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Occupational Intakes of Radionuclides Part 1 - ICRP

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1016<br />

1017<br />

1018<br />

1019<br />

1020<br />

1021<br />

1022<br />

1023<br />

1024<br />

1025<br />

1026<br />

1027<br />

1028<br />

1029<br />

1030<br />

1031<br />

1032<br />

1033<br />

1034<br />

1035<br />

1036<br />

1037<br />

1038<br />

1039<br />

1040<br />

1041<br />

1042<br />

1043<br />

1044<br />

1045<br />

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1047<br />

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1049<br />

1050<br />

DRAFT REPORT FOR CONSULTATION<br />

give a more realistic description <strong>of</strong> the human body than afforded in mathematical (or<br />

stylised) phantoms. Thus, the <strong>ICRP</strong> decided to use voxel models to define the<br />

reference phantoms to be used in the calculations <strong>of</strong> dose distribution in the body for<br />

both internal and external exposures. These models (or computational phantoms),<br />

described in Publication 110 (<strong>ICRP</strong>, 2009), represent the Reference Male and Female,<br />

and have organ masses in compliance with the reference anatomical values compiled<br />

in Publication 89 (<strong>ICRP</strong>, 2002). These phantoms are designed specifically for the<br />

calculation <strong>of</strong> the radiological protection quantities corresponding to the effective<br />

dose concept <strong>of</strong> the 2007 Recommendations.<br />

(27) Equivalent doses to organs and tissues, HT, are calculated separately for the<br />

Reference Male and Reference Female and then averaged in the calculation <strong>of</strong><br />

effective dose, E:<br />

Where :<br />

H<br />

H<br />

E <br />

M<br />

T<br />

F<br />

T<br />

<br />

<br />

<br />

T<br />

<br />

T<br />

<br />

T<br />

M H T H<br />

wT<br />

<br />

2<br />

w<br />

w<br />

R<br />

R<br />

D<br />

D<br />

T , R<br />

T , R<br />

F<br />

T<br />

<br />

<br />

<br />

(male)<br />

(female)<br />

(28) It is made clear in Publication 103 (<strong>ICRP</strong>, 2007) that effective dose is<br />

intended for use as a protection quantity on the basis <strong>of</strong> reference values and relates to<br />

reference persons rather than specific individuals. The main uses <strong>of</strong> effective dose are<br />

in prospective dose assessment for planning and optimisation in radiological<br />

protection, and retrospective demonstration <strong>of</strong> compliance for regulatory purposes.<br />

Sex-averaging in the calculation <strong>of</strong> equivalent and effective doses, implicit in the past<br />

use <strong>of</strong> hermaphrodite mathematical phantoms, is now explicit in the averaging <strong>of</strong><br />

equivalent doses to adult male and female phantoms. Sex- and age-averaging in the<br />

derivation <strong>of</strong> tissue weighting factors can be seen to obscure differences in estimates<br />

<strong>of</strong> absolute radiation detriment between men and women and between adults and<br />

children. However, practical protection would not be improved by calculating<br />

effective dose separately for males and females and to do so might give a misleading<br />

impression <strong>of</strong> the precision <strong>of</strong> these quantities.<br />

1.5 Biokinetic models implemented in this report<br />

(29) Biokinetic models for individual elements and their radioisotopes are used to<br />

calculate the total number <strong>of</strong> transformations occurring within specific tissues, organs<br />

or body regions (source regions) during a given period <strong>of</strong> time (usually 50 y for<br />

adults, or to age 70 y for children) by determining the time-integrated activity in each<br />

source region. Dosimetric models are used to calculate the deposition <strong>of</strong> energy in all<br />

important organs/tissues (targets) for transformations occurring in each source region,<br />

taking account <strong>of</strong> the energies and yields <strong>of</strong> all emissions (Eckerman, 1994).<br />

31

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