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i <br /> ATTACHMENT 3 <br /> FIELD AND LABORATORY PROCEDURES <br /> i <br /> Exploratory Drilling <br /> Soil borings were drilled using air rotary/casing hammer drilling equipment Using the Unified Sod <br /> Classification System and standard geologic techniques, sod cuttings from the borings were <br /> logged by a SECOR geologist to a depth of 70 feet bgs in the boring for well MW-8 and to a depth <br /> of 50 feet bgs in the boring for well MW-10 Lithology encountered within the boring for well MW- <br /> 9, beyond 70 feet bgs in the boring for well MW-8, and beyond 50 feet bgs in the boring for well <br /> MW-10 were also evaluated from the collection of soil samples at 10-foot intervals to the total <br /> depth explored All down-hole drilling and sampling equipment was steam-cleaned prior to and <br /> following the completion of each soil boring Down-hole sampling equipment was washed in a <br /> trisodium phosphate or alconox solution between samples <br /> Groundwater Monitoring Well Installation <br /> A groundwater monitoring well was completed in each of the three soil borings by installing a <br /> 2-inch diameter, flush-threaded, Schedule 40 PVC casing with 0 020-inch factory-slotted screen <br /> Approximately 10 feet of screen was placed in each of the groundwater monitoring wells An <br /> RMC 2112 sand pack, or equivalent, was placed in the annular space across the entire screened <br /> interval, and extended approximately 2 to 3 feet above the top of the screen for each well A 3- <br /> foot bentonite transition seal was placed atop the sand pack, and a cement grout mixture <br /> extended from the bentonite transition seal to the ground surface Each well was secured by a <br /> locking expandable well cap, and fitted with a traffic-rated well box set in concrete Boring bgs in <br /> Attachment 4 show well construction details <br /> Rinsate/Purge Water and Soil Cuttings <br /> Soil cuttings, ansate water generated during steam cleaning of equipment, and water encountered <br /> during the installation of the wells was stored in a roll-off bin placed along the northern boundary <br /> of the site During the course of drilling activities, approximately 2,400 gallons of water were <br /> removed from the bin by FRC of Rialto, California using a vacuum truck, and transported to their <br /> facility for treatment/recycling Following waste profiling, the bin containing the soil cuttings was <br /> removed from the site by FRC on December 22, 2003, the soil cuttings were transported to their <br /> facility for treatment/recycling <br /> The groundwater monitoring wells were developed and sampled by SECOR on December 10, <br /> 2003 The development procedure for each well consisted surging the length of the well screen, <br /> and pumping and/or bailing water from the well until (1) the water was visibly clear, (2) monitoring <br /> parameters of temperature, conductivity, and pH stabilized to within 10 per cent and turbidity had <br /> stabilized to less than 100 ntus, (3) the well went dry, or (4) until a maximum of ten casing <br /> volumes had been removed Approximately 140 gallons of purge water were generated during the <br /> development of wells MW-8 through MW-10, and stored DOT-approved 55-gallon steel drums <br /> During well development activities, residual water was pumped from the roll-off bin containing the <br /> soil cuttings, and transferred into additional drums on-site for future transport to A total of 7 drums <br /> containing water generated during drilling and well development activities will be removed from the <br /> site by FRS, and transported to their facility for treatment/recycling <br /> . Non-hazardous waste manifests for the transport of the bin containing soil cuttings, and water <br /> generated during drilling and well development activities are included in Attachment 8 <br />