SON68 nuclear glass dissolution kinetics: Current state of knowledge and basis of the new GRAAL model

This article summarizes the present state of knowledge concerning aqueous alteration of R7T7-type nuclear containment glasses, represented mainly by the inactive reference glass designated SON68. Based on this review, we propose to describe the glass alteration kinetics up to and including the final residual rate regime by means of a new mechanistic model known as GRAAL (glass reactivity with allowance for the alteration layer). Phenomenological analysis findings are reviewed for the various glass alteration regimes: interdiffusion, initial rate, rate drop, residual rate and, under very particular circumstances, resumption of alteration. These alteration regimes are associated with predominant mechanisms. Published work interpreting and modeling these mechanisms was examined in detail. There is a broad consensus on the general mechanisms of the initial rate and even the interdiffusion regime, whereas the mechanisms controlling the rate drop remain a subject of dispute not only with regard to nuclear glasses but also for the dissolution of silicate minerals. The reaction affinity responsible for the rate drop is expressed differently by different authors and depending on the underlying theories. The disagreement concerns the nature of the phase (glass or gel) or the activated complex controlling the rate drop, which in turn determines the elements that must be taken into account in the overall affinity term. Progress in recent years, especially in identifying the mechanisms responsible for the residual rate, has shed new light on these issues, allowing us to propose new theoretical foundations for modeling the different kinetic regimes of SON68 nuclear glass dissolution. The GRAAL model considers that water diffusion in the passivating reaction zone (the gel formed under saturation conditions) is a rate-limiting step in the overall glass dissolution kinetics. Moreover, this passivation zone is a soluble phase whose stability is directly dependent on the nature of the secondary phases likely to precipitate and on the solution renewal conditions.

[1]  T. Atake,et al.  Thermochemistry of nuclear waste glasses: an experimental determination , 2001 .

[2]  T. Advocat,et al.  Hydrolysis of R7T7 Nuclear Waste Glass in Dilute Media: Mechanisms and Rate as a function of Ph , 1990 .

[3]  T. Advocat,et al.  Kinetic aspects of basaltic glass dissolution at 90°C: role of aqueous silicon and aluminium , 1997 .

[4]  A. Abdelouas,et al.  Water diffusion in the simulated French nuclear waste glass SON 68 contacting silica rich solutions: Experimental and modeling , 2006 .

[5]  Eric H. Oelkers,et al.  General kinetic description of multioxide silicate mineral and glass dissolution , 2001 .

[6]  S. Gin,et al.  SON 68 nuclear glass alteration kinetics between pH 7 and pH 11.5 , 2001 .

[7]  Kathryn L. Nagy,et al.  Chemical weathering rate laws and global geochemical cycles , 1994 .

[8]  John Crank,et al.  The Mathematics Of Diffusion , 1956 .

[9]  C. Jantzen,et al.  Thermodynamic model of natural, medieval and nuclear waste glass durability , 1984 .

[10]  P. Aagaard,et al.  Thermodynamic and kinetic constraints on reaction rates among minerals and aqueous solutions; I, Theoretical considerations , 1982 .

[11]  S. Gin,et al.  Role of neoformed phases on the mechanisms controlling the resumption of SON68 glass alteration in alkaline media , 2004 .

[12]  A. Paul Chemical durability of glasses; a thermodynamic approach , 1977 .

[13]  B. Grambow,et al.  A comparison of the performance of nuclear waste glasses by modeling , 1987 .

[14]  Werner Lutze,et al.  Scientific basis for nuclear waste management , 1979 .

[15]  T. Advocat,et al.  Behaviour of actinides (Th, U, Np and Pu) and rare earths (La, Ce and Nd) during aqueous leaching of a nuclear glass under geological disposal conditions , 1998 .

[16]  T. Chave,et al.  Solid state diffusion during nuclear glass residual alteration in solution , 2007 .

[17]  T. Charpentier,et al.  Influence of glass composition and alteration solution on leached silicate glass structure: A solid-state NMR investigation , 2006 .

[18]  R. H. Doremus,et al.  INTERDIFFUSION OF HYDROGEN AND ALKALI IONS IN A GLASS SURFACE , 1975 .

[19]  M. I. Ojovan,et al.  THE ION EXCHANGE PHASE IN CORROSION OF NUCLEAR WASTE GLASSES , 2006 .

[20]  P. Frugier,et al.  The effect of composition on the leaching of three nuclear waste glasses: R7T7, AVM and VRZ , 2005 .

[21]  S. Gíslason,et al.  The mechanism, rates and consequences of basaltic glass dissolution: I. An experimental study of the dissolution rates of basaltic glass as a function of aqueous Al, Si and oxalic acid concentration at 25°C and pH = 3 and 11 , 2001 .

[22]  Roland Hellmann,et al.  The albite-water system: Part I. The kinetics of dissolution as a function of pH at 100, 200 and 300°C , 1994 .

[23]  B. C. Bunker,et al.  Molecular mechanisms for corrosion of silica and silicate glasses , 1994 .

[24]  S. Gin,et al.  Hydrogen–sodium interdiffusion in borosilicate glasses investigated from first principles , 2006 .

[25]  P. Barboux,et al.  Influence of insoluble elements on the nanostructure of water altered glasses , 2004 .

[26]  T. Advocat,et al.  Thermochemistry of nuclear waste glasses: application to weathering studies , 2001 .

[27]  Bernd Grambow,et al.  First-order dissolution rate law and the role of surface layers in glass performance assessment , 2001 .

[28]  J. Crovisier,et al.  Early phyllosilicates formed by alteration of R7T7 glass in water at 250°C , 1992 .

[29]  M. Kakihana,et al.  Materials Research Society Symposium - Proceedings , 2000 .

[30]  David K. Peeler,et al.  Measurement of kinetic rate law parameters on a NaCaAl borosilicate glass for low-activity waste , 1997 .

[31]  C. Jantzen,et al.  Scientific basis for nuclear waste management , 1985 .

[32]  P. Barboux,et al.  Numerical modelling of glass dissolution: gel layer morphology , 2001 .