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' 01 June 1999 <br /> AGE-NC Project No 95-0137 <br /> Page 24 of 26 <br /> ' 7.0. RECOMMENDATIONS FOR REMEDIATION OF HYDROCARBON- <br /> IMPACTED SOIL <br /> Vadose zone soil Impacted by TPH-d and TPH-g extends vertically to the saturated zone under the <br /> former UST area and extends under the building on-site Additional Impacted soil extends laterally <br /> in the saturated "smear" zone or capillary fnnge zone Excavation would require the removal of <br /> minor volume of overburden soil in the UST area, however, significant `clean' overburden soil <br /> would have to be removed to clean up Impacted soil in the surrounding capillary fringe or"smear <br /> zone" at approximately 15 to 20 feet bsg AGE believes that natural attenuation processes are too <br /> slow to rely on for Impacted ground water already in the Immediate vicinity of a domestic water well <br /> Therefore, AGE recommends that in-situ methods of remediation be considered <br /> ' Both In-situ methods described in this CAP could be effective for remediating the site SVE is <br /> effective for gasoline range hydrocarbons, but is moderately effective for diesel range hydrocarbons <br /> Diesel range hydrocarbons can be effectively addressed through bioremediation From a cost basis, <br /> ' Implementation of an in-situ bioremediation program is comparable to soil vapor extraction, <br /> although monitoring requirements, duration and limited control of the bio-technology could Increase <br /> the cost significantly AGE recommends installation of an SVE system at the site in the former UST <br /> area to address the BTEX compounds, TPH-g and lighter-end TPH-d components that are impacting <br /> the underlying ground water and posing a threat to the domestic well on the Jimco property AGE <br /> ' also recommends addressing the TPH-d impacted"smear"zone soil through enhancement of natural <br /> biodegradation through bioventing associated with sparging, which is discussed below Soil <br /> remediation methods, estimated durations and associated costs are summarized on Table 8 <br /> 1 An extraction unit capable of approximately 100 scfm will be required for remediation of vadose soil <br /> in the former UST area Due to the concentration of contaminants at the site, an IC unit would be the <br /> ' most cost-effective choice An electric blower and carbon filtration system may be used during the <br /> final stages of remediation A 12 to 18 month soil remediation period can be expected Installation <br /> of an SVE syatem would include installation of soil vapor extraction wells within the contaminated <br /> ' soil plume Installation of sparge lines, which would provide oxygen for bioventing is discussed <br /> below <br /> 1 <br /> 8.0. RECOMMENDATIONS FOR REMEDIATION OF HYDROCARBON- <br /> IMPACTED GROUND WATER <br /> AGE believes that an in-situ method would be more effective in both cost and performance over a <br /> ' "pump and treat" method Both in-situ methods described in this CAP could be effective in <br /> remediating the site However,due to limited regulatory acceptance in-situ bioremediation of ground <br /> water may not be the most cost-effective remedial alternative for the site, and should not be relied <br /> upon as the primary method for remediation of impacted ground water <br /> Advanced GeoEnvironmental,Inc <br />