Research Article | Open Access
Yunsu Lee, Mingyun Kim, Zhengxin Chen, Hanseung Lee, Seungmin Lim, "Chloride-Binding Capacity of Portland Cement Paste Blended with Synthesized CA2 (CaO·2Al2O3)", Advances in Materials Science and Engineering, vol. 2018, Article ID 5418930, 11 pages, 2018. https://doi.org/10.1155/2018/5418930
Chloride-Binding Capacity of Portland Cement Paste Blended with Synthesized CA2 (CaO·2Al2O3)
A chloride-binding capacity is the major factor to mitigate the ingress of chloride into concrete. This paper presents the chloride-binding capacity of Portland cement paste containing synthesized CA2 (CaO·2Al2O3). The CA2 was synthesized in the high-temperature furnace and characterized by X-ray diffraction for inspecting the purity. The synthesized CA2 was substituted for Portland cement by 0%, 5%, and 10% by weight, and the NaCl solution was used as an internal chloride, which is assumed as a total chloride. The chloride-binding capacity of cement paste was calculated from a water-soluble chloride extraction method by the application of the Langmuir isotherm equation. And the hydration products were analyzed using X-ray diffraction and thermogravimetric analysis. We demonstrate that the CA2 increases an AFm phase in the Portland cement system, and the incorporation of CA2 consequently enhances the chloride-binding capacity of cement paste samples.
Most modern structures are constructed using Portland cement as the primary material, but alternatives can be used, depending on specific environments. Calcium aluminate cement (CAC) exhibits excellent performance as a repair material, having higher early strength and a greater resistance against sulfate and abrasion than those of Portland cement [1–3]. CAC is also one of the materials that meet the global demand for reducing CO2 emissions .
CAC has a proportion of 40–80 wt.% Al2O3, higher than that of Portland cement which has 5–10 wt.% of Al2O3. CAC is also different from Portland cement in terms of the composition of the clinker. C3S (3CaO·SiO2) and C2S (2CaO·SiO2) are the major clinkers in Portland cement, whereas CA (CaO·Al2O3) is used in CAC. In particular, white CAC (with a proportion of Al2O3 greater than 70 wt.%) contains not only CA but also CA2 (CaO·2Al2O3) [1, 2].
As the hydration products of CAC generate problematic phase conversions (CAH10 or C2AH8 to C3AH6) depending on temperatures [3, 5], recent studies have focused on the improvement of the stability of CAC hydration products rather than the improvement of the strength of CAC binders [6–9]. CAC also has the drawback of reducing cost-effectiveness compared to Portland cement. As a result, studies on CAC incorporating Portland cement [10, 11], supplementary cementitious materials [8, 9, 12, 13], or chemical admixtures [9, 14] have been conducted to improve the stability and the durability of hydration products and economic benefits.
The hydration products of Portland cement blended with CAC are different depending on the ratios of Portland cement and CAC. If the proportion of CAC is more than 75%, calcium aluminate hydrates (e.g., CAH10, C2AH8, and C3AH6) are generated. In contrast, if the proportion is less than 25%, the AFm phase (e.g., C4AHx) is higher than that of hydration products in Portland cement paste [10, 15]. Based on the literature, this study focused on a Portland cement-based system with a proportion of CAC lower than 25%, as it resolves the problems of economic feasibility as well as improves the binding capacity of the harmful ions of the binder owing to the high proportion of the AFm phase [16, 17].
The AFm phase consists of a layered double hydroxide structure, where anions (e.g., OH−, CO32−, SO42−, and Cl−) are combined between positively charged layers of divalent and trivalent cations as shown in Figure 1. The AFm phase has a different chemical composition according to the temperature, humidity, and the proportion of anions in the surrounding environments [18–21].
If the concentration of chloride ions is high within the AFm phase in concrete, the compounds where chloride ions are fixed between positively charged layers of the AFm phase increase [19, 22, 23]. This can effectively delay the penetration of chloride ions into concrete, as it reduces the amount of free chloride. It is well known that anhydrous C3A (3CaO·Al2O3), C4AF (4CaO·Al2O3·Fe2O3), and AFm family, which generally consists of monosulfoaluminate (SO4-AFm), hydroxy-AFm (OH-AFm), and carbonate-AFm (CO3-AFm) in the Portland cement paste, reacts with chloride ions to form the bound chloride of the layer structure (Cl-AFm) [17, 22, 24–28]. However, as C3A, which plays an important role in the binding of chloride, is not suitable for mass concrete due to its high heat of hydration and low sulfate resistance, the proportion of C3A is limited [1, 2, 29].
In contrast, CA2 (a main clinker of the white CAC) is characterized by a low hydration reactivity and low heat of hydration . As CA2 generates a hydrocalumite-type AFm phase by reacting with Ca(OH)2 in the same way as C3A, it plays an important role in the uptake of chloride ions [31–33].
In this study, we examine the applicability of CA2, focusing on a performance evaluation of clinker CA2 prior to a study on the utilization of white CAC. Specifically, this study aims to determine the effect of CA2 on chloride-binding capacity within a Portland cement-based system. Therefore, Portland cement paste containing synthesized CA2 is employed. This study also evaluates the chloride-binding capacity of the synthesized CA2/Portland cement paste according to the amount of bound chloride and conducts a microanalysis on the hydrates.
2. Materials and Methods
2.1. Experimental Overview
CA2, the main material for this study, was synthesized in a high-temperature muffle furnace using industrial chemicals. The purity of the synthesized CA2 was analyzed using X-ray diffraction (XRD) and X-ray fluorescence (XRF).
After determining the purity of the synthesized CA2, we analyzed the chloride-binding capacity of binders, in which 0%, 5%, and 10% of the cement (by mass) was replaced by CA2. An aqueous solution of chloride ions was prepared by dissolving NaCl in the mixing water. The amounts of mixed chloride ions were 0%, 0.25%, 0.5%, 1%, 2%, and 3% of the binder mass. The cement paste was crushed at 28 days of curing, and the cement paste powder was analyzed via free chloride extraction, XRD, and thermogravimetric analysis (TGA).
2.1.1. Portland Cement
Type-1 ordinary Portland cement (Sungshin Cement, South Korea) was used, with the oxide composition analyzed via XRF. Table 1 presents the oxide composition of Portland cement.
2.1.2. Chloride Solution
Distilled water and a chloride ion solution were employed for preparing the cement paste. The chloride ion solution was made by mixing CP-grade NaCl (DAJEONG, South Korea) with distilled water.
2.1.3. Calcium Oxide and Aluminum Oxide
CP-grade calcium oxide (DAJEONG, South Korea) and aluminum oxide powders (DAJEONG, South Korea) were used to synthesize CA2.
2.3. Experimental Procedure
2.3.1. Synthesis of CA2
CA2 was synthesized by mixing combusting powders with calcium oxide (CaO) and aluminum oxide (Al2O3) in a high-temperature muffle furnace [30, 34]. Figure 2 shows the process of CA2 synthesis, in which the molar ratio of CaO to Al2O3 is 1 : 2. The substances were stirred sufficiently for homogeneity, and the mixed CaO and Al2O3 powder was combusted in a high-temperature muffle furnace with a heating rate of 5°C/min at a maximum temperature of 1550°C. The final substance was maintained at 1550°C for two hours and then cooled down to room temperature.
The synthesized CA2 was analyzed by XRD, XRF, and scanning electron microscope (SEM). The XRD and XRF were performed using a RIGAKU D/MAX-2500 with CuKα radiation of 100 mA and 40 kV, and the XRD measurement of the synthesized CA2 was conducted in a range of 5°–55° with a scanning rate of 4°/min. The SEM analysis used a TESCAN Mira3.
2.3.2. Fabrication of Cement Paste Samples and Microanalysis
Cement paste sample incorporating synthesized CA2 was prepared according to the mix proportions in Table 2, which shows 0%, 5%, and 10% (based on mass) of the cement being replaced by the synthesized CA2. The NaCl solution was used to evaluate the chloride-binding capacity of each cement paste. The chloride solution was prepared by mixing 0%, 0.25%, 0.5%, 1%, 2%, and 3% of binder mass with distilled water.
The cement paste samples were then sealed and cured at 20°C for 28 days. The samples were crushed after 28 days for the chloride extraction test and microanalysis. The crushed samples were immersed in acetone for stopping hydration and then dried at 40°C in a few minutes. The dried samples were crushed one more time to be filtered through a 150 µm sieve before use. The powdered samples were analyzed using XRD and TGA (CuKα radiation, 100 mA, 40 kV). The measurement was conducted in a range of 5°–60° with a scanning rate of 4°/min. TGA measurements were performed using the SHIMADZU DTG-60 instrument with approx. 40 mg of the powdered sample analyzed at a heating rate of 20°C/min in the N2 atmosphere.
2.3.3. Extraction and Detection of Soluble Chloride of Cement Paste
The extraction test for soluble chloride from the cement paste was conducted according to ASTM C1218 , and refer to existing studies [36, 37]. 1 g of a crushed sample was weighed and then added to 100 mL of distilled water, after which a chloride ion extraction test was conducted in a constant temperature bath at 60°C for five minutes. The sample was stabilized for 30 minutes, and then, the cement paste powder inside the aqueous solution was removed using a decompression filtration device. Obstacle factors from sulfide were removed from the filtered chloride ion solution using nitric acid (HNO3) and hydrogen peroxide (H2O2). Silver nitrate (AgNO3) was then used in potentiometric titration experiments. Figure 3 shows the free chloride extraction and detection tests.
The 1 g of powder was used for the free chloride extraction test, and the amount of soluble chloride was expressed by wt.% of the binder. The amount of bound chloride in each binder was calculated by subtracting the amount of measured water-soluble chloride from the total chloride content. The total chloride content was assumed to be the chloride content at the particular concentration that was added to the mixing water.
3. Results and Discussion
3.1. Synthesized CA2
The purity of the synthesized CA2 was measured by XRD and XRF analyses. Figure 4 shows the XRD results after performing Rietveld refinement using software Profex. The space group of CA2 is C12/c1, and its unit cell parameters are as follows: a = 12.89 Å, b = 8.89 Å, c = 5.44 Å, and β = 106.97°. The major three diffraction peaks of CA2 appeared at 19.90, 25.36, and 34.44 2-θ degrees, which correspond to the interplanar spacing of 4.46 Å, 3.51 Å, and 2.60 Å, respectively. The measured chemical composition of the synthesized CA2 was 89.4 wt.% of CA2, 6.6 wt.% of CA6, and 2.5 wt.% of CA. Although pure CA2 was not synthesized, the CA2 was still expected to have a significant effect on the properties of the cement paste unlike CA or CA6. This will be discussed in detail when the phase composition of an anhydrous binder is addressed. Table 3 presents the oxide composition of the synthesized CA2, and Figure 5 shows the SEM image of the synthesized CA2. The SEM analysis verified that the grain size of CA2 was approximately 5 µm.
3.2. Phase Composition of Anhydrous Binder
Table 4 gives the composition ratio of the clinker in each binder. Figure 6 presents the same data in a bar graph. The clinker composition of cement was calculated by applying the oxide composition of cement to the Bogue equation . The clinker composition ratio of CD5 and CD10 was calculated by considering the composition ratio of CA2 as calculated through the Rietveld analysis and using the mix ratio of the synthesized CA2 to the cement. As presented in Table 4, the ratio between CA6 and CA was calculated as 0.5 wt.% in CD5 and 1.0 wt.% in CD10; thus, the effect of CA6 and CA in each binder was expected to be minimal, while the effect of CA2 was expected to be significant.
3.3. Chloride-Binding Capacity of Cement Paste Mixed with Synthesized CA2
The bound chloride of the cement paste was calculated by subtracting the free chloride (as measured through the free chloride extraction test) from the total chloride. The bound chloride of the cement paste and free chloride results were curve-fitted by applying the Langmuir isotherm. A relationship between free chloride and bound chloride was evaluated by the Langmuir or Freundlich isotherm in general [17, 26, 39]. However, as various hydrates from cement-based materials, which contain various minerals, have their own chloride-binding capacity (differing from each other), it was difficult to evaluate the chloride-binding capacity for the cement paste . As the purpose of this experiment was only to approximate the chloride-binding capacity, only the Langmuir isotherm was applied. Figure 7 shows the relationship between bound chloride and free chloride, curve-fitted using the Langmuir isotherm. The Langmuir isotherm is expressed as follows:where is the bound chloride content and is the free chloride content; and are the binding capacity constants.
As shown in Figure 7, the highest chloride-binding capacity was for CD10, followed by CD5 and PC. This indicates that the higher the content of CA2, the higher the chloride-binding capacity. The effect of CA2 on chloride-binding capacity was similar to the effects of C3A, after the formation of the AFm phase in an environment with Ca(OH)2 [33, 40]. The change rate of chloride-binding capacity was larger in CD10/CD5 than CD5/PC. This indicates that the effect of CA2 on the binding of chloride ions was significant in an environment where chloride ions and Ca(OH)2 were present. This will be discussed in detail in Sections 3.4 and 3.5.
The blue dotted line in Figure 7 marks the result proposed in the study by Kim et al.  and indicates the result of chloride-binding capacity evaluated with the Langmuir isotherm according to the ratio of C3A in a Portland cement paste. As this was obtained at 56 days of curing and the water-to-binder ratio was 0.4 (different from the present study results), it cannot be compared directly with the present experimental results. However, it implies that CA2 had a strong effect on the chloride-binding capacity of paste, similar to the effect of C3A [40, 41].
Figure 8 shows the percentage of bound chloride and free chloride under the total chloride (the sum of bound chloride and free chloride). As shown in Figure 8, the bound chloride of PC continued to decrease from a 0.25 wt.% total chloride; however, the bound chloride of CD5 increased up to 0.5 wt.%, which subsequently decreased. The bound chloride of CD10 increased up to 1.0 wt.% and then decreased. The highest ratio of bound chloride to free chloride was for CD10 followed by CD5 and PC in all chloride conditions.
Bound chloride is a substance that is combined with chloride stably, even in an aqueous solution at 60°C. Thus, an increase in the content ratio of CA2 facilitated the production of bound chloride in a chloride-enriched environment. The XRD and TGA results, which will be discussed later, exhibit the main composition of the bound chloride that existed in the synthesized CA2/Portland cement paste.
3.4. XRD Patterns of Cement Paste Mixed with Synthesized CA2
Prior to the verification of the effects of synthesized CA2 on chloride binding in a chloride environment, hydration reactions of PC, CD5, and CD10 using only distilled water were conducted. Figure 9 presents the XRD patterns of PC, CD5, and CD10 as reacted with distilled water at 7 and 28 days.
As shown in Figure 9(a), all of PC, CD5, and CD10 showed the generation of Ca(OH)2 and a reduction in C3S and C2S. However, a CA2 pattern was not revealed in PC and CD5 at 7 days of curing, whereas a weak basal peak of CA2 (in which hydration reaction was not complete) was verified in the XRD pattern of CD10. The basal peak of CA2 completely disappeared at 28 days. The hydration rate of CA2, in which CaO/Al2O3 ratio was low, has been reported as low, but CA2 was completely dissolved after a few days .
As a pattern for CA2 was not observed at 28 days, it was assumed completely dissolved (as shown in Figure 9(a)). However, a previous study  proposed a situation, where only CA and CA2 were present, and further studies on the hydration of CA2 in the Portland cement-based system are required.
Figure 9(b) shows the enlarged graph of the XRD pattern between 5° and 20°, which shows a clear difference in patterns between 7 and 28 days, and 10° and 12°. The patterns of PC, CD5, and CD10 at 7 days did not show a clear peak between 10° and 12°; however, their patterns at 28 days showed a basal peak between 10.5° and 11.5°. The peak revealed between 10.7° and 11.5° was considered the basal peak of the AFm phase, which revealed a tiny shift between 10° and 12° according to the anion type in the interlayer (OH−, SO42−, CO32−, and Cl−) [19, 20, 23, 28].
Figure 9 shows the cement paste using distilled water, so an AFm phase mixed with OH−, SO42−, and CO32− at the interlayer was expected to be generated instead of chloride-AFm (Cl-AFm). The generation of OH-AFm, SO4-AFm, and CO3-AFm was determined by a comparison of the interplanar spacing of basal peaks amongst our XRD results as compared to those of existing study results [20, 28]. A peak at 11.5°, with an interplanar spacing of approximately 7.6 Å, was seen for PC, CD5, and CD10 at 28 days and was considered the monocarboaluminate peak. Furthermore, a peak at 10.7°, with an interplanar spacing of about 8.2 Å, was found in CD5 and CD10 at 28 days, which was determined to be the hemicarboaluminate peak.
Carbonation, which possibly occurred in the process of making cement paste power, could create mainly CO3-AFm. As mentioned above, a wide and continuous basal peak was seen (versus a well-defined peak). OH−, SO42−, and CO32− were seen to have an effect on the interlayer of the AFm phase complex. Without the carbonation effect, mainly OH-AFm was expected to be generated [10, 31, 32].
It was clear that the relative intensity of the main AFm phase peak was stronger at 28 days for CD5 and CD10 than for PC (as shown in Figure 9(b)). However, since no quantitative analysis was conducted using standard components, a change during the generation of the AFm phase cannot be deduced, but analyzed comprehensively using the TGA results. This will be discussed in Section 3.5. As the AFm phase was metastable, a phase change might occur according to the surrounding anion environment (as shown in Figure 9(b)), and the changes in the AFm phase could be verified by the XRD results.
Figure 10(a) shows the XRD patterns of PC, CD5, and CD10 binders, which were reacted with distilled water or chloride solution at 28 days. Figures 9(a) and 9(b) show an enlarged view of the main boundary from Figure 10(a) to compare the main peaks of Ca(OH)2 and the AFm phase. Figure 10(b) shows the difference between the AFm phase of PC, CD5, and CD10 using distilled water and chloride solution.
The AFm phase peak of PC, CD5, and CD10 mixed with distilled water was seen weakly between 10.7° and 11.5°, whereas the AFm phase peak of PC, CD5, and CD10 mixed with 1% and 3% chloride solution was seen strongly around 11°. The peak at 11° was verified as the main peak of Cl-AFm, which had a stronger relative intensity with the 3% chloride solution than the one with the 1% chloride solution. The highest relative intensity of Cl-AFm was for CD10, followed by CD5 and PC.
The synthesized CA2 was investigated to facilitate a formation of Cl-AFm in the Portland cement-based system. More specifically, the analysis showed that the type of Cl-AFm can vary according to the ratio of anion in the surrounding environment. In the Portland cement system, when sulfate is present, Kuzel’s salt mixed with Cl− and SO42− is typically seen in the interlayer of the AFm phase [19, 22, 28, 42]. Additionally, Cl-AFm is affected by OH− and CO32− such that a shift in a basal peak may be exhibited [19, 43]. The XRD peak with the 1% chloride solution was shifted more to the left than with the 3% chloride solution (from 11.1° to 11.0°, as shown in Figure 10(b)) due to the effect of CO32−, SO42−, and OH−.
Figure 10(c) shows a relative intensity of the major peak between the AFm phase and Ca(OH)2. The relative ratios of the XRD peaks equalize in the following order: CD10 > CD5 > PC. The relative ratios of the peaks became equal where the chloride ion concentration of the mixing water was high. The reduction in a relative intensity of the Ca(OH)2 major peak was due to the replacement of some cement with synthesized CA2, thereby decreasing the amount of generated Ca(OH)2 . This was because CD5 and CD10 generated more Cl-AFm phase than PC. This can be verified through TGA.
3.5. TGA Results of Cement Paste Mixed with Synthesized CA2
Figure 11(a) shows the DTG curve (offset) of each binder with various aqueous solutions. In general, the DTG curve of all types of the AFm phase revealed a similar peak. It has been reported that the DTG curve of pure Friedel’s salt or Kuzel’s salt showed that dehydration of the interlayer water was exhibited first between 100°C and 200°C, and then, dehydroxylation of the main layer water was seen between 200°C and 400°C [41, 42, 45, 46]. With the same aqueous solution, the mass reduction of CD5 and CD10 was larger than that of PC between 120°C and 400°C. The mass reduction of 3% Cl− PC, CD5, and CD10 (which had the highest chloride ion concentration) was the largest between 250°C and 350°C.
CD5 and CD10 were expected to have less generation of C-(A)-S-H than PC due to the reduction in C3S and C2S [44, 47], so the DTG peak for CD5 and CD10 between 120°C and 250°C was expected to be smaller than that of PC, but the opposite result was exhibited. This was due to the increase in the AFm phase generation in CD5 and CD10, where relatively more AFm phase was formed due to the synthesized CA2 mixed in the cement. For more detailed analysis, an offset of the DTG curve was removed.
Figure 11(b) shows the DTG curve between 120°C and 400°C without an offset. The change in mass reduction between 250°C and 350°C was more rapid in a more highly concentrated chloride aqueous solution, whereas the change in mass reduction between 120°C and 250°C did not exhibit a change due to the concentration of chloride. The change in mass reduction with a 1% chloride solution between 120°C and 250°C was larger than that of the 3% chloride solution. The major reason is due to the chemical composition of the interlayer in the AFm phase, although dehydration of various cement hydrates may have affected this as well . The reason for the higher change in mass reduction between 120°C and 250°C in a 1% chloride solution versus the 3% chloride solution is due to the higher ratio of water molecules, OH−, and SO42− that existed along with the Cl− at the interlayer as mentioned in the XRD results.
Figure 11(c) shows the DTG curve between 400°C and 600°C without an offset and is displayed to calculate the Ca(OH)2 content generated in PC, CD5, and CD10 for each aqueous solution. The peak shown between 400°C and 600°C was due to the dehydroxylation of Ca(OH)2. There was the shift of the peak to a lower temperature in high concentrations of chloride solution because chloride inhibits the hydrogen bond of Ca(OH)2 . The Ca(OH)2 content was calculated using integration of the DTG peak for Ca(OH)2, and a tangential integration method was employed [44, 49].
Table 5 presents the Ca(OH)2 content of PC, CD5, and CD10 for each aqueous solution. Overall, the Ca(OH)2 tended towards higher generation with a higher chloride concentration because NaCl mixed in the water facilitated dissolution of C3S . It is important that the production of Ca(OH)2 was noticeably reduced according to the increase in the content ratio of synthesized CA2 for the Portland cement system. The ratio of Ca(OH)2 generated in CD5 and CD10 was about 0.85 and 0.66 of PC, respectively. The main reason for this was the effective replacement of cement with CA2, which contributes to Ca(OH)2 generation. Furthermore, Ca(OH)2 may be consumed due to the formation of OH-AFm coming from the reaction of CA2 with Ca(OH)2 . The low pH environment from the increase of CA2 (in which ratio of aluminum oxide was high in the PC system) increased the dissolution of Ca(OH)2 to some extent .
It was conclusive that although the ratio of C-(A)-S-H and Ca(OH)2 reduced as the ratio of PC reduced, the highest chloride-binding capacity in CD10 was attributed mainly to the generation of the AFm phase. This result is consistent with exiting studies in which the AFm phase played a more important role than C-(A)-S-H and Ca(OH)2 in terms of chloride-binding capacity in the paste .
This study examined the effects of CA2 on the chloride-binding capacity of the Portland cement-based systems. And it is concluded that the synthesized CA2 contributes to the formation of the AFm phase in Portland cement paste, and CA2 plays an important role in the improvement of chloride-binding capacity in the synthesized CA2/Portland cement systems. The aforementioned results are summarized as follows:(1)Experiments were conducted using internal chloride to evaluate the chloride-binding capacity of a synthesized CA2/Portland cement paste. The bound chloride content was estimated using the Langmuir isotherm, and CA2 was determined to have significantly increased the chloride-binding capacity in the paste. In particular, the ratio between a bound chloride and a total chloride continued to increase with higher concentrations of chloride solution in the order CD10 > CD5 > PC. This indicates that the synthesized CA2 increases the chloride-binding efficiency of the paste.(2)The formation of Cl-AFm in 1% and 3% chloride solutions was in the order CD10 > CD5 > PC, and the results showed that as the chloride concentration became higher, the production of Cl-AFm increased. Furthermore, the major effect of OH−, SO42−, CO32−, and/or water molecules (other than Cl−) in the Cl-AFm interlayer composition was recognized.(3)The effect of synthesized CA2 on chloride binding for the Portland cement-based systems was observed using XRD and TGA. As the cement was replaced with synthesized CA2, the generation of Ca(OH)2 was decreased, while the generation of the AFm phase was increased at 28 days. As a result, it was concluded that CA2 contributes to the formation of AFm, which has higher chloride-binding capacity than Ca(OH)2. But the contribution was smaller in distilled water rather than chloride solutions.
Conflicts of Interest
The authors declare no conflicts of interest.
Yunsu Lee performed the experiments and wrote the paper. Mingyun Kim and Zhengxin Chen contributed to the preparation of experiments. Hanseung Lee and Seungmin Lim contributed to reviewing the discussion of the paper.
This research was supported by a grant (17SCIP-B103706-03) from the Construction Technology Research Program funded by the Ministry of Land, Infrastructure and Transport of the Korean government.
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