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Interfacial bonding characteristics between quartz sand supported nano-TiO2 functional aggregates and cement paste  PDF

  • WANG Gongxun 1,2
  • LI Xiong 1
  • DENG Jing 1
  • ZHU Mingqiao 1,2
  • QU Feng 1
1. School of Civil Engineering, Hunan University of Science and Technology, Xiangtan 411201, Hunan, P. R. China; 2. Hunan Engineering Research Center for Intelligently Prefabricated Passive House, Hunan University of Science and Technology, Xiangtan 411201, Hunan, P. R. China

CLC: TU528.01

Updated:2024-03-07

DOI:10.11835/j.issn.2096-6717.2022.002

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Abstract

Photocatalytic cement-based material is one of the research hotspots of advanced building functional materials, but TiO2 cement-based composites prepared by the traditional internal mixing method have low effective utilization rate of TiO2 and poor economic benefits. To solve this problem, cement mortar with quartz sand supported TiO2 (QST) aggregates were prepared and the effects of the QST aggregates on the drying shrinkage performance of the cement mortar was studied. The interfacial bond strength between the QST aggregates and the cement stone was measured using the pull-out strength method. The effects of the nano TiO2 on the hydration products and pore structure of the interfacial transition zone (ITZ) between the aggregates and the cement stone were studied via SEM, EDS and MIP methods. Compared with ordinary quarz sand aggregates, the QST aggregates can reduce the drying shrinkage of the cement mortar and improve the interfacial adhesion between the aggregates and the cement stone. The nano TiO2 that was loaded onto the surface of the aggregates promotes the hydration of the cement paste, reduces the enrichment of Ca(OH)2 in the ITZ, and refines the pore structure of the ITZ between the cement stone and the aggregates.

1 Introduction

Photocatalytic properties of nano-TiO2 have important and practical significance for air pollution control [

1], therefore, photocatalytic cement-based materials represent a critical industrial opportunity. Nowadays, many researchers have focused on the photocatalytic properties of nano-TiO2 cement-based materials used in buildings and pavement [2-5]. Some investigations have concentrated on the effects of the photocatalyst environment, such as humidity [6], and illumination intensity of photocatalytic efficiency [7]. Similarly, the effects of nano-TiO2 on the hydration of cement have also been studied [8-10]. Despite the effectiveness of TiO2 as a photocatalyst, its use in practical applications is relatively small. The common application method in construction is to mix nano-TiO2 directly into the cement paste or concrete in Fig.1(a) [11-14]. Since photocatalysis is a surface phenomenon, influenced by the chemistry of the immediate environment, the photocatalytic effects of nano-TiO2 can only be effectively activated under exposure to ultraviolet radiation [15-16]. When TiO2 is covered by cement, only a small portion of the TiO2’s surface is exposed in the surface layer. This results in a waste of the utilization and economic effectiveness of the relatively expensive nano-TiO2. The concrete surface must be engineered to maximize the photocatalysts accessibility (to reactants) and activation (illumination); therefore, increasing the effective exposure area of the nano-TiO2 and improving the photocatalytic efficiency of the nano-TiO2. These are important means in order to solve the above problems and are also an important research direction for nano-TiO2 cement-based composite functional materials [17-19].

(a)  Conventional TiO2 dispersions in concrete

(b)  Surface-mounted TiO2-aggregate composites on photocatalytic concrete

Fig. 1  TiO2 mixed directly into the concrete and quartz sand supported TiO2 (QST)[

20]

Wang, et al.[

20] proposed a surface mounting for a functional aggregate loaded with nano-TiO2 in Fig.1(b) to address these problems. Their research focused on the preparation process and the photocatalytic performance of the loaded nano-TiO2 aggregate mortar. The results showed that the photocatalytic efficiency of the loaded TiO2 aggregate mortar is considerably higher than that of the traditionally dispersed nano-doped TiO2 mortar [21-22]. The embedding depth (exposed area) of the loaded TiO2 aggregates directly affects the photocatalytic efficiency and the bonding strength between the aggregates and the mortar [23-24].

Under normal service conditions, the interface between the loaded TiO2 aggregates and the cement stone may be considered the weak zone due to the influence of environmental factors such as moisture movement potentially leading to phase precipitation [

25], and expansive crystallization [26], through variations in temperature, humidity, freezing, and thawing [27-28]. Nano-TiO2 has no pozzolanic activity and does not directly participate in the hydration reaction of the cement [29-30]; however, its nano particles contain high surface area sites for the nucleation of cement hydration products promoting the hydration of cement, enhancing space filling, and indirectly influencing the bonding characteristics of the interface [31-34].

This work focuses on the bond properties of the interface between loaded nano-TiO2 aggregates and cement under the conditions of dry shrinkage, dry and wet cycle, and studies the microstructure of the interface region between the aggregates loaded with nano-TiO2 and the cement stone in order to better understand the role of nano-TiO2 on the interface between the aggregates and the cement.

2 Experimental details

2.1 Raw materials

The aggregates used as TiO2 supports are ISO standard sand (ISO 679:2009) produced from Leucate, France (designated FS). The particle size of the quartz sand is 1-2 mm. Titanium tetra-isopropoxide (TTIP, 99.9%), acetic acid (CH3COOH, 99.6%), absolute ethanol (C2H5OH, 99.9%), NaOH (sodium hydroxide, 0.1 mol/L), were purchased from Sigma-Aldrich. Deionized water (18.2 MΩ·cm) was used throughout the TiO2 hydrosol preparation process.

The sand and CEM I 52,5N (PC) used to produce the mortar conforms to BS EN 196-1 (BSI, 2005) and BS EN 197-1 (BSI, 2011), respectively.

2.2 Methods

2.2.1 Preparation of quartz sand supported TiO2 (QST) aggregates

The TiO2 hydrosol preparation process and the QST aggregate preparation followed the method previously described by reference [

11]. The main steps are summarized here. In order to activate the quartz surface, the sand aggregates were first treated with 0.1 mol/L NaOH for 24 h followed by washing with deionized water three times. The activated sands were then immersed in anatase TiO2 hydrosol suspensions for 5 minutes at room temperature. The resulting composites were then separated by filtration and dried at 105 ℃ for 30 minutes. The process above was repeated for the required 6 coating cycles. In the final step, all samples were dried at 105 °C for 24 hours, then washed three times using deionized water before the final drying step. In reference [11], Yang , et al. confirmed that the TiO2 loading increases with the number of coating cycles. This translates to a loading thickness (d) of up to 1 850 nm at a TiO2/SiO2 mass fraction of 0.61% after 6 coating cycles. Fig. 2 shows an SEM micrograph of the QST aggregates. TiO2 can be observed on the aggregate surface as agglomerated nano-TiO2.

(a)  QST

(b)  TiO2

Fig. 2  SEM images of QST and TiO2 supported on the surface of QST

2.2.2 Preparation of QST cement mortar

Portland cement-sand-water were mixed in a mass ratio of 1:3:0.5 according to the procedures described in BS EN 196-1:2005[

35]. Mortar samples with a size of 100 mm×50 mm×50 mm were prepared for the drying shrinkage test. The process to prepare the aggregate exposed mortar is as follows:

1) Aggregates were sprinkled onto a 50 mm wide adhesive tape to ensure a specific amount of single layer aggregates were mounted to each test sample, the coated sand was pre-laid onto a 100 mm long adhesive tape. Typically, this enables 9 g to 10 g of the coated sand to be mounted.

2) Aggregate mounting: the aggregate-coated tape was then placed onto the freshly as-cast surface of the mortar substrate and pressed into the surface under the load of a concrete block to give the specified aggregate exposure (via the depth of embedding). The samples were demoulded after 24 hours and cured under standard conditions in water for 7 days. The tape was then peeled off from the hardened mortar, leaving a single layer of aggregates exposed onto the top surface of the mortar samples.

2.2.3 Measurement

1) Drying shrinkage test of the mortar.

Length lx and mass mx of the samples prepared for the drying shrinkage test were measured at various ages (x days) under 20 ℃ and 50% RH condition; x is the curing day since the samples were moved into the curing room (x=0, 1, 4, 7, 14, 21, and 28).

2) Dry-wet cycle test of the mortar.

After applying the aggregate coating, the samples were demoulded after curing at 20 ℃ and 100% RH conditions for 24 hours, and further cured in water for 6 days. Then, the samples were dried at 20 ℃ for 24 hours and the copper heads were pasted onto the sample ends using Araldite resin. When the resin hardened after 30 minutes, the samples were moved to the curing room (20 ℃, RH=50%) and the initial length l0 and the mass m0 were measured before they were immersed in water at 20 ℃. The dry-wet cycle (immersion for 8 hours, followed by drying at 60 ℃ for 8 hours) was repeated 200 times, after which the final length and the mass of sample was measured.

3) Pull-out strength test between the QST aggregates and the cement paste.

Samples were dried at 20 ℃ for 24 hours before the pull-out strength test was performed, as follows: Araldite resin was applied to the mortar and test equipment dolly. The samples were scratched prior to pressing the mortar and the dolly together in Fig. 3. After the resin set, a direct tensile load was applied to measure the bonding strength between the aggregates and the cement paste. The loading rate of the pull-out strength test was 20 psi/s.

Fig. 3  Posi-Test AT-A instrument for pull-out test and dolly glued on the surface of mortar

4) Characterization.

The samples’ morphology was observed using a scanning electron microscope (SEM, Zeiss EVO MA10) equipped with an energy dispersive X-ray spectrometry (EDS, Oxford INCA) for elemental composition analyses.

The mercury intrusion porosimetry (MIP) method was used to analyze the pore structure of the cement paste samples via the equipment of the AutoPore Ⅳ 9510, Micromeritics. The boundary conditions of the pressure and the pore sizes of the MIP equipment are 0.10-61 000 psia and 5-300 000 nm, respectively.

3 Results and discussion

3.1 Drying shrinkage ratio

The potential effects of nano-TiO2 on the hydration process and pore structure in the ITZ of QST and cement paste, along with its super-hydrophilic properties, could have a significant impact on the water transport properties in the ITZ. However, another factor to consider is the consequences of the interfacial bonding strength between the aggregates and the mortar when considering the relative movement of the porous cement matrix and the dimensionally stable aggregates. Based on the influences of nano-TiO2 on the hydration properties of the cement-based materials, the drying shrinkage of the hardened cement paste has been investigated and discussed.

Fig.4 shows the variations in the sample’s mass of various mortar samples coated by French sand (FS) and quartz sand supported TiO2 (QST) aggregates. Fig.5 is the curve of the drying shrinkage rate of different mortar samples coated by French sand (FS) and quartz sand supported TiO2 (QST) aggregates.

Fig. 4  Curve between loss weight rate and curing time of mortar samples

Fig. 5  Curve between the drying shrinkage rate and the curing time of the mortar samples

It can be concluded that the weight loss of the FS mortar was higher than that of the QST mortar as shown in Fig.4. In Fig.5, the drying shrinkage rate of the QST mortar is smaller than that of the FS mortar. The results match that of Zhang, et al. [

36], which concluded that the addition of nano-TiO2 can reduce the water loss of the sample. Shimomura, et al.[37], Maekawa, et al.[38], and Shimomura [39], proposed a micromechanical model of drying shrinkage behavior, which was based on pore size distribution and thermodynamic behavior of the water within the pores. Part of the model involved computation of the parameter rs, defined as the radius of the pores where the meniscus forms, i.e., the pores whose radii are smaller than rs are assumed to be filled with liquid water while pores larger than this are dry. As the drying progresses, the parameter rs decreases. The researchers hypothesized that the smaller the parameter rs, the larger the capillary tensile forces at the meniscus (the interface between water and air), hence the higher the resulting shrinkage [40].

Drying shrinkage of cementitious materials may be due to a higher volume of mesopores causing a higher capillary stress of the water meniscus developed within the capillary pores of the paste, resulting in a higher level of drying shrinkage. Nano-TiO2 particles present pore refinement effects on the cement-based materials; thus, resulting in a much denser microstructure and a lower shrinkage value [

36,41].

3.2 Pull-out strength of the mortar

Pull-out strength of the FS and QST mortar under different curing conditions are shown in Fig.6.

Fig. 6  Pull-out strength of the mortar samples under different curing conditions

It is observed that the pull-out strength of the QST mortar is higher than that of the FS mortar during the standard curing and the drying shrinkage conditions; however, the contrary result is observed under the dry-wet cycle condition. Regarding the hygroscopic properties, the increase of TiO2 content leads to mortar with higher open porosity and water absorption coefficients [

42]. When the samples were in the dry-wet cycle conditions, the QST mortar absorbed more water and caused a higher open porosity in the bonding area between the QST aggregates and the cement paste; thus, lowering the bonding strength between the QST and the cement paste.

3.3 Microstructure analysis

3.3.1 SEM of the QST aggregates dropped from the surface of the mortar

Fig.7 shows the QST dropped from the surface of the mortar. Hydration products of the binding area between the QST aggregates and the cement paste can be observed by SEM in Fig.7(b) and (c).

(a)  QST mortar

(b)  QST contactarea

(c)  QST lost from mortar

Fig. 7  Diagram of QST dropped from the surface of the mortar

Fig.8 shows an SEM micrograph of a QST particle dropped from the surface of the mortar and focused on a region originally in contact with the mortar.

(a)  QST dropped from the surface of the QST mortar

(b)  Hydration products of Aft on the surface of QST

(c)  Hydration products of Ca(OH)2 on the surface of QST

Fig. 8  SEM images

Fig.8(a) shows a QST aggregate partially covered by cement hydration products. Nano-TiO2 agglomeration on the surface of QST is observed in Fig.2(a) and is not found in Fig.8(a), indicating that the bonded interface saturated the SiO2 surface. The chemical bonding strength between TiO2 and the quartz aggregates is stronger than that of TiO2 and the cement paste. Ti—O—Si chemical linkages are confirmed in the reference [

11], and TiO2 accumulation has been shown on the surface in multiple agglomerated layers. Many needle-like hydration products (AFt) are observed in Fig.8(b); it is deduced that the degree of cement binding with the surface of QST is high. This is due to the nucleation effect of the TiO2 accelerating the cement hydration process. In Fig.8(c), hexagonal plate hydration products are observed on the surface and are typical of Ca(OH)2. The size of these Ca(OH)2 plates and their proximity to each other suggest regions of fluid filled porosity prior to failure, in which the crystallization of Ca(OH)2 could have presented regions prone to cleavage and mechanical weakening.

Fig.9 shows an SEM micrograph and EDS of a vacated site on the mortar, originally occupied by a QST particle.

(a)  SEM image of hydration products of Ca(OH)2 in QST-dropping area

(b)  SEM image of QST-dropping area

(c)  EDS elements spectra of QST-dropping area

Fig. 9  SEM image and EDS elements spectra

Fig.9(a) shows the recess as well as the massive crystals formed by Ca(OH)2 and were observed on the cement coated QST surface. Fig.9(b) shows analytical locations and Fig.9(c) is the EDS elements spectra of the vacated area on the surface of the mortar. The primary elements within this area are Si, O, Ca, Al, and C with only a small quantity of Ti. It can be deduced that some TiO2 has debonded from the aggregates, indicating that the bonding strength between TiO2 and the quartz is not uniform (as previously indicated by Yang, et al. for coatings of various thicknesses) [

11]. In Fig.2(a), a non-uniform distribution of TiO2 on the surface of the quartz aggregates are observed, with the possibility of multiple TiO2 layers. In reference [11], Yang, et al. discussed the weaker binding of TiO2 in thicker layers but emphasizes the stability of the monolayer closest to the surface.

3.3.2 EDS of the ITZ between the aggregates and the cement paste

In order to identify the effects of the nano-TiO2 on the microstructure of the interface between the QST and the mortar, SEM images of the FS and the QST mortar were obtained. Fig.10 are the EDS spectra of the ITZ between the FS and the cement paste.

(a)  SEM image of ITZ between the FS and the cement paste

(b)  EDS elements spectra of ITZ-dropping area

Fig. 10  SEM image and EDS elements spectra of the ITZ between the FS and the cement paste

Fig.10(a) shows the interface and the surrounding regions indicating a significant separation between the FS and the cement. Some separation regions contain a Ca-rich brightly colored substance identified as CaCO3. It is proposed that Ca(OH)2 produced in the interface between the FS aggregates and the cement paste during the cement hydration process is readily carbonated within the open/porous microstructure.

Fig.11 shows the direction of a line-scanning analysis across the interface between the FS and the cement paste.

(a)  SEM image of the interface region between the FS and the cement paste

(b)  SEM image of gap between FS particles

(c)  the Si element content of the gap between FS particles

(d)  the Al element content of the gap between FS particles

(e)  the Ca element content of the gap between FS particles

(f)  the Ti element content of the gap between FS particles

(g)  the S element content of the gap between FS particles

(h)  the Fe element content of the gap between FS particles

Fig. 11  Line-scanning analysis of the interface region between the FS and the cement paste

Fig.11(a) shows the scanning line position and Fig.11(b) is a partially enlarged detail of the scanning line area. The microstructure of the gap between the FS particles is loose in Fig.11(a) and (b). The elemental profiles (Fig.11(c) to (h)) indicate the presence at the interface of the primary chemical constituents of the cement, indicating that the aggregates have been squeezed into the mortar forcing the extrusion of the cement fragments into the inter-aggregate region.

Fig.12 shows the direction of a line-scanning analysis made across the interface between the QST and the cement paste.

(a)  SEM image of the ITZ between QST and cement paste

(b)  SEM image of spectra areas

(c)  EDS elements spectra of 534 area

(d)  EDS elements spectra of 535 area

(e)  EDS elements spectra of 536 area

(e)  EDS elements spectra of 537 area

Fig. 12  SEM image and EDS elemental spectra of the ITZ between the QST and the cement paste

Compared to Fig.10(a), the ITZ between the QST particles and the cement paste is more compact in Fig.12(a) and (b). In Fig.10(a), a significant separation exists between the FS and the cement. In these separations, many pores and Ca-rich substances are identified as CaCO3 (in Fig.10(b))and were found between the FS aggregates and the cement paste. However, an enlargement of Area 1 (Fig.12 (a)) confirms a denser microstructure compared with the FS system within the interface region. A large content of Ti (Fig.12 (c) indicates a layer of TiO2 which is to be expected on the surface of the aggregates. In Fig.12(d), the content of Ti reduces significantly, Si increases, and the ratio of Ca to Si is minimal; thus, showing that the primary composition within this area is probably SiO2 as well as cement hydration products. The compositions in Fig.12(f) are similar to those in Fig.12(d). In Fig.12(e), Ti does not exist, the content of Si is significantly reduced, Ca increases, and the ratio of Ca to Si is high. It shows that the primary composition within this area is more than likely the cement hydration products.

Compared to Fig.11, the microstructure of the ITZ between the QST and the cement paste is more compact than that of the FS. The micrographs and the elemental analysis indicate a higher level of pore filling by the hydration products at the QST-cement paste interface region than in the FS system. It can be deduced that TiO2 coated on the surface of the aggregates improves the degree of hydration of the cement and makes the microstructure and the interface between the aggregates and the cement denser. Hence, the pull-out strength of the QST-cement paste is higher than that of the FS-cement paste under standard curing and drying shrinkage curing conditions in Fig.6. However, the contrary results under the dry-wet cycle conditions still need further investigation.

Fig.13 is the line-scanning analysis of the ITZ between the QST and the cement paste.

(a)  SEM image of the ITZ between the QST and the cement paste

(b)  SEM image of partially enlarged detail of the scanning line area

(c)  the Si element content of the gap between FS particles

(d)  the Al element content of the gap between FS particles

(e)  the Ca element content of the gap between FS particles

(f)  the Ti element content of the gap between FS particles

(g)  the S element content of the gap between FS particles

(h)  the Fe element content of the gap between FS particles

Fig. 13  Line-scanning analysis of the ITZ between the QST and the cement paste

Fig.13(a) shows the scanning line position across the QST particle and the ITZ. Fig.13(b) is a partially enlarged detail of the scanning line area. According to Fig.13(f), it can be concluded that a layer of TiO2 within the line-scanning range from 4 μm to 8 μm exists in Fig.13(b). It can again be concluded that the interface between the QST and the cement paste is filled with the hydration products of cement as seen in Fig.13. The white particle crossed by the scanning line has a high content of Ca, Al, and Fe, but a lower content of S, which is probably the hydration products of C4AF. The needle-like hydration products are AFt because they have a higher Ca, S, and Al content.

3.3.3 Mercury intrusion porosimetry (MIP)

The most probable and average pore sizes are important parameters of the cement pore structure and characterize the pore structure of the overall situation. The pore size distribution of the ITZ between the various aggregates and the cement paste is shown in Fig.14. Table 1 is the pore structural index of the ITZ of the QST-cement paste and the FS-cement paste.

Fig. 14  Pore size distribution of the ITZ between the QST, the FS aggregates and the cement paste

Table 1  Pore structural index of the ITZ of the QST-cement paste and the FS-cement paste
SampleMost Probable pore diameter/nmPorosity/%Average pore diameter/nmPore size distribution/nm
>20050-20020-50<20
QST 41.26 17.30 19.98 11.33 21.61 30.76 36.3
FS 50.33 14.48 23.12 14.0 17.49 30.33 38.18

It shows that the most probable pore diameter of the ITZ between the QST and the cement paste is approximately 41.26 nm, which is smaller than that of the FS. The total porosity of the QST-cement stone ITZ is 17.30%, which is higher than that of the FS-cement stone ITZ. However, the average pore diameter of the QST-cement stone ITZ is smaller than that of the FS. When the aperture is larger than 200 nm, the content of the macropores in the FS-cement ITZ is more than that of the QST. In the range of 50-200 nm aperture, the pore content of the QST- cement stone ITZ is more than that of the FS, indicating that the aggregate surface loading of TiO2 refines the pore size structure of the ITZ. The content of the macropores is reduced as well. Compared with the SEM images of Fig.10(a) and Fig.12(a), it can be concluded that the ITZ of the QST-cement paste is more compact than that of the ITZ of the FS-cement paste. The MIP test proves this result. Chen, et al. [

43] and others’ study has also shown that nano-TiO2 can significantly increase the hydration level during the initial hydration stage with small content. The nucleation effect of nano-TiO2 decreases the total porosity of the hardened cement paste, reducing the pore volume primarily occurring within the capillary.

4 Conclusion

(1) Weight loss and drying shrinkage of the FS mortar were higher than those of the QST mortar. Nano-TiO2 particles present a pore refinement effect on the cement-based materials resulting in a much denser microstructure and lower shrinkage value. Pull-out strength of the QST mortar is higher than that of the FS mortar during the standard curing and the drying shrinkage conditions; however, the contrary result is observed under the dry-wet cycle condition. Further investigation regarding this observation is needed in future research.

(2) The high Ca(OH)2 content and porous microstructure in the FS-cement ITZ reduce the bonding strength between the FS and the cement paste. The microstructure of the ITZ between the QST and the cement paste is more compact than that of the FS. TiO2 coated on the surface of the aggregates improves the degree of hydration of the cement and makes the microstructure dense as well as the ITZ between the aggregates and the cement.

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