Microstructural modeling of compacted sodium-bentonite and application of unified molecular dynamics/homogenization analysis for diffusion process
Creators
- 1. Japan Nuclear Cycle Development Inst., Waste Management and Fuel Cycle Research Center, Tokai, Ibaraki (Japan)
- 2. Nagoya Univ., Nagoya, Aichi (Japan)
- 3. Tokyo Inst. of Tech. (Japan)
Description
For the better understanding of diffusion process in the buffer material of the HLW disposal system, microstructures of compacted Na-bentonite (Na-smectite content > 98 wt%) were studied by the Scanning Electron Microscopy (SEM) and the X-ray diffractometry (XRD). Consolidated clay particles of 100 μm in width, up to 10 μm in thickness in dry powder of the bentonite because finer ones in compacted bentonite saturated by aqueous solutions. These fine particles, called as stacks, consisted of several or more clay sheets of 100 to 10000 nm in width, 1 nm in thickness. The pore structure among stacks (external pore) was controlled by the swelling of stacks, because of the selective hydration of interlamellar space of smectite (internal pore). XRD profiles of the saturated bentonite changed with respect to dry densities of bentonite and salinity of solution. The diffraction peak related to basal spacings, d(001) of 3.52 nm disappeared at high dry densities > 1.0 Mg/m3. The peak due to the d(001) of 1.88 nm was observed at dry densities of 0.8 to 1.2 Mg/m3, while that of 1.56 nm was observed at dry densities > 1.6 Mg/m3. The influences of salinity on the d(001) were investigated at a dry density of 0.9 Mg/m3 and NaCl concentrations of 0.0 M to 0.5 M. There were peaks attributed to the d(001) of 3.52 nm and 1.88 nm. The former peak was observed at the low-saline conditions ≤ 0.1 M NaCl, while the latter one unchanged with respect to salinity. Absence of d(001) of 3.52 nm is indicative of aggregation of smectite crystal at the high-saline conditions. On the basis of the above observation, the external pore size, L was expressed as a function of the number of clay layers, n per a stack and a dry density ρdry as follows; L = nδ(1/(1+λ)2 ρclay/ρdry - 1) - (d(001)-δ)(n-1) where λ is a structural parameter, δ is a thickness of a smectite layer (1 nm) and ρdry and ρclay are dry densities of bentonite and smectite crystal, respectively. The external pore size abruptly increased with a decrease in the dry density and with an increase in the number of clay layer. Diffusion coefficients of tritiated water (HTO) predicted by the unified molecular dynamics and homogenization analysis for the uniform non-tortuous structure were about twice as large as those experimentally determined. These differences can be seem to be accounted by the tortuosity effects. (author)
Availability note (English)
Available from JICST Library (JICST: Japan Science and Technology Corporation, Information Center for Science and Technology), P.O. Box 10 Hikarigaoka, Tokyo 179-9810 Japan, FAX: +81-3-3979-4781 (domestic), FAX: +81-3-3979-2210 (oversea)Additional details
Publishing Information
- Imprint Pagination
- 73 p.
- Report number
- JNC-TY--8400-2001-003
INIS
- Country of Publication
- Japan
- Country of Input or Organization
- Japan
- INIS RN
- 33023540
- Subject category
- S12: MANAGEMENT OF RADIOACTIVE WASTES, AND NON-RADIOACTIVE WASTES FROM NUCLEAR FACILITIES;
- Resource subtype / Literary indicator
- Non-conventional Literature
- Descriptors DEI
- BENTONITE; COMPACTS; DIFFUSION; GEOLOGIC STRATA; HIGH-LEVEL RADIOACTIVE WASTES; HOMOGENIZATION METHODS; MATHEMATICAL MODELS; MICROSTRUCTURE; MOLECULAR DYNAMICS METHOD; NUMERICAL ANALYSIS; RADIOACTIVE WASTE DISPOSAL; UNDERGROUND DISPOSAL
- Descriptors DEC
- CALCULATION METHODS; CLAYS; GEOLOGIC STRUCTURES; INORGANIC ION EXCHANGERS; ION EXCHANGE MATERIALS; MANAGEMENT; MATERIALS; MATHEMATICS; MINERALS; RADIOACTIVE MATERIALS; RADIOACTIVE WASTE MANAGEMENT; RADIOACTIVE WASTES; SILICATE MINERALS; WASTE DISPOSAL; WASTE MANAGEMENT; WASTES
Optional Information
- Notes
- 31 refs., 17 figs., 3 tabs.