The 12th International Conference on Environmental ... - Events
The 12th International Conference on Environmental ... - Events
The 12th International Conference on Environmental ... - Events
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Sessi<strong>on</strong> 40-41 Abstracts<br />
Previous theoretical studies carried out recently have illustrated the potential magnitude of the problem, with reference to the<br />
fundamental nuclear data and typical isotopic compositi<strong>on</strong>s of wastes. Neutr<strong>on</strong> multiplicity counting can, in principle, differentiate<br />
between isotopes that undergo sp<strong>on</strong>taneous fissi<strong>on</strong>, however in practice the uncertainties in waste assay are such that this is rarely<br />
beneficial. More practical “compensati<strong>on</strong>” techniques use combinati<strong>on</strong>s of different assay techniques (for example passive and<br />
active neutr<strong>on</strong> counting) and knowledge of the actinide ratios in the waste stream fingerprint.<br />
In this paper we describe various waste assay applicati<strong>on</strong>s as case studies. For each example we describe the nature of the challenge<br />
and show how soluti<strong>on</strong>s have been developed for applicati<strong>on</strong>s where the presence of curium has caused problems. We<br />
describe the technical soluti<strong>on</strong>s, showing the limitati<strong>on</strong>s and assumpti<strong>on</strong>s of each. We also emphasise the role of robust Quality<br />
Assurance procedures, to ensure that the techniques are implemented reliably and with predictable outcomes. Finally, we describe<br />
the benefits that have been realised for the plant operati<strong>on</strong>s teams, with regard to improved measurement accuracy, avoidance of<br />
false over-estimati<strong>on</strong> of the Pu inventory and subsequent improvement in plant throughput.<br />
4) THEORETICAL MODELLING OF NUCLEAR WASTE FLOWS - 16377<br />
J.F. Adams, S.R. Biggs, M. Fairweather, D. Njobuenwu and J. Yao, University of Leeds (UK)<br />
A large amount of nuclear waste is stored in tailings p<strong>on</strong>ds as a solid-liquid slurry, and liquid flows c<strong>on</strong>taining suspensi<strong>on</strong>s of<br />
solid particles are encountered in the treatment and disposal of this waste. In processing this waste, it is important to understand<br />
the behaviour of particles within the flow in terms of their settling characteristics, their propensity to form solid beds, and the resuspensi<strong>on</strong><br />
characteristics of particles from a bed. A clearer understanding of such behaviour would allow the refinement of current<br />
approaches to waste management, potentially leading to reduced uncertainties in radiological impact assessments, smaller<br />
waste volumes and lower costs, accelerated clean-up, reduced worker doses, enhanced public c<strong>on</strong>fidence and diminished grounds<br />
for objecti<strong>on</strong> to waste disposal.<br />
Mathematical models are of significant value in nuclear waste processing since the extent of characterisati<strong>on</strong> of wastes is in<br />
general low. Additi<strong>on</strong>ally, waste processing involves a diverse range of flows, within vessels, p<strong>on</strong>ds and pipes. To investigate experimentally<br />
all waste form characteristics and potential flows of interest would be prohibitively expensive, whereas the use of mathematical<br />
models can help to focus experimental studies through the more efficient use of existing data, the identificati<strong>on</strong> of data<br />
requirements, and a reducti<strong>on</strong> in the need for process optimisati<strong>on</strong> in full-scale experimental trials. Validated models can also be<br />
used to predict waste transport behaviour to enable cost effective process design and c<strong>on</strong>tinued operati<strong>on</strong>, to provide input to<br />
process selecti<strong>on</strong>, and to allow the predicti<strong>on</strong> of operati<strong>on</strong>al boundaries that account for the different types and compositi<strong>on</strong>s of particulate<br />
wastes.<br />
SESSION 41 - TRANSPORTATION AND STORAGE OF HLW, FISSILE, TRU, AND SNF<br />
1) EXPERIENCE WITH DRY CASK STORAGE TECHNOLOGY IN GERMANY - 16416<br />
Heinz Geiser, Jens Schroeder, Dietrich Hoffmann, GNS mbH (Germany)<br />
In Germany spent fuel will exclusively be disposed of in deep geological formati<strong>on</strong>s. Until the availability of a final repository,<br />
spent fuel assemblies (SFA) are mainly stored in casks of the CASTOR® type which c<strong>on</strong>stitute dual-purpose casks for transport<br />
as well as for storage. For the storage of these casks, interim storage facilities (ISF) have been c<strong>on</strong>structed <strong>on</strong> the sites of each<br />
nuclear power plant (NPP) in Germany. In the meantime GNS has loaded more than 1000 casks at 25 different sites in Germany.<br />
This paper will discuss the experience gained during the first decade of using dry cask storage technology.<br />
2) CONTINGENCY OPTIONS FOR THE DRY STORAGE OF MAGNOX SPENT FUEL IN THE UK - 16330<br />
Jenny E. Morris, Gals<strong>on</strong> Sciences Limited (UK); Stephen Wickham, Phil Richards<strong>on</strong>, Gals<strong>on</strong> Sciences Ltd. (UK);<br />
Colin Rhodes, NDA (UK); Mike Newland, UKAEA (UK)<br />
<str<strong>on</strong>g>The</str<strong>on</strong>g> UK Nuclear Decommissi<strong>on</strong>ing Authority (NDA) is resp<strong>on</strong>sible for safe and secure management of spent nuclear fuel.<br />
Magnox fuel is held at some Magnox reactor sites and at Sellafield where it is reprocessed using a number of facilities. It is intended<br />
that all Magnox fuel will be reprocessed as described in the published Magnox Operating Programme (MOP). In the event, however,<br />
that a failure occurs within the reprocessing plant, the NDA has initiated a programme of activities to explore alternative c<strong>on</strong>tingency<br />
opti<strong>on</strong>s for the management of wetted Magnox spent fuel.<br />
Magnox fuel comprises metallic uranium bar clad in a magnesium alloy, both of which corrode if exposed to oxygen or water.<br />
C<strong>on</strong>sequently, c<strong>on</strong>tingency opti<strong>on</strong>s are required to c<strong>on</strong>sider how best to manage the issues associated with the reactivity of the metals.<br />
Questi<strong>on</strong>s such as whether Magnox spent fuel needs to be dried, how it might be c<strong>on</strong>diti<strong>on</strong>ed, how it might be packaged and<br />
held in temporary storage until a disposal facility becomes available, all require attenti<strong>on</strong>.<br />
During storage in the presence of water, the corrosi<strong>on</strong> of Magnox fuel produces hydrogen (H2) gas, which requires careful<br />
management. When uranium reacts with hydrogen in a reducing envir<strong>on</strong>ment, the formati<strong>on</strong> of uranium hydride (UH3) may occur,<br />
which under some circumstances can be pyrophoric, and might create hazards which may affect subsequent retrieval and/or repackaging<br />
(e.g. for disposal). Other factors that may affect the choice of a viable c<strong>on</strong>tingency opti<strong>on</strong> include criticality safety, envir<strong>on</strong>mental<br />
impacts, security and Safeguards and ec<strong>on</strong>omic c<strong>on</strong>siderati<strong>on</strong>s.<br />
3) WIPP: A PERSPECTIVE FROM TEN YEARS OF OPERATING SUCCESS - 16189<br />
Phillip C. Gregory, Washingt<strong>on</strong> TRU Soluti<strong>on</strong>s (USA)<br />
<str<strong>on</strong>g>The</str<strong>on</strong>g> Waste Isolati<strong>on</strong> Pilot Plant (WIPP) located 35 miles east of Carlsbad, New Mexico, USA is the first and, to the author’s<br />
knowledge, <strong>on</strong>ly facility if the world for the permanent disposal of defense related transuranic (TRU) waste. So<strong>on</strong> after plut<strong>on</strong>ium<br />
was first synthesized in 1940 by a team of scientists at the University of California’s Berkley Laboratory the need to find a permanent<br />
repository for plut<strong>on</strong>ium c<strong>on</strong>taminated waste was recognized due to the 24,100 year half-life of Plut<strong>on</strong>ium-239. In 1957 the<br />
Nati<strong>on</strong>al Academy of Sciences published a report recommending deep geological burial in bedded salt as a possible soluti<strong>on</strong>. However,<br />
more than 50 years passed before the soluti<strong>on</strong> was realized when in 1999 WIPP received the first shipment of TRU waste from<br />
the Los Alamos Nati<strong>on</strong>al Laboratory. Ten years later, more than 6,000 shipments of TRU waste have been disposed of in rooms<br />
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