The Influence of Metakaolin on Limestone Reactivity in Cementitious Materials

The Influence of Metakaolin on Limestone Reactivity in Cementitious Materials

Abstract

Recent studies have demonstrated that in the presence of limestone (CaCO3), carbonate-AFm phases (i.e., hemi- and/or mono-carboaluminate) may be stabilized at the expense of sulfate-AFm, which is more commonly found in cement systems. This suggests that enhancing AFm phase formation may be a novel way of incorporating increased quantities of limestone as a reactive component in cementbased systems. Often, in an ordinary portland cement (OPC), the quantity of the AFm hydrates formed is limited by the availability of aluminum. Therefore, as means of enhancing AFm phase formation, this paper evaluates metakaolin addition to determine how it affects limestone reactions and carbonate-AFm formation in the OPC systems. The results of a multi-method study including: X-ray diffraction with Rietveld refinement (QXRD), strength measurements, thermogravimetric analysis, and thermodynamic calculations are used to quantify solid phase constitutions, and the extent of limestone that has been consumed in reaction. Obtained results suggest that pozzolanic reactions which occur when metakaolin is used as an aluminous source are observed to be beneficial in offsetting the dilutive effects of OPC replacement noted in blended cement formulations.


CO2 pressures facing the construction industry are providing an increasing impetus to reduce the use of ordinary portland cement (OPC) as the primary binder phase in concrete [1]. Towards reducing OPC use, emphasis has been placed on replacing OPC with supplementary cementitious materials (SCMs) in the form of: fly ash, blast furnace slags, silica fume, etc. [2, 3]. While capable of providing suitable properties, quantities of common SCMs available to replace OPC, are often, especially at local scales, inadequate to satiate the desired OPC replacement demand [4]. Due to concerns of the limited/localized availability of SCMs, there is interest in using limestone (CaCO3), an abundant mineral, to reduce the clinker factors of OPC, and thus OPC use in concrete. The replacement of OPC by limestone induces a variety of effects ranging from: (a) dilution and strength reduction [5, 6], to (b) accelerated hydration at early ages that results from the socalled filler effects [7]. Of these effects, dilution, i.e., the reduction in strength that accompanies OPC replacement is a considerable issue, as technologically this is the most significant limitation which has ensured that, in practice, OPC replacement by CaCO3 remains limited [8]. OPC is comprised of four main phases tricalcium silicate (C3S), dicalcium silicate (C2S), tricalcium aluminate (C3A) and the ferrite (C4AF) phases, wherein the kinetics of hydration of each phase differs from the others1 [9]. Hydration of the C3A in the presence of sulfate ions, provided by gypsum (CSH2), forms ettringite (C6AS3H32; AFt) at early ages and the monosulfoaluminate (C4ASH12, SO4-AFm, Ms), at later ages when gypsum is exhausted. However, in cases where carbonate ions may be present, e.g. as provisioned by the dissolution of limestone, C3A reacts with such species to form the CO3-AFm phases instead of SO4-AFm and ettringite is stabilized to accommodate sulfate ions [10– 12]. In general, monocarboaluminate (C4ACH11; Mc) forms when there is an abundance of the (calcium) carbonate source present, and hemicarboaluminate (C4AC0:5H12; Hc) forms in the case of carbonate-deficient conditions [12]. In typical OPCs, the aluminate (mainly C3A) phase content is regulated by governing standards [10]. This ensures that the extent of CaCO3 that can react in a typical OPC is quite small and in the range of 2–5 % (by mass) [12]. As such, if it is desirable to increase CaCO3 reactivity and thus OPC replacement levels, it is necessary to enhance the quantity of aluminous phases that can provide sufficient Al (OH)4 − (aluminate) species, which under conditions of portlandite saturation would react with CaCO3 to produce the CO3-AFm phases. In this work metakaolin (MET) is evaluated as aluminous agent which can extend the limestone reactivity in portland cement systems.

Materials and Methods

An ASTM C150 compliant Type I/II ordinary portland cement (OPC) and commercially available limestone (nominally pure: >95 % CaCO3, d50 = 3 μm) were used. The oxide compositions of the OPC and metakaolin (MET) are presented in Table 1. A series of cementitious mixtures were prepared using de-ionized (DI) water at a fixed water-to-solids ratio (w/s = 0.45) as described in ASTM C305. The series of mixtures produced comprised of: (a) plain OPC, pastes in which: (b) 30 % of the OPC is replaced by limestone2 (c) 5-to-15 % of the OPC is replaced in 5 % increments by MET (d) 5-to-15 % of the OPC is replaced in 5 % increments by MET and an additional 30 % of the OPC is then replaced by limestone. Compressive strength measurements were carried out at 90 days using cubic specimens (50 mm × 50 mm × 50 mm) cured at 25 ± 1 °C in lime water as described in ASTM C109 [8]. For thermal analysis (TG/DTG) a Perkin Elmer STA 6000 thermal analyzer with a Pyris data acquisition interface was used to determine solid phase quantities in cementitious mixtures. To arrest hydration, solvent exchange was as described by Zhang and Scherer [13]. Quantitative X-ray diffraction analyses were carried out on powdered cementitious mixtures at desired ages using a Bruker D8 Advance diffractometer using Cu-Kα (λ = 1.54 Å) radiation. Care was taken to minimize preferred orientation errors by texturing the sample surface, and using a rotating sample stage. Xray structure information for the relevant anhydrous and hydrated crystalline phases was sourced from standard databases or from the literature [14, 15]. Rietveld analysis was carried out using the X’Pert HighScorePlus© [16]. Thermodynamic calculations were carried out using a geochemical speciation code, GEMS-PSI: version 2.3.1 [17]. Thermodynamic data of solid and aqueous species are sourced from the GEMS-PSI database, and amended with additional information relevant to cementitious systems [12]. Calculations were performed under conditions of 1 bar, 25 °C and CO2-free air.

Results and Discussion

As showed on Fig. 1, the replacement of OPC by metakaolin results in improved strength. Such beneficial effects of metakaolin addition, have also been highlighted by Vance et al. [18, 19] and Antoni et al. [20] and attributed to the pozzolanic character of metakaolin, and the formation of the Hc/Mc phases. This is significant in that in spite of very substantial reductions in the cement factor (CF), mechanical properties near equivalent to the pure OPC mixtures can be achieved. Figure 2 shows representative DTG traces at 90 days, and the portlandite content normalized by the cement factor (CF) for metakaolin containing mixtures. It is noted that portlandite contents of a given mixture decrease with increasing OPC replacement by metakaolin, even when dilution is accounted for. This is indeed expected due to the pozzolanic nature of metakaolin, which would consume lime to form a low(er) Ca/Si (and potentially higher Al-substituted) C-S-H phase which ensures that metakaolin containing mixtures show reduced decreases in compressive strength, in spite of the substantial OPC replacement. Figure 3 shows XRD patterns for the metakaolin containing mixtures after 90 days of hydration. It is noted that the portlandite content of a given mixture, in both limestone deficient/excess cases, reduces with increasing metakaolin content. Mc exists as the dominant phase, only when excess limestone is added to the system.

When only limestone intrinsic to the OPC (limestone deficient system) is present, Mc is stabilized only when no metakaolin is added. However, when OPC is replaced by metakaolin, in increasing proportion, Hc is stabilized as stable and dominant phase. This is in line with the observations made by Antoni et al. [20] and Vance et al. [18, 19]. Contents of the CO3-AFm (i.e., Hc/Mc) phases, reflect trends in limestone consumption. More CO3-AFm phases form with increasing metakaolin content, and when excess limestone is present. It should be noted that while these trends follow evolutions in the equivalent CO2/Al2O3 ratio, limestone reaction is limited, likely on account of its low dissolution rate. In spite of the near consumption of portlandite, e.g., in the 15 % metakaolin mixture containing excess limestone, strӓtlingite is not observed in the XRD patterns. It was noted that ettringite is present in both the deficient and excess limestone cases, wherein the release of sulfate ions, due to preferred CO3 2− ion uptake into the AFm phase, stabilizes ettringite in these systems. Figure 4 shows volumetric phase assemblages, calculated using GEMS, for 15 % OPC replacement by metakaolin in either limestone deficient or excess conditions. The systems presented show (determined by the portlandite match-point from TGA data) a degree of metakaolin reaction of 37 and 31 %, in limestone deficient and excess scenarios respectively. Due to pozzolanic reaction, metakaolin ensures consumption of lime and increased formation of C-S-H formed, albeit, of a lower Ca/Si ratio and potentially also higher Al substitution. In agreement with XRD data, both C2ASH8 and Hydrogrossular phases are not predicted to form for relevant levels of metakaolin reaction. In contrast to the observations herein, XRD data of Antoni et al. [20] showed the presence of C2ASH8 and portlandite in coexistence with each other. While this is in violation of thermodynamic phase relations established by Damidot et al. [21], it may be on account of the somewhat higher metakaolin contents used in their study, or inhomogeneous reaction zones. This discrepancy could however, also be on account of uncertainties in determination of solubility data, small variations in which could alter stability fields dramatically. For example, as noted in the simulations shown herein (Fig. 4), strӓtlingite is predicted to form only when portlandite is consumed. When only limestone intrinsic to the OPC is present (see Fig. 4a), at low levels of metakaolin reaction, Mc is stabilized. With the passage of time and increase in metakaolin reaction the phase relation changes and Hc becomes dominant with Mc existing as the minor CO3-AFm phase. For the degree of metakaolin reaction ascertained herein, Mc and Hc appear to exist in equivalent volumetric quantities, though on a mass basis this would translate to a larger quantity of Mc (the denser CO3-AFm phase), in contrast to the XRD data shown in Fig. 3. While this may indicate that the ascertained degree of metakaolin reaction is lower than reality, it may also suggest kinetic restraint in the formation of Hc, from the Mc, Ms and portlandite (or vice versa depending on the chemical environment). When excess limestone is present, Mc is predicted to be the dominant AFm phase (Fig. 4b). This is once again in contrast to the XRD observations in Fig. 3, where even under limestone excess conditions, when (15 %) metakaolin is present, Hc and Mc are noted to coexist; the reasoning for which is discussed above. It is seen that, at any degree of metakaolin reaction, a large quantity of limestone remains unreacted, ensuring modest levels of Hc/Mc formation. This leads to the idea that the compensation in mechanical properties (see Fig. 1), produced by the combined replacement of OPC, by limestone and metakaolin, is dominantly on account of the pozzolanic nature of metakaolin and less due to the formation of CO3-AFm phases.

Conclusions

Metakaolin was evaluated in blended binder formulations in terms of its ability to enhance the reaction of limestone in cementitious systems. Such enhancements in limestone reaction are provoked by systematic manipulation of the binder chemistry, e.g., in terms of the SO3/Al2O3 and CO2/Al2O3 ratios of the binder. It is noted that in spite of the provision of sufficient aluminium, calcium and water, the extent of limestone reacted is limited, mostly on account of its low reactivity (i.e., dissolution rate, and solubility). Due to reasonable (reactive) aluminum content metakaolin has shown to increase limestone reactivity and resulting formation of the CO3-AFm (hemi- and/or mono-carboaluminate). On the account of its pozzolanic nature, it is also effective at ensuring strength equivalence, or improvement (in spite of reductions in the OPC content) as compared to the pure OPC formulations.

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