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C A M B R I A Ms. Lori Duncan <br /> September 9,2005 <br /> vacuum of the vapor extraction wells observed during pilot testing. The treatment device is <br /> determined by the anticipated influent flow rate, hydrocarbon concentration, air quality <br /> requirements,and operating duration. <br /> AS is a remedial technology whereby air is injected into the saturated zone to remove volatile <br /> contaminants by stripping them from water, transferring them to the vapor phase, and removing <br /> the vapors by SVE. The technology is designed to operate at relatively high air flow rates <br /> (greater than 2 cubic feet per minute per injection point) in order to cause volatilization. SVE is <br /> most effective in moderate to high permeability soils. AS is not specifically aimed at stimulating <br /> biodegradation, although enhanced biodegradation may be realized as a secondary effect. AS <br /> © must operate in tandem with an SVE system that captures the volatile contaminants stripped from <br /> the saturated zone. <br /> Equipment required to implement AS would include a compressed air source (air compressor), <br /> compressed air conveyance piping, specifically designed AS wells, and a down-well delivery <br /> system (piping and/or stingers). The air compressor would be sized based on the number of <br /> injection points, pressure losses through the delivery system, and minimum pressure and flow <br /> delivery at the injection depth. <br /> Feasibility and Cost-Effectiveness: Design, permitting, and installation of an SVE/AS system at <br /> the subject site would cost an estimated $175,000 to $200,000. This estimate is based upon <br /> installing four additional SVE wells and four AS wells, installing underground piping, <br /> constructing a treatment compound, and installing the required equipment, including a new <br /> thermal oxidizer. Operational cost of an SVE/AS system for the first year is estimated at <br /> $60,000. SVE/AS operation is assumed for a minimum of 3 years and a maximum of 5 years to <br /> meet soil clean-up levels. Operational costs would decrease over time as influent concentrations <br /> and mass removal rates decrease and become asymptotic. As vapor concentrations decrease, a <br /> thermal oxidizer could be replaced by a more fuel-efficient catalytic oxidizer, and later by vapor- <br /> phase GAC adsorption vessels. The average annual operational cost is estimated at $40,000 per <br /> year <br /> SVE is likely to be somewhat effective at reducing source area hydrocarbon mass in the vadose <br /> zone. However,SVE effectiveness at the site would be limited by the high proportion of clay and <br /> silt (low permeability) soils above the current water table, and SVE would not directly treat <br /> groundwater and saturated soils. SVE with AS may be significantly more effective than SVE <br /> alone, since it also volatilizes and removes hydrocarbon constituents from groundwater and <br /> saturated soils beneath the site. However, as with SVE, AS effectiveness may be limited by the <br /> low permeability soils below the water table. Once concentrations appear to be approaching <br /> asymptotic conditions, pulsed operation may be needed to assess soil vapor and groundwater <br /> concentration rebound. To verify soil clean-up, confirmation soil borings would be required. <br /> The cost of four confirmation soil borings is estimated at$10,000. <br /> 15 <br />