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S E C 0 R <br /> ATTACHMENT B <br /> FIELD AND LABORATORY PROCEDURES <br /> Exploratory Drilling <br /> wl <br /> The sod borings will be drilled using air rotary with casing hammer drilling equipment to depths of aka <br /> approximately 120 feet bgs Borings will be logged by a SECOR International Incorporated scientist <br /> under the direction of a registered geologist using the Unified Soil Classification System and standard n <br /> geologic techniques Soil samples will be collected every 10 feet at depth from 80 to 120 feet using a <br /> split-spoon sampler Soil samples for chemical analysis will be retained in brass liners, capped with <br /> Teflon squares and plastic end caps, and sealed in clean zip-lock bags The samples will be placed <br /> on ice for transport to the laboratory accompanied by chain-of-custody documentation Down-hole ti <br /> drilling and sampling equipment will be steam-cleaned following the completion of the sod boring s <br /> Down-hole sampling equipment will be washed in a tri-sodium phosphate or alconox solution between <br /> samples <br /> Well Installation and Development <br /> The sod borings will be converted to groundwater monitoring wells by installing 2-inch diameter, flush- <br /> threaded, Schedule 40 PVC casing with 0 020-inch factory-slotted screen Heavy wall casing will be ;$ <br /> utilized as conductor casing and will be advanced following the drill bit to the total depth explored in <br /> each boring in order to seal the upper groundwater bearing zones from the lower groundwater <br /> bearing zones Approximately 5-10 feet of screen will be placed in the bottoms of the boring A y � <br /> grade of sand appropriate to the screen size will be placed in the annular space across the entre <br /> screened interval, and will extend approximately 2 feet above the top of the screen for the wells A <br /> bentonite seal will extend two to four feet above the sand pack The monitoring wells will be <br /> completed with neat cement from the bentonite seal to the ground surface The well casing will be a <br /> topped with a locking cap The wellhead will be contained in a watertight traffic-rated well box The <br /> boring logs will show well construction details <br /> The well will be developed after completion The development procedure for each well will consist of <br /> surging the well, then pumping or bailing water from the well until the water is visibly clear, the well <br /> goes dry, or until a maximum of ten casing volumes have been removed <br /> The newly installed wells will be surveyed by a California State Licensed Surveyor The well casings <br /> will be surveyed to the nearest 0 01 feet in elevation to a known benchmark <br /> Organic Vapor Procedures <br /> Sod samples collected at 5-foot depth intervals 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 ionization <br /> detector (FID) The test procedure will involve measuring approximately 30 grams from an - <br /> undisturbed soil sample, placing this subsample in a sealed container (either a zip-lock bag or a <br /> mason tar) The container will be warmed for approximately 20 minutes (in the sun), then the head- w <br /> space within will be tested for total organic vapor, measured in parts per million as benzene (ppm, <br /> volume/volume) The instrument will be calibrated prior to drilling using a 100-ppm isobutylene <br /> standard (in air) and a sensitivity factor of 55, which relates the photo-ionization potential of benzene <br /> to that of isobutylene at 100 ppm The results of the field testing will be noted on the boring logs PID <br /> and FID readings are useful for indicating relative levels of contamination, but cannot be used to <br /> evaluate hydrocarbon levels with the confidence of laboratory analyses <br /> Laboratory Procedures µ <br /> y <br /> k' <br /> ' Y <br /> {i <br />