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Bioventing Page 3 of 5 <br /> '-ow. ..� <br /> wells are used. <br /> System Design <br /> In general, remedial approaches that rely on biological processes should be subject <br /> to field pilot studies to verify and quantify the potential effectiveness of the <br /> approach and provide data necessary to design the system. For bioventing, these <br /> studies may range in scope and complexity from a simple soil column test or <br /> microbial count to field respirometry tests and soil vapor extraction (or injection) <br /> pilot studies. The scope of pilot testing or laboratory studies should be <br /> commensurate with the size of the area to be remediated, the reduction in <br /> constituent concentration required, and the results of the initial effectiveness <br /> screening. <br /> Design Radius of Influence (ROI) is an estimate of the maximum distance from a <br /> vapor extraction well (or injection well) at which sufficient air flow can be induced to <br /> sustain acceptable degradation rates. Establishing the design ROI is not a trivial <br /> task because it depends on many factors including intrinsic permeability of the soil, <br /> soil chemistry, moisture content, and desired remediation time. The ROI should <br /> usually be determined through field pilot studies but can be estimated from air flow <br /> modeling or other empirical methods. Generally, the design ROI can range from 5 <br /> feet (for fine-grained soils)to 100 feet(for coarse-grained soils). For sites with <br /> stratified geology, radii of influence should be defined for each soil type. The ROI is <br /> important in determining the appropriate number and spacing of extraction or <br /> injection wells. Stratified soils may require special consideration in design to ensure <br /> that less-permeable strata are adequately vented. <br /> At a site with homogeneous soil conditions, the well should be screened throughout <br /> the contaminated zone. The well screen may be placed as deep as the seasonal <br /> low water table. A deep well helps to ensure remediation of the greatest amount of <br /> soil during seasonal low groundwater conditions. <br /> At a site with stratified soils or lithology, the screened interval can be placed at a <br /> depth corresponding to a zone of lower permeability. This placement will help <br /> ensure that air passes through this zone rather than merely flow through adjacent <br /> zones of higher permeability. <br /> Airflow is particularly important for soils within the capillary fringe, where a <br /> significant portion of the constituents often reside. Fine-grained soils create a <br /> thicker capillary fringe than coarse-grained soils. The thickness of the capillary <br /> fringe can usually be determined from soil boring logs (i.e., in the capillary fringe, <br /> soils are usually described as moist or wet). The capillary fringe usually extends <br /> from one to several feet above the elevation of the groundwater table. Moisture <br /> content of soils within the capillary fringe may be too high for effective bioventing. <br /> Depression of the water table by groundwater pumping may be necessary to <br /> biovent soils within the capillary fringe. <br /> Fluctuations in the groundwater table should also be considered. Significant <br /> seasonal or daily (e.g., tidal or precipitation-related) fluctuations may, at times, <br /> submerge some of the contaminated soil or a portion of the well screen, making it <br /> unavailable for air flow. These fluctuations are most important for horizontal wells, <br /> in which screens are placed parallel with the water table surface and a water table <br /> rise could occlude the entire length of screen. <br /> Bacteria require moist soil conditions for proper growth. Excessive soil moisture, <br /> however, reduces the availability of oxygen, which is also necessary for bacterial <br /> metabolic processes, by restricting the flow of air through soil pores. The ideal <br /> range for soil moisture is between 40 and 85 percent of the water-holding capacity <br /> http://www.epa.gov/swerustl/cat/biovent.htm 6/17/2004 <br />