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___ <br /> V � <br /> A S S O C I A T E S I N C <br /> F.._.� ♦ Criterion 2: <br /> This alternative would reduce the existing levels and volume of impacted soil and groundwater <br /> over time by natural degradation and attenuation, but the rate of reduction is not known. The <br /> possible migration of petroleum hydrocarbons in soil caused by surface water flushing <br /> - contaminants into the groundwater is minimal due to the asphalt and concrete surface on site. <br /> The groundwater gradient direction has been consistently northwest with a magnitude of 0.003 <br /> ft/ft which makes it unlikely that the plume will migrate off site in the short term. <br /> ♦ Criterion 3: <br /> This alternative would not immediately remediate soil or groundwater to levels acceptable to <br /> regulatory agencies. Natural degradation of residual hydrocarbons would occur over time. <br /> ♦ Criterion 4: <br /> == Additional costs for implementing this alternative are 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 to r <br /> be about$7,000 per year for monitoring, $5,000 to $10,000 for enhancing biodegradation with <br /> introduction of oxygen if warranted, and$5,000 for a closure plan and well destruction. <br /> .- ♦ Criterion 5: <br /> This alternative is effective in minimizing the health-based risks in the short term. Exposure to <br /> humans by contamination releases to the air due to dust, or through ingestion or dermal <br /> exposure to impacted soil or groundwater is minimal during groundwater monitoring and we <br /> ll <br /> destruction activities but is otherwise nonexistent. <br /> ♦ Criterion 6: <br /> The long term effectiveness of this alternative is acceptable. This alternative would reduce the <br /> '=s3 toxicity and volume of the contaminants in the soil by natural biodegradation, but the rate of <br /> reduction is not known. The possibility for health-based risks in the long term is low as long as <br /> the site remains surfaced and exposure of humans to impacted soil does not occur during any <br /> type of site excavation or structure demolition activities. <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 occurring. <br /> When concentrations have reduced to levels acceptable to the regulatory agencies or an <br /> apparent decreasing trend is evident, a closure plan will be submitted. Well destruction permits <br /> would be obtained from the appropriate agencies and the wells would be destroyed by <br /> �- <br /> overdrilling the well casing and sand pack and pressure grouting the boring to the surface when <br /> concentrations have been reduced to an acceptable level. <br /> w:1451221repoM\parcap.doc 10 <br />