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Review

A State-of-the-Art Review on the Incorporation of Recycled Concrete Aggregates in Geopolymer Concrete

School of Engineering, Deakin University, Geelong, VIC 3216, Australia
*
Author to whom correspondence should be addressed.
Recycling 2022, 7(4), 51; https://doi.org/10.3390/recycling7040051
Submission received: 2 July 2022 / Revised: 23 July 2022 / Accepted: 25 July 2022 / Published: 27 July 2022
(This article belongs to the Special Issue Sustainable Materials from Waste and Renewable Sources)

Abstract

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Geopolymer concrete (GC) has the potential to incorporate recycled concrete aggregates (RCA) obtained from construction and demolition waste. This research aims to review the current state-of-the-art knowledge of the RCA in GC and identify the existing knowledge gaps for future research direction. This paper highlights the essential factors that impact the GC’s mechanical and durability properties. Moreover, the influence of various percentages of coarse and fine RCA and the pattern of their replacement will be assessed. The effect of aluminosilicate material, alkaline activators, and curing regime also will be evaluated. Besides, the durability-related characteristics of this concrete will be analysed. The impact of exposure to a higher temperature, freeze–thaw cycles, marine environment, and acid and alkali attack will be comprehensively reviewed. A literature review revealed that increasing alumina silicate content, such as slag and metakaolin, and increasing the Na2SiO3/NaOH ratio and alkali-activator-to-binder ratio improve the hardened GC. However, increasing slag and metakaolin content and the Na2SiO3/NaOH ratio has an adverse impact on its workability. Therefore, finding the optimum mix design for using RCA in GC is vital. Moreover, there is a scope for developing a self-compacting GC cured at ambient temperature using RCA.

Graphical Abstract

1. Introduction

The construction industry is arguably one of the significant waste sources, generating 40% of the complete solid waste worldwide [1]. This type of waste is generated during a facility’s construction, operation, and end of life [2], 35% of which has been sent to landfills worldwide [3,4]. It has had detrimental impacts on the environment over the years and increased the total construction cost due to the landfill levies and the cost of waste transportation [5].
The linear economy as a conventional strategy is an inappropriate solution for tackling the detrimental impacts of excessive CDW generation and natural resources consumption, so the concept of circular economy (CE) is introduced as a new solution in this regard [6]. CE is defined as a regenerative system with the minimum resource input, waste, pollutants, and energy wastage by slowing and tightening the material and energy loops, which can be accomplished by durable design, maintenance, reusing, repairing, remanufacturing, refurbishment, and recycling [7]. Based on this definition and other relevant literature, the CE helps optimise the raw material consumption, saving the material’s value during the whole lifecycle, preventing further waste generation, and supporting natural resource preservation [6,8]. The CE is also associated with the benefits of recycling and using by-product materials [8,9]. The construction industry can adopt the circular economy well, which has proper capabilities [8,10]. Meanwhile, the CE is considered an integral part of the CDW policies in some countries, such as Australia [11]. This research summarises the state of the art of incorporating the recycled concrete aggregates in a geopolymer concrete that uses industrial by-produced materials, such as fly ash and slag.
Added to the environmental drawbacks of CDW, natural aggregate (NA) resources are in danger of depletion due to the increase in urbanization and the construction industry’s need for a vast amount of concrete, in which 60% to 75% of its volume encompasses NA [12]. Extracting, transporting, and producing specific sizes of NA are energy intensive, and replacing them with recycled concrete aggregates (RCA) can save energy by 90–280 gigawatt hours [13].
In addition, using waste in concrete can decrease many adverse effects of concrete on the environment [14]. To this end, RCA obtained from a demolition building or CDW from landfilled sites has been used instead of NA. For example, Ghorbani et al. [15] replaced 25% of natural coarse aggregates with crushed concrete, while the strength of the ordinary Portland concrete improved. It is also reported that RCA incorporation in ordinary Portland cement (OPC) concrete could increase up to 30% [16]. However, geopolymer concrete provides the opportunity of using more amount of RCA. Lim and Pham [17] replaced all the aggregates with RCA, and compressive strength (CS) reached 46.24 MPa, which is a proper CS for structural application. Hence, geopolymer concrete has the potential to reuse a substantial amount of CDW.
In addition to the detrimental impacts of CDW, the construction industry is responsible for 30% of carbon dioxide generation globally [1]. The cement industry produces 8% of the total CO2 in the world [18]. Every kilogram of Portland cement consumes approximately 1.5 kg of raw material and has around 0.8 kg of CO2 [19]. Due to the high cement usage, concrete is a significant source of carbon emissions in the construction industry. There exist many attempts for CO2 reduction in the construction industry. One attempt is by Davidovits [20]. He suggested replacing Portland cement totally or partially with geopolymer material, such as fly ash (FA), ground-granulated blast-furnace slag (GGBS), silica fume, and red mud metakaolin (MK) and incinerated ash of municipal solid waste. Investigations show that using geopolymer concrete, which does not contain cement, reduces the global warming effect by up to 53% [21]. Besides, replacing RCA in a GC instead of NA minimises the leaching of toxic material, such as arsenic [22,23], chromium, and selenium in a silica fume FA-based GC [23].
The primary question addressed by this review study is: “How do various factors and conditions affect the mechanical and durability properties of a fresh and hardened structural RCA-based geopolymer concrete?” This study aims to review and analyse previous research on using RCA in geopolymer concrete for structural purposes. To this end, the general background to the properties and capabilities of geopolymer concrete for using RCA is presented to demonstrate the importance of using GC for reusing crushed aggregates. The method section provides the technique for retrieving relevant papers. Following that, the essential specifications of RCA-based geopolymer concrete are critically reviewed to evaluate the effect of each factor on the mechanical and durability properties of fresh and hardened geopolymer concrete with RCA.

2. Contextual Background

2.1. Geopolymer Concrete

Geopolymer is an environmental-friendly substitution for ordinary Portland cement, which reduces CO2 generation and reuses industrial by-product material, leading to lower cost. Its mechanical properties are the same as OPC concrete and demonstrate better performance in exposure to fire and harsh conditions [24]. Geopolymer concrete is obtained through the reaction between an alkaline activator and aluminosilicates, which are primarily used as fly ash [25], ground-granulated blast-furnace slag [26], and metakaolin [27].
The most popular and well-established type of GC is FA based. It is because fly ash is a great source of silica and alumina material, which makes it an excellent binder. Curing at a high temperature helps improve the compressive strength of fly-ash-based geopolymer concrete [28]. Curing in high temperatures limits the application of fly-ash-based GC, so slag helps to reduce the heat demand and improves the early-age strength of geopolymer concrete [29]. Unlike fly ash and slag, metakaolin is not an industrial by-product material and is obtained by heating kaolinite at temperatures higher than 500 °C. MK is a reach source of alumina and silica. Because of its highly reactive pozzolanic nature, it quickly reacts with Ca(OH)2, which generates hydrated calcium aluminates and silicon aluminates with the filling properties, improving concrete’s mechanical properties and durability [30].
There is no fixed mix guideline for preparing geopolymer concrete, and it is based on trial and error [31]. In the case of using a liquid alkali activator, the first step is preparing the alkaline solution 12 or 24 h earlier than the time of the experiment, as the dissolution of NaOH causes a high temperature and needs to be cooled before mixing with the other components [32,33]. Regarding mixing CA-based GC, Zhang et al. [34] mixed aluminosilicate precursors and alkaline activators before adding aggregates to obtain the binder of the mixture and then added aggregates. Uğurlu, Karakoç, and Özcan [26] first mixed fine aggregates with the binder and alkaline solution and then added coarse aggregates. Alumina silica material can be added and mixed after mixing aggregates with extra water [35], or in some studies, aggregates and aluminosilicate materials are mixed together simultaneously. Then an alkaline solution is added and mixed [36]. If a superplasticiser is required, it can be added finally [35,36]. However, Mehta and Bhandari [37] added a superplasticiser to the binder of the mixture and then mixed it with the aggregates. As regards better workability, in some cases, extra water is added at the final stage and then mixed thoroughly [36].
Geopolymerisation takes place in three main steps, including (1) the dissolution of Al and Si of an alumina–silica component by the action of OH ions, (2) precursor ions’ transition into monomers, and (3) monomers’ reconvertion to create three-dimensional polymer chains of Si-O-Al-O [38,39]. The polycondensation of hydrolysed aluminate and silicate components leads to the hardening of the geopolymer. The geopolymer component is shown as nM2O.Al2O3.xSiO2. yH2O. M is an alkali metal obtained from alkali activators, such as NaOH, KOH, NaCO3, and Na2SO4. Ions of Na, K, and Ca active Al and Si speed up the reaction [40].
As illustrated in Figure 1, within the mixing of RCA-based GC, at first, alumina silicate powders and old paste adhesive to RCA absorb water, and precursor material is formed. Meanwhile, many monomers of SiO4 and AlO4 are released due to the activation of aluminosilicate material with an alkali activator. Then, SiO4 and AlO4 are rapidly mixed with precursors. Through the continuation of the reaction, the framework grows and is connected. Ultimately, three-dimensional polymer chains of Si-O-Al-O are created [41].

2.2. Recycled Concrete Aggregates

RCA consists primarily of three components, including the body of a cement mortar, a mortar-covered gravel, and a gravel fully detached from the mortar. Fine RCA consists of sand particles adhering to cement slurry, sand particles without cement, and a little portion of broken stone. [42]. RCA has greater angles, rougher surfaces, and a more significant surface area than NA, which makes RCA’s chemical and mechanical properties significantly different from NA’s [42].
Although incorporating recycled crushed concrete as aggregates in concrete is environmental preservation, it has some drawbacks. The durability issue is considered the most crucial challenge of using RCA. For example, in one case, adding RCA causes an increase in chloride penetration by 27% [36]. In addition, the old paste around the aggregates causes more porosity than NA-based GC, leading to increased water absorption [43]. For example, replacing 50% of coarse aggregates with RCA results in around 5% enhancement of the initial water absorption rate, increasing to 18% by replacing 100% RCA [33]. In addition, replacing NA with RCA harms the mechanical properties of GC. For instance, replacing 100% NA with fine RCA reduces the tensile and flexural strength of a fly-ash-based GC by 27% and 36%, from 2.6 to 1.9 MPa and from 3.9 to 2.5 MPa, respectively [44]. Above all, RCA decreases the CS due to a lower mechanical characteristic of RCA. As an illustration, replacing 50% RCA in an FA-based GC reduces compressive strength by around 30%. It increases the percentages, resulting in a further drop in compressive strength [45].
Incorporating RCA in GC demonstrates better results compared with OPC concrete, even improves the compressive strength and module of elasticity [34,46], and enhances the interfacial transition zone (ITZ) bond between aggregates and paste compared with OPC-based concrete [47,48]. Despite the porous structure of old cement paste material, the rough surface of crushed aggregates provides better bonding between GC paste and aggregates. The unreacted bonding material fills the pores and cracks, transferring load better than RCA in OPC concrete [44,46,49]. Besides, the alkali-activated bonder in GC causes a reduction in Ca(OH)2 and voids, improving matrix homogeneity, which results in higher compressive strength compared with RCA-based OPC concrete [46]. For example, Zhang, Wan, Wu, and Hu [34] observed a decrease in the compressive strength of OPC concrete by using various amounts of RCA, while they stated that the compressive strength of GC with 30% and 70% RCA is higher than that GC with NA. However, several factors affect the fresh and hardened RCA-based geopolymer concrete’s mechanical and durability properties, which should be analysed to introduce an optimised concrete mix. In this review, most of research on the various methods and techniques is studied and critically examined.

2.3. Previous Review Studies

Several review studies on RCA-based geopolymer concrete have been published, demonstrating the importance of the outcomes and knowledge building in this field for the research community [50,51,52,53]. However, they do not address all aspects of implementation in the construction industry. A review study by Ye, Xiao, Duan, and Li [51] focused on geopolymer concrete made from recycled brick and concrete powder. They reviewed the effects of some parameters, such as alkaline solution, precursor material, and curing condition, on the concrete’s flowability, compressive strength, and durability. However, they did not study the effect of crushed concrete as the aggregates, and they focused on the mix of CDW, namely, concrete powder and recycled brick. In like manner, Xu, Huang, Liu, Deng, Hui, and Deng [52] conducted a literature review on the various types of aggregates recycled from geopolymer concrete, mudstones, rubber, and so on and their effects on the compressive, tensile, and flexural strength of GC. At the same time, they did not focus on just using aggregates made of crushed OPC concrete. Upshaw and Cai [50] reviewed the progress in utilising fine and coarse aggregates in the concrete and some of their effects. They also reviewed existing studies on various methods for improving the properties of crushed concert aggregates. They did not focus on geopolymer concrete with structural implications. Younis, Salihi, and Ibrahim [53] studied the effect of RCA on the compressive strength and flowability of GC. They did not evaluate the effect of RCA on the durability of the concrete in harsh conditions. Despite previous research, a critical review on the relevant, effective parameters on the properties of RCA-based GC with structural application remains to be found. Therefore, there is a scope for conducting a holistic literature study on using crushed concrete aggregates to produce structural geopolymer concrete.

3. Research Methodology

3.1. Systematic Review

The approach for conducting this research was selected as a systematic review, which is a suitable method for research synthesis to determine and collect international evidence related to a specific research question or research questions, summarize the results, and sometimes draw gaps of knowledge [54]. It aligns with the aim of this study to review the current evidence, synthesise the results, and finally provide a gap of knowledge for further research. The systematic review initially was popular in medical science. However, it is primarily applied in the construction industry [55,56].

3.2. Data Extraction

Within this review study, keywords of geopolymer AND (“crushed concrete” OR “recycled concrete” OR “recycled aggregate” OR “crushed aggregate”) are utilised for searching the topic, keywords, and abstract of the papers. Scopus is chosen as a database as this database is considered a proper database in the construction-related literature [2]. The most recent search version was on 4 April 2022, without any time limitation for selecting papers. All papers, including articles, conference proceedings, and book chapters written in English, were chosen for further studies. As illustrated in Figure 2, 200 papers based on the keywords mentioned above were extracted by searching on Scopus. Their title and abstract were thoroughly read based on the criteria of (1) paper must be related to structural applications of the geopolymer concrete and (2) crushed ordinary Portland concrete (OPC) must be used as the recycled aggregates. The excluded papers were about applying geopolymer as pavement or rolling concrete since they are not about the structural application of the GC (criteria 1) and must be excluded. Besides, several papers regarding other types of recycled aggregates, such as steel fibres or polyethylene terephthalate (PET) waste, sludge, crushed clay, or ground mixed recycled aggregates, were excluded, as papers must study the usage of aggregates made from crushed OPC (criteria 2). Therefore, 105 papers were obtained for conducting the literature review on the content of each paper, except that the full text of three papers could not be obtained. After examining the entire scope of the remaining 102 papers, 43 were excluded since some used the mixed CDW as the aggregate and did not focus on the crushed concrete as aggregates. Others were related to produced concrete with a lower compressive strength, unsuitable for structural application, and used in pavement or sub-base or waste concrete as an alumina silicate. Besides, four papers were excluded, as they were review studies and are considered the previous review study in the background section. Hence, this review study was conducted on 55 relevant papers, as illustrated in Table A1.

4. Findings and Discussions

4.1. Mechanical Properties of RCA-Based Geopolymers

4.1.1. Effect of Sources of RCA and Their Composition

There exist several sources for RCA. Most of research was conducted on GC with RCA obtained from crushed concrete lab specimens with the specified range of CS [36,41,58,59] or without specified CS [33,44,60,61]. Table A1 summarises experiments conducted on GC with RCA obtained from CDW landfilled sites [17,46] or extracted from a demolished building with specified CS [62,63] or unknown CS [64,65]. There is no agreement among researchers regarding the effect of the parent concrete. Some researchers believe that the quality of the parent concrete does not affect the mechanical specifications of the RCA, while the quality of the RCA is crucial to be considered [66,67]. On the other hand, opponents pointed out that the quality of the concrete is related to its concrete parent specifications [68]. However, Ohemeng et al. [69] stated that RCA obtained from high-strength concrete with CS higher than 50 MPa does not negatively affect the RCA-based concrete but uses low to regular concrete for extracting RCA results in CS drop by up to 30%.
Several properties must be considered regarding concrete aggregates’ physical and chemical properties. The physical properties evaluated by most researchers are summarised in Table 1. Besides, the chemical compositions of RCA and NA are tabulated in Table 2.
As illustrated in Table 1, specific gravity, density, dry density, saturated density, bulk density, and apparent density of RCA are lower than those of natural aggregates. It is due to the old paste attached to RCA, which causes a more porous structure than NA [75]. Another reason is the crushing of the parent aggregates to obtain RCA, degrading the structure of the RCA [72]. Moreover, the water absorption of RCA is significantly higher than that of NA. It is also attributed to the porous structure of RCA from the old paste in the aggregates [72]. Furthermore, from the Los Angeles test results on RCA, mass loss is higher than NA due to RCA’s weaker and more brittle structure from the old cement paste in RCA [59,76].
To conclude, three sources of RCA are considered in the relevant literature: crushed concrete lab specimens with or without specified CS, CDW landfilled sites, and demolished buildings with or without specified CS. The physical specifications of specific gravity, density, dry density, saturated density, bulk density, and apparent density of RCA are less than NA, and the mass loss of RCA is higher than that of NA in the Los Angeles test.

4.1.2. Effect of Treatments on RCA

Controlling the water content of RCA is one of the challenges in using recycled aggregate concrete in practices [67]. In most of the literature, RCA is used in the saturated surface condition (SSD) [76,77], which, based on some studies, has a positive effect on the flowability and an adverse impact on CS [36,59,63]. Hence, there is a need to investigate the treatment techniques and their influence thoroughly and develop a recommended practice.
There are several methods for the treatment of RCA to mitigate the adverse effects of using RCA, such as high-water absorption, which is the most unfavourable. These treatments are categorised into two groups, including porosity reduction and reducing an old mortar layer by acid or thermal treatment. As regards porosity reduction, these methods include acceleration carbonation, bio deposition, sodium silicate, nanoparticles, polymer emulsions, and pozzolana material [12]. However, treated RCA is just examined in OPC concrete. For example, for using pozzolana material, Junak and Sicakova [78] used two methods for RCA treatment. One method is coating RCA with geopolymer slurry (FA based with 8 M NaOH and Na2SiO3) in the mixture, leaving it for 30 minutes, adding cement, and finally, adding other materials. Another technique includes coating RCA with geopolymer slurry, being cured at an ambient temperature for 28 days, and then being used for OPC concrete production. As can be observed in Figure 3, both treatment methods significantly decrease the water absorption of the specimens, especially when progressing the time from 28 to 365 days. Moreover, both techniques enhance the compressive strength of the samples to around the same strength of concrete with NA.
Similarly, Gupta, et al. [79] coated RCA with a mix of sodium silicate, FA, and NaOH and cured them at 85 °C for 24 h. RCA was applied for casting OPC concrete, and also 10% FA and 90% OPC concrete, exposing them to acid attack, demonstrating better results than the cement coated and uncoated RCA-based concrete. In the same way, Junak and Sicakova [80] used a treatment technique for reducing the water absorption of RCA by coating with coal FA and 10 M NaOH to develop a modified RCA-based OPC concrete.
To sum up, most of the studies used SSD RCA, which has an adverse effect on CS. Hence, some treatments on RCA are examined just in OPC-based concrete, and there is no study on incorporating them into geopolymer concrete. Among these techniques, coating RCA with slurry geopolymer material can help to improve CS and water absorption. Thus, there is a need to examine this method for developing RCA-based GC.

4.1.3. Effect of Alumina Silicate Material

As illustrated in Table A1, the aluminosilicate bonding materials used for preparing RCA-based GC include Class F (low calcium) Fly ash, GGBS, fly ash, FA/GGBS, MK, MK/GGBS, ultrafine slag, MK/bottom ash, MK/FA, FA/ferrochrome ash, low-calcium FA/GGBS, waste concrete powder/FA, Class C (high calcium) FA/cement, Class C FA/MK, Class F FA/silica fume, and class C FA.
An increase in the aluminosilicate content of GGBS and MK results in compressive strength enhancement. It can be attributed to using more aluminosilicate content, reducing the adverse effect of adding RCA. A further amount of aluminosilicate helps reduce the negative impact of RCA on CS. For instance, Uğurlu, Karakoç, and Özcan [26] reported an 11.29%, 6.16%, and 5.95% reduction in CS for 300, 400, and 500 kg/m3 of the binder content, respectively, in a GGBS-based GC with 100% RCA. They stated that more binder content reduces the proportion of RCA aggregates. On the other hand, GGBS contains a higher amount of calcium, increasing calcium-alumina-silicate-hydrate (C-A-S-H) gel, improving compressive strength, and declining the adverse effect of using RCA on the strength of GC. In addition, GGBS has a positive role in improving the rigidity of CRA-based GC [26,35].
Moreover, Xie, Wang, Rao, Wang, and Fang [62] observed that increasing GGBS/FA-based GC’s content of GGBS enhances the compressive strength of GC. They also believe that FA cannot generate enough calcium for a strong bond between RCA and geopolymer paste, so a combination of GGBS and FA was suggested for an RCA-based GC. Similarly, Lim and Pham [17] observed improvement in GC strength by increasing the percentage of ultrafine slag (UFS) replacement in a UFS/FA-based GC. They also added extra UFS and observed better CS. Besides, increasing the amount of replacing FA with MK in an RCA-based GC improves the mechanical properties of an RCA-based GC. For instance, if MK replaces 30% FA, the compressive strength improves by 43%, from 32.9 to 47.2 MPa. In addition, 30% MK replacement enhances the splitting tensile and flexural strength by around 30% and 22%, respectively. The improved strength can be attributed to the role of MK particles in speeding up the geopolymerisation and forming a denser microstructure [77]. Furthermore, increasing the ratio of GGBS to MK from 1:1 to 7:3 enhances CS by 39%. It is because GGBS reacts with an alkali activator easier than MK [81]. Moreover, Nuaklong, Sata, Wongsa, Srinavin, and Chindaprasirt [76] examined the effect of replacing Class C FA with Portland cement by 5%, 10%, and 15%, improving CS and reaching a 49 MPa 28-day compressive strength.
In conclusion, increasing the amount of aluminosilicate material, such as GGBS and MK, enhances the CS of RCA-based GC. Moreover, increasing the ratio of GGBS to MK improves CS. Regarding GGBS/FA, UFS/FA, MK/FA, and OPC/FA geopolymer concrete, decreasing the ratio of FA (or increasing the share of the other binder) improves the mechanical properties of GC.

4.1.4. Effect of Additives

Several additives are reported to help improve RCA-based GC properties, as illustrated in Figure 4 and discussed below.
Waqas, Butt, Danish, Alqurashi, Mosaberpanah, Masood, and Hussein [36] used low-calcium bentonite. They replaced 5%, 10%, 15%, and 20% of high-calcium fly ash with bentonite, while they used a NaOH/Na2SiO3 ratio of 2 and a NaOH molarity of 12. They pointed out that replacing 10% of bentonite increased the compressive strength and split tensile strength by 5.71% and 8.69%, respectively, compared with 5% bentonite replacement. They also stated that more than 10% replacement harms the compressive strength. Besides, the effect of bentonite on the compressive strength of GC with RCA is more than that of specimens with NA.
Graphene oxide is another additive that helps improve the compressive strength, flexural strength, and split tensile strength of RCA-based GC when RCA replaces 50% and 100% of its coarse aggregates. 0.05% Graphene oxide increases the compressive strength of GGBS FA-based GC with 50% and 100% RCA by 20.53–21.55% and 9.58–13.59% for ages between 28 and 90 days [33]. Graphene oxide enhances the geopolymerisation reaction [82].
Fibres help decrease the brittleness characteristic of GC, as GC is brittle compared with OPC, and the tensile strength and flexural strength of GC are lower than those of OPC. Besides, fibres improve crack resistance and toughness [83,84]. Moreover, fibres help control the expansion of shrinkage cracks in RCA-based concrete, as adding RCA causes an increment of shrinkage cracks due to the old mortar attached to RCA [85]. Features such as fibre type, dimension, length-to-dimeter ratio (aspect ratio is between 30 and 150), strength, volume fraction, stiffness, and ITZ properties affect GC’s mechanical performance [86]. As illustrated in Figure 5, the impact of a different fibre content on RCA-based GC was studied in the previous literature. Among the studies, Mehta and Bhandari [37] studied the effect of adding alkali-resistant glass fibre on the mechanical properties of RCA-based GC. Glass fibre is made from silicon oxide and zirconium oxide. They found that adding glass fibre positively affects flexural strength by 20%. To this end, they added various amounts of glass fibre, including 0.3%, 1%, 2%, 3%, and 3.5% by the weight of concrete, to a GC with 50%, 80%, and 100% coarse RCA. The best result was reported for the combination of 3% glass fibre and 50% RCA, which increased the 28-day compressive and flexural strengths to 62 and 13 MPa.
Polyvinyl alcohol (PVA) fibres are another fibre used as an additive in an MK RCA-based GC. The addition of 1.2% PVA increased the compressive and flexural strengths of RCA-based GC by 26.6% and 83.8%, reaching 47.17 MPa and around 9 MPa, respectively [32]. In like manner, Xu, Huang, Liu, Deng, Hui, Deng, Zhao, and Qin [60] used steel fibre in a FA/MK-based geopolymer with RCA. They observed that 28-day compressive strength, tensile strength, and flexural strength increased by 15.72%, 64.1%, and 60.95%, respectively, reaching 47.11 and 5.12, and 7.79 MPa, respectively, while it contained 2.5% steel fibre. It can be attributed to the role of fibres as a bridge to transfer stress. Steel fibres also produce a three-dimensional grid system, enhancing distributing, transmitting, and bearing stress [60]. Additionally, basalt fibre improves the mechanical characteristics of RCA-based MK/GGBS geopolymer concrete. In other words, Basalt fibre helps to enhance 28-day the compressive and flexural strengths by 20% and 57%, reaching 42 and 8.8 MPa [70]. Similarly, adding less than 0.1% carbon fibres (CF) helps to improve the matrix structure of GC, leading to a compact microstructure and increasing the compressive strength by 11% to 21% for 0.2% CF and reducing the adverse effect of RCA replacement in GC. The optimum amount of CF is 0.2%, and further addition does not provide significant compressive strength. CF also improves the splitting tensile and flexural strength by 38% for 50% RCA and 54% for 100% RCA, respectively [44].
The iron filling also increases the compressive strength of an MK RCA-based GC by 2%, 5%, and 10% for 0.5%, 0.75%, and 1% iron filling, respectively. It also enhances the splitting tensile strength, flexural tensile strength, and modulus of elasticity by 32%, 42%, and 11%, respectively, for 1% iron filling. Iron filling fills the pores and improves the concrete’s internal structure [64].
Hypergolic and calcined coal gangues positively impact GC’s compressive and splitting strength. Hypergolic coal gangue demonstrates better results. It not only causes higher strength in NA-based GC but also improves the compressive strength and split tensile strength when replacing 30–50% RCA [71]. Ultrafine slag is another additive material that increases the compressive strength of FA-based GC. 30% of this material can provide 41 MPa compressive strength, while 100% of RCA is used. This effect is due to forming the improved calcium silicate hydrate gel, filling pores, and leading to a denser structure. Ultrafine slag also creates a shell coating around the RCA, reducing the stiffness difference between paste and RCA, resulting in better compressive strength [17].
Alhazmi, Shah, and Mahmood [58] replaced water with three effluents of sugar mill effluent mix (SF), fertilizer mill effluent mix (FF), and textile mill effluent mix (TF), reaching CSs of 16, 23, and 32 MPa. TF demonstrates the best CS improvement from 24 to 32 MPa. However, it harms the mass loss in acid attack tests. Rice husk ash (RHA), an agriculture waste, can be used as a SiO2-reach additive to improve the compressive strength of fly ash RCA-based geopolymer concrete cured in an ambient environment. It reaches a compressive strength of 36–38.1 MPa for the incorporation of 1.2% to 3.6% of the fly ash weight. It is because of the effect of RHA on the Si-O-Si bonds, resulting from having denser hydration products. Moreover, silica oxide increases the amorphous glassy phase, enhancing compressive strength. However, it harms the concrete fire resistance due to reduced voids and pores between paste and aggregate [59].
Adding 1% and 2% nano-SiO2 also improves the compressive strength of FA-based recycled aggregate GC from 32.9 to 39.6 and 42.6 MPa. It is attributed to the generation of a higher amount of silica, increasing the SiO2-to-Al2O3 ratio and leading to a higher amount of Si-O-Si bonds, which are more potent than Al-O-Al. Still, the additional nano-SiO2 harms CS by reducing water evaporation, preventing GC structure formation [76].
To conclude, adding fibres improves the mechanical properties of RCA GC. It is because the fibres bridge the crack region and prevents formation around RCA. The mortar around the RCA causes more pores once it is mixed with paste, producing a weaker bond between them. Therefore, cracks might be formed due to external matters. However, fibres can prevent crack formation [32]. The effect of fibres on the flexural strength is significantly higher, as fibres contribute to tension force resistance during bending, decreasing the generation of the cracks.

4.1.5. Effect of RCA Content

Much research demonstrates the adverse impact of RCA on the compressive strength of GC. On the other hand, observation exists for increasing compressive strength by adding RCA.
Replacing 30% of the coarse aggregates with crushed concrete when using fly ash as a bonding material reduces compressive strength by 13%, from 17.1 to 14.8 MPa for 0% and 30% RCA [87]. Likewise, as regards FA GGBS-based geopolymer concrete, using up to 30% RCA causes a slight decrease in compressive strength, and adding more RCA reduces the compressive strength significantly. Hence, the optimum amount of RCA was 30%. This trend was also observed in split tensile strength [88]. Similarly, in FA/GGBS geopolymer concrete, replacing coarse aggregates with RCA decreased the compressive strength at 28, 56, and 90 days by 1.75–4.46% and 12.89–17.77% for all ages and 50% and 100% RCA replacement, respectively [63]. Bhardwaj and Kumar [33] also confirmed decreasing compressive strength when adding RCA in a GGBS/FA concrete. Replacement of limestone coarse aggregates with RCA in a fly-ash-based GC demonstrates a 9% to 13% decline in compressive strength due to the porous structure of RCA [59].
Incorporating RCA in the geopolymer concrete improves the compressive strength in lower percentages. For example, the 28-day CS of GC increased from 24.27 to 24.51 MPa by adding 30% RCA, rising to 24.91 MPa by 50% RCA, and then dropping to 24.24 MPa by 70% RCA, ultimately reaching 23.58 MPa when 100% RCA was used. Parthiban and Saravana Raja Mohan [89] also examined a 50% RCA replacement as an optimum amount of RCA in GGBS-based GC. Likewise, Kathirvel and Kaliyaperumal [65] considered 50% of RCA as an optimum percentage of RCA in a GGBS-based GC with a CS of about 56 MPa. Similarly, Sanusi, Tempest, Ogunro, and Gergely [22] pointed out that 40% and 50% RCA are the optimum contents in a FA silica fume GC with CSs of 53.2 and 54.7 MPa, respectively. Sanusi, Tempest, and Ogunro [23] reported CS enhancement by 36% from 42 to 57 MPa by 50% RCA replacement.
The porous structure of RCA and the microcracks accrued in the original breakage explain the adverse effect of higher percentages of RCA on the mechanical properties. Although this can improve the fraction between RCA and paste, their attachment becomes weaker. In addition, extra water absorbed by RCA in SSD is more than natural aggregates, resulting in a weaker GC [59,71,90].
However, Tran [91] stated that replacing 100% of coarse RCA decreases the compressive strength by 4.8% compared with NA. The author believes that the properties of normal coarse aggregates and crushed concrete are similar. Krishnan and Purushothaman [92] observed a slight increase in CS when replacing 100% of coarse NA with RCA. They believe that this is due to the incorporation of high-quality RCA. In another research, all the coarse aggregates were replaced by RCA and reached 48 MPa [35]. Similarly, Ren and Zhang [93] observed enhancement in compressive strength when replacing 100% of RCA. RCA’s water absorption results in a lower amount of alkaline solution and higher CS.
Replacement of less than 10% of fine RCA enhances compressive strength, as the fine aggregates can fill the voids among the significant components [94]. However, replacing higher percentages of fine recycled aggregate negatively impacts the compressive strength of GC. It can be attributed to the higher water absorption of the fine RCA, including sand and cement paste, negatively affecting the geopolymerisation by disturbing the alkali activator. For instance, Tran [91] replaced 25%, 50%, 75%, and 100% of the fine aggregates with RCA and found out that increasing the fine RCA results in compressive strength drop, and the optimum amount of fine RCA was reported to be 25% with a reduction of just 2% in compressive strength. Saha et al. [95] also observed a 5.26% CS drop by replacing 25% fine RCA in a FA GGBS-based GC.
The main reasons for the CS improvement in RCA-based GC include: (1) the porous structure of the old paste concrete in RCA, which absorbs the alkaline solution, resulting in partial geopolymerisation in the original ITZ. Besides, the absorption of a more alkaline solution by RCA improves the new ITZ between RCA and the new paste. (2) A higher amount of calcium brought by RCA to the mixture speeds up GC’s hardening. It is due to the C-S-H generation in the existence of the calcium. Moreover, the more refined porous structures provided by calcium enhance the CS. (3) RCA has rougher surfaces, so increasing the amount increases sharp edges, increasing the friction between RCA and geopolymer paste, ultimately enhancing the compressive strength. (4) Adherent mortar around RCA causes a decline in the elastic modulus of GC, leading to little differences between RCA and GC paste. Hence, with the decline in the possibility of fracture. (5) RCA absorbs more water, helping complete the hydration reaction of RCA. (6) An old OPC adhesive to RCA adds calcium and CSH gel formation, enhancing GC’s compressive strength [22,23,71,89,93].
The size of the crushed aggregates also has a critical role in the mechanical properties of the RCA-based concrete. In one experiment, recycled concrete was crushed into pieces smaller than 5, 2, and 1 mm, then incorporated into an MK-based geopolymer. The best result was reported for aggregates with a particle size smaller than 2 mm, where the compressive strength was around 40–45 MPa. However, using particles smaller than 1 mm causes a decline in compressive strength, as their solidification process is faster than geopolymer’s solidification. Besides, bulk density decreases because of trapping gasses, leading to a drop in compressive strength [96]. Zhang, Wan, Wu, and Hu [34] also stated that replacing 70% of coarse aggregates by RCA with a maximum size of 20 mm improves the compressive strength and crack resistance of MK/FA-GC reinforced beams. It might relate to the lower amount of the concrete paste in GC, which distributes stress uniformly. The smaller particles of RCA contain more attached old mortars than coarse RCA, resulting in weaker characteristics of finer RCA [34,97].
To conclude, the effect of RCA content on CS is diverse. Some evidence shows that RCA has an adverse impact on CS, but if RCA is used in the lower content, the negative effect is negligible or even enhances CS in some cases. A further amount of RCA primarily results in reducing CS. However, there is evidence that a total replacement of RCA improves CS. In addition, the size of RCA affects CS. Compared with fine RCA, coarse RCA provides GC with better mechanical properties when replaced with NA.

4.1.6. Effect of Alkali Activator

An alkali activator is needed to geopolymerise active binder material [98]. It can be used as a solid form for a one-part GC or liquid form for a two-part GC [99]. To the author’s knowledge, there is no research on the one-part RCA-based geopolymer concrete. All the relevant studies in this field used liquid alkali activators, of which most types include the combination of sodium hydroxide (NaOH) and sodium silicate (Na2SiO3) [93] or potassium silicate solution [34].
Regarding liquid alkali activators, in most cases, NaOH, which is in the form of flakes or pellets, was mixed in the water to produce the needed concentration of NaOH, which causes a substantial amount of heat, so it should be prepared earlier than the concrete mixture [92]. As discussed below, some alkali-solution-related factors affect the RCA-based GC.
Previous experiments revealed that an increase in NaOH molarity (M) from 8 to 12 improves the compressive strength of RCA-based geopolymer concrete [92]. Nuaklong et al. [100] observed an increase in CS by adding NaOH molarity from 8 to 12 in a FA RCA-based GC and then a drop in CS at 16 M NaOH. Another experiment also confirmed this observation [101]. The reason is that the higher molarity of NaOH provides a higher amount of alkaline, increasing the chain of alumina silicate. Then the reaction between Si and Al tends to be activated. Besides, by curing at a higher temperature, high molarity helps this reaction happen suddenly at the primary age of concrete, leading to enhanced early strength [40]. Besides, Alalikhan, Habelalmateen, and Alhabbobi [25] observed CS enhancement from 8 to 14 NaOH molarity. By contrast, Ren and Zhang [93] observed a slight drop in compressive strength by increasing the NaOH molarity of an RCA-based geopolymer from 10 to 14. They mentioned that this is due to the higher amount of water in 14 M NaOH than 10 M NaOH molarity, resulting in an adverse effect on compressive strength. However, they did not mention the CS for 12 M NaOH. The CS might be increased by adding NaOH molarity from 10 to 12 M NaOH, and then dropped by 14 M NaOH. As illustrated in Figure 6, CS enhancement can be observed between 8 and 12 NaOH molarity, and exceeding the NaOH molarity by more than 12 reduces CS. This finding is also confirmed by Alhawat et al. [102].
Another factor is sodium silicate modulus. Wang, Bian, Li, Dai, Chen, Jiang, Zhang, Dong, Huang, and Ding [41] stated that the reduction of Na2SiO3 modulus improves the strength of RCA-based GC but increases the brittleness. They prepared seven concrete mixtures with Na2SiO3 moduli of 0.6, 0.9, 1.2, 1.5, 1.8, 2.1, and 2.4, while other parameters remained constant. The highest compressive strength was obtained when the modulus of Na2SiO3 was 0.9. The reason is that decreasing the Na2SiO3 modulus raises the amount of OH and Na, activating more alumina, calcium, and silicate ions. It will assist in forming more C-A-S-H gel and sodium aluminosilicate hydrate (N-A-S-H) gel, which results in a denser geopolymerisation structure. Hence, the compressive strength improves [41].
Moreover, the sodium-silicate-to-sodium-hydroxide ratio (SS/SH) is vital for compressive strength. Based on a study by Koushkbaghi et al. [103], three SS/SH ratios of 2, 2.5, and 3 were examined in an MK-based geopolymer with 10% to 30% RCA. More SS/SH increases the geopolymerisation reaction, leading to better compressive strength. However, by increasing the amount of RCA, the effect of SS/SH becomes negligible due to the angular shape of the RCA. Due to the adverse impact of RCA on workability, it is suggested to decrease the SS/SH ratio [74]. However, the effect of SS/SH depends on the type of binder material and curing conditions [103,104].
Moreover, increasing the ratio of alkali activator solution to binder materials (AAS/b) enhances the workability, decreasing the compressive strength. Regarding the higher amount of water absorption of RCA, in some cases, it suggests increasing the alkali-activator-to-binder ratio [72]. For example, in a fine RCA-based FA GC, increasing the alkali-activator-to-binder ratio from 0.4 to 0.6 results in enhancing CS due to the higher amount of alkali activator, which results in a better reaction between the alkali activator and FA [95].
Increasing the NaOH molarity from 8 to 12 can enhance the mechanical properties of the RCA-based GC. Moreover, reducing the sodium silicate modulus causes both CS and brittleness increment, so obtaining the optimum amount of Na2Sio3 modulus is crucial. In addition, increasing the SS/SH ratio improves CS, but it is suggested to decrease SS/SH due to the adverse effect of RCA on workability. In addition, increasing the AAS/B ratio can improve the CS of the RCA-based GC.

4.1.7. Effect of Curing Regime

Geopolymer concrete can be cured at an ambient temperature; however, higher temperatures can help to improve chemical reactions between silica ions and alumina ions, enhancing compressive strength [75,93]. Besides, the geopolymerisation process accelerates at higher temperatures and increases its compressive strength [105]. Hence, a 28-day compressive strength is higher than a 7-day CS of a GC when the GC is cured at 80 °C for the first 24 h. The reason is that the geopolymerisation is almost completed during the high-temperature curing early age. It minimises compressive strength gain for the rest of its life [35]. Moreover, a higher temperature helps generate a compact aluminosilicate gel, improving the bond between RCA and unreacted aluminosilicate [35]. Not completing geopolymerisation in low-temperature curing could result in unsatisfying compressive and tensile strength [35,61].
As illustrated in Figure 7, curing at 60 °C for 48 h increases the compressive strength of fly-ash-based GC by 67% [101]. Likewise, Kanagaraj, Kiran, Anand, Al Jabri, and Justin [61] tested FA-based geopolymer concrete with 40% coarse recycled aggregates. They examined three curing techniques of heating in an oven at 60 °C for 24 h, ambient temperature, and water curing. The results obtained by curing at 60 °C improve compressive strength, elastic modulus, and toughness, while the other two curing methods of ambient temperature and water curing are not beneficial. Likewise, curing at 60 °C for 24 h of an FA RCA-based GC demonstrates a 10% improvement in compressive strength, from 30–31 to 34–35 MPa [75]. Delayed ambient temperature settings are a downside of low-calcium GC [106], limiting GC application to just precast concrete. However, GGBS can be used with FA to help receive an early initial setting without elevated temperature and ambient temperature [33].
Regarding the analysis of the curing temperature effects, Tran [91] examined the impact of heating during curing of a fly ash RCA-based GC and pointed out that increasing the temperature from 80 °C for 24 h to 120 °C for 8 h increases the compressive strength by 4–6%. It contrasts with another study on the rising curing temperature, which demonstrates that, at first, the compressive strength of fly-ash-GGBS-based GC increases with a temperature of 80 °C. The compressive strength will decrease, so the optimum temperature was reported to be 80 °C. In other words, between 80 and 100 °C, a reduction in compressive strength was observed [35]. The reason is that a higher temperature harms the microstructure of the GC, resulting in incremental cracks [107].
Researchers have no agreement regarding the optimum curing temperature for geopolymer concrete. Some believe that curing with less than 60 °C of fly ash GC will not improve the compressive strength. However, others argue that 75–85 °C is the optimum temperature. This difference might be due to the usage of various alkali activators. Besides, curing temperature has different effects on multiple aluminosilicates. For instance, regarding fly-ash-GGBS-based geopolymer, although a low temperature is proper for the reaction of GGBS, in higher temperatures, fly ash is dominated [35].
As regards the effect of curing time on compressive strength, geopolymerisation accelerates at first (within the first 12 h). The early strength of GC improves, and if curing continues for 24 h, the strength will increase slowly. Krishnan and Purushothaman [92] stated that curing for up to 24 h enhances geopolymerisation, resulting in a proper bond between alumina and silica. However, curing at a high temperature for a long time has an adverse effect, resulting in microcracks in the geopolymer matrix due to thermal stress [35].
To conclude, a higher temperature helps speed up geopolymerisation, resulting in strong bonding between RCA and unreacted aluminosilicate and enhancing CS. By increasing the temperature of curing, the CS increases at first and then drops by increasing the temperature and continuing heating, so it is crucial to find the optimum temperature and time of curing. Curing at an elevated temperature limits GC application to just precast concrete. Using GGBS with FA helps to cure GC at an ambient temperature, so it is possible to cast in place.

4.2. The Durability of RCA-Based Geopolymer Concrete

Throughout the life cycle of a structure, exposure to a harsh environment impacts concrete performance. These effects include chemical attacks, weathering, degradation, and abrasion. Besides, some factors, chloride penetration, water absorption, sorptivity, submerged absorption, and the existence of too many voids and pores, impact the durability of concrete [108]. In addition, concrete might have severe exposure to high temperatures, a marine environment, freezing and thawing cycles, and acid attack. Replacement of RCA primarily harms durability due to the increment of the voids and pores between the aggregates and paste, so it is of utmost importance to evaluate the durability properties of RCA-based geopolymer concrete.
On the other hand, geopolymer concrete has a more porous structure than OPC concrete due to the alkaline activator and sodium silicate [109]. However, Srinivas and Manoj Anand [110] stated that a 30% RCA content in GC demonstrates better sorptivity and water permeability results than OPC concrete. Despite this, sorptivity and water permeability are slightly affected by adding RCA.

4.2.1. Exposure to a Marine Environment

As regards the evaluation of the durability of structures exposed to a marine environment, a permeability test shall be conducted. Ayub, Mahmood, and Khan [87] did not suggest using RCA-based GC for a marine environment based on a permeability test on FA-based GC. They reported that water penetration in specimens with 30% RCA is higher than that in NA-based GC, and further water penetration can be seen by continuing the tests from 28 to 720 days. It is because of old mortar attached to RCA, which leads to significant water absorption compared with NA-based GC. Besides, they stated that the water penetration of GC is higher than that of OPC due to the effect of the alkaline solution in creating a more porous texture. Additionally, a higher amount of sodium silicate enlarges the pores’ size, negatively affecting water permeability [87,109]. However, Srinivas and Manoj Anand [110] conducted a permeability test on the class F fly ash/GGBS geopolymer with 30% RCA. They observed that although RCA increases permeability, it is in an acceptable range.
Ayub, Mahmood, and Khan [87] also exposed RCA-based geopolymer concrete to a salt spray in the form of a fog to simulate a marine environment. The potential half-cell tests revealed that RCA-based GC is vulnerable in a marine environment. The pores in GC lead to a higher conductivity, resulting in a higher chloride penetration, increasing the chance of steel corrosion and debonding between concrete and steel bars.
Chloride ion migration is also crucial in marine conditions. If the amount of chloride ion increases on the surface of the steel bars, corrosion will occur, resulting in a volumetric change due to iron rust. It results in spalling the concrete around the steel bars. By using FA, the chloride penetration depth decreases because of creating CSH gel and filling the pores between paste and aggregates, leading to a denser structure and avoiding chloride migration [58]. In addition, Nuaklong, Sata, and Chindaprasirt [77] pointed out that increasing the amount of MK in an MK/FA RCA-based GC increases the chloride penetration depth. It is attributed to the decrease in the amount of FA, which results in a lower amount of calcium that decreases the CSH generation.
Lim and Pham [17] stated that the increment of RCA results in decreasing chloride penetration resistance due to the porous structure of ITZ between RCA and new paste, which produces paths for chloride ion penetration. Nuaklong, Sata, and Chindaprasirt [100] also pointed out that using coarse RCA in a GC results in a higher chloride penetration depth due to higher pores and voids in ITZ among RCA. Additionally, the weaker structure of the old paste attached to RCA helps penetrate chloride. Similarly, Saha, Rajasekaran, and Gupta [95] also observed increasing chloride penetration by incorporating 25% fine RCA.
Some factors affect the chloride migration of RCA-based GC. For instance, a higher NaOH molarity in an FA RCA-based GC decreases the chloride penetration. Increasing the NaOH concentration, Si, and Al results in improved GC polycondensation reaction, reducing pores and chloride migration [100]. Increasing the ratio of the alkali activator to the binder also improves chloride resistance [95].
Figure 8 demonstrates that increased RCA results in increased water absorption. As an illustration, by replacing 100% of coarse aggregates with RCA in a GC, water absorption increased by 29%. It might be due to the pores on the surface of RCA [36]. In addition, increasing RCA in a GC causes a higher sorptivity and water absorption [111]. Nuaklong, Wongsa, Sata, Boonserm, Sanjayan, and Chindaprasirt [74] confirmed that increasing the RCA content elevates the water absorption by 11.1%, 11.3%, 12.6%, and 13.4% for 25%, 50%, 75%, and 100% fine RCA compared with zero RCA. A GC with 30% RCA experienced increased water penetration at 28, 90, 180, 365, and 720 days compared with specimens with NA [87].
Replacement of coarse aggregates only increases water absorption. For instance, incorporating 50% and 100% of coarse aggregates in an MK GGBS-based GC increases the initial water absorption by approximately 5% and 18%, respectively [33]. Ayub, Mahmood, and Khan [87] believed this might be due to higher geopolymer materials and a smaller amount of aggregates in RCA-based than that of GC with NA. As regards salt spray and a potential half-cell test and analysis of the effect of chloride penetration and its impact on steel bars, NA-based GC indicates better results than RCA-based GC. However, the adverse effect of adding RCA to a GC is less than that of adding RCA in OPC concrete [87].
Some materials have a positive effect on the durability properties of RCA-based GC. For instance, adding PVA reduces the porosity ratio due to the role of fibres in preventing microcrack creation and minimising the porosity ratio. PVA also decreases mass loss in the abrasion test [32]. Likewise, graphene oxide helps lower the initial water absorption rate [33], and carbon fibres reduce water absorption [44]. Bentonite also positively impacts water absorption and chloride migration [36]. Besides, replacing 5% to 15% of FA with OPC results in better chloride ion resistance [76].
In conclusion, RCA negatively impacts water permeability and chloride penetration resistance due to the porous structure of ITZ between RCA and old paste, and increasing RCA content results in more water absorption and chloride penetration. However, the negative effect of RCA on the chloride penetration in GC is less than the effect of RCA in OPC concrete. A higher NaOH molarity and AAS/b decrease chloride penetration. Besides, some additives, such as PVA fibres, carbon fibres, bentonite, and graphene oxide, positively impact durability.

4.2.2. Exposure to High Temperature

Studying fire safety for a concrete structure design, and exploring which factors affect it, is essential. Exposure to high temperatures decreases compressive strength and flexural strength. While geopolymer concrete shows less spalling and cracks in fire exposure [112], the compressive strength reduces due to the expansion of paste and aggregates at higher temperatures [112]. It is also correlated with the materials, activator, activator-to-binder ratio, and curing regime [113,114]. The adverse effect of high temperature is due to the evaporation of free water in the paste, which results in internal pressure [115]. Once the internal pressure has reached a certain level, the thermal stress in the matrix cannot be sustained, creating cracks on the surface of the concrete and the microcracks in ITZ [116]. Replacement of RCA harms the thermal resistance due to the breakage of RCA at a specific temperature [117]. As illustrated in Figure 9, exposure to elevated temperature decreases CS. For instance, Topal, Karakoç, and Özcan [111] observed a decline in compressive strength by 8%, 40%, 47%, 64%, and 91% for 100, 200, 400, 600, and 800 °C for 1 hour of heating a GGBS-based concrete with 100% RCA. In contrast, Fakhrian, Behbahani, and Mashhadi [73] reported that the adhesive between RCA and GGBS-based concrete paste becomes firmer at higher temperatures. However, Şahin, Uysal, Canpolat, Aygörmez, Cosgun, and Dehghanpour [70] pointed out that the compressive strength of RCA-based MK-based GC with the additive of basalt fibre increases by heating up to around 200 or 300 °C, higher temperature causes compressive strength drop, and the concrete is disintegrated at 800 °C, which might be due to the decomposition of old OPC mortar around the RCA [59].
The level of fire damage in the GC microstructure is relevant to the exposure level. For instance, research by Nuaklong, Jongvivatsakul, Pothisiri, Sata, and Chindaprasirt [59] shows that after 30 min of heating, the residual compressive strength of RCA-based FA geopolymer was around 34% higher than its counterpart with NA, which might be because of the decline in the expansion of aggregates with OPC material around the RCA particles. They reported that the compressive strength significantly dropped for 60 min heating, as the calcium hydroxide, which exists in the mortar around the aggregates, began to decompose, destroying the bonding between paste and aggregates. Similarly, based on research by Nuaklong, Jongvivatsakul, Pothisiri, Sata, and Chindaprasirt [59], after 60 min fire exposure at about 900 °C, cracks on the surface of the fly-ash-based GC specimens can be seen due to the escape of evaporated water from the inside of the specimens.
In addition, the water absorption and sorptivity of RCA-based geopolymer concrete, exposed to higher temperatures, are higher than those of geopolymer concrete with NA. Further, RCA increases the sorptivity and water absorption cracks and deterioration of the structure at higher temperatures [111].
Some additives have a positive effect on fire resistance. For instance, adding 0.4% PVA increases the compressive strength of RCA-based GC by 26% at 200 °C. PVA has a positive impact on strength, as PVA produces a three-dimensional network that helps keep all the geopolymer components together. However, PVA negatively affects higher temperatures as it is melted, resulting in more pores [32]. Similarly, adding 1.2% basalt fibre increases the compressive and flexural strength of RCA-based GC at 200 °C from 38.99 and 2.26 MPa to 45.16 and 3.6 MPa, respectively [70].
To sum up, RCA has an adverse impact on the CS, water absorption, and sorptivity of GC after exposure to elevated temperature. Higher temperatures result in decreasing the CS and increasing the water absorption and sorptivity. Moreover, increasing the time of heating results in a further reduction in the CS. The PVA and basalt fibre additives improve the mechanical properties of RCA-based GC after exposure to higher temperatures.

4.2.3. Exposure to Freezing and Thawing

Compared with OPC, geopolymer concrete represents better and improved compressive strength after a freeze–thaw cycle. It is due to the high consumption of pozzolanic materials in GC, especially slag [118]. Pozzolanic reaction continues within the freeze–thaw cycle [119]. Besides, a compacted and dense matrix of geopolymer concrete has an essential role in this regard, so 180 cycles of freezing–thawing cycles, like a curing condition, improve the mechanical properties of MK-based GC with polyvinyl alcohol [118]. Likewise, MK/GGBS-based GC improves compressive strength during freezing–thawing [32].
As depicted in Figure 10, Nazarpour and Jamali [120] reported the proper freeze–thaw durability properties for partial RCA replacement in a GGBS-based GC. However, the CS dropped slightly by around 7–14% for 100, 200, and 300 freeze–thaw cycles. In like manner, Uğurlu, Karakoç, and Özcan [26] reported a 12% to 15% compressive strength drop for 25% to 100% RCA replacement in a GGBS-based GC after 100 cycles of freezing and thawing. Due to the weaker structure and higher water absorption of RCA, continuing the cycle of freezing and thawing of the existing water in the aggregates causes internal stress, leading to the weak structure of GC. In addition, this is the reason for the further reduction in CS by adding more RCA.
Some materials positively impact the freeze–thaw resistance of RCA-based geopolymer and even increase the compressive strength of GC after the cycles of freeze and thaw. For instance, 1.2% PVA increases the compressive and flexural strength by 44.80% and 110%, respectively, rather than the identical fibreless specimens and enhances the compressive strength after 180 cycles of freeze–thaw [32]. Likewise, basalt fibres improve the compressive strength of RCA geopolymer concrete by 16% after 180 cycles of freezing–thawing compared with their counterpart without basalt fibres [70]. The positive effect of these two types of fibres is due to the positive impact of fibre networks on mechanical properties and avoiding flattering the microcracks due to the existence of RCA [32].
To conclude, RCA adversely impacts the freeze–thaw durability, and increasing the RCA content results in a further drop in CS after freezing and thawing. However, the negative effect of partial RCA replacement is negligible. Additives of PVA and basalt fibres improve the freeze–thaw resistance of RCA-based GC.

4.2.4. Exposure to Acid and Alkali Attacks

Concrete is alkaline, and contact with acid breaks down its component. Geopolymer concrete demonstrates better acid resistance than OPC concrete, as its water absorption and calcium content are lower than those of OPC, so lower soluble particles will be generated [121]. Waqas, Butt, Danish, Alqurashi, Mosaberpanah, Masood, and Hussein [36], replacing NA with RCA, increases the mass loss in an acid attack. It is because of the cementation paste around RCA. This observation is confirmed by other studies [36,77,95,100]. However, exposing a 25% fine RCA-based FA GC to an alkali solution such as magnesium did not show any mass loss but caused a CS drop. Generally, alkali attacks have better results than acid attacks [95]. As illustrated in Figure 11, the CS loss due to the alkali attack will increase if the RCA percentages increase [89]. This phenomenon is because the reaction of the cement paste in RCA with sulphate generates harmful materials, such as gypsum and ettringite, leading to the CS drop [89].
Some factors can improve acid resistance. For example, bentonite has a positive effect and decreases the acid attack mass loss. Incorporating 15% bentonite reduces the mass loss of 90-day RCA GC specimens by 12% [36]. Besides, replacing 10% and 20% FA with MK in an MK/FA RCA-based GC demonstrates better acid attack resistance than zero MK [77]. Higher NaOH molarity also improves acid resistance. For example, for 8, 12, and 16 NaOH molarity for FA RCA-based GC, 18.9%, 12.4%, and 10.3% mass losses were observed after 120 days of exposure to sulphuric acid [100]. Increasing the ratio of alkali activator to binder also enhances acid attack resistance, while 25% fine RCA is incorporated in a FA GGBS-based GC [95].
Regarding alkali attacks, increasing the binder content leads to decreased CS loss due to the acid attack. For instance, exposing a GGBS-based GC with 25%, 50%, 75%, and 100% RCA demonstrates 14.4–21.9%, 10.9–19.7%, and 9.1–17.3% CS loss, for 300, 400, and 500 kg/m3 GGBS material, respectively, when it is exposed to 3% MgSO4 solution for 12 weeks. The reason is that increasing the binder content increases the content of geopolymer, leading to a decline in permeability, resulting in less impact of alkali. [26]. Besides, increasing AAS/b decreases the CS drop due to an alkali attack [95].
To sum up, incorporating RCA has adverse effects on the alkali and acid attack resistance of RCA-based GC. Factors such as adding bentonite, replacing 10% to 20% FA with MK, higher NaOH concentration, or increasing the AAS/b ratio can improve acid resistance. Besides, increasing the binder content and increasing AAS/b enhance alkali resistance.

4.3. Properties of Fresh RCA-Based Geopolymer Concrete

4.3.1. Setting Time

The initial setting time in an RCA-based geopolymer concrete depends on the type of binder, binder-to-aggregate (b/A) ratio, hydroxide sodium concentration, SS/SH ratio, water/binder ratio, and RCA content [63,93].
GGBS decreases the initial and final setting time [62]. It is due to the higher amount of calcium that reacts with water, and the existence of an alkali activator expedites it. However, MK reacts with alkali solution, and if FA is replaced with the same amount of MK, this increases both the initial and final setting time. It is due to the higher Ca+2 in FA than in MK [81]. Low-calcium fly ash extends the initial and final setting time to high-calcium fly ash due to the lower amount of CaO, as CaO expedites the setting by fast-producing CSH gel [74]. Using waste concrete fine (WCF) also decreases the initial setting time due to the high amount of calcium in WCF, resulting in CSH production, which generates heat, speeding up the condensation process [93]. Increasing the ratio of b/A also extends the setting time, as a higher b/A means a higher amount of liquid, which lubricates GC and improves the setting time [93]. In addition, the higher molarity of NaOH causes the setting time to extend due to the higher amount of OH. Besides, increasing the ratio of SS/SH causes condensation among silicate content and leads to an extended setting time. Moreover, the increase in the water/binder ratio increases the setting time [63].
Xie, Chen, Wang, Fang, Zhang, and Liu [81] pointed out that RCA’s application does not significantly affect the setting time, and various amounts of RCA slightly affect the setting time. The reason is that hydration occurs in the paste and ITZ. However, the setting time increased somewhat due to RCA’s extra water. In contrast, Ren and Zhang [93] observed a much shorter initial setting time for RCA-based GC than NA-based GC. They stated that the reason was the rougher surface of RCA than NA. Besides, RCA might break during mixing, absorbing more water and decreasing the initial setting time. However, in another research, increasing the amount of RCA to 100% demonstrates a 10.4% increase in the setting time of a GGBS/FA concrete [63].
In conclusion, the binder materials of GGBS and WCF decrease the setting time due to the higher amount of calcium. However, MK and low-calcium FA extend the setting time. Moreover, increasing the b/A, NaOH molarity, SS/SH ratio, and water/binder ratio raises the setting time.

4.3.2. Workability

The effect of RCA content on the slump and workability of fresh GC is diverse. Figure 12 studies state that incorporating RCA in GC leads to more voids, resulting in higher water absorption. Moreover, RCA has a rough surface, which increases the harshness, negatively affecting the workability [122]. For instance, replacing NA with 100% RCA demonstrates a drop in slump from 125 to 60 mm [17]. In like manner, Parthiban and Saravana Raja Mohan [89] observed a decrease in slump from 117 to 106 mm for 0% and 100% RCA, respectively, in a GGBS-based geopolymer. Likewise, Kathirvel and Kaliyaperumal [65] confirmed a drop in slump by adding RCA in developing a GGBS-based GC. They believe that it might be due to the existence of the pores in RCA.
In contrast, some researchers stated that RCA has no adverse effect on GC workability. For instance, Bhardwaj and Kumar [33] pointed out that additional RCA has no negative impact on workability, as RCA is used as an SSD, and it needs further water to reach the SSD. Likewise, Waqas, Butt, Danish, Alqurashi, Mosaberpanah, Masood, and Hussein [36] stated that RCA helps achieve better workability in a high-calcium FA-based GC due to the more water in GC. Similarly, Nuaklong, Jongvivatsakul, Pothisiri, Sata, and Chindaprasirt [59] pointed out that the slump for an RCA-based GC is 14% higher than its counterpart with natural aggregates. Again, replacing 100% of RCA results in a 10% increase in a slump of GGBS/FA concrete [63]. Furthermore, adding RCA causes an increase in passing ability, viscosity, and segregation. Based on investigations, this is associated with the Na2SiO3/NaOH ratio and the molarity of NaOH [123]. For instance, adding 30% of RCA to a fly-ash-based GC, Na2SiO3/NaOH = 2.5, and molarity 8, viscosity, passing ability, and segregation increased by 18%, 7%, and 4%, respectively [87].
Various factors affect NA-based and RCA-based GC. Regarding the effect of alumina silicate material, the increase in the ratio of GGBS to MK in RCA-based GC from 1:1 to 7:3 results in a lower slump, whereas this improves the compressive strength, even better than OPC. The reason is that a GGBS particle has an angular shape, and its reduction helps workability. Moreover, an MK particle is smaller than a GGBS particle. Increasing them helps to achieve better workability as well. Another reason is that a decline in calcium due to the lower amount of GGBS might help delay condensation and improve workability [81]. Likewise, in a fly ash GGBS GC, increasing the amount of FA or decreasing the amount of GGBS, while the water-to-binder ratio is constant, helps to achieve better workability due to the angular shape of GGBS and the effect of the reaction of high-calcium GGBS [62]. Regarding comparing the effect of MK and FA on the workability of RCA-based GC, increasing the number of MKs results in a slump drop due to the more fine and angular shape of MKs compared with the spherical shape of FA particles [77].
Another influential factor is alkali-activated-solution (AAS)- to-binder ratio (AAS/b). Increasing AAS/b enhances the slump due to the higher amount of AAS. For instance, increasing AAS-to-FA percentage from 0.4 to 0.5 increases the slump by 10% (from 16 to 20 cm) but decreases CS by around 9% [75]. Similarly, Le, Bui, and Tang [72] reported 16, 18, and 20 cm for AAS/FAs of 0.4, 0.45, and 0.5, respectively, while 100% coarse aggregates were replaced by RCA.
Furthermore, the water/binder ratio significantly impacts workability. It increases from 0.3 to 0.5 in a GGBS/FA geopolymer concrete with 100% RCA, resulting in 48.7% workability enhancement [63]. Moreover, increasing the ratio of Na2SiO3 to NaOH also decreases slump by enhancing alkali activator adhesiveness with a higher amount of Na2SiO3 [123]. In addition, increasing the molarity of NaOH leads to a drop in slump, while the water-to-binder ratio remains constant. It is due to the higher amount of alumina and silica due to the higher NaOH molarity, rising geopolymerisation, and stiffness of the concrete [100,123]. For instance, slumps of 750, 740, and 710 mm are reported for 8, 10, and 12 NaOH M, respectively, in RCA-based GC, and the same manner is reported for NA-based GC [123].
The addition of some material has a positive effect on workability. For example, the ultrafine slag particle’s spherical shape and fine ultra slag particle enhance workability [17]. A superplasticiser also improves workability. For instance, lignosulfonate increases the slump of an FA-based GC with 100% coarse RCA by around 2 cm, with a negligible effect on compressive strength [72].
To conclude, RCA has a diverse impact on the workability of GC, and there is evidence for increasing or decreasing the slump due to the RCA incorporation. The factors that help to achieve better workability include: (1) increasing the ratios of AAS/b and w/b; (2) decreasing the ratios of GGBS/MK, GGBS/FA, MK/FA, and SS/SH, and (3) decreasing NaOH molarity, (4) adding ultrafine slag, (5) adding superplasticisers.

4.3.3. Self-Compacting Concrete

Self-compacted geopolymer concrete is concrete with a flowability level that allows it to compact by the gravity load. This type of concrete has been developed to tackle the issue of failure resulting from inappropriate compaction [124]. Regarding the properties of fresh self-compacting concrete, flowability, viscosity, passing ability, and segregation must be evaluated by conducting the tests of the slump, T500 slump-flow or V-funnel, L-box, and segregation resistance (sieve). Based on concrete applications, slump-follow for self-compacting concrete must be between 550 and 850 mm [125].
There are a few studies to produce a self-compacting RCA-based GC. For instance, Ayub, Mahmood, and Khan [87] analysed a self-compacting FA-based geopolymer with 30% RCA and 7% superplasticiser, which was cured at 70 °C for 24 h. They compared it with a GC with 100% natural aggregate. Although the changes in the properties of fresh GC were satisfying, the compressive strength was 14.8 MPa, which is unsuitable for structural applications. In another research for developing a self-compacting RCA-based GC, Salihi and Younis [123] just studied the properties of fresh GC, did not mention curing conditions, and did not consider mechanical and durability properties. Hence, there is a scope for a study on self-compacting RCA-based GC with a CS suitable for structural applications, which will be cured in an ambient environment.

5. Scopes for Further Research

This paper identified the knowledge gap in the relevant literature based on the three main techniques for spotting gaps, including Confusion, Neglect, and Application, which were first introduced in [126] and used in construction-related studies [127]. When there is knowledge regarding the matter, but this information is confusing, and there is no agreement among researchers, this type of gap is considered ‘Confusion’. ‘Neglect’ mode, which is the most common type of gap, happens when there are no reasonable studies regarding the issue, or it is still under research. The gap category is ‘Application’ when it is required to extend, augment, or modify. Accordingly, the following gaps were identified based on this gap-spotting method throughout this review. There is a scope for further research in the following identified gaps.
  • Self-compacting RCA-based GC, which can be cured in ambient temperature with CS, ranged in structural application. (Neglect)
  • Applying RCA-based GC in a simulated coastal environment. (Neglect)
  • Using the solid alkali activator. The previous studies are conducted on a two-part geopolymer concrete using a liquid alkali activator. (Neglect)
  • The optimum temperature and time for curing. There is no agreement among researchers on this aspect. (Confusion)
  • The effect of RCA on the compressive strength of GC. There is no agreement among researchers on this aspect. Some believe that RCA increases CS, and others state that RCA decreases CS. (Confusion)
  • The effect of RCA on the setting time and flowability. There is no agreement among researchers on this aspect. (Confusion)
  • The various treatment of RCA applied in GC. There are no studies on this aspect. (Application)
  • Identify the optimum amount of GC mix components for developing RCA-based GC. The effect of considerable amounts of silica fume on an FA/silica fume GC. The impact of multiple ratios of waste concrete powder to FA and FA to ferrochrome ash should be considered in future studies. (Application)

6. Discussion and Conclusions

This research reviewed the most important factors influencing the mechanical and durability properties of the fresh and hardened RCA-based geopolymer concrete. The conclusions are drawn and categorised into three groups as below:
  • Mechanical properties of RCA-based geopolymer concrete
    • There are three sources for RCA in the literature: concrete lab specimens, CDW landfilled, and demolished buildings. Specific gravity, density, dry density, saturated density, bulk density, and apparent density of RCA are less than NA.
    • There are some techniques for RCA treatment, including coating aggregates with geopolymer slurry or cement and so on to improve the properties of RCA. However, there is no study on the implications of treated RCA in GC.
    • Increasing the aluminosilicate content, such as GGBS in a GGBS-based GC, GGBS in a GGBS FA-based GC, and the amount of UFS in a UFS FA-based GC, GGBS in GGBS an MK-based GC, MK in an MK FA-based GC results in enhancing CS. Besides, increasing the ratio of Portland cement in a Portland cement FA-based GC improves CS.
    • Glass fibre, carbon fibre, nano-SiO2, steel fibre, polyvinyl alcohol fibre, graphene oxide, basalt fibre, rice husk ash, low-calcium bentonite, hypergolic coal, iron filling, and silica fume are reported as the additives that improve RCA-based GC. Besides, using textile mill effluent instead of freshwater improves the CS of GC.
    • There are diverse ideas regarding the effect of RCA on the CS of GC. Some researchers believe that RCA harms CS, so just a few percentages of NA should be replaced by RCA, and further RCA will drop CS significantly. Thus, the optimum amount of RCA should be determined for each GC mix. On the other hand, there exists evidence that RCA increases CS, and it is possible to use 100% RCA, while the drop in CS is negligible.
    • The alkali-activator-related factors, such as NaOH molarity, SS/SH ratio, sodium silicate modulus, and alkali-solution-to-binder ratio, affect the properties of RCA-based geopolymer.
    • GC does not have an exact curing temperature and time depending on the aluminosilicates and alkali activator. GC can be cured ambient, but a higher temperature helps accelerate chemical reactions, create a good bond between alumina and silica, and increase CS. However, a higher temperature or additional curing time causes microcracks and a decline in compressive and flexural strength. The reaction of GC in higher temperatures depends on the type of materials, activator, activator-to-binder ratio, and curing regime. A higher temperature results in a decline in the CS of RCA-based GC, but in some cases, CS increases up to 200 °C heating and then will drop. Moreover, increasing the time of exposure to fire increases the damage. Besides, some additives, such as PVA and basalt fibre, positively impact the GC properties in higher temperatures.
  • The durability of RCA-based geopolymer concrete.
    • Incorporating RCA increases permeability, chloride penetration, and water absorption. However, the suitability of this type of GC for the marine environment depends on the kinds of aluminosilicate material, the ratio of alkali solution to the binder, and NaOH molarity. The percentages of RCA or patterns of RCA replacement in fine or coarse aggregates also have a noticeable impact. Some materials positively affect the marine durability of RCA-based GC, such as PVA, graphene oxide, carbon fibres, and bentonite, and replacing 5% to 15% of FA with OPC.
    • GC demonstrates better freeze–thaw resistance than OPC concrete, resulting in better strength after freezing and thawing cycles. Some materials positively impact the freezing and thawing durability of a GC, including PVA and basalt fibres.
    • RCA harms the acid attack resistance of GC. Some factors can improve it: adding bentonite, higher NaOH molarity, and increasing the ratio of the alkali activator to the binder.
  • Properties of fresh RCA-based geopolymer concrete.
    • Several factors affect the setting time of RCA-based GC, including bonding-to-aggregate ratio, NaOH concentration, SS/SH ratio, water/binder ratio, RCA content, and the type of aggregates. GGBS and fine waste concrete (as a binder) decrease the setting time. However, adding MK instead of a portion of FA results in a longer setting time. There is no agreement on the effect of RCA in the setting time. Some studies demonstrate that adding RCA results in shorter or longer setting times.
    • The effect of RCA on workability is diverse, and decreases and increases in workability of GC by adding RCA are reported. Influential factors on GC’s workability include the aluminosilicate material type, AAS/b ratio, w/b ratio, SS/SH ratio, and NaOH molarity.

Author Contributions

Conceptualization, B.N. and R.A.-A.; methodology, B.N. and R.A.-A.; validation, B.N. and R.A.-A.; formal analysis, B.N.; writing—original draft preparation, B.N.; writing—review and editing, R.A.-A.; visualization, B.N.; supervision, R.A.-A.; project administration, R.A.-A. All authors have read and agreed to the published version of the manuscript.

Funding

This research received no external funding.

Data Availability Statement

Not applicable.

Conflicts of Interest

The authors declare no conflict of interest.

Appendix A

Table A1. Summary of RCA-based GC characteristics.
Table A1. Summary of RCA-based GC characteristics.
ReferenceAluminosilicatesRCACompacting or
Self-Compacting
SuperplasticizerCuring ConditionMax 28-Day CS (MPa)Remarks
Replacement
Percentages
Coarse or FineSource of RCA
[17]FFA, ultrafine slag 25%, 50%, and 100%NMWSNMYA46Ultrafine slag is used as an additive and a substitution for FA from 0% to 30%. The best CS is for the addition of 30% UFS and 100% RCA, reaching to 46.24 MPa.
[22]FFA, Silica Fume 0%, 10%, 20%, 30%, 40%, 50%, 60%, 70%, 80%, 90%, 100%CDCNMNO55The optimum amount of RCA is considered 40% and 50%. They evaluated the leaching characteristics and found that RCA decreases the leaching of arsenic.
[23]FA, silica Fume0%, 10%, 50%CDCNMYO56 They found that As, Cr, and Se leaching in RCA-based GC is lower than in NA-based GC. CSs are 42, 54, and 56 MPa for 0%, 10%, and 50% RCA.
[25]FA100%CFLSNMYA34They analysed the effect of SH molarity on hollow steel columns grouted with RCA GC, and SH 14 M shows better results than using NA.
[26]GGBS0%, 25%, 50%, 75%, 100%CFLSNMNO65Effect of various percentages of RCA, and three binder contents of 300, 400, and 500 kg/m3 were evaluated on freeze/thaw cycling. 500 kg/m3 and 100% RCA show around 65 MPa CS.
[27]MK, OPC100%CFNMNMYNM30Replacing 30% cement with MK demonstrates better CS than just using MK.
[32]MK, GBFS 100% FNMNMNO47The best result for 0.4% polyvinyl alcohol as an additive can be seen.
[33]FA, GGBS 50% and 100%CLSCYA 42 Graphene oxide increases CS by 20.53–21.55% and 9.58–13.59% for 50% and 100% RCA content, respectively.
[34]MK, FA 30% 70%, 100%CWSNMYA41Aggregate replacement pattern was studied for both partial and total replacement of just coarse aggregates, and the best result is for 70% coarse RCA.
[35]FA, GGBS 100%CDBCYO48 The optimum curing regime is 80 °C for 12–24 h.
[36]CFA 100%CLSCYO3510% is an optimum content for bentonite as an additive, leading to an increase in CS and split tensile strength.
[37]FFA50%, 80%, 100%CLSCYO62The optimum ratio of SS/SH is 1.5. The optimum ratio of glass fibre is 3% of the weight of concrete for 50% RCA with CS of 62 MPa.
[41]GGBS, FA 100%CLSCNO38The effect of water-glass modules is studied. The impact of the mould size on the CS was also considered, with the larger size showing higher CS.
[44]CF, FFA50%, 100%FLSNMYO49The effect of carbon fibre was studied. For 100% fine RCA, 0.2% carbon fibre provides a proper CS. 50% RCA shows the best CS and abrasion resistance.
[45]FA, Ferrochrome ash10%, 20%, 30%, 40%, 50%CDC, LSCYO30The optimum percentage of RCA is 20%.
[46]FA0%, 50%, 100%CWSCNO72The CS for RCA-based GC was higher than their OPC-based counterpart. 86, 72, and 55 for 0%, 50%, and 100% RCA.
[47]FA, fine waste concrete 50%FLSNMNANMThey stated that the bond between RCA and GP paste is strengthened compared with GC with NA, OPC concrete with NA, and OPC concrete with RCA.
[58]FA, GGBS 100%NMLSNMNA32Three various types of effluent are used instead of freshwater, including sugar mill effluent mix (SF), fertilizer mill effluent mix (FF), and textile mill effluent mix (TF). The best one is TF, with a 133% improvement in CS.
[59]CFA100%CLSNMNA38The effect of rice husk (RH) and nano-SiO2 was studied. RH has a better impact on CS compared with nano-SiO2.
[60]FFA, MK 60%, 65%, 70%NMLSCNO47The optimum content of steel fibre could not be found. The optimum amount of RCA is 65%, with a CS of 47 MPa.
[61]FA40%CLSCNO, A43Curing in ambient and oven temperature were studied, so oven heating at 60 °C provides better CS.
[62]GGBS, FA100%CDCCY O 80They evaluated the effect of various GGBS/FA ratios and W/b ratios.
[63]GGBS, FA0%, 30%, 50%, 70%, and 100% CDCCYO62 The effect of various RCA percentages and the water-to-binder ratio was evaluated.
[64]MK100%CFDCCYA29The effect of iron filling was evaluated. Its optimum amount is 1%.
[65]GGBS0%, 25%, 50%, 70%, and 100%CDCCYA, H56The optimum of RCA is 50%, leading to a CS of around 56 MPa
[70]MK, GGBS 100%FNMCNO42The effect of basalt fibre was studied, and the optimum amount is 1.2%.
[71]FA, slag 30%, 50%, 70%, 100%CCBCNO 29 The effect of hypergolic and calcined coal gangues was studied, and both provide the range of structural CS. Hypergolic demonstrates better CS.
[72]FA100%CNMCYA, O35The effect of curing temperature, alkaline solution to FA ratio, and superplasticizer was assessed, and two models were evaluated for predicting compressive strength. Lignosulfonate superplasticizer is not appropriate for GC.
[73]GGBS0%,10%, 20%, 30%, 40%, 50%, 60%, 70%, 80%, 90%, 100%FNMNMYANMThey used the gene expression programming model to predict CS and mass loss in higher temperatures. 30% RCA is considered the optimum.
[74]FFA, CFA0%, 25%, 50%, 75%, and 100%FLSNMYO47FFA/CFA 1:1 and 25% RCA suggested.
[75]FA100%COld concreteCNA35Alkaline activator/FA ratios of 0.4, 0.45, and 0.5 were compared, and the optimum ratio was introduced as 0.4, which is economical and provides the highest CS.
[76]CFA and Cement 100%CLSCNO49The optimum amount of nano-SiO2 as an additive is around 1%.
[77]CFA, MK 100%CLSCNO47They evaluated the effect of the replacement of MK instead of FA for NA- and RCA-based GC.
[81]GGBS, MK0%, 50%, 100%CDCCYO47 They evaluated the effect of various GGBS/MK ratios.
[87]FFA30%CLSSCYO15A self-compacting GC was developed.
[88]FFA, GGBS 0%, 10%, 20%, 30%, 40%, and 50% LSNMYO5730% is considered the optimum percentage of RCA.
[89]GGBS0%, 25%, 50%, 75%, and 100%CLSNMYA, H57 for 50% RCAThe effect of various percentages of RCA in a GC cured in ambient temperature was studied.
[91]FA100%
0%, 25%,
50%, 75%,
100%
C
F
DBCNO36Replacement of C RCA has a negligible impact on CS, and the optimum F RCA is 25%.
[92]FFA100% CLSNMY O65They evaluated the effect of NaOH molarity, curing time, and temperature. The best result was for NaOH M = 12 and curing at 90 °C for 24 h.
[93]Waste concrete fine, FA100%FCLSNMNA32 They examined the binder to aggregate (b/A) ratio, SH molarity, SS/SH ratio, curing regime, and RCA on the CS and initial setting time. The highest CS obtained for NaOH=10 M and SS/SH: 1.1.
[95]FA, GGBS 25%FLS NMNA63They compared the effect of AAS/b on the CS and acid and alkali attack. There were around 63 and 38 MPa for AAS/b of 0.4 and 0.6, respectively.
[96]MK, bottom ash100%NMDCNMNA45Various sizes of crushed aggregates of 5, 2, and 1 mm are incorporated. The best results for CS are 40 to 45 MPa for aggregates smaller than 2 mm.
[100]CFA 100%CLSSCNO38They evaluated the effect of NaOH molarity, so the optimum NaOH molarity was reported to be 12 M.
[101]CFA100%CLSNMNA, O37 12 is the optimum SH molarity. CS is 27.8 to 36.8 MPa for heated curing and 8.6 to 12.2 MPa for ambient curing.
[103]MK10%, 20%, and 30%CNMNMYA28The effect of SS/SH was studied. Increasing the SS/SH ratio improves CS. By adding 30% RCA and SS/SH = 3, CS decreases by 28%, but it is still in the range of structural application.
[110]FFA, GGBS 0%, 10%, 20%, 30%, and 40%CNMNMYONMThe various RCA percentages were studied, and 30% is considered the optimum percentage of RCA.
[111]GGBS0%, 25%, 50%, 75%, and 100%CLSNMNO 70CS drops of 8%, 40%, 47, 64%, and 91% for 100, 200, 400, 600 and 800 °C for 1 hr heating are observed.
[120]GGBS20%, 30%, and 40%CLSNMNA44Good resistance in freeze–thaw was observed with the CS reduction between 7% and 14% for 100, 200, and 300 freeze–thaw cycles.
[123]FFA100%CDC SYNMNMThey evaluated the effects of SH molarity and SS/SH ratio on fresh and hardened GC properties.
2.5 was the optimum SS/SH.
[128]FA, GGBS 100%CLSNMYA35They used this RCA-based GC to produce a large-scale column and tested and analysed a different number of bars and the distances between them.
[129]MK100%CFLSCYA26The application of RCA-based GC in a wall was evaluated.
[130]FA0%, 50%, 100%NMNMCNONMStudy on steel tubular columns filled with RCA-based GC and OPC, resulting in a drop in CS by adding RCA while ductility improved.
[131]FA0%, 50%, 100%CWSCNONMA study on the steel tubular columns filled with RCA GC and OPC resulted in a drop in CS; adding RCA improved ductility.
[132]FA0%, 50%, 100%CNMCNO72CSs are 86, 72, and 55 MPa for 0%, 50%, and 100% RCA
[133]FFA 20%, 30%, 40%, 50%, and 60%CLSNMYO3240% RCA is an optimum RCA percentage for fresh and hardened specifications.
NM (not mentioned), coarse aggregate (C), fine aggregate (F), lab specimens (LS), CDW landfilled sites (WS), demolished construction (DC), NaOH (SH), Na2SiO3 (SS), self-compacted (SC), compacted (C), oven curing (O), ambient temperature curing (A), humidity curing (H), Class F fly ash (FFA), Class C fly ash (CFA), binder (b).

References

  1. Institute, C.R. Resource Efficiency in the Building Sector; DG Environment: Rotterdam, The Netherlands, 2014. [Google Scholar]
  2. Nikmehr, B.; Hosseini, M.R.; Wang, J.; Chileshe, N.; Rameezdeen, R. BIM-Based Tools for Managing Construction and Demolition Waste (CDW): A Scoping Review. Sustainability 2021, 13, 8427. [Google Scholar] [CrossRef]
  3. Kabirifar, K.; Mojtahedi, M.; Wang, C.; Tam, V.W.Y. Construction and demolition waste management contributing factors coupled with reduce, reuse, and recycle strategies for effective waste management: A review. J. Clean. Prod. 2020, 263, 121265. [Google Scholar] [CrossRef]
  4. Ajayi, S.O.; Oyedele, L.O.; Akinade, O.O.; Bilal, M.; Owolabi, H.A.; Alaka, H.A.; Kadiri, K.O. Reducing waste to landfill: A need for cultural change in the UK construction industry. J. Build. Eng. 2016, 5, 185–193. [Google Scholar] [CrossRef]
  5. Zoghi, M.; Kim, S. Dynamic modeling for life cycle cost analysis of BIM-based construction waste management. Sustainability 2020, 12, 2483. [Google Scholar] [CrossRef] [Green Version]
  6. Purchase, C.K.; Al Zulayq, D.M.; O’Brien, B.T.; Kowalewski, M.J.; Berenjian, A.; Tarighaleslami, A.H.; Seifan, M. Circular economy of construction and demolition waste: A literature review on lessons, challenges, and benefits. Materials 2021, 15, 76. [Google Scholar] [CrossRef] [PubMed]
  7. Geissdoerfer, M.; Savaget, P.; Bocken, N.M.P.; Hultink, E.J. The Circular Economy—A new sustainability paradigm? J. Clean. Prod. 2017, 143, 757–768. [Google Scholar] [CrossRef] [Green Version]
  8. Bilal, M.; Khan, K.I.A.; Thaheem, M.J.; Nasir, A.R. Current state and barriers to the circular economy in the building sector: Towards a mitigation framework. J. Clean. Prod. 2020, 276, 123250. [Google Scholar] [CrossRef]
  9. Jacobsen, N.B. Industrial symbiosis in Kalundborg, Denmark: A quantitative assessment of economic and environmental aspects. J. Ind. Ecol. 2006, 10, 239–255. [Google Scholar] [CrossRef]
  10. Brambilla, G.; Lavagna, M.; Vasdravellis, G.; Castiglioni, C.A. Environmental benefits arising from demountable steel-concrete composite floor systems in buildings. Resour. Conserv. Recycl. 2019, 141, 133–142. [Google Scholar] [CrossRef]
  11. Zhao, X.; Webber, R.; Kalutara, P.; Browne, W.; Pienaar, J. Construction and demolition waste management in Australia: A mini-review. Waste Manag. Res. 2022, 40, 34–46. [Google Scholar] [CrossRef] [PubMed]
  12. Wang, B.; Yan, L.; Fu, Q.; Kasal, B. A Comprehensive Review on Recycled Aggregate and Recycled Aggregate Concrete. Resour. Conserv. Recycl. 2021, 171, 105565. [Google Scholar] [CrossRef]
  13. Ahmed Shaikh, F.U.; Nath, P.; Hosan, A.; John, M.; Biswas, W.K. Sustainability assessment of recycled aggregates concrete mixes containing industrial by-products. Mater. Today Sustain. 2019, 5, 100013. [Google Scholar] [CrossRef]
  14. Tavakoli, D.; Hashempour, M.; Heidari, A. Use of waste materials in concrete: A review. Pertanika J. Sci. Technol 2018, 26, 499–522. [Google Scholar]
  15. Ghorbani, S.; Sharifi, S.; Ghorbani, S.; Tam, V.W.; de Brito, J.; Kurda, R. Effect of crushed concrete waste’s maximum size as partial replacement of natural coarse aggregate on the mechanical and durability properties of concrete. Resour. Conserv. Recycl. 2019, 149, 664–673. [Google Scholar] [CrossRef]
  16. Sabău, M.; Remolina Duran, J. Prediction of Compressive Strength of General-Use Concrete Mixes with Recycled Concrete Aggregate. Int. J. Pavement Res. Technol. 2022, 15, 73–85. [Google Scholar] [CrossRef]
  17. Lim, Y.Y.; Pham, T.M. Effective utilisation of ultrafine slag to improve mechanical and durability properties of recycled aggregates geopolymer concrete. Clean. Eng. Technol. 2021, 5, 100330. [Google Scholar]
  18. Petroche, D.M.; Ramirez, A.D. The Environmental Profile of Clinker, Cement, and Concrete: A Life Cycle Perspective Study Based on Ecuadorian Data. Buildings 2022, 12, 311. [Google Scholar] [CrossRef]
  19. Chen, C.; Habert, G.; Bouzidi, Y.; Jullien, A. Environmental impact of cement production: Detail of the different processes and cement plant variability evaluation. J. Clean. Prod. 2010, 18, 478–485. [Google Scholar] [CrossRef]
  20. Davidovits, J. 30 years of successes and failures in geopolymer applications. Market trends and potential breakthroughs. In Proceedings of the Geopolymer 2002 Conference, Melbourne, Australia, 28–29 October 2002; p. 29. [Google Scholar]
  21. Imtiaz, L.; Kashif-ur-Rehman, S.; Alaloul, W.S.; Nazir, K.; Javed, M.F.; Aslam, F.; Musarat, M.A. Life Cycle Impact Assessment of Recycled Aggregate Concrete, Geopolymer Concrete, and Recycled Aggregate-Based Geopolymer Concrete. Sustainability 2021, 13, 13515. [Google Scholar] [CrossRef]
  22. Sanusi, O.; Tempest, B.; Ogunro, V.; Gergely, J. Leaching characteristics of geopolymer cement concrete containing recycled concrete aggregates. J. Hazard. Toxic Radioact. Waste 2016, 20, 04016002. [Google Scholar] [CrossRef]
  23. Sanusi, O.; Tempest, B.; Ogunro, V. Mitigating leachability from fly ash based geopolymer concrete using recycled concrete aggregate (RCA). In Geo-Frontiers 2011: Advances in Geotechnical Engineering; American Society of Civil Engineers: Dallas, TX, USA, 2011; pp. 1315–1324. [Google Scholar]
  24. Hassan, A.; Arif, M.; Shariq, M. A review of properties and behaviour of reinforced geopolymer concrete structural elements- A clean technology option for sustainable development. J. Clean. Prod. 2020, 245, 118762. [Google Scholar] [CrossRef]
  25. Alalikhan, A.A.; Habelalmateen, M.A.; Alhabbobi, A.M. Strengthening of short hollow steel columns using grouted geopolymer concrete with recycled components. Technology 2018, 9, 832–841. [Google Scholar]
  26. Uğurlu, A.İ.; Karakoç, M.B.; Özcan, A. Effect of binder content and recycled concrete aggregate on freeze-thaw and sulfate resistance of GGBFS based geopolymer concretes. Constr. Build. Mater. 2021, 301, 124246. [Google Scholar] [CrossRef]
  27. Al-Jaberi, L.; Al-Saraj, A.-S.K.W.; Al-Serai, A.-S.J.S. Scanning Electron Microscopy of Metakaolin Based Geopolymer Concrete. J. Phys. Conf. Ser. 2021, 2114, 012061. [Google Scholar] [CrossRef]
  28. Fernández-Jiménez, A.; Palomo, A. Characterisation of fly ashes. Potential reactivity as alkaline cements. Fuel 2003, 82, 2259–2265. [Google Scholar] [CrossRef]
  29. Muhammad Nasir, A.; Khan, K.; Javed, M.F.; Aslam, F.; Muhammad Ghulam, Q.; Faraz, M.I. Prediction of Mechanical Properties of Fly-Ash/Slag-Based Geopolymer Concrete Using Ensemble and Non-Ensemble Machine-Learning Techniques. Materials 2022, 15, 3478. [Google Scholar] [CrossRef]
  30. Jindal, B.B.; Alomayri, T.; Hasan, A.; Kaze, C.R. Geopolymer concrete with metakaolin for sustainability: A comprehensive review on raw material’s properties, synthesis, performance, and potential application. Environ. Sci. Pollut. Res. 2022, 1–26. [Google Scholar] [CrossRef]
  31. Alabi, S.A.; Mahachi, J. Chloride ion penetration performance of recycled concrete with different geopolymers. Mater. Today Proc. 2021, 38, 762–766. [Google Scholar] [CrossRef]
  32. Sahin, F.; Uysal, M.; Canpolat, O.; Cosgun, T.; Dehghanpour, H. The effect of polyvinyl fibers on metakaolin-based geopolymer mortars with different aggregate filling. Constr. Build. Mater. 2021, 300, 124257. [Google Scholar] [CrossRef]
  33. Bhardwaj, B.; Kumar, P. Performance Assessment of Graphene Oxide–Reinforced Sustainable Geopolymer Concrete. J. Mater. Civ. Eng. 2021, 33, 04021322. [Google Scholar] [CrossRef]
  34. Zhang, H.; Wan, K.; Wu, B.; Hu, Z. Flexural behavior of reinforced geopolymer concrete beams with recycled coarse aggregates. Adv. Struct. Eng. 2021, 24, 3281–3298. [Google Scholar] [CrossRef]
  35. Wang, J.; Xie, J.; Wang, C.; Zhao, J.; Liu, F.; Fang, C. Study on the optimum initial curing condition for fly ash and GGBS based geopolymer recycled aggregate concrete. Constr. Build. Mater. 2020, 247, 118540. [Google Scholar] [CrossRef]
  36. Waqas, R.M.; Butt, F.; Danish, A.; Alqurashi, M.; Mosaberpanah, M.A.; Masood, B.; Hussein, E.E. Influence of Bentonite on Mechanical and Durability Properties of High-Calcium Fly Ash Geopolymer Concrete with Natural and Recycled Aggregates. Materials 2021, 14, 7790. [Google Scholar] [CrossRef]
  37. Mehta, S.; Bhandari, M. Effect of glass fiber and recycled aggregates on Geopolymer concrete. In Proceedings of the 2nd Indo-European Conference on Sustainable Materials, Environment and Construction, Mohali, India, 23–24 September 2021. [Google Scholar]
  38. Ahmad Zaidi, F.H.; Ahmad, R.; Al Bakri Abdullah, M.M.; Abd Rahim, S.Z.; Yahya, Z.; Li, L.Y.; Ediati, R. Geopolymer as underwater concreting material: A review. Constr. Build. Mater. 2021, 291, 123276. [Google Scholar] [CrossRef]
  39. Shehata, N.; Mohamed, O.A.; Sayed, E.T.; Abdelkareem, M.A.; Olabi, A.G. Geopolymer concrete as green building materials: Recent applications, sustainable development and circular economy potentials. Sci. Total Environ. 2022, 836, 155577. [Google Scholar] [CrossRef] [PubMed]
  40. Ryu, G.S.; Lee, Y.B.; Koh, K.T.; Chung, Y.S. The mechanical properties of fly ash-based geopolymer concrete with alkaline activators. Constr. Build. Mater. 2013, 47, 409–418. [Google Scholar] [CrossRef]
  41. Wang, Q.; Bian, H.; Li, M.; Dai, M.; Chen, Y.; Jiang, H.; Zhang, Q.; Dong, F.; Huang, J.; Ding, Z. Effects of a Water-Glass Module on Compressive Strength, Size Effect and Stress–Strain Behavior of Geopolymer Recycled Aggregate Concrete. Crystals 2022, 12, 218. [Google Scholar] [CrossRef]
  42. Zhu, Z.; Gu, S.e.; Tang, Z.; Song, L. Experimental Study on Recycling of Waste Concrete Based on Geopolymer Technology. In Environmental Science and Engineering, Proceedings of the International Congress on Environmental Geotechnics, Hangzhou, China, 28 October–1 November 2018; Springer: Singapore, 2018; pp. 336–343. [Google Scholar]
  43. Quattrone, M.; Cazacliu, B.; Angulo, S.C.; Hamard, E.; Cothenet, A. Measuring the water absorption of recycled aggregates, what is the best practice for concrete production? Constr. Build. Mater. 2016, 123, 690–703. [Google Scholar] [CrossRef]
  44. Nuaklong, P.; Wongsa, A.; Boonserm, K.; Ngohpok, C.; Jongvivatsakul, P.; Sata, V.; Sukontasukkul, P.; Chindaprasirt, P. Enhancement of mechanical properties of fly ash geopolymer containing fine recycled concrete aggregate with micro carbon fiber. J. Build. Eng. 2021, 41, 102403. [Google Scholar] [CrossRef]
  45. Saha, S.; Mohanty, T.; Saha, P. Mechanical Properties of Fly Ash and Ferrochrome Ash-Based Geopolymer Concrete Using Recycled Aggregate. In Recent Developments in Sustainable Infrastructure; Springer: Singapore, 2021; pp. 417–426. [Google Scholar]
  46. Shi, X.S.; Collins, F.G.; Zhao, X.L.; Wang, Q.Y. Mechanical properties and microstructure analysis of fly ash geopolymeric recycled concrete. J. Hazard. Mater. 2012, 237–238, 20–29. [Google Scholar] [CrossRef]
  47. Ren, X.; Zhang, L. Experimental study of interfacial transition zones between geopolymer binder and recycled aggregate. Constr. Build. Mater. 2018, 167, 749–756. [Google Scholar] [CrossRef]
  48. Liu, Z.; Cai, C.; Peng, H.; Fan, F. Experimental study of the geopolymeric recycled aggregate concrete. J. Mater. Civ. Eng. 2016, 28, 04016077. [Google Scholar]
  49. McNeil, K.; Kang, T.H.-K. Recycled concrete aggregates: A review. Int. J. Concr. Struct. Mater. 2013, 7, 61–69. [Google Scholar] [CrossRef] [Green Version]
  50. Upshaw, M.; Cai, C. Critical review of recycled aggregate concrete properties, improvements, and numerical models. J. Mater. Civ. Eng. 2020, 32, 03120005. [Google Scholar] [CrossRef]
  51. Ye, T.; Xiao, J.; Duan, Z.; Li, S. Geopolymers made of recycled brick and concrete powder—A critical review. Constr. Build. Mater. 2022, 330, 127232. [Google Scholar] [CrossRef]
  52. Xu, Z.; Huang, Z.; Liu, C.; Deng, X.; Hui, D.; Deng, S. Research progress on mechanical properties of geopolymer recycled aggregate concrete. Rev. Adv. Mater. Sci. 2021, 60, 158–172. [Google Scholar]
  53. Younis, K.H.; Salihi, K.A.; Ibrahim, T.K. An Overview of Geo-Polymer Concrete Including Recycled Aggregate. Int. J. Sci. Technol. Res. 2020, 9, 6239–6242. [Google Scholar]
  54. Munn, Z.; Peters, M.D.; Stern, C.; Tufanaru, C.; McArthur, A.; Aromataris, E. Systematic review or scoping review? Guidance for authors when choosing between a systematic or scoping review approach. BMC Med. Res. Methodol. 2018, 18, 143. [Google Scholar]
  55. Lima, L.; Trindade, E.; Alencar, L.; Alencar, M.; Silva, L. Sustainability in the construction industry: A systematic review of the literature. J. Clean. Prod. 2021, 289, 125730. [Google Scholar] [CrossRef]
  56. Babalola, O.; Ibem, E.O.; Ezema, I.C. Implementation of lean practices in the construction industry: A systematic review. Build. Environ. 2019, 148, 34–43. [Google Scholar] [CrossRef]
  57. Page, M.J.; McKenzie, J.E.; Bossuyt, P.M.; Boutron, I.; Hoffmann, T.C.; Mulrow, C.D.; Shamseer, L.; Tetzlaff, J.M.; Akl, E.A.; Brennan, S.E. The PRISMA 2020 statement: An updated guideline for reporting systematic reviews. Int. J. Surg. 2021, 88, 105906. [Google Scholar] [CrossRef] [PubMed]
  58. Alhazmi, H.; Shah, S.A.R.; Mahmood, A. Sustainable Development of Innovative Green Construction Materials: A Study for Economical Eco-Friendly Recycled Aggregate Based Geopolymer Concrete. Materials 2020, 13, 4881. [Google Scholar] [CrossRef] [PubMed]
  59. Nuaklong, P.; Jongvivatsakul, P.; Pothisiri, T.; Sata, V.; Chindaprasirt, P. Influence of rice husk ash on mechanical properties and fire resistance of recycled aggregate high-calcium fly ash geopolymer concrete. J. Clean. Prod. 2020, 252, 119797. [Google Scholar] [CrossRef]
  60. Xu, Z.; Huang, Z.; Liu, C.; Deng, X.; Hui, D.; Deng, Y.; Zhao, M.; Qin, L. Experimental study on mechanical properties and microstructures of steel fiber-reinforced fly ash-metakaolin geopolymer-recycled concrete. Rev. Adv. Mater. Sci. 2021, 60, 578–590. [Google Scholar] [CrossRef]
  61. Kanagaraj, B.; Kiran, T.; Anand, N.; Al Jabri, K.; Justin, S. Development and strength assessment of eco-friendly geopolymer concrete made with natural and recycled aggregates. Constr. Innov. 2022, in press.
  62. Xie, J.; Wang, J.; Rao, R.; Wang, C.; Fang, C. Effects of combined usage of GGBS and fly ash on workability and mechanical properties of alkali activated geopolymer concrete with recycled aggregate. Compos. Part B Eng. 2019, 164, 179–190. [Google Scholar] [CrossRef]
  63. Xie, J.; Wang, J.; Zhang, B.; Fang, C.; Li, L. Physicochemical properties of alkali activated GGBS and fly ash geopolymeric recycled concrete. Constr. Build. Mater. 2019, 204, 384–398. [Google Scholar] [CrossRef]
  64. Alserai, S.J.; Alsaraj, W.K.; Abass, Z.W. Effect of iron filings on the mechanical properties of different types of sustainable concrete. Open Civ. Eng. J. 2018, 12, 441–457. [Google Scholar] [CrossRef]
  65. Kathirvel, P.; Kaliyaperumal, S.R.M. Influence of recycled concrete aggregates on the flexural properties of reinforced alkali activated slag concrete. Constr. Build. Mater. 2016, 102, 51–58. [Google Scholar] [CrossRef]
  66. Pani, L.; Francesconi, L.; Rombi, J.; Mistretta, F.; Sassu, M.; Stochino, F. Effect of parent concrete on the performance of recycled aggregate concrete. Sustainability 2020, 12, 9399. [Google Scholar] [CrossRef]
  67. Le, H.-B.; Bui, Q.-B. Recycled aggregate concretes—A state-of-the-art from the microstructure to the structural performance. Constr. Build. Mater. 2020, 257, 119522. [Google Scholar] [CrossRef]
  68. Tabsh, S.W.; Abdelfatah, A.S. Influence of recycled concrete aggregates on strength properties of concrete. Constr. Build. Mater. 2009, 23, 1163–1167. [Google Scholar] [CrossRef]
  69. Ohemeng, E.A.; Ekolu, S.O.; Quainoo, H. Models for predicting strength properties of recycled concretes made with non-treated CRCAs: Empirical approach. Constr. Build. Mater. 2021, 307, 124585. [Google Scholar] [CrossRef]
  70. Şahin, F.; Uysal, M.; Canpolat, O.; Aygörmez, Y.; Cosgun, T.; Dehghanpour, H. Effect of basalt fiber on metakaolin-based geopolymer mortars containing rilem, basalt and recycled waste concrete aggregates. Constr. Build. Mater. 2021, 301, 124113. [Google Scholar] [CrossRef]
  71. Liu, C.; Deng, X.; Liu, J.; Hui, D. Mechanical properties and microstructures of hypergolic and calcined coal gangue based geopolymer recycled concrete. Constr. Build. Mater. 2019, 221, 691–708. [Google Scholar] [CrossRef]
  72. Le, H.-B.; Bui, Q.-B.; Tang, L. Geopolymer recycled aggregate concrete: From experiments to empirical models. Materials 2021, 14, 1180. [Google Scholar] [CrossRef] [PubMed]
  73. Fakhrian, S.; Behbahani, H.; Mashhadi, S. Predicting post-fire behavior of green geopolymer mortar containing recycled concrete aggregate via GEP approach. J. Soft Comput. Civ. Eng. 2020, 4, 22–45. [Google Scholar]
  74. Nuaklong, P.; Wongsa, A.; Sata, V.; Boonserm, K.; Sanjayan, J.; Chindaprasirt, P. Properties of high-calcium and low-calcium fly ash combination geopolymer mortar containing recycled aggregate. Heliyon 2019, 5, e02513. [Google Scholar] [CrossRef] [Green Version]
  75. Le, H.-B.; Bui, Q.-B. Predicting the Compressive Strength of Geopolymer Concrete: An Empirical Model for Both Recycled and Natural Aggregates. In CIGOS 2021, Emerging Technologies and Applications for Green Infrastructure; Springer: Singapore, 2022; pp. 793–802. [Google Scholar]
  76. Nuaklong, P.; Sata, V.; Wongsa, A.; Srinavin, K.; Chindaprasirt, P. Recycled aggregate high calcium fly ash geopolymer concrete with inclusion of OPC and nano-SiO2. Constr. Build. Mater. 2018, 174, 244–252. [Google Scholar] [CrossRef]
  77. Nuaklong, P.; Sata, V.; Chindaprasirt, P. Properties of metakaolin-high calcium fly ash geopolymer concrete containing recycled aggregate from crushed concrete specimens. Constr. Build. Mater. 2018, 161, 365–373. [Google Scholar] [CrossRef]
  78. Junak, J.; Sicakova, A. Effect of surface modifications of recycled concrete aggregate on concrete properties. Buildings 2017, 8, 2. [Google Scholar] [CrossRef] [Green Version]
  79. Gupta, A.; Mandal, S.; Ghosh, S. Durability of geopolymer coated recycled aggregate concrete exposed to Sulphuric acid. Int. J. Appl. Eng. Res. 2012, 7, 91–103. [Google Scholar]
  80. Junak, J.; Sicakova, A. Precycled concrete aggregates with modified surface as a filler in concrete. In Proceedings of the International Multidisciplinary Scientific GeoConference SGEM, Albena, Bulgaria, 29 June–5 July 2017; Volume 17, pp. 161–168. [Google Scholar]
  81. Xie, J.; Chen, W.; Wang, J.; Fang, C.; Zhang, B.; Liu, F. Coupling effects of recycled aggregate and GGBS/metakaolin on physicochemical properties of geopolymer concrete. Constr. Build. Mater. 2019, 226, 345–359. [Google Scholar] [CrossRef]
  82. Xu, G.; Zhong, J.; Shi, X. Influence of graphene oxide in a chemically activated fly ash. Fuel 2018, 226, 644–657. [Google Scholar] [CrossRef]
  83. Farhan, N.A.; Sheikh, M.N.; Hadi, M.N.S. Behaviour of Ambient Cured Steel Fibre Reinforced Geopolymer Concrete Columns Under Axial and Flexural Loads. Structures 2018, 15, 184–195. [Google Scholar] [CrossRef]
  84. Vijaya Prasad, B.; Anand, N.; Kiran, T.; Jayakumar, G.; Sohliya, A.; Ebenezer, S. Influence of fibers on fresh properties and compressive strength of geo-polymer concrete. Mater. Today Proc. 2022, 57, 2355–2363. [Google Scholar] [CrossRef]
  85. Ahmed, W.; Lim, C.W. Production of sustainable and structural fiber reinforced recycled aggregate concrete with improved fracture properties: A review. J. Clean. Prod. 2021, 279, 123832. [Google Scholar] [CrossRef]
  86. Balagopal, V.; Panicker, A.S.; Arathy, M.S.; Sandeep, S.; Pillai, S.K. Influence of fibers on the mechanical properties of cementitious composites—A review. Mater. Today Proc. 2022, in press. [CrossRef]
  87. Ayub, T.; Mahmood, W.; Khan, A.-u.-R. Durability performance of SCC and SCGC containing recycled concrete aggregates: A comparative study. Sustainability 2021, 13, 8621. [Google Scholar] [CrossRef]
  88. Srinivas, T.; Sukesh Reddy, G. Mechanical properties of geopolymer concrete made with partial replacement of coarse aggregate by recycled aggregate. Int. J. Eng. Adv. Technol. 2019, 9, 2301–2304. [Google Scholar] [CrossRef]
  89. Parthiban, K.; Saravana Raja Mohan, K. Influence of recycled concrete aggregates on the engineering and durability properties of alkali activated slag concrete. Constr. Build. Mater. 2017, 133, 65–72. [Google Scholar] [CrossRef]
  90. Behera, M.; Bhattacharyya, S.; Minocha, A.; Deoliya, R.; Maiti, S. Recycled aggregate from C&D waste & its use in concrete–A breakthrough towards sustainability in construction sector: A review. Constr. Build. Mater. 2014, 68, 501–516. [Google Scholar]
  91. Tran, N.T. Experimental Study of Geopolymer Concrete Using Re-cycled Aggregates Under Various Curing Conditions. In Proceedings of the International Conference on Green Technology and Sustainable Development, Da Nang City, Vietnam, 27–28 November 2020; pp. 469–478. [Google Scholar]
  92. Krishnan, T.; Purushothaman, R. Optimization and influence of parameter affecting the compressive strength of geopolymer concrete containing recycled concrete aggregate: Using full factorial design approach. In Proceedings of the International Conference on Civil Engineering and Infrastructural Issues in Emerging Economies (ICCIEE 2017), Thanjavur, India, 17–18 March 2017. [Google Scholar]
  93. Ren, X.; Zhang, L. Experimental study of geopolymer concrete produced from waste concrete. J. Mater. Civ. Eng. 2019, 31, 04019114. [Google Scholar] [CrossRef]
  94. Ledesma, E.; Jiménez, J.; Fernández, J.; Galvín, A.; Agrela, F.; Barbudo, A. Properties of masonry mortars manufactured with fine recycled concrete aggregates. Constr. Build. Mater. 2014, 71, 289–298. [Google Scholar] [CrossRef]
  95. Saha, S.; Rajasekaran, C.; Gupta, P. Performance of eco-friendly mortar mixes against aggressive environments. Adv. Concr. Constr. 2020, 10, 237–245. [Google Scholar]
  96. Somrang, P.; Wannagon, A.; Choeycharoen, P.; Sornlar, W. Strengthening geopolymer with selective sizes of concrete block waste. Chiang Mai J. Sci. 2021, 48, 1657–1678. [Google Scholar]
  97. Akhtar, A.; Sarmah, A.K. Construction and demolition waste generation and properties of recycled aggregate concrete: A global perspective. J. Clean. Prod. 2018, 186, 262–281. [Google Scholar] [CrossRef]
  98. Davidovits, J. Geopolymers. J. Therm. Anal. 1991, 37, 1633–1656. [Google Scholar] [CrossRef]
  99. Rahman, S.K.; Al-Ameri, R. The Need for a User Friendly Geopolymer Concrete-Ongoing research. In Proceedings of the Concrete 2021, Sydney, Australia, 5–8 September 2021. [Google Scholar]
  100. Nuaklong, P.; Sata, V.; Chindaprasirt, P. Influence of recycled aggregate on fly ash geopolymer concrete properties. J. Clean. Prod. 2016, 112, 2300–2307. [Google Scholar] [CrossRef]
  101. Tho-In, T.; Sata, V.; Cao, T.; Chindaprasirt, P. Use of recycled concrete aggregate in high-calcium fly ash geopolymer concrete. In Key Engineering Materials; Trans Tech Publications: Baech, Switzerland, 2017; pp. 163–168. [Google Scholar]
  102. Alhawat, M.; Ashour, A.; Yildirim, G.; Aldemir, A.; Sahmaran, M. Properties of geopolymers sourced from construction and demolition waste: A review. J. Build. Eng. 2022, 50, 104104. [Google Scholar] [CrossRef]
  103. Koushkbaghi, M.; Alipour, P.; Tahmouresi, B.; Mohseni, E.; Saradar, A.; Sarker, P.K. Influence of different monomer ratios and recycled concrete aggregate on mechanical properties and durability of geopolymer concretes. Constr. Build. Mater. 2019, 205, 519–528. [Google Scholar] [CrossRef]
  104. Rodríguez, E.D.; Bernal, S.A.; Provis, J.L.; Paya, J.; Monzo, J.M.; Borrachero, M.V. Effect of nanosilica-based activators on the performance of an alkali-activated fly ash binder. Cem. Concr. Compos. 2013, 35, 1–11. [Google Scholar] [CrossRef]
  105. Ahmed, M.F.; Nuruddin, M.F.; Shafiq, N. Compressive strength and workability characteristics of low-calcium fly ash-based self-compacting geopolymer concrete. Int. J. Civ. Environ. Eng. 2011, 5, 64–70. [Google Scholar]
  106. Nath, P.; Sarker, P.K. Use of OPC to improve setting and early strength properties of low calcium fly ash geopolymer concrete cured at room temperature. Cem. Concr. Compos. 2015, 55, 205–214. [Google Scholar] [CrossRef]
  107. Noushini, A.; Castel, A. The effect of heat-curing on transport properties of low-calcium fly ash-based geopolymer concrete. Constr. Build. Mater. 2016, 112, 464–477. [Google Scholar] [CrossRef]
  108. Farooq, F.; Jin, X.; Javed, M.F.; Akbar, A.; Shah, M.I.; Aslam, F.; Alyousef, R. Geopolymer concrete as sustainable material: A state of the art review. Constr. Build. Mater. 2021, 306, 124762. [Google Scholar] [CrossRef]
  109. Olivia, M.; Nikraz, H.R. Strength and water penetrability of fly ash geopolymer concrete. Parameters 2006, 1, 3. [Google Scholar]
  110. Srinivas, T.; Manoj Anand, P. Permeation properties of geopolymer concrete made with partial replacement of recycled coarse aggregates. Int. J. Innov. Technol. Explor. Eng. 2019, 8, 2987–2990. [Google Scholar] [CrossRef]
  111. Topal, Ö.; Karakoç, M.B.; Özcan, A. Effects of elevated temperatures on the properties of ground granulated blast furnace slag (GGBFS) based geopolymer concretes containing recycled concrete aggregate. Eur. J. Environ. Civ. Eng. 2021, 26, 4847–4862. [Google Scholar] [CrossRef]
  112. Sarker, P.K.; Kelly, S.; Yao, Z. Effect of fire exposure on cracking, spalling and residual strength of fly ash geopolymer concrete. Mater. Des. 2014, 63, 584–592. [Google Scholar] [CrossRef] [Green Version]
  113. Pan, Z.; Sanjayan, J.G.; Collins, F. Effect of transient creep on compressive strength of geopolymer concrete for elevated temperature exposure. Cem. Concr. Res. 2014, 56, 182–189. [Google Scholar] [CrossRef]
  114. Bakharev, T. Thermal behaviour of geopolymers prepared using class F fly ash and elevated temperature curing. Cem. Concr. Res. 2006, 36, 1134–1147. [Google Scholar] [CrossRef]
  115. Aygörmez, Y.; Canpolat, O.; Al-mashhadani, M.M. A survey on one year strength performance of reinforced geopolymer composites. Constr. Build. Mater. 2020, 264, 120267. [Google Scholar] [CrossRef]
  116. Jiang, X.; Xiao, R.; Zhang, M.; Hu, W.; Bai, Y.; Huang, B. A laboratory investigation of steel to fly ash-based geopolymer paste bonding behavior after exposure to elevated temperatures. Constr. Build. Mater. 2020, 254, 119267. [Google Scholar] [CrossRef]
  117. Celik, A.; Yilmaz, K.; Canpolat, O.; Al-Mashhadani, M.M.; Aygörmez, Y.; Uysal, M. High-temperature behavior and mechanical characteristics of boron waste additive metakaolin based geopolymer composites reinforced with synthetic fibers. Constr. Build. Mater. 2018, 187, 1190–1203. [Google Scholar] [CrossRef]
  118. Zhao, R.; Yuan, Y.; Cheng, Z.; Wen, T.; Li, J.; Li, F.; Ma, Z.J. Freeze-thaw resistance of Class F fly ash-based geopolymer concrete. Constr. Build. Mater. 2019, 222, 474–483. [Google Scholar] [CrossRef]
  119. Yunsheng, Z.; Wei, S.; Zongjin, L.; Xiangming, Z.; Chungkong, C. Impact properties of geopolymer based extrudates incorporated with fly ash and PVA short fiber. Constr. Build. Mater. 2008, 22, 370–383. [Google Scholar] [CrossRef]
  120. Nazarpour, H.; Jamali, M. Mechanical and freezing cycles properties of geopolymer concrete with recycled aggregate. Struct. Concr. 2020, 21, 1004–1012. [Google Scholar] [CrossRef]
  121. Aiken, T.A.; Gu, L.; Kwasny, J.; Huseien, G.F.; McPolin, D.; Sha, W. Acid resistance of alkali-activated binders: A review of performance, mechanisms of deterioration and testing procedures. Constr. Build. Mater. 2022, 342, 128057. [Google Scholar] [CrossRef]
  122. Shaikh, F.U.A. Mechanical and durability properties of fly ash geopolymer concrete containing recycled coarse aggregates. Int. J. Sustain. Built Environ. 2016, 5, 277–287. [Google Scholar] [CrossRef] [Green Version]
  123. Salihi, K.; Younis, K.H. Rheological Behavior of Self-Compacting Geopolymer Concrete Containing Recycled Aggregates: Effect of Na2SiO3/NaOH and Molarity of NAOH. In Key Engineering Materials; Trans Tech Publications: Baech, Switzerland, 2021; pp. 79–84. [Google Scholar]
  124. Thakur, M.; Bawa, S. Self-Compacting geopolymer Concrete: A review. Mater. Today Proc. 2022, 59, 1683–1693. [Google Scholar] [CrossRef]
  125. BIBM; CEMBUREAU; ERMCO; EFMCO; EFCA; EFNARC. The European Guidelines for Self-Compacting Concrete; European Federation of Concrete Admixtures Associations (EFCA): Brussels, Belgium, 2005; pp. 1–63. [Google Scholar]
  126. Sandberg, J.; Alvesson, M. Ways of constructing research questions: Gap-spotting or problematization? Organization 2011, 18, 23–44. [Google Scholar] [CrossRef]
  127. Hosseini, M.R.; Chileshe, N. Global virtual engineering teams (GVETs): A fertile ground for research in Australian construction projects context. Int. J. Proj. Manag. 2013, 31, 1101–1117. [Google Scholar] [CrossRef]
  128. Raza, A.; Manalo, A.C.; Rafique, U.; AlAjarmeh, O.S.; Khan, Q.U.Z. Concentrically loaded recycled aggregate geopolymer concrete columns reinforced with GFRP bars and spirals. Compos. Struct. 2021, 268, 113968. [Google Scholar] [CrossRef]
  129. Alsaraj, W.K.; Fadhi, S.H.; Alserai, S.J. Structural Behavior of Geopolymer Concrete Thin Wall Panels Based on Metakaolin and Recycled Concrete Aggregate. Open Civ. Eng. J. 2019, 13, 109–117. [Google Scholar] [CrossRef]
  130. Shi, X.-S.; Wang, Q.-Y.; Zhao, X.-L.; Collins, F.G. Structural behaviour of geopolymeric recycled concrete filled steel tubular columns under axial loading. Constr. Build. Mater. 2015, 81, 187–197. [Google Scholar] [CrossRef]
  131. Shi, X.S.; Wang, Q.-Y.; Zhao, X.L.; Collins, F. Experimental study on strength and ductility of steel tubular stub columns filled with geopolymeric recycled concrete. In Proceedings of the ISTS 2012: Proceedings of the 14th International Symposium on Tubular Structures, London, UK, 12–14 September 2012; pp. 757–764. [Google Scholar]
  132. Shi, X.S.; Wang, Q.Y.; Zhao, X.L.; Collins, F. Discussion on properties and microstructure of geopolymer concrete containing fly ash and recycled aggregate. In Advanced Materials Research; Trans Tech Publications: Baech, Switzerland, 2012; pp. 1577–1583. [Google Scholar]
  133. Bhoopesh, J. Strength and behaviour of recycled aggregate geopolymer concrete beams. Adv. Concr. Constr. 2017, 5, 145. [Google Scholar]
Figure 1. Reaction mechanism of the geopolymerisation of the RCA-based GC.
Figure 1. Reaction mechanism of the geopolymerisation of the RCA-based GC.
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Figure 2. PRISMA flowchart of the data screening process (adapted from Page, et al. [57]).
Figure 2. PRISMA flowchart of the data screening process (adapted from Page, et al. [57]).
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Figure 3. Effect of coated RCA on the water absorption of concrete (adapted from Junak and Sicakova [78]).
Figure 3. Effect of coated RCA on the water absorption of concrete (adapted from Junak and Sicakova [78]).
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Figure 4. Maximum CS for RCA-based GC using various additives [17,32,33,36,37,44,58,59,60,64,70,71,76].
Figure 4. Maximum CS for RCA-based GC using various additives [17,32,33,36,37,44,58,59,60,64,70,71,76].
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Figure 5. Relationship between fibre content and CS [32,37,44,60,70].
Figure 5. Relationship between fibre content and CS [32,37,44,60,70].
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Figure 6. Relationship between NaOH molarity and CS [25,92,93,100,101].
Figure 6. Relationship between NaOH molarity and CS [25,92,93,100,101].
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Figure 7. Effect of curing regime on CS [35,61,75,91,101].
Figure 7. Effect of curing regime on CS [35,61,75,91,101].
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Figure 8. Effect of RCA content on water absorption [33,36,74].
Figure 8. Effect of RCA content on water absorption [33,36,74].
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Figure 9. Relationship between heating temperature and CS [70,111].
Figure 9. Relationship between heating temperature and CS [70,111].
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Figure 10. Relationship between the freezing and thawing cycles and CS [26,120].
Figure 10. Relationship between the freezing and thawing cycles and CS [26,120].
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Figure 11. Relationship between RCA content and CS drops due to magnesium sulphate exposure (adapted from Parthiban and Saravana Raja Mohan [89]).
Figure 11. Relationship between RCA content and CS drops due to magnesium sulphate exposure (adapted from Parthiban and Saravana Raja Mohan [89]).
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Figure 12. Adverse effect of RCA on workability [17,65,89].
Figure 12. Adverse effect of RCA on workability [17,65,89].
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Table 1. Physical specification of NA and RCA.
Table 1. Physical specification of NA and RCA.
ReferenceSpecific Gravity (g/cm3)Fineness ModulusWater Absorption (%)Dry Density (g/cm3)Saturated Density (g/cm3)Dry-Rodded Unit Weight (g/cm3)Density (g/cm3)Bulk Density (g/cm3)Apparent Density (g/cm3)Los Angeles (%loss)
NARCANARCANARCANARCANARCANARCANARCANARCANARCANARCA
[33]2.742.476.626.620.685.30
[34] 0.76.6 2.8352.647
[44]2.632.383.013.061.075.5 1.7641.256
[45]2.772.48 0.664.47 1.7811.409
[59]2.652.26 0.615.90 1.5111.241 33.937.1
[61]2.812.62 0.65.56 1.751.62
[70]2.862.46
[71] 0.772.8 2.7042.517
[72]2.662.6 1.15.82.592.262.612.39
[73]2.662.342.942.612.5 1.681.376
[74]2.632.383.013.061.075.50 1.7641.256
Table 2. Chemical composition of RCA and NA.
Table 2. Chemical composition of RCA and NA.
ReferenceChemical Composition (%)SO3SiO2Fe2O3TiO2Al2O3CaOK2OMgONa2OL.O.I.
[32]RCA-60.565.820.750.5212.011.301.832.6914.52
NA (Basalt Sand)-56.98.10.917.67.01.92.13.81.15
[70]RCA-60.565.821.305.8212.012.31.832.6914.52
NA (Basalt Sand)-57.98.10.917.67.01.92.33.90.4
[75]RCA1.051.111.3-26.14.7-1.71.350.7
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Nikmehr, B.; Al-Ameri, R. A State-of-the-Art Review on the Incorporation of Recycled Concrete Aggregates in Geopolymer Concrete. Recycling 2022, 7, 51. https://doi.org/10.3390/recycling7040051

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Nikmehr B, Al-Ameri R. A State-of-the-Art Review on the Incorporation of Recycled Concrete Aggregates in Geopolymer Concrete. Recycling. 2022; 7(4):51. https://doi.org/10.3390/recycling7040051

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Nikmehr, Bahareh, and Riyadh Al-Ameri. 2022. "A State-of-the-Art Review on the Incorporation of Recycled Concrete Aggregates in Geopolymer Concrete" Recycling 7, no. 4: 51. https://doi.org/10.3390/recycling7040051

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