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Article

Mechanical Properties of Glass-Based Geopolymers Affected by Activator and Curing Conditions under Optimal Aging Conditions

Department of Harbor and River Engineering, National Taiwan Ocean University, No. 2, Pei-Ning Rd., Zhongzheng Dist., Keelung City 202301, Taiwan
Crystals 2021, 11(5), 502; https://doi.org/10.3390/cryst11050502
Submission received: 9 April 2021 / Revised: 24 April 2021 / Accepted: 29 April 2021 / Published: 2 May 2021
(This article belongs to the Special Issue Advances in Cement-Based Composites and Novel Construction Products)

Abstract

:
Inorganic polymeric materials react slowly at room temperature and therefore, usually require high-temperature curing. This study determined the correlation between temperature and duration in high-temperature curing. The results revealed optimal values for each alkali equivalent of an activator (weight ratio of Na2O/glass powder), curing temperature, and curing duration. Increasing the curing duration and curing temperature had positive effects when the alkali equivalent was lower than the optimal percentage. However, over-curing resulted in the visible cracking of the specimens. Furthermore, despite being initially high, the compressive strength of specimens gradually diminished after standing in air. To ensure the durability of glass-based geopolymers, the curing temperature and duration should not exceed 70 °C, and 1 day, respectively.

1. Introduction

The relentless usage of natural resources to fuel economic growth has resulted in the problem of resource shortage [1]. Therefore, the reuse of waste products and the use of environmentally friendly materials have become growing international concerns [2]. Portland cement is the most commonly used inorganic cementing material in civil engineering; however, its production involves one grinding process as well as two burning processes at high temperature of 1300~1400 °C, generating 1 ton of carbon dioxide per ton of cement [3]. Global cement production accounts for 5–7% of global annual greenhouse gas emissions [3,4], and the amount of greenhouse gases generated in cement production is increasing by 5% each year [3]. Thus, developing a low-cost, low polluting inorganic cementing material with low energy requirements as a replacement for Portland cement is crucial for environment protection. Alkali-activated binders are possible replacements for Portland cement.
Alkali-activated binder materials are essentially cementing materials consisting of aluminosilicates, alkaline solution, and alkali silicate solution. Aluminosilicates, which dissolve in strong alkaline solutions to release sufficient quantities of Si and Al, can supply sufficient amounts of silicate oligomers to enhance the polymerization of alkali-activated binders [5,6], for example, by increasing the strength and density of binder microstructure. Alkali-activated binder materials are environmentally friendly. Moreover, they require a considerably lower calcination temperature than Portland cement (1400 °C), produce 20–50% less CO2 and consume less energy [7]. In addition, their weathering resistance, acid erosion properties, and fire insulation properties are superior. Currently, alkali-activated binder materials are used in applications such as fire insulation, waste solidification, and structural materials production [8,9,10,11].
Alkali-activated cementitious materials are produced using various raw materials, such as metakaolin [9,12], ground-granulated blast-furnace slag (GGBFs) [13], fly ash [14], silica fume [15], bottom ash [16], graphene oxide [17], construction and demolition waste [18], eggshell powder [19], and calcined reservoir sludge [20]. These materials are mixed with an activator that is usually composed of alkali metal hydroxide and sodium silicate. In the alkali-activation reaction of inorganic polymers, the dissolution of the ions of aluminosilicate minerals is mainly caused by alkali metal hydroxide. The subsequent polycondensation of some silicate precursors is partially caused by sodium silicate. Compared with Portland cement, inorganic binders have a substantially higher compressive strength due to their mixture with activators of sodium hydroxide and sodium silicate.
Alkali-activated inorganic binders are categorized into two types according to their microstructures: alkali-activated slag (AAS) and geopolymer. AAS has a microstructure with a low Ca/Si ratio and contains C-S-H gel [21]. Geopolymer, also known as Class-F fly ash, has a colloidal microstructure containing tetrahedron SiO4 and AlO4- [22,23].
If they are to be competitive with traditional types of cement, binders composed of waste products must have lower manufacturing costs. This study used 100% waste glass to create an alkali-activated binder. The composition was optimized to reduce the cost of activator use and improve the material properties. Habert et al. suggested using industrial waste with a suitable molar ratio to reduce the amount of sodium silicate required in activators because the productions of sodium silicate exerts more severe environment impacts than does that of Portland cement [24]. Waste glass has the aforementioned characteristics, and studies have found that glass is a suitable geopolymer. Luhar et al. reviewed various studies on the effects of glass geopolymers on durability, thermal properties, and microstructural properties [25]. Waste glass is also recycled in ceramics [26] and used as a material in cement firing [27], foam glass firing [28], concrete [29], and asphalt [30]. Christiansen examined the influence of different types of glass and alkali activators on the properties of geopolymers [31]. Chen et al. [32] proposed an aging process to produce glass-based geopolymers with mechanical properties equivalent to those of geopolymers not containing silicate. Another study indicated that changing the curing conditions can enhance the mechanical properties of glass-based geopolymers [33]. The current study, which is based on the study by Chen et al. [32], used waste glass as an activator to replace sodium silicate, which is expensive and environmentally unfriendly. The curing conditions were adjusted under optimal aging conditions to determine whether the adjustment of curing temperature and duration resulted in variations in the performance of the glass-based geopolymer, the compressive strength of which was correlated with the durability, bending strength, and shear strength of concrete.

2. Materials and Methods

2.1. Raw Materials

After the selection and transport of waste glass containers from a recycling plant to a laboratory, various steps must be performed before they could be used as raw material for geopolymer fabrication. First, the glass bottles were cleaned and dried in air. Next, the bottles were crushed to a particle size of less than 300 μm and then ground into powder by using a pan mill. The physical and chemical properties of the glass powder are presented in Table 1. The X-ray diffraction (XRD) patterns of the glass powder (Figure 1), which were obtained at a scanning rate of 2θ/min and over a scanning range of 10°–80°, revealed highly amorphous characteristics. The physical properties, chemical properties, and XRD patterns of the glass powder indicate that it had a high content of reactive silica, one of the most crucial substances to geopolymer formation. In short, glass powder was successfully used to replace sodium silicate in geopolymer preparation.

2.2. Activator

Two parameters were used to examine the effects of the activator: the alkali-equivalent content (AE%) and the water/binder (W/B) ratio. The alkali-equivalent content is defined as the ratio of the weight fraction of Na2O to glass powders. The W/B ratio is the ratio of the weight of water to the summed weights of glass powders. Sodium hydroxide (99%; ECHO Chemical Co., Ltd.) was used as the activator, and the W/B ratio was fixed as 0.3 for all the glass-based geopolymer specimens. The mixture proportions of the specimens with varying AE% = 1–6% are listed in Table 2.

2.3. Aging Process

First, sodium hydroxide was mixed thoroughly with water; then, the alkali solution was cooled to room temperature. Next, a bath tank was heated to the preset aging temperature by using a temperature-controlled heating device, and the glass powder and alkali-activator mixture were poured into a sequencing batch reactor, after which they were combined by using a direct current (DC) mixer at 500 rpm for 30 s at room temperature. The mixture was then covered with plastic wrap and placed in a water bath to maintain its temperature. Mixing was continued at 500 rpm with the DC mixer until the preset time, after which the mixture was poured into 3 cm × 3 cm × 3 cm three-gang cube molds in two layers. The mixtures were tamped at a frequency of 60 Hz by using a vibration table (Italy CONTROLS) to eliminate the bubbles within the specimens. The following aging times were adopted for AE% of 1–6% below the aging temperature of 70 °C: 105, 55, 40, 35, and 25 min [32].

2.4. Curing Process

To prevent moisture loss, the specimens were wrapped with plastic film and then placed into an oven, with the molds, for curing over a preset duration. The specimens were removed from the oven and demolded when they had cooled to room temperature and then allowed to stand at room temperature for 4 days. The curing temperatures for each glass slurry and AE% were 60 °C, 70 °C, 80 °C, 90 °C, and 100 °C. The curing durations were increased by 8 h until 4 days had passed. For instance, a curing duration of 8 h indicates that the specimens were in the oven for 8 h, demolded, and then maintained at room temperature for 88 h. The curing was completed over 4 days, after which the compressive strength of the specimens was measured using a Shimadzu UHC-100A universal tester with a constant loading speed of 300 KPa/s for stress control.

2.5. Specimen Strength Development

To determine the effect of curing temperature on the compressive strength of the specimens, the compressive strength was measured at AE% of 3% and 6%; a curing duration of 24 h; standing times of 0, 7, 14, 21, and 28 days; and curing temperatures between 60 °C and 100 °C. Specifically, the compressive strength was measured at a curing temperature of 70 °C; curing durations of 8, 16, 24, 48, and 96 h; and a standing time of 0 days. It was also measured after the specimens had cooled to room temperature (in approximately 1 h). For the remaining curing durations, we measured compressive strength after letting the specimens stand in the air for the corresponding period.

3. Results and Discussion

3.1. Effects of the AE% on the Curing Process

Table 3 presents the curing conditions corresponding to the optimal compressive strength for each AE%. At the same curing temperature, a higher AE% corresponded to a shorter optimal curing duration. For instance, for a curing temperature of 80 °C, the optimal curing duration was 64 h when the AE% was 1%. This duration shortened to 48 and 40 h when the AE% was 3% and 6%, respectively. Regardless of the curing conditions, all the final compressive strengths, except those at a curing temperature of 60 °C and AE% of 1% and 2%, were controlled by the AE%. For a curing temperature of 60 °C and AE% of 1% and 2%, 4 days was insufficient for the specimens to reach their ultimate compressive strength (indicated by <> in Table 3). The researcher speculates that by extending the curing duration, the approximate ultimate compressive strength can be reached under the aforementioned conditions. When the curing duration is shorter than the optimal curing duration, an increase in the curing temperature or curing duration causes OH to bond with additional Si and Al, which are required for geopolymer formation. However, if the curing duration exceeds the optimal curing duration, water molecules and OH ions may diffuse to the surface of undissolved glass particles and corrode them [34]. The higher the AE%, the more severe this corrosion. An increase in the curing duration causes an increasing number of OH ions to corrode polymerized glass-based geopolymers, reducing its compressive strength. Thus, polymers with lower AE% require higher curing temperatures or longer curing durations. This result is similar to the conclusion presented by Chen [33].

3.2. Effects of the Curing Temperature on the Compressive Strength

Figure 2, Figure 3 and Figure 4 indicate that before the optimal AE% (3%) was reached, the compressive strength of the glass-based geopolymer increased with the curing temperature (60 °C, 70 °C, 80 °C, 90 °C, and 100 °C) at a fixed curing duration of 24 h. When AE% = 1%, the compressive strength increases from 25.87 MPa to 65.31 MPa; when AE% = 2%, the compressive strength increases from 44.56 MPa to 82.31 MPa, and when AE% = 3%, the compressive strength increases from 85.85 MPa to 96.21 MPa under increases in the curing temperature from 60 °C to 100 °C. When the curing duration was extended to 48 h, an optimal compressive strength of 69.96 MPa was achieved at an AE% of 1% and a curing temperature of 90 °C. For the same curing duration, optimal compressive strengths of 101.89 and 129.97 MPa were achieved at AE% of 2% and 3%, respectively, under a curing temperature of 80 °C.
Figure 5, Figure 6 and Figure 7 present the variations with curing duration in the compressive strength of the geopolymer specimens at various curing temperatures when the optimal AE% of 3% was exceeded. For a curing duration of 24 h, the compressive strengths of the specimens with AE% of 4%, 5%, and 6% increased from 73.16 to 94.09 MPa, 77.19 to 83.28 MPa, and 72.84 to 109.37 MPa, respectively, under increases in the curing temperature from 60 °C to 90 °C. However, when the curing temperature increased to 100 °C, the compressive strengths of the specimens with AE% of 4%, 5%, and 6% decreased to 88.64, 71.13, and 71.98 MPa, respectively. When the curing duration was increased to 48 h, the compressive strengths of the specimens with AE% of 5% and 6% increased with the curing temperature between 60 °C and 80 °C but decreased with the curing temperature between 80 °C and 100 °C. For example, when AE% = 5%, the compressive strength increased from 98.80 to 114.84 MPa between 60 °C and 80 °C and then decreased to 55.02 MPa at 100 °C. By contrast, when AE% = 6%, the compressive strength remained relatively constant between 60 °C and 80 °C, with com-pressive strengths of 95.82, 92.59, and 94.03 MPa at curing temperatures of 60 °C, 70 °C, and 80 °C, respectively. When the curing temperature increased to 100 °C, the compressive strength decreased to 49.27 MPa.
As shown in Figure 2, Figure 3, Figure 4, Figure 5, Figure 6 and Figure 7, the compressive strength increased with the curing temperature until the optimal curing temperature was reached, regardless of the AE%. The optimal curing temperature decreased with an increase in the AE%, indicating that an increase in the curing temperature accelerated the rate at which the glass slurry solidified. However, if the curing temperature continues to rise, the compressive strength then declines. This result is similar to those observed for fly ash and GGBF geopolymers under different curing temperatures [35].

3.3. Effects of the Curing Duration on the Compressive Strength

Figure 2, Figure 3, Figure 4, Figure 5, Figure 6 and Figure 7 present the relationship between the compressive strength and curing duration of the geopolymer specimens at various curing temperatures. The compressive strength increased with the curing duration until the optimal curing duration was reached and then decreased with the curing duration. For a curing temperature of 80 ℃ and a curing duration shorter than 24 h, the compressive strength of the specimens with AE% of 1%, 2%, and 3% increased significantly with the curing duration, from 2.18 to 50.12 MPa, 2.44 to 81.45 MPa, and 3.62 to 125.79 MPa, respectively. When the curing duration was longer than 24 h, the influence of the curing duration on the compressive strength decreased considerably. Compressive strengths of 69.53, 101.89, and 129.97 MPa were observed at AE% of 1%, 2%, and 3%, respectively, and at curing durations of 64, 48, and 48 h, respectively. When the curing duration was increased to 4 days, the compressive strengths of the samples with AE% of 1%, 2%, and 3% decreased to 59.18, 66.78, and 67.45 MPa, respectively. The specimens with AE% of 4–6% exhibited the same trends as those with AE% of 1–3%. For example, at a curing temperature of 70 °C and curing durations shorter than 24 h, the compressive strength of the specimens with AE% of 4%, 5%, and 6% increased significantly with the curing duration, from 3.47, 0.71, and 0 MPa to 117.01, 97.81, and 99.66 MPa, respectively. When the curing duration exceeded 24 h, the influence of the curing duration on the compressive strength decreased substantially. Compressive strengths of 119.65, 107.96, and 103.60 MPa were observed at AE% of 4%, 5%, and 6%, respectively, and at curing durations of 64, 64, and 56 h, respectively. When the curing duration was increased to 4 days, the compressive strength of the samples with AE% of 4%, 5%, and 6% decreased to 77.61, 73.98, and 76.07 MPa, respectively.
Except for the specimens cured at 60 °C, all the specimens with AE% of 1–5% exhibited an increase in their compressive strength over 4 days. Regardless of the curing temperature or duration, the curing process of the glass-based geopolymer can be di-vided into three phases. During the first phase, the polymerization reaction of the glass is vigorous, and the amount of consolidated colloid increases considerably, strengthening the geopolymer. During the second phase, the compressive strength increases marginally with the curing duration. Low alkali content and curing temperatures necessitate a long curing duration, which results in a clear distinction between the first and second phases. As the AE% and curing temperature increase, the second phase becomes less distinguishable from the first phase. Finally, in the third phase, the glass consolidation period extends but the compressive strength decreases. Overcuring led to thermal cracking in the geopolymer, negatively affecting its performance and compressive strength (Figure 8).

3.4. Effects of the Curing Process on Long-Term Strength Development

As mentioned in Section 3.2, an increase in the curing temperature can shorten the curing duration. Strength development in the specimens was investigated—specifically, that in those with AE% of 3% and 6% as they were maintained in air for 28 days after constant 24-h curing and curing over 8, 16, 24, 48, and 96 h.
As presented in Figure 9 and Figure 10, among the specimens with an AE% of 3%, the specimen cured at 100 °C over 24 h had the highest compressive strength (121.30 MPa) after cooling for 1 h in air. However, after standing in air for 28 days, this specimen had the lowest compressive strength (51.14 MPa) among the specimens with the same AE%. By contrast, the specimen cured at 70 °C had a compressive strength of 97.75 MPa after cooling in air for 1 h; however, after standing in air for 28 days, its compressive strength increased to 121.93 MPa. Among the specimens with an AE% of 6%, the specimen cured at 80 °C exhibited the highest compressive strength of 83.50 MPa immediately after curing. After standing in air for 28 days, the specimen cured at 60 °C exhibited the highest compressive strength of 96.08 MPa. These results demonstrate that excessively high curing temperatures had adverse effects on the compressive strength of the geopolymer. The researcher speculates that only a part of the geopolymer rapidly solidified within a short period. After standing in air, cracks formed between its regions, reducing its compressive strength.
Figure 11 and Figure 12 illustrate the strength development of the specimens that were maintained in air after curing over varying durations. Among the specimens with AE% = 3%, the specimen cured for 24 h exhibited the highest compressive strength of 121.93 MPa after standing in air for 28 days. The specimen cured for 96 h exhibited the highest compressive strength of 120.75 MPa immediately after curing. Among the specimens with AE% = 6%, the specimen cured at 70 °C for 48 h exhibited the highest compressive strength of 100.37 MPa immediately after curing. The specimen cured for 24 h exhibited the highest compressive strength of 83.93 MPa after standing in air for 28 days. These results indicate that the optimal curing duration must be adopted for a glass slurry to dehydrate into a glass-based geopolymer. Excessive thermal energy damages glass microstructures in the long term. The Fourier transform infrared (FTIR) spectroscopy results of the specimens under optimal curing and overcuring conditions are presented in Figure 13. The peak at the wavenumber of 1560 cm−1 in the FTIR spectrum of the specimen subjected to overcuring is attributed to the presence of sodium carbonate [36]. No peak was observed in the FTIR spectrum of the geopolymer cured for the optimal duration.

4. Conclusions

The objective of this study was to examine variations in the compressive strength of a glass-based geopolymer subjected to high-temperature curing under the optimal aging process. The results indicate that the compressive strength of the glass-based geopolymer was affected by its solidification process. By increasing the curing duration and temperature the compressive strength specimens were increased. However, overcuring resulted in thermal cracking, reducing the compressive strength. The optimal curing temperature and duction depended on the AE%. Higher AE% required shorter curing durations and lower curing temperatures. Overall, the compressive strength was not influenced by the curing duration and temperature; instead, it was controlled by AE%.
Excessively high curing temperatures and excessively long curing durations had adverse effects on specimen strength in the long term, with the temperature having particularly severe impact. Therefore, curing temperature should not exceed 70 °C. Furthermore, curing durations shorter than 24 h enable the gradual development of polymer strength.

Funding

This work received no external funding.

Institutional Review Board Statement

Not applicable.

Informed Consent Statement

Not applicable.

Conflicts of Interest

The author has no conflict of interest to declare.

References

  1. Arndt, N.T.; Fontboté, L.; Hedenquist, J.W.; Kesler, S.E.; Thompson, J.F.; Wood, D.G. Future global mineral resources. Geochem. Perspect. 2017, 6, 1–171. [Google Scholar] [CrossRef] [Green Version]
  2. Hodges, C.A. Mineral resources, environmental issues, and land use. Science 1995, 268, 1305–1312. [Google Scholar] [CrossRef] [PubMed]
  3. Davidovits, J. Geopolymer cements to minimise carbon-dioxide greenhouse-warming. Ceram. Trans. 1993, 37, 165–182. [Google Scholar]
  4. Mehta, P.K. Reducing the environmental impact of concrete. Concr. Int. 2001, 23, 61–66. [Google Scholar]
  5. Xu, H.; Van Deventer, J.S.J. The geopolymerisation of alumino-silicate minerals. Int. J. Miner. Process. 2000, 59, 247–266. [Google Scholar] [CrossRef] [Green Version]
  6. Krizan, D.; Zivanovic, B. Effects of dosage and modulus of water glass on early hydration of alkali-slag cements. Cem. Concr. Res. 2002, 32, 1181–1188. [Google Scholar] [CrossRef]
  7. Davidovits, J. Geopolymers: Man-made rock geosynthesis and the resulting development of very early high strength cement. J. Mater. Educ. 1994, 16, 91–139. [Google Scholar]
  8. Davidovits, J. 30 years of successes and failures in geopolymer applications. Market trends and potential breakthroughs. In Proceedings of the Keynote Conference on Geopolymer Conference, Melbourne, VIC, Australia, 28–29 October 2002. [Google Scholar]
  9. Davidovits, J. Geopolymers: Inorganic polymeric new materials. J. Therm. Anal. 1991, 37, 1633–1656. [Google Scholar] [CrossRef]
  10. Wang, S.D.; Pu, X.C.; Scrivener, K.; Pratt, P.L. Alkali-activated slag cement and concrete: A review of properties and problems. Adv. Cem. Res. 1995, 7, 93–102. [Google Scholar] [CrossRef]
  11. Roy, D.M. Alkali-activated cements opportunities and challenges. Cem. Concr. Res. 1999, 29, 249–254. [Google Scholar] [CrossRef]
  12. Medri, V.; Papa, E.; Lizion, J.; Landi, E. Metakaolin-based geopolymer beads: Production methods and characterization. J. Clean. Prod. 2019, 244, 118844. [Google Scholar] [CrossRef]
  13. Ez-zaki, H.; Bellotto, M.; Valentini, L.; Garbin, E.; Artioli, G. Influence of cellulose nanofibrils on the rheology, microstructure and strength of alkali activated ground granulated blast-furnace slag: A comparison with ordinary Portland cement. Mater. Struct. 2021, 54, 1–18. [Google Scholar] [CrossRef]
  14. Atiş, C.D.; Görür, E.B.; Karahan, O.; Bilim, C.; Ilkentapar, S.; Luga, E. Very high strength (120 MPa) class F fly ash geopolymer mortar activated at different NaOH amount, Heat Curing Temperature and Heat Curing Duration. Constr. Build. Mater. 2015, 96, 673–678. [Google Scholar] [CrossRef]
  15. Bahrami, M.; Shalbafan, A.; Welling, J. Development of plywood using geopolymer as binder: Effect of silica fume on the plywood and binder characteristics. Eur. J. Wood Prod. 2019, 77, 981–994. [Google Scholar] [CrossRef]
  16. Chindaprasirt, P.; Jaturapitakkul, C.; Chalee, W.; Rattanasak, U. Comparative study on the characteristics of fly ash and bottom ash geopolymers. Waste Manag. 2009, 29, 539–543. [Google Scholar] [CrossRef]
  17. Sun, Q.; Liu, J.; Cheng, H.; Mou, Y.; Liu, J.; Peng, Y.; Chen, M. Fabrication of 3D structures via direct ink writing of kaolin/graphene oxide composite suspensions at ambient temperature. Ceram. Int. 2019, 45, 18972–18979. [Google Scholar] [CrossRef]
  18. Lampris, C.; Lupo, R.; Cheeseman, C.R. Geopolymerisation of silt generated from construction and demolition waste washing plants. Waste Manag. 2009, 29, 368–373. [Google Scholar] [CrossRef] [PubMed]
  19. Shekhawat, P.; Sharma, G.; Singh, R.M. Strength behavior of alkaline activated eggshell powder and flyash geopolymer cured at ambient temperature. Constr. Build. Mater. 2019, 223, 1112–1122. [Google Scholar] [CrossRef]
  20. Yang, K.H.; Lo, C.W.; Huang, J.S. Production and properties of foamed reservoir sludge inorganic polymers. Cem. Concr. Compos. 2013, 38, 50–56. [Google Scholar] [CrossRef]
  21. Dung, N.T.; Chang, T.P.; Chen, C.T.; Yang, T.R. Cementitious properties and microstructure of an innovative slag eco-binder. Mater. Struct. 2016, 49, 2009–2024. [Google Scholar] [CrossRef]
  22. Mehta, A.; Siddique, R. Properties of low-calcium fly ash based geopolymer concrete incorporating OPC as partial replacement of fly ash. Constr. Build. Mater. 2017, 150, 792–807. [Google Scholar] [CrossRef]
  23. Nguyen, H.A.; Chang, T.P.; Shih, J.Y.; Chen, C.T. Influence of low calcium fly ash on compressive strength and hydration product of low energy super sulfated cement paste. Cem. Concr. Compos. 2019, 99, 40–48. [Google Scholar] [CrossRef]
  24. Habert, G.; d’Espinose de Lacaillerie, J.B.; Roussel, N. An environmental evaluation of geopolymer based concrete production: Reviewing current research trends. J. Clean. Prod. 2011, 19, 1229–1238. [Google Scholar] [CrossRef]
  25. Luhar, S.; Cheng, T.W.; Nicolaides, D.; Luhar, I.; Panias, D.; Sakkas, K. Valorisation of glass wastes for the development of geopolymer composites–Durability, thermal and microstructural properties: A review. Constr. Build. Mater. 2019, 222, 673–687. [Google Scholar] [CrossRef]
  26. Adediran, A.; Lemougna, P.N.; Yliniemi, J.; Tanskanen, P.; Kinnunen, P.; Roning, J.; Illikainen, M. Recycling glass wool as a fluxing agent in the production of clay-and waste-based ceramics. J. Clean. Prod. 2021, 289, 125673. [Google Scholar] [CrossRef]
  27. Chen, G.; Lee, H.; Young, K.L.; Yue, P.L.; Wong, A.; Tao, T.; Choi, K.K. Glass recycling in cement production—an innovative approach. Waste Manag. 2002, 22, 747–753. [Google Scholar] [CrossRef]
  28. Suvorova, O.V.; Manakova, N.K.; Makarov, D.V. Use of Bulk Industrial Wastes in the Production of Glass Foam Materials. Glass Ceram. 2021, 77, 384–389. [Google Scholar] [CrossRef]
  29. Ali, S.; Iqbal, S.; Room, S.; Ali, A.; Rehman, Z.U. Value added usage of granular steel slag and milled glass in concrete production. J. Eng. Res. 2021, 9. [Google Scholar] [CrossRef]
  30. Simone, A.; Mazzotta, F.; Eskandarsefat, S.; Sangiorgi, C.; Vignali, V.; Lantieri, C.; Dondi, G. Experimental application of waste glass powder filler in recycled dense-graded asphalt mixtures. Road Mater. Pavement Des. 2019, 20, 592–607. [Google Scholar] [CrossRef] [Green Version]
  31. Christiansen, M.U. Effects of Composition and Activator Type on Glass-Based Geopolymers. ACI Mater. J. 2019, 116, 239–250. [Google Scholar] [CrossRef]
  32. Chen, T.A.; Chen, J.H.; Huang, J.S. Effects of activator and aging process on the compressive strengths of alkali-activated glass inorganic binders. Cem. Concr. Compos. 2017, 76, 1–12. [Google Scholar] [CrossRef]
  33. Chen, T.A. Optimum curing temperature and duration of alkali-activated glass inorganic binders. J. Chin. Inst. Eng. 2020, 43, 592–602. [Google Scholar] [CrossRef]
  34. Hosoi, K.; Kawai, S.; Yanagisawa, K.; Yamasaki, N. Densification process for spherical glass powders with the same particle size by hydrothermal hot pressing. J. Mater. Sci. 1991, 26, 6448–6452. [Google Scholar] [CrossRef]
  35. Verma, M.; Dev, N. Effect of ground granulated blast furnace slag and fly ash ratio and the curing conditions on the mechanical properties of geopolymer concrete. Struct. Concr. 2021. [Google Scholar] [CrossRef]
  36. Swanepoel, J.C.; Strydom, C.A. Utilisation of fly ash in a geopolymer material. Appl. Geochem. 2002, 17, 1143–1148. [Google Scholar] [CrossRef]
Figure 1. X-ray diffraction patterns of the glass powder.
Figure 1. X-ray diffraction patterns of the glass powder.
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Figure 2. Variations with curing duration in the 4-day compressive strength of geopolymer specimens at various curing temperatures when AE% = 1%.
Figure 2. Variations with curing duration in the 4-day compressive strength of geopolymer specimens at various curing temperatures when AE% = 1%.
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Figure 3. Variations with curing duration in the 4-day compressive strength of geopolymer specimens at various curing temperatures when AE% = 2%.
Figure 3. Variations with curing duration in the 4-day compressive strength of geopolymer specimens at various curing temperatures when AE% = 2%.
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Figure 4. Variations with curing duration in the 4-day compressive strength of geopolymer specimens at various curing temperatures when AE% = 3%.
Figure 4. Variations with curing duration in the 4-day compressive strength of geopolymer specimens at various curing temperatures when AE% = 3%.
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Figure 5. Variations with curing duration in the 4-day compressive strength of geopolymer specimens at various curing temperatures when AE% = 4%.
Figure 5. Variations with curing duration in the 4-day compressive strength of geopolymer specimens at various curing temperatures when AE% = 4%.
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Figure 6. Variations with curing duration in the 4-day compressive strength of geopolymer specimens at various curing temperatures when AE% = 5%.
Figure 6. Variations with curing duration in the 4-day compressive strength of geopolymer specimens at various curing temperatures when AE% = 5%.
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Figure 7. Variations with curing duration in the 4-day compressive strength of geopolymer specimens at various curing temperatures when AE% = 6%.
Figure 7. Variations with curing duration in the 4-day compressive strength of geopolymer specimens at various curing temperatures when AE% = 6%.
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Figure 8. Thermal cracking in geopolymer specimens caused by overcuring.
Figure 8. Thermal cracking in geopolymer specimens caused by overcuring.
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Figure 9. Changes in compressive strength with standing time in air under various curing temperatures after 24-h curing when AE% = 3%.
Figure 9. Changes in compressive strength with standing time in air under various curing temperatures after 24-h curing when AE% = 3%.
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Figure 10. Changes in compressive strength with standing time in air under various curing temperatures after 24-h curing when AE% = 6%.
Figure 10. Changes in compressive strength with standing time in air under various curing temperatures after 24-h curing when AE% = 6%.
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Figure 11. Changes in compressive strength with standing time in air under various curing durations of specimens cured at 70 °C when AE% = 3%.
Figure 11. Changes in compressive strength with standing time in air under various curing durations of specimens cured at 70 °C when AE% = 3%.
Crystals 11 00502 g011
Figure 12. Changes in compressive strength with standing time in air under various curing durations of specimens cured at 70 °C when AE% = 6%.
Figure 12. Changes in compressive strength with standing time in air under various curing durations of specimens cured at 70 °C when AE% = 6%.
Crystals 11 00502 g012
Figure 13. Fourier-transform infrared spectroscopy spectra of a specimen cured for the optimal duration and an overcured specimen.
Figure 13. Fourier-transform infrared spectroscopy spectra of a specimen cured for the optimal duration and an overcured specimen.
Crystals 11 00502 g013
Table 1. Physical and chemical properties of the glass powder produced from waste glass in this study.
Table 1. Physical and chemical properties of the glass powder produced from waste glass in this study.
SiO2Al2O3Fe2O3CaOMgONa2OK2OGsAbsorptionSpecific Surface Area
72.5%2%0.06%10.5%1%13%0.5%2.550.2%4303 cm2/g
Table 2. Mixture proportions of the glass-based geopolymer specimens with varying AE% = 1–6%.
Table 2. Mixture proportions of the glass-based geopolymer specimens with varying AE% = 1–6%.
W/BAE%Sodium Hydroxide (g)Water (g)Glass Powder (g)
0.31%12.91303.871000
2%25.82307.751000
3%38.73311.621000
4%51.64315.491000
5%64.55319.371000
6%77.47323.241000
Table 3. Ultimate compressive strengths of the specimens under various curing temperatures when AE% = 1–6%.
Table 3. Ultimate compressive strengths of the specimens under various curing temperatures when AE% = 1–6%.
AE% = 1%AE% = 2%AE% = 3%
Curing
Temperature
(°C)
Curing
Duration
(h)
Compressive Strength
(MPa)
Curing
Duration
(h)
Compressive Strength
(MPa)
Curing
Duration
(h)
Compressive Strength
(MPa)
6096<55.24>96<76.26>96129.65
708871.9788106.7280136.77
806469.5348101.8948129.97
904869.963285.8932126.83
1002465.312482.312496.21
Ultimate compressive strength69.19 94.20 123.89
AE% = 4%AE% = 5%AE% = 6%
Curing
Temperature
(℃)
Curing
Duration
(h)
Compressive Strength
(MPa)
Curing
Duration
(h)
Compressive Strength
(MPa)
Curing
Duration
(h)
Compressive Strength
(MPa)
6096122.6288119.2588108.17
7064119.6564107.9656103.60
8048105.3448114.8440115.91
9032103.0532100.7224109.37
10016111.241697.01896.86
Ultimate compressive strength112.38 107.96 106.78
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Chen, T.-A. Mechanical Properties of Glass-Based Geopolymers Affected by Activator and Curing Conditions under Optimal Aging Conditions. Crystals 2021, 11, 502. https://doi.org/10.3390/cryst11050502

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Chen T-A. Mechanical Properties of Glass-Based Geopolymers Affected by Activator and Curing Conditions under Optimal Aging Conditions. Crystals. 2021; 11(5):502. https://doi.org/10.3390/cryst11050502

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Chen, Tai-An. 2021. "Mechanical Properties of Glass-Based Geopolymers Affected by Activator and Curing Conditions under Optimal Aging Conditions" Crystals 11, no. 5: 502. https://doi.org/10.3390/cryst11050502

APA Style

Chen, T. -A. (2021). Mechanical Properties of Glass-Based Geopolymers Affected by Activator and Curing Conditions under Optimal Aging Conditions. Crystals, 11(5), 502. https://doi.org/10.3390/cryst11050502

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