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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This publication is no longer valid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 77<br />

FIG . 6. DWL values f o r 60Co and 137 Cs in the ca se o f aqueous re le a se .<br />

in 4.1, so that one set can be read every quarter and one every year.<br />

It is also recommended to take measurements once a week with a<br />

portable scintillometer (scale in fJR/h).<br />

Samples of milk should be taken every month at four positions<br />

for determining I, and every quarter for other nuclides. Fallout<br />

samplers should be positioned at the air-sampling points;<br />

samples should be taken corresponding to periods of one month.<br />

Once a year a soil sample should be analysed (the top 5 cm) to<br />

measure the accumulated deposition. Weekly samples of river<br />

water should be taken about 100 m downstream from the discharge<br />

pipe.<br />

Every quarter sediment samples should also be taken in the<br />

water sampling zone. In.addition, measurements should be made<br />

with a scintillometer (graduated in /uR/h) once a month along the<br />

bank (several hundred m) and at the Club de Pesca.<br />

From time to time samples should also be taken from grown<br />

plants and pasture land up to a distance of 3 km from the power<br />

station, and fish samples should be taken at Zarate.<br />

The analytical results obtained (for the nuclides included in<br />

Figs 5 and 6) should be compared with the corresponding DWL<br />

values and the value f = measured value/DWL should be recorded.<br />

If this fraction is more than 10%, the sampling should be.repeated<br />

and if the result is confirmed, the release records should be<br />

examined. If f is close to unity, the waste processing procedures<br />

should be re-examined or the release limits reset.

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