Cs adsorption sites in clay influenced by solution concentration
Since the nuclear crisis at Fukushima, the Cs decontamination works have yielded a large amount of contaminated soil. The urgency of reducing the volume of contaminated soil has become a serious concern with respect to the acceleration of ongoing work. The contaminated soil is reduced in volume through water treatment, using water circulation equipment specially designed. The fundamental principle of volume reduction is that radioactive Cs dissolved in water tends to strongly adsorb onto the surface of two-dimensional (2D) nanosheets, a basic structural unit of clay minerals.
Smaller particles of contaminated soil exhibit higher specific surface area for Cs adsorption in aqueous solution, enabling them to associate with a larger amount of radioactive Cs. The circulation of a lump of contaminated soil in aqueous solution is thus able to separate the fractions that contain high doses of radioactive Cs, which accumulated around the fine soil particles accompanying the clay minerals.
To aid the ongoing decontamination work, the adsorption of Cs in aqueous solution across a wide Cs molarity range is studied for the case of saponite clay as adsorbent, an inorganic layered material that is an abundant mineral in the soil environment. The local structure built by two-nanosheet insertion in clay is schematically shown in Figure 1 (see (I)). This local molecular structure contains three kinds of Cs adsorption sites: (a) nanosheet surfaces, (b) nanosheet edges, and (c) wedge-shaped parts. Cs ions are physisorbed at the nanosheet surfaces, which are negatively charged because of local compositional and structural fluctuations. Heavily adhesive Cs adsorption, so-called specific Cs adsorption, occurs both at the nanosheet edges and wedge-shaped parts. 2D nanosheets are also able to form other local molecular structures where both sides are hexagonal cavities and one side is a hexagonal cavity (see (II) and (III)). In these local molecular structures, Cs physisorption occurs at (d) oncoming hexagonal cavities and (e) hexagonal cavities. Furthermore, a step structure can be formed by the 2D nanosheets, which exhibit the nanosheet edge sites (see (IV)).
Figure 2 shows the concentrations of nanosheet surfaces, cs, nanosheet edges, ce, and oncoming hexagonal cavities, co, as a function of solution concentration, which were revealed by the newly developed analytical method. Here, the concentration of wedge-shaped parts is assumed to be ~ 9×10-2 mmol kg-1 for all the Cs-loaded samples. The concentrations of the three molecular sites all increase with increasing Cs molarity of the solution. This indicates that more Cs ions adsorb at the nanosheet surfaces, nanosheet edges, and oncoming hexagonal cavities in more highly concentrated Cs solutions. The cs value rapidly increases with increasing solution concentration up to 0.5 M and then gradually increases up to 2 M. In contrast, the concentration of oncoming hexagonal cavities, co, increases with the Cs molarity of the solution more slowly than that of nanosheet surfaces, cs, indicating that adsorption of Cs into the oncoming hexagonal cavities is less favorable than that on the nanosheet surfaces. The concentration of the nanosheet edges ce continues to slowly increase with the Cs molarity of the solution up to 2 M, indicating that the adsorption of Cs there is the most difficult among the three adsorption sites. In view of the decontamination of radioactive Cs from clay minerals, the nanosheet edge sites are of particular significance because of their capability for heavily adhesive Cs adsorption. The present results imply that the nanosheet edges should be targeted as the local molecular sites for the future decontamination of radioactive Cs.
Department of Environmental Sciences, Tokyo Gakugei University, Koganei, Tokyo, Japan
Molecular studies of Cs adsorption sites in inorganic layered materials: the influence of solution concentration.
Sato K, Hunger M
Phys Chem Chem Phys. 2017 Jul 19