Chapter 6.4 Stabilisation and solidification of hazardous wastes Notes on this chapter The material in this chapter gives an overview of the essential issues in the stabilisation and solidification (S/S) of hazardous wastes. Some of the issues may also appear in other chapters. It is desirable however to consolidate the topic into a single chapter so that trainers will have a complete picture of the objectives and processes involved in the S/S of hazardous wastes. The slides briefly outline the main issues. For further details, trainers should consult the references given below. List of slides Title slide Slide 2 Immobilisation Slide 3 Aims of S/S of hazardous waste Slide 4 Waste pre-treatment Slide 5 Stabilisation Slide 6 Solidification Slide 7 Additives Slide 8 Key factors Slide 9 Waste assessment Slide 10 Performance tests Slide 11 Properties of S/S treated wastes Slide 12 Re-use applications for S/S waste Slide 13 Wastes typically treated by S/S Slide 14 Case study 1 UK Slide 15 Schematic of S/S plant part 1 stabilisation Slide 16 Schematic of S/S plant part 2 solidification Slide 17 Waste types treated by UK plant Slide 18 Treated waste specification Slide 19 Key considerations Slide 20 Summary Background notes 1 Stabilisation and solidification aim to immobilise the toxic constituents of hazardous wastes to prevent them leaching from the wastes once disposed. 2 Immobilisation is accomplished by reducing the solubility of the waste components, and by physically isolating the waste and decreasing its surface area. S/S therefore involves both physical and chemical processes. TRP Chapter 6.4 1 3 Different terms – such as immobilisation, fixation, solidification and stabilisation - are used to describe the various techniques whereby certain hazardous wastes are converted into a suitable form for long-term disposal. This text uses ‘immobilisation’ as an umbrella term to include both stabilisation and solidification. 3 S/S technologies are often used to treat the residues from other treatment processes such as fly ash from incineration or sludges from heavy metal precipitation. The technologies are most suitable for treating inorganic wastes. Organic constituents in the waste may make the application of S/S techniques unsafe and inappropriate. 4 S/S technologies are effective in treating a variety of difficult to manage inorganic wastes. They can be used for wastes containing mixtures of contaminants and can economically treat large waste volumes. However, certain waste components may interfere with the reactions and setting of the solidification binders used. 5 The chemistry of S/S wastes treatment is complex. Selection of a suitable solidification binder depends on correctly predicting complex interactions between waste components and binders to ensure acceptable and reliable results. Although there is no definitive guide to successfully selecting a binder, processing method and disposal regime, a wellstructured testing programme guided by an understanding of the mechanisms involved in S/S systems will reduce uncertainty. 6 In the USA, S/S has been identified as the Best Demonstrated Available Technology (BDAT) for treating a wide range of hazardous wastes. It is increasingly used for treating contaminated soil at sites being redeveloped. 7 While the principal aim of S/S is to produce an end product less environmentally threatening than the original waste, there may be an added benefit if the S/S waste can be put to practical use. This could provide economic and environmental advantages eg because of the avoided need for disposal. Nevertheless, concerns about the long-term performance of S/S products and the possible exposure of human or ecological receptors to contaminants restrict end-use options. In practice, relatively few S/S- treated wastes have been re-used to date. 8 S/S may improve the handling and physical characteristics of hazardous wastes. However S/S technologies for hazardous waste should primarily be regarded as prelandfill waste treatment processes. S/S is often the final waste treatment stage prior to disposal. 9 Apart from the limited opportunities to re-use S/S treated wastes, they should be disposed in a secure landfill site. They should not be co-disposed with other wastes such as MSW as the acid leachate produced by these may cause severe degradation of S/S wastes. TRP Chapter 6.4 2 Sources of further information Batstone, R; Smith, JE & Wilson, DC editors (1989) The safe disposal of hazardous wastes: The special needs and problems of developing countries World Bank, Washington, Technical paper No 93 in 3 volumes ISBN 0-8213-1144-1 (available as pdf files from www.worldbank.org/publications/) Conner, JR (1989) Chemical fixation and solidification of hazardous wastes, Van Nostrand Reinhold, New York ISBN 0-4422-0511-2 De Bruin, T (1990) Co-disposal and encapsulation Waste Management & Research Vol 8 No 2 Gilliam, TM & Wiles, Carlton C Editors (1992) Stabilization and Solidification of Hazardous, Radioactive and Mixed Wastes: 3rd volume, American Society for Testing & Materials STP 1123, Philadelphia ISBN 0-8031-1443-5 Guyer, Howard H (1998) Industrial processes and waste stream management Wiley ISBN 0-4712-9984-7 LaGrega, MD; Buckingham, PL; Evans, JC & ERM Group (1994) Hazardous Waste Management McGraw Hill, New York ISBN 0-07-019552-8 Lohwongwatana, B; Soponkanaporn, T & Sophonsridsuk, A Industrial hazardous waste treatment facilities in Thailand Waste Management & Research Vol 8 No 2 Means, JL, Smith LA & Nehring, KW (1994) The application of solidification / stabilisation to waste materials Lewis Publishers, USA ISBN 1-5667-0800-9 Mehu, J; Keck, G; & Navarro, A Editors (1999) Proceedings of Waste Stabilisation and Environment, 13-16 April 1999, Lyon, France (available from E.et.T@wanadoo.fr) Nash, JM; Cheung, B; Fung, CH; Lei PK, Mak, PW; Rootham, RC; Stokoe, MJ & Tong, R (1991) Control and treatment of hazardous (chemical) waste in Hong Kong Waste Management & Research Vol 9 No 3 Razzell, WE (1990) Chemical fixation, solidification of hazardous waste, Waste Management & Research, Vol 8 No 2 Technical guidelines from the Secretariat of the Basel Convention www.basel.int TRP Chapter 6.4 3