Effects of the orientation of smectite particles and ionic strength on diffusion and activation enthalpies of I− and Cs+ ions in compacted smectite
Source abstract
Abstract
Abstract The apparent diffusion coefficients (Da) for I− and Cs+ ions in compacted Na-smectite which is a major constituent clay mineral of bentonite were studied as a function of smectite's dry density (0.9–1.4 Mg/m3), ionic strength ([NaCl] = 0.01, 0.51 M), temperature (22–60 °C) and diffusion direction to the orientated direction of smectite particles. The Na-smectite was prepared by ion-exchanging with Na+ ions a Na-bentonite, Kunipia-F®, of which smectite content is over 99 wt.%. The Da-values for both ions showed a tendency to be higher in the parallel direction than in the perpendicular direction to the orientated direction of smectite particles at a low-ionic strength of [NaCl] = 0.01 M. The Da-values for I− ions showed different trends depending on diffusion direction and dry density at a high-ionic strength of [NaCl] = 0.51 M. Namely, although the Da-values for I− ions showed a tendency to be higher in the parallel direction than in the perpendicular direction to the orientated direction of smectite particles at a high-dry density of 1.4 Mg/m3, these showed a reciprocal tendency at dry densities of 0.9–1.0 Mg/m3. The Da-values for Cs+ ions uniformly increased with an increase of ionic strength in both diffusion directions. Considering electrostatic effect from smectite surface and the change in tortuosity on dry density, ionic strength and diffusion direction to the orientated direction of smectite particles, I− ions are considered to mainly diffuse in interstitial pores. While, Cs+ ions can diffuse in both interlayer and interstitial pores, and the Da-values are considered to have elevated by competing with Na+ ions. The activation enthalpies (ΔEa) for I− ions, slightly higher (ΔEa = 19.8−20.0 kJ/mol) than that of the diffusion coefficient in free water (Do) for I− ions (ΔEa = 17.36 kJ/mol) at a low-ionic strength of [NaCl] = 0.01 M, decreased with an increase of ionic strength, became of similar level to that of the Do at a high-ionic strength of [NaCl] = 0.51 M, increased with an increase of dry density. On the contrary, the ΔEa-values for Cs+ ions, clearly higher (ΔEa = 25.6−28.4 kJ/mol) than that of the Do for Cs+ ions (ΔEa = 16.47 kJ/mol) even in low-dry density over the ionic strength, increased with an increase of dry density. The ΔEa-values for Cs+ ions are considered to be due to the decrease in the activity of porewater in addition to the effect of ion exchange enthalpy between Cs+ and Na+ ions in smectite.
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Research context
OpenAlex topics: Soil and Unsaturated Flow · Clay minerals and soil interactions · Landfill Environmental Impact Studies
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References (33)
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1. Crank · 1975
2. Eriksen · 1981
3. Alkali metal cation exchange on chambers montmorillonite10.2136/sssaj1972.03615995003600010003x ↗
4. Japan Nuclear Cycle Development Institute (JNC), 2000a. Second progress report on research and development for the geological disposal of HLW in Japan—H12: Project to establish the scientific and technical basis for HLW disposal in Japan—Project Overview Report. JNC Tech. Rep. JNC TN1410 2000-001.
5. Japan Nuclear Cycle Development Institute (JNC), 2000b. Second progress report on research and development for the geological disposal of HLW in Japan—H12: Project to establish the scientific and technical basis for HLW disposal in Japan—Supporting report 3: Safety assessment of the geological disposal system. JNC Tech. Rep. JNC TN1410 2000-004.
6. Moisture adsorption and volume change of partially saturated bentonite buffer materials
7. Kozaki, T., 1999. Fundamental study on corrosion of overpack in buffer material and nuclide migration behaviour in the geological disposal of high-level radioactive waste. Doctoral Thesis. Hokkaido University (in Japanese).
8. Activation energy for diffusion for cesium in compacted sodium montmorillonite10.3327/jnst.33.522 ↗
9. Effect of dry density on activation energy for diffusion of strontium in compacted sodium montmorillonite
10. Activation energy for diffusion of chloride ions in compacted sodium montmorillonite10.1016/S0169-7722(98)00116-8 ↗
11. Diffusion mechanism of cesium ions in compacted montmorillonite10.1016/S0013-7952(99)00077-0 ↗
12. Lever, D. A., 1986. Some notes on experiments measuring diffusion of sorbed nuclides through porous media. Tech. Rep. of the United Kingdom Atom. Ener. Authority Harwell. AERE R 12321.
13. Effects of silica sand and salinity on nuclide migration behaviour in clay
14. Effect of silica sand on activation energy for diffusion of sodium ions in montmorillonite and silica sand mixture10.1016/S0169-7722(02)00115-8 ↗
15. McKinley, I.G., Hadermann, J. 1984. Radionuclide sorption database for Swiss safety assessment. NAGRA Rep. NTB 84–40.
16. Diffusion mechanism of strontium, cesium and cobalt in compacted sodium bentonite
17. The dependence of the diffusion coefficients of 3H and Cs on grain size in compacted montmorillonite
18. Diffusion behaviour of Se(-II) and Sm(III) in compacted sodium bentonite10.1524/ract.1998.82.special-issue.173 ↗
19. The effect of pore structural factors on diffusion in compacted sodium bentonite
20. A study on the effect of clay particle orientation on diffusion in compacted bentonite
21. Sato, H., 2003. Effects of orientation of clay particles and ionic strength on diffusion and activation energies of Cs+ and I− ions in compacted bentonite. JNC Tech. Rep. JNC TN1400 2003-016.10.1557/PROC-824-CC8.46 ↗
22. Sato, H., Shibutani, T., 1994. Study on adsorption and diffusion mechanism nuclides in buffer material and geosphere. PNC Tech. Review, No.84, PNC TN8410 94-284, pp. 71–89.
23. Fundamental study on the effect of an orientation of clay particles on diffusion pathway in compacted bentonite
24. Fundamental study on the effect of an orientation of clay particles on diffusion pathway in compacted bentonite10.1016/S0169-1317(03)00086-3 ↗
25. Effect of dry density on diffusion of some radionuclides in compacted sodium bentonite10.3327/jnst.29.873 ↗
26. Study on retardation mechanism of 3H, 99Tc, 137Cs, 237Np and 241Am in compacted sodium bentonite
27. Diffusion behavior for Se and Zr in sodium-bentonite
28. Shibata, M., Sasamoto, H., Jintoku, T., Yui, M., 2004. Status of assessment technique for long-term stability of buffer material. JNC Tech. Rep. JNC TN8400 2004-010 (in Japanese).
29. Suzuki, S., 2002. Study on diffusion behavior of nuclide in buffer material. JNC Tech. Rep. JNC TN8400 2002-006.
30. Study on anisotropy of effective diffusion coefficient and activation energy for deuterated water in compacted sodium bentonite10.1016/S0169-7722(03)00139-6 ↗
31. In situ observations of the swelling of bentonite aggregates in NaCl solution for interpretation of water permeability in compacted bentonite
32. Thermodynamic properties of water in compacted bentonite under external pressure-free conditions
33. Thermodynamic properties of water in compacted sodium montmorillonite10.13182/NT96-A35276 ↗