Shaughnessy D A, Nitsche H, Booth C H, Shuh D K, Waychunas G A, Wilson R E, Gill H, Cantrell K J, Serne R J
Chemical Sciences Division, Lawrence Berkeley National Laboratory, Berkeley, California 94720, USA.
Environ Sci Technol. 2003 Aug 1;37(15):3367-74. doi: 10.1021/es025989z.
The sorption of Pu(VI) onto manganite (MnOOH) and hausmannite (Mn3O4) was studied as a function of time, solution pH, and initial plutonium concentration. Kinetic experiments indicate that the surface complexation of plutonium occurs over the first 24 h of contact with the mineral surface. The sorption increases with pH beginning at pH 3 until it reaches a maximum value of 100% at pH 8 (0.0011-0.84 micromol of Pu/m2 of manganite and 0.98-1.2 micromol of Pu/m2 of hausmannite) and then decreases over the pH range from 8 to 10. The ratio of solid to solution was 10 mg/mL for manganite experiments and 4 mg/mL for hausmannite samples. Carbonate was not excluded from the experiments. The amount of plutonium removed from the solution by the minerals is determined by a combination of factors including the plutonium solution species, the surface charge of the mineral, and the mineral surface area. X-ray absorption fine structure taken at the Pu L(III) edge were compared to plutonium standard spectra and showed that Pu(VI) was reduced to Pu(IV) after contact with the minerals. Plutonium sorption to the mineral surface is consistent with an inner-sphere configuration, and no evidence of PuO2 precipitation is observed. The reduction and complexation of Pu(VI) by manganese minerals has direct implications on possible migration of Pu(VI) species in the environment.
研究了钚(VI)在水锰矿(MnOOH)和黑锰矿(Mn3O4)上的吸附情况,考察了其与时间、溶液pH值和初始钚浓度的关系。动力学实验表明,钚与矿物表面接触的最初24小时内发生表面络合。吸附量从pH值3开始随pH值升高而增加,在pH值8时达到最大值100%(水锰矿为0.0011 - 0.84 μmol Pu/m2,黑锰矿为0.98 - 1.2 μmol Pu/m2),然后在pH值8至10范围内下降。水锰矿实验的固液比为10 mg/mL,黑锰矿样品为4 mg/mL。实验中未排除碳酸盐。矿物从溶液中去除的钚量由多种因素共同决定,包括钚溶液形态、矿物表面电荷和矿物表面积。在钚L(III)边采集的X射线吸收精细结构与钚标准光谱进行比较,结果表明钚(VI)与矿物接触后被还原为钚(IV)。钚在矿物表面的吸附符合内球构型,未观察到二氧化钚沉淀的迹象。锰矿物对钚(VI)的还原和络合作用对钚(VI)物种在环境中的可能迁移具有直接影响。