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epr-method (2003) - IAEA Publications - International Atomic Energy ...

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(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

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