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To be presented at 1999 Petroleum Hydrocarbons Conference, Houston, Texas <br />Laboratory -Scale Evaluation of In Situ Aerobic MTBE <br />Biodegradation Options for Vandenberg Air Force Base, California <br />Ryan D. Wilson, Mario Schirmer , Claudia N. Naas, Amanda Smiths, <br />Christy Smiths, Kate M. Scows, Mike R. Hyman$ and Douglas M. Mackay <br />Department of Earth Sciences, University of Waterloo, Waterloo, Ontario, Canada, N2L 3G1 <br />* UFZ Centre for Environmental Research Leipzig -Halle, Department Industrial and Mining Landscapes <br />Permoser Str. 15, 04318 Leipzig, Germany <br />t Dept. of Land, Air and Water Resources, University of California, One Shields Avenue, <br />Davis, CA 95616-8627 <br />$ Department of Microbiology, Campus Box 7615, North Carolina State University, Raleigh NC 27695 <br />Abstract <br />Methyl tert-butyl ether (MTBE) has rapidly become a contaminant of significant concern throughout the US, <br />and is increasingly gaining attention throughout Europe. Dissolved plumes of MTBE travel at the speed of <br />groundwater and resist biodegradation under typical plume conditions, negating natural attenuation as a plume <br />management strategy. Thus some form of in situ treatment is often indicted. As part of ongoing work at <br />Vandenberg AFB (VAFB), we are examining three general approaches to enhancing in situ aerobic degradation <br />of MTBE at the lab scale: 1) enhancement of activity of indigenous microbes capable of metabolizing MTBE, <br />2) emplacement of non-native MTBE -metabolizing microbes, and 3) stimulation of cometabolism by <br />indigenous microbial consortia. Sediment and water samples were collected from an area that has been highly <br />characterized and where in situ treatment pilot tests are on-going or planned. For the cometabolic evaluations, a <br />series of batch microcosms were set up consisting of sediment and water from the site and combinations of <br />MTBE and either hexane (n -alkane), isopentane (branched alkane), or cyclohexane (cyclic alkane). These <br />alkanes have all been shown by others to result in cometabolic MTBE degradation by various enriched or pure <br />microbial cultures. <br />There is evidence from microcosm studies that there may be indigenous microbes present at VAFB capable of <br />utilizing MTBE as a primary substrate under aerobic conditions. Lab tests have also shown that a gram- <br />negative proteobacteria strain isolated from a compost -filled biofilter treating volatile emissions from a water <br />treatment plant is capable of degrading MTBE when introduced to VAFB soils and water. With regard to <br />prospects for cometabolism, one or more of the tested alkanes were degraded in sediment from upgradient or <br />within the plume, however, MTBE cometabolism was noted in only a subset of these cases. These results may <br />suggest either spatially variable microbial populations, the presence of one or more undetected inhibitory <br />compound(s), and/or the lack of some required nutrient within the plume. Additional work with soils from the <br />plume has shown vigorous microbial growth on propane, modest growth on n -butane, and minor growth on <br />isobutane — three gases we have identified as potential primary substrate candidates for field testing of MTBE <br />cometabolism. Further tests suggests that organisms grown on all three alkanes cometabolize MTBE. Ongoing <br />microcosm work includes examining the effects of various nutrient additions, potential inhibition caused by <br />other alkanes and/or aromatics, and initial MTBE concentration on the rate of MTBE oxidation. The aims of <br />these efforts are to 1) identify the geochemical conditions that can practically be induced in the field to support <br />in situ aerobic degradation of MTBE and 2) identify any potential degradation inhibitors. <br />Page 1 <br />