\1 / United States Environmental Protection Agency Risk Reduction Engineering Laboratory Cincinnati OH 45268 Research and Development EPA/600/S2-89/017 Jan. 1990 &EPA Project Summary Assessment of International Technologies for Superfund Applications - Technology Identification and Selection Thomas Nunno, Jennifer Hyman, Peter Spawn, John Healy, Clay Spears, Margaret Browne, and Edward J. Opatken Technologies being developed or applied for remediation of hazardous waste sites in countries other than the United States were Identified. An assessment was made of the applica- bility of each of the technologies to Superfund sites. Of the 83 technol- ogies screened, 12 were selected as being sufficiently promising that follow up was warranted. Of these, two are thermal treatment tech- niques, eight are physical/chemical or electrolytically-driven technologies and two are biological treatment systems. This Project Summary was devel- oped by EPA's Risk Reduction Engi- neering Laboratory, Cincinnati, OH, to announce key findings of the research project that Is fully documented in a separate report of the same title (see Project Report ordering Information at back). Introduction The objective of the assessment was to identify technologies that are being evaluated or are in use in countries in Europe, Asia, and North America, exclud- ing the United States, which could be utilized for hazardous waste site remedi- ation within the United States. The approach focused on the location, acqui- sition, and interpretation of existing data, and studies and related documentation for remedial technologies. Data were ob- tained through a comprehensive literature survey and telephone interviews with personnel associated with agencies, industries, vendors, research groups, and others involved in the development and marketing of technologies. Emphasis was placed on technologies that have been developed or applied in Europe, Japan and Canada. Findings As a result of the investigation, 83 technologies have been identified that may be applicable to Superfund site remediation activity. Factors considered in assessing the applicability of each technology were: • Function—purpose of the technology and its applicability; • Description—flow schematic, discus- sion of theoretical operating principles and design features; • Performance— demonstrated performance of the process for clean- up of uncontrolled hazardous waste sites; • Limitations—physical or chemical characteristics that limit the applica- bility of the technology; • Economics—the capital, operating, and maintenance costs; and • Status—current development status, availability, and research plans. These characteristics were used to select technologies for follow up. Each technology was described in a fact sheet that summarized available information. An example fact sheet is presented in Table 1. The screening of the technologies resulted in selecting 12 that were recom- mended for further study, along with 10 additional that may warrant further study. ------- Table 1. International Technology Fact Sheet Process: Onsite Soil Cleaning Using the "Oil Crep System" Type of Treatment: Physical/Chemical Country: Federal Republic of Germany Institution/Contact: Dipl.-lng. Peterson AEG Shiffbau BREMER Vulcan TBSG Industrie Anlage Function: Removal of oil (containing CB/Halogen) from soil using a mobile cleaning system that washes out oil, forming a separable emulsion allowing recycling of the water phase. Description: System is a basic washing procedure but uses the product CREP (Cleaning, Recycling, Environmental Protection), which forms a separable emulsion with water and, therefore, allows the recycling of the water layer. CREP itself is not toxic, contains no aromatics, is not a dispersion agent, leaves the basic structure of the pollutant oil, and has the "Environment Friendly" seal of the German environmental agency. The system operates on the basic principle of adsorption and cold water washing with high pressure to create a separable emulsion. This allows skimming of the oil layer and after clarification, return of clean wastewater to the wastewater system without special treatment. Heavy metals are removed as hydroxides. Process steps include centrifuge, oil removal, pH adjustment, detoxification through oxidation or reduction, heavy metal precipitation, water clarification, and neutralization through ion exchange. Performance: Pilot plant was successfully operated, and in 1985, a 20-ft mobile container unit was built. This unit has been in use with success since then. Bremen University has conducted independent tests on one site and found that sand contaminated with 14,000 ppm oil was reduced to 190 ppm, which is well below the 300 ppm level for reuse of sand in the FRG. Efficiency was 98.7%. Limitations: Soil must be conditioned to reduce particle size to 60 mm. Economics: Exact data not available, but considered a proven system. Status: System is now in use in Europe. Efficiency is high. Extensive test data is available (GCMS runs, etc.). Recommendations: Further evaluation and comparison with U.S. techniques. Reference: Brown, Margaret. Correspondence of October 19, 1987. Technologies not considered further include: 1. those that are applicable to only a small percentage of Superfund wastes, 2. those similar to conventional tech- niques in use in the United States, and 3. experimental technologies that are not well developed. Among the 12 most promising tech- nologies, 2 are thermal treatment techniques, 8 are physical/chemical or electroiytically-driven technologies, and 2 are biological treatment systems. Twelve additional technologies are already being studied under the NATO/CCMS Pilot Study program. Hazardous Waste Management Hazardous waste management in countries throughout Europe, Asia, and North America (excluding the United States) is an evolving practice that involves continually developing policies and regulatory approaches to the problems posed by hazardous waste production and disposal. Most foreign countries have developed a wide variety of technologies for dealing with hazard- ous waste problems, in addition to spon- soring significant research and develop- ment efforts in the field. The European approach to hazardous waste management is one of decentral- ization, whereby individual countries or provinces most often assume the re- sponsibility for the collection and dis- posal of hazardous wastes produced in their locality. While implementation of hazardous waste management systems is often a local responsibility, most coun- tries do have a National Environmental Protection Agency that creates the envi- ronmental policy for the country and develops the regulatory framework for meeting the goals of that policy. Decentralization seems to allow for greater dissemination of information, a well as the development of organize collection and transport systems d« signed to meet the unique needs of eac locality. However, problems do arise 01 of the lack of uniformity of environment. regulation and policy enforcemer throughout the country, in addition to th lack of local facilities available for prope waste disposal. Some European cour tries including the Netherlands, Sweder Austria, Denmark, and Norway hav constructed centralized incineration faci ities and landfills that accept waste from all over the country, in response t the shortage of local facilities. A common practice of countrie lacking proper disposal facilities of thei own is the exporting of hazardou wastes to neighboring countries, primar ily in the Federal Republic of Germany Other uncommon waste disposal prac tices seen in Europe and Japan an codisposal of hazardous wastes witl municipal wastes and disposal at sea. The high costs of disposal oftei incurred by local municipalities am extrepreneurs, along with the lack o proper disposal facilities, tends to resul in numerous incidence of illegal dump ing throughout Europe. This is especially true in the more populated anc politically-reactive developing countries where enforcement poses unique diffi cullies. This, and the fact tha environmental regulations are only < recent phenomenon, give rise to the contemporary issue of what to do witr old, abandoned, contaminated waste sites, known or suspected to exist ir large quantities throughout these countries. Most foreign countries are onl^ beginning to catalogue their abandonee sites with no country surveyed yet hav- ing a regulatory mechanism for the remediation of such sites as sophis- ticated as the United States' Compre- hensive Environmental Response Com- pensation and Liabilities Act (CERCLA). The Canadian Council of Resource and Environmental Ministers (CCREM), how- ever, is currently working on establishing a "national contingency fund" to respond to the problem of abandoned sites in Canada. Most central govern- ments are responding to the problem of abandoned hazardous waste sites by directing nationwide studies and provid- ing subsidies to local communities for remediation efforts. However, it is likely in the near future that in most European communities, the restoration of aban- ------- doned hazardous waste sites will con- inue to be a local affair. The full report was submitted in partial fulfillment of Contract No. 68-03-3243 by Alliance Technology Corporation under sponsorship of the U.S. Environmental Protection Agency. ------- Thomas Nunno. Jennifer Hyman, Peter Spawn, John Healy, Clay Spears, and Margaret Browne are with Alliance Technologies Corporation, Bedford, MA 01730.; the EPA author Edward J. Opatken (also the EPA Project Officer, see be- low) is with the Risk Reduction Engineering Laboratory,Cincinnati, OH 45268 The complete report, entitled "Assessment of International Technologies for Super- fund Applications—Technology Identification and Selection," (Order No. PB 89- 205 959/AS; Cost: $28.95, subject to change) will be available only from: National Technical Information Service 5285 Port Royal Road Springfield, VA 22161 Telephone: 703-487-4650 The EPA Project Officer can be contacted at: Risk Reduction Engineering Laboratory U.S. Environmental Protection Agency Cincinnati, OH 45268 United States Environmental Protection Agency Center for Environmental Research Information Cincinnati OH 45268 Official Business Penalty for Private Use $300 EPA/600/S2-89/017 UNOFFICIAL MAIL; 025 = ~ 603044.; I 000085833 PS IttunUnUULM. ------- |