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R10/71-51-1C <br /> between drilling locations The 11 soil borings were advanced to depths ranging between <br /> 5 feet to 94 feet Table 3 (see Appendix C) summarizes the soil boring (SB15, S1317, <br /> SB18, SB22, and SS23) specifications and Table 4 summarizes the monitoring well <br /> (MW13, MW14, MW16, MW19, MW20, and MW24) construction information <br /> Soil samples were obtained initially at approximately 1 5 feet below the surface and then <br /> at approximately five-foot intervals or change in lithology down to predetermined depths <br /> or groundwater encounter Where groundwater was encountered and a monitoring well <br /> was not to be installed in that boring, water samples were collected in order to get an <br /> idea of the potential groundwater contamination The laboratory results for these water <br /> samples will not be used for defining contamination plume nor will these be used as a <br /> quantitative measurement of contaminant levels The boreholes were then promptly <br /> backfilled with bentonite grout and cement All drill-samples were obtained using a <br /> modified California split-spoon sampler The appropriate number of stainless steel <br /> r sleeves and dummy brass sleeves depending on the inner diameter (either 2-inch or 2 5- <br /> inch) of the sampler were used The split-spoon sampler and sleeves were cleaned using <br /> a detergent solution and deionized water and inspected for complete decontamination <br /> 1 prior to use The soil samples were retained in sleeves placed inside the sampler <br /> Immediately following collection at each horizon, the stainless steel sleeve nearest the <br /> driving tip of the sampler were immediately covered with a Teflon sheet and capped at <br /> both ends The sieeves were then placed in resealable plastic bags and then placed into <br /> a cooler with ice for preservation of sample integrity The soil in the sleeves above the <br /> sleeves taken out for chemical sampling were emptied into resealable plastic bags and <br /> 1 were subsequently exposed under the sun and read the head space with a Foxboro <br /> Organic Vapor Analyzer <br /> Samplers were advanced eighteen inches by the repeated 30-inch drop of a 140-pound <br /> hammer Blow counts were recorded for each six inches of advance Refusal, caused <br /> by the encounter of sub-surface obstructions, was defined as failure to advance more <br />' than six inches for fifty blow-counts or the encounter of insurmountable boulders by the <br /> auger <br />' Soil logging and drilling activities were conducted under the supervision of Mr Ramesh <br /> Shah, a California-registered geologist Soil/Waste descriptions including information <br /> concerning the color, grain-size, grain-sorting, soil moisture and soil density as indicated <br />' by blow counts and any unusual features were entered in the field log book Soils were <br /> described with reference to the Unified Soil Classification System (USCS) (ASTM D2488- <br /> 84) The data were utilized to prepare soil boring logs presented in Appendix D <br /> r <br /> 13 <br /> r <br />