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Table 4-1 <br /> Evaluation of Remediation Options <br /> Option A-Intrinsic Bioremediation Option B-Pumping and Aboveground <br /> Criteria Demonstration with ASISVE Treatment with ASISVE <br /> Overall Protection of Human Health <br /> j and the Environment <br /> • Contact with contaminated No potential for contact with shallow Contact could occur in the event of a <br /> groundwater groundwater has been identified. treatment system leak,spill,or failure. <br /> • Migration of gasoline The currently operating AS/SVE system The currently operating AS/SVE system <br /> constituents from soil to component of Option A is removing NAPL component of Option B is removing.NAPL <br /> groundwater from the soil/groundwater interface as well as from the soil/groundwater interface as well as <br /> residuals in the vadose zone. residuals in the vadose zone. <br /> • Migration of gasoline Groundwater flow,and thus contaminant Migration is controlled by the inward gradient <br /> i constituents with groundwater <br /> � migration,is naturally limited by the created by groundwater pumping. <br /> confining formation. Natural biodegradation <br /> at the perimeter will provide further <br /> confinement. <br /> . • Contact with contaminated Direct contact with contaminated soil or.soil Direct contact with contaminated soil or soil <br /> soil or soil vapor vapor is not a potential risk due to thadepth to vapor is not a potential risk due to the depth to <br /> fuel constituents. fuel constituents. <br /> I. <br /> Reduction of Toxicity,Mobility, Produces geochemical data that will document Provides slightly greater contaminant mass <br /> Contaminant Mass or Volume mass removal rates and contaminant fate i removal(0.12 lb/day)through groundwater <br /> mechanisms and identify rate limiting stripping. Reduces mobility by creating an <br /> { processes. inward gradient. <br /> Short-Term and Long-Term No potential for exposure during Some potential for human exposure during <br /> (i Effectiveness implementation. Demonstrates short-term implementation. Only demonstrates longer- <br /> evidence of degradation/remediation processes term contaminant concentration reductions. <br /> as well as longer-term contaminant Time to achieve complete remediation is <br /> concentration reduction. Time to achieve expected to be greater than 30 years. <br /> complete remediation goals is expected to be <br /> greater than 30 years. <br /> Implementation <br /> • Construction and operation No additional construction or equipment Requires installation of pumping wells, <br /> needed. piping,treatment equipment,a foundation,and <br /> i utilities. Also requires long-term maintenance <br /> and operation of equipment. <br /> • Permitting and approval State policy currently developing would allow A widely accepted technology. State and <br /> fuel constituents to remain after source local agencies are likely to approve.A <br /> material removal as long as monitoring discharge permit is required to send treated <br /> continues and a contingency plan is in place. groundwater to a POTW. increases hydraulic <br /> No permits required. loading to the POTW. Air quality permit and <br /> j building permit is required. <br /> • Public perception <br /> The public should receive information about Public may perceive the option as active . <br /> intrinsic bioremediation so they do not remediation. Noise and visual impacts are <br /> perceive the option as no action and no noise, associated with a pumping and treatment <br /> i visual impacts,or obvious activity, system. <br /> Costs <br /> • Capital Cost $ 11,700 $138,000 <br /> E. • Annual O&M Cost $ 16,460 $32,865 <br /> .'p <br /> } • Present Worth Cost $323,288 $760,138 <br /> SF010090995DOC <br />