Actinide mixed oxide conversion by advanced thermal denitration route
Graphical abstract
Introduction
This study is part of the recycling of recoverable materials (U, Pu actinides) from spent nuclear fuels. Conversion is a key step at the interface between the separation and purification processes and fabrication steps of uranium-plutonium oxide fuels called MOx (Mixed Oxides). Briefly, it consists in converting quantitatively a solution containing the products obtained from purification processes. Generation IV (GEN IV) reactors should allow a multi-recycling of Pu as well as the transmutation of minor actinides, but conversion routes must suit additional needs compared to the current process:
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Continuous process with higher throughput will be necessary to increase conversion rates as the amount of matter to convert;
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Conversion must integrate fluxes with the minimum of possible additional operations, avoiding redox adjustments or concentration steps of feeding actinide solutions still for a better efficiency;
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Conversion process must be able to synthesize oxide powders with different Pu contents for both LWR and SFR MOx fuel fabrication;
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MOx synthesis has to be favored to prevent the proliferation risk associated to Pu multi-recycling;
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MOx or mixture of oxides synthesized must be adapted for fuel pellet shaping directly, without any grinding and sieving steps to reduce dust generation;
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Management of effluents and gas release should be simple and efficient processes.
Meeting these requirements explains the large number of studies conducted so far to synthesize mixed oxides containing both uranium and plutonium.
In the literature, actinide co-conversion routes can be categorized into three major families: precipitation routes, sol-gel routes and denitration routes. Although precipitation processes offer a complementary partitioning factor and allow the synthesis of a single phase U1-xPuxO2±δ powder after a single calcination, these processes require a redox adjustment (U(IV)/Pu(III) oxalic co-conversion), bring filterability difficulties and produce effluents hardly manageable (carbonate conversion route) [[1], [2], [3], [4], [5], [6], [7]]. Sol-gel routes come in two forms: internal or external gelations [[8], [9], [10]]. They have the advantage of not forming dust with the synthesis of oxide microspheres, but whatever internal or external gelation routes, they involve the managing of a large amount of hazardous effluents, including ammonium nitrate solutions, and they cannot achieve the targeted cadences [7,10]. Denitration routes are more direct conversion pathways. Among them, microwave-assisted denitration of actinide salts was developed and industrialized by Japan Nuclear Fuel Industry Limited [11,12]. The dielectric properties of uranyl nitrates and plutonium nitrates, initially hydrated, make it possible to carry out microwave thermal co-denitration in four steps: heating, concentration, denitration, followed by a last complementary step for maintaining the denitrated product heating. The recovered product is a U3O8/PuO2 mixture followed by calcination under a reducing atmosphere to form UO2/PuO2 mixture [13,14]. In Nitrox process [15], a concentrated solution has to be prepared first and cold crystallization follows. The powder obtained is then dehydrated and denitrated, with the objective of staying at a temperature below the melting temperature corresponding to the instantaneous decomposition of the salt [16]. MDD (modified direct denitration) process was developed at Oak Ridge National Laboratory [17,18]. This process involves the addition of ammonium nitrate to the initial solution of uranyl nitrate. This leads to the formation of double nitrate salts of uranyl and ammonium, which decompose without going through a melting state. A last step of calcination under reducing atmosphere is required to form a UO2/PuO2 mixture [7,19,20]. Advantages of all these thermal denitration processes are the rapidity of the reaction and the absence of filtration step. However, two major drawbacks can be noticed on these routes: a NOx treatment has to be added to avoid release and/or corrosion problems, and the production of actinide oxide dusts either directly or due to the requirement of a milling step prior to fuel pelletization [7].
As a result, none of the conversion routes studied so far suits all the additional specifications exposed below and associated to GEN IV fuel cycle. For these reasons, it was necessary to develop a new way of conversion with simultaneous management of uranium and plutonium. A present proposed chemical route is inspired by NPG (nitrate polyacrylamide gel) synthesis method [[21], [22], [23], [24]]. It permits a mono [25] or poly cationic [21] oxide synthesis and comprises four distinct steps. An aqueous solution containing cations and additives is prepared and then gelified in a crosslinked polymer by adding an initiator. The gelation makes it possible to trap all the cations present in solution in a homogeneous manner. This gel is then dehydrated to synthetize a xerogel which is then calcined to form the final oxide [21,25]. So far, this chemical route had never been applied to actinide oxides. Such a synthesis method is flexible, coping with high versatility in terms of acidity, cation concentration, use of chelating agents and choice in starting monomer [[26], [27], [28], [29], [30], [31]]. Based on these results, this work explores the so called “Advanced thermal Denitration in presence of Organic Additives (ADOA) process” conversion route, to synthetize mixed actinide oxides. It will also describe all the developments and adjustments performed to suit the requirements linked to the synthesis of nuclear fuel precursors (e.g. sulphur and chloride free using safe reagents).
This paper presents the synthesis by advanced thermal denitration in presence of organic additives of UO2+δ, U0.55Pu0.45O2±δ and U0.9Am0.1O2-δ enabling to demonstrate the feasibility of such conversion route applied to single or mixed actinide solutions.
Section snippets
Sample preparation
The characteristics of the reagents used are given in Table 1.
The various steps that take place during gel formation are shown Fig. 1: the actinides (uranium or uranium associate with plutonium or americium) are mixed into a nitric solution in proportions matching the targeted stoichiometry expected in the final oxide. For UO2+δ and U0.55Pu0.45O2±δ syntheses, uranium nitrate (UO2(NO3)2) is dissolved in nitric acid and then, Pu as nitric solution is added to the uranium solution if required.
Results and discussion
As the whole actinide solution is embedded inside the gel, this synthesis route avoids any actinide leak in residual waters and withdraws any filtration issues during the process. Moreover, the actinide ratio of the solution is maintained inside the final oxide. To ensure having the targeted actinide ratio, UV-vis spectrometry was carried out on actinide solutions. First, the former Pu and Am solutions were analysed to confirm their concentrations. It was found for the Pu solution that 97% of
Conclusion
The main objective of this study was to explore the possibility to synthetize mono and mixed actinide oxides using the so-called “advanced thermal denitration in presence of organic additives” synthesis route, a derivate synthesis route from one commonly used in other fields to obtain poly-cationic oxides. Feasibility is demonstrated here by successful synthesis of three oxides: UO2.04, U0.55Pu0.45O2±δ and U0.9Am0.1O2-δ. The proposed synthesis route is robust and concerns the synthesis of both
Acknowledgments
The authors thank: Romain Vauchy and Alexis Jolie for U/Am XRD, Gauthier Jouan and Jean-Robert Sevilla for SEM images and Alexandre Quemet and Eric Esbelin for XRF and TIMS analysis. This work was part of the French National Research Agency (ANR) through the project ‘‘ASTUTE” (contract ANR-15-CE08-0011-01).
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