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r <br /> ATTACHMENT B <br /> FIELD AND LABORATORY PROCEDURES <br /> Health and Safety <br /> y <br /> As required by the Occupational Health and Safety Administration (OSHA) Standard <br /> "Hazardous Waste Operations and Emergency Response" guidelines (29 CFR 1910 120), and <br /> by California Occupational Health and Safety Administration (Cal-OSHA) "Hazardous <br /> Waste Operations and Emergency Response" guidelines (CCR Title 8, Section 5192), <br /> SECOR will prepare a Site-Specific Health and Safety Plan prior to the commencement of <br /> fieldwork The Site-Specific Health and Safety Plan will be reviewed by the field staff and <br /> contractors before beginning field operations at the site <br /> Exploratory Drilling <br /> The soil borings will be drilled using an 8-inch hollow-stem auger drilling equipment to <br /> approximately 70 feet bgs The borings will be logged by a SECOR representative using the <br /> Unified Soil Classification System and standard geologic techniques Soil samples for <br /> logging will be collected at approximately 5-foot depth intervals using a California-modified <br /> split-spoon sampler The sampler will be driven a maximum of 18 inches using a 140-pound <br /> hammer with a 30-inch drop Soil samples collected for chemical analysis will be retained in <br /> brass liners, capped with Teflon squares and plastic end caps, and sealed in clean zip-lock <br /> bags The samples will be placed on ice for transport to the laboratory accompanied by <br /> chain-of-custody documentation Down-hole drilling and sampling equipment will be steam- <br /> cleaned prior to and following the completion of the soil boring Down-hole sampling <br /> equipment will be washed in an alconox or equivalent solution between sample collection <br /> Groundwater Monitoring Well Installation <br /> The borings will be converted to a groundwater monitoring well by installing 2-inch <br /> diameter, flush-threaded, Schedule 40 PVC casing with 0 020-inch factory-slotted screen <br /> Approximately 15 feet of screen will be placed in the bottom of each boring A grade of <br /> sand appropriate to the screen size will be placed in the annular space across the entire <br /> screened interval, and will extend approximately 2 feet above the top of the screen for each <br /> well A bentonite seal will extend two feet above the sand pack The monitoring wells will <br /> be completed with neat cement from the bentonite seal to ground surface The well casings <br /> will be topped with a locking cap The well heads will be contained in watertight well boxes, <br /> either traffic rated and flush mounted or in a "stove-pipe" arrangement The boring logs will <br /> show well construction details The wells will be developed after completion by pumping or <br /> bailing water from each well until the water is visibly clear, the wells go dry, or until a <br /> maximum of ten casing volumes have been 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 photo-ionization detector (PID) with a 10 2 eV <br /> .} lamp or a flame ionization detector (FID) The instrument will be calibrated prior to drilling <br /> using a 100-ppm isobutylene standard (in air) and a sensitivity factor of 55, which relates the <br /> photo-ionization potential of benzene to that of isobutylene at 100 ppm The results of the <br />