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DRAFT <br /> decrease over time, continued monitoring of site groundwater would serve no useful <br /> purpose. <br /> The only way to ensure complete removal of lingering, residual, detectable <br /> concentrations of petroleum constituents in site groundwater would be to excavate an <br /> additional several thousand cubic yards of affected soil to depths in excess of 50 feet. <br /> This would entail a substantial disruption of streets, businesses, sewers and other utilities <br /> while producing little or no benefit to current or anticipated beneficial uses of the <br /> minimal area of groundwater not meeting Basin Plan objectives. <br /> Furthermore, if complete removal of detectable traces of petroleum constituents <br /> becomes the standard for UST corrective actions, the statewide technical and economic <br /> implications will be enormous. For example, disposal of soils from comparable areas of <br /> excavation throughout the state would.greatly impact already limited landfill space. In <br /> light of the minimal if any benefit to be gained, the evidence of continuing attenuation of <br /> residual petroleum concentrations, and the precedent that would be set by requiring <br /> additional excavation at this site, attaining background water quality in this limited area is <br /> not feasible. While it is impossible to determine the precise level of water quality that <br /> will be attained given the residual petroleum constituents that remain at the site, in light <br /> of all the factors discussed above, a level of water quality will be attained that is <br /> consistent with the maximum benefit to the people of the state4. <br /> The final step in determining whether cleanup to a level of water quality less <br /> stringent than background is appropriate for this site requires a determination that the <br /> 4 In approving an alternative level of water quality less stringent than background, the SWRCB has also <br /> considered the factors contained in California Code of Regulations,title 23, section 2550.4,subdivision <br /> (d). As discussed earlier,the adverse effect on shallow groundwater will be minimal and localized,and <br /> there will be no adverse effect on the groundwater contained in deeper aquifers,given the physical and <br /> chemical characteristics of petroleum constituents;the hydrogeological characteristics of the site and <br /> surrounding land; and the quantity of the groundwater and direction of the groundwater flow. In addition, <br /> the potential for adverse effects on beneficial uses of groundwater is low, in light of the proximity of <br /> groundwater supply wells; the current and potential future uses of groundwater in the area; the existing <br /> quality of groundwater; the potential for health risks caused by human exposure;the potential damage to <br /> wildlife,crops,vegetation,and physical structures;and the persistence and permanence of potential effects. <br /> Finally, a level of water quality less stringent than background is unlikely to have any impact on <br /> surface water quality, in light of the volume and physical and chemical characteristics of petroleum <br /> constituents; the hydrogeological characteristics of the site and surrounding land; the quantity and quality <br /> of groundwater and the direction of groundwater flow; the patterns of precipitation in the region,and the <br /> proximity of residual petroleum to surface waters. <br /> , f <br />