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I <br />' 25 February 2005 <br /> AGE-NC Project No 95-0104 <br />' Page 3 of 10 <br /> analyzed for 1,2-DCA were collected from probe boring P-1 in July 2000 Analysis of the post <br />' remediation soil samples indicated that there Is no 1,2-DCA Impacted soil beneath the site(Table 2) <br /> 2.0. SITE CONCEPTUAL MODEL <br />' Based on the data collected to date from the monitoring wells on-site, AGE has developed a site <br /> conceptual model(SCM)for the migration and distribution of the l,2-DCA dissolved In the ground <br /> water at the site (Figures 3 through 6) <br /> The soil profile beneath the site Is generally composed of sandy silt and silty sand with lenses of fine- <br /> grained sand and silt (Figures 3, 4 and 5) Based on ten years of quarterly monitoring, the depth to <br />' ground water has ranged between approximately 52 27 feet and 82 58 feet bsg(Table 1) at the site, <br /> and has consistently had a northeast flow direction, with the exception of the past two quarterly <br /> monitoring events In June 2003 and September 2004(Figure 7)the ground water flow direction has <br />' been toward the north,with an average September 2004 depth to water of 77 feet bsg Ground water <br /> occurs in a generally sandy silt unit interbedded with fine to medium sands that dominate the <br /> llthology of the site <br /> Thereatest concentrations of hydrocarbon-impacted soil has been encountered at vapor well VW-I <br /> g <br /> Figures 8 and 9 depict general lrthology and selected soil sample results beneath the site in cross <br />' sectional view The UST appears to have been the release point,once discharged into the subsurface <br /> the contamination migrated vertically to 50 or 55 feet bsg, intercepted a high water table level and <br />' dissolved Into the ground water The dissolved hydrocarbons and fuel additive 1,2-DCA migrated <br /> east-northeast as depicted In Figure 6 <br />' A volume-mass calculation using the data collected during Investigation of the former UST area, <br /> yields approximately 308 gallons of gasoline In the Impacted soil at the site Assuming that VW-1 <br /> Is within the source area, an effective radius of fifteen-feet was used to estimate the volume of <br /> Impacted soil An average concentration of 14,000 mg/kg was used to calculate the total volume of <br /> remaining hydrocarbons from 15 to 30 feet bsg, while 1 1 mg/kg was used to calculate the total <br /> volume from 30 to 45 feet bsg Petroleum hydrocarbon-Impacted soil volume assumptions and <br />' calculations are also Included In Appendix A <br /> Hydrocarbon Impacted-soil was vertically defined In the source area,by soil samples collected from <br />' <br /> soil boring V W 1 The only soil samples collected from the site that have been analyzed for 1,2-DCA <br /> were collected from probe boring P-1 In July 2000 Analysis of those soil samples Indicated that <br /> there Is no 1,2-DCA Impacted soil beneath the site (Table 2) <br /> Total petroleum hydrocarbons as gasoline and diesel (TPH-g and TPH-d), benzene, toluene, <br />' Advanced GeoEnvironmental,Inc <br />