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THORIUM AS AN ENERGY SOURCE - Opportunities for Norway ...

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6. THE BACK END OF THE <strong>THORIUM</strong> FUEL CYCLE<br />

The Back End of the Thorium Fuel Cycle<br />

The back end of the thorium fuel cycle consists of fuel reprocessing and waste storage. It differs<br />

from the back end of a uranium cycle in some important aspects:<br />

• Virtually no plutonium or other transuranic elements are produced.<br />

• The waste products are free from the long-lived alpha-emitters.<br />

• Due to the stability of thorium dioxide, more aggressive chemicals must be used in the process,<br />

thus increasing the corrosion problems in the reprocessing plant.<br />

6.1 Thorium Cycle in Reactors<br />

Breeding of U-233 in thermal reactors is difficult and requires excellent neutron economy and online<br />

fuelling-reprocessing. Breeding of U-233 in fast reactors is possible, but the doubling time of<br />

the fissile inventory is much higher (about 250 years) than in the case of Pu-239 breeding.<br />

The reactor must be started with U-235 or Pu-239 (topping fuel), or with an accelerator-driven<br />

neutron generator. After a number of years, sufficient U-233 is <strong>for</strong>med to obtain equilibrium<br />

without further addition of topping fuel.<br />

At present, the best thermal reactors <strong>for</strong> the thorium cycle are the Molten Salt Reactor (MSR),<br />

the Heavy Water Reactor (HWR, or C<strong>AN</strong>DU) and the High Temperature Reactor (HTR). Thorium<br />

could also be used in Light Water Reactors (LWRs). Thorium can be used without any topping in<br />

conventional fast reactors.<br />

6.1.1 Once-Through (Open) Thorium Cycle<br />

In the case of the once-through cycle (open cycle) in LWRs, there is always a need <strong>for</strong> topping fuel.<br />

Maximum benefit from the produced U-233 requires as high as possible burnup, and U-233 is the<br />

best topping fuel <strong>for</strong> minimum actinide production. The introduction of thorium reduces the<br />

average annual consumption of uranium only by a few percent [135]. The radiotoxicity due to the<br />

actinides in the spent fuel is significantly reduced compared with that of spent UO2 fuel. After 10<br />

000 to 30 000 years of storage, the remaining U-233 dominates the radiotoxicity. However, in this<br />

last period of geological storage the actinides <strong>for</strong>m only a minor risk, as fission products dominate<br />

the dose due to dispersion.<br />

Reactors with higher fertile-to-fissile conversion ratios can benefit more from thorium fuelling. An<br />

example of what can be achieved with the once-through cycle in a C<strong>AN</strong>DU heavy-water reactor is<br />

reported by the Energy Research Centre of the Netherlands (ECN) [136], [137]. In Figure 6.1 the<br />

curve labelled “A” represents the effect of using thorium with HEU topping. The thorium-cycle<br />

waste results in a relatively low waste toxicity immediately after the fission product period (up to<br />

about 600 years) because less plutonium and americium are <strong>for</strong>med. Later, the radiotoxicity<br />

becomes as high as that of unreprocessed LWR spent fuel because of Ra-226 from U-234.<br />

However, higher burnup could further reduce the radiotoxicity. In practice other topping fuels can<br />

be used (such as MEU), <strong>for</strong> economic reasons or to fulfil non-proliferation requirements, but this,<br />

un<strong>for</strong>tunately, leads to additional radiotoxicity contributions.<br />

Similar results are obtained in the HTR, since it has the same conversion ratio and uses similar<br />

annual quantities of thorium and natural uranium fuel as the LWR. In a fast reactor, the open<br />

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