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Co-transport of U(Ⅵ) and gibbsite colloid in saturated granite particle column: Role of pH, U(Ⅵ) concentration and humic acid

机译:U(Ⅵ)和三水铝灰石胶在饱和花岗岩颗粒柱中的共运:pH,U(Ⅵ)浓度和腐殖酸的作用

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Understanding the in-situ transport behavior of U(VI) in granitic formations is of considerable interest for geological disposal of high-level radioactive wastes (HLW). In this context, the co-transport of U(VI) and representative naturally-occurring colloids, i.e., humic add (HA) and gibbsite colloid (GC), was studied in granite column as a function of pH, U(VI) concentration and HA amount. It was found that, in addition to pH, co-transport of U(VI) and GC was also controlled by U(VI) concentration, the effect of which can be transport-facilitating and transport-impeding for U(VI) at relatively low concentration (2.0 x 10(-6) mol/L) and for U(VI) at high concentration (5.0 x 10(-6) mol/L), respectively. HA can present opposite effects on GC transport depending on HA amount. The transport-impeding effect by small amount of HA (5 mg/L) is due to strong aggregation between GC and HA from electrostatic attraction and complexation, whereas the transport-facilitating effect by big amount of HA (20 mg/L) is because of the complete HA coating which stabilizes associated colloids and alters surface charge from positive to negative. In ternary co-transport systems, a similar HA-dependent effect was also observed for both U(VI) and GC regardless of presence of high concentration U(VI). Besides the application of the Derjaguin-Landau-Verwey-Overbeek (DLVO) theory, the mechanisms behind binary and ternary co-transport of U(VI), GC and HA were also analyzed by assessing the evolutions of zeta potential and particle size in the column effluents. Finally, a two-site non-equilibrium model and a two-site kinetic attachment/detachment model were applied to describe the breakthrough curves of U(VI) and individual/combined colloids, respectively. The findings of this study indicated that combined effects of GC and HA on radionuclides transport is dominated by the amount of HA, and a facilitating transport of radionuclide can be expected in the underground environment rich in humic acid. (C) 2019 Elsevier B.V. All rights reserved.
机译:对于高放射性废物(HLW)的地质处置,了解花岗岩层中U(VI)的原位运输行为具有相当大的兴趣。在这种情况下,研究了花岗岩柱中U(VI)与代表性天然胶体(腐殖酸添加物(HA)和三水铝石胶体(GC))的共同运输与pH,U(VI)浓度的关系。和HA金额。研究发现,除了pH值外,U(VI)和GC的共同转运也受U(VI)浓度的控制,在相对较高的浓度下,U(VI)的转运促进和转运阻碍作用。低浓度(2.0 x 10(-6)mol / L)和高浓度(5.0 x 10(-6)mol / L)的U(VI)。 HA可能根据HA量对GC传输产生相反的影响。少量HA(5 mg / L)的运输阻碍作用是由于GC和HA之间由于静电吸引和络合产生的强聚集作用,而大量HA(20 mg / L)的运输促进作用是由于完整的HA涂层的涂层,可稳定相关的胶体并使表面电荷从正变负。在三元共同运输系统中,无论是否存在高浓度的U(VI),U(VI)和GC都观察到类似的HA依赖效应。除了应用Derjaguin-Landau-Verwey-Overbeek(DLVO)理论外,还通过评估Zeta电位和颗粒中Zeta势的演变来分析U(VI),GC和HA的二元和三元共转运的机理。柱流出物。最后,使用两点非平衡模型和两点动力学附着/分离模型分别描述了U(VI)和单个/组合胶体的穿透曲线。这项研究的结果表明,GC和HA对放射性核素运输的综合影响主要由HA决定,在富含腐殖酸的地下环境中,放射性核素的运输有望得到促进。 (C)2019 Elsevier B.V.保留所有权利。

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