Solid Radioactive Waste Strategy Report.pdf - UK EPR
Solid Radioactive Waste Strategy Report.pdf - UK EPR
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.