Dissolution of montmorillonite in compacted bentonite by highly alkaline aqueous solutions and diffusivity of hydroxide ions

被引:85
作者
Nakayama, S [1 ]
Sakamoto, Y
Yamaguchi, T
Akai, M
Tanaka, T
Sato, T
Iida, Y
机构
[1] Japan Atom Energy Res Inst, Dept Fuel Cycle Safety Res, Tokai, Ibaraki 3191195, Japan
[2] Kanazawa Univ, Inst Nat & Environm Technol, Kanazawa, Ishikawa 9201192, Japan
关键词
bentonite; montmorillonite; alkaline alteration; diffusion; hydroxide ion;
D O I
10.1016/j.clay.2003.12.023
中图分类号
O64 [物理化学(理论化学)、化学物理学];
学科分类号
070304 ; 081704 ;
摘要
Highly alkaline environments induced by cementitious materials in radioactive waste repositories are likely to alter montmorillonite, the main constituent of bentonite buffer materials. Over long time periods, the alteration may cause the physical and/or chemical properties of the buffer to deteriorate. For the purpose of acquiring quantitative data to determine the effect of alteration on the permeability of a bentonite buffer, dissolution rates of montmorillonite and diffusivity of hydroxide ions in compacted sand-bentonite mixture specimens have been measured under highly alkaline, simulated groundwater conditions. Dissolution of montmorillonite was described by the linear dependence on time, W(t)=W(0)-R(A)t, under the employed experimental conditions of pH 13 to 14 and temperatures of 90 to 170 degreesC, where W(t) denotes the density of montmorillonite (mg of montmorillonite/m(3) of sand-bentonite mixture), W(0) the initial density, RA (Mg m(-3) s(-1)) the rate of density decrease and t(s) the time after the contact with the simulated groundwater. RA is a function of pH and temperature (K), and expressed as R-A=(0.013+/-0.007)exp[-(3.7+/-0.2) x 10(4)/RT for the "pH 14.0" simulated groundwater, where R is the gas constant. The diffusivity of hydroxide ions was obtained in through-diffusion experiments combined with a pore diffusion model. The experiments were performed under relatively low temperatures of 10 to 50 degreesC to minimize the effect of alteration of bentonite. The effective diffusivity of hydroxide ions was in the order of 10(-10) to 10(-11) m(2)/s, and is in the same order as those of Cl-, I- and tritiated water. (C) 2004 Elsevier B.V. All rights reserved.
引用
收藏
页码:53 / 65
页数:13
相关论文
共 35 条
[1]  
ADLER M, 1998, MINERAL MAG, P15
[2]  
ATKINSON A, 1985, 11777 AERER UK AT EN
[3]   Kaolinite transformation in high molar KOH solutions [J].
Bauer, A ;
Velde, B ;
Berger, G .
APPLIED GEOCHEMISTRY, 1998, 13 (05) :619-629
[4]   Kaolinite and smectite dissolution rate in high molar KOH solutions at 35° and 80°C [J].
Bauer, A ;
Berger, G .
APPLIED GEOCHEMISTRY, 1998, 13 (07) :905-916
[5]  
BERNER U R, 1992, Waste Management, V12, P201, DOI 10.1016/0956-053X(92)90049-O
[6]   CONTROLS ON SILICATE DISSOLUTION RATES IN NEUTRAL AND BASIC PH SOLUTIONS AT 25-DEGREES-C [J].
BRADY, PV ;
WALTHER, JV .
GEOCHIMICA ET COSMOCHIMICA ACTA, 1989, 53 (11) :2823-2830
[7]  
BRINDLEY GW, 1970, ISRAEL J CHEM, V8, P409
[8]   Smectite dissolution kinetics at 80°C and pH 8.8 [J].
Cama, J ;
Ganor, J ;
Ayora, C ;
Lasaga, CA .
GEOCHIMICA ET COSMOCHIMICA ACTA, 2000, 64 (15) :2701-2717
[9]   Zeolite formation during the alkaline reaction of bentonite [J].
de la Villa, RV ;
Cuevas, J ;
Ramírez, S ;
Leguey, S .
EUROPEAN JOURNAL OF MINERALOGY, 2001, 13 (03) :635-644
[10]   Migration experiments in compacted Ca-bentonite [J].
García-Gutiérrez, M ;
Missana, T ;
Molinero, J ;
Yllera, A ;
Mingarro, M .
SCIENTIFIC BASIS FOR NUCLEAR WASTE MANAGEMENT XXII, 1999, 556 :695-701