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Appendix CRF - Part 3 - Northamptonshire County Council

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Radiological Assessment 0820-2<br />

Version 2<br />

2.2 Wastes<br />

The nuclear industry is generating significant quantities of radioactive waste from<br />

decommissioning, and these types of waste will continue to arise as decommissioning<br />

continues. Some of these wastes are potentially suitable for disposal at landfill sites.<br />

Wastes from other activities and industries, such as hospitals, universities and<br />

radiochemical manufacture, could also be considered for disposal at such sites.<br />

To ensure that the potential radiological consequences of the disposal of a<br />

representative range of LLW can be assessed, the radionuclides listed in Table 2.5<br />

have been considered in the radiological assessment. Radionuclides with half-lives<br />

less than one year have not been explicitly assessed. Where such radionuclides arise<br />

from ingrowth, they are included through the assumption that they will be in secular<br />

equilibrium with the parent radionuclide, and the dose coefficients used are adjusted<br />

accordingly.<br />

Radionuclide<br />

Half-life<br />

(years)<br />

3 H 12.3<br />

14 C 5,730<br />

36 Cl 3.01E+05<br />

55 Fe 2.73<br />

60 Co 5.27<br />

63 Ni 96.0<br />

90 Sr 28.8<br />

94 Nb 2.00E+04<br />

99 Tc 2.11E+05<br />

106 Ru 1.02<br />

108m Ag 418<br />

125 Sb 2.80<br />

126 Sn 2.07E+05<br />

129 I 1.57E+07<br />

133 Ba 10.7<br />

134 Cs 2.10<br />

137 Cs 30.0<br />

147 Pm 2.60<br />

152 Eu 13.3<br />

154 Eu 8.80<br />

155 Eu 4.96<br />

210 Pb 22.3<br />

Daughters assumed to be in secular<br />

equilibrium<br />

90 Y<br />

106 Rh<br />

126 Sb<br />

137m Ba<br />

210 Bi, 210 Po<br />

Galson Sciences Limited 11 14 July 2009<br />

WS010001/ENRMF/CONSAPP<strong>CRF</strong> 561

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