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ATTACHMENT B <br /> FIELD AND LABORATORY PROCEDURES <br /> Chevron Service Station 9-3232, 8660 Lower Sacramento Road, Stockton, California <br /> Health and Safety <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 prepared a Site-Specific Health and Safety Plan for use during fieldwork The field <br /> staff and contractors reviewed the Site-Specific Health and Safety Plan before beginning <br /> field operations at the site <br /> Exploratory Drilling <br /> The soil borings were advanced using 8-inch hollow-stem auger drilling equipment to <br /> approximately 46 feet bgs in the shallow borings and approximately 67 feet bgs in the deep <br /> borings A SECOR representative using the Unified Soil Classification System and standard <br /> geologic techniques logged continuous soil samples using a California-modified split-spoon <br /> sampler from the deep borings and in five foot intervals from the solo shallow well (MW-7) <br /> Soil samples were retained in brass liners, capped with Teflon squares and plastic end caps, <br /> and sealed in zip-lock bags The samples were then placed on ice for transport to the <br /> laboratory accompanied by chain-of-custody documentation Down-hole drilling and <br /> sampling equipment was steam cleaned prior to and following the completion of each soil <br /> boring Down hole sampling equipment was washed in a tri-sodium phosphate or alconox <br /> solution between samples <br /> Groundwater Monitoring Well Installation <br /> The borings were 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 15 feet of screen was placed in the bottom of each shallow boring and approximately <br /> five to ten feet of screen was placed in the bottom of each deep boring A grade of sand <br /> appropriate to the screen size was placed in the annular space across the entire screened <br /> interval, and extends approximately 2 feet above the top of the screen for each well A <br /> bentonite seal extends two feet above the sand pack The monitoring wells were completed <br /> with neat cement from the bentonite seal to ground surface The well casings were topped <br /> with a locking cap The well heads are contained in watertight well boxes, traffic rated and <br /> flush mounted The boring logs show well construction details The wells were developed <br /> after completion by pumping or bailing water from each well until the water was visibly <br /> clear, the wells went dry, or until a maximum of ten casing volumes had been removed <br /> Slug Testing <br /> The slug test consists of quickly raising (slug insertion) or lowering (slug removal) the water <br /> level in a well from equilibrium and measuring the subsequent rate of rise or fall, <br /> respectively Slug insertion and slug removal tests were performed on each well using a slug <br />