Fate and transport of uranium (VI) in weathered saprolite

被引:10
|
作者
Kim, Young-Jin [1 ]
Brooks, Scott C. [2 ]
Zhang, Fan [3 ]
Parker, Jack C. [4 ]
Moon, Ji-Won [5 ]
Roh, Yul [6 ]
机构
[1] Samsung C&T Corp, Civil Engn Div, Seoul 137956, South Korea
[2] Oak Ridge Natl Lab, Div Environm Sci, Oak Ridge, TN 37831 USA
[3] Chinese Acad Sci, Inst Tibetan Plateau Res, Key Lab Tibetan Environm Changes & Land Surface P, Beijing 100085, Peoples R China
[4] Univ Tennessee, Dept Civil & Environm Engn, Knoxville, TN 37996 USA
[5] Oak Ridge Natl Lab, Biosci Div, Oak Ridge, TN 37831 USA
[6] Chonnam Natl Univ, Fac Earth Syst & Environm Sci, Kwangju 500757, South Korea
关键词
Uranium(VI); Transport; Modeling; Saprolite; SOLUTE TRANSPORT; BLIND PREDICTION; ADSORPTION; SORPTION; SURFACE; URANYL; GOETHITE; KINETICS; U(VI); GROUNDWATER;
D O I
10.1016/j.jenvrad.2014.10.008
中图分类号
X [环境科学、安全科学];
学科分类号
08 ; 0830 ;
摘要
Batch and column experiments were conducted to investigate sorption and transport of uranium (U) in the presence of saprolite derived from interbedded shale, limestone, and sandstone sequences. Sorption kinetics were measured at two initial concentrations (C-0; 1, 10 mu M) and three soil:solution ratios (R-s/w; 0.005, 0.25, 2 kg/L) at pH 4.5 (pH of the saprolite). The rate of U loss from solution (mu mole/L/h) increased with increasing R-s/w. Uranium sorption exhibited a fast phase with 80% sorption in the first eight hours for all C-0 and R-s/w values and a slow phase during which the reaction slowly approached (pseudo) equilibrium over the next seven days. The pH-dependency of U sorption was apparent in pH sorption edges. U(VI) sorption increased over the pH range 4-6, then decreased sharply at pH > 7.5. U(VI) sorption edges were well described by a surface complexation model using calibrated parameters and the reaction network proposed by Waite et al. (1994). Sorption isotherms measured using the same R-s/w and pH values showed a solids concentration effect where U(VI) sorption capacity and affinity decreased with increasing solids concentration. This effect may have been due to either particle aggregation or competition between U(VI) and exchangeable cations for sorption sites. The surface complexation model with calibrated parameters was able to predict the general sorption behavior relatively well, but failed to reproduce solid concentration effects, implying the importance of appropriate design if batch experiments are to be utilized for dynamic systems. Transport of U(VI) through the packed column was significantly retarded. Transport simulations were conducted using the reactive transport model HydroGeoChem (HGC) v5.0 that incorporated the surface complexation reaction network used to model the batch data. Model parameters reported by Waite et al. (1994) provided a better prediction of U transport than optimized parameters derived from our sorption edges. The results presented in this study highlight the challenges in defining appropriate conditions for batch-type experiments used to extrapolate parameters for transport models, and also underline a gap in our ability to transfer batch results to transport simulations. (C) 2014 Elsevier Ltd. All rights reserved.
引用
收藏
页码:154 / 162
页数:9
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