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Emergency Remediation 2480 Tracy Blvd., Tracy, CA. Page 17 <br /> Each batch of soil removed from the stockpile was spread in a layer between 6 in. and <br /> 9 in. in thickness over the area of the site where it was to be treated. This transfer was <br /> made using the 4 cu. yd. front loader. The front loader and the excavator were also used <br /> to work the stockpile by inverting piles of soil and dribbling soil from the buckets. This <br /> was done to induce aeration of components of gasoline so that the remaining quantities to . <br /> be removed by the final treatment process would as little as possible and the time required <br /> to complete the treatment reduced to a practical minimum. The five soil spreads that were <br /> used to aerate the contaminated soil are shown on Figures 5 through 9. <br /> After each batch of soil was placed in its treatment area and spread, it was rototilled using <br /> a large rototiller powered by an agricultural tractor. This procedure encouraged natural <br /> aeration and volatilization of gasoline from the spread soil. The spreads of soil were <br /> rototilled at frequent intervals and from time to time they were picked up and turned over <br /> ' before being re-spread and rototilled again so as to ensure that components of gasoline <br /> had been thoroughly volatized from the full thickness of the spread material. <br /> ' As the soil treatment of a spread of soil progressed, it was checked from time to time for <br /> visual and olfactory indicators of gasoline. When none could be detected by an <br /> experienced observer treatment was terminated and the spread of soil was either <br /> consolidated in a stockpile or left in place for later use by the general construction <br /> contractor. <br /> Sampling and Analysis of Treated Soil <br /> Before a batch of the spread of treated soil was released to the general construction <br /> contractor for incorporation into the works, it was sampled by the technique that is <br /> described below and that follows the procedures established by the United States <br /> Environmental Protection Agency (EPA) for evaluating the attainment of cleanup <br /> standards of soil and solid media(Ref. 3). <br /> Six sampling points within each soil spread were selected randomly by throwing die to <br /> separately and randomly select a set of alphabetic and numeric identifiers associated with <br /> the 35 ft. square sub-area into which the site had been subdivided by previously-described <br /> 1 grid system. Alphanumeric character combinations read from the die that identified sub- <br /> areas not covered with the treated soil that had been placed in a given spread were ignored <br /> and the die thrown repeatedly until the requisite number of randomly-selected sub-areas <br /> that included the soil spread being sampled had been identified. <br /> The sub-areas selected for sampling in each of the five soil spreads are shown on Figures <br /> 5 through 9. (Note: Due to the limited size of those spreads, only two and three sub-areas, <br /> respectively, were selected for sampling in Soil Spreads No. 2 and No. 4.) <br /> Specific sampling location within the selected sub-areas were selected arbitrarily by <br /> tossing a sampling tube into the square without consideration for any zones of color <br /> change or other small-scale variation in the visual characteristics of the soil. <br />