well will consist of pumping or balling water from the well until the water is <br /> visibly clear, the well goes dry, or until a maximum of ten casing volumes have been <br /> removed <br /> Organic Vapor Procedures <br /> Soil samples collected at 5-foot depth intervals during drilling will be analyzed in the field <br /> for ionizable organic compounds using a flame-ionization detector (FID) or a photo- <br /> ionization detector (PID) with a 10 2 eV lamp The test procedure will involve measuring <br /> approximately 30 grams from an undisturbed soil sample, placing this subsample in a ziplock <br /> type bag or in a clean glass jar, and sealing the far with aluminum foil secured under a ring- <br /> type threaded lid The container will be warmed for approximately 20 minutes (in the sun), <br /> then the head-space within the container will be tested for total organic vapor, measured in <br /> parts per million as benzene (ppm, 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 isobutylene at 100 ppm The <br /> results of the field testing will be noted on the boring logs FID readings are useful for <br /> indicating relative levels of contamination, but cannot be used to evaluate hydrocarbon levels <br /> with the confidence of laboratory analyses <br /> Laboratory Procedures <br /> Selected soil samples taken from the monitoring well locations will be analyzed for the <br /> presence of total petroleum hydrocarbons as diesel (TPH-d), total petroleum hydrocarbons as <br /> gasoline (TPH-g), and benzene, toluene, ethylbenzene, xylenes (BTEX), by EPA <br /> Methods 8015 Modified, and 8020 MtBE will be analyzed by EPA Method 8260 and Total <br /> Lead by EPA Method 6010 Selected samples taken from Boring B-4 will be analyzed for <br /> the above listed analytes plus cis-1,2-Dichloroethene (cis-1,2-DCE), trans-1,2-Dichlorethene <br /> (trans-1,2-DCE), Tetrachlorethene (PCE), and Trichlorethene (TCE) by EPA Method 8010 <br /> One sample from the location of Boring B-4 will be analyzed for Tier One RBCA physical <br /> parameters <br /> Groundwater samples collected from the monitoring wells and the sample collected from <br /> Boring B-4 will be submitted to a California State-certified laboratory for analysis <br /> Groundwater samples will be analyzed for the presence of TPH-d, TPH-g, and BTEX by <br /> 910-017 IA/WPLAN A - 2 July 15, 1999 <br />