Uranium fate during crystallization of magnetite from ferrihydrite in conditions relevant to the disposal of radioactive waste

被引:32
|
作者
Marshall, Timothy A. [1 ,2 ]
Morris, Katherine [1 ,2 ]
Law, Gareth T. W. [1 ,3 ]
Mosselmans, J. Frederick W. [4 ]
Bots, Pieter [1 ,2 ]
Roberts, Hannah [1 ,2 ]
Shaw, Samuel [1 ,2 ]
机构
[1] Univ Manchester, Res Ctr Radwaste Disposal, Sch Earth Atmospher & Environm Sci, Manchester M13 9PL, Lancs, England
[2] Univ Manchester, Williamson Res Ctr Mol Environm Sci, Sch Earth Atmospher & Environm Sci, Manchester M13 9PL, Lancs, England
[3] Univ Manchester, Ctr Radiochem Res, Sch Chem, Manchester M13 9PL, Lancs, England
[4] Diamond Light Source Ltd, Didcot OX11 0DE, Oxon, England
关键词
uranium; magnetite; incorporation; EXAFS; radioactive waste; geodisposal; RAY-ABSORPTION SPECTROSCOPY; U(VI) SORPTION; 111; SURFACE; REDUCTION; KINETICS; U(IV); DIFFRACTION; COMPLEXES; OXIDATION; SEDIMENTS;
D O I
10.1180/minmag.2015.079.6.02
中图分类号
P57 [矿物学];
学科分类号
070901 ;
摘要
Uranium incorporation into magnetite and its behaviour during subsequent oxidation has been investigated at high pH to determine the uranium retention mechanism(s) on formation and oxidative perturbation of magnetite in systems relevant to radioactive waste disposal. Ferrihydrite was exposed to U(VI)(aq) containing cement leachates (pH 10.5-13.1) and crystallization of magnetite was induced via addition of Fe(II)(aq). A combination of XRD, chemical extraction and XAS techniques provided direct evidence that U(VI) was reduced and incorporated into the magnetite structure, possibly as U(V), with a significant fraction recalcitrant to oxidative remobilization. Immobilization of U(VI) by reduction and incorporation into magnetite at high pH, and with significant stability upon reoxidation, has clear and important implications for limiting uranium migration in geological disposal of radioactive wastes.
引用
收藏
页码:1265 / 1274
页数:10
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