title: Sorption and retardation of strontium in saturated Chinese loess: experimental results and model analysis.
abstract: Geological burial and landfill have been widely practiced for disposal of nuclear wastes. However, radionuclides in the waste leachate from landfill facilities can contaminate soil and groundwater. Chinese loess is widely distributed in China and has been involved in large-scale disposal of nuclear wastes. Consequently, there has been an urgent need for understanding and predicting the fate and transport of contaminants in both vadose and saturated zones in the loess. In this paper, the distribution coefficient (K(d)) values of Strontium between a Chinese loess and groundwater were determined in batch experiments. The isotherm could be described with nearly linear isotherm model, which resulted in a K(d) value of 40.0 cm(3)/g. Based on this K(d) value, the retardation factor (R(d), the ratio of pore water velocity to solute transport velocity) value was calculated to be 112.6. As an alternative approach, the R(d) value was also determined through independent column experiments and transport modeling. Bromide (Br(-)) was used as a non-reactive tracer, and reagent SrCl(2) was used as a surrogate for the radioactive isotope ((99)Sr) in the experiment because they share the same adsorption and transportation characteristics. An equilibrium-based model and a two-region non-equilibrium model were employed to interpret the column sorption data of Sr. The computer program, CXTFIT 2.1, was used to estimate the parameters by simulating the breakthrough and retention curves of Br and Sr, respectively. The resultant D (dispersion coefficient) value for Sr transport was much lower than that of Br(-), indicating the important effect of chemical non-equilibrium of Sr in the loess system. The observed Sr retention curves in the loess were best modeled by the two-site transport model. The R(d) value determined from batch equilibrium tests differed markedly from that determined from the column transport experiments, and the R(d) value decreased with increasing pore-water velocity. The relationship between D and pore water flow velocity (v) was determined as a D = 1.192v(1.26). The results from this work indicate that the strong flow and non-equilibrium effects on the transport parameters (R(d) and D) must be taken into account in Sr transport modeling.
authors.affiliation: Institute of Environmental Science, Taiyuan University of Science and Technology, Taiyuan, Shanxi 030024, PR China.
authors.forename: Lijuan
authors.initials: L
authors.lastname: Huo
authors.forename: Tianwei
authors.initials: T
authors.lastname: Qian
authors.forename: Junting
authors.initials: J
authors.lastname: Hao
authors.forename: Dongye
authors.initials: D
authors.lastname: Zhao
mesh_terms: D000327:Adsorption; D002681:China; D060587:Groundwater / Q000737:chemistry; D008962:Models, Theoretical; D011834:Radiation Monitoring; D011850:Radioactive Waste; D012037:Refuse Disposal; D012990:Soil Pollutants, Radioactive / Q000737:chemistry*; D013324:Strontium / Q000737:chemistry*; D014872:Water Movements; D014875:Water Pollutants, Radioactive / Q000737:chemistry*
chemical_list: D011850:Radioactive Waste; D012990:Soil Pollutants, Radioactive; D014875:Water Pollutants, Radioactive; D013324:Strontium