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Interim Corrective Action Plan <br /> . Frontier Transportation, Inc. <br /> December 20, 2005 <br /> Page 7 <br /> Cost estimates for in situ SVE range between $10 and $50 per cubic meter ($10 and <br /> $40 per cubic yard) of soil Pilot testing typically costs $10,000 to $100,000 Exact cost <br /> estimates for contaminant cleanup would not be known until after pilot testing at the site <br /> However, since most of the contamination at this site is in dissolved phase, the cost to run a <br /> pilot test and perform SVE would be very great for a minimal amount of contaminant <br /> removal <br />' Soil vapor extraction is a corrective action method that is typically used at <br /> contamination sites with elevated adsorbed phase contamination and moderately permeable <br />' soil types This site has elevated contamination levels mostly in dissolved phase, with minor <br /> residual amounts adsorbed in the soil Furthermore, the lithologic records indicate that clays <br /> are present throughout the site, winch would severely limit the extraction efficiency Soil <br />' vapor extraction effectiveness is limited by clayey soils with high organic content, as exists at <br /> this site Boring logs identify primarily tight-grained fines with clays and silts predominantly <br /> Iin the limited vadose zone at the site <br /> In addition, groundwater at approximately 10' bgs would be mounded and possibly <br />' interfere with soil vapor extraction systems at cubic foot per minute capacity necessary to <br /> create an achievable zone of influence in the relatively impermeable soil column to 10' bgs <br /> Given the soil and groundwater conditions at this site, soil vapor extraction is not a <br />' recommended treatment method <br /> 5.0) CONCLUSIONS <br /> I <br /> It is concluded that the first groundwater table at the site at 10' bgs is retarded in part <br /> by a clayey layer Groundwater at the screened interval from 30' to 40' bgs has typically <br />' identified low level or no dissolved TPH-gas, BTEX and oxygenates in past monitoring <br /> Elevated levels of contaminants were isolated to those shallow screened groundwater <br /> monitoring wells during quarterly monitoring performed from 2000 until 2004 Some vertical <br />' leakage of the aromatic and oxygenate gasoline constituents appears to have occurred in <br /> 2005, as evidenced by identification of dissolved phase gasoline aromatics and oxygenates in <br /> deep screened (30' to 40' bgs) monitoring wells, which had no detectable concentrations of <br />' the gasoline constituents in previous testing It is evident that lateral migration of the <br /> oxygenate constituents is occurring as identified by recent increasing concentrations of <br /> MTBE in MW-9 r <br />' <br /> Several corrective action methods were evaluated for feasibility as well as cost <br /> Excavation is not practicable due to the location of the contamination The location of the <br />' building is directly next to, and possibly over, the source area, driving the cost up and the <br /> 1 <br /> I <br />