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i <br /> • <br /> a i re provided in Table 1 and presented graphically m Appendix C UVB-MW1 is located <br /> approximately 5 feet from the UVB well, screened from 35 to 40 feet bgs, and approximates <br />' the same depth interval of the lower screened interval of the UVB well, which was used for <br /> groundwater extraction As presented in the UVB-MW 1 hydrograph (Appendix C), the <br /> concentrations of benzene and TPH-g when operation of the UVB began in February 1997 <br /> were 7,200 }Lg/L and 99,000 µg/L, respectively Concentrations decreased to 1,200 µg/L <br /> benzene and 17,000 µg/]L TPH-g in October 1997 After October 1997, the benzene and <br /> TPH-g concentrations increased to 12,000 µg/L and 130,000 µg/L, respectively, in <br />' September 2000, when the UVB system was shut down Groundwater concentrations in well <br /> UVB-MW 1 have remained near the current levels of 11,600 µg/L benzene and 122,000 µg/L - <br /> TPH-g since the UVB system was shut down Because operation of the UVB system hadt-�rm�GJu <br /> little or no effect on concentrations of hydrocarbons in a monitoring well located within 5 <br /> feet, UVB is not considered an applicable technology, given site conditions <br />' • Ozone Sparging. Ozone is a relatively strong oxidant when compared with persulfate, <br /> hydrogen peroxide, and permanganate However, it is very unstable The short half-life of <br /> ozone greatly limits its travel distance even within ideal conditions of permeable and <br /> homogeneous soils Ozone is not considered an applicable technology for this site for the <br /> following reasons <br /> The free hydroxyl radicals generated by ozone can only react with dissolved phase <br /> compounds Thus, ozone is not an effective remedial technology for free-phase or residual <br />' . LPH in source areas <br /> Because the saturated zone is heterogeneous and largely silty, infected material is not <br /> expected to be uniformly distributed and instead flows in preferential channels in the <br /> saturated zone, making hydrocarbon removal from fine-grained materials difficult These <br /> preferential pathways for groundwater movement may help explain the limited effect air <br />' sparging had due to site conditions Air spargmg was conducted in conjunction with SVE at <br /> the site from February 1994 through August 1996 in and downgradient of the former tank <br /> field Though spargmg well SW2 is located approximately 15 feet upgradient of well UVB- <br />' MW1, the hydrocarbon concentrations in groundwater measured in UVB-MW1 did not <br /> substantially decrease in this area due to spargmg <br />' • Groundwater Pump-and-Treat. Groundwater pump-and-treat is a traditional technology <br /> which is widely used due to its conceptual simplicity The lack of solubility of hydrocarbons <br /> in groundwater and partitioning of hydrocarbons between groundwater and soil limit the <br /> effectiveness of groundwater pump and treat systems A pump-and-treat system at this site <br /> would generate a significant amount of groundwater for treatment and disposal over an <br /> extended period of time, while potentially promoting the migration of hydrocarbons and <br />' MTBE from neighboring offsite sources As this technology is less applicable for sites <br /> containing LPH, it should not be implemented as the only means of remediating the site It <br /> is, however, being considered in conjunction with dual-phase extraction as a means of <br />' dewatering the site and therefore enhancing the effectiveness of dual-phase extraction <br /> 1 <br /> CrlProjects173942VMASTER�WP\%M3031Wft doc 16 <br />