1. Introduction:
Ordinary Portland Cement (OPC) is a hydraulic binder manufactured in a rotary kiln whose raw materials contain adequate amounts of lime, silica, and, in smaller proportions, alumina and iron oxide [
1]. The mixture is first calcined at 900ºC, followed by a clinkering stage at 1450ºC, to allow the formation of alite (CaO)
3.SiO
2 and, in smaller amounts, belite (CaO)
2.SiO
2 [
1]. The produced clinker, with a density of ~3.1 g/cm
3 [
2], is then ground to an optimum particle size distribution [
3], obtaining a specific surface area that ranges from 3000 to 5000 cm
2/g [
4,
5,
6]. When in contact with water, OPC goes through an exothermic hydration reaction responsible for the material's strength development. This reaction can release more than 250 J/g of cumulative heat after 72 h of hydration [
7].
OPC is mainly used in the production of mortar (cement mixed with water and sand) and concrete (cement mixed with water, sand, and other coarse aggregates). Concrete is extremely resilient and durable, can bear heavy compressive loads, and resist severe environmental conditions, making it the world's most widely used construction material [
7]. The main factors that influence the compressive strength of concrete are hydration time, the type of cement used, and temperature and curing conditions [
1]. OPC is not only a widely used material with well-established manufacturing technology but is also a low-cost commodity, as it is made from raw materials abundant in the Earth’s crust (SiO
2 and CaO). Hence, due to these unique properties and the growing need for housing, services, and transport network development, cement consumption is expected to significantly increase in the next decade [
8].
Nevertheless, the production of OPC has a significant environmental impact. In fact, for each ton of clinker produced about 800 kg of CO
2 is concomitantly produced, which means that the production of one ton of OPC may result in the release of up to 540 kg of CO
2 into the atmosphere [
9,
10]. These CO
2 emissions result from to two main sources: CO
2 process emissions (CPE) and CO
2 energy emissions (CEE). CPE come from to chemical reaction involved in the decarbonization of limestone, while CEE are related to the burning of fossil fuel required for heating the cement kiln [
11].
Consequently, reducing the environmental impact of cement production has become an increasing concern. In the 2022 Energy Agency Report [
8], one of the thresholds to reach by 2050 was the “near-zero emission” of the cement industry, aiming for over 80% of reduction of the emissions, as compared to the present best available technology.
Nevertheless, the quest for carbon neutrality depends on the rapid scale-up deployment of alternative clinker technologies such as alkali-activated materials (AAM) [22] or low calcium hydraulic binders (LCHB), which may reduce CO
2 emissions by decreasing the amount of CaCO
3 used in their production [
12,
13,
14,
15,
16,
17,
18,
19].
LCHBs are materials rich in phases with lower calcium content than alite, such as belite, rankinite (CaO)
3(SiO
2)
2, or wollastonite CaO.SiO
2. Belite is a hydraulic phase but has a much slower hydration kinetics than alite due to its densely packed structure and lower solubility, lowering the compressive strength of the binder at early ages [
20,
21]. Both rankinite and wollastonite are non-hydraulically active, hence, binders rich in these phases usually go through a carbonation process instead of a hydration reaction [
19,
22].
In 2015, an alternative LCHB was developed and patented internationally [
12,
17]. The precursor idea involves the production of a material with a Ca/Si ratio of ~1, corresponding approximately to the chemical composition in which wollastonite crystallizes in equilibrium conditions [
13], but processed in a way that promotes the formation of an amorphous phase upon cooling instead of the crystalline one. In fact, it was shown that, by melting a mixture with a Ca/Si ratio of ~1 at a temperature between 1460 and 1550ºC, corresponding to the liquid or the liquid + pseudowollastonite zone, followed by a fast quenching, a material with hydraulic properties is obtained [
12,
13,
17]. This material is mostly amorphous (~94% wt%), with the presence of a small proportion of pseudowollastonite (<10%). The reduction of the calcium content of this material results in a decrease of more than 25% of the CPE, as compared to alitic clinkers [
10]. Moreover, the complete melting of this amorphous-wollastonitic low-calcium hydraulic binders (AWLCs) enables for the perspective of the full electrification of the production process [
10], which, theoretically, may result in “near zero” CEE emissions.
Several studies have been made to characterize the properties and hydraulic activity of AWLCs. The chemical composition and microstructure of AWLCs and its respective hydration products were determined using X-ray fluorescence (XRF), Nuclear Magnetic Resonance (NMR), Fourier-transform infrared spectroscopy (FTIR), X-ray diffraction (DRX), and High-resolution Transmission Electron Microscopy (HR-TEM) [
13,
23,
24,
25]. The hydration of the binder with water has been characterized by measuring the compressive strength of pastes at various ages [
17,
26,
27,
28], and its chemical reaction has been followed by using isothermal calorimetry and computational work [
29]. More recent works explored the impact of an alkaline activation of AWLC [
15,
30]. In the following points, the state-of-the-art review in what concerns the production, characterization, and optimization of AWLCs, as well for the the perspectives for future developments, is presented.
4. Alkaline activation of the binder
The use of alkaline activation to improve the compressive strength and performance of AWLC with a Ca/Si ratio of ~1.1 was studied by Santos
et al. [
15] and Mendes
et al. [
30]. The alkaline activators studied were Na
2CO
3, Na
2SO
4, CaSO
4, and a mixture of Na
2SiO
3 and NaOH. The main observation of these works was that the AWLC activated with Na
2SiO
3 solution presented, by far, better performances. When Na
2SiO
3 solution is used as an activator, the mechanical strength of AWLC can overcome that of OPC. In this way, in this review, we will refer only to activation with Na
2SiO
3.
Santos
et al. [
15], tested the compressive strength after 7. 28, and 90 days of hydration of pastes with a w/b of 0.375 activated with Na
2SiO
3. The compressive strength together with the evolution of the respective pseudowollastonite and tobermorite contents are shown in
Figure 10. Comparing these results with those of
Figure 7 for water hydrated pastes, it is observed that activation of the AWLC with Na
2SiO
3. May lead to an invrease of the compressive strength of up to 300%. Furthermore, the results indicate that the formation of tobermorite is related to the development of mechanical properties of the pastes [
14].
Since the degree of hydration (α) quantifies the extent of hydration of a binder over time, the experimental data from [
16] was used to calculate the degree of hydration between water-hydrated AWLC and Na
2SiO
3 activated AWLC. We have used the methodology proposed by Poole
et al. [
56], that calculated this parameter by the ratio of heat at each hydration time, H(t) with total amount of heat available H
max, α=H(t)/H
max. The results were compared with a typical Type I OPC in
Figure 11. The results in
Figure 11 indicate that when the AWLC binder is hydrated with water, the degree hydration remains below 0.1 for the first 100 hours. However, by activating the material with Na
2SiO
3., a considerable increase in the degree of hydration is observed, indicating an increase in the hydration kinetics allowing the formation of CSH/tobermorite structures particularly at earlier ages, as observed by HR-TEM, XRD-Rietveld (
Figure 5 and
Figure 6).
To reduce the amount of Na
2SiO
3 and optimize the Na
2O content in the hydrating solution, Mendes et al. [
30] used a Na
2O and Si/Na modulus of 1.2, followed by a successive reduction of 25%wt of Na
2SiO
3 until a combination of just NaOH and water was reached (0%. of Na
2SiO
3). The activation properties of each mixture were studied by calorimetry and compressive strength tests on pastes with a w/b ratio of 0.25. The calorimetric results and the compressive strength of each studied condition are shown in
Figure 12 and
Figure 13, respectively. The isothermal calorimetry analysis obtained by the authors showed a delay in the maximum hydration peak with the rise of Na
2SiO
3 on the activator. However, the increase of Na
2SiO
3 content also promoted a more controlled kinetic after the peak, consequently, these samples released more heat after 7 days of hydration. As a result, after 7 days of hydration, the amount of heat released increases with the increase of Na
2SiO
3 concentration. Compressive strength results on pastes activated with the studied solutions showed that the samples with a higher heat released originated higher compressive strength results at later ages.
Author Contributions
Conceptualization, R.C., R.B.H. and R.L.S.; methodology, R.C., M..A, R.L.S.; validation, R.C., R.B.H.; formal analysis, R.C., R.B.H., RLS.; investigation, M.A. and R.L.S.; data curation, M.A.; writing—original draft preparation, M.A. and R.L.S.; writing—review and editing, R.C., RBH.; visualization, R.C., R.L.S. and M.A.; supervision, R.C., R.B.H. and R.L.S.; project administration, R.C; funding acquisition, R.C. All authors have read and agreed to the published version of the manuscript.