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Solid Radioactive Waste Strategy Report.pdf - UK EPR

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<strong>EPR</strong> <strong>UK</strong><br />

N° NESH-G/2008/en/0123<br />

REV. A PAGE 104 / 257<br />

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Minimisation of operator dose uptake (limitation of required personnel, limitation<br />

of work at contact, minimisation of operation durations, use of mobile radiological<br />

shielding protection);<br />

Use as far as necessary of services like static and/or dynamic containment to<br />

avoid any contamination risk;<br />

Minimisation of dismantling cost;<br />

Limitation of investment cost; use as far as possible existing equipment present<br />

on site from normal operations;<br />

Limitation of technical risk by using existing and proven technologies;<br />

Management of the waste and minimisation of secondary and induced waste<br />

generated.<br />

8.1.5 Raw waste characteristics<br />

8.1.5.1 ILW<br />

8.1.5.1.1 Contaminated ILW<br />

Based on preliminary calculations, the contaminated ILW resulting from the immediate<br />

dismantling of the whole plant (considering classification at the dismantling date) will be limited<br />

to the waste resulting from decontamination of the primary circuit which results in the production<br />

of contaminated ion exchange resins.<br />

This waste amounts to about 30 to 40 m 3 of resins. The β/γ activity on the resins will range<br />

between 1E5 Bq/g and 4.5E5 Bq/g.<br />

Based on 60 years of electricity production for an <strong>EPR</strong> followed by the immediate dismantling of<br />

a single reactor, the ILW resins will be produced in year 61.<br />

After interim storage up to the 100 years after the beginning of reactor operation (40 years after<br />

reactor shutdown), the activity of these wastes will be significantly reduced and a proportion of<br />

may be reclassified as LLW.<br />

8.1.5.1.2 Activated ILW<br />

Based on preliminary calculations, the ILW resulting from the immediate dismantling of the<br />

whole plant (considering classification at the dismantling date) will be limited, depending of the<br />

decay time considered, to:<br />

· The neutron shield;<br />

· Most of the reactor pressure vessel internals (upper and lower internals, excepted the far<br />

upper sections of these components);<br />

· The core shells of the reactor vessel (part of the reactor vessel located near the core<br />

cavity);<br />

· Part of the concrete of the reactor compartment.<br />

These wastes amount to approximately 450 te of raw solid metallic waste and 180 te of<br />

concrete.

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