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GeoHydrologic Consultants, Inc. <br /> seen within the treatment zone. The results of the long-term bromate attenuation test are <br /> presented in Table 1 1 of the Prima Report located in Appendix B. <br /> 4.4 Conclusions <br /> The ozone bench scale study demonstrated that site petroleum hydrocarbons in soil and <br /> groundwater can be successfully destroyed with ozone treatrriunt. in both the low dose <br /> (1,600 mg) and high dose (2,600 mg)ozone treatments greater than 99%of COCs were <br /> destroyed in the groundwater, with less than I%detected in off-gases. The entire Prima <br /> Bench Scale Test Report which presents soil and groundwater sampling results, and the <br /> effectiveness of this bench scale study, is attached in Appendix B. <br /> Cr(VI) and bromate were generated with treatment of ozone at concentrations that <br /> exceeded the maximum contaminant levels (MCLs) in groundwater for Cr(VI) of 0.050 <br /> mg/L and bromate of 0.010 mg/L. The results of the Cr(VI) attenuation study indicated <br /> that the soil from the Site has some ability to reduce Cr(VI) and that ozone may affect the <br /> ability of the soil to attenuate Cr(VI), but the magnitude of the effect depends on the <br /> amount of ozone applied. The results of the long-term Cr(VI) attenuation test showed that <br /> Cr(VI) readily attenuated in simulated downgradient conditions with complete removal of <br /> Cr(VI) in only seven days. In contrast, the concentration of Cr(VI) initially increased <br /> within the treatment area, but then slowly attenuated. Complete removal had not occurred <br /> with 60 days. The results of the long-term bromate attenuation tests showed that bromate <br /> appeared to attenuate slowly in tests simulating downgradient conditions; by 28 days the <br /> bromate concentration had decreased from 0.31 mg/L to 0.16 mg/L, still well above the <br /> MCLs for bromate (0.010 mg/L). In contrast no attenuation was seen within the treatment <br /> zone during the study. Other secondary parameters behaved as expected, with alkalinity <br /> decreasing and pH increasing. <br /> 5.0 CONCLUSIONS AND RECOMMENDATIONS <br /> The ozone bench scale study demonstrated that site petroleum hydrocarbons in soil and <br /> groundwater can be successfully destroyed with ozone treatment however ozone sparging <br /> generated elevated concentrations of Cr(VI) and bromate at concentrations that exceeded <br /> the California MCL for these compounds. In addition, the attenuation study conducted for <br /> the CC(VI) and bromate which was formed demonstrated that both of the compounds <br /> were relatively slow to attenuate downgradient to concentrations below the MCL and <br /> attenuation within the treatment zone either showed very slow attenuation rates with <br /> respect to Cr(VI) or no appreciable attenuation with respect to bromate. Therefore, based <br /> on these results ozone sparging is no longer being proposed for the Site because of the <br /> elevated risk that ozone sparging activities will create a new Cr(VI) and bromate plume <br /> within the treatment area at concentrations that will exceed the California MCLs for these <br /> compounds. <br /> Based on the recent developments at the Site which included removal of the USTs, fuel <br /> lines, and dispensers it does not appear that the Site will be used for retail fuel sales in the <br /> TOC#172 Bench Scale Test Page 15 <br />