journal article·2021-11-25Open access

Perspective Compounds for Immobilization of Spent Electrolyte from Pyrochemical Processing of Spent Nuclear Fuel

Svetlana A. Kulikova, Sergey S. Danilov, Anna V. Matveenko, Anna V. Frolova, Kseniya Y. Belova, Vladimir G. Petrov, Sergey E. Vinokurov, Boris F. Myasoedov

Applied Sciences· Volume 11· Issue 23

Abstract

Immobilization of spent electrolyte–radioactive waste (RW) generated during the pyrochemical processing of mixed nitride uranium–plutonium spent nuclear fuel is an acute task for further development of the closed nuclear fuel cycle with fast neutron reactors. The electrolyte is a mixture of chloride salts that cannot be immobilized directly in conventional cement or glass matrix. In this work, a low-temperature magnesium potassium phosphate (MPP) matrix and two types of high-temperature matrices (sodium aluminoironphosphate (NAFP) glass and ceramics based on bentonite clay) were synthesized. Two systems (Li0.4K0.28La0.08Cs0.016Sr0.016Ba0.016Cl and Li0.56K0.40Cs0.02Sr0.02Cl) were used as spent electrolyte imitators. The phase composition and structure of obtained materials were studied by XRD and SEM-EDS methods. The differential leaching rate of Cs from MPP compound and ceramic based on bentonite clay was about 10−5 g/(cm2·day), and the rate of Na from NAFP glass was about 10−6 g/(cm2·day). The rate of 239Pu from MPP compound (leaching at 25 °C) and NAFP glass (leaching at 90 °C) was about 10−6 and 10−7 g/(cm2·day), respectively. All the synthesized materials demonstrated high hydrolytic, mechanical compression strength (40–50 MPa) even after thermal (up to 450 °C) and irradiation (up to 109 Gy) tests. The characteristics of the studied matrices correspond to the current requirements to immobilized high-level RW, that allow us to suggest these materials for industrial processing of the spent electrolyte.
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Research context

OpenAlex topics: Nuclear materials and radiation effects · Chemical Synthesis and Characterization · Advanced ceramic materials synthesis

SciVX discovery tags are terminology-based. OpenAlex topics are source-provided classifications.

Affiliations

Vernadsky Institute of Geochemistry and Analytical Chemistry of Russian Academy of Sciences, 19 Kosygin St., 119991 Moscow, Russia

Department of Chemistry, Lomonosov Moscow State University, 1, bld. 3, Leninskie Gory, 119991 Moscow, Russia

Frumkin Institute of Physical Chemistry and Electrochemistry of Russian Academy of Sciences, 31, bld. 4, Leninsky Prospect, 119071 Moscow, Russia

Funding

Ministry of Science and Higher Education of Russia

References (33)

Show source-provided references
1. PH process as a technology for reprocessing mixed uranium–plutonium fuel from BREST-OD-300 reactor10.1134/S1066362216030085 ↗
2. Modelling aqueous corrosion of nuclear waste phosphate glass10.1016/j.jnucmat.2016.10.033 ↗
3. Development of iron phosphate ceramic waste form to immobilize radioactive waste solution10.1016/j.jnucmat.2014.04.033 ↗
4. A glass-encapsulated calcium phosphate wasteform for the immobilization of actinide-, fluoride-, and chloride-containing radioactive wastes from the pyrochemical reprocessing of plutonium metal10.1016/j.jnucmat.2006.11.011 ↗
5. Ceramic-composite waste forms from the electrometallurgical treatment of spent nuclear fuel10.1007/BF02914764 ↗
6. Morrison, M.C., Bateman, K.J., and Simpson, M.F. (2010). Scale Up of Ceramic Waste Forms for the EBR-II Spent Fuel Treatment Process, Office of Scientific and Technical Information Technical Reports.
7. The Ceramic Waste Form Process at Idaho National Laboratory10.13182/NT08-A3948 ↗
8. Study of sorption properties of lithium and potassium inoculated NaA zeolite sorbent
9. Investigation of the incorporation of spent alkali chloride melt in ceramic10.1007/s10512-007-0032-0 ↗
10. Park, H.S., Ahn, B.-G., Kim, H.-Y., Kim, I.-T., Cho, Y.-Z., and Lee, H. (2015). Solidification Method of Radioactive Waste Accompanying Chloride Recycling or Radioactive Iodide Removing and the Device Thereof. (No. 9,087,618 B2), U.S. Patent.
11. Investigation of physical and chemical properties for upgraded SAP (SiO2Al2O3P2O5) waste form to immobilize radioactive waste salt10.1016/j.jnucmat.2019.01.004 ↗
12. Ringwood, A.E. (1978). Safe Disposal of High Level Nuclear Reactor Wastes: A New Strategy, Australian National University Press. [1st ed.].
13. Immobilization of high-level nuclear reactor wastes in SYNROC: A current appraisal10.1016/0191-815X(81)90055-3 ↗
14. Orthophosphates of langbeinite structure for immobilization of alkali metal cations of salt wastes from pyrochemical processes10.1134/S1066362212060057 ↗
15. Murataite as a universal matrix for immobilization of actinides10.1134/S1075701506050011 ↗
16. Murataite: A matrix for immobilizing waste generated in radiochemical reprocessing of spent nuclear fuel10.1007/s10967-018-6236-z ↗
17. Matveenko, A.V., Varlakov, A.P., Zherebtsov, A.A., Germanov, A.V., Mikheev, I.V., Kalmykov, S.N., and Petrov, V.G. (2021). Natural Clay Minerals as a Starting Material for Matrices for the Immobilization of Radioactive Waste from Pyrochemical Processing of SNF. Sustainability, 13.10.3390/su131910780 ↗
18. Kulikova, S.A., Belova, K.Y., Tyupina, E.A., and Vinokurov, S.E. (2020). Conditioning of Spent Electrolyte Surrogate LiCl-KCl-CsCl Using Magnesium Potassium Phosphate Compound. Energies, 13.10.3390/en13081963 ↗
19. Kulikova, S.A., and Vinokurov, S.E. (2019). The Influence of Zeolite (Sokyrnytsya Deposit) on the Physical and Chemical Resistance of a Magnesium Potassium Phosphate Compound for the Immobilization of High-Level Waste. Molecules, 24.10.3390/molecules24193421 ↗
20. Kulikova, S.A., Danilov, S.S., Belova, K.Y., Rodionova, A.A., and Vinokurov, S.E. (2020). Optimization of the Solidification Method of High-Level Waste for Increasing the Thermal Stability of the Magnesium Potassium Phosphate Compound. Energies, 13.10.3390/en13153789 ↗
21. Candidate waste forms for immobilisation of waste chloride salt from pyroprocessing of spent nuclear fuel10.1016/j.jnucmat.2011.09.020 ↗
22. Phase composition, structure, and hydrolytic durability of glasses in the Na2O-Al2O3-(Fe2O3)-P2O5 system at replacement of Al2O3 by Fe2O310.1134/S1066362215040037 ↗
23. Phase Composition, Structure, and Hydrolytic Stability of Sodium-Aluminum(Iron) Phosphate Glass Containing Rare-Earth Oxides10.1007/s10717-018-0034-5 ↗
24. XPS study of neptunium and plutonium doped iron-bearing and iron-free sodium-aluminum-phosphate glasses10.1016/j.jnoncrysol.2017.12.010 ↗
25. Bentonite clays from 10th khutor deposite: Features of genesis, composition and adsorption properties
26. NP-019-15 (2015). Federal Norms and Rules in the Field of Atomic Energy Use “Collection, Processing, Storage and Conditioning of Liquid Radioactive Waste. Safety Requirements”.
27. GOST R 52126-2003 (2003). Radioactive Waste. Long Time Leach Testing of Solidified Radioactive Waste Forms.
28. Magnesium Potassium Phosphate Compound for Radioactive Waste Immobilization: Phase Composition, Structure, and Physicochemical and Hydrolytic Durability10.1134/S1066362218010125 ↗
29. Wagh, A.S. (2016). Chemically Bonded Phosphate Ceramics: Twenty-First Century Materials with Diverse Applications, Elsevier. [2nd ed.].10.1016/B978-0-08-100380-0.00002-6 ↗
30. Effects of Temperature on the Properties of α-High-level Radioactive Waste Immobilized, Hardened Magnesium Phosphate Cement
31. Characterization of and Structural Insight into Struvite-K, MgKPO4·6H2O, an Analogue of Struvite10.1021/acs.inorgchem.0c02802 ↗
32. Crystallization of iron phosphate glasses10.1007/BF01915267 ↗
33. Radiation and Thermal Ageing of Nuclear Waste Glass10.1016/j.mspro.2014.10.031 ↗