1. Introduction
In 1983 in Japan a problem related to the durability of structures intensively arose, due to the incomplete or excessive consolidation of the concrete. As a solution, in 1986 Okamura introduced the self-compacting concrete (SCC) with its essential ability of being compacted under its own weight without any mechanical or human effort [
1,
2,
3]. To achieve its enhanced properties, such as the high filling and passing ability, specific modifications in the mix design of the composition of SCC are required, compared to the conventional vibrated concrete (VC) [
2,
4]. The most widely accepted changes are related to the addition of modern active chemical admixtures and fine-grained fillers at appropriate proportions. The chemical admixtures mostly used are Super-Plasticizers (SP), which provide the mixture with high fluidity by decreasing the yield stress, and Viscosity Modifying Agents (VMA), which increase the robustness and the viscosity of the mixture [
5]. Fillers are added to the composition to reduce segregation and improve the microstructure of the concrete by optimizing the packing of the dry ingredients (i.e. cement and aggregates) [
6,
7,
8]. An important subject of scientific research is the type of filler, with parameters such as size, shape and chemical composition being the most critical. Rising number of research teams are trying to use industrial by-products as fillers to contribute to sustainability and greener constructions, utilizing materials that would potentially be air or soil pollutants [
7,
9]. Especially, when it comes to cement plants, thousands of tons of waste material are collected annually, making the need for their utilization imperative. In more detail, during the continuous feeding of kilns with raw materials for clinker production, large quantities of fine-grained material are trapped in the gases and removed by control devices, such as cyclones, bag houses or electrostatic filters [
10]. Their incorporation into concrete to partially replace cement or conventional fillers (such as limestone dust) constitutes a topic of increasing interest.
Wang et al., 2018 [
11], claimed that the addition of limestone filler to concrete can either have a positive or negative effect on the workability depending on the incorporation proportion, the particle size in comparison to the corresponding cement particles, or the MgO content; the increase of which enhances the viscosity of concrete. An increase in limestone powder may cause a decrease in the compressive strength of concrete due to the dilution effect of a high filler content, however at an optimum amount and size it can create a closer packing of the dry materials and thus increase the compressive strength. Limestone filler is considered to be a material of higher stiffness compared to concrete, which leads to a higher Modulus of Elasticity. Elyamani et al., 2014 [
6], compared the effect of different fillers on the rheological and mechanical properties of SCC. The non-pozzolanic fillers, such as marble dust, alleviated the phenomena of bleeding and segregation compared to pozzolanic fillers, such as silica fume and metakaolin, while the presence of marble dust decreases the water absorption. No significant alterations were observed in terms of compressive strength when comparing pozzolanic to non-pozzolanic fillers, however, the latter, although not involved in the hydration reactions, improved the microstructure of the cement paste with a positive effect on the bulk paste matrix and the transition zone. Sfikas et al., 2014 [
12], investigated the partial replacement of limestone filler or cement with metakaolin resulting in a higher demand for chemical admixtures, as the ratio of metakaolin-to-limestone powder or cement increased due to the higher specific surface area and the non-spherical shape of metakaolin particles.
Abukhashaba et al., 2014 [
13], used cement kiln dust (CKD) in fiber reinforced SCC and produced a sustainable SCC. However, due to the physical properties of CKD a higher demand of SP dosages required to achieve the desired rheological behavior. Siddique et al., 2006 [
14], claimed that the incorporation of CKD into concrete at an appropriate amount can have a positive effect on sorptivity and alkali-silica reactions, while it does not appear to adversely affect properties such as the compressive and flexural strengths. Bagheri et al., 2020 [
15], used CKD and fly ash in different proportions (0-40% and 0-30%, respectively) to produce a green concrete with improved fresh and hardened properties. Replacing 20% of cement with 5% of CKD and 15% of fly ash led to a higher compressive strength, while for mixtures with 20% or higher CKD the compressive strength decreased sharply. Maslehuddin et al., 2009 [
16], also investigated the mechanical properties and durability of concrete containing 0-15% CKD. Increasing CKD decreases the compressive strength of the concrete. Nevertheless, for 5% of cement replacement with CKD, the compressive strength and drying shrinkage were not affected significantly. Najim et al., 2014 [
17] claim that compressive strength decrease due to CKD incorporation could mainly be detected in cases of CKD with high free lime content, as free lime reacts with water and produces additional Ca(OH)
2 resulting in pores of higher volume and subsequently greater internal stresses leading to a decreased strength for the chemical compounds of CKD.
Viacava et al., 2012 [
18], produced medium strength SCC by replacing cement with CKD at ratios of 20% and 30%. They concluded that replacing cement with CKD improves the rheological properties effectively reducing the use of chemical admixtures. Specifically, for a 20% replacement of cement with CKD, the lowest segregation tendency and highest viscosity are observed from segregation and a V-funnel test respectively.
Ashteyat et al., 2018 [
19], produced five SCC compositions by replacing 0-25% cement with white cement by-pass dust (BPD) without facing any problem in terms of workability. Even when the compressive strength was sufficient, a scalable, according to BPD content, reduction occurred. The drying shrinkage as well as capillary porosity measurements showed a slight increase due to the incorporation of BPD. The porosity decreased when replacing 10% of cement with BPD, while the most encouraging result concerned the SCC resistance to alkali-silica reaction.
In almost all the afore-mentioned studies, a common approach is found for the mix design process, considering the specific by-products of clinker processing as supplementary cementitious materials (SCMs) and replacing cement in various percentages. The purpose of this paper is to investigate the possibility of utilizing two raw by-products of cement industry as fine filler materials of SCC; cement kiln dust (CKD) and by-pass dust (BPD) in comparison with a reference mixture containing only marble powder (MP), by designing two series of SCC mixtures of dissimilar water-to-cement ratio and filler content. The properties and the characteristics of CKD and BPD are governed by the clinker raw materials and the kilns’ layout details such as fuels and filters used. Therefore, the quality and the suitability of similar by-products for further use in the building sector should be evaluated by taking into consideration the specific process characteristics of each cement production plant. After the characterization of the fillers in terms of chemical composition, skeletal density and particle size distribution, compositions of concrete of high water-to-cement ratio and low cement content were produced. Properties of fresh and hardened concrete were studied. The analysis of the results on the rheological and mechanical properties, demonstrated a high potential of utilizing the examined by-products for sustainable SCC compositions.
Author Contributions
Conceptualization, A.K., E.B. and I.M.; methodology, A.K., E.B. and K.S.; validation, A.K., and E.B.; formal analysis, A.K.; investigation, A.K.; writing–original draft, A.K.; writing–review and editing, A.K., E.B., K.S., S.A.; visualization, A.K.; supervision, E.B.; project administration A.K. and E.B.; All authors have read and agreed to the published version of the manuscript.
Figure 1.
Particle size distribution of fine materials used.
Figure 1.
Particle size distribution of fine materials used.
Figure 2.
XRD patterns of CKD (top) and BPD (bottom): 1. Illite, 2. Kaolinite, 3. Larnite, 4. Quartz, 5. Calcite, 6. Anhydrite, 7. Albite, 8. Sylvite, 9. C3S 10. Wollastonite, 11. Dolomite, 12. Lime.
Figure 2.
XRD patterns of CKD (top) and BPD (bottom): 1. Illite, 2. Kaolinite, 3. Larnite, 4. Quartz, 5. Calcite, 6. Anhydrite, 7. Albite, 8. Sylvite, 9. C3S 10. Wollastonite, 11. Dolomite, 12. Lime.
Figure 3.
XRD patterns of cement: 1. C¬2S, 2. Calcite, 3. Gypsum, 4. C4AF, 5. C3S, 6. C3A, 7. Anhydrite.
Figure 3.
XRD patterns of cement: 1. C¬2S, 2. Calcite, 3. Gypsum, 4. C4AF, 5. C3S, 6. C3A, 7. Anhydrite.
Figure 4.
Chemical admixtures consumption in relation with rheological performance indices of each SCC mixture.
Figure 4.
Chemical admixtures consumption in relation with rheological performance indices of each SCC mixture.
Figure 5.
Compressive strength of each SCC composition at 7, 28 and 90 days.
Figure 5.
Compressive strength of each SCC composition at 7, 28 and 90 days.
Figure 6.
Correlation between the compressive strength (28 days) and the air content of the SCC mixtures.
Figure 6.
Correlation between the compressive strength (28 days) and the air content of the SCC mixtures.
Figure 7.
Modulus of Elasticity values of each SCC composition.
Figure 7.
Modulus of Elasticity values of each SCC composition.
Figure 8.
Tensile splitting strength of each SCC composition at the age of 90 days.
Figure 8.
Tensile splitting strength of each SCC composition at the age of 90 days.
Figure 9.
Flexural strength of each SCC composition at the age of 90 days.
Figure 9.
Flexural strength of each SCC composition at the age of 90 days.
Figure 10.
Indicative longitudinal sections of SCC cylindrical specimens.
Figure 10.
Indicative longitudinal sections of SCC cylindrical specimens.
Figure 11.
Free shrinkage for each SCC composition measured at 7, 14, 28 and 90 days.
Figure 11.
Free shrinkage for each SCC composition measured at 7, 14, 28 and 90 days.
Figure 12.
Correlation between drying shrinkage after 90 days and air content in the fresh SCC mixtures.
Figure 12.
Correlation between drying shrinkage after 90 days and air content in the fresh SCC mixtures.
Figure 13.
Mass loss and drying shrinkage for each SCC composition after 90 days of drying at 65% RH and 23°C.
Figure 13.
Mass loss and drying shrinkage for each SCC composition after 90 days of drying at 65% RH and 23°C.
Table 1.
Physical properties of the fine materials used.
Table 1.
Physical properties of the fine materials used.
Properties and size characteristics |
Cement |
MP |
CKD |
BPD |
Specific Gravity (kg/m3) |
3150 |
2700 |
2700 |
2800 |
Specific Surface Area (cm2/g) |
3470 |
12700 |
25000 |
5000 |
d10 (μm) |
4.74 |
1.44 |
1.13 |
12.95 |
d50 (μm) |
19.82 |
4.88 |
3.71 |
50.72 |
d90 (μm) |
57.41 |
12.27 |
14.66 |
115.63 |
Table 2.
Chemical analysis (w/w %) of the fine materials used.
Table 2.
Chemical analysis (w/w %) of the fine materials used.
Compound (%) |
Cement |
MP |
CKD |
BPD |
SiO2 |
19.02 |
0.35 |
10.18 |
19.39 |
Al2O3 |
4.59 |
- |
3.64 |
5.13 |
Fe2O3 |
3.63 |
0.07 |
2.06 |
3.46 |
CaO |
63.43 |
55.41 |
43.53 |
52.73 |
MgO |
2.02 |
0.76 |
1.31 |
2.22 |
MnO |
- |
0.01 |
- |
- |
SO3 |
3.48 |
- |
1.18 |
6.73 |
K2O |
0.47 |
- |
1.71 |
4.84 |
Na2O |
0.28 |
- |
0.37 |
0.46 |
P2O5 |
0.17 |
- |
- |
- |
TiO2 |
0.28 |
- |
- |
- |
Cl |
- |
- |
0.35 |
2.16 |
Loss of Ignition (LOI) |
2.62 |
43.4 |
35.65 |
2.88 |
Table 3.
Ingredients’ content (kg/m3) in SCC compositions produced.
Table 3.
Ingredients’ content (kg/m3) in SCC compositions produced.
Mixture |
Water |
Cement |
MP |
CKD |
BPD |
Sand |
g1 |
g2 |
w/c |
w/p |
REF1 |
180 |
300 |
200 |
0 |
0 |
900 |
560 |
240 |
0.60 |
0.36 |
CKD1 |
180 |
300 |
100 |
100 |
0 |
900 |
560 |
240 |
0.60 |
0.36 |
BPD1 |
180 |
300 |
100 |
0 |
100 |
900 |
560 |
240 |
0.60 |
0.36 |
REF2 |
198 |
300 |
250 |
0 |
0 |
900 |
525 |
225 |
0.66 |
0.36 |
CKD2 |
198 |
300 |
100 |
150 |
0 |
900 |
525 |
225 |
0.66 |
0.36 |
BPD2 |
198 |
300 |
100 |
0 |
150 |
900 |
525 |
225 |
0.66 |
0.36 |
Table 4.
Fresh SCC test results and chemical admixtures needed for each SCC composition.
Table 4.
Fresh SCC test results and chemical admixtures needed for each SCC composition.
|
SP/ Cement |
VMA/ Cement |
Unit Weight |
Air Content |
Slump Flow |
T500 |
V-Funnel |
U-Box |
L-Box |
Sieve Segregation |
Mixture |
(%) |
(%) |
(kg/m3) |
(%) |
(mm) |
(s) |
(s) |
- |
- |
(%) |
REF1 |
1.7 |
- |
2411 |
2.2 |
705 |
3.35 |
12.7 |
0.84 |
0.86 |
3.8 |
CKD1 |
2.4 |
- |
2365 |
2.5 |
700 |
2.50 |
22.8 |
0.79 |
0.87 |
1.3 |
BPD1 |
3.1 |
0.3 |
2403 |
1.8 |
690 |
5.60 |
28.5 |
0.77 |
0.50 |
1.5 |
REF2 |
1.5 |
- |
2256 |
2.9 |
690 |
1.59 |
5.1 |
0.93 |
0.88 |
7.5 |
CKD2 |
2.3 |
- |
2264 |
3.3 |
695 |
1.07 |
3.6 |
0.89 |
0.90 |
8.0 |
BPD2 |
2.7 |
- |
2358 |
1.5 |
700 |
2.82 |
15.3 |
0.78 |
0.71 |
2.2 |