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ti <br /> +1 i <br /> KEI-P91-0202 .R7 <br /> March 18 , 1993 <br /> Page 3 <br /> The highest concentrations of soil contamination at the <br /> subject site were detected near the south end of the eastern <br /> most former underground fuel storage tank. MW1 is the closest <br /> well to this location. Therefore, the Boring Log for MW1 was <br /> used to create the soil data. Various physical and chemical <br /> properties of the soil types were obtained from standard <br /> geological and engineering references. The location of the <br /> former underground fuel storage tanks, monitoring wells, and <br /> exploratory borings are shown on Figure 1 . <br /> The pollutant characteristics data was created to simulate the <br /> migration of benzene through the unsaturated zone. Various <br /> physical and chemical properties of benzene were obtained from <br /> standard chemical references . These included molecular <br /> weight, solubility, an air diffusion coefficient, Henry ' s law <br /> constant, an organic carbon/water partitioning coefficient, <br /> and a soil adsorption coefficient. Biodegradation was not <br /> considered and was assigned a zero value for Simulation #1 . <br /> Benzene was used because the maximum contaminant level (MCL) <br /> for benzene is the most stringent of the contaminants being <br /> considered. Therefore , using benzene as the chemical pollut- <br /> ant yields the most conservative simulation that can be <br /> performed. <br /> The application parameters used were also extremely conserva- <br /> tive. In an effort to remove as much of the contaminated soil <br /> as possible, the underground fuel storage tank pit was <br /> overexcavated in the area of highest contamination to a depth <br /> of approximately 26 feet below the surface . Therefore, the <br /> results of soil samples collected at a depth of 26 feet in the <br /> area of highest contamination were used as a contamination <br /> source for the SESOIL model . <br /> Beginning at a depth of 26 feet, four soil layers with varying <br /> properties and thicknesses were used in the model, based on <br /> soils encountered in the boring for well MW1 . The horizontal <br /> area of the soil column was assumed to be 20 feet by 20 feet. <br /> This is an extremely conservative estimate because SESOIL <br /> assumes that the contamination introduced to the subsurface is <br /> uniform in concentration throughout the entire area of <br /> simulation. Therefore, SESOIL assumed a greater amount of <br /> contamination than was actually present. The area of the <br /> SESOIL model for Simulation #1 is shown of Figure 1. <br /> Contamination of the subsurface system was simulated by <br /> entering an instantaneous spill corresponding to the time of <br /> . the tank excavation (which was in March of 1991) . This source <br /> was assumed to be present only in the first month of the <br /> simulation. The simulation was run for a period of ten years <br />