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S E C 0 R <br /> Soil and Groundwater Assessment Work Plan <br /> 7-Eleven Store #32262 fi <br /> August 12, 2003 <br /> Page 2 <br /> equipped with 8-inch diameter hollow stem augers to a total depth of approximately 17 feet below <br /> ground surface (bgs)to accommodate installation of a monitoring well Borings MW-1 and MW-5 will <br /> be continuously cored from 5 to 17 feet bgs to identify any high permeability sand beds at the site <br /> Sod samples will be collected from MW-2, MW-3, and MW-4 every 5 feet using a split spoon sampler <br /> lined with 2-inch diameter by 6-inch-long brass sample tunes Down hole drilling equipment will be <br /> steam cleaned before drilling each borehole, and sampling equipment will be cleaned between each <br /> sampling interval Each soil sample will be screened for hydrocarbon vapors using a portable <br /> photaonization detector (PID) Soils encountered during drilling will be logged using the Unified Soil <br /> Classification System by a SECOR field geologist, working under the supervision of a California <br /> registered geologist <br /> All soil generated through drilling will be placed in Department-of-Transportation (DOT) approved 55- <br /> gallon drums on site pending characterization and disposal Water generated by steam cleaning will <br /> be contained in a steam-clean trailer and temporarily stored on site in DOT approved 55-gallon <br /> drums <br /> All soil samples collected using 2-inch diameter by 6-inch-long brass sample tubes will be sealed <br /> with Teflon® sheeting and plastic caps, then labeled and placed on ice in an insulated container for <br /> delivery to Kiff Analytical located in Davis, California Soil samples collected at 5, 10, and 15 feet <br /> • bgs will be analyzed for benzene, toluene, ethylbenzene and xylenes (BTEX), total petroleum <br /> hydrocarbons-as-gasoline (TPHg), and methyl-tert butyl ether (MtBE) di-isopropyl ether (DIPE), tert- <br /> amyl-methyl ether (TAME), ethyl-t-butyl ether (ETBE), and tert-butyl alcohol (TBA) using <br /> Environmental Protection Agency(EPA) Method 8260B <br /> Well Installation and Well Development <br /> Each monitoring well will be constructed using 2-inch diameter polyvinyl chloride (PVC) blank casing <br /> and 0 020-inch-slot well screen set from 7 feet bgs to 17 feet bgs A sand filter pack will be placed <br /> within the annulus of the well from the bottom of the boring to approximately one foot above the top <br /> of the well screen The annulus of the well will be sealed with two feet of bentonite on top of the <br /> sand, and a portland cement/bentonite slurry to the surface An 8-inch-diameter, traffic-rated, <br /> watertight street box will be installed to protect the well from surface traffic Each monitoring well will <br /> be installed at the location depicted on Figure 2 <br /> Following installation the well will be developed by surging and bailing using a surge block and bailer <br /> to remove fine-grained sediments from the well and sand pack Periodic measurements of pH, <br /> conductivity and temperature will be made during development to establish baseline values for <br /> groundwater Approximately 10 well casing volumes will be removed from the well during <br /> development All water generated during the development activities will be stored in DOT approved <br /> 55-gallon drums pending disposal <br /> Following installation, the new well will be professionally surveyed to establish horizontal position in <br /> relation to pertinent site features and elevation with respect to mean sea level <br /> GROUNDWATER MONITORING AND SAMPLING <br /> Groundwater monitoring and sampling will be conducted to evaluate the groundwater quality by <br /> collecting representative samples Prior to sampling, depth to water in the groundwater monitor well <br /> will be taken and subjective analyses performed Each well will be sampled by purging <br /> �6 <br /> A <br />