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Appendix CRF - Part 3 - Northamptonshire County Council

Appendix CRF - Part 3 - Northamptonshire County Council

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Radiological Assessment 0820-2<br />

Version 2<br />

Radionuclide<br />

Pathways associated<br />

with water contaminated<br />

by leachate<br />

Drinking<br />

water<br />

Specific dose<br />

(μSv y -1 per MBq)<br />

Fish Crops<br />

Pathways associated with soil<br />

contaminated by irrigation with<br />

contaminated water<br />

Livestock and<br />

associated<br />

products<br />

Am-241 1.76E-08 1.45E-09 3.88E-07 2.08E-12 1.67E-13<br />

Cm-243 1.32E-08 1.09E-09 2.91E-07 3.59E-12 1.25E-13<br />

Cm-244 1.07E-08 8.76E-10 2.34E-07 2.90E-12 1.01E-13<br />

Table 5.5 Specific doses via exposure pathways associated with spillage of<br />

leachate into a surface water resource. Results do not include the<br />

effects of ingrowth of long-lived daughter radionuclides.<br />

Sensitivity studies to show the effect of different assumptions about the exposed<br />

individual are presented in <strong>Appendix</strong> C, where specific doses for an adult, an infant (1<br />

year old) and child (10 year old) are given for the different potential exposure<br />

pathways following a leachate spill to a surface water body. A comparison of the<br />

calculated specific doses for different age groups shows that for pathways associated<br />

with the consumption of fish and crops the greater consumption rates for adults<br />

outweigh the higher dose coefficients for infants and children. For the pathways<br />

associated with livestock and drinking water, the age group with the highest specific<br />

dose depends on the radionuclide, but in all cases the ratio of specific doses between<br />

age groups is less than a factor of 10. Only in the case of exposure through the<br />

consumption of contaminated soil are specific doses to infants and children higher<br />

than those to adults by a factor of more than 10, because of the greater consumption<br />

rates assumed for these age groups.<br />

5.4.3 Aerosol pathway<br />

Specific doses calculated for workers and members of the public via the aerosol<br />

pathway are presented in Table 5.6. These calculations are based on the assumptions<br />

described in Section 4.1.8 and in <strong>Appendix</strong> A, and are presented as specific doses per<br />

hour of exposure to aerosols.<br />

Radionuclide<br />

Specific dose<br />

(μSv y -1 per MBq per<br />

hour)<br />

Workers Public<br />

Radionuclide<br />

Galson Sciences Limited 51 14 July 2009<br />

Soil<br />

Specific dose<br />

(μSv y -1 per MBq per<br />

hour)<br />

Workers Public<br />

H-3 2.51E-12 2.09E-12 Ra-226 1.88E-07 1.57E-07<br />

C-14 5.6E-11 4.66E-11 Ac-227 5.49E-06 4.57E-06<br />

Cl-36 7.04E-11 5.87E-11 Th-229 2.47E-06 2.06E-06<br />

Fe-55 7.43E-12 6.19E-12 Th-230 9.65E-07 8.04E-07<br />

Co-60 2.99E-10 2.49E-10 Th-232 1.64E-06 1.36E-06<br />

WS010001/ENRMF/CONSAPP<strong>CRF</strong> 601

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