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A critical review on mechanical, durability, and microstructural properties of industrial by-product-based geopolymer composites

  • Ahmed Babeker Elhag , Ali Raza EMAIL logo , Qaiser uz Zaman Khan , Muhammad Abid , Bilal Masood , Muhammad Arshad and Ahmed Farouk Deifalla
Published/Copyright: April 17, 2023
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Abstract

For the sustainability of the construction industry, geopolymers (GPMs) play an important role compared with Portland cement due to their improved mechanical properties, enhanced durability, and outstanding performance in alkali and acidic conditions. Most of the previous review investigations explored the general behavior of GPM developed with kaolin, silica fume (SF), rice husk ash, ground granulated blast furnace slag, fly ash, etc., but a comprehensive review study on the industrial by-products, including granite waste powder (GWP) and bauxite residue (BR), is required to investigate their suitability in the construction industry. The current investigation aims to present a detailed review of the fresh, mechanical, durability, and microstructural behavior of the GPM paste produced using BR and GWP from the literature. The effect of different ingredients and testing conditions are evaluated for the fresh, mechanical, durability, thermal, and microstructural performance of the GPM paste. The results indicate that the pure BR having a lower ratio of SiO2/Al2O3 reacts poorly; therefore, it should be blended with other aluminosilicates comprising a higher ratio of SiO2/Al2O3 for better geopolymerization. Pre-activation of BR including 3 h calcination at 800°C, 1 h thermal pretreatment of alkali with solid activators at 800°C, mechanical co-grinding, and pulverization presented improved strength and microstructural properties of GPM. When mixing GWP in large quantities, heat curing is preferred for 8 h at 60–80°C for better behavior of GPM. Incorporating the nanomaterials into GWP-based GPM showed a significant impact on initial compressive and tensile strengths. Further studies on the synergistic use of GWP with aluminosilicate products and BR with silica-rich pozzolanic ingredients for GPM are required. Improved physiochemical features of BR-GPM and GWP-GPM are the potential research areas that can be addressed by incorporating raw materials for enhancing the internal matrix, such as nanoparticles, bio-additives, micro-fibers, etc., that have been observed to be effective for the GPM pastes.

1 Introduction

For the sustainability of the environment, one of the most important environmental concerns is reduction of wastes produced by industrial and mining projects. Therefore, deploying and adopting the latest possible processes for conversion of wastes into high-value products have become an increasingly evolving research field [1,2,3]. Currently, among many other measures to minimize environmental impacts, ordinary Portland cement (OPC) is being replaced with alkali-activated cementitious binders. These binders are generally produced from industrial wastes comprising Al2SiO5-based products of either geological origins or other various products containing high aluminosilicate content. These products are used either separately or are applied by combining them with other materials in the form of composites [4,5,6,7,8,9,10]. Likewise, replacing the cement with geopolymer (GPM) binders not only reduces the consumption of the energy linked with producing the cement but also minimizes CO2 emitted from the process of carbonate combustion [11]. This study primarily targets two wastes derived from industrial activities, i.e., bauxite residue (BR) and granite wastes. BR is an industrial (aluminum) waste, known as bauxite residue. Extracted through the Bayer process of bauxite refinement and treating the bauxite ore with NaOH solution, BR primarily comprises SiO2, Al2O3, Fe2O3, Na2O, CaO, K2O, TiO2, MnO, MgO, P2O5, and SO3. Generation of a ton of alumina yields about 1.5–2.5 tons of BR approximately. Nonetheless, depending on the bauxite source and extraction parameters, this amount may vary [8,12]. These wastes are generally handled by either disposing them in the natural water bodies after neutralization or by dumping them on the land [13,14,15]. Stockpiling the BR not only affects natural resources but also contaminates the soil, atmosphere, and water because of its highly alkaline nature and its extreme capability to exchange cations [16,17,18]. In case the heavy metallic elements from BR start leaching, they may cause severe environmental problems by contaminating the soil and polluting the groundwater. Therefore, appropriate management and comprehensively utilizing the BR have become a serious concern for the alumina sector.

Although disposing of BR may result in a major risk to the population and ecosystem, BR itself cannot be considered hazardous waste. Because of being alkaline, BR has certain limitations for reusability. But it has been gaining popularity in GPM technology because it contains high alumina and silica content, along with Na2O in abundance [19]. Appropriate re-utilization and recycling of the BR may reduce the damaging effects on the environment [20,21,22,23]. Various experiments have been performed to treat the BR by de-alkalizing the process and extracting important metals harmlessly. But, most of the processes have their limitations. One of these includes acid neutralization; for instance, desulfurizing the acid flue gases inside the thermal power plant to eliminate SO2 and control pollution. It is also employed as an alternative approach for the alkalinity reduction from BR by employing the alkali in BR to neutralize the acidic flue gas. Desulfurized BR also serves as an important candidate for synthesizing GPM [4,24,25]. Calcification–carbonization (CC) is also a valuable approach to recovering alkali as well as alumina by almost 90 and 50%, respectively. Also, the leftover residue from CC contains suitable calcium-rich compounds to produce cement [16]. Increasing problems associated with the disposal of BR led to its efficient usage in construction and engineering projects. Its utilization includes, but is not limited to, product clinker [26], BR bricks [5], hollow brickwork [13], blocks pavements [27], fired bricks [28], lightweight aggregates [29], partially substituting the cement [30], manufacturing special types of cements [31], as a raw material in composite pastes [32,33], ceramic tile [34], and as fillers in composites [35]. In addition, BR has its application in the water treatment industry to extract arsenic and phosphate metals [36], catalyze different biological reactions [37], and produce X-ray-based shield composites [38], landfill-covering substances with a small fraction of bentonite added [13]. Also, BR brick exhibits justified compressive strength (CS) with those of building bricks, conventionally utilized in construction work [13]. GPM-based BR composites also include applications in industries incorporating the phase-changing material (PCM) to provide thermal relief [39]. However, by using such kinds of wastes in construction materials, the important issues associated with the production of BR are disposing of the waste and environmental hazards, etc.; also, the consumption of cement and lime can be significantly minimized. Marvila et al. [40] studied the behavior of GPM tiles at high temperatures and different saturation conditions. The specimens were prepared by changing the molar ratio of SiO2/Al2O3 between 2.25 and 4.00, while the curing was done at ambient temperatures. Sodium hydroxide, metakaolin, sodium silicate, and water were used as raw materials in this study. Initially, the samples were evaluated in normal conditions performing tests of density, linear shrinkage, flexural tensile strength, optical microscopy, and mineralogical investigation. It was observed that preparations 2.25, 2.50, and 3.00 had well-suited features, while preparations 3.50 and 4.00 did not represent effectiveness in the geopolymerization process because of the extra sodium in the composites. Preparations 2.25, 2.50, and 3.00 produced larger contents of zeolite X (faujasite) and zeolite A (sodalite cage), which are minerals produced after the geopolymerization process. This did not occur with preparations 3.50 and 4.00.

2 Geopolymerization process

The polymerization of GPM is a reaction occurring between a source material and an alkaline solution consisting of aluminosilicate that produces a 3-D polymeric chain structure containing Si–O–Al–O bonds [41]. The reaction of GPM contains different steps such as dissolution, orientation, transportation, and polycondensation processes [42]. Various kinds of alumino-silicate materials are used for improvements of the complex process of the reaction in GPM. The polymerization reactions of GPM continue at ambient temperature. Consequently, it can be considered energy-efficient and considerably clean:When the polymerization reaction of GPM starts, the process involves the dissolving of the Si and Al atoms of FA by OH, construction of monomers due to the precursor, and the development of a polymeric matrix of monomers due to polycondensation [43,44]. The occurrence of these three phases can be simultaneous. The water is detached through this phase in the second reaction in the above-stated polymerization reaction of GPM. Additionally, because of different charge densities and diverse sizes, the alkali cations influence the production of nucleation reactions and aluminosilicate chains in diverse ways to separately change the speed and amount of the polymerization process of GPM [45,46]. Due to larger sizes of K+ cation and lower charge densities of Na+ cation, a higher degree of polymerization is obtained in the reaction of GPM [45,47]. The setting and hardening processes of the GPM are not well elaborated yet; nevertheless, the second reaction in the aforementioned chemical technique shows the proposed process of polymerization reaction of GPM [48]. The polymerization process of GPM between the NaOH activator and the Si−Al source constituents also obeys the two-phase process. During the first phase, Si and Al atoms from the source constituent react with OH to fabricate GPM ions. During the second phase, the monomers polymerize to produce the 3-D GPM structure [41,49].Being a felsic igneous rock, granite is found in abundance all over the crust of the earth [50]. Granite waste of almost 20–25% of its production from all over the world is generated when we saw, polish, finish, and cut the granite rocks [51]. This waste predominantly comprises MgO, Na2O, K2O, SiO2, Al2O3, and CaO, and also significant traces of iron oxides. Finer particles of granite produce an enormous amount of colloidal waste during the process of washing off by water. This approach ultimately impacts the permeability and porosity of soil that finally results in waterlogging issues and pollutes the water reservoirs [52]. When humans inhale the granite particles, they may get exposed to different respiratory problems such as bronchitis, silicosis, etc. Appropriate disposal and treating such wastes are of major concern related to health and the environment; therefore, reusability of the wastes is required. Because of its favored characteristics, e.g., pozzolanic activities, gradations, and fineness, previous studies have strongly recommended utilizing granite wastes as partial and sole replacements for fine aggregate and as a substitute for cementing material in concrete production [5159]. Granite waste, having sufficient traces of aluminum oxide and silica, can be employed to synthesize GPM via the alkali activation approach. Besides, it has its role in building materials to gain sustainable developments in engineering projects. Figure 1 presents the percentage usage of the BR and GWP waste by researchers from different countries based on their experimentation in various engineering projects.

Figure 1 
               (a) Utilization of BR and (b) utilization of GWP in the field and research in different countries.
Figure 1

(a) Utilization of BR and (b) utilization of GWP in the field and research in different countries.

3 Scope and significance

Appropriately utilizing the waste in construction works can help solve important issues related to the mining industries, e.g., storing the waste material and disposal and reducing environmental hazards. Being a rich source of GPM, both BR and granite waste can be added to substitute the cement, thus minimizing the CO2 emissions to address such a global environmental problem. Because these are available in abundance and free around the world, utilizing such wastes to produce GPM is a viable solution. In addition, synergistic usage of BR, as well as those of the GWP, will prove to be a sustainable solution to manage the waste for industries, thereby resulting in green construction making the process suitable commercially. Table 1 presents the chemical compositions of different alkali-activated substances.

Table 1

Chemical composition of alkali-activated composites [48,6063]

Compound CaO Al2O3 Fe2O3 SiO2 MgO K2O P2O5 MnO Na2O SO3 TiO2 LOI
FA (%) 1–24 15–30 4–7 45–62 0.47–5 0–1.5 0–0.97 0.62 0.39–1.59
GWP (%) 1–2 10–20 1–10 60–75 0.3–3.5 3–6 0–0.4 0–0.2 1–4 0–0.3 3–6 0–0.5
RHA (%) 0–0.93 0–0.56 0–0.27 90–96 0–0.19 2.3–2.6 0–0.66 0–0.29 0–0.1 2.3–2.6 0–3.67
GGBS (%) 30–45 10–20 0.41–0.7 30–40 5–12 0.3–1 0.01 0–0.6 0.2–0.4 1.8 0.49–0.8 1.41
BR (%) 1–15 10–35 30–60 5–30 0–0.32 0–3 0–0.4 0–0.6 3–20.2 0–12 0–3 1–16
MK (%) 0.05–0.1 35–55 0.3–2 40–60 0.05–0.1 0.4–1.1 0–0.1 0–0.02 1–2 0–2.7

Novel investigations of the GPM materials were performed using databases such as SpringerLink, Taylor and Francis, Hindawi, ScienceDirect, ResearchGate, Multidisciplinary Digital Publishing Institute, Web of Science, Google Scholar, and others. Most of the previous review investigations explored the mechanical, durability, and microstructural behavior of GPM developed with kaolin, SF, rice husk ash, ground granulated blast furnace slag, fly ash (FA), etc., but a comprehensive review study on the industrial by-products including GWP and BR is required to check their suitability in the construction industry. The current study aims to utilize and minimize industrial wastes including BR and GWP. Moreover, being a rich source of aluminosilicate for GPM, these wastes along with developing the mortars are studied at great length. This work also targets various factors impacting the mix design factors, e.g., alkaline activators, the molar concentration of these activators, water to solid ratio (WSR), liquid to solid ratio (LSR), NaOH/Na2SiO3 ratio, and molar ratios of different substances, e.g., SiO2/Na2O and SiO2/Al2O3 influencing the BR’s strength and granite waste derived GPM as well as those of the mortars. In addition, plasticizers’ impact on the duration and temperature of curing on the CS of GPM is focused. The durability behavior and the thermal efficiency of BR-made GPM are presented after exposing them to wet and dry cycles, chemical and acid attacks, and the freezing and thawing phenomenon. In addition, the microstructure of BR and GPM binders derived from granite waste is elaborated.

4 Use of granite waste

Several scientific works are available on the usage of waste granite slurry/powder to partially replace fine aggregates or cement. But there are very few studies targeting the application of GWP in GPM. The rougher and angular texture of GWPs, comprising particles lower than 50 µm, with higher water requirements, make their usage highly unsuitable [51]. Because of finer-sized particles, GWP predominantly acts as a filler in the initial stages but later on, dominated by pozzolanic reactivity, it becomes advantageous for blended types of cement and other supplementary cementitious products [54]. Because of the wide applications of GWP in fine aggregate substitution in concrete[5153], it has been used in bricks and aerated concrete units [63]. Likewise, Bakhoum et al. [64] partially replaced the cement and fine aggregates with nano-granite waste and concluded that nano-SiO2, nano-Al2O3, nano-Fe2O3, and nano-TiO2 of nano-granite wastes resulted in better durability characteristics and enhanced mechanical strength of cement mortar. Partial substitution of nano-granite wastes for fine aggregates and cement saved a lot of energy and emitted much lesser CO2.

To synthesize high-strength blocks for the pavements, Sailalasa and Reddy [65] recommended granite-FA sourced GPM concrete. According to a previous study [50], the waste of muscovite granite also had advantages of producing flooring tiles with better bulk density, cost-effectiveness, higher strength in bending, and compression along with less absorption. Granite sludge subjected to short-duration calcination in the temperature range from 700 to 900°C resulted in reddish pigments. Due to their better mechanical properties, pigments are widely used to synthesize colored cement-sourced mortars [66]. GWPs found their application in self-compacting concrete and ceramic tiles to enhance their mechanical as well as physical characteristics and for better thermal stability [67,68]. In comparison with the GWP-based studies, as discussed above, very limited literature is available to assess its potential to synthesize GPM binders, mortars, and concrete. Subsequently, the following section summarizes different parameters influencing the GWP binder, for instance, workability properties, mechanical strength, and microstructural analysis based on the published research.

4.1 Fresh properties

The characteristics of GPM mortars sourced from ground granite waste and slags were investigated by Eroshkina and Korovkin [69]. The slag content, the concentration of Na2SiO3 solution, and NaOH were considered as varying influential factors to assess the workability. The number of mortar samples comprising different contents (%) of slags such as 15–20, Na2SiO3 (%) ranging from 10 to 15, and NaOH (%) with 3–5, by weight of binders were developed. Results showed that keeping the water content constant, an increase in Na2SiO3 activators by 10–15% and NaOH by 3–5% retarded the workability of samples. Figure 2 presents the influence of NaOH and Na2SiO3 on the workability of the GPM paste.

Figure 2 
                  Influence of NaOH and Na2SiO3 on the workability of mixtures [69].
Figure 2

Influence of NaOH and Na2SiO3 on the workability of mixtures [69].

4.2 Mechanical performance

This section elaborates on several parameters affecting the mechanical characteristics of GWP sourced GPM, e.g., liquid-to-binder ratio (LBR), types and molarity of an alkaline activating solution, calcination temperature, aggregate-to-binder ratio, curing environments, usage of plasticizers, and role of additives.

4.2.1 Influence of calcination temperature

Using varying percentage contents of Na2O by weight of GWP, Tchadjié et al. [70] examined the prospective impact of 2 h long alkali fusion at 550°C. The process mainly comprised the addition of NaOH pallets to GWP in a dry state and mixing them for 5 min, followed by 2 h of calcination. Subsequently, the resulting product was pulverized and sieved at 90 µm to synthesize the GPM. Increasing the Na2O (%) to 60 from 0, increased the reactive phases of GWP powders to 54% from 5.70% as presented in Figure 3(a). Although higher content of alkali resulted in more reactive phases in GPM, excessive alkali beyond 40% had a negative impact on the water resistance and 38% of CS decreased after reaching 40.50 MPa as presented in Figure 3(b).

Figure 3 
                     (a) Amount of reactive phase in GWP and fused materials and (b) CS of GPM pastes at 28 days [70].
Figure 3

(a) Amount of reactive phase in GWP and fused materials and (b) CS of GPM pastes at 28 days [70].

4.2.2 Influence of alkali activators

A previous study [71] investigated the effect of Ca-enriched substances such as ground granulated blast furnace slag (GGBFS) and OPC on the initial strength gain of entirely decomposed granite (CDG) sourced GPM. With long-term weathering and chemical attacks, the authors entirely decomposed the GWP. CDG-OPC and CDG-GGBFS were the two polymers synthesized using Na2SiO3 solution and 14 M NaOH. GGBFS-CDG GPM mix comprising 30% GGBFS with the same molarity of activator exhibited better CS at 7 days with 20.34 MPa, whereas the CS gain of the CDG-OPC mix was comparatively lesser at 19.25 MPa. It was concluded that a high concentration of CaO in OPC and GGBFS favored the production of additional hydrated Ca₂SiO₄ composite, which contributed to the initial strength of CDG-made GPM paste. Tchadjié et al. [70] proposed using the GWP-sourced GPM for low-strength construction materials. To synthesize GWP-sourced GPM, 40% metakaolin (MK), alkali-pretreated GWP, and Na2SiO3 solution were utilized, whereas GWP was preheated up to a temperature of 550°C for 2 h. Not only did reactive amorphous phases increase but also newly formed crystalline phases of Na2SiO3 were formed because of alkali pretreatment. GWP-MK activated by 40% of Na2O showed better CS with 40.50 MPa. However, after 60 days of immersion, resistance against water was compromised due to the large formation of cracks. Other mixtures with 20–30% Na2O demonstrated superior water confrontation, with no cracking appearing after 60 days of immersion. Also, the resulting CS was better and ranged from 10.94 to 21.90 MPa. A previous study [72] utilized alkali-activated slag-granite waste comprising a Na2SiO3 mixture (5% Na2O), NaOH, and SiO2/Na2O ratio of 1.40. The slag in the mixture contained 0, 5, 10, 15, and 20% of GWP. The GPM mix with the addition of 0–20% GWP reduced the CS gradually from 69.60 to 41.90 MPa. Table 2 presents the strength obtained for GWP-sourced GPM synthesized with different binders.

Table 2

Range of CS for GWP-sourced GPM composites

Binding material GWP and OPC GWP and GGBS GWP and GGBS GWP and GGBS GWP and MK
Ref. [71] [69] [72] [70]
Alkali content (%) 14 M (NaOH) 14 M (NaOH) 3–5% NaOH and 10–15% Na2SiO3 5% Na2O 5% Na2O 40% Na2O
Binder ratio 70 GWP and 30 OPC 70 GWP and 30 GGBS 15–20% GGBS 20 GWP and 80 GGBS 15 GWP and 85 GGBS 60 GWP and 40 MK
CS (MPa) 19.25 20.34 30 41.9 57.1 40.5
Curing temperature 60°C 60°C Ambient cured Ambient cured Ambient cured Ambient cured
Curing duration 7 days 7 days 60 h ambient cured and 8 h at 80°C 28 days 28 days 28 days
Heating scheme GWP dried at 105°C GWP dried at 105°C Alkali fusion at 550°C
SiO2/Na2O 1.5 1.5 2.7 1.4 1.4 3.22

4.2.3 Influence of molar concentrations

Tchadjié et al. [70] observed that by increasing the alkali amount from optimum concentration, the CS and water confrontation of GWP-MK-based GPM paste are reduced. With the increase in the alkali content (%) from 10 to 40, of Na2O by weight of GWP, the number of reactive stages and CS of GWP-MK polymers is enhanced. Also, the authors attained the highest CS by using optimal alkali content of 40% of Na2O, and with a further increase in Na2O, it decreased to 21.80 MPa. Reactive phases also improved to 46.40% at 40% of Na2O. However, with time, these results remained stable. Eroshkina and Korovkin [69] noticed that an appropriate amount of NaOH and Na2SiO3 is required for proper workability of slag-sourced GPM and by further increasing the molar concentration beyond the optimum content, workability is lost.

4.2.4 Influence of LBR

GWP-GPM was mostly acquired at an LBR of 0.5–1.2. Tchadjié et al. [70] synthesized such GPM using an LBR of 1.20 that showed an encouraging CS value of 40.50 MPa. Gao et al. [72] considered the CS characteristics of alkali-activated slag composites using different percentages of granite waste with LBR ranging from 0.50 to 0.55. Concerning the influence of GWP, the substitution of up to 15% results in a gradual reduction of CS from 69.6 to 57.1 MPa (by 18%) after 28 days of curing. Further, an increase of up to 20% leads to a more obvious reduction of CS to 41.9 MPa (Figure 4).

Figure 4 
                     CS of alkali-activated composites with BA and/or GWP with (a) LBR = 0.5 and (b) LBR = 0.55 [72].
Figure 4

CS of alkali-activated composites with BA and/or GWP with (a) LBR = 0.5 and (b) LBR = 0.55 [72].

4.2.5 Influence of raw materials

For well cementing, Alvi et al. [73] synthesized many mixes of GWP-sourced GPM by the addition of an appropriate amount of nanomaterials such as the liquid form of MWCNT-OH (hydroxyl-functionalized nanotubes) and alumina-based AL-0450. Similar to those of the reference paste (as presented in Figure 5), an increase in the nanoparticles resulted in significant improvement in both tensile and CS of the GPM. However, compared to that 7 days’ strength, 28 days' tensile strength of composites was influenced by the nanoparticles [7483]. Therefore, the long duration of curing affected the mechanical strength and flexibility of GPM when the nanomaterials were added to the mix.

Figure 5 
                     Mechanical properties of the GWP-GPM paste: (a) CS and (b) tensile strength [73].
Figure 5

Mechanical properties of the GWP-GPM paste: (a) CS and (b) tensile strength [73].

4.2.6 Influence of the sand-to-binder ratio

GWP-MK GPM mortars synthesized by Tchadjié et al. [70] had an AGBR of 2.75:1 and an activator modulus of 3.22. Their test sample obtained the highest CS value of 40.50 MPa. On the other hand, Eroshkina and Korovkin [69] noticed the highest CS of 30 MPa for GPM mortars with a slag-GWP binder having a fine aggregate-to-binder ratio of 2:1.

4.2.7 Influence of curing

The improvement in both CS and flexural strength of GPM was achieved by Eroshkina and Korovkin [69] with a curing time kept from 20 to 60 h and the temperature raised to 80 from 60 (before heat treatment of the mortar as shown in Figure 6). Authors noticed that both, the initial curing period and curing temperature, have a great impact on the flexural and CS of the GPM mortar comprising binders with magnetic source, e.g., granite waste. Zha and Zhu [71] synthesized CDG-GGBS and CDG-OPC GPM with a curing temperature of 60 and 7 days of curing duration. Conforming to these test conditions, the CDG-GGBS GPM mix attained a better CS in compression with 20.34 MPa, which was comparatively higher than that obtained from CDG-OPC GPM subjected to 7 days of thermal treatment.

Figure 6 
                     Mechanical properties of the slag-GWP-GPM paste at different curing temperatures: (a) CS and (b) flexural strength [69].
Figure 6

Mechanical properties of the slag-GWP-GPM paste at different curing temperatures: (a) CS and (b) flexural strength [69].

4.2.8 Influence of molar ratios

Better strength properties are obtained by a geopolymerization reaction of the activator modulus or silicate ratio (SiO2/Na2O), which can be achieved with the addition of an appropriate amount of NaOH/Na2SiO3 solution. The highest CS of 20.34 MPa was attained by Zha and Zhu [71] by using a SiO2/Na2O ratio of 1.50 for CDG-GGBS GPM. Likewise, Tchadjié et al. [70] synthesized a new type of GPM comprising SiO2/Na2O ratio of 3.2 with 10–60 (%) changing Na2O content for GPM. It comprised MK and granite waste and gained the highest CS of 40.50 MPa. GWP-GGBS-sourced GPM was synthesized by Eroshkina and Korovkin [69] with a SiO2/Na2O ratio of 2.70. The resulting product showed the highest CS value of 30 MPa. Gao et al. [72] observed that by reducing the SiO2/Na2O ratio to as low as 1.40 for slag-GWP-GPM, CS increases to 41.90 MPa.

4.2.9 Influence of plasticizers

In the early stages, GWP was used as a cement substitute but it caused a dispersing problem during mixing, and due to the presence of free water content, its usage was limited. Gao et al. [72] deliberated the workability features of alkaline-activated slag composites. They utilized GWP to replace the cement and assessed its impact on workability. In this study, waste BA was dried to eliminate the free water to secure a constant starting condition. The sticky GWP was first dispersed in water with the accumulation of a superplasticizer, and this pre-dispersion procedure led to a well-dispersed GWP in water, which can be used directly in mortar production.

4.3 Microstructural properties

Gao et al. [72] conducted a microstructural analysis of slag-sourced cementitious composites. These composites were developed with a combination of different solid wastes such as GWP and municipal solid waste incineration (MSWI) bottom ash (BA). By increasing the water requirement, the porous nature of the BA adversely influenced the mortars’ strength. However, during the alkali activation process, GWP hindered the construction of primary reaction by-products. Likewise, the reaction kinetics indicated that the addition of two industrial waste materials either in the form of binders/aggregates decreased the overall heat release, as presented in Figure 7.

Figure 7 
                  Normalized heat flow of alkali-activated composites, waste BA, and GWP [72].
Figure 7

Normalized heat flow of alkali-activated composites, waste BA, and GWP [72].

The fabricated specimens with only alkali-activated slag presented a homogeneous paste, which can be a sign of a reaction product having high strength. For the control samples with alkali-activated slag only, the equally dispersed angular-shaped phases portrayed the partly reacted anhydrous slag particles that are bounded by the reaction products, as shown in Figure 8. Replacement of 20% slag resulted in no significant change in the morphology of the matrix. By replacing the alkali-activated slag with normal sand, the aggregates were well surrounded by the mortar, and a well-connected interfacial transition zone (ITZ) was detected. Furthermore, the addition of BA in place of the slag resulted in a lower CS and porous structure. The porous structure can also absorb a certain content of the activator solution after mixing and then influence the early age reaction and bound water quantity to some extent. Also, Tchadjié et al. [70] studied the microstructure of raw GWP and alkali thermal pretreated or alkali-fused GWP. The raw GWP experienced reduced suspension in alkali solutions and ultimately resulted in a reduced geopolymerization process. The fused GWP with different amounts of Na2O showed modified mineral composition, resulting in the development of Na-enriched reactive stages. These stages favored the initiation of extremely reactive Si and Al and enhanced the speed of geopolymerization activity.

Figure 8 
                  SEM images of mixtures of samples at 100 µm with (a) alkali-activated slag only, (b) 20% GWP replacement, (c) normal sand, (d) larger-sized BA particles, and (e) smaller-sized BA particles [72].
Figure 8

SEM images of mixtures of samples at 100 µm with (a) alkali-activated slag only, (b) 20% GWP replacement, (c) normal sand, (d) larger-sized BA particles, and (e) smaller-sized BA particles [72].

5 Use of BR

Being an alkaline and great source of GPM, BR comprises aluminosilicates and results in inorganic polymer composites by activating the alkali; this is also defined as geopolymerization. But to attain higher levels of strength, alkali solutions including Na2SiO3 and NaOH are required. Because the raw products have a lower SiO2/Al2O3 ratio and are poor enough to react during geopolymerization, therefore to improve their reactivity, Manfroi et al. recommend their finer grinding at elevated temperatures of 800–900°C [84] or adding them with different substances with activated SiO2 [85]. BR has been widely applied as a binding material along with different admixtures such as MK, arsenic sludge (AS), municipal solid waste, rice husk ash, FA, GGBFS, coal gangue (CG), etc. [39]. A previous study reviewed the usage of BR to yield alkali-activated composites including hybrid alkali-activated mortar, GPM, and inorganic polymers [86]. The current study primarily targets the characterization of BR-based synthesized GPM by covering all important factors influencing the process, e.g., workability and setting time (ST), mechanical properties, thermal performance, and durability properties as well as that of the microstructure. Table 3 shows the worldwide production of BR in different years. Figures 9 and 10 present the patent distribution and other studies on BR applications in different areas from 1964 to 2018. Among these, BR has been extensively utilized as a raw material in wastewater treatment, catalysts, buildings, and adsorbents.

Table 3

Worldwide production of BR from 1970 to 2019 [88]

Country Production year (thousand metric tons)
1970 1980 1990 2000 2010 2016 2017 2018 2019
Australia 9,255 27,180 41,390 53,800 68,530 83,515 89,420 96,545 105,310
Brazil 500 4,630 9,750 14,380 32,030 39,245 38,120 32,005 32,005
China 510 1,750 3,650 7,950 36,830 66,150 68,390 68,390 68,410
Guinea 2,610 13,910 16,150 17,990 17,630 32,425 51,700 59,575 63,230
Guyana 3,210 3,050 1,420 2,690 1,080 1,480 1,460 1,925 2,005
Indonesia 1,220 1,249 1,164 1,151 27,410 1,458 4,400 10,500 10,500
India 1,370 1,780 4,850 7,560 12,660 24,220 22,775 23,230 26,050
Jamaica 12,015 1,198 10,960 11,125 8,545 8,545 8,240 9,965 9,000
Kazakhstan 990 NA NA 37,730 5,315 4,800 4,845 6,105 3,810
Russia NA NA NA 5,000 5,470 5,430 5,525 5,655 5,570
Saudi Arabia 6.0 NA NA NA NA 4,465 3,705 4,325 4,325
Sierra Leone 450 670 1,140 NA 1,050 1,370 1,790 1,940 2,000
Vietnam NA NA NA 16 80 1,500 2,700 3,600 3,600
Others NA NA NA 13,540 121,560 15,350 10,960 9,230 9,700
World 5,725 93,270 115,010 138,890 228,800 289,970 314,040 332,985 345,535
Figure 9 
               BR applications [87].
Figure 9

BR applications [87].

Figure 10 
               BR utilization rate in various applications for the period from 1964 to 2018 [87].
Figure 10

BR utilization rate in various applications for the period from 1964 to 2018 [87].

5.1 Fresh properties

The Na2O/Al2O3 ratio, silica/alumina ratio, and LSR of the GPM affect the ST of BR. To assess the impact of changing the concentration of the Na2SiO3 solution on BR-dependent GPM’s ST, Ahmed et al. [89] obtained SiO2/Al2O3 of 3.6, 4.0, and 4.4, respectively. It was also observed that with an increase in the SiO2/Al2O3 ratio to 4, initial and final ST also increased and it declined with a further increase. This increase in the ST may be associated with the silica–silica reaction that takes place when the amount of silica is increased. The process is not as rapid as that of the silica–aluminum reaction. However, the initial and final ST of BR-GPM dropped when Na2O/Al2O3 was increased from 1.5 to 1.7. This increase in alkalinity reduced the workability, resulted in rapid setting, and led to a significant decline in the CS of test samples. Increased ST was observed for BR-GPM comprising a higher LBR of almost 0.6. Reducing this ratio further to 0.50 and 0.55 led to setting the GPM more rapidly.

Nie et al. [4] manufactured the BR-FA-GPM using the original BR with a pH of 12.5 and desulfurized BR (DRM) having a pH of 4.5. DRM waste is produced when BR is used in flue-gas desulfurization (FGD) for burning coal in power plants and to eliminate SO2 from acidic gases to minimize the pollution level. It primarily reduces the BR’s alkalinity by using the BR’s alkali content to neutralize the acidic flue gases. Alkaline activators having a concentration more than those required for the optimum level also influenced the ST of GPM at two different pH values. The GPM derived from the original BR exhibited increased ST beyond the optimum concentration level of 2.5 M of alkali, while DRM GPM experienced this increase in their ST beyond 3.5 M of NaOH solution. When BR was added to GPM with FA containing rich calcium content, ST for the binders increased significantly. Likewise, in comparison to FA-derived GPM with a lesser ST of 3 min, BR-FA with a 50:50 mix ratio increased to almost 3 h. Therefore, not only chemical properties but also the source of aluminosilicate affects the GPM’s LST.

Lemougna et al. [7] developed the GPM using the BR-slag and tested it for the ST by increasing the BR content up to 75%; they observed a significant increase in ST with an increase in the BR content. However, test results showed that with 75% of BR in BR-slag GPM, the initial and final STs were 57 and 146 min, respectively. Being less reactive, when compared with the slag, BR delays the course of hardening when BR is increased. Pan et al. [90] analyzed the ST of alkali-activated slag-BR cementitious material (ASBC) concerning a 525 OPC of GB 175-1992 Chinese standard. Experimentation showed that cementitious composites comprising 30% BR resulted in 62 and 95 min of initial and final STs, respectively. The OPC material achieved higher ST when compared to that of the ASBC (257 and 181 min, respectively, as per Chinese code GB 175-1992). The ST decreased when BR was added to the GPM system.

Kim et al. [5] analyzed the workability of a mix comprising BR-FA binders by using a mini-slump and visual interpretation and found that flowability tends to reduce when more than 20% of BR was added. Researchers also studied the impact of NaOH and water on the flow ability of the test paste. An increase in the water-to-binder ratio from 0.40 to 0.48 increased the flow diameter by approximately 17%. Because of the dispersing characteristics of NaOH, flowability also improved when NaOH was added at 1, 3, and 5%. Moreover, the addition of NaOH was more advantageous than increasing the water content to gain enough strength and workability. Also, the mean particle size affected the workability and ST of BR-based GPM. Zhang et al. [91] observed the characteristics of GPM comprising BR with different particle sizes such as 7, 13, 20, 30, and 43 µm. Test results showed that the finer particles in BR changed their morphology to spherical or ellipsoidal shapes. Finer particles were highly reactive with improved dissolution efficiency of aluminosilicates. Also, they tend to have an improved rate of geopolymerization while coarser particles exhibited the formation of GPM composites with increased contents of silicates. An increase in the mean particle size resulted in a decrease of dissolution efficiency and led to enhance the initial and final STs of GPM. The workability of the GPM initially reduced when the mean particle size (µm) was increased from 7 to 20 and it improved thereafter. This increase in the fluidity of the GPM of BR7 and BR13 may be associated with the morphologic effects in comparison to those of BR20 GPM.

Li et al. [92] studied the influence of gypsum types on the flowability of alkali-activated BR-slag grouting composites. Several pastes were developed from BR-slag-phosphogypsum (PG), BR-slag-FGD gypsum, and BR-slag-gypsum dihydrate (NG) amalgamation. It was observed that not only did the rheological properties including initial and final STs decrease but also the flow diameter decreased by increasing the gypsum in all the concrete mixes. NG considerably affected the BR-slag grout’s workability but FGD’s influence on the fluidity was the least. Moreover, for all the samples of concrete mix, BR-slag grout ST experienced significant reduction initially up to an optimum gypsum level but after that it increased. NG had a noticeable impact on ST but PG’s influence was the least represented. Figure 11 shows the impact of varying gypsum contents on the initial and final STs of BR-dependent slag grout samples.

Figure 11 
                  ST of the BR-slag mortar having various kinds of gypsum: (a) initial ST and (b) final ST [92].
Figure 11

ST of the BR-slag mortar having various kinds of gypsum: (a) initial ST and (b) final ST [92].

5.2 Mechanical performance

This section discusses the impact of many parameters including but not limited to calcination at varying temperatures, activator solutions, the ratio of binder/sand, curing duration and temperature, usage of plasticizers, the molarity of the activator, the ratio of NaOH/Na2SiO3, molar ratios of chemical composites, and the ratio of liquid/solid which affects the mechanical properties of the BR-made GPM paste.

5.2.1 Influence of the calcination temperature

Being poorly reactive, BR is frequently utilized after the calcination process at higher temperatures. The process ultimately dissolves the SiO2 with Al2O3 significantly by enhancing the Si and Al in BR to accomplish higher levels of CS. Calcination decomposes the three crystalline phases of Al, Ca, and Fe by calcination via dehydration, dehydroxylation, and carbonation in different ranges of temperatures. Transformation of these phases converts the crystalline-based Al, Ca, and Fe to other phases such as aluminum oxide phases, AlNa12SiO5 phases, gehlenite crystalline phases, and alkali-enriched nepheline stages [89]. The addition of the alkali or thermal pretreatment for the alkali activation before calcination makes BR more reactive and enhances the formation of glassy and amorphous stages.

Hu et al. [12] developed BR-based GPM utilizing FA, pretreated BR specimen with alkali-thermal pre-activation along with a solution of Na2SiO3 activators. Researchers emphasized the encouraging aspect of thermally pretreated alkali or BR’s calcination to geopolymerize and strengthen the BR-dependent GPM. The BR has no active participation in the geopolymerization process and comprises Si and Al traces in crystalline forms. Pretreating the alkali with thermal pre-activation or calcination of alkali-treated BR at elevated temperatures ranging from 600 to 900°C makes the BR reactive and dissolves the SiO2 and Al2O3. Soluble, alkaline, and sodium-rich nepheline and peralkaline aluminosilicate formation in alkali thermal pretreating stages of BR increase the Na2O by 5–10%. Being an important hydraulic component of BR-dependent GPM, the peralkaline phase improves the strength properties. Figure 12 highlights the dissolution efficacy of SiO2 and Al2O3 in alkali mixtures subjected to various ranges of calcination temperatures. The optimum dissolution efficacy was obtained at 800°C. Ye et al. [93] observed the impact of temperature for the calcination process on the CS of GPM comprising BR and GBFS with a 5:5 wt ratio. Increasing the temperature from 100 to 800°C leads to an increase in the CS from 17.50 to 49.20 MPa and thus influences the conversion of mineral phases of BR by forming latest developed phases with higher solubility levels within the alkaline atmosphere. Calcination of BR enhances the development of good soluble aluminosilicates leading to a dynamic suspension in an alkali environment and ultimately improves the geopolymerization process.

Figure 12 
                     Influence of calcination temperature for dissolution efficacy of (a) Al2O3 and (b) SiO2 in an alkali solution [12].
Figure 12

Influence of calcination temperature for dissolution efficacy of (a) Al2O3 and (b) SiO2 in an alkali solution [12].

Ye et al. [94] established OGPs using alkali pre-thermal pre-activated BR as well as SF. After drying at 105°C and mixing the BR with NaOH pellets, the calcination process was carried out at 800°C for 1 h duration. Pretreating the BR not only contributed to achieving appropriate hardening of the design mix after 24 h but was also found effective in developing the early (3 days) CS of 7.5 MPa. GPM mixtures without alkali pretreatment in BR exhibited no strength after 24 h of casting. Twenty-eight days of curing of BR-dependent OPG portrayed a CS of 31.5 MPa when 25% of SF was added to the mix. A previous study [62] developed BR-MK-derived GPM and emphasized the favorable impact of the calcination process to dissolve the aluminosilicates effectively. After drying the as-received BR at 100°C for almost 1 h, calcination was then carried out for 3 h at 800°C. The 24 h cured GPM comprising 20% of calcined BR at 60°C curing temperature followed by 25°C for 2 months demonstrated a higher CS with 14.20 MPa. To effectively dissolve the alumina and silica traces in an alkaline atmosphere, pretreating the alkali with thermal pretreatment appeared preferable in establishing higher levels of CS.

5.2.2 Influence of alkali activators

The popular alkaline activators employed in the polymerization process include alkali silicates and alkali hydroxides [95] comprising KOH or NaOH and Na2SiO3 or K2SiO3, which are the most commonly utilized in GPM. Si and Al types from aluminosilicates’ precursors actively dissolve in the alkali mixture. He et al. [96] investigated the structural behavior and microstructure of BR-FA derived GPM (BR-GPM), activated with Na2O⋅3SiO2 powder having a molarity of 1.5 M with varying contents of BR and FA weight ratio in the GPM. They also compared it with MK-based GPM (MK-GPM), which was activated with NaOH and Na2SiO3 solution. MK-GPM exhibited relatively a greater CS of 31 MPa. This increase in CS may be attributed to its higher pH value, which was even higher than 14. This pH was mainly subsidized by the addition of the NaOH mixture of 6.7–7.8 M, whereas BR-GPM (pH of 11.9) showed the largest CS of 13 MPa. Interestingly, this strength was obtained without the addition of extra NaOH and by only employing the remaining NaOH (20.2 wt%) available in raw BR. Likewise, He and Zhang [97] reported the structural behavior of BR-FA-GPM with two diverse silicate solutions, such as Na2SiO3 and Na2O⋅3SiO2 solutions. GPM activated using trisilicate solution showed more stiffness, more strain, and also improved CS. The availability of higher reactive silica in the solution supported the geopolymerization process better. Similarly, He et al. [8] developed the GPM using BR and rice husk ash and further activated it with NaOH to investigate the mechanical properties. They found that without Na2SiO3 solution, GPM showed a maximum CS of 20.5 MPa. Moreover, because RHA contains rich traces of reactive amorphous silica, Na2SiO3 or Na2O⋅3SiO2 solutions for BR-RHA GPM are irrelevant.

A previous experimental investigation produced an ASBC comprising 70% slag and 30% BR, activated with solid water glass (8% by weight of binders) and sodium aluminate clinker (8% by weight of binders) [90]. They evaluated the strength characteristics of ASBC and its resistance against chemical attacks concerning a 525 OPC (as per GB 175–1992). The CS obtained with ASBC was comparable with the strength developed with OPC. The ASBC showed a higher CS of 56 MPa with 28 days of curing period. Over the same period, the material’s bending strength improved to 8.4 MPa exhibiting inferior density, greater water requirement, and shorter ST. Its resistance against corrosion attacks, free–thaw cycles, and carbonation remained in comparison to that of 525 OPC. Hu et al. [12] prepared BR-GPM using alkali-thermal pretreated BR and FA by mixing BRs with dry alkali or solid NaOH pills resulting in calcination at 800°C for a 1 h duration. The pretreatment significantly enhanced the reactivity of Si and Al in BR. This further improved the dissolution efficiency in an alkaline solution resulting in maximum CS up to 23.8 MPa at 5% Na2O, whereas BR-FA-GPM without thermal pretreatment showed much lower strength, i.e., 5 MPa.

One-part GPM (OPG) includes “just add water” GPM. These are developed by mixing the water right into the ready-mix GPM binders [98]. OPG utilizes different solid alkaline activators, for instance, hydroxides of calcium and lithium, Na2SiO3, Na₂O, K2CO3, and their mixtures [99]. Ke et al. [98] pretreated the alkali of BR with powdered alkali activators to obtain BR-based OPG with 10, 15, and 5% of Na2O at 800°C for 1 h. With thermal treatment, silicates and aluminosilicates decomposed efficiently improving the reactive phase formation and resulting in peak 7 day CS of up to 9.8 MPa at 10% Na2O accumulation. On the other hand, alkali addition adversely influenced the long-term strength of purely BR-based OPG. Figure 13 portrays the CS of BR-GPM at different curing periods with varying Na2O contents in alkali [12,98]. This strength decreased due to excessive alkali hindering the formation of the Si–O–Si bond for both the GPM once an optimal amount of alkali was obtained.

Figure 13 
                     CS of BR-GPM with varying amounts of Na2O [12,98].
Figure 13

CS of BR-GPM with varying amounts of Na2O [12,98].

Lemougna et al. [7] produced BR-slag GPM in 75:25, 50:50, and 25:75 mixing ratios of BR and slag. They developed all the mixes with solid NaOH and Na2SiO3 solution and investigated their use in lightweight materials and mortars. The GPM’s CS of 50:50 mix samples tested at an ambient curing temperature had an upward-growing effect. This pattern of increasing strength was found to vary from 65 to 85 MPa and was associated with increments in silica modulus (SM) of the activator mixture ranging from 1.60 to 2.00. Beyond this optimum level of silica, the strength decreased to 60 MPa. This decrease in strength may be associated with the excessive silicates hindering the evaporation of water and breaking the GPM chain into different monomers, accordingly decreasing the strength. Zhang et al. [100] synthesized BR-FA-GPM using a 1.5 M Na2O⋅3SiO2 solution without NaOH and assessed the GPM’s potential feasibility for its application in pavement materials because of its strength developed to 13 MPa. Li et al. [101] investigated the strength parameters of BR-sourced composite materials (BCM) with AS. They concluded that the activator lime significantly affects the BCM unconfined CS (UCS). Because the AS predominantly comprises calcium sulfate, it promotes hydration products. Also, when BR reacts with lime, the sludge activates the BR. Binders of 28 days without activators showed a UCS of only 5.3 MPa. Due to the utilization of the lime in the test mix, amorphous ettringite under ambient circumstances was developed with a binder/lime ratio of 94:6, which led to an ultimate increase in UCS of up to a maximum of 12.05. Guidelines followed for BCM strength standards were in line with those suggested by MU10 FA brick (JC239-2001). A previous study [102] developed FA-derived inorganic OPG by utilizing BR as a source of NaOH or an alkaline activator. Comparing the CS of BR-dependent inorganic OGP with that of FA-based OGP activated with NaOH pallets, researchers found that the addition of 3–5% of NaOH in FA-based OGP exhibited almost the same pattern in comparison to those obtained by the addition of 40–60% BR in FA-based inorganic GPM.

Ye et al. [94] innovatively established OGPs with SF and BR by alkali-thermal pretreatment at 800°C for 60 min and then subjected the samples to cool at normal room temperature. A number of these BR specimens were obtained by pretreating the alkali with 10 and 15% of Na2O. GPM comprising 75% of alkali-pretreated BR activated with 10% of Na2O showed higher strength in compression; 20 days’ strength was a maximum of 31.5 MPa. Mucsi et al. [103] investigated 0.476 mol·l−1 of alkali content in BR and observed its impact as an alkali and FA substitute in GPM derived from FA. The FA-based GPM with zero proportion of BR, activated with 6 M NaOH solution, showed a relatively lower strength of almost 2.6 MPa. It was found that the alkali content finally decreased by various percentages as FA was substituted by BR, which was gradually added to the GPM in different increments from 5 to 30% with increments of 5%. FA was substituted with 5% BR, and a 40% NaOH activator solution was added. The amount of NaOH added was decreased to 35% by the consequent accumulation of 10, 15, and 20% BR. Only 30% of NaOH was added to the GPM mixes containing 25 and 30% BR. Substituting the FA with 15% BR and curing the samples at 90°C for 3,600 min resulted in 7 days’ CS of 5.5 MPa.

Zhou et al. [104] developed GPM using waste mudstones, BR, and GGBS activated by the mix synthesized from NaOH and Na2SiO3 solutions. This GPM was prepared to utilize the refuse mudstones and those of alkali activators in different contents (%), e.g., refuse mudstones were in the range of 30, 50, and 70, whereas the latter constitutes varied from 10 to 30 with increments of 5; however, GGBS/BR ratio was kept to 7:3. Experimentation revealed that in comparison to the GPM strength obtained from varying percentages of alkali activator, variation in the refuse mudstones significantly influenced the strength. Alkali activators affected by the refuse mudstone influenced geopolymerization. Refuse mudstone is an inactive substance with crystalline mineralogy that severely influences both the mechanical properties and the geopolymerization process. Nevertheless, GPM with 20% alkali and 30% refuse mudstone content showed the highest strength value of 23.86 MPa.

Hu et al. [105] recommended not to use only NaOH but they suggested the use of NaOH and Na2SiO3 solution for maximum attainment of CS. BR being alkaline in nature improves the geopolymerization process; however, addition of additional NaOH is always recommended for higher strength levels. Therefore, based on the published work as cited, it is obvious that a mix comprising Na2SiO3 and NaOH solution frequently forms BR-dependent GPM. Being alkaline in nature and utilizing the available residual NaOH to synthesize the GPM, NaOH consumption is always less in BR-dependent GPM binders. This drop is much lower when compared with those of the binders derived from FA, slag, MK, etc. Interestingly, in situations where BR comprises more than 20% residual NaOH, Na2SiO3 solution is sufficient to synthesize the GPM without extra sodium hydroxide.

5.2.3 Influence of binder/sand ratio

Lemougna et al. [7] synthesized GPM mortars using ¼, ½, and ¾ sand proportions for slag-BR mud systems. Importantly, due to the weak interfacial connection between GPM’s internal structure and sand particles, 28 days’ strength of the mortar decreased with an increase in the sand content for all the slag-sourced mixes comprising 25, 50, and 75% BR proportion at a curing temperature of 25°C. Figure 14 shows the CS of the slag-BR-GPM paste with different sand contents.

Figure 14 
                     CS of the slag-BR-GPM paste with different sand contents [7].
Figure 14

CS of the slag-BR-GPM paste with different sand contents [7].

Nevertheless, the addition of a higher content of slag amounting to 75% significantly impacts the mortars’ strength. It was recommended to use the slag-BR-GPM mortar in the construction industry, particularly for low-budget units. As it is known that increasing the sand decreases the strength of the mortar, Singh et al. [106] prepared a new type of GPM bricks by partial utilization of the GBFS in place of sand and also by FA and BR. Figure 15 shows the resulting strength (both dry and wet) developed with varying ratios of binder to aggregates (BTA).

Figure 15 
                     Influence of the ratio of binder/fine aggregate on CS of PM bricks: (a) 1:1 and (b) 1:2 [106].
Figure 15

Influence of the ratio of binder/fine aggregate on CS of PM bricks: (a) 1:1 and (b) 1:2 [106].

Considering the BTA of 1:1 and 1:2, a higher concentration (%) of GBFS with 0, 20, 30, 40, and 50 was utilized in replacement of sand. With the increase in the BTA, GPM with BR content (%) of 10, 30, and 50 showed decreased strength. To achieve the maximum wet and dry CS of 9.50 and 11.10 MPa, respectively, 30% BR and 1:1 BTA was required. The CS was further increased to 15.50 MPa by using 50% of BR and 1:1 BTA with 50% GBFS. The highest CS of 23.86 MPa was achieved by introducing the GPM composite mortar, which was made up of BR, GGBS, and standard sand as aggregate with 1:1 BTA. Also, refuse mudstone and alkali activators were added to act as varying parameters in the mix [104].

5.2.4 Influence of curing

Singh et al. [19] investigated the strength of BR-sourced FA-GPM with two different BRs, i.e., unprocessed and processed BR. Both GPMs were subjected to ambient and thermal curing conditions. Compared to thermal curing conditions, ambient curing of BR-FA geomaterials comprising 30% BR showed a higher CS of 40.0 MPa with 6.0 M NaOH. Because thermally cured specimens experienced several crack formations, researchers suggested that GPM synthesized with pulverized BR should not be exposed to thermal curing. Likewise, to develop the highest CS with 38 MPa via thermal curing, unprocessed BR-sourced GPM needed greater concentration with up to a value of 12 M NaOH. Hajjaji et al. [61] observed BR-MK GPM’s mechanical properties using a thermal curing approach by keeping the temperature at 50°C for a whole day after maintaining the room curing temperature for the upcoming 24 h followed by 28 days of water curing. To investigate the impact of curing duration, GPM was tested for CS development at both stages of 24 h curing and 28 days curing. The GPM samples comprising maximum BR concentration (MK/BR ratio of 1:12 and 1:10) exhibited 25% higher strength after 28 days in comparison to that obtained with 24 h of testing. However, other mixtures having an MK/BR ratio of 1:6 and 1:4 resulted in a negligible increase of strength (with only a 10% increase in strength) from 1 to 28 days.

Pan et al. [90] found an increasing trend for the two types of strengths, i.e., in compression and in bending for ASBC subjected to a long-term period of 180 days of curing. Figure 16 presents the formation of the ASBC strength in bending and in compression. Zhang et al. [107] examined the durability of BR-FA-GPM (RFFG) subjected to H2SO4 and deionized water (DW) in varying conditions of curing temperatures, i.e., under an elevated temperature of 80°C and at normal room temperature. Researchers carried out different tests to investigate the leaching potential of GPM soaked in DW and SA for 128 days. With the leaching experiments, it was observed that the identified heavy metals were within the acceptable standards set by US EPA. GPM subjected to curing at 80°C performed comparably to that of GPM in ambient curing conditions derived from concentrated heavy metals, e.g., Cd, Cr, Cu, and As found in leachates. Leaching in BR-sourced GPM remained independent of thermal curing. Zhao et al. [108] investigated the impact of varying curing environments on the durability and mechanical characteristics of GPM developed from BR slurry and class F FA (RMSFFA). Exposing the 50°C cured test specimen to freezing–thawing cycles had improved durability and strength properties in comparison to those of room temperature and 80°C cured specimen. On the other hand, RMSFFA-GPM was more resistant to freezing–thawing cycles and exhibited the highest CS at a curing temperature of 50°C. Likewise, in comparison to those of 28 days cured specimen, 14 days cured GPM showed higher resistance against the freeze–thaw environment (of 50 cycles) without any notable reduction in strength (Figure 17).

Figure 16 
                     Mechanical properties of the ASBC composite: (a) flexural strength and (b) CS [90].
Figure 16

Mechanical properties of the ASBC composite: (a) flexural strength and (b) CS [90].

Figure 17 
                     Effect of curing conditions on UCS of RMSFFA composites [108].
Figure 17

Effect of curing conditions on UCS of RMSFFA composites [108].

Panias et al. [109] investigated the influence of curing conditions on CS of BR-MK-sourced GPM. At all curing temperatures between 80 and 40°C, it was revealed that GPM dried more rapidly during the first 3 h of curing. After 96 h of curing, the drying rate entirely decreased. Increasing the temperature of curing to 80°C from 60°C resulted in more notable cracks. At an optimal curing temperature of 60°C, 96 h of cured BR-MK GPM exhibited better strength in reduction with minor cracks at a moderate rate of drying. Considerable shrinkage was found at almost all the ranges of temperature during the first phases of curing where the drying rate was comparatively higher. The authors examined the mechanical characteristics of a GPM derived from MK and BR at various curing conditions, including room temperature, 50°C for 24 h, and 80°C for 5 h. Increasing the curing temperature resulted in a drop in both, i.e., CS and bulk density. This loss in CS and rapid hardening with the dissolution of GPM may be associated with lower ratios of silica/alumina, and the development of notable cracks in the mix due to considerable loss of water along with the development of voids at elevated curing temperatures. Furthermore, the addition of inert fillers such as sand enhances the amount of other inert fillers available in the GPM BR ultimately resulting in debonding and reduction in strength.

Nie et al. [4] noticed that increasing the curing age resulted in a consistent pattern in the strength of BR-FA-GPM sourced from both the novel and desulfurized BR. With the increase in the curing duration to 28 from just 3 days, BR-GPM and desulfurized-BR-GPM CS gradually increased to 15.20 from 6.00 MPa and 23.20 from 7.00 MPa, respectively. According to He et al. [8], BR-RHA GPM needed a prolonged period, i.e., 35 days for complete curing to develop the highest CS of 11.82 MPa. This outcome supports the findings of Sekou et al. [110] that deal with 33 days of cured BR-supported GPM with rice husk ash acting as an additive to gain the highest strength of 11.0 MPa. To attain maximal stiffness and strength, GPM with raw materials containing significant quantities of unreacted amorphous stages and non-reactive crystalline segments must be allowed to cure for longer periods. Lemougna et al. [7] obtained reasonably comparable CS ranging from 55 to 60 MPa using 7 days cured BR-slag GPM comprising 50% BR at standard curing conditions. Increasing the BR to 75% resulted in a significant decrease in CS of 10 MPa at 7 days, whereas, with the same content of BR, 28 days BR-slag GPM showed a maximum CS of 30 MPa. Therefore, it was concluded that to attain this strength with more than 50% BR, a minimum of 28 days of curing period is mandatory. Likewise, curing temperature ranging from 25 to 60°C also affects the GPM’s strength. GPM comprising BR up to 50% exhibited the highest CS of 85 MPa at 40°C, but with additional BR content of more than 50 strength was finally decreased. Commonly, heat curing yields rapid dissolution of silica–alumina composites with faster development of the GPM composite. Nevertheless, the source materials determine the threshold limits of the temperature, beyond which GPM is set rapidly due to inadequate dissolution and quick geopolymerization reaction that ultimately reduces the final strength. Bădănoiu et al. [111] examined the early age of 3 days CS of GPM comprising BR and waste glass (WG) powder activated with 5.0 M NaOH at 60°C curing temperature. The CS of composite materials, comprising 25% of BR instead of glass powder, improved as the curing duration increased. GPM, which was cured at 60°C and was 3 days aged, attained the highest CS of 16 MPa. However, with 1, 2, and 3 days of curing at 60°C, with subsequent curing up to 20°C for 7 days, the CS of the composites reached 15.90, 18.50, and 20.50 MPa, respectively.

Hoang and Do [112] investigated the advantageous influence of autoclaving with extreme pressure and higher temperatures on the dissolution efficiency of aluminosilicate composites. Instead of high-temperature curing under atmospheric pressure, this approach resulted in better strength of BR-FA-GPM. Without any additional NaOH,10 h of autoclaving at 201°C, under atmospheric pressure of 1.60 exhibited a better CS of 14.20 MPa. Additionally, with a pressure of 1.22 and 16 h of curing at 188°C, the CS increased to 20.10 MPa when 1 M NaOH was added. Researchers suggested autoclaved BR-FA-GPM for the masonry construction. Figure 18 represents the impact of curing conditions on the 7-day UCS of BR-FA sourced GPM’s base materials [113]. The mechanical behavior of these materials was assessed in comparison with those of FA-derived GPM and conservative lime-FA and cement-FA sourced stabilizing composites. Increasing the temperature to 38°C from 20°C resulted in better CS of BR-FA-GPM ranging from 10.50 to 16.10 MPa. The reported strength was much higher than that obtained for the mix prepared by utilizing conventional resources. However, decreasing the humidity levels (%) to 45 from 98 adversely influenced the CS.

Figure 18 
                     Impact of curing conditions on the 7-day UCS of BR-FA sourced GPM composites [113].
Figure 18

Impact of curing conditions on the 7-day UCS of BR-FA sourced GPM composites [113].

5.2.5 Influence of plasticizers

To synthesize OGPs from SF and BR, Ye et al. [94] adopted a WSR in the range of 0.55–0.65. When the water retarder, 0.50% (by wt) sodium lignosulfonate (SNF),was added to regulate the mix’s workability, WSR decreased to 0.55, 0.50, and 0.45. As shown in Figure 19, the addition of 0.50% (by wt) dispersant SNF aided in the reduction of WSR to 0.45, to gain the highest 28 days CS of 31.50 MPa, and to impact the pH of binders that was reported to be higher in comparison to that of the GPM binders having no SNF.

Figure 19 
                     Effect of 0.5% SNF on WSR and CS of BR-GPM pastes [94].
Figure 19

Effect of 0.5% SNF on WSR and CS of BR-GPM pastes [94].

Li et al. [114] examined the BR-slag GPM grouting substances with several types of plasticizers including naphthalene-based superplasticizers (SPN), aliphatic-superplasticizers (SPA), and polycarboxylate-superplasticizers (SPC), and investigated their mechanical characteristics along with workability properties. Compared to SPC, SPN and SPA remained highly stable when subjected to alkaline conditions. Researchers found that the geopolymeric grouting substances showed improved fluidity when superplasticizers in various ratios of water to binders were added. SPN and SPA were more workable with better strength when the water-to-binder ratio was decreased. However, SPC performance remained poor due to less stability with an adverse impact on the CS.

5.2.6 Influence of molar concentrations

Concentrated alkali activators, e.g., NaOH, play a vital role in the rapid dissolution of aluminosilicate traces to expedite the process of geopolymerization and thus yield binders with better stiffness and higher strength [96]. Among these activators, utilizing 0–16 M of NaOH is considered an effective and frequently adopted approach for the geopolymerization of various aluminosilicate traces in different molar ratios [8,98,102]. Kim et al. [5] utilized NaOH mixture in 5, 3, and 1 wt% in BR-CNF (a combination of Na2CO3, Ca(OH)2, and FA) amalgamated mixture, which led to pore size improvement, higher flowability, enhanced CS, better geopolymerization process, and development of CSH stages. Instead of increasing the water-to-binder ratio, increasing the amount of NaOH showed better mixing ability and initial-stage strength attainment in GPM.

Hu et al. [105] studied the impact of different concentrations of NaOH on the CS of BR-class C FA-GPM. The results obtained were compared with the findings derived from the experimentations of BR-class F FA-GPM. In comparison to another FA-derived GPM (up to 10 M NaOH), BR-based FA-GPM was developed with considerably lower NaOH concentration, ranging from 2.50to 7.50 M. Higher the amount of CaO in C class FA, the higher the CS obtained with 15.20 MPa at relatively lower content of 2.50 M NaOH mixture, even at normal curing temperature in the laboratory. Replacing NaOH with the solution of Na2SiO3 and NaOH led to a considerable enhancement in CS of all the test samples of GPM. Nonetheless, this increase was insignificant at higher curing temperatures. Ke et al. [98] developed BR OGP using alkaline activators with 5, 10, and 15% of Na2O. They observed that the test samples gained maximum strength after 7 days of curing. However, at later stages of the curing period, the strength decreased reasonably. Because alkalinity yields rapid hardening at earlier stages and GPM develops early strength even after 24 h, the tested GPM comprising 10% of Na2O showed a maximum CS of 9.80 MPa. Nie et al. [4] investigated GPM produced from received and desulfurized BR (after FGD) subjected to varying molar concentrations of NaOH (0–6.50 M) under normal curing environments (Figure 20).

Figure 20 
                     Influence of NaOH concentration on 28-day CS [4].
Figure 20

Influence of NaOH concentration on 28-day CS [4].

Compared to desulfurized BR, original BR-based GPM containing residual NaOH requires a lower concentration of NaOH (2.50 M) to obtain the maximum CS of 15.20 MPa. However, BR after the FGD does not contain any residual NaOH; therefore, being lesser alkaline in nature, desulfurized BR-based GPM requires a higher level of NaOH concentration (3.50 M) to develop a maximum CS of 20.30 MPa. Even after 28 days of the curing period, FA-based GPM activated with 2.50 M NaOH solution failed to gain any strength in compression. In addition to the original BR, desulfurized BR proved to be a potential candidate in the synthesis of GPM. Alkaline activators in BR-dependent GPM containing the residual NaOH are generally much lower than that needed to produce the FA-derived GPM.

Singh et al. [19] studied the application of industrial products to activate the BR via slag/micro-silica and FA with the NaOH flake and Na2SiO3 solution. GPM under ambient curing conditions was prepared by using 10 wt% slag, whereas GPM subjected to thermal curing was developed utilizing 10 wt% micro-silica as an additive in the mix. An increase in the NaOH solution (M) from 6 to 10 resulted in a reduction in CS of BR FA comprising 30% BR and 10% of added slag. The specimen was subjected to curing under ambient conditions. Test samples prepared with 6.0 M NaOH solution gained a maximum strength of 40.50 MPa, whereas GPM with thermal curing having 10% microscopic and prepared with 12.0 M NaOH showed a maximum CS of 38.0 MPa. Figure 21 highlights the impact of the increase in NaOH concentration on CS of BR-based GPM [8,19].

Figure 21 
                     Influence of NaOH molarity on the CS of BR-GPM [8,19].
Figure 21

Influence of NaOH molarity on the CS of BR-GPM [8,19].

Alam et al. [115] developed GGBS-stabilized BRs with the Na2SiO3 solution in different concentrations (M), e.g., 0.25, 0.50, and 1.00. With the increase in the concentration of Na2SiO3, both BR, i.e., one in slurry form NALCO red mud (NRM) and the remaining in a drier form (called HINDALCO red mud (HRM)) showed a substantial enhancement in the UCS. HRM-25% GGBS with 1 M Na2SiO3 exhibited 8.30 MPa of CS, whereas utilizing the same concentration of Na2SiO3, NRM GPM mix having 25%GGBS showed higher CS of 11.20 MPa. BR-dependent GPMs having different concentrations of alkaline activators with their corresponding CS are presented in Table 4.

Table 4

Range of CS for BR-sourced GPM composites

Binding material Ref. Binder ratios Curing temperature Curing duration CS at various NaOH concentrations (MPa)
BR + RHA [110] BR: 25 and RHA: 75 60°C 24 h 2 M 4 M 6 M 8 M
15 11.9 8.1 5.9
BR + FA [4] BR: 50 and FA: 50 Ambient 0 M 2.5 M 4.5 M 6.5 M
3 15.2 9 6.5
BR (after FGD) + FA [4] BR: 50 and FA: 50 Ambient 0 M 2.5 M 4.5 M 6.5 M
3 15.5 14.9 8
0.25 M 0.5 M 1 M
BR + GGBS [115] BR: 95 and GGBS: 5 Ambient 1.2 1.4 1.5
BR: 85 and GGBS: 15 Ambient 2.4 5 5.5
BR: 75 and GGBS: 25 Ambient 3.5 5.5 11.5
6 M 8 M 10 M
BR + FA + 10%GGBS [19] BR: 90 and FA: 0 Ambient 17 14.2 9.8
BR: 70 and FA: 20 Ambient 22.7 19.7 11
BR: 50 and FA: 40 Ambient 26.5 25 14.3
BR: 30 and FA: 60 Ambient 40.5 29.5 29.2
6 M 8 M 10 M 12 M
BR + FA + 10% silica [19] BR: 90 and FA: 0 60°C 24 h 5.3 5.5 5.9 6.3
BR: 70 and FA: 20 60°C 24 h 9.3 11.9 14.7 19.2
BR: 50 and FA: 40 60°C 24 h 16.7 20.4 23.6 28.3
BR: 30 and FA: 60 60°C 24 h 23.7 31.9 34.2 38
BR: 10 and FA: 80 60°C 24 h 23 28.9 33.9 36.2

5.2.7 Influence of the NaOH/Na2SiO3 ratio

Due to the corrosive properties of alkali hydroxide-based activating agents and their higher thermal emissions in aluminosilicates’ dissolution, a blend of alkali hydroxide and alkali silicate is recommended. To facilitate the reactivity between raw agents and alkali solution, Na2SiO3 along with NaOH is generally utilized. Cheng et al. [116] synthesized NaOH and Na2SiO3 slag-BR-based geomaterial known as slag-sourced cementitious materials (SRCM). Considering a NaOH/Na2SiO3 ratio of 1:3 for SRCM comprising 30 and 70% of BR and slag, respectively, they achieved 28 days’ maximum CS of 16.70 MPa. This strength gain was associated with alumina-enhanced dissolution. Likewise, Zhang et al. [107] developed BR-FA-GPM (RFFG) with NaOH, NaO9Si3, and DW with a proportion of 3:7:3. They also maintained Si/Al and Na/Al ratios of 2 and 0.6. Exposing the RFFG specimen to different conditions of DW and H2SO4 resulted in a significant impact on the durability of the tested samples. Soaking the RFFG specimen in acid resulted in a reduction of UCS from 10 to 6 MPa, whereas UCS decreased to 7.30 after immersing the samples in water for 120 days. Long-term exposure of the GPM to an aggressive environment yields comparable durability and strength with those obtained from OPC specimens subjected to a similar environment.

Hu et al. [105] investigated NaOH-activated BR-FA-GPM’s strength at concentrations of 2.50, 5.00, 7.50, and 10.00 M. The specimen was compared with the GPM activated with a composite solution of NaOH and Na2SiO3 with a ratio of 1.0:2.50 and concentrations of 2.50, 5.00, 7.50, and 10.00 M. Tests were conducted in severe and ambient circumstances. GPM derived from NaOH and Na2SiO3 composites led to enhanced CS at both elevated and ambient temperatures. NaOH-activated BR-class C FA (BR-FC) GPM exposed to thermal curing showed the highest CS of 18.30 MPa. On the other hand, GPM activated via the composite solution exhibited comparable results under both conditions, i.e., ambient and severe environments. Likewise, under similar temperature conditions, the BR-FC specimen with a composite solution achieved the highest CS of 30.30 and 34.50 MPa, respectively. However, NaOH-activated BR-FC was inadequate to achieve notable strength under an ambient environment. Also, necessary thermal curing was needed for the highest CS gain of 20.40 MPa. Ambient-cured BR-FF GPM with a composite solution showed a strength of 24.60 MPa. Hu et al. [113] synthesized a stabilizing composite BR-FA-GPM with a NaOH/Na2SiO3 ratio of 1:2.5 for pavement constructions and tested its feasibility for application in aggregate base concerning lime-FA and cementitious-FA agents. BR-FA-GPM base composites showed minor evidence of drying shrinkage with comparable UCS to those obtained from lime-FA and cementitious-FA derived composites, respectively. Singh et al. [117] synthesized BR-FA-derived GPM coatings with a NaOH/Na2SiO3 ratio of 1:2.5 while varying the BR (in %) with 10, 30, 50, 70, 90, and 100 M a NaOH ranging from 6 to 12. 28 days GPM comprising 30% BR activated with 12.0 M NaOH showed improved CS with 38 MPa.

5.2.8 Influence of the molar ratio

A few of the most important variables to formulate the geopolymerization include but are not limited to alkalinity (M2O/H2O) and silica modulus (SiO2/M2O), whereas M = K, Na, or Ca. An increase in alkalinity enhances the dissolution potential of solid aluminosilicate by leaching the alkali elements. Likewise, better strength characteristics can be achieved by catalyzing the geopolymerization with enhancements in SM [118]. Also, an increase in SiO2/M2O to 1.70 from 1.30 in BR-slag-derived GPM yielded superior strength in compression, and it dropped beyond the identified optimum range of SM. This drop may be associated with the establishment of cyclic silicates due to excessively concentrated silica species hindering the reaction between the tetrahedral monomers [93]. According to Hajjaji et al. [61], Na2O/SiO2 increases with an increase in BR concentration in MK-BR derived GPM at different ratios of MK/BR such as 0.25, 0.17, 0.125, 0.10, and 0.08. Increasing the Na2O/SiO2 to 0.10 in the GPM comprising MK/BR led to a better CS of 10.8 MPa at 28 days.

Lemougna et al. [119] synthesized BR-dependent GPM and activated them using a solid form of NaOH along with sodium of liquid glasses species using SiO2/Na2O ratios of 1.60, 1.80, 2.00, and 2.20. GPM comprising SiO2/M2O ratios of 1.80 and 2.0 cured at 60°C showed an increase in dry CS to 45 MPa when compared with wet CS of 25 MPa. This strength reduction (%) from 85 and 65 may be associated with the SiO2/M2O ratio ranging from 1.6 to 2.2, respectively. Lemougna et al. [7] witnessed strength gain from 65 to 85 MPa under the ambient environment of curing with the increase in SiO2/M2O ratio from 1.60 to 2.00 after incorporating the slag into BR-GPM comprising 50:50 ratio of the mix. At an ideal value of 2.0, SM supports rapid reactivity during the early phases of hydration and develops higher strength. Zhang et al. [120] studied the BR-class F FA-GPM using Na/Al ratio varying from 0.60, 0.70, 0.80, and 1.00 by changing the concentration of NaOH/Na-trisilicate solution from 0.2 to 0.4. BR is the primary raw material, and FA was sourced from three different locations. Initially, Si/Al was taken as 2 for all the test specimens. Both Si/Al and Na/Al play an important role in geopolymerization needed to activate the aluminosilicates’ dissolution. Using energy-dispersive X-ray spectroscopy (EDX), the authors observed that in comparison to those of the starting material, results obtained for Si/Al and Na/Al of the GPM composite were much better with the highest CS of 13.50 MPa in compression with maximum EDX as presented in Figure 22.

Figure 22 
                     SEM-EDX results of GPM specimens: (a) B2-T23, (b) B2-T50, and (c) B2-T80 [120].
Figure 22

SEM-EDX results of GPM specimens: (a) B2-T23, (b) B2-T50, and (c) B2-T80 [120].

Figure 23 presents the impact of Na/Al on the CS of BR-coal MK GPM composites [121]. Test samples were developed with the consistent use of Si/Al of 1.20 and varying Na/Al ratios of 0.80, 0.90, 1.00, 1.10, 1.20, and 1.30 with different concentrations of NaOH. Additionally, the strength increased with an increase in the Na/Al ratio to 1 but it decreased afterward. Microstructural tests revealed that the GPM sample with a Na/Al ratio of 1 produced greater composites without unreacted BR. Surplus alkalinity above the optimal concentration had a harmful impact on microstructure and CS by preventing the development of GPM composites.

Figure 23 
                     Influence of the Na/Al ratio on CS of the BR-coal MK GPM paste [121].
Figure 23

Influence of the Na/Al ratio on CS of the BR-coal MK GPM paste [121].

GPM strength mainly depends on the ratio of silica to alumina (SiO2/Al2O3). Ye et al. [94] developed OPG by pretreatment of alkali-thermal BR and SF. They observed that BR-GPM without SF demonstrated low strength because of lower SiO2/Al2O3 in BR. This ratio was significantly lower than that of the acceptable range of 3.30–4.50 [122]. The results demonstrated that the addition of 20% SF in OGP BR-GPM with alkali pretreated BR was stable in the long term when compared with strength in their initial stages. Also, the test samples attained the maximum 28 days’ strength of 13.50 MPa. The addition of SF ranging from 20 to 30% enhanced the GPM’s molar ratio to acceptable limits, i.e., H2O/M2O 10–25, SiO2/Al2O3 3.30–4.50, and M2O/SiO2 0.20–0.48 [122]. Li et al. [123] prepared BR-sourced GPM with solid waste incineration FA (MSWIFA). The binding agents were automatically activated with a solution of Na2SiO3 and NaOH. Varying mass ratios of binders to alkali activators in the range of 100:8 to 100:16 were examined. As the concentration of Na2SiO3 increased to 14% from 8%, UCS increased to 10 MPa for BR-sourced GPM comprising 30% of MSWIFA and 70% BR with maximum strength observed for the mix developed from SiO2/Al2O3 of 2.08.

Singh et al. [19] investigated the impact of processing the BR subjected to varying ratios of alumina to silica on the CS of BR-FA-GPM materials subjected to ambient curing and elevated temperature curing conditions. Mechanically activated BR was pulverized to improve the BR-sourced GPM’s strength by making the unreactive silica reactive in nature. BR was processed to a size even lower than 5 µm. Depending upon the processed BR, SiO2/Al2O3 ratios for GPM subjected to ambient curing were in the range of 2.20–4.70 against the processed BRs (in %) added at 90, 70, 50, 30, and 0. GPM under 7 days of ambient curing conditions, depending upon the processing levels of BRs, comprising 30% BR and SiO2/Al2O3 ratio of 4 resulted in the CS gain of up to 40 MPa. On the contrary, for GPM comprising varying incorporation of raw BR (%) from 90 to 0, SiO2/Al2O3 varied to 5.50 from 3.0. Also, experimental results confirmed that the 7 day’s strength of BR-FA-GPM subjected to thermal curing increased by increasing the SiO2/Al2O3 ratio. The highest CS was achieved at a SiO2/Al2O3 ratio of 5.1 and it dropped thereafter. Pulverized BRs comprising reactive silica of 5.12% with BR size smaller than 5 µm reacted better than those of unprocessed BR having a reactive silica content of 1.62%. Bobirica et al. [124] studied BA-sourced GPM comprising 10% WG and 10–30% of BR. By the addition of the BR in the mix, the SiO2/Al2O3 ratio of GPM increased significantly. Increasing the SiO2/Al2O3 ratio to 5.98 increased the CS of GPM comprising 10% BR up to 14.50 MPa. On the other hand, the addition of BR from 20 to 30% increased the SiO2/Al2O3 ratio to 10.40 from 8.23, which ultimately resulted in a strength reduction from 10.40 to 8.50 MPa. Ahmed et al. [89] investigated the impact of the increase in the SiO2/Al2O3 ratio on the strength of alkali-pretreated BR-based GPM under varying curing duration. An increase in the SiO2/Al2O3 ratio from 3.60 to 4.40 MPa showed a notable increase in the CS at both the 7 and 28 days of cured samples. For a SiO2/Al2O3 ratio of 4.40, the 28 days’ maximum strength was 37 MPa. This increase in the strength may be associated with a higher concentration of silica that is contributed by the potential source of the aluminosilicate composite developed from the solution of Na2SiO3.

5.2.9 Influence of LSR

To synthesize BR-sourced GPM, the majority of the researchers recommend using the LSR in the range of 0.30–1.20 due to its influencing characteristics to develop the binding properties in GPM [12,97,125128]. Dimas et al. [126] found that an increase in LSR tends to increase the CS of BR-MK geomaterials. To ensure the workable, strong, and shrinkage-resistant BR-MK geomaterials, the optimal SLR was found to be ranging from 2.80 to 3.0. Higher solid concentration in aqueous levels showed an increasing content of Si–O–Al, and Si–O–Si, which resulted in GPM binders having better CS due to the polycondensation phenomenon. Alkali pretreated BR-GPM showed an increase in the CS from 32 to 44 MPa for LSR of 0.55 and 0.50, respectively. With the increase in LSR from 1.00 to 1.50, BR-FA-GPM comprising 20% BR also resulted in better CS ranging from 3 to 13 MPa. This encouraging impact of the increase in LSR to improve the BR-FA-GPM’s strength was mainly because of the availability of better efficiency of reactive silica to dissolve the mix of solids [97].

Geng et al. [128] synthesized GPM using a 5.0 M NaOH solution along with sodium liquid glasses with an LSR of 0.40. Raw geomaterials were used with a ratio of BR/CG of 8:2 wt. The study recommended a novel approach of co-grinding sourced activation for the geopolymeric precursors without adopting the calcination process. The 20 min long grinding of the BR mixture along with CG was carried out in a planetary ball mill for milling at 200 revolutions per minute. In comparison to GPM activated via calcination, geomaterials milled by the co-grinding technique showed higher dissolution efficacy of SiO2 and Al2O3. Hu et al. [12] developed BR-sourced GPM with an LSR of 0.45, using BR with alkali treatment along with FA. They activated the mix with the Na2SiO3 solvent. With a BR/FX ratio of 50:50, the alkali pretreated BR-FA mix attained the highest CS of 23.80 MPa with only 5% of Na2O. Using an LSR of 1.20, He et al. [8] synthesized BR-GPM containing different weight ratios via the BR and RHA mixture. The mix containing an RHA/BR weight ratio of 0.50 and 4 M NaOH exhibited the highest CS of 20.40 MPa.

5.2.10 Influence of additives

According to Ahmed et al. [89], BR-GPM with nano-silica in varying contents had better strength properties. Nano-silica was incorporated (wt% of BR) in 0.10, 0.20, 0.30, 0.40, and 1.0. Studies revealed the encouraging impact of nano-silica on the CS of composites. Also, the addition of nano-silica in varying percentages in BR-made GPM led to better strength when compared with that of the control mixture, excluding the mixtures comprising 0.10 and 1.0% of nano-silica. Nano-silica with Ca composites yields accelerated development of CSH and the GPM composite that finally increases the strength properties. High amounts of nano-silica result in a substantial content of unreacted silicate ions that ultimately impact the CS of binders. Li et al. [92] investigated the potential of various types of gypsums, e.g., NG, FGD gypsum, and PG on the BR-slag grouting mortar in varying amounts [92]. The strength results achieved from these types of gypsum are presented in Figure 24. The 3 and 28 days’ CS of BR-slag grout had notable improvement when NG and FGD were added into the mix. However, insignificant enhancement in the strength was reported with the BR-slag grout incorporated with PG. Also, Bošković et al. [127] investigated the positive influence of different concentrations of NaOH (8 and 4 M) in BR-MK GPM with Ca(OH)2. Nonetheless, BR-MK GPM exhibited a lower strength in comparison to that obtained with MK GPM. Incorporating Ca(OH)2 supported the CSH development and ultimately improved the strength in compression. However, even with Ca, the CS reduced with an increase in alkalinity. This reduction in strength may be associated with more alkaline content preventing the formation of CSH and only allowing the formation of the GPM composite. A decrease in alkalinity yields better strength and a denser microstructure with minimum cracking.

Figure 24 
                     CS of the BR-slag grouting GPM mortar having various forms of gypsum at (a) 3 days and (b) 28 days [92].
Figure 24

CS of the BR-slag grouting GPM mortar having various forms of gypsum at (a) 3 days and (b) 28 days [92].

5.2.11 CS behavior

Many studies have suggested different approaches to mechanically activate BR, such as pulverizing, grinding, alkali thermal pretreatment, or calcination, to improve the CS of BR-dependent GPM. Likewise, to pre-active the BR, Geng et al. [128] recommended a co-grinding pre-activation process (CGPP) and studied the impact of CGPP of raw composites on BR-GPM’s strength. A blending ingredient known as CG, consisting of higher Al and Si concentrations was adopted. CGPP involving mix grinding of the majority of the raw composites was performed without calcination in a mill rotating at 2,000 revolutions per minute for 20 min. The CGP of BR with CG showed an improved geopolymeric process of the raw BR and enhanced the dissolution potential of alumina and silica resulting in the highest CS gain of 25.50 MPa after 28 days of curing. Thus, CGPP entirely removes the requirement of calcination by supporting the strength gain. Li et al. [123] examined the impact of mechanically activated BR by ball milling utilizing MSWIFA at 500 revolutions per minute. The process took 30 min to grind the particles of size (µm) lower than 80. Mechanically activated BR-MSWIFA-GPM comprising 14% Na2SiO3 solution showed better CS with 12.7 MPa in comparison to 10 MPa resulting from the GPM sample lacking mechanical activation. Increasing the BR (%) from 40 to 90, 4.0 M NaOH-activated GPM sourced from sawdust and acid-modified BR reported higher CS ranging from 138.0 to 8.30 MPa [125].

Zhang et al. also explored the positive impact of the particle size on mechanical characteristics of BR-sourced GPM and concluded that this GPM comprising finer and coarser particles both yield improved properties [129]. Therefore, based on desired characteristics, particle sizes can be classified. Because of the greater leaching potential of Al3+ and Si4+ with fine particles and the micro aggregate filling impact of coarse particles, mechanical characteristics improve significantly. Also with fine BR, Al2O3, SiO2, and CaO amounts decreased, while that of Na2O and Fe2O3 experience a slight increase. The increase in the particle size of BR decreased strongly in the beginning but eventually it increased. Mendes et al. [20] examined the role of BR in the mechanical characteristics of MK-based GPM paste. The addition of BR improved the bulk density of the paste; nevertheless, the CS dropped. The reason may be associated with a decrease in SiO2/Al2O3 due to increasing BR content and also it is less potential to react in comparison to that MK. Table 5 presents the CS of BR-sourced GPM resulting from various heat curing circumstances.

Table 5

Influence of heat curing conditions on the CS of BR-GPM pastes

Binding material Ref. Binder ratio Alkali amount Curing duration Curing temperature LSR CS at 28 days (MPa)
BR + MK [62] BR: 0 and MK: 100 16 M NaOH and Na2SiO3 8 weeks and 1 day 60°C for 1 day and 25°C for 8 weeks 1.96 51.5
BR: 10 and MK: 90 1.85 13.4
BR: 20 and MK: 80 1.72 14.2
BR: 30 and MK: 70 1.64 10.6
BR + slag [116] BR: 5 and slag: 95 NaOH/Na2SiO3 = 1:3 28 days 50°C 13.7
BR: 10 and slag: 90 NaOH/Na2SiO3 = 1:3 28 days 50°C 11.5
BR: 20 and slag: 80 NaOH/Na2SiO3 = 1:3 28 days 50°C 13.69
BR: 30 and slag: 70 NaOH/Na2SiO3 = 1:3 28 days 50°C 16.7
BR: 40 and slag: 60 NaOH/Na2SiO3 = 1:3 28 days 50°C 11.3
BR: 50 and slag: 50 NaOH/Na2SiO3 = 1:3 28 days 50°C 7.3
BR + coal gangue (CG) [128] BR: 80 and CG: 20 5 M NaOH 28 days 80°C for 1 day and ambient for 27 days 0.4 25.5
BR + BA + WG [124] BR: 0 and BA: 66.67 and WG: 0 10 M NaOH and Si/Al: 3.24 24 h 60°C 0.35 7.3
BR: 0 and BA: 56.67 and WG: 0 10 M NaOH and Si/Al: 3.63 24 h 60°C 0.35 9.3
BR: 10 and BA: 46.67 and WG: 10 10 M NaOH and Si/Al: 5.98 24 h 60°C 0.35 14.5
BR: 20 and BA: 36.67 and WG: 10 10 M NaOH and Si/Al: 8.23 24 h 60°C 0.35 10.4
BR: 30 and BA: 26.67 and WG:1 0 10 M NaOH and Si/Al: 10.4 24 h 60°C 0.35 8.5
BR + Class F FA [105] BR: 50 and FA: 50 NaOH and Na2SiO3: 2.5 M 24 h 60°C 0.50 13.6
BR: 50 and FA: 50 NaOH and Na2SiO3: 5 M 24 h 60°C 0.50 15.2
BR: 50 and FA: 50 NaOH and Na2SiO3: 7.5 M 24 h 60°C 0.50 17.8
BR: 50 and FA: 50 NaOH and Na2SiO3: 10 M 24 h 60°C 0.50 22.8
BR + FA [12] BR: 50 and FA: 50 Na2O: 0% 24 h 60°C 0.45 5
BR: 50 and FA: 50 Na2O: 2.5% 24 h 60°C 0.45 19
BR: 50 and FA: 50 Na2O: 5% 24 h 60°C 0.45 23.8
BR: 50 and FA: 50 Na2O: 7.5% 24 h 60°C 0.45 20
BR: 75 and FA: 25 Na2O: 5% 24 h 60°C 0.45 8
BR: 25 and FA: 75 Na2O: 5% 24 h 60°C 0.45 16.5

5.3 Durability performance

Alam et al. [115] applied GGBS-mixed BR composite materials in the field of geotechnical engineering and investigated its UCS and other durability properties by subjecting the geo-material to alternative cycles of wet and dry (W–D) environments. Compared to strength gain with 28 days of curing, all GPM specimens activated with 1 M Na2SiO3 solution under 12 consecutive and alternate wet and dry cycles showed better UCS. Also by testing slaking durability index (SDI) to assess the durability of the constituent part subjected to flowing water, it was reported that 25% GGBS-mixed BR-GPM with greater SDI resisted much better to the disintegration of the particles. Although SDI (%) dropped after each cycle, it remained within the limit of medium to higher durability with 95–98. To assess the crushing potential of the GPM, BR stabilized with varying percentages of GGBS was tested for impact strength. Due to greater unit weight and dense packing within the microstructure, 25% of GGBS resulted in the highest resistance to the disintegration of particles. On the other hand, resistance was lower for 5, 10, and 15% of GGBS samples.

Pan et al. [90] examined resistance to carbonation, chemical attacks, and freeze–thaw successions of ASBC composites and contrasted them to those of the characteristics of 525 OPC (Chinese standard GB 175–1992). Compressive and bending strength tests were performed to compare the resistance to carbonation before and after 28 days of carbonation. After 28 days of improved carbonation, there were no discernible strength changes for ASBC; however, such changes were acceptable and were on par with OPC. Compared to OPC, ASBC resisted better chemical attacks including but not limited to sulfates and chlorides of Mg and Na, diluted HCI, and simulated seawater. The ASBC showed similar freeze–thaw resistance (assessed in the rate of mass loss) to OPC after 13, 25, and 50 cycles. ASBC subjected to 50 cycles of free–thaw experienced the highest rate of mass loss of 2.70%, which was relatively low in comparison to that of OPC resulting in 3.30%. When compared to cement mortar, BR-sourced GPM mortar resisted much better to chloride ion permeability attacks [130]. A previous study [107] assessed the durability properties of BR-FA-sourced GPM subjected to deionized H2SO4 and water. Samples were submerged in an acidic solution and water for 128 days and their physical changes were examined at different durations of immersion. Just a day after immersion, the RFFG specimen gained remarkable weight; however, it reduced after 2 to 21 days. This degradation amounting to almost 1.05 times the initial weight was associated with partially dissolved GPM subjected to a period of 2 and 28 days of immersion in DW and acidic solution. After 21 days of immersion, partial dissolution stopped and no weight loss was noted. Also, the strength loss caused by water and acid in the GPM specimen was almost identical to that observed in the control OPC specimens.

Li et al. [123] assessed the long-term stability (LTS) characteristics and durability properties of BR-MSWIFA-sourced GPM (RGM) by performing the freeze–thaw cycle and water absorption tests. The water absorption results for RGM were clearly in line with those of the guidelines suggested by MU10 (JC239-2001) FA-developed bricks (14.2–16.7%). Assuring the LTS of RGM subjected to freeze–thaw successions, the degree of mass loss was computed. Also, based on the lower rate of mass loss (%) of 1.7 (generally less than 5.0), utilizing the RGB to replace the durable and LTS-based FA bricks is recommended. Likewise, Singh et al. [117] examined the potential of GPM-made concrete blocks to resist fire and acid attacks and observed that it improved up to BR50 mix with minimum loss in the CS. Increasing the BR up to 30% and utilizing 12 M NaOH resulted in better strength of BR-sourced GPM.

5.4 Microstructural properties

BR is mainly defined by the large traces of inactive fillers of crystalline phases added to the GPM matrix. These phases do not support the process of the geopolymerization reaction and remain inactive throughout the reaction time, which ultimately decreases the strength properties of BR-based GPM due to a higher concentration of the added BR [20]. Cheng et al. [116] investigated that the BR enhanced the pore matrix of SRCM by reducing the pores and densifying the matrix. Before the addition of the BR to the slag system, it was observed that the structure was highly porous. However, with the addition of 30% BR, the porosity of the slag system dropped and the microstructure appeared denser. Amorphous ettringite and C–S–H are the main products of hydration and they showed improved porosity and better CS with 16.70 MPa. Increasing the BR also increases the amount of C–S–H; however, an excessive amount of BR makes the microstructure more complex. He et al. [96] investigated BR-FA-GPM and MK-sourced GPM and observed that due to the micromorphological properties of the raw composites, their microstructure was considerably different. The former had inactive porous phases and due to partial dissolution in an alkaline solution, it appeared bulkier and negatively impacted the CS. However, the latter appeared denser and relatively continuous. Also, adequate mixing time (not less than 15 min) was suggested to thoroughly mix the raw composites and alkali solution. Figure 25 shows the SEM micrographs of the three investigated raw materials. Hu et al. [12] observed the impact of the alkaline thermal pre-activation process on Fe-enriched BR-FA-GPM and concluded that the pre-activation approach strongly affected the raw BRs’ phase transformation. BR pre-activated at 800–900°C by the addition of the alkali (Na2O, in %) from 0.0 to 7.5 exhibited the development of reactive phases, for instance, peralkaline aluminosilicate phases (Na6Al4Si4O17) and nepheline (NaAlSiO4). Also, the phases increased the alkalinity, effectively dissolved SiO2 and Al2O3, and resulted in better strength gain. BR pre-activated at 800°C showed the highest dissolution potential.

Figure 25 
                  SEM micrographs of the three raw materials: (a) and (b) MK, (c) FA, and (d) BR [96].
Figure 25

SEM micrographs of the three raw materials: (a) and (b) MK, (c) FA, and (d) BR [96].

Alam et al. [115] investigated the effect of freeze–thaw cycles (12 in number) on microstructural characteristics and examined the durability and particle integration of BR-GGBS-based geomaterials subjected to flowing water. Compared to 28 days of curing, BR-GGBS geomaterials subjected to alternate cycles of drying and wetting showed highly packed microstructure comprising relatively more hydrated components. The approach leads to the adequate formation of the composite with BR preactivated using 25% of GGBS ultimately resulting in better strength. Likewise, Choo et al. [102] analyzed the microstructure of BR-sourced fly-ash GPM and observed that by increasing the BR content, the dissolution efficiency increased in a more alkaline environment resulting in better UCS of FA-sourced OPG due to the polycondensation reaction. Pan et al. [90] investigated that compared to ASBC composites, the OPC microstructure was less compacted with compromised integrated morphology. The porous microstructure of ASBC along with the finer level of amorphous hydration products (primarily due to the C–S–H composite) was mainly responsible for resistance to chemical attack, resistance against the freeze–thaw environment, better strength, and durability to withstand carbonation. According to Kaya and Soyer-Uzun [62], Fe plays an important role in developing the mechanical and microstructural properties of BR-MK-based GPM with different Fe/Si ratios ranging from 0.155 to 0.003. An increase in the Fe species along with the addition of BR not only influences the structural growth but also improves the geopolymerization reaction. An increase in the Fe species decreased the geopolymerization rate by preventing the dissolution potential of aluminosilicates. Li et al. [101] developed BCM using BR combined with AS synthesized from lime additive and Pb/Zn smelter. The microstructural analysis of BCM showed the higher formation of ettringite and C–S–H composites. This leads to better strength at an early age and improved the solidifying potential of heavier metals. However, raw materials experienced a subsequent decrease in strength with a prolonged period of curing because of the re-dissolution process leading to depolymerization. BR-sourced GPM is highly influenced by the particle size of BR [129]. An increase in the mean particle fraction of BR from 39 to 392 results in a denser structure. This compaction of structure may be associated with fine particles comprising the greater leaching potential of Al3+ and Si4+ and the higher content of Na+ that balances out the negatively charged AlO4. Particle sizes did not influence the hydration products and N–A–C–S–H, calcite, and the GPM composite were the predominant products of hydration. The porosity of BR-slag GPM experienced an initial increase, but later on, it decreased when the BR size increased. The findings of the research were in line with those obtained by Zhang et al. [91], confirming the fact that the average-sized BR particles improve the microstructure by reducing the leaching potential of aluminosilicates.

5.5 Thermal properties

In general, GPM is thermally stable in comparison to those conventional construction materials. Also compared to those of OPC [131] and other hydraulic lime-sourced mortars [132,133], GPM experiences the least expansion in temperature, having less thermal conduction, with minor loss of mass at elevated thermal conditions. GPM produced using BR had a lower thermal conductivity value of 1.203 W·m−1·K−1 compared to that of 1.206 W m−1·K−1 of OPC [134]. Figure 26 shows the response surface graphs and their projections onto the ternary diagram for the thermal conductivity of GPM samples after 28 days of curing. The increase in the conductivity value of BR-sourced GPM was mainly because of a higher Fe content in BR. Blending BR with RHA in a 50:50 ratio mix, showed decreased conductivity values ranging from 0.484 to 1.203 W·m−1·K−1. Likewise, ternary GPM comprising diatomaceous earth material, BR, and RHA had better expansion when subjected to a temperature limit of 950°C. On the other hand, the cement paste remained unable to resist this temperature and finally was damaged. Compared to alkali-activated slag-BR composites, cementitious materials showed a 2.36% decrease of thermal conductivity. However, it increased when the BR content in BR composites was increased from 0 to 20%, and later on, it showed enhanced reduction [135].

Figure 26 
                  Response surface graphs and their projections onto the ternary diagram for thermal conductivity of GPM samples after 28 days of curing [134].
Figure 26

Response surface graphs and their projections onto the ternary diagram for thermal conductivity of GPM samples after 28 days of curing [134].

Lemougna et al. [119] synthesized structural composites such as lower-temperature ceramic materials using BR-GPM after sintering at an elevated temperature of fewer than 800°C (lower compared to the generally adopted temperature for sintering). As presented in Figure 27, the authors further assessed the strength properties of BR-GPM subjected to post-heating by increasing the temperature from 300 to 800°C. This resulted in stable GPM products in water. Likewise, compared to 55 MPa at 100°C, post-heated GPM products experienced better-wet CS of 55 MPa at 700°C. Compared to 55 MPa at 700°C, GPM products sintered at 400°C showed dry CS of 40 MPa. Based on BR-GPM having no blend of BR with other aluminosilicates, post-heated BR-geomaterials had better stability and higher strength, resulting in the potential formation of structural composites.

Figure 27 
                  Wet and dry CS of BR-GPM composites post-heated at different temperatures [119].
Figure 27

Wet and dry CS of BR-GPM composites post-heated at different temperatures [119].

Yang et al. [136] investigated the post-heating effect on BRFA-GPM at varying temperature ranges. GPM subjected to 50°C of curing for 7 days followed by subsequent curing for additional 7 days at ambient temperature resulted in the highest UCS approaching 19 MPa. Also, GPM was subjected to varying temperatures, e.g., room temperature, 400, 600, 800, and 1,000°C each for 1 h duration. Heating the GPM to 600°C improved the mechanical properties. Also, post-heating the BR-GPM at varying temperature ranges enhanced their stability in water. Likewise, compared to 22.50 MPa at 100°C, GPM subjected to post-heating up to 700°C increased the wet CS up to the highest value of 55 MPa. GPM sintered at different temperatures had dry CS ranging from 40 MPa at 400°C to 55 MPa at 700°C. Therefore, post-heating resulted in stable and strong BR-GPM and improved the structural behavior of the materials based on BR-GPM without BRs, blended with other aluminosilicates. Figure 28 portrays the impact of post-heating on BRFA-GPM’s CS. GPM subjected to 160°C improved the UCS to a maximum value of 32 MPa. Volume shrinkage and formation of various cracks, with more burning of the GPM specimens to 400 and 600°C reduced their CS to 16.40 and 15.60 MPa, respectively. The 14 days cured sample subjected to 800°C showed a remarkable loss in strength by 70%. Raising the heating temperature to 400°C resulted in weight loss, whereas heating up to 600°C dried up the structural and free water resulting in volume shrinkage. Loss in weight was constant between the temperatures ranging from 800 to 400°C. Heating the samples above 800°C resulted in further loss in weight, and rapid and continuous expansion in volume followed by crystalline phased microstructure from the amorphous phase. RHA-BR sourced GPM comprising 40 and 20% BR were subjected to post-heating of 1,000°C for 2 h to assess their thermal resistance. Compression strength results revealed the strength gain ranging from 30.1 to 67.8 after post-heating, respectively [137,138]. Due to the increase in energy requirements around the globe, phase change material (PCM) integrated GPM with better thermal efficiency in residential construction has been attracting attention. PCMs being energy-efficient are applied in cementitious composites and GPM to reduce the heating and cooling requirement and to improve the thermal inertia of building units. Because of the advantageous characteristics of PCM-integrated GPM, in comparison to PCM-integrated cementitious materials, PCM-integrated GPM composites have certain advantages with their contribution to lesser energy requirement, energy effectiveness, strength gain, waste usage, and affordable manufacturing [139141].

Figure 28 
                  Influence of temperature on UCS of the BRFA-GPM paste [136].
Figure 28

Influence of temperature on UCS of the BRFA-GPM paste [136].

Afolabi et al. [39] assessed the efficiency of composite walls comprising BR-GPM with 30% added microencapsulated PCM, against elevated temperatures. After impregnating the paraffin into expanded graphite, PCM was applied for encapsulation, which ultimately resulted in improved conductivity of GPM wall surfaces. Compared to those with conventional types of cement, clay, and gypsum-sourced mortar surfaces with 52, 64, 60, and 58°C, respectively, this technique also improved the latent heat and decreased the mean surface temperature up to 52°C. With the thermal characteristics of GPM, not only emitted CO2 decreased but also resulted in a decreased significant amount of energy consumption. With better curing and incorporation of the PCM, GPM composites showed an increase in CS with improved energy efficiency.

5.6 Environmental aspects

BR being a toxic waste in solid form contains several toxic metals, for example, As, Cd, Cr, Pb, and Ni. These heavy metals in BR with higher leaching prospective make their disposal and treatment comparatively much more difficult. Thus, to examine the leaching potential of heavy metals and contamination risk, assessments are necessarily required after converting the BR into viable products. Yao et al. [142] commented how BR’s ecology unsafe characteristics made it unsuitable for utilization as a binder material. But, right after stabilizing the BR with FA and other coal refuse, limiting to permissible thresholds, concentrated heavier metals in the leachate, decreased significantly. Belonging to the thresholds recommended by USEPA [143], BR comprises Cu and Zn in lower concentrations. However, Cd, Pb, and Cr are in higher concentrations. Also compared to those of raw BRs, the leaching potential of Cd, Pb, and Cr of BR-FA-GPM decreased noticeably. This decrease was even below those of the limits recommended by EULFD and USEPA guidelines. Kim et al. [5] synthesized environmentally friendly BR-FA sourced GPM bricks depending on the toxicity; also, several leaching tests were performed using the toxicity characteristic leaching procedure. With these tests, the content of heavy metals such as As, Cd, Cr, Pb, and Ni was examined. Just after immersing the specimen in acetic acid for 18 h, the leachate was filtered using a filtering membrane. Using ICP-OES, the leachate was evaluated for its limits and it was found that the concentration of metals was remarkably lower than those recommended by EPA-defined thresholds. After stabilizing the BR with alkali-activated GGBS, BR comprising the toxic metals, for instance, Hg, Pb, As, and Cr decreased to the permissible threshold of EPA [115]. Likewise, Li et al. [123] immersed the BR-FA-GPM in acetic acid comprising DW with a solid/liquid ratio of 1:20 and assessed their toxicity properties by examining the leaching concentration of the studied metals. It was noticed that the concentration was significantly lower in comparison to those of the raw materials. Also, for newly resulting hydration products of GPM, the interaction and stability of heavy metals were examined. Ensuring the safety of BR-sourced GPM against toxicity, an oxidized fraction of heavy metals was stable and effectively encapsulated within the network of GPM. Encapsulating the heavy metals within the chains of the GPM network results in a reduction of heavy metals available in BR and ultimately minimizes the associated risk [97]. Therefore, based on the literature cited above, recycling the BR into GPM products decreases toxicity and reduces the potential damage to human health and the environment.

6 Conclusions

The present study has tried to examine the fresh, mechanical, durability, and microstructural behavior of the GPM paste produced using industrial wastes from the literature studies. The effects of different ingredients such as sand-to-binder ratio, liquid-to-solid ratio, kinds of activator, superplasticizer, curing conditions, the molar ratio of various compounds, the concentration of alkali activator, and other different raw materials are assessed for the fresh, mechanical, durability, thermal, and microstructural performance of the GPM composites. The following are the conclusions interpreted from the reviewed articles:

  1. Compared to pure BR, pre-activated BR is mostly adopted to enhance the strength of GPM. For better microstructure and enhanced strength, different pre-activation approaches of BR include 3 h calcination at an elevated temperature of 800°C, 1 h thermal pretreatment of alkali with solid activators at 800°C, mechanical co-grinding, and pulverization.

  2. Pure BR reacted poorly and had a lower SiO2/Al2O3 ratio than the nominal ratio of 2.0. Therefore, these were the limiting factors mainly controlling the efficient usage of BR in geopolymerization. Also, BR should be blended with other aluminosilicates having a higher ratio of SiO2/Al2O3.

  3. Because the residual NaOH available in the form of Na2O ranges from 3 to 20.20%, therefore, for cost-effective production of GPM, alkaline BR itself should be adopted to supply the NaOH activator for geopolymerization.

  4. The residual NaOH within the BR minimizes the utilization of NaOH activators and thus results in better strength when Na2SiO3 solution is added for the sole alkaline activation process.

  5. The chemical composition, pH, nature of the base materials, and the SiO2/Al2O3 and SiO2/Na2O ratios determine the optimal concentration of the alkaline activators. The strength of BR-sourced GPM does not necessarily increase with an increase in the alkaline content. In addition, for BR-based GPM, Na2SiO3/NaOH ratios of 2.50 and 3.00 are typically utilized.

  6. BR-based GPM should be subjected to ambient curing conditions to meet the lower strength demands. Also, heat curing ranging from 60 to 80°C may be adopted for better durability and initial strength gain.

  7. Because of its non-reactive crystalline morphology that may be significantly overwhelmed by the alkali fusion process and GPM technology, very few studies are available to assess the GWP potential for cementitious materials.

  8. For 2 h, alkali pretreatment of GWP at 550°C enabled the material more reactive and enhanced the CS under an ambient curing environment. When GWP was mixed in large quantities, 8 h of heat curing is preferred at temperatures ranging from 60 to 80°C. Before heat treatment, a longer duration of GWP-sourced GPM for up to 60 h increased their strength and crack resistance.

  9. Incorporating the nanomaterials into GWP-sourced GPM showed a significant impact on the initial compressive and tensile strength.

  10. There is a lot of scope for further studies on the synergistic use of GWP with other aluminosilicate products and BR with other silica-rich pozzolanic ingredients for GPM and its practical uses. However, a limited number of scientific work is available on creep and the thermal resistance of BR and GWP-sourced GPM. Improved physio-chemical features of BR-GPM and GWP-GPM are the potential research areas that can be addressed by incorporating raw materials for enhancing internal matrix, such as nanomaterials, bio-additives, epoxy composites, microfibers, quartz powder, alccofine, nano-alumina, nano-calcium carbonate, nano-calcium oxide, nano-sodium oxide, nano-titanium dioxide (titania), nano-silica, etc., that have been observed to be effective for GPM pastes. To use BR-GPM and GWP-GPM for structural repairing and strengthening of building structures and precast items, detailed investigations of their mechanical and durability characteristics are required.

Environmental and economic aspects need the upgrading of conventional concrete fabrication materials. This aim can be attained by producing an effective GPM for cleaner construction. The production of GPM utilizing waste materials (FA, BR, GWP, GGBS, etc.) is an operative substitute for conventional Portland cement concrete. GPM can provide enhanced economic benefits, high early strength, greater durability, reduced carbon emissions, less use of sodium silicate solution, and higher serviceability of structures. Therefore, the fabrication of raw material-based GPM significantly depends on the alkali-activated polymerization process. The production of GPM needs systematic care and cautious material arrangement. Through the activation process for the fabrication of GPM, larger alkalinity also offers a safety danger and increased energy utilization and production of greenhouse emissions. Additionally, GPM is highly influenced by the curing temperatures and curing time as well as by the properties and quantities of the constituents.

GPM is a better substitution composite to Portland cement and can be competently utilized to substitute Portland cement for practical uses in construction works. Future works on GPM are suggested for the amelioration of strength and durability features of GPM by the incorporation of microfibers and enhancement of microstructure by the accumulation of nanoparticles. The engineering features of GPM should be examined by bearing in mind the influence of aggregate amount and different types of additives for utilization in structural members. Furthermore, proper procedures for the section of aggregate quantity in GPM are suggested with a vibrant mix design method. The addition of fibers enhances the ductility of GPM and, hence, there is a requirement for studies on the seismic efficiency of fiber-reinforced GPM. GPM with greater confrontation to the corrosive phenomenon and abridged shrinkage features can yield a revolution in pre-stressed concrete by lowering stress losses. The use of industrial waste materials in GPM composites significantly leads to sustainable construction and development.

Acknowledgments

The authors extend their appreciation to the Deanship of Scientific Research at King Khalid University for funding this work through Large Groups Project under grant number R.G.P. 2/152/43.

  1. Funding information: This work was funded by Large Groups Project under grant number R.G.P. 2/152/43 from the Deanship of Scientific Research at King Khalid University.

  2. Author contributions: All authors have accepted responsibility for the entire content of this manuscript and approved its submission.

  3. Conflict of interest: The authors state no conflict of interest.

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Received: 2022-10-04
Revised: 2023-02-02
Accepted: 2023-02-20
Published Online: 2023-04-17

© 2023 the author(s), published by De Gruyter

This work is licensed under the Creative Commons Attribution 4.0 International License.

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