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Ingestion radiotoxicity (Sv/t spent fuel)<br />

10 8<br />

10 7<br />

10 6<br />

10 5<br />

10 4<br />

10 9 1500 a (Partial Pu 99.5% Am + Cm 90%)<br />

270 a<br />

Total<br />

Actinides<br />

Fission products<br />

Ref. 7.83 t U in equilibrium<br />

With P&T<br />

130 000 a<br />

10 3<br />

500 a (Full Pu 99.5% Am + Cm 99%)<br />

10 2<br />

1000 a (Full Pu 99.5% Am + Cm 95%)<br />

10 1 10 2 10 3 10 4 10 5 10 6<br />

Time (a)<br />

FIG. 1. Ingestion radiotoxicity of 1 t of spent nuclear fuel.<br />

99% for americium and curium). The cross-over point is 500 years. If the<br />

curium is left in the waste, this time is extended to 1000 years.<br />

(c) Full multiple recycling of plutonium as well as americium and curium,<br />

with less overall efficiency of P&T processes (99.5% for plutonium and<br />

95% for americium and curium). The cross-over point is 1000 years.<br />

(d) Partial multiple recycling: multiple recycling of the plutonium (99.5%<br />

P&T efficiency) and one single recycling of the americium and curium. In<br />

this case the americium and curium are transmuted in targets in a fast<br />

reactor (FR), with a 90% P&T overall efficiency foreseen. Thus the crossover<br />

point is around 1500 years. In this strategy we can also consider<br />

leaving the curium in the waste; in this event 3000 years is required.<br />

Based on these results, it can be concluded that P&T can help to reduce<br />

the time during which nuclear waste should be isolated from the biosphere<br />

from 130 000 years to between 500 and 1500 years. The fission products radiotoxicity<br />

curve gives the theoretical limit to the total radiotoxicity reduction in<br />

5

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