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NEA press roomPress kit: Radioactive waste managementRadioactive waste, in a commonly cited definition is "...any material that contains a concentration of radionuclides greater than those deemed safe by national authorities, and for which no use is foreseen."* Most civilian radioactive waste is produced by nuclear power generation, with the remainder generated by the use of nuclear materials in medical, industrial and research processes. The volume of radioactive waste, in comparison with industrial toxic waste, is relatively small. The amount, type and physical form of radioactive waste varies considerably. Some forms of radioactive waste need only be stored for a relatively short period of time while their radioactivity naturally decays to safe levels. Others remain radioactive for hundreds or even thousands of years. This is usually expressed using the term 'half-life', the time it takes for half of any given number of atoms to decay. Low-level waste (LLW) can normally be handled without particular shielding, while intermediate-level waste (ILW) might require shielding and may contain significant amounts of long-lived radionuclides. Definitions of what constitutes LLW and ILW vary from country to country, but typically LLW is defined as such materials as rubber gloves, shoe covers, lab coats, cleaning cloths, paper towels, etc., that have been used in an area where radioactive material is present. ILW usually requires special precautions during handling to limit radiation exposures. Some forms of ILW need long-term isolation because of the long-lived radionuclides that they contain. Typical examples of ILW are filter ion-exchange resins, filter sludges, precipitates, evaporater concentrates, incinerator ash and fuel cladding. LLW and ILW may be further subdivided into catagories according to the half-lives of the radionuclides they contain, with "short-lived" waste decaying in less than 30 years and "long-lived" taking more than 30 years to decay.
High-level radioactive waste (HLW) refers to the highly radioactive waste requiring shielding and permanent isolation from man's environment. Typically this is the spent nuclear fuel produced by nuclear power plants. Most of these materials also need long-term cooling. Because of these characteristics special disposal practices are needed. Although the relative amount of HLW is small with respect to the total volume of radioactive waste produced in nuclear power programmes, it contains 99% of the radioactivity. While the half-lives required for the radioactivity of HLW to decay completely may be up to a million years, it typically takes about 10 000 years for the radioactivity of such waste to decay to the level which would have been generated by the original ore from which the nuclear fuel was produced, should this ore never have been mined. The IAEA estimates that the generation of electricity from a typical 1000 MW(e) nuclear power station produces approximately 300 m3 of low and intermediate-level waste per year and some 30 tonnes of high-level, solid, packed waste per year. Radioactive waste must be safely stored pending shipment, processing or disposal. "Short-term" storage is provided at many facilities before the waste is shipped off-site for treatment or disposal. In other cases, radioactive waste may be placed in "long-term" storage to allow the level of radioactivity in the waste to decay. If it is intended to retrieve the waste at a later date it is considered stored, rather than in final disposal. Because of the low volume (compared with other industrial processes) of waste produced and the special processing and disposal methods required, it is often more economic to transport radioactive waste to central processing, storage or disposal facilities. All such transport must be carried out in accordance with the relevant national and international model regulations (the ADR for road transport, the ADN for inland waterways, the RID for rail transport, the IMO dangerous goods code for sea transport and the ICAO technical instructions for air transport). The transboundary movements of radioactive waste in Europe are also subject to European Union regulations. In the case of some LLW from nuclear reactors, medical applications and research, the half-lives of the radioactive substances in the waste are short enough that effective disposal is achievable by deposition in supervised near-surface vaults, whilst decay takes place. The current preferred option for eventual disposal of HLW is emplacement in repositories deep underground in well-chosen geological media. In general, the geological disposal concept involves treating the waste in order to achieve a suitable physical and chemical form, packaging it inside long-lived engineered barriers emplaced deep underground, and sealing these facilities with appropriate materials. In these underground surroundings, as opposed to the surface environment, conditions remain stable over the long periods needed to allow the radioactivity to decay to a sufficiently low level. In operation since 1999 is the US Department of Energy Waste Isolation Pilot Plant (WIPP), in New Mexico, which permanently disposes of transuranic radioactive waste left from the research and production of nuclear weapons. Spent nuclear fuel requires both isolation from the human environment and long-term cooling. In July 2002, the US Senate approved the Yucca Mountain site in Nevada as a long-term geological repository for spent nuclear fuel and HLW. The US Department of Energy must now develop a plan for transporting HLW to the site and apply to the US Nuclear Regulatory Commission for a license to construct and operate the Yucca Mountain repository. It is expected that this application will be submitted during 2004. If approved, construction of the repository could begin in 2007-2008, with the first fuel shipments being made by 2010. Construction of an underground laboratory for an HLW deep geologicalal disposal site in Eurajoki, Finland began in 2004. The Finnish parliament approved the scheme in 2002. The process of choosing a site for disposal of spent fuel in Sweden is in progress and two municipalities are currently participating in site investigations. Once the site investigations are complete a site wil be proposed in 2007 by the company set up to deal with Swedish radioactive waste. A final decision on where the deep repository is to be built will be taken by the government around 2010. The Swedish repository should be ready to accept fuel shipments towards 2015. NEA Radioactive waste management programme Related NEA reports and publications Stakeholder Involvement in Decommissioning Nuclear Facilities Fostering a Durable Relationship between a Waste Management Facility and its Host Community NEA News: Advanced fuel cycles and radioactive waste management Post-closure Safety Case for Geological Repositories The Handling of Timescales in Assessing Post-closure Safety The Regulator's Evolving Role and Image in Radioactive Waste Management An International Peer Review of the Yucca Mountain Project TSPA-SR Reversibility and Retrievability in Geologic Disposal of Radioactive Waste The Role of Underground Laboratories in Nuclear Waste Disposal Programmes Confidence in the Long-term Safety of Geological Repositories: Its Development and Communication Low-Level Radioactive Waste Repositories: An Analysis of Costs Progress Towards Geological Disposal of Radioactive Waste: Where Do We Stand? The Environmental and Ethical Basis of Geological Disposal of Long-lived Radioactive Waste Related links Recent NEA radioactive waste press releases The International Atomic Energy Agency Division of Nuclear Fuel Cycle & Waste Technology (NEFW) Yucca Mountain Project Posiva Oy Radwaste.org Transport
*International Atomic Energy Agency definition. Last updated: 19 November 2007 |
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