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C • <br /> Following sampling, boreholes will be tremae grouted to the surface using Oxygen Release <br /> Compound (ORCO) ORCO is used in this application to stimulate aerobic microbe activity <br /> by releasing oxygen into the surrounding soil <br /> Groundwater Monitoring Well Installation <br /> The borings will be converted to groundwater monitoring wells by installing 2-inch diameter, <br /> flush-threaded, Schedule 40 PVC casing with 0 020-inch factory-slotted screen Approxi- <br /> mately 20 feet of screen will be placed in the bottom of the boring An RMC 2/12 sand pack, <br /> or equivalent, will be placed in the annular space across the entire screened interval, and will <br /> extend approximately 2 feet above the top of the screen for the well A 2 to 3 foot bentomte <br /> transition seal will be placed atop the sand pack, and a Portland cement seal will extend from <br /> the bentonite transition seal to the ground surface The Portland cement seal will be <br /> emplaced by tremae pipe or through the center of the hollow-stem augers in one continuous <br /> operation from the bottom of the interval to be filled to the top Emplacement of the Portland <br /> cement grout specifically shall not be accomplished by "free fall' from the ground surface <br /> The boring logs will show well construction details The groundwater monitoring wells will <br /> be developed after completion The development procedure for each well will consist of <br /> pumping or balling water from the well until the water is visibly clear, the well goes dry, or <br /> until a maximum of ten casing volumes have been removed <br /> • <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 far, and sealing the far with aluminum foal secured under a ring- <br /> type threaded lad 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 wall 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 PID 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 collected from the soil borings and groundwater samples collected from <br /> the wells will be analyzed for the presence of total petroleum hydrocarbons calculated as <br /> • 9111-005 1S/WPLAN A - 2 June 10, 1998 <br />