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.1 <br /> KEI-P91-0202 .R7 <br /> March 18 , 1993 <br /> Page 4 <br /> and assumed zero volatilization, which was again extremely <br /> conservative. No surface parameters or volatilization to the <br /> atmosphere were considered since the source was assumed to be <br /> at a depth of 25 feet below the surface. Input parameters <br /> used in Simulation #1 are included in Appendix A. <br /> 2 . Simulation #2 <br /> The second simulation was conducted using assumptions which <br /> were more realistic and representative of the actual parame- <br /> ters encountered in the field. The input data were again <br /> divided into four general categories, which included climate, <br /> soil, pollutant characteristics , and application data. <br /> The climate and soil input data used were the same as for <br /> Simulation #1, since the characteristics of these categories <br /> are unique to the site and not to the simulation. <br /> The pollutant characteristics were again created to simulate <br /> the migration of benzene The properties of benzene used were <br /> the same as in Simulation #1, except that a conservative but <br /> more realistic biodegradation rate was introduced in this <br /> simulation. <br /> The application parameters used were more realistic than those <br /> used in Simulation #1 . The source of contamination was again <br /> assumed to be at a depth of 26 feet below the surface, corre- <br /> sponding to the area of highest contaminant concentration left <br /> in place. The horizontal area was assumed to be five feet by <br /> five feet, corresponding to the width of the largest excava- <br /> tion bucket typically used to remove soil . The five by five <br /> foot area is considered to be a more realistic dimension for <br /> an area of contaminated soil left in place beneath a former <br /> underground tank. SESOIL conservatively assumes that the <br /> entire five by five foot area is contaminated with the maximum <br /> concentration of benzene detected at that depth. The area of <br /> the SESOIL model for Simulation #2 is shown on Figure 2 . <br /> The introduction of pollutants to the subsurface system was <br /> again created by entering an instantaneous spall corresponding <br /> to the time of the tank excavation (which was in March of <br /> 1991) . This source was again assumed to occur only in the <br /> first month of the simulation. The simulation was run for a <br /> period of ten years as before, and assumed partial volatiliza- <br /> tion, which is more realistic than zero volatilization as in <br /> Simulation #1. As before, no surface parameters or volatil- <br /> ization to the atmosphere were considered since the source was <br /> Is assumed to be at a depth of 26 feet below the surface. Input <br /> parameters used in Simulation #2 are included in Appendix A. <br />