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Regional Basic Professional Training Course in Korea

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❙ 1027 ❙<br />

20. Waste Management<br />

These <strong>in</strong>clude trash (e.g. protective cloth<strong>in</strong>g and plastics, paper, cardboard, wood,<br />

<strong>in</strong>sulation materials), metal scrap, worn‐out devices, and air filters. A specific group with<br />

regard to activity level and <strong>in</strong>ventory is the components removed from the reactor core,<br />

so called activated metal waste.<br />

The classification of NPP operational waste depends on the stage of management. Prior<br />

to treatment and condition<strong>in</strong>g, it is practicable to classify waste accord<strong>in</strong>g to their physical<br />

form, e.g. dry/wet waste, combustible/<strong>in</strong>combustible, compressible/<strong>in</strong>compressible and<br />

dispersible/ non‐dispersible.<br />

With regard to treatment, condition<strong>in</strong>g and storage, waste is usually classified as:<br />

Low level waste, which can be handled without particular radiation protection<br />

arrangements;<br />

Intermediate level waste, which requires effective radiation protection<br />

arrangements radiation shields or remote handl<strong>in</strong>g); and<br />

High‐level waste, which requires cool<strong>in</strong>g and very effective radiation protection<br />

arrangements.<br />

The approximate borderl<strong>in</strong>e between low and <strong>in</strong>termediate level waste is the<br />

concentration of strong gamma emitters of 1 MBq/kg. In high‐level waste, the<br />

concentration of strong gamma emitters is more than 10 GBq/kg. NPP operational waste<br />

is generally of low or <strong>in</strong>termediate level. Only <strong>in</strong> activated metal waste the activity<br />

concentration may exceed the limit for high‐level waste, but <strong>in</strong> a conditioned form even<br />

this can normally be classified as <strong>in</strong>termediate level waste.<br />

With regard to disposal, the classification of waste is generally based on its activity<br />

concentration and on the lifetime of the activity, expressed <strong>in</strong> half‐lives of the dom<strong>in</strong>at<strong>in</strong>g<br />

nuclides. LILW is normally divided <strong>in</strong>to two classes, short‐lived waste and long‐lived

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