************************************************************* SOILTECH ATP SYSTEMS, INC. (Anaerobic Thermal Processor) This vendor is participating in the EPA Superfund Innovative Technology Evaluation (SITE) Program. The following technology profile has been reproduced from the SITE Technology Profile document, 7th edition. The SITE profile has been supplemented by MVA Consulting Inc. using information obtained from the vendor or from other SITE publications, referenced at the end of this file. TECHNOLOGY DESCRIPTION: The SoilTech ATP Systems, Inc. (SoilTech), anaerobic thermal processor (ATP) uses a rotary kiln unit to desorb, collect, and recondense contaminants from feed material (see figure below). The ATP can also be used in conjunc-tion with a dehalogenation process to chemically destroy halogenated hydrocarbons at elevated tempera- tures. The proprietary kiln contains four separate inter-nal thermal zones: preheat, retort, combustion, and cooling. In the preheat zone, water and volatile organic compounds (VOC) are vaporiz-ed. The hot solids and heavy hydrocarbons then pass through a proprietary sand seal to the retort zone. The sand seal allows solids to pass and inhibits gas and contaminant movement from one zone to the other. Concurrently, hot treated soil from the combus- tion zone enters the retort zone through a second sand seal. This hot treated soil provides the thermal energy necessary to desorb the heavy organic contaminants. The vaporized contaminants are removed under slight vacuum to the gas handling system. After cyclones remove dust from the gases, the gases are cooled, and con- densed oil and water are separated into their various fractions. The coked soil passes through a third sand seal from the retort zone to the combustion zone. Some of the hot treated soil is recycled to the retort zone through the second sand seal as previously described. The remainder of the soil enters the cooling zone. As the hot combusted soil enters the cooling zone, it is cooled in the annular space between the outside of the preheat zone and the kiln shell. Here, the heat from the combusted soils is transferred indirectly to the soils in the preheat zone. The cooled, treated soil exiting the cooling zone is quenched with water and conveyed to a storage pile. Flue gases from the combustion zone pass through the cooling zone to an emission control system. The system consists of a cyclone and baghouse to remove particulates, a wet scrubber to remove acid gases, and a carbon adsorption bed to remove trace organic compounds. When the ATP system dechlorinates contami-nants, an oil mixture containing alkaline dehalogenation reagents is sprayed on the con- taminated soil as it enters the preheat zone. The reagents dehalogenate or chemically break down chlorinated compounds, including polychlori-nated biphenyls (PCB), in the ATP system. WASTE APPLICABILITY: The ATP system was originally developed to recover oil from tar sands and shales. The system is now also used to dechlorinate PCBs and chlorinated pesticides in soils and sludges; to separate oils and water from refinery wastes and spills; and, in general, to remove hazardous VOCs and semivolatile organic compounds (SVOC) from soils and sludges. The ATP technology has also been selected to remediate contaminated soil at two Superfund sites contaminated with polynuclear aromatic hydrocarbons, pesticides, dioxins, and furans. STATUS: The ATP system has been demonstrated at two sites. At the first demonstration, in May 1991, a full-scale unit dechlorinated PCB- contaminated soil at the Wide Beach Development Superfund site in Brant, New York. At the second demon-stration, completed in June 1992, a full-scale unit remediated soils and sediments at the Waukegan Harbor Superfund site in Waukegan, Illinois. The technology has since treated PCB, polychlorinated aromatic hydrocarbons, and pesticide-contaminated soils at two additional Superfund sites. Two additional Superfund sites have since been remediated by the ATP system in Ohio and Kentucky. Test results from both SITE demonstrations indicate the following: > The SoilTech ATP system removed over 99 percent of the PCBs in the contaminated soil, resulting in PCB levels below 0.1 parts per million (ppm) at the Wide Beach Development site and averaging 2 ppm at the Waukegan Harbor Superfund site. > Dioxin and furan stack gas emissions were below the site-specific standards. > PCB stack gas emissions were equivalent to 99.9999 percent destruction and removal efficiency at the Waukegan Harbor site. > No volatile or semivolatile organic degradation products were detected in the treated soil. Also, no leachable metals, VOCs, or SVOCs were detected in the treated soil. > For the Wide Beach Development and Waukegan Harbor remediation projects, soil treatment costs were approximately $265 and $155 per ton, respectively. The regulatory support, mobilization, startup, and demobil- ization costs totalled about $1,400,000 for each site. FOR FURTHER INFORMATION EPA PROJECT MANAGER: Paul dePercin U.S. EPA Risk Reduction Engineering Laboratory 26 West Martin Luther King Drive Cincinnati, OH 45268 513-569-7797 Fax: 513-569-7620 TECHNOLOGY DEVELOPER CONTACTS: Alistair Montgomery Canonie Environmental Services Corp. 94 Inverness Terrace East, Suite 100 Englewood, CO 80112 303-790-1747 Fax: 303-799-0186 Joseph Hutton SoilTech ATP Systems, Inc. 800 Canonie Drive Porter, IN 46304 219-929-4343 Fax: 219-929-1776 __________________________________________________________ Sources of information in this profile: EPA Superfund Innovative Technology Evaluation Program Technology Profiles Seventh Edition, November 1994. EPA/540/R-94/526. *************************************************************