4Utpo3so UM-P-88/125
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4utpo3So UM-P-88/125 The Incorporation of Transuranic Elements in Titanatc Nuclear Waste Ceramics by Hj. Matzke1, B.W. Seatonberry2, I.L.F. Ray1, H. Thiele1, H. Trisoglio1, C.T. Walker1, and T.J. White3'4'5 1 Commission of the European Communities, Joint Research Centre, i Karlsruhe Establishment, ' \ 'I European Institute for Transuranium Elements, Postfach 2340, D-7500 Karlsruhe, Federal Republic of Germany. 2 Advanced Materials Program, Australian Nuclear Science and Technology Organization, Private Mail Bag No. 1, Menai, N.S.W., 2234, Australia. 3 National Advanced Materials Analytical Centre, School of Physics, The University of Melbourne, Parkville, Vic, 3052, Australia. Supported by the Australian Natio-al Energy Research, Development and Demonstration Programme. 4 Member, The American Ceramic Society 5 Author to whom correspondence whould oe addressed 2 The incorporation of actinide elements and their rare earth element analogues in titanatc nuclear waste forms are reviewed. New partitioning data are presented for three waste forms contining Purex waste simulant in combination with either NpC^, PuC>2 or An^Oo. The greater proportion of transuranics partition between perovskitc and ztrconoiite, while some americium may enter loveringite. Autoradiography revealed clusters of plutonium atoms which have been interpreted as unrcacted dioxide or scsquioxide. It is concluded that the solid state behavior of transaranic elements in titanate waste forms is poorly understood; certainly inadequate to tailor a ceramic for the incorporation of fast breeder reactor wastes. A number of experiments are proposed that will provide an adequate, data base for the formulation and fabrication of transuranic-bearing jj [i waste forms. ' ' 1 ~> I. Introduction The potential of titanate-based ceramics as media for the solidification and stabilization of high level nuclear waste has been extensively documented. These studies have in the main been concerned with the formulation and preparation of the waste forms, optimization of their physical and chemical properties, and microstructural characterization. Significantly, the majority of this work has been conducted on material containing simulated (non-radioactive) waste. Considering ceramic waste forms have, on occasion, been promoted as superior to vitreous waste forms for the disposal of transuranic (TRU) rich fast breeder reactor (FBR) wastes,1 surprisingly little effort has been made to verify this assumption. , For titanate waste forms, the available evidence suggests that all the 'actinide (ACT) elements can be incorporated amongst perovskite and the zirconolite polytypes. However, there has been no rigorous investigation designed specifically to establish the solid solution limits of ACT elements in these phases nor their partitioning coefficients. In those cases where samples containing transuranic nuclides have been fabricated, the physical changes accompanying self-irradiation, rather than crystallochemical properties, have been emphasized. This paucity of solid state chemical data is now limiting discussion of the merits of TRU immobilization in titanate assemblages. In this paper, we review the literature describing the incorporation of ACT elements in titanate phases and present the results of a microstructural investigation of three titanate waste forms containing neptunium, plutonium and americium. Using this evidence we summarize the crystallochemical properties of the ACT elements and suggest a number of experiments which should be undertaken to optimize the design of a dedicated TRU waste form. 4 II. Previous Investigations TRU elements are often regarded as comparable to rare earth (RE) elements of similar ionic radii and valence (Table I), and many workers have used these non-active analogues to evaluate the characteristics of ACT species.2-3'4 Although much useful data can be collected in this way, care is required when a mixture of REs is involved to ensure that each is simultaneously in the correct oxidation state to simulate the TRU element of interest. For example, Ce + and Nd + could adequately simulate Np and Am respectively. However, under the reducing conditions used to fabricate titanate waste forms, cerium (as well as neodymium) is trivalent, thereby obviating the desired mimicry of solid state behavior.5»<>.7 An alternate experiment in which the waste form is fabricated under oxidizing conditions to stabilize tetravalent cerium is equally misleading, as trivalent titanium would not be formed. Since this species plays a key role in maintaining charge balance in many altervalent substitutions8 the partitioning of the TRU simulants would be different to that expected under actual fabrication conditions, and the proportions of radwaste bearing phases would alter.^ Therefore, in polyphase assemblages, where the simulation of two or more TRU elements is required, it is often impossible to design an appropriately controlled experiment. This complicates the correlation of properties of RE analogues with TRU elements and can limit the usefulness of this approach. It is, however, often practical to carry out simulation experiments using (nearly) single phase material and one RE analogue. A summary of relevant studies is given in Table II. (1) RE ind ACT Incorporation in Single Phase Ceramics Zirconolite Polytypes. Several studies have been made of the partitioning of trivalent REs into zirconolite polytypes.^ These phases which protypically have the formula CaZr^Oy,11 can employ two cation acceptor sites to accommodate REs; 3 3 8 a larger CaOg cube (volume = 21.3 A ) and smaller Zr07 polyhedron (15 A ). Rosscll concluded that small REs partition onto both sites, whereas the larger, lighter REs (e.g. Nd ) enter the calcium-site only.12 However, at the time of this work the polytypic nature of zirconolite was not recognized. A more recent study by Fielding et al.13 has shown that when zirconolite-2M is doped beyond 5 wt% neodymium it is impossible to prepare this polytype as single phase. Rather, it coexists with zirconolite-3T and another polytype with as yet lmdctermined crystal structure. The 2M polytype has neodymium partitioned strongly into the calcium- site whilst the 3T form exhibited equal part;,ioning of neodymium over both cation acceptor sites. Small RE elements (e.g. Yb ) do not stabilize zirconolite-3T and reside almost exclusively in the zirconium-site. Thorium, the largest ACT will partition into either the calcium- or zirconium- sites of the zirconolite polytypes in accordance with charge balance 1 A 4 + considerations.14 If no small ions suitable to replace titanium are present, Th will isomorphically replace Zr in zirconolite-2M. In the presence of Mg , Fe or Al thorium enters the calcium-site with the concommitant stabilization of zirconolite-3T. At higher levels, these coupled substitutions cause the formation of zirconolite-30.1^ Tetravalent uranium14 and plutonium16 have been examined individually as dopant species and both are reported as entering the zirconium-site. No data exists for neptunium, although it would be reasonable to assume that iis behavior would parallel that of uranium and plutonium. Of the trivalent ACTs, curium is believed to partition between the calcium- and zirconium-sites.17 The properties of trivalent plutonium and americium have not been examined. Pyrochlore. Unlike the zirconolite polytypes for which a rudimentary data base exists for the prediction of TRU partitioning, the other titanate phases which are usually considered as suitable immobilization matrices, viz. perovskite and pyrochlore, have received little attention. A recent examination of uranium incorporation in a calcium-rich betafite (pyrochlore) suggested that although the stoichiometry of this phase can be approximated to CaUTi20^, the Ca/U ratio is probably not unity.18 A plutonium analogue of nominal stoichiometry CaPuTi-O^ was prepared by Clinard et al.19 Similarity, cerium is reported as replacing zirconium to stabilize CaCeTi^O^ pyrochlore,20 although iti solid solubility with CaZrTi20^ has not been determined. 6 Perovskite. The only data relating to ACT partitioning in CaTiO* perovskite was presented by Rossouw et al.21 These workers found that about S at% uranium could enter the structure replacing calcium; it is believed that charge balance was achieved by the reduction of tetravalent titanium. The existence of the end- member CaThCK has been reported, but there is no evidence for extensive miscibility with CaTiO,.22 An attempt to synthesise CaPuO-, has been unsuccessful.23 Evans and Marples24 reported the synthesis of [Ca Q^PU 04] lT*l Ov however no chemical data was presented in support of this stoichiometry. (2) TRU Partitioning in Polyphase Assemblages In addition to studies of (predominantly) single phase systems a number of experiments have been devised to determine the partitioning of one or more TRU !? ! elements in polyphase assemblages resembling those of| projected waste forms (Table III). Angelini et al.25 prepared a four phase assemblage containing hollandite, perovskite, zirconolite (polytype unspecified) and pseudobrookite doped with plutonium, americium and curium. Using autoradiography they determined that all three TRU elements entered zirconolite and perovskite. However, they were unable to examine the valence of higher TRU cations, and the relevance of this experiment is unclear since the ceramic was prepared from the melt to promote grain growth. Consequently, elemental partitioning is likely to be different from that encountered