$EPA NRMRL \ NATIONAL RISK MANAGEMENT RESEARCH LABORATORY www.epa.gov/nrmrl GROUND WATER AND ECOSYSTEMS RESTORATION RESEARCH MTBE Diving Plumes Introduction There are approximately 400,000 confirmed releases of gasoline from underground storage tanks in the United States. At least 200,000 contain methyl tertian butyl ether (MTBE) at significant concentrations. The impact from these releases on ground water are monitored with shallow wells surrounding the releases. Because there are so many spills and because monitoring wells are expensive, there is a strong economic incentive to keep the network of monitoring wells simple and small. Occasionally, MTBE plumes will move below the bottom of the screen of conventional monitoring wells and escape detection. This is called plume diving. If the MTBE plume escapes detection, it can contaminate public water supply wells. Background Because MTBE does not sorb to aquifer material and because there is no biological degradation in many plumes, there is an opportunity for MTBE plumes to be very long. The longer the plume, the more likely that it will dive below the screen of conventional monitoring wells. Plumes can dive deeper into an aquifer by a number of mechanisms. Plumes can be buried by recharge of precipitation, moving down to the aquifer from the surface. Plumes tend to flow around clay layers and through sand or gravel layers. If the layers that control flow of ground water dive into the aquifer, so will the plume. Objectives • Document the phenomenon of plume diving at real gasoline spills • Determine the properties of the aquifer that caused the plume diving • Develop or evaluate tools that can be used to predict plume diving, and identify the best depth intervals for monitoring wells in order to detect diving plumes • Develop criteria that can be used to recognize MTBE plumes with no natural biodegradation Approach Detailed case studies were conducted on MTBE plumes at East Alton, Illinois; Spring Green, Wisconsin; and Milford, Michigan. Each of these plumes impacted a municipal water supply well. Plume diving through burial by recharge was estimated, using an EPA application available on the Web. Plume diving caused by structure of the aquifer was estimated by determining the vertical distribution of clay and sand layers, and the vertical distribution of hydraulic conductivity. The geochemistry of the receiving ground water and of the plume was characterized in order to recognize conditions where MTBE did not degrade. Screened Interval Conventional UST Well Point of Discharge -X 2000 3000 -W00 5000 6000 Distance (feet) The National Risk Management Research Laboratory's mission is to advance scientific and engineering solutions that enable EPA and others to effectively manage current and future environmental risks. NRMRL possesses unique strengths and capabilities and is dedicated to providing credible technological information and scientific solutions that support national priorities and protect human health and the environment. ------- Accomplishments At all three sites, the MTBE plumes dived deeply into the aquifer. Diving of the plume at Spring Green, Wisconsin, could be predicted from aquifer recharge, using the plume diving calculator. Visit: EPA Online Tools for Site Assessment Calculation (http://www.epa.gov/extrmurl/learn2model/part-two/onsite/diving .htm). Plumes at the East Alton, Illinois, and the Milford, Michigan, sites followed layers of sand and were constrained by layers of clay in the aquifer. The plume was found at the contact between a deep layer of sand and the layer of clay above it. Clay and silt often have high electrical conductivity and sand and gravel often have low conductivity. A simple tool recently available on the market can determine the electrical conductivity of aquifer material to depths of 100 feet or greater at reasonable cost. The tool was used at the East Alton site to map the clay and sand layers and predict the most likely interval to harbor the plume. Water samples were collect in discrete vertical intervals. The highest concentrations of MTBE were in the intervals that were predicted from the electrical conductivity measurements. In most aquifers, bacteria will degrade MTBE readily if oxygen is available. At all three sites, the MTBE plume was devoid of oxygen. At the East Alton, Illinois, site, the uncontaminated water in the aquifer was also devoid of oxygen. Future Tasks An EPA report on plume diving is in preparation. Wilson, J.T., R.R. Ross, and S. Acree. (Submitted for publication). "Site Characterization to Determine the Influence of Stratigraphy on a Diving Plume of MTBE in a Municipal Well Field." Ground Water Monitoring and Remediation. Investigators Collaborators Illinois Environmental Protection Agency Michigan Department of Environmental Quality New York Department of Environmental Conservation Steven Acree John Wilson U.S. EPA Region 5 Wisconsin Department of Natural Resources The National Risk Management Research Laboratory's mission is to advance scientific and engineering solutions that enable EPA and others to effectively manage current and future environmental risks. NRMRL possesses unique strengths and capabilities and is dedicated to providing credible technological information and scientific solutions that support national priorities and protect human health and the environment. ------- |