On April 6, representatives of four federal agencies signed a memorandum of agreement to cooperatively test and document the cost and performance of three innovative technologies for treating dense, nonaqueous-phase liquids, or DNAPLscompounds that have traditionally proven difficult to characterize and remediate. Although the MOA was signed only recently, the Interagency DNAPL Consortiums (IDC) Core Management Team has been working together for more than a year to prepare for the side-by-side demonstration and comparison of DNAPL technologies. Early accomplishments of the team include delineating each agencys role in the project, selecting and characterizing the demonstration site at Launch Complex 34 at the Cape Canaveral Air Station in Florida, and selecting the vendors whose technologies will be demonstrated. Members of the consortium are the U.S. Department of Energys Subsurface Contaminants Focus Area; the U.S. Environmental Protection Agencys National Risk Management Research Laboratory in Cincinnati, Ohio; the U.S. Department of Defenses Air Force Research Laboratory at Tyndall Air Force Base, Florida; the National Aeronautics and Space Administrations Kennedy Space Center, Florida; the U.S. Air Force 45th Space Wing at Patrick Air Force Base, Florida; and the Cape Canaveral Air Station, Florida. DNAPLsa tough and widespread problem When DNAPLs are spilled, they tend to migrate downward through the soil and continue to sink through the groundwater until relatively impermeable material is encountered. Because gravity rather than direction of groundwater flow controls DNAPL movement, DNAPLs can flow down a sloping aquifer even when groundwater flow is in the opposite direction. As DNAPLs migrate in the subsurface, they leave behind a trail of droplets and ganglia in pore spaces. When low-permeability zones are encountered, DNAPLs may form pools of free product. Residual droplets, ganglia, or pools of free product may continue to contaminate groundwater for centuries. The U.S. Air Force estimates that chlorinated solvents are, after spilled fuel, the second most common contaminant in soils and groundwater and anticipates cleaning up nearly 600 sites. Approximately 30 sites at 15 DOE facilities are confirmed or believed to have high potential for DNAPLs. One of the largest DOE spills, at the A/M Area at the Savannah River Site, may contain up to 1,750 tons of DNAPL, which has contaminated an estimated 4 billion gallons of otherwise potable groundwater. The chemical and physical behavior of these contaminants makes them difficult to detect, characterize, and treat and raises the possibility of health-threatening contamination continuing for centuries or even millennia. The difficulty of this challenge has been declared as unprecedented in the field of groundwater engineering. Ten years ago, the problem was described in most dire terms by Allan Freeze and John Cherry in the journal Ground Water (Volume 27, Number 3, MayJune, p. 463): There is now little doubt that at sites where DNAPLs are the problem, the local groundwater zone has terminal cancer. A cure, in the form of returning aquifer quality to drinking water standards, is unachievable at almost any cost. At DNAPL sites, costs are going up and aquifers are not much improved. There are no established technologies available to economically address this problemonly innovative technology systems hold out hope, but comparative performance data are needed. More progress through collaboration Early says that it was recognized that funding for technology development was on the downswing and that agencies could improve the retrograde funding picture and leverage resources by working together. Also, the emphasis began to move toward cleanup, using innovative technologies that we had in the toolbox now. Instead of developing more technologies, more progress could be made by focusing on the testing of technologies that could be deployed within five to ten years. We didnt have a good way to compare these technologies, so we were at the point to jointly sponsor a side-by-side demonstration of their performance and cost. Early believes the testing at Cape Canaveral is only the first step. It will be necessary to conduct other comparative demonstrations to test the robustness of these technologies at other sites with more complex conditions than exist at Launch Complex 34. DOE Subsurface Contaminants Focus Area Lead Office Manager Jim Wright also stresses the importance of collaboration. This interagency collaborative effort to clean up a DNAPL-contaminated site at the NASA Launch Pad 34 will yield many benefits. First is the demonstrated ability to put together a major remediation project with multiple agencies sharing resources and expertise to solve a common problem. Second will be the verified cost and performance data that each agency can use to advance its baseline remediation techniques. And lastly, this effort will result in a willingness to address other common problems in a cooperative and cost-effective manner. Technologies ready for testing Six-Phase Soil Heating SPSH relies on indigenous soil moisture to create an in situ source of steam that strips volatile and semivolatile contaminants from soils. An electrical current passes through soil, which generates heat due to the soils electrical resistance. The temperature within the remediation area is increased to the boiling point of water. Soil moisture becomes steam that is captured by vapor recovery wells for removal. Soil contaminants are also vaporized and are captured for ex situ treatment. SPSH is an enhancement to soil vapor extraction, which is ineffective if contaminants cannot be easily vaporized or if the soil is tightly bound, as in silts and clays. SPSHs electrical soil heating overcomes this obstacle by raising the temperature of the soil and contaminants, increasing the contaminants vapor pressure and thus their removal rate. Dynamic Underground Stripping plus Hydrous Pyrolysis/Oxidation In this method, the area to be cleaned is ringed with wells for injecting steam at temperatures above 100° C. Extraction wells in the central area are used to vacuum out vaporized contaminants. To ensure that thick layers of less permeable soils are heated sufficiently, electrode assemblies are sunk into the ground. The heated soil forces trapped liquids to vaporize and move to the steam zone for removal by vacuum extraction. These combined processes achieve a hot, dry, contaminant-free zone of earth surrounded by cool, damp, untreated areas. Steam injection and heating cycles are repeated as long as underground imaging, primarily Electrical Resistance Tomography, shows that cool (and therefore untreated) regions remain. More recently, Livermore scientists developed Hydrous Pyrolysis/Oxidation, a process that introduces oxygen into the underground to convert contaminants into benign products such as carbon dioxide, chloride ions, and water. To provide the oxygen, steam and air are injected in parallel pipes, building a heated, oxygenated zone in the subsurface. When injection is halted, the steam condenses and contaminated groundwater returns to the heated zone. The groundwater then mixes with the condensed steam and oxygen, which destroys dissolved contaminants. By destroying DNAPLs and dissolved contaminants in place, this process eliminates the need to handle, treat, and dispose of contamination at the surface. During the summer of 1997, both DUS and Hydrous Pyrolysis/Oxidation were used at a four-acre site in Visalia, California, owned by Southern California Edison. The utility company had used the site for 80 years to treat utility poles by dipping them into creosote or a pentachlorophenol compound. By the 1970s, these highly toxic substances had seeped into the subsurface to depths of approximately 100 feet. SteamTech Environmental Services of Bakersfield, California is currently cleaning up the Visalia site. During the first six weeks of operation, between June and August 1997, the team removed or destroyed in place approximately 300,000 pounds of contaminants, a rate of about 46,000 pounds per week. As of March 1, a total of 865,000 pounds of contaminants have been removed from the site. For nearly 20 years, Southern California Edison had been removing contaminants using pump-and-treat, most recently at a rate of just 10 pounds per week. At the IDC demonstration site at Launch Complex 34, Integrated Water Technologies of Santa Barbara, California will engineer cleanup using DUS and Hydrous Pyrolysis/Oxidation. To verify cleanup results, other Livermore-developed technologies will be used: underground imaging, noble-gas-tracer monitoring, supercomputer modeling, and accelerator mass spectrometry. In Situ Chemical Oxidation with Potassium Permanganate During a 1997 field test of this technology at the DOE Portsmouth Gaseous Diffusion Plant in Ohio, groundwater was pumped from an upgradient horizontal well and collected in a portable mix tank. Crystalline KMnO4 was continually added to the tank to maintain an oxidant concentration of 1 percent KMnO4. The oxidant solution was then injected into the downgradient horizontal well, while groundwater was continuously extracted from the upgradient well. The system operated in a recirculation mode for two to four weeks and successfully reduced trichloroethylene (TCE) concentrations in all sampling wells below 5 ppb (the drinking water standard). OST and the Portsmouth Office of Environmental Restoration jointly funded the demonstration. IT Corporation will be demonstrating In Situ Chemical Oxidation using Potassium Permanganate at the IDC demonstration site at Cape Canaveral. Operational details Florida State Universitys Institute for International Cooperative Environmental Research will provide day-to-day field project management through a cooperative agreement with DOE. The EPA Superfund Innovative Technology Evaluation (SITE) program will conduct quality assurance, quality control monitoring, and independent technology evaluations. More information |