ORNL-5388 - the Molten Salt Energy Technologies Web Site
ORNL-5388 - the Molten Salt Energy Technologies Web Site
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.