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ORNL-5388 - the Molten Salt Energy Technologies Web Site

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232"<br />

Fig. 3.0-1. Decay of 232U.<br />

<strong>ORNL</strong>-DWG 65-55DR3<br />

3-4<br />

The radioactivity associated with <strong>the</strong><br />

233U significantly impacts <strong>the</strong> associated fuel<br />

cycle. The fabrication, shipping, and handling<br />

of <strong>the</strong> fresh denatured fuel is expected to<br />

differ markedly from <strong>the</strong> o<strong>the</strong>r cycles , primari ly<br />

due to <strong>the</strong> fact that remote procedures will<br />

have to be employed throughout. To design <strong>the</strong><br />

necessary facilities will require a knowledge<br />

of <strong>the</strong> concentrations of 232U (and its daughter<br />

products) in <strong>the</strong> fuel as a function of time.<br />

To date, insufficient data are available on<br />

this subject, but on <strong>the</strong> basis of some pre-<br />

liminary investigations some estimates are<br />

given in Section 3.1 on <strong>the</strong> 232U concentrations<br />

that could be expected in <strong>the</strong> recycled fuel of<br />

LWRs , HTGRs , and FBRs operating on denatured<br />

233u.<br />

The radiological hazards associated wfth<br />

<strong>the</strong> use of denatured 233U fuel represent ano<strong>the</strong>r<br />

aspect of <strong>the</strong> cycle demanding attention.<br />

Again<br />

little information is available, but Section 3.2<br />

discusses <strong>the</strong> toxicity of <strong>the</strong> various isotopes<br />

present in <strong>the</strong> fuel and also in thorium ore,<br />

as well as <strong>the</strong> effects of exposure to <strong>the</strong> gamma<br />

rays emitted from <strong>the</strong> fresh fuel.<br />

In assessing <strong>the</strong> safeguard features of denatured 233U fuel, <strong>the</strong> isotopics of <strong>the</strong> cycle<br />

must be examined from several viewpoints.<br />

an inherent property of <strong>the</strong> 4denatured fuel cycle, <strong>the</strong> concentration of <strong>the</strong> isotopic denaturant,<br />

238U, is controllable.<br />

<strong>the</strong> denatured fuel cycle.<br />

venting <strong>the</strong> intrinsic isotopic barrier is increased.<br />

also increases <strong>the</strong> 239Pu concentration in <strong>the</strong> spent fuel so that an obvious trade-off of<br />

proliferation concerns exists between <strong>the</strong> front and back ends of <strong>the</strong> denatured fuel cycle.<br />

As pointed out in Section 3.3.1, <strong>the</strong> enrichment criteria for denatured 233U fuel are still<br />

being formulated.<br />

While <strong>the</strong> 232U contamination will be essentially<br />

The presente of both isotopes affects <strong>the</strong> proliferation potential of<br />

As <strong>the</strong> 238U concentration is increased, <strong>the</strong> difficulty of circum-<br />

However, increasing <strong>the</strong> 238U fraction<br />

The requirement for remote operations throughout <strong>the</strong> fuel cycle will in itself<br />

constitute a safeguard feature in that access to fissile material will be difficult at all<br />

stages of <strong>the</strong> cycle.<br />

of <strong>the</strong> fuel recycling steps and operations.<br />

But this requirement will also be a complicating factor in <strong>the</strong> design<br />

This subject is treated in more detail in<br />

Chapter 5, but Section 3.3.2 of this chapter points out that <strong>the</strong> remote operation requirement<br />

could dictate <strong>the</strong> selection of techniques, as, for example, for <strong>the</strong> fuel fabrication process.

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