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      The role of nano-perovskite in the negligible thorium release in seawater from Greek bauxite residue (red mud)

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          Abstract

          We present new data about the chemical and structural characteristics of bauxite residue (BR) from Greek Al industry, using a combination of microscopic, analytical, and spectroscopic techniques. SEM-EDS indicated a homogeneous dominant “Al-Fe-Ca-Ti-Si-Na-Cr matrix”, appearing at the microscale. The bulk chemical analyses showed considerable levels of Th (111 μg g −1), along with minor U (15 μg g −1), which are responsible for radioactivity (355 and 133 Bq kg −1 for 232Th and 238U, respectively) with a total dose rate of 295 nGy h −1. Leaching experiments, in conjunction with SF-ICP-MS, using Mediterranean seawater from Greece, indicated significant release of V, depending on S/L ratio, and negligible release of Th at least after 12 months leaching. STEM-EDS/EELS & HR-STEM-HAADF study of the leached BR at the nanoscale revealed that the significant immobility of Th 4+ is due to its incorporation into an insoluble perovskite-type phase with major composition of Ca 0.8Na 0.2TiO 3 and crystallites observed in nanoscale. The Th L III-edge EXAFS spectra demonstrated that Th 4+ ions, which are hosted in this novel nano-perovskite of BR, occupy Ca 2+ sites, rather than Ti 4+ sites. That is most likely the reason of no Th release in Mediterranean seawater.

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          Most cited references11

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          The challenges of reusing mining and mineral-processing wastes.

          Mining and mineral-processing wastes are one of the world's largest chronic waste concerns. Their reuse should be included in future sustainable development plans, but the potential impacts on a number of environmental processes are highly variable and must be thoroughly assessed. The chemical composition and geotechnical properties of the source rock determine which uses are most appropriate and whether reuse is economically feasible. If properly evaluated, mining waste can be reused to reextract minerals, provide additional fuel for power plants, supply construction materials, and repair surface and subsurface land structures altered by mining activities themselves.
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            The red mud accident in ajka (hungary): plant toxicity and trace metal bioavailability in red mud contaminated soil.

            The red mud accident of October 4, 2010, in Ajka (Hungary) contaminated a vast area with caustic, saline red mud (pH 12) that contains several toxic trace metals above soil limits. Red mud was characterized and its toxicity for plants was measured to evaluate the soil contamination risks. Red mud radioactivity (e.g., (238)U) is about 10-fold above soil background and previous assessments revealed that radiation risk is limited to indoor radon. The plant toxicity and trace metal availability was tested with mixtures of this red mud and a local noncontaminated soil up to a 16% dry weight fraction. Increasing red mud applications increased soil pH to maximally 8.3 and soil solution EC to 12 dS m(-1). Shoot yield of barley seedlings was affected by 25% at 5% red mud in soil and above. Red mud increased shoot Cu, Cr, Fe, and Ni concentrations; however, none of these exceed toxic limits reported elsewhere. Moreover, NaOH amended reference treatments showed similar yield reductions and similar changes in shoot composition. Foliar diagnostics suggest that Na (>1% in affected plants) is the prime cause of growth effects in red mud and in corresponding NaOH amended soils. Shoot Cd and Pb concentrations decreased by increasing applications or were unaffected. Leaching amended soils (3 pore volumes) did not completely remove the Na injury, likely because soil structure was deteriorated. The foliar composition and the NaOH reference experiment allow concluding that the Na salinity, not the trace metal contamination, is the main concern for this red mud in soil.
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              Characterization of red mud derived from a combined Bayer Process and bauxite calcination method.

              Red mud can be derived from the processing of bauxite using different methods. The chemical and mineralogical composition of the combined Bayer Process and bauxite calcination red mud (BPBCRM) differs markedly from those of the pure Bayer Process red mud (PBPRM). In this study, red mud derived from a combined Bayer Process and bauxite calcination method was characterized. The results show that pH of the red mud decreased with increasing duration of storage time. Na dominated among the soluble cations, but the concentration of soluble Na decreased with increasing duration of storage time as a result of leaching. Cation exchange capacity also decreased with increasing duration of storage time, probably due to a decrease in pH causing a reduction in negatively charged sites on the red mud particles. Ca was the predominant exchangeable cation in the fresh red mud but the concentration of exchangeable Ca markedly decreased in the old red mud, which was dominated by exchangeable Na. The degree of crystallization and thermal stability of the red mud increased with increasing duration of storage. The acid neutralizing capacity of red mud obtained from this study was about 10 mol kg(-1), which is much greater than the reported values for the pure Bayer Process red mud. Column filtering experiment indicates that the red mud also had a very strong capacity to remove Cu, Zn and Cd from the filtering solution. It is conservatively estimated that the simultaneous removal rates of Cd, Zn and Cu by red mud are over 22,250 mg kg(-1), 22,500 mg kg(-1) and 25,000 mg kg(-1), respectively. The affinity of these metals to the red mud was in the following decreasing order: Cu>Zn>Cd. In general, the fresh red mud retained more heavy metals than the old red mud did.
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                Author and article information

                Journal
                Sci Rep
                Sci Rep
                Scientific Reports
                Nature Publishing Group
                2045-2322
                22 February 2016
                2016
                : 6
                : 21737
                Affiliations
                [1 ]Center for Electron Nanoscopy, Technical University of Denmark , 2800 Kongens Lyngby, Denmark
                [2 ]Faculty of Geology & Geoenvironment, National and Kapodistrian University of Athens, Zografou Campus , 15784 Athens, Greece
                [3 ]Institute of Solid State Physics, University of Latvia , Kengaraga str. 8, 1063 Riga, Latvia
                [4 ]Karlsruhe Institute of Technology, Institute for Nuclear Waste Disposal , Hermann-von-Helmholtz-Platz 1, 76344 Eggenstein-Leopoldshafen, Germany
                [5 ]Faculty of Physics, National and Kapodistrian University of Athens, Zografou Campus , 15784 Athens, Greece
                [6 ]Karlsruhe Institute of Technology, ANKA Synchrotron Radiation Facility , Hermann-von-Helmholtz-Platz 1, 76344 Eggenstein-Leopoldshafen, Germany
                [7 ]Department of Electrical and Computer Engineering, Nuclear Technology Laboratory, Aristotle University of Thessaloniki , 54124 Thessaloniki, Greece
                [8 ]Department of Automation Engineering, Alexander Technological Educational Institute of Thessaloniki , 57400 Thessaloniki, Greece
                [9 ]KU Leuven, Department of Materials Engineering , Kasteelpark Arenberg 44, 3001 Leuven, Belgium
                [10 ]University of Patras, Department of Chemical Engineering , 26500 Rio, Greece
                [11 ]PANalytical B.V. , 7600 AA Almelo, The Netherlands
                [12 ]School of Geology, Aristotle University of Thessaloniki , 54124, Thessaloniki, Greece
                Author notes
                Article
                srep21737
                10.1038/srep21737
                4761986
                26899139
                8937a9ff-22ca-4043-8bed-d15a511120e8
                Copyright © 2016, Macmillan Publishers Limited

                This work is licensed under a Creative Commons Attribution 4.0 International License. The images or other third party material in this article are included in the article’s Creative Commons license, unless indicated otherwise in the credit line; if the material is not included under the Creative Commons license, users will need to obtain permission from the license holder to reproduce the material. To view a copy of this license, visit http://creativecommons.org/licenses/by/4.0/

                History
                : 06 August 2015
                : 25 January 2016
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