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• un 1995 15PM IEG TECHNOLOGIES No 2615 P 5/1JA <br /> 95-WP 103 05 <br /> monitoring wells 3IOW1 and 3IPW1, the following average hydraulic parameters are calculated (Earth <br /> Technologies Corporation, 1994) <br />• ' HYdraulic conductivity (k) 90 5 SPdlf ((average Site 31 value) <br /> Hydraulic gradient (i) 0 007 (December 1994 average condition) <br /> • Effective porosity (n.) 272% <br /> • Transport velocity (V) 0 31 friday <br /> TECHNOLOGY DESCRIPTION <br /> The WB technology uses a system of chemical, physical, and biological processes to treat VOC- <br /> contanunated groundwater and subsurface sods The UVB system consists of a specially adapted <br /> groundwater treatment well, a negative pressure stripping reactor, an aboveground vacuum extraction <br /> blower, and an off-gas treatment system if necessary (e g, activated carbon adsorption units)(Figure 2) <br /> The UVB treatment well is constructed with two screened zones one section which is placed at the <br /> bottom of the treatment interval, and one section which straddles the groundwater interface The <br /> borehole annulus between the two screened zones is sealed with bentonite. A packer is installed m the <br /> treatment well between the two screened zones to ensure one duectional flow of the groundwater through <br /> the treatment well. A pipe is placed through the packer and connected to a pump which provides <br /> groundwater from the lower zone to the upper zone where the stripper reactor is situated The upper end <br /> of the pipe terminates at the reactor <br /> The upper, closed part of the well, is maintained at below atmospheric pressure by a centrifugal blower. <br /> The air for the in-situ stnppmg is drawn m through a 3-inch diameter fresh air pipe the upper end is <br /> open to the atmosphere, and the lower end terminates m a pinhole plate (diffuser) located in the reactor <br /> Soil air is also drawn into the treatment well from the vadose zone through the upper well screen. The <br /> negative pressure within the upper part of the well also causes a water level rise within the treatment <br /> well <br /> The stripper reactor is balanced below the groundwater level within the treatment well and is free- <br /> floating to allow for changing water levels The location of the reactor month respect to the water level <br /> in the well determines the ratio of au that is drawn from the atmosphere through the air intake pipe, to <br /> the air that is drawn into the well from the vadose zone through the upper screen- This also controls the <br /> air to water ratio within the stepper reactor since only the air drawn from the surface through the air <br /> intake pipe is directed to the pinhole plate in the stripper reactor. Balancing of the system within the <br /> well is achieved by installing buoyancy tank; below the pump <br /> The zone within the well between the pinhole plate and the water surface is the stripping zone, in which <br /> an air bubble flow develops and strips VOCs from the groundwater The rising air bubbles produce an <br /> air lift pumping effect, which moves the water, and causes a suction effect at the bottom of the well <br /> Stnpped air from the groundwater, and extracted soil gas, is transported up through the casing and <br /> blower, for treatment, if necessary, before venting to the atmosphere <br /> The upward-streaming, stripped groundwater leaves the we❑ casing through the upper screen section of <br /> the treatment well The mass of flowing groundwater leaving the upper screen is counterbalanced by <br /> • the flow of groundwater toward the lower screened section, thereby setting up a three-dimensional <br /> groundwater circulation cell around the UVB well Contaminated groundwater flows toward the well <br /> 3 <br />