epr-method (2003) - IAEA Publications - International Atomic Energy ...
epr-method (2003) - IAEA Publications - International Atomic Energy ...
epr-method (2003) - IAEA Publications - International Atomic Energy ...
You also want an ePaper? Increase the reach of your titles
YUMPU automatically turns print PDFs into web optimized ePapers that Google loves.
(1) precautionary 9 urgent protective action to prevent severe deterministic health effects by<br />
keeping doses below those for which intervention would be expected to be undertaken<br />
under any circumstances 10,11 ;<br />
(2) urgent protective action to prevent stochastic health effects by averting doses, in<br />
accordance with international standards 12 ;<br />
(3) agricultural countermeasures, countermeasures for ingestion and longer term protective<br />
measures, in accordance with international standards 12 ; or<br />
(4) protection for the workers responding (undertaking an intervention), in accordance with<br />
international standards 13 .<br />
A minimal threat assessment could be accomplished by identifying:<br />
(1) the threat category of facilities within the State, based on Table III and Appendix 4;<br />
(2) any national territory that is within the emergency zones or food restriction planning<br />
radius (see Appendix 5) of the threat category I and II facilities within or outside the<br />
State<br />
(3) the threat category of the jurisdictions within the State, based on Table IV; and<br />
(4) the operators of dangerous mobile sources (threat category IV in Table I) that can result<br />
in emergencies anywhere in the State.<br />
This threat assessment for facilities can be based on the results of generic accident studies [12,<br />
13] as summarized in Tables III and IV. This is generally sufficient for the emergency<br />
planning process. If a detailed analysis is to be performed, it should consider a range of<br />
potential emergencies and not be limited to “design basis” accidents.<br />
The threat assessment should also identify significant non-radiological threats (e.g. UF 6 or<br />
other hazardous chemical releases) to the people on and off site associated with the facility.<br />
A minimum level of threat (threat category IV in Table I) should be assumed to exist for all<br />
jurisdictions. Therefore States should assess their vulnerability to emergencies that can occur<br />
anywhere. This should include:<br />
(1) what types of radioactive material shipments have passed through the State, and the<br />
main routes and focal points (e.g. distribution centres). The system used to identify such<br />
shipments and the current level of training provided to carriers and first responders<br />
should also be characterized [16];<br />
(2) uses of dangerous mobile sources (e.g. for medical or industrial uses). This should<br />
include the system to ensure their control and proper disposal; and<br />
(3) the locations at which there is a significant probability of encountering a dangerous<br />
source that has been lost, abandoned, stolen or illicitly transported. This should include<br />
large scrap metal processing facilities and national border crossings.<br />
9 Initiated on the basis of conditions at the facility before environmental monitoring is carried out.<br />
10 Schedule IV of Ref. [3], r<strong>epr</strong>oduced in Appendix 2.<br />
11 Including events with a very low estimated probability of occurrence.<br />
12 Schedule V of Ref. [3], r<strong>epr</strong>oduced in Appendix 1.<br />
13 Appendix V, paras V.27–V.32 of Ref. [3], summarized in Appendix 3.<br />
18