Modelling chemical ordering in aluminosilicates and subsequent prediction of cation immobilisation efficiency John L. Provis, Peter Duxson, Grant C. Lukey and Jannie S. J. van Deventer * Department of Chemical and Biomolecular Engineering The University of Melbourne Victoria 3010 AUSTRALIA Abstract A statistical thermodynamic model is developed for description of aluminium-silicon ordering in aluminosilicate materials, with particular reference to geopolymeric and glassy materials. The ‘Loewenstein aluminium avoidance principle’ is examined, and found not to hold strictly in these materials. These findings, in agreement with NMR data on glasses and natural and synthetic minerals and with quantum chemical calculations, show that the tendency for formation of Si-O-Al linkages in preference to Si-O-Si and Al-O-Al, leading to a significant degree of chemical ordering in these materials, is based on energetic considerations. The model outlined in this paper is developed by minimisation of the Gibbs energy of mixing in an amorphous aluminosilicate phase. Predictions of the degree of ordering in a range of geopolymeric and glassy materials are compared to quantitative data obtained from solid-state NMR. Formation of Al-O-Al bonds will prove very important in the utilisation of both geopolymerisation and vitrification as methods of immobilising toxic or radioactive metals in cationic form. These bonds are significantly weaker than Si-O-Al bonds with respect to the energy required to remove an Al atom from the material structure, and so any degree of Al-O-Al formation will be significantly detrimental to immobilisation efficiency over a prolonged period. Analysis of the relative degrees of Al-O-Al formation observed in geopolymers and in aluminosilicate glasses suggests that, on this basis and in addition to significant advantages in processing, geopolymerisation will in many instances prove a more effective method of waste immobilisation than vitrification. Keywords: Geopolymer, aluminosilicates, short-range ordering, immobilisation, cations * Author to whom correspondence should be addressed: jannie@unimelb.edu.au – Phone +61 3 8344 6619 – Fax +61 3 8344 7707 1. Introduction Geopolymers are a class of high-performance mineral binders obtained by the reaction of an aluminosilicates powder with alkali metal hydroxide or silicate solutions at ambient or slightly elevated temperature (Davidovits 1991). The composition of the geopolymeric binder is represented as (SiO2)x(MAlO2)1-x, where M is Na+ and/or K+, and 0.52<x<0.70 for the samples investigated here. Geopolymers are believed to have a primarily gel-like structure, are essentially X-ray amorphous and thus have no clearly defined network topology. Recently, 29Si MAS-NMR spectra of geopolymers with a range of compositions have been presented (Duxson et al. 2005). Deconvolution of these spectra provides meaningful information regarding the distribution of the tetrahedral silicon and aluminium sites forming the geopolymeric gel network structure (Duxson et al. 2005), as has also been observed in aluminosilicate glasses (Lee & Stebbins 1999) and minerals (Phillips et al. 1992). Geopolymers have been identified as having significant potential in the area of radioactive waste treatment (Davidovits & Comrie 1988, Khalil & Merz 1994, Bao et al. 2003, Chervonnyi & Chervonnaya 2003), as they are able to strongly encapsulate a range of cations. In particular, immobilisation of Cs + and Sr2+ is of significance in the control and cleanup of contaminated sites and wastewater. These cations can each be strongly bound into the geopolymeric matrix structure, which is therefore a much more stable form of immobilisation than the encapsulation or vitrification methods currently in use (Siemer 2002). Therefore, understanding of the degree of chemical ordering in geopolymers, which will play a significant role in determining long-term chemical stability of these systems, is critical in the widespread utilisation. The notation introduced by Engelhardt et al. (1974) will be followed in this work, with Qn(mAl) (0 ≤ m ≤ n ≤ 4) representing a silicate centre bonded to n other centres, of which m are aluminium and (n-m) are silicon. Similarly, qn(m’Al) (0 ≤ m’ ≤ n ≤ 4) will be used to represent an aluminium centre coordinated to n other centres, of which m are aluminium and (n-m) are silicon. The vast majority of tetrahedral sites within a geopolymeric network have been observed by NMR to have cross-link density n = 4 (Rahier et al. 1996, Duxson et al. 2005). Therefore, n = 4 will be treated as constant throughout this investigation. 2. Model Development The standard starting point in analysis of short-range order in aluminosilicates is Loewenstein’s rule (Loewenstein 1954), which states that no two aluminium ions can occupy the centres of tetrahedra linked by one oxygen. This ‘rule’ is often assumed to be obeyed strictly in aluminosilicate structures. However, there is no firm thermodynamic basis for strict application of aluminium avoidance, but rather an energetic preference towards avoidance of Al-O-Al bond formation. Theoretical calculations have shown that this tendency is due primarily to the exothermicity of the reaction (1) both in solution and in the solid state. Si - O - Si Al - O - Al 2 Si - O - Al (1) Free energy minimization considerations may therefore be used to interpret the observed tendency towards Al-O-Al avoidance in aluminosilicate structures. The energy penalty associated with formation of Al-O-Al bonds in solution is believed to be responsible for the observed short-range ordering in hydrothermally synthesised aluminosilicates (Catlow et al. 1996). Increasing temperature has been shown to increase the extent of disorder (Gordillo & Herrero 1992, Lee & Stebbins 2000), and this must also be reflected in any model formulation. The basic formulation of the model presented here was originally applied by Efstathiadis et al.(1992) to ordering within an amorphous Si-C-H alloy. Here, the model will be presented on a 2-component basis, describing the ordering of tetrahedral SiO 4/2 and AlO-4/2 centres within an aluminosilicate network. The choice of this particular model was largely determined by the fact that all other existing models for Al-Si ordering rely on an understanding of the network topology. This is currently unavailable for geopolymeric materials due largely to their X-ray amorphous nature, meaning that more complex models cannot yet be applied to this system. As was noted previously, the energetic basis of chemical ordering in geopolymers is due primarily to the exothermicity of Equation (1). The heat released by this reaction is dependent on several factors including the cations present and the positions of the centres within the network structure. This energy is therefore treated as a model parameter denoted and defined by Equation (2), where E(I-O-J) represents the energy of a bond linking tetrahedral centres I and J = 2E(Si - O - Al) - E(Si - O - Si) - E(Al - O - Al) (2) is known to be relatively independent of x (Bosenick et al. 2001). However, will depend on the nature of the charge-balancing cations present, and this will be considered in the application of the model to the different geopolymers under investigation. Next-nearest neighbour (NNN) effects have been calculated to contribute approximately ±20% to the value of (Palin et al. 2001). However, incorporation of this effect causes significant complications in modelling and it is therefore often neglected. For the sake of simplicity, NNN effects will not be considered explicitly in this model, but rather will be discussed later as a potential source of error. The Gibbs free energy of mixing (network formation), G M, may be expressed in terms of the entropy and enthalpy of mixing: GM = HM – TSM (3) The entropy of mixing is given by the Boltzmann equation, Equation (4): SM = kB ln (4) where is the number of distinct states the system may occupy. is then given approximately by SiAl, where I is the number of possible configurations of tetrahedral sites containing framework cation I (Onabe 1982, Efstathiadis et al. 1992). Due to the equivalency of each of the 4 bonds linked to a given tetrahedral site, Equations (5) and (6) for Si and Al respectively may be obtained. These expressions relate to a system containing N tetrahedral sites, N(Si) = xN of which are silicon and N(Al) = (1-x)N are aluminium, with NI,J defined as the concentration of centres of type I bonded via I-O-J bonds to sites of type J (Efstathiadis et al. 1992). It must also be noted that NAl,Si = NSi,Al . N Si ! Si N Si,Si ! N Si, Al ! 4 N Al ! Al N Al,Al ! N Si, Al ! (5) 4 (6) Substituting Equations (5) and (6) into Equation (4) and simplifying by use of Stirling’s approximation, Equation (7) is obtained. This expression is given in terms of the ‘normalised bond concentrations’ nI,J of each type of bond (Efstathiadis et al. 1992), where nI,J = NI,J/N(Si), and is asymptotically correct in the limit of large N(Si). 1 x x S M 4k B N Si nSi,Si ln nSi,Si nAl,Al ln nAl,Al 2nSi,Al ln nSi,Al ln x 1 x (7) The enthalpy of mixing for a system of N atoms may be expressed in terms of heats of formation of free tetrahedra H0(I) and bond energies E(I-O-J) by Equation (8). 1 x H 0 MAlO 4 / 2 2nSi ,Si E Si O Si 4nSi , Al E Si O Al x 2n Al , Al E Al O Al ] (8) H M N Si [H 0 SiO 4 / 2 Equations (3), (7) and (8) may then be combined to give an expression for G M in terms of the normalised bond concentrations. Differentiation with respect to nSi,Si, with the observation that n Al , Al 1 and nSi, Al 1 , then allows the use of Equation (2) to n Si,Si n Si,Si replace the combination of E(I-O-J) terms from Equation (8) by . Setting G M 0 nSi,Si and simplifying then gives Equation (9). nSi2 , Al nSi,Si n Al , Al exp 2k BT (9) Combining Equation (9) with a mole balance (Equations (10) and (11)) and solving algebraically, Equation (12) is obtained. This is an analytical expression for the degree of Si-O-Al bonding in terms of x, , and T. A geopolymer synthesis temperature of 40°C is used throughout this work. nSi,Si + nSi,Al = 1 (10) nSi,Al + nAl,Al = 1 x x (11) nSi,Al 1 exp x 2k BT 2 1 2 exp 2 4 exp 1 x 2k BT 2k BT 1 2 exp 2k BT (12) Equations (10)-(12) may then be used to calculate the total number of each type of bond present in the system for any given x, and . This allows the calculation of the geopolymer composition in terms of tetrahedral centres Q 4(mAl) and q4(mAl). Application of a random bond distribution model (ie. neglecting NNN effects) then allows the calculation of FSi(m) and FAl(m), the fraction of all tetrahedra present that are Q4(mAl) and q4(mAl) respectively, as presented in Table 1. The coefficients 1,4,6,4,1 are due to the equivalency of all possible different arrangements of m Al and 4-m Si centres around a given tetrahedral site, giving each value of m a degeneracy factor according to the binomial distribution (Yin & Smith 1991). Table 1. Tetrahedron fractions calculated from random bond distribution. Si sites FSi(m) Al sites FAl(m) Q4(0Al) xnSi4 ,Si q4(0Al) x4 n4 3 Si , Al 1 x Q4(1Al) 4 xnSi3 ,Si nSi, Al q4(1Al) 4 x4 n3 n 1 x 3 Si, Al Al , Al Q4(2Al) 6 xnSi2 ,Si nSi2 , Al q4(2Al) 6 x4 n2 n2 1 x 3 Si, Al Al , Al Q4(3Al) 4 xnSi,Si nSi3 , Al q4(3Al) 4 x4 n n3 1 x 3 Si, Al Al , Al Q4(4Al) xnSi4 ,Al q4(4Al) x4 n4 1 x 3 Al , Al Only silicon sites are directly observable by 29Si MAS NMR, so the calculated quantity available for comparison to experimental data will be F Si(m)/x, the fraction of the silicon present that is coordinated to m aluminium sites. In application of this model to the metakaolin-based geopolymer system, a correction for the unreacted material present must be made. Metakaolin has a layered structure, and so tends to preferentially release aluminium in the early stages of dissolution as the relatively weak Al-O-Al bonds are broken. Therefore, the remnant unreacted material, which is estimated to comprise approximately 10% of the total metakaolin added, will be somewhat dealuminated with respect to its original composition. An empirical correction assuming 90% reaction and a remnant metakaolin composition of x = 0.600 was therefore applied to the experimental data, and provides a very good fit of the model to the experimental data. The application of the model to the data of Duxson et al. (2005) is shown by Figures 1-3, for Na, K, and mixed Na/K systems respectively. Percentage of Si sites The energy penalty was found to be 40 ± 5 kJ/mol for Na systems and 30 ± 2 kJ/mol for K systems. The mixed (1:1) Na/K system was found to be adequately described simply by taking the mean value of the two endmembers, 35 kJ/mol. 100% Q4(0Al) 90% Q4(1Al) 80% Q4(2Al) 70% Q4(3Al) Q4(4Al) 60% 50% 40% 30% 20% 10% 0% Exp Model 0.535 Exp Model 0.589 Exp Model 0.632 Exp Model 0.669 Exp Model 0.699 xcorr Percentage of Si sites Figure 1. Comparison of model predictions to the data of Duxson et al. (2005) with compositions corrected for 10% unreacted metakaolin. Na geopolymers, = 40 kJ/mol. 100% Q4(0Al) 90% Q4(1Al) 80% Q4(2Al) 70% Q4(3Al) Q4(4Al) 60% 50% 40% 30% 20% 10% 0% Exp Model 0.535 Exp Model 0.589 Exp Model 0.632 xcorr Exp Model 0.669 Exp Model 0.699 Figure 2. Comparison of model predictions to the data of Duxson et al. (2005) with compositions corrected for 10% unreacted metakaolin. K geopolymers, = 30 kJ/mol. Percentage of Si sites 100% Q4(0Al) 90% 80% Q4(1Al) Q4(2Al) 70% Q4(3Al) Q4(4Al) 60% 50% 40% 30% 20% 10% 0% Exp Model 0.535 Exp Model 0.589 Exp Model 0.632 xcorr Exp Model 0.669 Exp Model 0.699 Figure 3. Comparison of model predictions to the data of Duxson et al. (2005) with compositions corrected for 10% unreacted metakaolin. Mixed (1:1) Na/K geopolymers, = 35 kJ/mol Table 2 provides a comparison between the predicted degree of Al-O-Al bond formation for geopolymers with x = 0.50 and the experimentally observed proportion of Al-O-Al bonds formed in glassy aluminosilicates of comparable composition. It can be seen from these data that the proportion of the relatively unstable Al-O-Al bonds in geopolymeric materials is much lower than is observed in glasses of similar composition. This expected also to be true at the higher Si/Al ratios which are of primary interest in a practical sense, but the difficulties inherent in experimentally identifying Al-O-Al bonds in high-Si systems mean that comparisons are most readily conducted in systems of relatively high Al content. Table 2. Proportions of Al-O-Al bonds present in different amorphous aluminosilicates Geopolymer composition (T = 40°C) KAlSiO4 Na0.5K0.5AlSiO4 NaAlSiO4 Glass composition (Tg ~ 780°C) NaAlSiO4 LiAlSiO4 Fraction Al-O-Al (Model predictions) 2.65 % 1.67 % 1.05 % Fraction Al-O-Al (Experimental, Lee & Stebbins 2000) 9.5 ± 0.5 % 10.6 ± 0.5 % It is also seen that the use of sodium as the charge-balancing cation within a geopolymeric structure gives the lowest extent of Al-O-Al formation of any system investigated. This may mean that sodium-containing geopolymers are the most appropriate for use in waste immobilisation, which is advantageous considering the high levels of sodium present in many low-level radioactive waste streams (Siemer 2002). However, much further work remains to be done in this area, particularly with regard to the relative reactivities and leachabilities of different alkali metal cations within the geopolymeric structure. 3. Conclusions A statistical thermodynamic model describing the ordering of tetrahedral Si and Al centres within an X-ray amorphous geopolymeric binder has been formulated, and shown to fit experimental data for metakaolin-based geopolymers. The need to minimise the presence of relatively unstable Al-O-Al linkages in materials used in radioactive waste immobilisation to prevent leaching of immobilised cations suggests that geopolymers may be a valuable tool in the treatment of radioactive waste streams, in preference to vitrification or simple encapsulation methods. References BAO, Y., KWAN, S., SIEMER, D. D. & GRUTZECK, M. W. (2003) J. Mater. Sci., 39, 481. BOSENICK, A., DOVE, M. T., MYERS, E. R., PALIN, E. J., SAINZ-DIAZ, C. I., GUITON, B. S., WARREN, M. C., CRAIG, M. S. & REDFERN, S. A. T. (2001) Miner. Mag., 65, 193. CATLOW, C. R. A., GEORGE, A. R. & FREEMAN, C. M. (1996) Chem. Commun., 1311. CHERVONNYI, A. D. & CHERVONNAYA, N. A. (2003) Radiochem., 45, 182. DAVIDOVITS, J. & COMRIE, D. C. (1988) Long term durability of hazardous toxic and nuclear waste disposals. In DAVIDOVITS, J. & ORLINSKI, J. (Eds.) Proceedings of Geopolymer '88 First European Conference on Soft Mineralurgy. Compeigne, France, Universite de Technologie de Compeigne. DAVIDOVITS, J. (1991) J. Therm. Anal., 37, 1633. DUXSON, P., PROVIS, J. L., LUKEY, G. C., SEPAROVIC, F. & VAN DEVENTER, J. S. J. (2005) Langmuir, In press. EFSTATHIADIS, H., YIN, Z. & SMITH, F. W. (1992) Phys. Rev. B, 46, 13119. ENGELHARDT, G., JANCKE, H., HOEBBEL, D. & WIEKER, W. (1974) Z. Chemie, 14, 109. GORDILLO, M. C. & HERRERO, C. P. (1992) Chem. Phys. Lett., 200, 424. KHALIL, M. Y. & MERZ, E. (1994) J. Nucl. Mater., 211, 141. LEE, S. K. & STEBBINS, J. F. (1999) Am. Miner., 84, 937. LEE, S. K. & STEBBINS, J. F. (2000) J. Non-Cryst. Solids, 270, 260. LOEWENSTEIN, W. (1954) Am. Miner., 39, 92. ONABE, K. (1982) J. Phys. Chem. Solids, 43, 1071. PALIN, E. J., DOVE, M. T., REDFERN, S. A. T., BOSENICK, A., SAINZ-DIAZ, C. I. & WARREN, M. C. (2001) Phys. Chem. Miner., 28, 534. PHILLIPS, B. L., KIRKPATRICK, R. J. & CARPENTER, M. A. (1992) Am. Miner., 77, 484. RAHIER, H., VAN MELE, B., BIESEMANS, M., WASTIELS, J. & WU, X. (1996) J. Mater. Sci., 31, 71. SIEMER, D. D. (2002) Mater. Res. Innov., 6, 96. YIN, Z. & SMITH, F. W. (1991) Phys. Rev. B, 43, 4507. Acknowledgements This work was funded through the Particulate Fluids Processing Centre, a Special Research Centre of the Australian Research Council.