************************************************************* SOIL WASHING This profile provides the following general information about thermal desorption: 1. Description 2. Applicability 3. Limitations 4. Availability and vendor list 5. Performance data and field applications 6. Sources of information for this profile 1. DESCRIPTION Soil washing is a water-based process for scrubbing soils ex situ to remove contaminants. The process removes contaminants from soils in one of two ways:  By dissolving or suspending them in the wash solution (which is later treated by conventional wastewater treatment methods).  By concentrating them into a smaller volume of soil through particle size separation, gravity separation, and attrition scrubbing (similar to those techniques used in sand and gravel operations). Soil washing systems incorporating most of the removal techniques offer the greatest promise for application to soils contaminated with a wide variety of heavy metal, radionuclides, and organic contaminants. Commercialization of the process, however, is not yet extensive. The concept of reducing soil contamination through the use of particle size separation is based on the finding that most organic and inorganic contaminants tend to bind, either chemically or physically, to clay, silt, and organic soil particles. The silt and clay, in turn, are attached to sand and gravel particles by physical processes, primarily compaction and adhesion. Washing processes that separate the fine (small) clay and silt particles from the coarser sand and gravel soil particles effectively separate and concentrate the contaminants into a smaller volume of soil that can be further treated or disposed of. Gravity separation is effective for removing high or low specific gravity particles such as heavy metal-containing compounds (lead, radium oxide, etc.). Attrition scrubbing removes adherent contaminant films from coarser particles. The clean, larger fraction can be returned to the site for continued use. 2. APPLICABILITY The target contaminant groups for soil washing are SVOCs, fuels, and inorganics. The technology can be used on selected VOCs and pesticides. The technology offers the potential for recovery of metals and can clean a wide range of organic and inorganic contaminants from coarse- grained soils. 3. LIMITATIONS Factors that may limit the applicability and effectiveness of the process include: Fine soil particles (e.g., silt, clays) may require the addition of a polymer to remove them from the washing fluid. Complex waste mixtures (e.g., metals with organics) make formulating washing fluid difficult. High humic content in soil may require pretreatment. The aqueous stream will require treatment 4. AVAILABILITY AND VENDOR LIST Soil washing is commercially available from a number of vendors. A full vendor list is provided below: Alternative Remedial Technologies, Inc. (813) 264-3506 B&W Nuclear Environmental Services, Inc. (804) 948-4610 Benchem (412) 361-1426 Bergmann USA (615) 452-5500 Biogenesis Bio-Recovery Systems, Inc. (505) 523-0405 Biotrol, Inc. (612) 942-8032 Canonie Environmental Services Corp. (303) 790-1747 Divesco, Inc. (601) 932-1934 Earth Decontaminators, Inc. (714) 262-2290 Geochem Division of Terra Vac (303) 988-8902 Lockheed Corporation (702) 897-3626 Nukem Development (713) 520-9494 OHM Corporation (510) 256-6100 On-Site Technologies, Inc. (408) 371-4810 RREL Scientific Ecology Group, Inc. (412) 247-6255 Turboscope Velco Environmental Service (713) 799-5289 Warren Spring Laboratory (44-438) 74-122 (UK) West Pac Environmental, Inc. (206) 762-1190 Westinghouse Remediation Services, Inc. (404) 299-4736 5. PERFORMANCE DATA At the present time, soil washing is used extensively in Europe but has had limited use in the United States. During 1986-1989, the technology was one of the selected source control remedies at eight Superfund sites. Soil washing is most commonly used in combination with the following technologies: bioremediation, incineration, and solidification/stabilization. Depending on the process used, the washing agent and soil fines are residuals that require further treatment. When contaminated fines have been separated, coarse- grain soil can usually be returned clean to the site. The time to complete cleanup of the "standard" 18,200-metric-ton (20,000-ton) site using soil washing would be less than 3 months. 6. Source: Marks, Peter J., Walter J. Wujcik and Amy F. Loncar, October 1994. REMEDIATION TECHNOLOGIES SCREENING MATRIX AND REFERENCE GUIDE, SECOND EDITION. DOD Environmental Technology Transfer Committee. NTIS No. PB95-104782. Reproduced for the Bloomington, Indiana PCB Superfund Sites Bulletin Board with the permission of USAEC, SFIM-AEC-ETD, APG, MD. Supplmented by MVA Consulting, Inc. *************************************************************