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

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Abstracts Sessi<strong>on</strong> 12<br />

joint awareness that cooperati<strong>on</strong> <strong>on</strong> the scientific, technical, and social challenges related to geological disposal is needed, and the<br />

cooperati<strong>on</strong> will be beneficial for the timely and safe implementati<strong>on</strong> of the first geological disposal facilities. Such a dem<strong>on</strong>strati<strong>on</strong><br />

of a viable soluti<strong>on</strong> for the management of high-level radioactive waste will enhance stakeholder c<strong>on</strong>fidence in Europe. Several<br />

decades of research, development and dem<strong>on</strong>strati<strong>on</strong> (RD&D) have been carried out in the field of geological disposal. <str<strong>on</strong>g>Internati<strong>on</strong>al</str<strong>on</strong>g><br />

opportunities of cooperati<strong>on</strong> and establishing a technology platform were explored in the European Commissi<strong>on</strong> co-funded<br />

projects like Net.Excel and CARD. According to the CARD project, the majority of the funding for RD&D in waste management<br />

comes from the implementing organizati<strong>on</strong>s.<br />

G) WVP MELTER ANALYSIS AND MODELLING FOR LIFETIME EXTENSION - 16209<br />

Clare Booth, Sellafield Sites (UK); Mark D’Vaz, Sellafield Ltd (UK)<br />

<str<strong>on</strong>g>The</str<strong>on</strong>g> purpose of the Sellafield Waste Vitrificati<strong>on</strong> Plant (WVP) is to immobilise highly active liquors produced during reprocessing<br />

of magnox and oxide fuel operati<strong>on</strong>s by means of a Vitrificati<strong>on</strong> process b<strong>on</strong>ding the fissi<strong>on</strong> products as metal oxides into<br />

a borosilicate glass matrix. This provides the stability required for safe l<strong>on</strong>g term storage of waste fuel products.<br />

Over the last two years the WVP technical department has carried out a study in prol<strong>on</strong>ging the life of the melter vessels used<br />

within WVP. <str<strong>on</strong>g>The</str<strong>on</strong>g> melter vessel is a critical part of the vitrificati<strong>on</strong> process. <str<strong>on</strong>g>The</str<strong>on</strong>g> purpose of this vessel is a crucible in which to heat,<br />

mix and react glass and fissi<strong>on</strong> products (as a calcine) and pour the glass product into a stainless steel c<strong>on</strong>tainer for l<strong>on</strong>g term storage.<br />

Several research projects have been carried out in partnership with the Nati<strong>on</strong>al Nuclear Laboratory to further understand the<br />

failure mechanisms within the melter vessel. Research has been focused in two areas:<br />

• <str<strong>on</strong>g>The</str<strong>on</strong>g> metallographic destructive examinati<strong>on</strong> of two inactive melters used to simulate plant c<strong>on</strong>diti<strong>on</strong>s experienced within<br />

WVP active lines with respect to thermal recycling and corrosi<strong>on</strong> attack. From relating this work to plant process data such<br />

as thermal cycling temperatures and HAL chemical compositi<strong>on</strong>, a set of operati<strong>on</strong> parameters can be established with the<br />

intenti<strong>on</strong> of prol<strong>on</strong>ging the life of the melter vessels within WVP.<br />

• <str<strong>on</strong>g>The</str<strong>on</strong>g> development of modelling techniques. <str<strong>on</strong>g>The</str<strong>on</strong>g> models have been designed to simulate a variety of operating c<strong>on</strong>diti<strong>on</strong>s<br />

and aim to predict behaviour of the vessel and melt in a large variety of c<strong>on</strong>trol regimes, and glass characteristics for a<br />

large set of feed compositi<strong>on</strong>s. From this informati<strong>on</strong> we can formulate operating envelopes that extend the life of the<br />

melter vessel by anticipating required operating c<strong>on</strong>diti<strong>on</strong>s given different feedstocks and mitigating or postp<strong>on</strong>ing primary<br />

failure modes.<br />

H) FEBEX IN SITU TEST - SHOWING THE VALUE OF VERY LONG TERM (>10 YEARS) EXPERIMENTS - 16422<br />

Irina Gaus, NAGRA (Switzerland); Erik Thurner, SKB (Sweden); Marjut Vahanen, Posiva, (Finland);<br />

Pedro Luis Martín Martín, CIEMAT (Spain); Juan Carlos Mayor, ENRESA (Spain);<br />

Jose Luis García-Siñeriz, Aitemin, (Spain); Ant<strong>on</strong>io Gens, UPC (Spain)<br />

<str<strong>on</strong>g>The</str<strong>on</strong>g> FEBEX experiment at the Grimsel Test Site (GTS) c<strong>on</strong>sists of an in-situ full-scale engineered barrier system (EBS) test<br />

for the disposal of high level waste (HLW) performed under natural c<strong>on</strong>diti<strong>on</strong>s.<br />

With heating starting in 1997 and led by Enresa, the FEBEX experiment, is the l<strong>on</strong>gest running experiment of its scale and has<br />

been the research subject in three subsequent European projects. In 2008, a c<strong>on</strong>sortium of four partners (SKB, Ciemat, Posiva,<br />

Nagra) c<strong>on</strong>tinued running the experiment under the project name FEBEXe until at least 2012, when excavati<strong>on</strong> of the sec<strong>on</strong>d and<br />

last heater is planned.<br />

<str<strong>on</strong>g>The</str<strong>on</strong>g> experiment is based <strong>on</strong> the Spanish reference c<strong>on</strong>cept in crystalline rock in which the canisters are placed horiz<strong>on</strong>tally in<br />

drifts and surrounded by a clay barrier c<strong>on</strong>structed of highly compacted bent<strong>on</strong>ite blocks. A c<strong>on</strong>stant temperature of 100°C has been<br />

maintained, while the bent<strong>on</strong>ite buffer has been slowly hydrating in a natural way. A total of 632 sensors were installed in the clay<br />

barrier, the rock mass, the heaters and the service z<strong>on</strong>e to measure the following variables: temperature, humidity, total pressure,<br />

displacement, water pressure etc. Partial dismantling and sampling of the in-situ test was carried out during 2002.<br />

Although <strong>on</strong>e of the main goals of the experiment has been fulfilled (dem<strong>on</strong>strating the feasibility of handling and c<strong>on</strong>structing<br />

the EBS), with the length of the dataset increasing, the observed thermo-hydro-mechanical (THM) and thermo-hydro-geochemical<br />

(THG) behaviour has revealed several features of interest, such as the underestimati<strong>on</strong> of re-saturati<strong>on</strong> times and the degree of<br />

uncertainty in key parameters.<br />

I) PARTITIONING RATIOS AMONG SOLID-, LIQUID-, AND GAS-PHASES FOR C-14<br />

LABELED SODIUM ACETATE IN PADDY AND UPLAND SOILS - 16112<br />

Nobuyoshi Ishii, Nati<strong>on</strong>al Institute of Radiological Sciences (Japan)<br />

In Japan, transuranic (TRU) waste is grouped into four types. Group 2 type includes hulls and end pieces, which c<strong>on</strong>tain significant<br />

amounts of C-14. As C-14 is l<strong>on</strong>g-lived, soluble and has little sorpti<strong>on</strong> properties, it is the key nuclide in safety assessment<br />

for a geological repository of TRU waste.<br />

Recently, the possibility of leaching of organic carb<strong>on</strong> compounds from hull waste has been reported. However, there is little<br />

informati<strong>on</strong> for reliable migrati<strong>on</strong> data sets of such organic C-14. Thus, it is hard to deny any possible migrati<strong>on</strong> of organic C-14<br />

from a TRU repository site to the sphere of human habitati<strong>on</strong>.<br />

To assess human expose to C-14 through crops intake, it is necessary to understand the behavior of organic C-14 in agricultural<br />

fields. In this study, we determined solid-, liquid-, and gas-partiti<strong>on</strong>ing ratios of organic C-14 in paddy and upland soils by using<br />

batch cultures. Investigati<strong>on</strong> of factors affecting the partiti<strong>on</strong>ing ratios between paddy soils and upland soils was also carried out.<br />

Paddy soils (n = 63) and upland soils (n = 79) were collected from throughout Japan. Each of these agricultural soils was flooded<br />

with dei<strong>on</strong>ized water at a solid-liquid ratio of 1:10 in a bottle. <str<strong>on</strong>g>The</str<strong>on</strong>g> flooded samples supplemented with [1, 2-14C] sodium acetate<br />

were shake-incubated for 7 days. At the end of incubati<strong>on</strong>, radioactivites of C-14 in the soil suspensi<strong>on</strong> and the supernatant were<br />

counted by using liquid scintillati<strong>on</strong> counting. Values of the sample pH were measured at the end of incubati<strong>on</strong>.<br />

69

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