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The 12th International Conference on Environmental ... - Events

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Abstracts Sessi<strong>on</strong> 25-26<br />

During the decommissi<strong>on</strong>ing planning period, the scenarios covering possible routes of materials release into the envir<strong>on</strong>ment<br />

and radioactive waste disposal, should be discussed and evaluated. Unc<strong>on</strong>diti<strong>on</strong>al and c<strong>on</strong>diti<strong>on</strong>al release to the envir<strong>on</strong>ment, l<strong>on</strong>gterm<br />

storage at the nuclear site, near surface or deep geological disposal and relevant material management techniques for achieving<br />

the final status should be taken into account in the analysed scenarios. At the level of the final decommissi<strong>on</strong>ing plan, it is<br />

desired to have the waste management scenario optimised for local specific facility c<strong>on</strong>diti<strong>on</strong>s taking into account a nati<strong>on</strong>al decommissi<strong>on</strong>ing<br />

background.<br />

<str<strong>on</strong>g>The</str<strong>on</strong>g> analytical methodology for decommissi<strong>on</strong>ing waste management scenarios evaluati<strong>on</strong>, presented in the paper, is based <strong>on</strong><br />

the materials and radioactivity flow modelling which starts from waste generati<strong>on</strong> activities like pre-dismantling dec<strong>on</strong>taminati<strong>on</strong>,<br />

selected methods of dismantling, waste treatment and c<strong>on</strong>diti<strong>on</strong>ing, up to materials release or c<strong>on</strong>diti<strong>on</strong>ed radioactive waste disposal.<br />

Necessary input data for scenarios, e.g. nuclear installati<strong>on</strong> inventory database (physical and radiological data), waste processing<br />

technologies parameters or material release and waste disposal limits, has to be c<strong>on</strong>sidered. <str<strong>on</strong>g>The</str<strong>on</strong>g> analytical methodology principles<br />

are implemented into the standardised decommissi<strong>on</strong>ing parameters calculati<strong>on</strong> code OMEGA, developed in the DECOM<br />

company. In the paper the examples of the methodology for the scenarios optimizati<strong>on</strong> are presented and discussed.<br />

3) CHARACTERISATION OF RACTOR GRAPHITE TO INFORM STRATEGIES FOR<br />

DISPOSAL OF REACTOR DECOMMISSIONING WASTE - 16389<br />

Andrew Hetheringt<strong>on</strong>, Phil Davies, NDA (UK)<br />

Graphite has been used extensively as a neutr<strong>on</strong> moderator and reflector in reactors in the UK since the 1950s. <str<strong>on</strong>g>The</str<strong>on</strong>g> UK nuclear<br />

decommissi<strong>on</strong>ing programme will result in some 90,000 t<strong>on</strong>nes of waste graphite being removed. A number of other countries also<br />

have graphite reactors scheduled for decommissi<strong>on</strong>ing, but UK has the largest graphite waste liability of any.<br />

<str<strong>on</strong>g>The</str<strong>on</strong>g> current UK baseline strategy, which is to package graphite waste and then c<strong>on</strong>sign it to geological disposal is c<strong>on</strong>sidered<br />

feasible, but it has not yet been shown to represent the optimum soluti<strong>on</strong> in terms of cost, safety and protecti<strong>on</strong> of the envir<strong>on</strong>ment.<br />

<str<strong>on</strong>g>The</str<strong>on</strong>g> NDA is currently engaged in investigating alternative soluti<strong>on</strong>s for reactor graphite. A review of worldwide developments has<br />

enabled a decisi<strong>on</strong> chart to be compiled for managing graphite waste showing, at a high level, the strategic opti<strong>on</strong>s and processes<br />

needed to take the graphite from a shut?down reactor, to the point where it is finally disposed of.<br />

Physical characterisati<strong>on</strong> is needed to provide a detailed radi<strong>on</strong>uclide inventory for the graphite to supplement theoretical calculati<strong>on</strong>s.<br />

Such an inventory, together with informati<strong>on</strong> about the physical and chemical characteristics of the material is a prerequisite<br />

for making decisi<strong>on</strong>s about its interim management as well as final dispositi<strong>on</strong>. <str<strong>on</strong>g>The</str<strong>on</strong>g>re is a need to progress understanding of<br />

uncertainties in the activity of the l<strong>on</strong>g?lived radi<strong>on</strong>uclides in graphite and of particular significance is precise characterisati<strong>on</strong> in<br />

relati<strong>on</strong> to Carb<strong>on</strong>?14 and Chlorine?36. Using informati<strong>on</strong> about the impurity levels in graphite at the various sites al<strong>on</strong>g with irradiati<strong>on</strong><br />

history, modelling tools will be used to assess the profile of key radi<strong>on</strong>uclides within the graphite with a view to optimising<br />

the disposal route.<br />

4) DEMONSTRATION OF UK ILW TREATMENT BY GEOMELT VITRIFICATION - 16105<br />

Keith Witwer, Kevin Finucane, Eric Dysland, AMEC, GeoMelt Divisi<strong>on</strong> (USA)<br />

Experiments for airborne dispersi<strong>on</strong> ratio of radi<strong>on</strong>uclides during plasma arc cutting were carried out in a c<strong>on</strong>taminati<strong>on</strong> c<strong>on</strong>trol<br />

enclosure, using stored radioactive metal wastes arising from the decommissi<strong>on</strong>ing activities of Japan Power Dem<strong>on</strong>strati<strong>on</strong><br />

Reactor, which was a boiling water type reactor. Neutr<strong>on</strong> induced-activated piping and surface c<strong>on</strong>taminated piping were segmented<br />

into pieces using air plasma arc cutting, using a current power was 100A. In additi<strong>on</strong>, similar experiments for c<strong>on</strong>taminated piping<br />

of the Advanced <str<strong>on</strong>g>The</str<strong>on</strong>g>rmal Reactor, Fugen were carried out.<br />

As a result, dispersi<strong>on</strong> ratios for activated piping were 0.2 to 0.7% of Co-60 and 0.4% of Ni-63 under the c<strong>on</strong>diti<strong>on</strong> with a covered<br />

cap <strong>on</strong> the head. And those for surface c<strong>on</strong>taminated piping were from 18 to 23%. In additi<strong>on</strong>, those for vertically segmented<br />

piping which simulated flat plate were from 34 to 43%. <str<strong>on</strong>g>The</str<strong>on</strong>g>re was no difference of dispersi<strong>on</strong> ratios between stainless steel and<br />

carb<strong>on</strong> steel base materials. All values obtained were smaller than the Handbook recommended value of 70% for c<strong>on</strong>taminated<br />

materials.<br />

Filtering collecti<strong>on</strong> efficiencies of the coarse dust filter were approximately 40% for activated piping and approximately 55 to<br />

80 % for surface c<strong>on</strong>taminated piping. However there was no effect for collecti<strong>on</strong> of aerosols smaller than 1μm.<br />

Size distributi<strong>on</strong> analysis indicated a greater c<strong>on</strong>centrati<strong>on</strong> of radi<strong>on</strong>uclides in particles smaller than 0.1μm when compared<br />

with larger particles. In additi<strong>on</strong>, there was a tendency that the Ni-63 was c<strong>on</strong>centrated to the particles smaller than 0.3μm compared<br />

with the Co-60.<br />

<str<strong>on</strong>g>The</str<strong>on</strong>g> results support data obtained in the previous studies using n<strong>on</strong>-radioactive materials.<br />

SESSION 26 - D&D UPDATE AND MANAGEMENT ISSUES<br />

1) RENEWING THE FOCUS ON DECOMMISSIONING: BRINGING A NEW<br />

MANAGEMENT PERSPECTIVE TO SELLAFIELD - 16243<br />

Russ A Mellor, Sellafield Ltd (UK)<br />

Sellafield site, <strong>on</strong> the West Coast of Cumbria, has recently emerged from a l<strong>on</strong>g competiti<strong>on</strong> process with new Parent Body<br />

Organisati<strong>on</strong> Nuclear Management Partners taking the helm of the UK nuclear industry flagship.<br />

Bringing together three major companies, URS Washingt<strong>on</strong> Divisi<strong>on</strong>, AREVA and AMEC, all leaders in their fields, NMP<br />

bring a new perspective to the way the Sellafield site is managed, using an approach that focuses <strong>on</strong> three Ps People, Partnership<br />

and Performance.<br />

Following a restructure of the company, <strong>on</strong>e of the key drivers for future lifetime plans is that of handling the legacy waste and<br />

a major reorganisati<strong>on</strong> of the site led to the evolvement of two distinct arms, Projects and Support. Sitting within Projects, and<br />

evolved from the Nuclear Decommissi<strong>on</strong>ing and Major Projects Group, the Clean-up directorate look after four key areas; C<strong>on</strong>taminated<br />

land, Legacy P<strong>on</strong>ds & Silos, Windscale and Decommissi<strong>on</strong>ing & Waste.<br />

<str<strong>on</strong>g>The</str<strong>on</strong>g> paper will look in more depth at<br />

87

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