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magnitude of 0.003 ft/ft, but the plume has already migrated off site and this method.would-- <br /> do nothing to prevent further off-site migration. <br /> ♦ Criterion 3: <br /> This alternative would not immediately remediate soil or groundwater to levels acceptable <br /> to regulatory agencies. Natural degradation of residual hydrocarbons would occur over <br /> time. <br /> ♦ Criterion 4: _ <br /> Additional costs for implementing this alternative arc related to the costs associated with the <br /> continued monitoring to ensure natural attenuation is occurring and the permitting and <br /> destruction of existing wells at,project completion.. The cost of this alternative is estimated <br /> to be about $20,000 per year for monitoring, $15,000- to. .$20,000- for-'enhancing <br /> biodegradation with introduction of oxygen if warranted,and$30,000 for a closure plan and <br /> well destruction. - E, <br /> ♦ Criterion 5: <br /> This alternative is effective in 'minimizing the health-based risks in the'short' term. <br /> Exposure to humans by contamination releases to the air due to dust,or through ingestion or <br /> dermal exposure to impacted soil or groundwater is minimal during groundwater <br /> monitoring and well destruction activities but is otherwise nonexistent. <br /> ♦ Criterion b: <br /> The long term effectiveness of this-alternative is•iiot'acceptable. This alternative would <br /> reduce the toxicity and volume of the contaminants in the soil and groundwater by natural <br /> biodegradation, but the rate of reduction is not known.' The possibility for health-based <br /> risks in the longterm is moderate because contamination has already migrated off site. <br /> ♦ Criterion 7: <br /> Of all the alternatives the passive remediation approach is the easiest to implement. <br /> Groundwater monitoring activities would continue to ensure natural attenuation is <br /> occurring. When concentrations have reduced' to levels acceptable to the regulatory <br /> agencies or an apparent decreasing trend is evident, a closure plan will be submitted. Well <br /> destruction permits would be obtained from the appropriate agencies and the wells would be <br /> destroyed by overdrilling the well casing and sand pack and pressure grouting the boring to <br /> the surface when concentrations have been reduced to an acceptable level. <br /> ♦ Criterion 8: , <br /> Since minimal activity would be conducted at the site, the impact on the community would <br /> be very minor and not disruptive to the businesses located on the site and nearby. <br /> i <br /> S A22493\reports\CAP.doc 9 <br />