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Safety_Series_041_1975 - gnssn - International Atomic Energy ...

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This publication is no longer valid<br />

Please see http://www.ns-iaea.org/standards/<br />

72 APPENDIX IV<br />

2. D e riv e d W ork in g L im its . M eth od ology<br />

The Derived Working Limits for routine environmental monitoring<br />

at Atucha were determined by the methods indicated below,<br />

which will be described in greater detail in another document.<br />

2.1. DWL for the contamination of foodstuffs by one<br />

radionuclide<br />

In the case of a standard man, not exposed to external radiation,<br />

and consuming only one type of contaminated foodstuff, the DWL=IL/g,<br />

where IL is the uptake limit and g the annual amount of the foodstuff<br />

consumed. Obviously, the dose resulting from consumption of a<br />

foodstuff with a concentration C over a period of one year will give<br />

a dose commitment of (C/DWL) XDL, where Dl is the corresponding<br />

dose limit.<br />

2.2. DWL for the case of irradiation due to contamination of<br />

various foodstuffs and to external radiation, in both<br />

cases by one radionuclide<br />

Let the concentration of the radionuclide in each foodstuff be<br />

termed Q and the external radiation dose to the organ R. The<br />

dose limits are not exceeded if<br />

If the concentrations and external dose are equal to their respective<br />

DWL values, the expression is equal to one. The equation can<br />

be solved for a given DWL if the relations between the concentrations<br />

(and the external dose) are known. This is the case when all<br />

exposure pathways have a common precursor compartment in the<br />

'exposure model1. If the concentration in this precursor is Ca,<br />

Fai is the transfer parameter to the foodstuff i, and FaR is the<br />

transfer parameter to the external dose, then we have

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