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ENSR AECOM <br /> 1 <br /> 5.0 Conclusions and recommendations <br /> 5.1 Status of response actions <br /> Soil and groundwater beneath the site has been adequately assessed. Some additional delineation <br /> downgradient could be performed as part of a commingled plume investigation in conjunction with the Vintage <br /> Car Wash site. However, because the data from U-20 and U-21 suggest that Unocal plume is a relatively <br /> minor component of the commingled plume, and because downgradient concentrations approach MCLs, <br /> downgradient delineation is not considered as high a priority, as remediation operations such that additional <br /> oxygen is introduced to the system to enhance the natural attenuation processes that are ongoing at the site. <br /> Permeability testing has not been performed at the site. Some permeability testing, including evaluation of <br /> pilot test data, is recommended to allow better analysis of plume fate and transport and to getter evaluate <br /> remedial alternatives at the site. <br /> 5.2 Implications of the conceptual site model <br /> The complex, interbedded alluvial deposits at the site and the history of groundwater fluctuations make <br /> remediation extremely challenging. Sparging relies on generating contact between injected gases and source <br /> area contaminants. While petroleum has been detected in both fine-grained and coarse-grained soils, <br /> ' sparged gases are preferentially passed through coarse-grained materials. Accordingly, most ozone sparge <br /> points have been installed in coarser-grained lenses within the formation. <br /> Given the near forty-year age of the release,the plume is almost certainly at_stea�state with the natural <br /> attenuation processes us further mi ration of the plume is not a valid concern. In addition, natural �. <br /> attenuation parameter data are consistent with some meas re o anaerobic biodegradation occurring at the <br /> site. Because anaerobic degradation is much less efficient than aerobic degradation and because the <br /> ' downgradient wells are approaching MCLs, remediation will likely incorporate a method that introduces oxygen <br /> to the aquifer to enhance the natural attenuation processes that are already occurring. <br /> ' 5.3 Existing remedial system <br /> Given that the evidence indicates that the ozone sparge system has not been operating as intended, a <br /> reevaluation of technical feasibility and potential system effectiveness is necessary. This reevaluation should <br /> be performed in a phased fashion. The first phase will involve rehabilitating the sparge wells on site and <br /> performing necessary system repairs, collecting some new baseline data and performance testing the repaired <br /> sparge system to determine whether it is adequately raising oxygen concentrations in the aquifer. Because <br /> ' replacing lines beneath the street will be an involved process,the decision regarding the disposition of these <br /> wells will be made following evaluation of the initial performance testing results. <br /> New baseline data would include dissolved oxygen, oxidation-reduction potential measurements and VOC <br /> concentration data, including a search for tentatively identified compounds (TICS)that are indicative of <br /> biodegradation of gasoline hydrocarbons (e. ., alcohols and phenolics). These data would be obtained at <br /> g <br /> , <br /> wells in the vicinity of, and downgradient o eon-Mea sparge sys em (i.e., U-3, U-8, U-9 and U-10 and the <br /> NP-1 and NP-2 well clusters). Performance testing should be conducted over a period of three months with <br /> field chemistry parameters monitored monthly and TIC samples obtained during quarterly monitoring events. <br /> The next phase of remediation evaluation and testing activities will depend on the results of the initial <br /> performance test. If the rehabilitated system works as intended, then the lines and wells across California <br /> Street associated with sparge clusters SP-5 and SP-6 should be rehabilitated and repaired. However, if the <br /> results of the performance test indicate that raisin ox levels in thea uifer is not feasible with the given <br /> i• . <br /> JARem_EngTroject File51P60(6000- <br /> ' 6999)16940-UNOCAL Portfolio Closure%940 -1 January 2006 <br /> UNOCAL Portfolio Closure\Site 0187-Stockton <br /> East MinoACSM FleporACSM Report_Final.doc <br />