1. Introduction
The production of Portland cement leaves behind an estimated global carbon footprint of 7-10% of the global emissions [
1]. This puts pressure on the global efforts to address climate change and other related environmental concerns [
2]. Using alternative binders to reduce the consumption of Portland cement in concrete constructions is considered as one of the viable options to a sustainable construction industry [
3,
4]. The most promising achievable option is through cement dilution, i.e. by replacing a fraction of ordinary Portland cement (OPC) with powders having different degrees of reactivity, the most commons being fly ash, ground granulated blast furnace slags, calcined clay and finely ground limestone. These filler materials may be inert or reactive in the cement hydration process [
3,
5]. When displaying some degree of reactivity in blends with OPC, they are commonly known as Supplementary Cementitious Materials (SCMs) and have the potential to reduce the amount of emitted CO
2 per unit mass of binder [
4]. With the various options in which these materials are utilized to produce the different concrete, the aspect of familiarity, versatility, strength, durability, wide availability, fire resistance, resistance to the elements, and comparatively low cost, remains key factors to be considered [
6]. The use of filler materials to substitute the clinker, considerably meets these requirements [
7].
Among the different possible approaches to the use of SCMs in blended cements, Limestone Calcined Clay Cement (LC
3) is a promising binder, with the potential to reduce global CO
2 emissions to the atmosphere by about 40% due to clinker replacing up to about 45% [
8,
9]. In its most common formulation, LC
3 incorporates 50 wt.% OPC clinker, 30 wt.% calcined clay (CC), 15 wt.% limestone (LS) and 5 wt.% gypsum (Gy). Several advantages have been reported from the pilot trials implemented across the world [
10,
11,
12]. According to [
13], high strength LC
3 binder comparable to OPC after 28 days can be produced with calcined clay having kaolinite content as low as 40%. This gives the considerable option of using impure kaolinitic clay in LC
3 production [
14]. Further, low-grade limestone can also be used [
15,
16,
17]. The synergy between limestone and calcined clay gives a great potential of reducing the clinker fraction to about 50% [
18]. Similarly, the lower demand for energy in production gives an advantage over OPC production. Optimal industrial temperatures not exceeding 900℃ are needed in the calcination process [
12,
19,
20]. Other studies also show a possible lower temperature requirement with higher pozzolanic activity when other mineral materials such as dolomite are co-calcined with clay [
14,
21].
Incorporation of other filler materials into similar ternary blends is also possible. This allows, for examples, industrial and agricultural wastes materials to be utilized. Such waste includes rice husk ash (RHA), broken fired bricks, and ceramic wastes among others [
22,
23,
24]. Previous studies also show that the filler materials such as limestone can accelerate the early rate of hydration [
2,
25,
26]. This effect can be accounted for by two phenomena: (1) the filler materials provide an increased surface area which then enables enhanced heterogeneous nucleation of the hydration products, and (2) enhanced water availability per unit mass of cement particles (i.e., w/c increase or dilution) [
27,
28,
29]. Improved early age properties therefore leads to better performance of the binder.
Generally, most of the studies have explored the incorporation of different types of filler materials in blended cements. Several concerns such as compromise in the performance of the cement due to poor development of cementing properties have been reported before, depending on the nature and amount of the additions [
30,
31]. Similarly, utilization of calcined clay and further extension of clinker substitution rates were hindered by such concerns [
32]. However, most challenges such as reduced workability, high water demand in concrete mixes, and delayed strength development can now be addressed by the use of superplasticizers and other admixtures [
33,
34,
35]. These recent advancements expand the scope of SCMs and fillers, and their utilization in blended cements. With this realization, a better understanding of the different fillers is possible. Further, potentially viable implementation of sustainable mixture designs can be optimized to allow increased substitution of the clinker fraction [
36,
37].
The present study aims at investigating the potential of utilizing “kunkur”, a nodular calcium carbonate rock formed in semi-arid regions, which is also commonly known as “caliche” or “calcrete”. These are naturally cemented soils formed due to evaporation of water containing dissolved calcium carbonate [
38]. They are composed of small calcite crystals, and other minerals that are commonly found in soils, and hence have found several applications in cement production and road construction [
39,
40,
41].
For example, in Kenya “kunkur” has been used in cement production [
42,
43]. However, the fines formed by quarrying of “kunkur” have not been so far utilized as they are considered wastes and are commonly stockpiled. However, due to the significant calcite content and its wide availability in specific locations, kunkur fines mat represent a suitable candidate for replacing primary limestone in ternary blends affine to LC
3 cement. This study therefore explored the potential of utilizing kunkur fines in achieving higher clinker fraction substitution and improved performance of LC
3 cement, using a Design of Experiments (DoE) approach.
Author Contributions
Conceptualization, J.M.M. and V.K.M.; methodology, J.M.M. and L.V.; formal analysis, V.K.M. and L.V.; investigation, V.K.M; resources, J.M.M and L.V.; writing—original draft preparation, V.K.M.; writing—review and editing, L.V., J.M.M. and C.M.M.; visualization, V.K.M. and L.V.; supervision, J.M.M., C.M.M. and L.V.; project administration, J.M.M., C.M.M. and L.V.; funding acquisition, J.M.M. and L.V. All authors have read and agreed to the published version of the manuscript.
Figure 2.
X-ray pattern of (top to bottom) kunkur fines, raw clay and calcined clay. A, C, K, Mi, Mu, and Q represent albite, calcite, kaolinite, microcline, muscovite and quartz.
Figure 2.
X-ray pattern of (top to bottom) kunkur fines, raw clay and calcined clay. A, C, K, Mi, Mu, and Q represent albite, calcite, kaolinite, microcline, muscovite and quartz.
Figure 3.
Particle size distribution curves of raw clay (RC) and kunkur fines (KF).
Figure 3.
Particle size distribution curves of raw clay (RC) and kunkur fines (KF).
Figure 4.
Isoresponse plots of the compressive strength at 2, 7 and 28 days of curing.
Figure 4.
Isoresponse plots of the compressive strength at 2, 7 and 28 days of curing.
Figure 5.
Experimental results for the cement paste and mortar samples compressive strengths at various curing days.
Figure 5.
Experimental results for the cement paste and mortar samples compressive strengths at various curing days.
Figure 6.
XRD pattern for the cement samples S1’, S2’ and S3’ at 2, 7 and 28 days of curing. C, CH, C3S, C2S, C3A, Ett, Hc, K, Mi, P and Q denote calcite, portlandite, alite, belite, aluminate, ettringite, hemicaboaluminate, kaolinite, microcline, and quartz respectively.
Figure 6.
XRD pattern for the cement samples S1’, S2’ and S3’ at 2, 7 and 28 days of curing. C, CH, C3S, C2S, C3A, Ett, Hc, K, Mi, P and Q denote calcite, portlandite, alite, belite, aluminate, ettringite, hemicaboaluminate, kaolinite, microcline, and quartz respectively.
Figure 7.
Pozzolanic activity of the cement paste at curing age 2, 7 and 28 days.
Figure 7.
Pozzolanic activity of the cement paste at curing age 2, 7 and 28 days.
Figure 8.
SEM-BSE images for samples S1’, S2’ and S3’ (the length of the white bar corresponds to 100 μm) and example EDS spectra acquired in matrix areas, representative of the hydration products composition.
Figure 8.
SEM-BSE images for samples S1’, S2’ and S3’ (the length of the white bar corresponds to 100 μm) and example EDS spectra acquired in matrix areas, representative of the hydration products composition.
Table 1.
Mix composition (wt.%) for the prepared cement blends.
Table 1.
Mix composition (wt.%) for the prepared cement blends.
Mix |
Clinker % |
KF % |
CC % |
GY % |
S1 |
55.0 |
15.0 |
25.0 |
5.0 |
S2 |
40.0 |
15.0 |
40.0 |
5.0 |
S3 |
40.0 |
30.0 |
25.0 |
5.0 |
S4 |
40.0 |
22.5 |
32.5 |
5.0 |
S5 |
47.5 |
22.5 |
25.0 |
5.0 |
S6 |
47.5 |
15.0 |
32.5 |
5.0 |
S7 |
45.0 |
20.0 |
30.0 |
5.0 |
S8 |
95.0 |
- |
- |
5.0 |
Table 2.
Mix composition (wt.%) for the prepared cement blends used for validation of the DoE model.
Table 2.
Mix composition (wt.%) for the prepared cement blends used for validation of the DoE model.
Mix |
Clinker % |
KF % |
CC % |
GY % |
S1’ |
41.0 |
16.0 |
38.0 |
5.0 |
S2’ |
42.0 |
26.0 |
27.0 |
5.0 |
S3’ |
45.0 |
18.0 |
32.0 |
5.0 |
OPC |
95.0 |
|
|
5.0 |
Table 3.
XRF chemical composition (wt.%) of the starting materials.
Table 3.
XRF chemical composition (wt.%) of the starting materials.
Chemical composition (w%) |
Clinker |
Calcined clay |
Gypsum |
Kunkur fines |
SiO2
|
21.3 |
59.26 |
7.2 |
52.32 |
Al2O3
|
6.3 |
29.49 |
1.26 |
9.55 |
Fe2O3
|
3.7 |
4.79 |
0.83 |
7.87 |
CaO |
62.2 |
0.74 |
29.54 |
14.49 |
SO3
|
1.5 |
- |
40.48 |
0.16 |
MgO |
3.9 |
2.13 |
0.28 |
3.22 |
K2 O |
1.0 |
2.37 |
0.31 |
1.13 |
Na2O |
0.4 |
1.21 |
- |
- |
Cl |
- |
- |
- |
0.01 |
L.O. I |
0.8 |
|
|
|