Shiju Joseph
Özlem Cizer- Civil Engineering Department, KU Leuven, Leuven, Belgium
Optimizing the mix composition of alkali-activated materials is sometimes overwhelming due to the higher number of potential parameters that could be varied compared to designing a mix based on Portland cement. The present work focuses on understanding the correlations between compressive strength, bound water content, and heat release from the calorimeter. Different slag and fly ash proportions are studied at two different solution-to-binder (S/B) ratios. Alkali solutions are made with 5 M NaOH and water glass to have a final silica modulus of 1.28. Results indicate that, at similar S/B ratios, mixes with high amounts of slag develop high compressive strength corresponding to high bound water contents until 28 days and high heat release until 7 days. A good correlation exists between compressive strength with cumulative heat release and bound water content when the water-to-solid ratio of the initial mixture is also considered. These findings promise a less tedious method that could be employed to optimize the process for the mix design of alkali-activated materials.
Introduction
Portland cement has been the standard binder in the global use of concrete in construction for more than a century. As a result, cement production contributes to a large share of manmade emissions and environmental footprint due to the massive volumes of concrete production worldwide. One of the many possible routes (Juenger et al., 2011) to reduce its detrimental impact is the use of alkali-activated materials (AAMs) in concrete with desired engineering and durability performance in specific applications (Roy, 1999; Provis and Deventer, 2014; Pachego-Torgal et al., 2015; Provis, 2018). This class of binders, studied considerably in the past decades, generally uses supplementary cementitious materials (SCMs) as precursors. These SCMs are mostly industrial by-products such as blast furnace slag and coal combustion fly ashes. While several other possible SCMs are available, the sheer quantity available on a global scale (Snellings, 2016) and the significant amount of research conducted on these materials make these two the most favorable choices for AAM. SCMs are hardly reactive while mixed with water. Hence, strong alkalis such as sodium hydroxide (NaOH) and/or water glass (sodium silicates, Na2O.nSiO2) are needed for their activation as a binder.
Blends of blast furnace slag and fly ash have increased popularity that could complement each other. Blast furnace slag is highly reactive (Puligilla and Mondal, 2013), and fly ash can greatly improve the workability of the mixes owing to its spherical morphology (Kutchko and Kim, 2006). It is often reported that blends with slag and fly ash provide better mechanical performance than with blast furnace slag alone (Wardhono et al., 2015). Nevertheless, beyond a certain limit (typically 20%–35%), the replacement of slag with fly ash typically negatively affects the mechanical strength (Kumar et al., 2010).
One of the major criticisms of AAM on its ability to reduce the carbon footprint is the fact that they require large volumes of blast furnace slags to achieve comparable mechanical properties with Portland cements without high temperature curing at early ages. While almost all of the blast furnace slag produced globally is currently used to produce blended Portland cement, the carbon footprint cannot be solely reduced with this technology (Scrivener et al., 2018). In contrast, blast furnace slag usage in AAM further promotes the usage of other SCMs, which do not have sufficient reactivity to be used in Portland cement-based systems (Li et al., 2018; Skibsted and Snellings, 2019; Suraneni et al., 2019), which can be blended with slag to be efficiently activated with high concentration alkalis. Furthermore, there are many other niche applications where AAM could be more beneficial and efficient than Portland cement systems (Provis and Bernal, 2014; Luukkonen et al., 2019).
One of the major challenges in optimizing the mix composition of AAMs is the vast number of parameters that seriously impact the fresh and hardened properties. While the water-to-cement ratio (W/C) and temperatures are the major factors that govern the properties of Portland cement-based composites, AAMs are further dependent on the composition of the activators, including the type of the activating solution (e.g., NaOH, Na2O.nSiO2, Na2SO4, and Na2CO3), its molar concentration (which varies with the water-to-binder ratio), ratio of activators, and total amount of activators. Some studies have also investigated the possibility of improving the properties using additives such as reactive MgO and alkali activators (Jin et al., 2014; Fei et al., 2015).
Although recently more studies have focused on the usage of near-neutral activators (Rashad et al., 2013; Bernal, 2016; Mutti et al., 2020), sodium silicate-based activators are still more common because of the higher strength they impart. The composition of the sodium silicate solution has a considerable effect on the kinetics of the reaction. Increasing the silica modulus (Ms = SiO2/Na2O) without changing the Na2O content increases the induction period, reduces the pH of the pore solution, reduces the early age strength, and typically increases the later age strength. The optimal composition of sodium silicate solution typically ranges from 0.75 to 1.5 Ms for maximum strength (Wang et al., 1994). The optimal total Na2O content for maximum strength further depends on the slag and fly ash used as well (Marjanović et al., 2015).
Furthermore, as SCMs are generally waste products, their chemical and mineralogical composition often varies quite a lot depending upon the source, and such changes in the composition of the precursors could alter the hydration products (Gong and White, 2016; Jin and Stephan, 2019). Furthermore, the fineness of the material, which significantly affects the kinetics of the reaction and the overall degree of hydration and strength development, mostly introduces another variability factor. Hence, the optimization challenge for these AAMs with respect to the fresh and hardened properties, also considering the economic point of view, is sometimes overwhelming and expensive.
This work aims to investigate the link between heat release, bound water content, and compressive strength so that the screening process, which needs to consider different factors, will be less tedious. In this work, heat release from isothermal calorimetry and bound water content determined from the thermogravimetric analysis is compared to the mortar compressive strength. The effects of different slag and fly ash ratios and solution-to-binder ratios are discussed.
Experimental Protocol
The oxide compositions of the primary raw materials, ground granulated blast furnace slag, and coal combustion fly ash determined from X-ray fluorescence are reported in Table 1. The fineness of these materials determined using laser diffraction (Malvern Mastersizer 2000) is shown in Figure 1 Alkali solutions were prepared using 99% pure sodium hydroxide pellets and sodium silicate solution (Na2O 8.3%, SiO2 27.5%). The activating solution of silica modulus (Ms) of 1.28 was prepared with 50% 5 M NaOH solution and 50% sodium silicate solution.
TABLE 1. Oxide composition of slag and fly ash.
FIGURE 1. Particle size distribution.
The different mixes used at various slag/fly ash ratios are tabulated in Table 2. Two sets of solution-to-binder ratios (S/B) were used, at a constant S/B ratio (of 0.7) and a varying S/B ratio, which give similar flow ( ∼ 200 mm) for mortars prepared with river sand (0–2 mm) following the mixing protocol as described in EN 196–1. Although the fineness of fly ash is much higher compared to slag, the addition of fly ash considerably reduces the amount of solution required to achieve a similar flow. This should be attributed to the ball-bearing effect of the spherical fly ash particles. All mix compositions were prepared at a fixed alkali modulus (SiO2/Na2O = 1.28).
TABLE 2. Mixes used in this work. S: solution; B: binder, w: water; s: solid.
The compressive strength for the different mixes listed in Table 2 was measured on mortar beams following the protocols from EN 196–1. Compressive strength was measured at 3, 7, and 28 days for all mixes, and additional measurements at 90 days were carried out only for the mixes at an S/B ratio of 0.7. The heat release from pastes was recorded using TAM Air 8 channel isothermal calorimeter at 20°C for 7 days of hydration. The pastes were mixed in a temperature-controlled room at 20°C and then transferred to 20 ml ampules of the calorimeter. Therefore, the initial data of ∼ 45 min after mixing are not considered in the data of cumulative heat release, including the initial ∼ 15 min for mixing and placing in the calorimeter and the next 30 min measurement to achieve thermal stability in the calorimeter. Thermogravimetric analysis (TGA) was performed on pastes at 3, 7, and 28 days for all samples and at 90 days for samples with an S/B ratio of 0.7. TGA was carried out after hydration stoppage using a freeze dryer (0.025 mbar, −60°C, 2 h) without the initial pre-freezing with liquid nitrogen. Approximately 25–40 mg of ground samples (Joseph and Cizer, 2020) was used for thermogravimetric analysis (TGA) using NETZSCH STA 409 PC at a heating rate of 10°C/min for a temperature range of 20°C–600°C with a nitrogen atmosphere (60 ml/min flow rate).
Results and Discussion
Heat Release From Isothermal Calorimetry
Figure 2 compares the heat release measured from isothermal calorimetry for all the mixes. As previously reported, hydration of NaOH activated slag results in the main peak between 1 and 24 h while sodium silicate-activated slag exhibits a relatively long induction period and the main reaction peak only after 2 days (Shi and Day, 1995; Haha et al., 2011; Haha et al., 2012). Nevertheless, similar cumulative heat of hydration is achieved in both cases. In our case, where the slag is activated with a mixture of NaOH and sodium silicate solution, the main hydration peak is observed after 5 h. Hubler et al. (2011) attributed this main peak to be derived from nucleation and growth of C-S-H based on nucleation seeding experiments.
FIGURE 2. Rate of heat release measured from isothermal calorimeter for all mixes listed in Table 2.
With a decrease in the amount of slag and an increase in the amount of fly ash in the mixes, we observe a later occurrence of the main hydration peak with a lower intensity. In other words, relatively shorter induction periods and narrower peaks are observed with increasing slag content. This is attributed to the higher reactivity of slag over fly ash, particularly to the fast reaction of the very fine slag particles during early hours, which increases silicate concentration and thereby supersaturation with respect to C-S-H (Gruskovnjak et al., 2006). An increase in the induction period with the addition of fly ash is often reported for Portland cement and C3S (Deschner et al., 2012; Joseph et al., 2017b; Schöler et al., 2017). Mixes with 25% slag (S25F75_0.7 and S25F75_0.52) and without slag (S0F100_0.7 and S0F100_0.52) do not show a distinctive peak within 7 days. The lower heat release with a broader peak and the longer exothermal activity imply slower hydration of the slag-fly ash mixes leading to a lower early-age compressive strength (c.f. Compressive Strength section).
An interesting finding is the earlier occurrence of the main peak of hydration at lower solution-to-binder ratios. A slight decrease in the induction period and a faster occurrence of the main peak of alite hydration are often reported for Portland cement and C3S systems at low W/C ratios (Thomas, 2007; Hu et al., 2014; Joseph et al., 2017a). The faster occurrence of the main hydration peak in our samples with slag and fly ash may be due to the variations of alkali concentrations in the solution. We explain this based on two assumptions:
1) With the progress of the reaction, there is more consumption of silicate ions compared to OH− ions from the alkali solution;
2) The degree of reaction and microstructure formation for mixes at different S/B ratios are identical till the acceleration period;
It is known that the increase in pH of the pore solution accelerates the occurrence of the main hydration peak (Altan and Erdoǧan, 2012; Gebregziabiher et al., 2015) due to the increased dissolution of slag and fly ash, which is strongly dependent on the pH (Song and Jennings, 1999). Although the initial concentrations are the same with different S/B ratios, there are higher amounts of alkalis (c.f. Table 2) and higher water content in the overall system with a higher S/B ratio. Hence, at the same degrees of reaction, the concentration of silicates in the pore solution would be lower for the mix with a lower S/B ratio. In that case, the system’s pH would be higher for mixes with a lower S/B ratio as the silicate ions induce lower pH compared to the OH− ions. Nevertheless, further study is required to explore this issue in more detail.
Figure 3 shows the cumulative heat released measured until 7 days of reaction. Mixes with higher amounts of slag exhibit higher heat release as expected, owing to its faster reaction kinetics. The heat release is almost similar with respect to the change in the S/B ratio, although it is slightly higher for mixes with a higher S/B ratio. This difference is more pronounced for mixes with a higher volume of slag than those with a lower volume of slag, which is attributed to the increased consumption of alkalis at higher degrees of reaction and lower amount of alkalis in the initial mix composition at lower S/B ratios (c.f. Table 2). Nevertheless, it is remarkable that the deviation is almost negligible for all the mixes at least till 1 day of reaction. It should be noted that the heat release within the initial 45 min of reaction has been omitted in the results because this is the time required from mixing to placing the samples in the calorimeter and the time required for the stabilization.
FIGURE 3. Cumulative heat release measured from isothermal calorimeter till 7 days for all mixes listed in Table 2.
Bound Water Content From TGA
Figure 4 shows the thermogravimetric data and DTG for all the mixes at a 0.7 S/B ratio after 28 days of reaction. In the hydrated alkali-activated slag (S100F0_0.7), two main hydration products are formed as detected in the TGA data: C-S-H (main weight loss at 50°C–200°C) and hydrotalcite-like phase (weight loss at around 200°C and 400°C), which is in agreement with the previous findings (Wang and Scrivener, 2003; Gruskovnjak et al., 2006; Haha et al., 2011). The mass loss from C-S-H consists of the water chemically bound to the structure of C-S-H and physically bound water (Köster and Odler, 1986). The broad peak of hydrotalcite at around 400°C remains almost the same in systems blended with fly ash up to 50%. Increasing fly ash contents beyond this ratio, this hydrotalcite peak becomes weaker. The C-S-H formed from slag hydration is characterized by a higher crystallinity, low Ca/Si ratios, and generally higher aluminum incorporation than that formed in OPC or blended OPC systems (Schneider et al., 2001; Wang and Scrivener, 2003; Gruskovnjak et al., 2006).
FIGURE 4. (A) TG and (B) DTG plots of mixes with an S/B ratio of 0.7 after 28 days of curing.
From the DTG data, it is noticeable that irrespective of the proportion of slag and fly ash, the profile of the rate of mass loss is similar. While more C-(A)-S-H type reactants are expected from calcium-rich slag-based systems, N-(A)-S-H type reactants are expected to form in low calcium fly ash-based systems (Garcia-Lodeiro et al., 2011). Previous studies also suggest that the dehydroxylation temperature of these C-S-H type gels occurs at similar temperatures (Winnefeld et al., 2010; Ismail et al., 2014). The peak of weight loss in activated fly ash without slag (S0F100_0.7) occurs at around 100°C and is much broader than the one reported by Winnefeld et al. (2010), who attributed this peak to sodium aluminosilicate hydrates. Incorporating the slag and increasing its content, this peak becomes much sharper.
Figure 5 shows the thermogravimetric (TG) data and the first derivative of TG (DTG) for S50F50_0.55 mix after 3, 7, 28, and 90 days of curing. Total mass loss is consistently increasing with an increase in age as expected. Most mass loss occurs before 500°C, indicating a C-(A)-S-H type reaction product (Sakulich et al., 2010). The nature of the peaks does not change over the course of the reaction, and they follow the same trend. As reported previously, alkali-activated slag-fly ash blends can demonstrate the co-existence of the C-A-S-H type gel and geopolymer gel (N-A-S-H) (Wang and Scrivener, 1995; Brough and Atkinson, 2002; Ben Haha et al., 2011; Ismail et al., 2014). The lack of a peak around 600°C–800°C confirms no significant degradation in the samples due to carbonation (Lothenbach et al., 2016).
FIGURE 5. (A) TG and (B) DTG plots of S50F50_0.55 at 3, 7, 28, and 90 days.
Figure 6 shows the total bound water content measured from TGA, corresponding to the mass loss between 20°C and 600°C (Lothenbach et al., 2016). With an increasing amount of slag, the bound water content is generally higher because slag exhibits a faster reaction than fly ash. This is noticeable at 3 days when the activated slag (S100F0_0.7) indicates the highest bound water content. However, after 7 days, this situation changes in favor of slag blended with 25% fly ash (S75F25_0.7), showing higher bound water content than activated slag. A striking difference is an increase in the bound water content with an increase in the S/B ratio. This is expected as there is a high amount of alkalis in the system (c.f. Table 2), which will continue to react with slag and fly ash. This difference is more pronounced at later ages due to the increased consumption of the alkalis.
FIGURE 6. Bound water content of the mixes from Table 2.
Compressive Strength
The compressive strength development of the samples listed in Table 2 is plotted in Figure 7. A lower S/B ratio consistently shows higher strengths than the same blends with a higher S/B ratio (Ruiz-Santaquiteria et al., 2012), most likely due to the lower porosity of the system when the S/B ratio is lower. At a similar S/B ratio of 0.7, the strength results are comparable with cumulative heat (Figure 3) and bound water content (Figure 6), particularly till 7 days.
FIGURE 7. Compressive strength of the mixes from Table 2 (part of the results were partially published in Uppalapati et al. (2017).
Regarding the sample S100F0_0.7, the strength does not increase significantly after 7 days. On the one hand, an increase in the bound water content is recorded until 90 days. This seems to be due to microcracking induced by shrinkage that can cause a strength loss (Collins and Sanjayan, 2001; Wardhono et al., 2015). On the other hand, there is a continuous increase in the strength of the other samples. In the early ages (3 and 7 days), samples with a higher proportion of blast furnace slag yield a higher strength which could be attributed to the higher reactivity of slag over fly ash. At 28 days, for the same S/B ratio of 0.7, the compressive strengths of S100F0_0.7, S75F25_0.7, and S50F50_0.7 are almost similar. Considering the samples with a similar flow, by 28 and 90 days, the samples with 25% and 50% slag replacement with fly ash (S75F25_0.6 and S50F50_0.55, respectively) have higher strength values than the one with 100% slag (S100F0_0.7). Compared to Portland cement, while the strength of 25% slag (S25F75_0.52) after 28 days is in the same range with CEM I 52.5 with a 0.5 W/C ratio, samples with higher percentages of slag are much superior even at higher S/B ratios. There are no surprises here as similar results are often reported in the literature (Puertas et al., 2000; Nath and Sarker, 2014; Fang et al., 2018).
Bound Water Content Versus Heat Release
Figure 8 compares the overall cumulative heat released per gram of binder measured from isothermal calorimetry with the bound water content measured from TGA after 3 and 7 days of curing. A good correlation exists with an R2 value of 0.97. The comparison could only be drawn until 7 days due to the lack of calorimetry data beyond 7 days. A remarkable outcome of this correlation is that irrespective of the amount of slag and fly ash in the current systems, the bound water content and heat release is proportional to each other, both being a good indication for hydrate formation. Nevertheless, there is an offset for the trend line amounting to around 56 J. Part of this could be due to the omission of heat release in the first 45 min. This needs to be addressed in detail in future studies by comparing the early age heat release with TGA (<3 days).
FIGURE 8. Comparison of cumulative heat released measured from isothermal calorimetry with the bound water content measured from TGA after 3 and 7 days.
Compressive Strength Versus Bound Water Content
Figure 9 compares the compressive strength with the bound water content determined from TGA. While the general trend can be captured, the correlation is slightly poor, with an R2 value of less than 0.7, due to the different S/B ratios that lead to differences in initial porosity. This is evident from Figure 6 and Figure 7, as a lower S/B ratio leads to a higher compressive strength but a lower bound water content. Hence, the mixes with the same S/B ratio of 0.7 are compared in Figure 10, which gives much better correlations (R2 of ∼ 0.9). The outlier S100F0_0.7 after 90 days of reaction is marked in Figure 10.
FIGURE 9. Comparison of bound water content with compressive strength for all mixes in Table 2.
FIGURE 10. Comparison of bound water content and compressive strength for mixes with an S/B ratio of 0.7. The point marked inside the red circle is the 90-day result of S100F0_0.7.
To consider the effect of the porosity while varying the S/B ratio, a new parameter
where BW is the bound water content in percentage and Ws is the water-to-solid ratio (W/S). The rationale behind selecting such a parameter is that this could consider the effect of initial porosity to a certain extent. A higher W/S ratio will contribute to a decrease in strength and vice versa. Such a parameter could mimic Schiller’s model (Schiller et al., 1971), where the increase in strength is correlated with the decrease in capillary porosity and initial porosity. An increase in bound water content corresponds to the hydrate formation and thereby reduction in total porosity.
A significant improvement in the correlation with an R2 of 0.88 is obtained when compressive strength is compared with
FIGURE 11. Comparison of compressive strength with
TGA is costly equipment, so an alternative route using an oven could be considered. The mass loss could be calculated for samples after arresting the reaction from a laboratory oven by keeping the sample at 600°C by taking the mass before and after placing it in the oven. Precautions need to be made with respect to the holding time, as the temperature displayed in the oven may not be the temperature of the material. Furthermore, there could be errors in measurements due to oxidation at high temperatures if an inert gas such as N2 is not used (Bernal et al., 2017).
Compressive Strength Versus Heat Release
This section compares the compressive strength with heat release from calorimetry till 7 days. Similar to the approach used in the previous section, to consider the effect of the S/B ratio, the parameter
where Q is the cumulative heat released measured from the isothermal calorimeter and Ws is the water-to-solid ratio (W/S).
Figure 12 shows a good correlation between the compressive strength and
FIGURE 12. Comparison of compressive strength with
Conclusion
This work studies different blends of alkali-activated slag and fly ash with isothermal calorimetry, thermogravimetric analysis, and compressive strength to understand the correlations between them. Ground granulated blast furnace slag and coal combustion fly ash at different proportions (100:0, 75:25, 50:50, 25:75, and 0:100) are used with two different solution-to-binder (S/B) ratios. A constant S/B ratio of 0.7 and a varied S/B ratio, which give similar mortar flow, were used. Alkali solution comprises 50% 5 of 5 M NaOH and 50% of water glass (sodium silicate solution).
The major conclusions of this study are as follows:
1) At similar S/B ratios, mixes with higher amounts of slag have higher compressive strength and bound water content till 28 days and higher heat release till 7 days.
2) Comparing mixes with similar flow and varying S/B ratios, fly ash replacement up to 50% has a higher strength than the mix with 100% slag. This is due to the ball-bearing effect of fly ash, which reduces the water demand to achieve similar workability.
3) The S/B ratio hardly affects the cumulative heat released till 1 day of reaction. On the contrary, there is a considerable increase in the bound water content with an increase in S/B, particularly at later ages.
4) A good linear correlation is obtained between bound water content and heat release measured from the calorimeter.
5) Compressive strength correlates well with cumulative heat release and bound water content when the water-to-solid ratio of the initial mixture is also considered.
Data Availability Statement
The original contributions presented in the study are included in the article/Supplementary Material, further inquiries can be directed to the corresponding author.
Author Contributions
SJ conducted the experiments, analysed the data, prepared the figures, and wrote the manuscript. ÖC acquired funding, supervised the study, and edited the manuscript.
Funding
This study was supported by the EOS-program under the fund grant No. 30439691.
Conflict of Interest
The authors declare that the research was conducted in the absence of any commercial or financial relationships that could be construed as a potential conflict of interest.
Publisher’s Note
All claims expressed in this article are solely those of the authors and do not necessarily represent those of their affiliated organizations or those of the publisher, the editors, and the reviewers. Any product that may be evaluated in this article, or claim that may be made by its manufacturer, is not guaranteed or endorsed by the publisher.
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Keywords: alkali-activation, blast furnace slag, fly ash, heat release, bound water, strength
Citation: Joseph S and Cizer Ö (2022) Comparative Analysis of Heat Release, Bound Water Content and Compressive Strength of Alkali-Activated Slag-Fly Ash. Front. Mater. 9:861283. doi: 10.3389/fmats.2022.861283
Received: 24 January 2022; Accepted: 15 February 2022;
Published: 21 April 2022.
Edited by:
Neven Ukrainczyk, Darmstadt University of Technology, GermanyReviewed by:
Marios Soutsos, Queen’s University Belfast, United KingdomZhenming Li, Delft University of Technology, Netherlands
Copyright © 2022 Joseph and Cizer. This is an open-access article distributed under the terms of the Creative Commons Attribution License (CC BY). The use, distribution or reproduction in other forums is permitted, provided the original author(s) and the copyright owner(s) are credited and that the original publication in this journal is cited, in accordance with accepted academic practice. No use, distribution or reproduction is permitted which does not comply with these terms.
*Correspondence: Özlem Cizer, ozlem.cizer@kuleuven.be