Effects of Activator Properties and Curing Conditions on Alkali-Activation of Low-Alumina Mine Tailings

The mining industry generates a notable amount of mine tailings (MTs). Disposal of MTs creates environmental impacts such as air pollution and the release of heavy metals into surface and underground water. The European Union (EU)-funded project “Integrated mineral technologies for more sustainable raw material supply” (ITERAMS) includes an effort to produce eco-friendly backfill materials to enhance operation and mine safety and covers for surface deposits of tailings based on geopolymerization technology. This paper investigates the effects of activator concentration, curing temperature and time on alkali-activated materials based on low-alumina MTs from the Cu/Ni mine in Northern Finland. Alkaline activators containing sodium silicate solution (Na2SiO3) at different concentrations were used and two different curing temperatures, 40 °C and 60 °C, for periods of 7, 14, and 28 days were considered. Scanning electron microscopy/energy-dispersive X-ray spectroscopy (SEM/EDS) and X-ray diffraction (XRD) were performed to investigate the structure, morphology and phase compositions of the alkali-activated products. The effect of curing temperature and alkaline solutions on mechanical strength and water absorption were investigated. The results indicate that the alkalinity and curing temperature affect the mechanical and microstructural properties of the compositions of alkali-activated MTs. The 30 wt% Na2SiO3 addition enables the alkali activated MT to improve the compressive strength with a highest value of 6.44 and 15.70 MPa after 28 days of curing at 40 °C and 60 °C, respectively. The results of this study deliver useful information for recycling and utilization of MTs as sustainable material through the alkali activation.


Introduction
The mining industry creates a huge amount of mine tailings (MTs) each year [1,2]. MTs are crushed rock deposits left over after the metal-bearing minerals have been extracted from the ore [3]. MTs are made into a slurry or paste and then transported to on-site impoundments behind rock dams or stacked in tailings storage areas. The huge amount of MTs produced by mining operations and caused environmental and safety problems, including serious water pollution. The pollution raised up from contamination of surface water, groundwater, and soils by the leaching of heavy metals, and sulphur compounds [4].
Developing cost-effective and environmentally acceptable strategies for the disposal of such waste has thus become critical for the productivity of mining operations. There are different approaches to reduce the potential environmental hazards related to MTs: (i) isolation of MTs, which includes isolation of MTs from the nearby environment by capping the tailing impoundment surface (ii) chemical stabilization of MTs by chemical or cementitious material additions in order to immobilize the heavy metals through physical-chemical reactions, and (iii) a combination of these two methods. For the simultaneous use of isolation and stabilization techniques, the tailing surface can be treated with additives such as water glass (Na 2 SiO 3 ), organic polymers, and Ordinary Portland Cement (OPC). The effect of additives cause an improvement at the surface erosion resistance and reduce water penetration, which led to isolates the underlying tailings from the surrounding environment [5][6][7]. Although OPC recommends benefits in the stabilization of MTs, there are still some problems such as high energy consumption and CO 2 emissions which are related to the OPC addition.
Geopolymerization or alkali-activation of tailings has been suggested in place of a promising method for immobilizing the tailings as a raw material for construction. Through alkali-activation, different raw materials can be transformed into valuable cementitious-like materials with low environmental impact. Geopolymers not only deliver comparable performance to OPC in many applications, but also have additional advantages, such as excellent devotion to aggregates, rapid development of mechanical strength, high acid resistance, immobilization of toxic and hazardous materials, and a considerable reduction in greenhouse gas emissions [3,8,9].
Generally, geopolymers are formed from the reaction of aluminosilicate minerals and silicate or alkaline hydroxide solution [3,10]. Until now, the research on geopolymers has been concentrated on the utilization of kaolinite, fly ash, and blast furnace slag as the aluminosilicate source material. Different parameters, such as activator type and concentration [11,12], curing process, and the composition of aluminosilicate sources, [13] considerably influence the geopolymerization processes and the final specifications of geopolymers. Sodium silicate solutions are identified to have a notable impact on the dissolution performance and precipitation characteristics of geopolymers, by enhancing alkali-metal attack on aluminosilicate particles and consequently accelerating geopolymer formation [14,15]. It is also known that using a silicate activating solution instead of a hydroxide have possibility of controlling the geopolymerization process, strength development in geopolymeric binders, and the microstructure of the activated products [16][17][18]. Beyond the ideal alkaline solution and concentration, the geopolymer curing condition have a significant effect on microstructural and mechanical strength development in cementitious systems alkali activated process [6]. Curing at higher temperatures leads to produce a fast geopolymerization process to achieve an acceptable strength within very short periods.
Recently, one-part alkali activation process received a great attention. One-part alkali activation involves a dry mix, contains different precursors and solid alkali sources, and then water addition, which is similar to preparation of the commercial cementitious materials [19][20][21][22][23]. Regardless of all proposed environmental and economic benefits of alkali-activated binders, there are some difficulties for these binders such as large drying shrinkage and efflorescence. In order to minimize the problems, different methods have been proposed. The methods include using thermal curing, different additives, and fibers [24][25][26][27][28][29][30][31][32][33].
Currently, an increasing interest in recycling of mine tailings as raw materials for producing geopolymers have 1 3 been developed. However research on geopolymerization or alkali-activation of MTs is still in its initial stages. Until now, Zhang et al., Ahmari et al., and Li et al. [1,3,4,7,[34][35][36][37] have studied the effect of different factors (i.e., activators and curing temperature) on alkali-activated binders based on copper MTs and confirmed the MT wastes can be used as an alternative raw material for the preparation of geopolymer. Torgal et al. [38] first emphasised the possible use of a combination of calcined tungsten mining waste (TMW) mud and calcium hydroxide for the improvement of a high early strength geopolymeric binder, and Kiventerä et al. [39] have investigated the effect of using sulphide mine tailings as suitable raw materials for alkali activation purposes. They concluded the sulfidic mine tailings could be activated with the addition of low amount (5 wt%) of blast furnace slag as a co-binder. They also studied the immobilization of heavy metals in alkali-activated materials [40,41]. However, none of the previous studies have investigated the reusing of low alumina mine tailings for alkali activation process and geopolymerization. Furthermore, using of MT as precursor for the alkali activation process to make a backfill materials and cover layer surface has not been considered.
The main purpose of this study is to investigate the effects of using different alkali activator concentration, curing temperature and time on the morphology, elemental composition and mechanical properties of the selected low alumina-MTs. This paper studies the feasibility of alkali-activated mine tailings (AAMTs) with different percentages of Na 2 SiO 3 solution. Different factors, such as curing temperature and curing time, are examined on the AAMTs with different Na 2 SiO 3 concentrations. Compression tests are conducted to investigate the mechanical properties of AAMTs produced at different conditions. Scanning electron microscopy (SEM) imaging and X-ray diffraction (XRD) analyses are also performed to investigate the microstructure and material phases of AAMTs. Furthermore, a detailed microstructural characterization of the final products was conducted to help understand the origin of the properties of the resulting products. It should be noted that this research is an initial experiment which carried out at different curing temperatures to improve the reaction speed. Further experiments will be done at room temperature and expected to achieve the same results specifically similar strength but with slower reaction and in the longer curing time.

Materials
MTs were supplied by Cu/Ni mine in Northern Finland in the Lapland province. Sodium silicate solution (from VWR chemicals) with a modulus of 3.2 (Ms = SiO 2 /Na 2 O) and water content of 55% was selected as an alkali activator. The chemical composition of the MTs was determined by X-Ray fluorescence (Axios mAX; Malvern PANalytical) equipped with a rhodium tube with a maximum power rating of 4 kW. In relation to the chemical compositions, the MT was rich in Magnesium (MgO: 21.82 wt%) and the amounts of silica (SiO 2 : 47.96 wt%), iron (Fe 2 O 3 : 12.06 wt%), and calcium (CaO: 11.28 wt%) were significant. Additionally, the tailings have a considerably low amount of alumina (Al 2 O 3 : 3.99 wt%). Figure 1 shows the mineral compositions of ovendried MT tested by X-ray diffraction (XRD) using Rigaku SmartLab 9 kW with Cu Kα (Kα1 = 1.78892 Å; Kα2 = 1.79278 Å; Kα1/Kα2 = 0.5) radiation operated at 45 kV and 40 mA, with a step of 0.02° and a scan rate of 3°/min from 5° and 90° (2θ). Phase identification was performed by using X'pert HighScore Plus Particle size analysis of the powdered material (MT) was performed with LS 13 320 laser diffraction particle size analyzer from Beckman Coulter using the Fraunhofer model [42]. In order to increase the reactivity of the mine tailings and thus increasing the ultimate strength of the alkaliactivated materials, different approaches were successfully tested. The thermal treatment of the MT showed that the reactivity of the material can be increased by calcination at temperatures above 700 °C which is most likely linked to the dehydration of chlorite. Since calcination is an energy intense process and requires large investment, this procedure was not further investigated in this study.
For the further synthesis, the MT was sieved and milled to achieve a grain size of less than 5 µm. The milling of the material was produced by using a vibratory disc mill (RS 200) for 30-60 s to accomplish the preferred particle size. The MT had a d 50 value and density of 422.12 µm and 3.05 g/cm 3 , respectively. Although the milling process could be cost effective in the mine site but according to some mineralogical analysis of the MT, a higher specific surface area should increase the dissolution rate and consequently a faster hardening for the alkali activated final products. Figure 2 displays the particle size distribution curve of the MTs before and after grinding.

Specimen Synthesis and Curing
The alkali-activated mine tailings (AAMTs) were prepared by adding the activator solutions to the solid materials. The molarity of the alkaline activator solution was 6 and additional water was added to the mixture to achieve the desired slurry concentration. The MTs were mixed with 10, 15, 20, 25, and 30 wt% of the Na 2 SiO 3 solution, and then water was added to the mixture to adjust the liquid-to-solid mass ratio to 0.23. The slurry was stirred for another 5 min, transferred to prismatic beam molds (20 × 20 × 80 mm), and vibrated for 60 s on a vibrating table. The fresh pastes were then sealed in plastic and subjected to cure for 24 h at 40 °C and 60 °C. The specimens were then de-molded, unsealed, and subjected curing at 40 °C and 60 °C for 7, 14, and 28 days. The recipes for the mixtures are provided in Table 1. The samples are designated as MT, MT-NA x[%, where x% refers to the weight% Na 2 SiO 3 content of the AAMT.
Regarding the use of the five different percentages of the activator additives (10,15,20,25, and 30 wt% of the total solid mass), a total of 30 prismatic beams were prepared and then tested to measure the compressive strength. Three or four specimens were tested for each mixture at different curing conditions to give average values.
The following properties were determined after curing: phase analysis, morphology and micro-structure, water absorption, and mechanical strength.

Three-Point Bending Test (TPB)
In total, 30 prismatic beams with dimensions of 20 × 20 × 80 mm were used to measure the flexural behaviour of the beams made with MTs and alkali activated materials under a three-point bending (TPB) test in agreement with the ASTM C293 recommendation [43].
The flexural load was recorded by using a wick, Z100 Roell testing machine with a load cell of 100 kN capacity. For each mix composition which prepared at different curing conditions three prismatic beams were tested with a constant flexural load speed of 0.6 mm/min. The flexural load was submitted to the beams under a displacement control. The flexural strength of specimens calculated by using the Eq. (1) under the TPB test: where F is the total flexural load, L is span length, b and h are width (20 mm) and height (20 mm) of beams, respectively.

Compressive Test
The compressive strength of the specimens was measured conferring the ASTM C116-90 by using the portions of prismatic beams broken in flexural tests [44]. The compressive load was measured using a testing machine (Z100; Zwick-Roell) with a maximum load capacity of 100 kN. All the broken prismatic beams were measured under a compressive load with a constant displacement rate of 2 mm/min. The compressive strengths of the mixtures were obtained

Microstructural Analysis
To examine the phase morphology and microstructure evolution, selected crushed and dried specimens were observed by field emission scanning electron microscopy (FE-SEM) (Ultra Plus; Zeiss) fitted with an electron dispersive x-ray spectroscopy (EDS). An accelerating voltage of 15 keV was used to analyze the structural and chemical texture of the samples. The samples were carbon-coated with a 7-9 nm carbon layer.

Water Absorption
The effect of water absorption on AAMTs was investigated in agreement with BS EN ISO 62:1999 [45]. Overall, 15 prismatic beams (20 × 20 × 80 mm) were prepared and cured for 28 days using the procedure mentioned at Sect. 2.2 The prismatic bar specimens were immersed in a water bath at 23 °C for 24 h. Then, the specimens were removed from the water and the surface water was removed by wiping with a clean dry cloth. The wiped specimens were then weighed again in one minute after removing from water. All specimens were heated by using an oven at 105 ± 2 °C for 24 h, the masses of the cooled specimens checked to reach a constant mass. The water absorption capability was defined by using the following Eq. (2): where W a is water absorption, W f is the weight of specimen after immersion (g), and W i is the mass of the dried specimens (oven-dry weight) (g).

XRF Analysis
The chemical compositions of the treated MTs before and after activation with Na 2 SiO 3 are presented in Table 2.
Concerning the chemical compositions, the alkali activation process happened, so then the composition of the AAMTs changed. The increase in Na and Si with increasing sodium silicate content is reasonable but the change in the Fe and Mg contents is related to the uncertainty of the analysis.

XRD Analysis
A selection of representative powder XRD patterns of the MT activated by different sodium silicate contents at the age of 28 days and curing of 40 °C are shown in Fig. 3 [38,39,41]. In AAMTs (Fig. 3), the C-S-H peak is shown at near 28° 2θ, resembling the diffraction pattern of a poorly ordered calcium silicate hydrate (C-S-H). The reason of not having a sharp peak of C-S-H is probably due to the lack of enough silicon inside or because of the lower quantity detection limit of the XRD instrument. Calcite peaks do not show any differences in intensity at the mix compositions with different sodium silicate contents, this is suggesting an attendance the residue of untreated MTs.
The XRD patterns for the AAMT cured at 60 °C for 28 days keep the same crystalline peaks as the peaks released in the 40 °C cured samples. It should be noted that there is no difference realized even in the XRD pattern of the samples cured at room temperature which indicates that the major constituent of the alkali activation process happened at ambient temperature and the XRD patterns of the AAMTs

Flexural Strength of AAMT
The influences of different contents of Na 2 SiO 3 , curing time and temperature on the flexural strength are illustrated in Fig. 4. Increasing the addition of Na 2 SiO 3 increased the flexural strength, and the maximum flexural strength was recorded in the mixture of MT-30% Na 2 SiO 3 at 60 °C for 28 days (around 13 MPa). At the early curing time (7 days), the maximum flexural strength is attributed to the mix composition have been cured at 60 °C (around 10 MPa), and the minimum was related to the mixture incorporating 10% Na 2 SiO 3 and have been cured at 40 °C.
According to the results presented in Fig. 4, regardless of sodium silicate content, specimens cured at 60 °C and 40 °C showed the maximum and minimum flexural strength, respectively. This outcome could be explained by the effect of curing conditions on polycondensation process.
Moreover, using higher amount of sodium silicate led to slightly higher flexural strength which could be described by the formation of more reaction products. Through increasing in the curing time from 7 to 28 days a strength improvement was distinguished in the mixtures, which was governed by the curing approach. Ghafoori et al. and Abdollahnejad et al. [20,46] showed a comparative study to evaluate the effects of using different curing conditions in geopolymers and onepart alkali-activated waste binders.

Compressive Strength of AAMT
The compressive strength of AAMT specimens cured at 40 °C and 60 °C for 7, 14, and 28 curing days containing different Na 2 SiO 3 addition of 10, 15, 20, 25, and 30 wt% are shown in This result indicates that the compressive strength increases with increasing of the activator addition (Na 2 SiO 3 here) and curing temperature. Similarly, the maximum 14 and 28 day compressive strengths were also noticed at the 30 wt% addition of Na 2 SiO 3 for both 40 °C and 60 °C curing conditions. At 40 °C and 60 °C curing temperatures, the 14 day compressive strengths are 14.78   The strength difference between curing at 60 °C and curing at 40 °C is higher for the shorter curing time (7 days) than for 14 and 28 days. This indicates a faster reaction rate at a higher temperature in a shorter curing time. The final strength of the product at 60 °C is obtained somewhere between 14 and 28 days, while it took a little longer for the sample cured at a lower temperature (40 °C) to reach the same strength level. This could be related to the hydration process for that special AAMT that needs longer time in lower temperatures to be completed. Furthermore, the strength and compressibility of the MT treated with Na 2 SiO 3 solution is related to the structure as confirmed with microstructure analysis (Figs. 6 and 8). In general, the highest strength of all mixes was attained with the addition of 30 wt% of Na 2 SiO 3 solution at 60 °C curing condition.
It is obvious from the test results that increasing the activator solution content from 10 to 30 wt% not only increases the compressive strength of the specimen at a selected curing temperature but also increased strength with time (Fig. 5). It should be noted that the curing time and temperature have a significant impact on mechanical strength development.
It is worth mentioning this research was an initial experiment for investigating the feasibility of alkali activation of the selected low alumina MT. The selected curing temperatures used for the speed up the reaction and further analysis will be done in an ambient temperature based on the field requirements. Figure 6 shows the variation of compressive strength achievements with curing temperatures at different additions of Na 2 SiO 3 contents. The effect of Na 2 SiO 3 contents on the compressive strength depends on the curing temperature. At a curing temperature of 40 °C, the compressive strength slightly increases with greater Na 2 SiO 3 addition. At a curing temperature of 60 °C, there is an increase in the compressive strength when the Na 2 SiO 3 addition increases from 10 to 30 wt%. Temperature speeds up the alkaline activation of a solid mixture as it happens with most of the chemical reactions. Equally when temperature increases, the rate of the reactions increases.

SEM/EDS Analysis of the AAMT
The effect of using various amount of Na 2 SiO 3 on the morphology of specimens cured at 40 °C for 28 days is indicated in Fig. 7(b-d). Figure 7a shows that the MT particles have irregular shapes with the rough surface, and the fine particles are attached to the surface of coarse particles. It is obvious, the addition of Na 2 SiO 3 greatly impacted the matrix morphologies and increased the degree of reaction, which made the matrix denser and resulted in an improvement in the compressive strength. The unreacted MT particles were highlighted in the AAMT contains 10% Na 2 SiO 3 (Fig. 7b), indicating a lower degree of dissolution of MT and alkaliactivated materials. The matrix of the AAMT with 30% Na 2 SiO 3 was almost entirely transformed into fused rectangular prisms, which indicates a more complete transition in high-alkaline conditions. EDX analysis demonstrated that sodium silicate addition led to an increase in the Si/Al, Si/ Ca and Mg/Al contents (see Table 3). Lower Ca/Si molar ratios result in the formation of higher strength stability and illustrated a higher degree of alkali activation process. This is perhaps a result of improvement in the final strength of the sample contains more Na 2 SiO 3 .
The microstructure of MT with a 30 wt% Na 2 SiO 3 content (Fig. 7d) reveal a morphology consisting of a random array of sheet-like un-aggregated particles corresponding to the identified phases by XRD. The structure appeared to be more homogenous and denser, which is due to the dissolution of available silica, magnesia, and calcium in the mixture. Moreover, with increase in Na 2 SiO 3 content, the flocculated nature of the structure and the areas of flatness in the structure become more obvious.
Alkaline solution plays two important roles during alkali activation process, dissolution of silica species and increasing pH, and charge-balancing by providing the presented metal cations [47]. The current experimental results show an increase in compressive strength with Na 2 SiO 3 concentration. The increase in compressive strength with higher Na 2 SiO 3 concentration is due to the presence of more silica components and thus incorporation of larger quantities of silica components in the activation process. However, the current experiment indicates that the compressive strength increases with alkalinity, which is possibly due to the dissolution of crystalline silica, calcium, and magnesium to form C-S-H or M-S-H, this result is in agreement with XRD analysis.
However, the Ca/Si ratios are in the range of 0.1-0.34 which are obviously lower than the value of 0.67 usually reported for C-S-H [48]. Lower Ca/Si atomic ratios result in the formation of a denser matrix and higher strength stability. A low Ca/Si ratio led to a higher degree of alkali activation process. It could be due to the incorporation of magnesium in calcium silicate hydrate because the presence of notable amount of magnesium in the mixture. The presence of other compounds, such as Mg, during the alkali activation process can induce modification in the hydrated product, for instance the incorporation of Mg 2+ into the structure. Pytel [49] and Fernandez et al. [50]. identified the possible incorporation of magnesium into the CSH structure and observed a new phase attributed to the formation of a magnesium silicate hydrate (MSH). MSH gel formation is only considered into the CSH gel of low CaO/SiO 2 .The existence of different silicate structure prevents the formation of M-C-S-H phase but leads to the presence of separate M-S-H and C-S-H phases in the mixture containing magnesium and calcium [48,51].

3
The improving effect of high alkalinity on the compressive strength can be described by the presence of sufficient calcium and formation of C-S-H as a result of higher alkalinity concentration, which has been reported by different researchers [52][53][54][55][56][57]. The formed C-S-H gels block the voids in the matrix and make a stronger microstructure [56,57].
A schematic illustration of the phase relations in the system of MgO-SiO 2 -CaO-H 2 O, including specimens contain 10, 15, 20 and 30 wt% Na 2 SiO 3 is given in the ternary diagram of Fig. 8. The composition of the hydrated phase has been projected on to the anhydrous base of the system. Each point has been plotted from EDX analysis of Table 3. The M-S-H (MgO-SiO 2 binary system) and C-S-H are included and confirmed the composition of the AAMTs. The samples are nearer to the chemical composition of C-S-H than M-S-H and this can be deduced from Fig. 8. Figure 9 shows the SEM micrographs and EDS analysis results of the MT treated with 30 wt% addition of Na 2 SiO 3 cured at 60 °C for 28 days. The higher magnification micrograph (see dash lines) shows that the particles are reacted on their surface and bonded to each other, showing coherent correlation in the structure. Furthermore, the dense structure formed in AAMT with 30 wt% Na 2 SiO 3 at 60 °C ( Fig. 9a and b) and it looks slightly different from the same sample which cured at 40 °C (Fig. 7d). It is worth noting that the structure is consistent with the compressive strength changes of AAMTs prepared at different conditions. The EDS analysis results indicate the presence of Na, Si, Ca, Mg, Fe, and a tiny amount of Al, which is confirmed by EDS elemental mapping of identified elements (Figs. 9 (c, d)). The Pyrrhotite and Magnetite can be identified in the raw materials (MT) and the presence of the small isolated spots of Fe ions in Fig. 8c could be a possible role of Fe in the EDX imaging.

Water Absorption
The effect of the alkali-activated additive on absorbability of the specimens cured for 28 days at 40 °C and 60 °C are shown in Fig. 10. This calculation provides an indirect approach to estimating the porosity network and idea about the influences of using different alkaline activator contents and curing regimes on the pore structure of the compositions. As was predicted (and as revealed in the results in Fig. 10), curing conditions affected pore structure, so that the water absorption varied in the range of 10-17%. Moreover, the water absorption of the specimens decreased with the higher Na 2 SiO 3 concentration, which indicates a denser structure (less porosity) [45,58]. Interestingly, it was observed that increasing the content of sodium silicate solution reduced the water absorption which could explain the slight increase in compressive strength. The minimum water absorption of the 28-day cured specimen at 40 °C and 60 °C came from AAMT with 30 wt% Na 2 SiO 3 (12.62% and 9.98%, respectively), indicating a higher degree of reaction compared with other specimens and resulting in the highest compressive strength (15.84 and 22 MPa). When the MT is activated with a high amount of Na 2 SiO 3 solution, the resulting material develops a very dense structure with the lowest apparent porosity. In fact, good correlation is observed mostly between compressive strength and water absorption in AAMT. Consequently, increasing the Na 2 SiO 3 contents and curing temperature have led to escalate the amount of soluble silica in the mixture and finally accelerating the alkali activation process.
According to the successful usage of alkali activation technology in low-alumina mine tailings to produce sustainable construction materials, it is also proposed to use these materials in the production of lightweight thermal and acoustic panels. These materials use the combined advantages of alkali-activated binders, lightweight, good thermal resistance, and high sound absorption [59][60][61][62][63][64][65][66][67][68].

Conclusions
The promising experimental results from this study indicate that MT can be used to produce AAMTs as a potential sustainable material for operation or closure of mines. Stabilization of mine tailings using Na 2 SiO 3 activation solution transforms such waste into a composition with adequate strength. This article reported the special effects of alkali activator concentration and curing time and temperature on the mechanical properties, microstructure, elemental and phase composition of AAMTs. The  Fig. 9 a, b SEM micrograph of MT-30% Na 2 SiO 3 cured at 60 °C for 28 days, the image 8b shows the highlighted area in the 8a at a higher magnification, d backscattered electron image a and c, e EDS element map and EDS spectra analysis of the backscattered electron image (Fig. 8d) feasibility of developed AAMTs was studied by conducting compressive tests, water absorption tests, SEM imaging, and XRD analysis. Na 2 SiO 3 concentration and curing temperature/time are the factors that affect the compressive strength and microstructural properties of AAMTs. The SEM/EDS results indicate a heterogeneous matrix for AAMTs. The matrix is denser at higher curing temperatures. The XRD patterns at the optimum conditions show a change in both amorphous and crystalline phases, and the compressive strength is improved at elevated curing temperatures.
The ideal curing temperature (i.e., the curing temperature at the maximum compressive strength) depends on the Na 2 SiO 3 concentration. The compressive strength increased with the increase of alkaline solution addition from 10 to 30 wt%. More Na 2 SiO 3 addition and a higher curing temperature contribute to the dissolution of silica and subsequent formation of a higher amount of alkali-activated gels, resulting in a higher compressive strength. Among the mixtures examined in this study, the mixtures having 30 wt% Na 2 SiO 3 solution can be considered the optimum mixture for reasonable compressive strength under the curing conditions studied here. The highest compressive strength of AAMT samples after 28 days of curing at 40 °C and 60 °C reached 14.78 and 20.49 MPa, respectively. The addition of Na 2 SiO 3 to the MT results in higher compressive strength and lower water absorption.