Safety_Series_041_1975 - gnssn - International Atomic Energy ...
Safety_Series_041_1975 - gnssn - International Atomic Energy ...
Safety_Series_041_1975 - gnssn - International Atomic Energy ...
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122 APPENDIX IV<br />
maximum degree of radiological exposure is trivial at this stage,<br />
equivalent to a m ere 0.07% of the derived working lim it, it marks<br />
an important step in environmental measurements. A sim ilar series<br />
of calculations can be carried out for contamination of beach material,<br />
for which the only important nuclides are caesium-137 and -134.<br />
The maximum conceivable exposure by this route is even less than<br />
by consumption of fish and shrimps, at 0.02% of the derived working<br />
limit.<br />
(C) Exposure not measurable by any method<br />
Dilution of discharges from some sites is so large compared<br />
with the quantities of radioactivity involved that it can be predicted<br />
with confidence that no environmental material will be measurably<br />
contaminated. Although there may be little or no scientific need to<br />
carry out any environmental monitoring, a limited program me is<br />
generally undertaken, at least in the early period of operation of a<br />
site, prim arily to allay public fears. Ultimately, the program m es<br />
can be contracted, and if this situation of no measurable contamination<br />
persists after the station has reached operational equilibrium, it<br />
will be possible to dispense with monitoring altogether, leaving any<br />
occasional checks to the operator.<br />
A good example of this type of site is provided by the nuclear<br />
power station at Dungeness, Kent. Radiological exposure is not<br />
measurable by any method, direct or indirect, but monitoring is<br />
still designed on the critical path model which provides the only<br />
meaningful and scientific basis for expressing results. Detectable<br />
contamination is not necessary before potential critical routes can<br />
be identified. Two groups of the public would be important in this<br />
way — fishermen and bait-diggers — and the monitoring program me<br />
is designed to cover their habits. Plaice and whelks are sampled<br />
at approximately quarterly intervals subject to seasonal availability,<br />
and a simple total beta assay is sufficient to show that no artificial<br />
radioactivity is present. Occasionally, samples are analysed by<br />
gam m a-spectrom etry to confirm that no radionuclides are being<br />
m issed by the m ore simple beta analysis. Bait-digging for lugworm<br />
is a regular occupation on the beaches to the east of the<br />
power station and the potential critical effect would be external<br />
gamma radiation exposure resulting from adsorption of radioactivity<br />
on to the fine sand in this area. To cover this pathway gamma d oserate<br />
measurements are made at selected points from half a m ile to<br />
four m iles from the discharge point. Measurements have so far