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��� <br /> t"� .�. <br /> ' - '/ '+6���tfi�i��'`�'n-i �T'+��•dK,&e69�Y 1Ii��. � M�' � F ` - <br /> ft <br /> i <br /> fH <br /> safety or groundwater resources exists. This is further <br /> supported by the non-detectable levels of gasoline <br /> hydrocarbons in a groundwater sample (Mw1) collected beneath <br /> the area of highest soil contamination. The 38 foot depth <br /> to water provides a large zone of atteE;uation (28 feet <br /> uncontaminated soil) which greatly reduces the <br /> potential of <br /> the shallow soil contamination from adversely affecting <br /> groundwater quality. The relatively low permeability silty <br /> soil types occurring to a depth of 28 feet should limit the <br /> r rate of vertical migration of the residual soil <br /> contamination. In addition, the surface above and <br /> surrounding this area is graded to prevent ponding and <br /> covered by impermeable surfaces (asphalt, concrete and the <br /> Police station structure) which greatly limits infiltration <br /> of precipitation. This will further seduce the already.,' <br /> limited for':vertical migration of contaminants As such, <br /> the on-site well IM-11E, completed in a deeper water <br /> affected. strata (> 170 feet) should not be adversely <br /> Y. <br /> 6.0 REMEDIAL ALTERNATIVE <br /> Soil remediation alternatives include cap/monitoring, <br /> excavation and in-situ treatment approaches. A summary of <br /> each alternative is presented below. <br /> 6.1 Alternative 1 <br /> The area of documented soil contamination as, well as 95t of <br /> the project site as a whole is covered by impermeable <br /> surfaces. Because this significantly reduces the <br /> infiltration of moisture to the subsurface the potential for <br /> migration (driven by percolation of moisture through the <br /> contaminated soil horizon) is limited. Natural degradation <br /> of the residual hydrocarbon contamination should occur over <br /> time. Periodic monitoring/sampling of well MW1 would <br /> Provide assurance that groundwater quality is not baing <br /> adversely affected. <br /> 6.2 Alternative 2 <br /> Excavation of the shallow soil contamination and treatment <br /> on-site (aeration) or disposal to a certified waste <br /> disposal facility would remove the potential source of <br /> groundwater contamination. As discussed in the previous <br /> section, a circular area with a 15 foot radius to a depth <br /> Of' 10 feet should define the limits of contamination. The '- <br /> excavation of contaminated material <br /> would be limited to the <br /> north, due to the existing police station structure. On- <br /> site aeration, if possible, would be preferred to disposal <br /> because of the continued long term liability associated with <br /> f disposal of contaminated material at an off-sits facility. <br /> e - Confirmaticn soil sampling should be conducted on the walls <br /> ---and -floor--of excavation--to--assure--all -of-- the------. .-- - -- - <br /> w: <br />