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locations of the former USTs, respectively. The highest concentration of benzene was detected in <br /> the soil sample collected from Bl at 60 feet bgs. Benzene was detected in soil samples at <br /> ' concentrations ranging from nondetectable to 19 mg/kg. The lateral extent of benzene in vadose <br /> zone soil is shown on Figures 9 and 10. <br /> ' MTBE has been detected in only one boring (B2). MTBE was detected in soil samples collected <br /> from the vadose zone of B2 from 31 feet bgs, 35 feet bgs, and 50.5 feet bgs at concentrations of <br /> 0.012 mg/kg, 0.024 mg/kg, and 0.01 mg/kg, respectively. The lateral extent of MTBE in vadose <br /> zone soil is shown on Figures 11 and 12. <br /> ' 4_2 Estimated Extent of Hydrocarbon-Impacted Groundwater <br /> The lateral extent of impacted groundwater has not been defined yet. Laboratory analytical <br /> ' results of groundwater samples collected from monitoring wells MW 1 through MW9 and the on- <br /> site domestic well on November 20, 2003, indicate petroleum hydrocarbons were present in <br /> groundwater samples collected from MWI, MW2, MW4, MW5, MW6, and MW9. Petroleum <br /> ' hydrocarbons were not detected in the groundwater samples collected from upgradient well <br /> MW3, downgradient well MW8, or the domestic well. The estimated lateral extents of <br /> groundwater impacted with TPHg, benzene, and MTBE are shown on Figures 13, 14, and 15, <br /> ' respectively. The highest concentrations of dissolved petroleum hydrocarbons are present in the <br /> vicinity of MW2. <br /> ' 5.0 DESIGN PLANS AND SPECIFICATIONS <br /> The proposed interim soil and groundwater remediation systems will consist of combined vapor <br /> extraction and air sparge treatment systems.The systems will function as interim remedial measures <br /> for on-site hydrocarbon impacted soil and groundwater. <br /> 5_1 Design Parameters <br /> 5.1.1 Vapor Extraction-Wellhead Vacuum,Flow Rate, and Radius of Influence <br /> Vapor extraction pilot testing performed at the site on September 29, 2003, indicated that a radius <br /> ' of influence (ROI) of up to 55 feet was achieved with air flow rates ranging from 53.5 to 78.9 cubic <br /> feet per minute (cfm) and observation wellhead vacuums ranging from 0.44 to 2.7 inches of water. <br /> During the long-term(approximately five hours)vapor extraction test conducted on VE3,the vapor <br /> ' extraction rate appeared to equilibrate at approximately 62 cfm with a vacuum of approximately 42 <br /> inches of water. The actual radius of influence for each vapor extraction well will vary depending <br /> on subsurface geologic conditions, the extent and distribution of hydrocarbon-impacted soil, the <br /> ' effect of concurrently operating the air sparge system, and site-specific operating conditions of the <br /> vapor extraction system (VES). The effective radius of influence should be evaluated following <br /> long-term operation of the VES. <br /> S:\environmental\25291\reports\irp.doc 4 <br />