606
I. Amamoto et al. / Journal of Physics and Chemistry of Solids 66 (2005) 602–607
conversion facility and obtained results in this experiments
are summarised as below:
(
a) From the results of X-ray diffraction analysis, NaUF6,
Na UF , and Na UF were identified as some of the
3
6
2
8
uranium compounds adsorbed on NaF;
(
b) Volatilitization of UF6 from spent NaF could be
effectively prevented by the reduction of UF to UF
using the reducing agent, H in this experiment;
6
4
2
(c) The spent NaF, after treatment by H reduction, can
2
have the uranium removed by electrolysis. There was,
however, difficulty in attaining the hypothetical clear-
ance level caused by the disproportionate reaction, i.e.
Fig. 7. Result of uranium separation under medium concentration of
uranium (Run-5).
3
C
U
re-dissolution into the electrolyte.
(
d) With the use of mixed salt, i.e. NaF–NaCl system as the
electrolyte, uranium in the bath would likely form some
involatile compounds at the experimental temperature
(973 K) without the need of reduction treatment. A
sufficient recovery rate of uranium could be obtained
using the NaF–NaCl eutectic due to the absence of the
disproportionate reaction of uranium deposit at a
relatively lower temperature. However, the current
efficiency decreased markedly caused by the electro-
lysis of NaCl after long-time operation. From the
viewpoint of waste reduction, not all the electric energy
are lost as some are used for the decomposition of NaCl.
The economical realization of the molten salt technique
should be further pursued.
Fig. 8. Result of uranium separation under high concentration of uranium
(Run-6).
(
e) After the removal of uranium from NaF, we should look
into the possible recycling of NaF into a new resource as
well as its safe disposal. The stable solidification of
4.4. Separation and recovery experiment with low uranium
concentration range (RUN-6)
fluorides i.e. Na AlF , etc. or oxidation (NaF0Na O)
3
6
2
is being considered as one of the disposal methods.
Conducted in succession Run-5, Run-6 were carried
out using the uranium concentration attained in Run 5,
i.e. 0.02 wt% for confirmation of the recovery possibility
of uranium from the spent NaF below a hypothetical
clearance level (0.001 wt%: this value is equal to the
clearance level of 0.3 Bq/g of uranium concentration by
IAEA Recommendation [10]), Fig. 8 shows the result of
the change of uranium concentration to the quantity of
electricity. Below the clearance level, could be achieved
after 8 h of experimental operation. Its decontamination
factor (DF) reached above 1000 in view of 1.09 wt% as
its initial concentration. However, its current efficiency of
Acknowledgements
The authors wish to thank Mr T. Hoshino (School of
Engineering, University of Tokyo, Tokyo, Japan) for his
useful and helpful advice on the X-ray diffraction
analysis.
References
0.3% was very low. This electric loss is mainly due to
the electrolysis of NaCl.
[
[
1] I. Amamoto, T. Terai, et al., Behaviour of impurities in recycled
uranium at uranium conversion process, J.Nucl. Sci. tchnol., Suppl. 3
(
2002).
2] Y. Yaita, I. Amamoto, et al., Wet process using hydrochloric acid for
treatment of uranium waste, Proceedings of 2003 Fall Meeting of the
Atomic Energy Society of Japan, Shizuoka, Japan, Sep 24–26, 2003,
pp. 548 [in Japanese].
5
. Conclusion
Fundamental experiment on the molten salt technique for
[
3] M. Takai, I. Amamoto, et al., Study on fluorination processing method
for spent uranium absorbent, Proceedings of 2001 Fall Meeting of the
Atomic Energy Society of Japan, Sapporo, Japan, Sep 9–21, 2001, pp.
772 [in Japanese].
uranium separation and recovery from the spent NaF was
carried out to investigate its possibility for the decrease in
the amount of radioactive waste from the uranium