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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This publication is no longer valid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 />

APPENDIX IV<br />

EXAMPLES OF ENVIRONMENTAL MONITORING<br />

PROGRAMMES<br />

ARGENTINA<br />

Environmental monitoring in the neighbourhood of the<br />

Atucha Nuclear Power Station<br />

1. Introduction<br />

The purpose of the environmental monitoring programme<br />

described below is to check that the Basic <strong>Safety</strong> Standards and the<br />

ICRP recommendations are being properly observed as regards<br />

exposure of the public during normal operation of the power station.<br />

Monitoring is not an end in itself, but is merely a technique<br />

employed in radiological protection. An essential component of<br />

the monitoring programme is, therefore, that the results should be<br />

interpreted in the light of the ICRP recommendations. The latter<br />

recommendations include 'dose-equivalent limits' and radionuclide<br />

'uptake lim its', and these can be used in interpreting the monitoring<br />

results.<br />

Many of the measurements performed in a monitoring programme<br />

cannot be expressed directly in terms that are comparable with the<br />

recommended ICRP limits. To interpret these results one needs<br />

to use an 'exposure model', which establishes a quantitative relation<br />

between the measured quantities and the resulting dose-equivalents<br />

of radiation. The expression 'Derived Working Limits' (DWL)<br />

describes those values of the monitored quantities that correspond<br />

in the exposure model to the dose limits recommended by ICRP.<br />

In view of the 'super-safe' hypothesis applied in selecting the<br />

'exposure model1, observance of the DWL values gives the virtual<br />

certainty that the recommended ICRP dose limits are observed as<br />

well.<br />

It should be stressed, nevertheless, that environmental monitoring<br />

is not in itself sufficient to ensure adequate protection of the<br />

public. This type of monitoring should be accompanied by suitable<br />

'monitoring of release', in order to be able to estimate the resulting<br />

doses in cases where the environmental levels are difficult to<br />

measure or to distinguish from radioactive fall-out.<br />

71

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