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A Study of Long-Term MTBE Attenuation in the Borden Aquifer, Ontario, Canada
Authors:Mario Schirmer  James F. Barker
Affiliation:Mario Schirmer;is a Ph.D. student in hydrogeology at the University of Waterloo (Department of Earth Sciences, Waterloo, ON N2L 3G1, Canada. Phone 888–4567, ext. 6002;e-mail mschirmer@cgrpc.watstar.uwaterloo.ca), working on multiscale aspects of biodegradation modeling. He obtained his Diplom in geophysics from the University Mining Academy Freiberg (Germany) and worked as a research associate at the University of Stuttgart (Germany) before coming to Waterloo. James F. Barker;is a professor in earth sciences at the University of Waterloo (Department of Earth Sciences, Waterloo, ON N2L 3G1, Canada). His research interests include intrinsic and active bioremediation and in situ control technologies (reactive walls, funnel-and-gates) for dealing with ground water contaminated by organics.
Abstract:In 1988 and 1989, a natural gradient tracer test was performed in the shallow, aerobic and aquifer at Canadian Forces Base (CFB) Borden. A mixture of ground water containing dissolved oxygenated gasoline was injected below the water table along with chloride (Cl-) as a conservative tracer. The migration of BTEX, MTBE, and Cl was monitored in detail for 16 moths. The mass of BTEX compounds in the plume diminished significantly with time due to intrinsic aerobic biodegradation, while MTBE showed only a small decrease in mass over the 16-month period. In 1995/96, a comprehensive ground water sampling program was undertaken to define the mass of MTBE still present in the aquifer. Since the plume had migrated into an unmonitored section of the Borden Aquifer, numerical modeling and geostatistical methods were applied to define an optimal sampling grid and to improve the level of confidence in the results. A drive point profiling system was used to obtain ground water samples. Numerical modeling with no consideration of degradation pedicted maximum concentrations in excess of 3000 μg/L; field sampling found maximum concentrations of less than 200 μg/L. A mass balance for the remaining MTBE mass in the aquifer eight years after injection showed that only 3% of the original mass remained. Sorption, volatilization, a biotic degradation, and plant uptake are not considered significant attenuation processes for the field conditions. Therefore, we suggest that biodegradation may have played a major role in the attenuation of MTBE within the Borden Aquifer.
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