Overview
ABSTRACT
Among nuclear waste the most hazardous type is the high-level and long-lived (HLLL) . It emits ionizing radiation for several thousands and even million of years and thus significant amounts of heat. The spent fuel is mainly composed of plutonium, actinides (americium, curium and neptunium) called "minor" due to their presence in low quantities and finally fission products. In order to treat minor actinides, they must be separated from the spent fuel and a transmutation reaction must be implemented. This reaction allows for their fragmentation, reducing their radio toxicity (they then emit beta radiation which are far less toxic than the previous alpha radiations) and also reducing the time they require to recover stability. This article presents spent fuel components as well as the methods and processes for separation and transmutation.
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Read the articleAUTHORS
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Sylvie PILLON: Senior expert at the French Atomic Energy and Alternative Energies Commission (CEA) - Head of innovative fuel design and irradiation laboratory
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Dominique WARIN: Head of the Radiochemistry and Processes Department at the French Atomic Energy and Alternative Energies Commission (CEA)
INTRODUCTION
The long-lived radionuclides contained in spent fuel assemblies are responsible for the persistence of radioactivity over thousands, even millions of years. The main elements contributing to the radiotoxicity of spent fuel are plutonium (1% of spent fuel), the "minor" actinides americium, curium and neptunium (0.07% of spent fuel) and fission products (4% of spent fuel).
Plutonium, considered a resource rather than a waste in France, is already the subject of an industrial recycling strategy implemented in PWRs, using MOX fuel. For the other long-lived radionuclides present in waste, research is being carried out at international level into solutions for separating them from spent fuel and transmuting them into short-lived or inert elements in nuclear reactors, as an alternative to geological storage in a glass matrix.
Research carried out in France until 2006 under the December 30, 1991 law on the management of high-level, long-lived radioactive waste, and continued today under the June 28, 2006 law on the sustainable management of radioactive materials and waste, shows that not all types of nuclear reactor offer the same transmutation potential, and that not all radionuclides can be transmuted efficiently. Thus, the best transmutation performances are obtained in fast neutron spectrum reactors, and transmutation is only reasonably applicable to minor actinides (mainly americium, neptunium and curium). In the case of fission products, their contribution to the radiotoxicity inventory decreases after several hundred years, which, combined with the technical difficulties involved in their implementation, greatly reduces the value of transmutation.
Transmutation of minor actinides is necessarily accompanied by their prior separation, individually or in groups, from spent fuel. Separation and transmutation are therefore the two inseparable stages on which research has been intensively pursued since 1991, and which this article aims to review.
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Fuels and targets for the transmutation of HAVL radioactive waste
Bibliography
Website
EUROTRANS European FP6 project http://hal.in2p3.fr/in2p3-00195198
European CONFIRM project under FP5 http://cordis.europa.eu
Documentation sources
High-level and long-lived radioactive waste/Research and results. Law of December 30, 1991. Focus 1.
Final report, December 2005 (CEA collective work).
Report CEA/DEN/DDIN/2005-568.
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