Lead-Zinc Mine Tailings Valorization Through Fly Ash-Based Geopolymer for Building Material: Synthesis, Microstructure, and Mechanical Properties | Research Square window.SnipcartSettings = { analytics: { enabled: false } }; (function() { var accessVector = localStorage.getItem('access_vector') || ''; window.dataLayer = window.dataLayer || []; if (accessVector) { window.dataLayer.push({ user: { profile: { profileInfo: { snid: accessVector } } } }); } })(); (function(w,d,s,l,i){w[l]=w[l]||[];w[l].push({'gtm.start':new Date().getTime(),event:'gtm.js'});var f=d.getElementsByTagName(s)[0],j=d.createElement(s),dl=l!='dataLayer'?'&l='+l:'';j.async=true;j.src='https://www.googletagmanager.com/gtm.js?id='+i+dl;f.parentNode.insertBefore(j,f);})(window,document,'script','dataLayer','GTM-K279D39R'); Browse Preprints In Review Journals COVID-19 Preprints AJE Video Bytes Research Tools Research Promotion AJE Professional Editing AJE Rubriq About Preprint Platform In Review Editorial Policies Our Team Advisory Board Help Center Sign In Submit a Preprint Cite Share Download PDF Research Article Lead-Zinc Mine Tailings Valorization Through Fly Ash-Based Geopolymer for Building Material: Synthesis, Microstructure, and Mechanical Properties ALSENY BAH, Andrea ORTIZ Ramos, Feng Daolun, jie Jin, Alhassane Bah, and 1 more This is a preprint; it has not been peer reviewed by a journal. https://doi.org/ 10.21203/rs.3.rs-996321/v1 This work is licensed under a CC BY 4.0 License Status: Under Review Version 1 posted 4 You are reading this latest preprint version Abstract Using geopolymerization to value mining wastes in order to meet construction demand is a sustainable and environmentally friendly strategy. Fly ash geopolymer materials have been developed to address environmental issues such as climate change caused by the emissions of CO 2 from coal fly ash plants, mining, and cement industry into the atmosphere. The main objective of this study is to study the feasibility of using mine tailings to produce environmentally friendly building materials (so-called geopolymer products) with excellent mechanical strength through fly-based geopolymer technology. Fly ash (F.A.) and mine tailings (M.T.) were utilized as raw materials and gypsum (G.Y.) as additives. Sodium hydroxide (NaOH) at (5-10M) and sodium silicate (water glass) constituted the alkaline solution and were added separately to the mixture. The mechanical property and microstructure of the geopolymers were assessed by performing the Unconfined Compressive Strength (UCS), Scanning Electron Microscopy (SEM), X-ray diffractions (XRD), and Fourier transforms infrared (FTIR). A 24 MPa was achieved at 10M NaOH with 100% F.A. Besides, low UCS values were obtained with only M.T. as a binder. The SEM imaging analysis confirmed similar results showing that the geopolymer specimens cured with 100% of F.A. at 10M NaOH with a moderate amount of gypsum are denser than those prepared without gypsum at 5M. The findings revealed that F.A., MT, and gypsum, together with the alkali reagents, influenced the geopolymerisation process. These factors responded effectively to the microstructural performance(increasing density), resulting in increased unconfined compressive strength. Environmental Chemistry Toxicology Geopolymer Solidification Fly ash Mine tailing gypsum mechanical strength microstructure. Figures Figure 1 Figure 2 Figure 3 Figure 4 Figure 5 Figure 6 Figure 7 Figure 8 Figure 9 Figure 10 Figure 11 Figure 12 Figure 13 1. Introduction Valorising mine tailings through geopolymerisation to meet construction demand is a sustainable and environmentally friendly approach. Environmental problems have become a worldwide concern. In addition, Heavy metals such as lead (Pb), zinc (Zn), Copper (Cu) are among the most dangerous pollutants which lead to the death of the living organism (Humans, animals) through environmental pollution that occurs by the exploitation of mineral resources. Crushed rocks, as well as effluents from mineral exploration, make up mine tailings. These are the byproducts left over from extracting products from mining ores that have never been a 100 percent effective system; not all agents and chemicals used are recoverable. Mine tailings are also discarded products that provide no economic advantage to the mineral miners at the time of manufacture. Hence they are often kept in the most cost-effective manner possible to meet obligations. (Xiaolong et al. 2021 ). On the other side, Every year, the issue of long-term dumping of tailings (M.T.) that pile in tailing ponds and mining waste landfills becomes increasingly pressing.(Ngole-Jeme and Fantke 2017; Kinnunen et al. 2018 ; Krishna et al. 2021 ). Besides, it occurs as a result of higher manufacturing quantities in mining and metallurgical entities, as well as the absence of meaningful waste-handling techniques. However, also, it is stated, particularly in developed countries, tightening environmental regulations. The continuous inflow of toxic substances, radioactive elements, and other harmful substances into the ecosystem, polluting the soil, is indeed a serious outcome of tailings storage. (W. Zhang et al. 2020 ), water (Sheoran and Sheoran 2006 )and air (Csavina et al. 2012 ). The use of M.T. as a major contributor to alkali-activated materials and geopolymers represents an attractive trend for their application. (Kiventerä et al. 2020 ). This process is an opportunity not just to reduce the dynamics of M.T. accretion and decrease the occurrence of industrial contamination, but it also integrates the benefits of geopolymer technology related to the diminution of carbon dioxide liberation into the atmosphere, the potential for utilizing certain technogenic aluminosilicate waste, and the adaptability of the characteristics of geopolymers as an overall building material (Ma, Awang, and Omar 2018; Hassan, Arif, and Shariq 2019 ; Lazorenko et al. 2020 ; Krishna et al. 2021 ) Sustainable management of tailings through geopolymers has increasingly attracted the attention of a diverse group of experts, including general practitioners. Numerous research has indeed been reported, highlighting an attempt to improve understanding of the mechanics of tailings geopolymerization to control the characteristics of MT-based geopolymers for long-term development (Moukannaa et al. 2019 ). Owing to its appealing attributes like superior mechanical properties, enhanced heat resistance, prolonged durability, and reasonable manufacturing costs, geopolymers have indeed been extensively explored as a Portland cement replacement in recent years (Moukannaa et al. 2019 ) In order to find sustainable solutions to address these issues, some environment materials such as « Geopolymers » by geopolymerization process that engages chemical reaction of aluminosilicates oxides with Alkali polysilicates yielding polymeric Si-O-Al bonds (Davidovits 1991 ) and some techniques such as « Solidification / Stabilization technology » have been developed to encapsulate toxic chemical and radioactive waste. In order to diminish the quantity of fly ash from a power plant to be disposed of in the world such as the Czech Republic, the fly ash has to be added to cement and concretes(Škvára, Jílek, and Kopecký 2005; Zhao et al. 2019 ), in addition, using alkaline solutions reagents such as NaOH, or Na 2 SiO 3 contribute strongly to geopolymerization process as said (Rattanasak et al. 2011), that geopolymerization happens in alkaline solution, especially in the sodium hydroxide/sodium silicate system. Gypsum has been utilized in some recent studies to ameliorate the mechanical strength of fly ash-based geopolymers when activating the fly ash by sodium hydroxide(NaOH) and Sodium silicate(Na-silicate) (Jun et al., 2015). CaSO 4 or gypsum is a suitable additive due to its availability in the market with acceptable cost (Boonserm et al., 2012 ). This research, therefore, evaluates the performance of raw materials ( Fly Ash (F.A.), Mine Tailings(M.T.), and Gypsum(Gy)) and the Alkali reagents ( NaOH and Sodium Silicate) to study the mechanical property and microstructure of geopolymers. In order to achieve this research, the XRF, XRD diffractometer, FTIR, SEM imaging, and the Unconfined Compressive Strength (UCS) analysis were performed to investigate the Geopolymer-based solidification of Lead-Zinc mine tailings. 2. Materials And Methods 2.1. Materials Based on the availability, affordability, and applicability, the following materials were chosen to conduct this research, including fly ash (F.A.), gypsum (G.Y.), and mine tailings (M.T.), Sodium hydroxide (NaOH), sodium silicate, and distilled water. Both the F.A. and the G.Y. were obtained from Jiangsu Nanre Power Generation Co., Ltd. (Nanjing, China), M.T. was achieved from Nanjing Yinmaoqianxin Mining Industry Co., Ltd. (Nanjing, China). 96% NaOH pellets were supplied by Shanghai Macklin Biochemical Co., Ltd., and sodium silicate solution (SiO 2 13.36%; Na 2 O 29.84%) was obtained from Ganjiashan Yourui Refractories Co., Ltd. Sodium hydroxide and sodium silicate were selected as alkaline agents due to the sodium geopolymers had higher mechanical strength than potassium geopolymers ( Rao et al., 2015 ) . The chemical compositions of both F.A. and M.T. were obtained by the fused X-ray fluorescence (XRF) method, and the results are shown in Tables 1 &2. The X-ray diffraction (XRD) analysis of the raw materials and geopolymers specimens was performed on an XRD-6100 diffractometer (Shimadzu, Japan), the Fourier Transform Infrared Spectroscopy (FTIR) data were collected on Is5 infrared spectrometer, and The scanning electron micrograph (SEM) of the raw materials and geopolymers specimens were measured by using a Hitachi japan SU1510 microscope. 2.2. Synthesis of Geopolymer To achieved the objective of this study, forty (40) geopolymer recipes were performed. Samples were prepared by blending the dry reagents about 7 min then gradually adding the alkaline liquid such as NaOH at 5 -10M and sodium silicate in the different recipes) and further mixing for 5 min. The alkaline solution was prepared by blending the sodium hydroxide solution to de-ionized water (DIW) at 5 M and 10 M with sodium hydroxide flakes and stirring for at least 5 min. Due to the heat generation, adequate time was required for the solution to cool down to room temperature one day before it was used; however, the NaOH solution and sodium silicate were injected into the dry mixture separately. The samples were cast in 20x 20 x 20 mm cubes at room temperature for 72 hours before being removed from the molds and kept for another four days at room temperature. Two measurements of the 12 cubes made to measure the compressive strength of 7, 14, and 28 days will be taken. Table (3) presents the mixture design of the different samples performed in the study to find the best recipe to encapsulate the toxic metals, where the labels will represent using letters which are represented by fly ash (F), gypsum (G), mine tailing (M), sodium hydroxide (S), water glass (W). Where W/S expresses the ratio between sodium hydroxide (S) with a water glass or sodium silicate soln (W) were added in some of the mixes. In addition, silica or quartz is the principal impurity in fly ashes. In geopolymerization, silicate is an important activator, so Si / Al ratios higher than 2.5 were commonly investigated in the literature. In this work, the Si / Al ratios of all specimens having in their composition fly ash vary from 1 to 2.54, coinciding with the work of Davidovits and his co-workers, where they concluded that the Si / Al ratio in fly ash-based geopolymers should be between 1 and 3( Rao et al., 2015 ). On the other hand, the specimens with a high Si/Al ratio that varies between 10.33 and 12.25 belong to the 100% of M.T. in the composition. In some works, gypsum applications can reduce porosity; however, an excess amount of gypsum may cause volume instability within the material. As fly ash is an industrial waste material, varying impurities of different chemical substances may be found within fly ash, which resultantly may cause significant changes in reactions; however, gypsum was also added with other ingredients such as calcium silicates and other types of sodium silicates(Jun et al., 2015), that is why in some recipes was added a portion of 10 or 20 grams of the gypsum. Then the crystallization phase of geopolymers with the highest value of compressive strength was analyzed through FTIR and XRD machines. 2.3. Mechanical Property Test The unconfined compressive strength (UCS) test is known and utilized to measure geopolymers' solidification effectiveness. It is generally accepted that a UCS of 0.35 MPa (psi) is appropriate for the physical integrity of solidification/ stabilization waste type to withstand standards landfill overburden pressures. (Choi et al., 2009 ). 20 x 20 x 20 mm cube specimens were cast for the strength test on mortar at 3, 7, and 28 days UCS. The mortar specimens were cast and cured at 25–30°C room temperature. The molds have been covered with protective plastic sheets shortly after casting and de-molded after 24 hours. The compression tests were carried out using a load compression testing machine. At least three samples were tested for every age, as well as the average of the recorded UCS values is being used. 2.4. Geopolymer Microstructure Analysis To understand the geopolymers' properties, physical observation and Methods of mechanical detection were utilized upon selected geopolymers products based on their performance in terms of compressive strength results. FTIR test results were acquired and used an ASTM Standard (IS5 infrared spectrometer) from Thermo Fisher USA and a Shimadzu (Japan) XRD machine model (XRD-6100) with an objective function of (20-60KV and 2-80mA) for the phasing characteristics. Furthermore, morphological properties of geopolymer samples were studied using Hitachi (Japan) SU1510 SEM equipment. 3. Results And Discussion 3.1. Characterization of Fly Ash, Mine Tailing, and Gypsum To comprehend the effectiveness of raw resources, including mine tailings, fly ash, and gypsum, in forming a geopolymer, it is necessary to understand their physical and chemical properties, including chemical compositions, mineralogical composition, and size distribution. Table 1&2 shows the chemical composition of fly ash (F.A.) and mine tailings (M.T.) that consisted mostly in a vitreous phase comprising 40.15% and 35.50% of SiO 2 and Al 2 O 3 , respectively. Also another oxide in lower percentages including CaO, Fe 2 O 3 , and MnO 2 to 8.33%, 7.57%, and 0.11%, respectively. The LOI limitations are 8% and 6% according to CSA A3001 for Type F fly ash and for Types CI and C.H. fly ashes, respectively; considering the acceptable limitations for LOI, the F.A. level is 1.64, allowing the specimen to be utilized for testing and obtaining a great outcome. Heavy metal quantities including Pb, Cu, Y, Cr, and As could also be found in F.A., as shown in Table 2. Fig. 1 shows the XRD patterns of fly ash composition that are utilized in this research. It is clear that the presence of the quartz is 7.9% and mullite 24.5%, which are the non-reactive crystalline phase, and the amorphous phase present in the F.A. is 67.6%. The distinctive shape of the original fly ash morphology is shown in Fig. 3 (a). It appears to be made up of nearly uniform spherical (cenospheres) vitreous fragments with diameters ranging from 2 to 14 m. Mine tailings mineralogy is largely dependent on the type of the original ore, minerals manufacturing techniques, as well as the level of deterioration during storing in tailings ponds. (Kossoff et al. 2014 ). Furthermore, The reactivity of prospective geopolymerization precursors is determined by the alkali solubility of silicon and aluminum, determined by their mineralogy. As a result, mine tailings' reactivity can be estimated based on their mineralogical features. (Xu, H., van Deventer 2000 ). Tables 1 & 2 display the mine tailings’ chemical composition (major oxides and trace elements). It can be seen in these tables that M.T. consist mainly of Si, Fe, and Al, as shown by the major oxide composition of 18.83%, 29.49%, 9.12%, 6.20%, and 1.61% for SiO 2 , CaO, MnO 2, Fe 2 O 3 , and Al 2 O 3 , respectively. The tailings also contain a lower concentration of heavy metal, which could confirm the results of the study “ A Research on the Leaching Toxicity of the Solid Waste of a Pb-Zn mine ” of Wang et al. (Wang et al. 2015 ), in which the chemical study revealed that harmful component level in the mine tailings was low, indicating that there was no risk of pollution. As a result, it was determined that mine tailing specimens are not harmful substances. The predominant minerals included in mine tailings, according to XRD examination, are crystalline solids such as sphalerite, gehlenite, gypsum, calcite, brushite, and quartz, (Fig. 1 ).For the last description of M.T., the bans around 3316cm-1 were attributed to loosely bound water (H-O-H), and the absorption band 1660 cm-1was induced by O-H stretching from adsorbed water. The band 1393 cm-1 is associated with symmetric stretching vibration from adsorbed CO2, and the band 1016 cm-1 was assigned to apical Si-O stretching and Si-O-Si stretching. The M.T particle size distribution is shown in Fig. 4 ; roughly 42.50 percent of both the particulates are less than 60 m, with the remaining 5.56 to 9.41 wt percent having a size ranging from 60 to 200 m. Ultimately, the second-highest figure in size particle distribution is 13,02 wt percent of particles larger than 200 m. Fig. 3 (b,c) also depicts the M.T. amorphous crystals in various sizes. Because mine tailing particulates are angular, dried tailings have a higher strength angle. Since its magnitude is dependent on the mineral processing requirements, it is hard to extrapolate. (Xiaolong et al. 2021 ). The description of gypsum was compared with the band standards of the gypsum spectra, the peak around 3396 -3562 cm −1 and 1623 cm −1 own to the H-O *H. The S-O, which including the asymmetrical vibration, will be in the band 1139 cm-1; the bands 590 to 669 cm-1 represent the asymmetrical deformation vibration. (Wei et al. 2016). The SEM results of the gypsum and the varied forms and structures of both the particulates are shown in Fig. 3 (d). The FTIR spectra of F.A., G.Y., and M.T. are shown in Fig. 2 . At first, it will be described the bands of F.A. At 568 cm-1 is due to Al-O-Si symmetric stretching. For Si-O-Si asymmetric stretching is shown in the band at 1066 cm. The structural and geometric knowledge from SEM analysis of crystals helps us define the distinction between raw resources and geopolymers' crystallization. 3.2. The Physical Characteristic of Geopolymers Once the mixtures were done, bulks had different physical characteristics such as color, shape, and integrality. In Fig. 13 (a), (b), and (c), different series of geopolymers were shown, whose compositions are described in Table 3; all of them have a cubic shape with a dimension of 20 x 20 x 20 mm. The specimens labeled with the codes FMS-0x (x = 1, 2, 3, 4, and 5) have the following characteristics, the colors of these bulks vary from a gray color that little by little changes to a shade of brown by the increase in the amount of mine tailing respectively, the two last specimens of the series FMS-04 and FMS-05 do not conserve the initial cubic shape. The second series with the code FMSW-0x had the same variety of colors with the difference that are a little bit dark, as for its shapes are cubic but with a presence of cracking in the surface of all the series. Finally, the series FMS-0xa, which were activated with NaOH at 10M, these series also presented a variety of color but little more intense compared to others, but that is caused by the increase of mine tailing in the mixture, but covered with a white layer that could be due to the interaction of sodium hydroxide with carbon dioxide. By simple observation, it was possible to determine the integrality order of this series of geopolymer specimens as follows: FMS-01 > FMS-02 > FMS-03 > FMS-04 > FMS-05 FMSW-01 > FMSW -02 > FMSW -03 > FMSW -04 > FMSW -05 FMS-01a > FMS-02a > FMS-03a > FMS-04a > FMS-05a The specimen's codes FGMS-0x belong to the first line of Fig. 12 (a), the colors of these bulks vary from a gray to brown but FGMS-05, was covered with a white layer, cubic shapes with a presence of cracking in the surface of FGMS-03, -04 and -05, and also observed a light erosion at the corners of the cube in FGMS-05. In the second series with the code FGMS-0xa, the colors of the different bulks presented a grayscale and were observed a slight erosion in the cubic shapes. The integrality order of these series of geopolymer specimens are as follows: FGMS-01 / FGMS-02 > FGMS-03 > FGMS-04 > FGMS-05 FGMS-01a > FGMS-02a > FGMS-03a > FGMS-04a > FGMS-05a 3.3. Mechanical Property and Microstructure of Geopolymers 3.3.1 Mechanical Property of Geopolymers In order to investigate and figure out the mechanical property of the geopolymer specimens, the effect of the curing time, sodium hydroxide (NaOH), Fly Ash (F.A.), and gypsum (Gy) on the Unconfined Compressive Strength (UCS) were performed based on some selected geopolymers matrix. Furthermore, Table 4 summarizes the samples that have the higher values of UCS of the different series. 3.3.1.1. Effect of Curing Time on Mechanical Strength The role of curing time on the compressive strength (UCS) has been investigated with the proportion of F.A. (0%, 25%, 50%, 75%, 100%). Fig. 5 shows the result of curing time on the compressive strength for FMS-0xa geopolymer specimens at 10M NaOH. These mixtures were cured for different curing times, which are 7, 14, and 28 days. Only the FMS-05a mixture with 0% of F.A. decreased with the increase of curing time. The trends of FMS-04a with 25% of F.A. which to pass the days will decrease gradually with the increase of curing time but not completely to zero compared to the FMS-05a mixture. that showed the F.A. particles have high reactivity and play a great role in the mechanical properties. The lack of data in compressive strength of the geopolymer specimens with 100% mine tailing (M.T.) was reported in many research that there is no geopolymerization. Additives like fly ash, gypsum were utilized in geopolymerization processes to consolidate mine tailings (Rao and Liu 2015). Figure 5 summarizes the specimens cured at room temperature whose compressive strength values increase with the cured time. A longer curing period increases the polymerization rate resulting in higher compressive strength. The results show that longer curing periods did not lower the compressive strength of geopolymer concrete as declared (Jaarsveld et al. 2002 ). These will be the best candidates to perform the toxicity study to determine the encapsulation capacity of toxic metals. 3.3.1.2 Effect of Fly Ash and NaOH Concentration on Mechanical Strength Figure 12 (a-b) displays the result of Unconfined Compressive Strength (UCS) of fly ash-based geopolymer specimens cured at room temperature for seven days with various F.A. proportions (0%, 25%, 50%, 75%, 100%) and NaOH concentration at 5M and 10M. This figure shows that both F.A. and NaOH contribute strongly to the increase of strength. Higher the amount of F.A. and NaOH is greater than the UCS value, as demonstrated in another study (Zhang et al. 2011 ). This is due to higher O.H. or sodium oxide content during the geopolymerization reaction, as claimed by Zhuang et al. There are reactions and condensation between fly ash and alkaline reagents. The outcome, Si 4+ , and Al 3+ , combined with complex crystallization, oligomerization, and polymerization, yields a new aluminosilicate-based polymer with a novel amorphous three-dimensional network structure (Zhuang et al. 2016 ). The Si/Al ratio played a great role in the geopolymerization as the main precursor. Furthermore, as demonstrated by Zhang et al. (L. Zhang et al., 2011 ), the elevated of the Unconfined Compressive Strength (UCS) with the proportion of F.A. is owing to the Si/Al ratio of the MT/FA mixture and its reactivity. Generally, a low Si/Al ratio is preferable for a good geopolymerization (Rangan et al., 2014) and should be within 1-3 (Xu et al., 2003 ; Zhang et al. 2011 ; Rangan et al., 2014). 3.3.1.3. Effect of Gypsum (G) on Mechanical Strength In order to investigate the effect of gypsum (G) on the Unconfined Compressive Strength (UCS), three series of geopolymers specimens (FMS-0x, FGMS-0x, and FGMS-0xa) were performed with different proportions of F.A. (0%, 25%, 50%, 75%, and 100%) cured for seven days at 5M NaOH with Gypsum that range at 0g, 10g, and 20g. Fig. 12 (c) shows the role of gypsum with different proportions of fly ash on the compressive strength. It can be seen that the strength of the geopolymers with gypsum increase compare with those without G, which means adding gypsum can improve the geopolymerization as claimed (Boonserm et al., 2012 ). The highest peak of strength was gained by adding 10g of G. This increase happened because of the entering of Ca 2+ in the bond Si-O-Al-O and equilibrating the charge Al ions (Fernández-Jiménez et al. 2006 ), that contributes strongly to the formation of CSH, aluminosilicate structure and lead to the improvement of compressive strength (Boonserm et al. 2012 ). Further, the trend drops down with the increased amount of G (Rattanasak et al., 2011 ). 3.3.2 Microstructure and Microchemistry of Geopolymers In order to characterize and evaluate the microstructure and microchemistry of fly ash-based-geopolymer matrix and figure out the connection between the microstructure and compressive strength of geopolymers, SEM imaging, XRD diffractometer, and FTIR spectra of selected geopolymers specimens were evaluated. Finally, it can be noted that one of the most important factors that contribute to the mechanical strength is the water ratio used. Basically, the lower this ratio is, the greater the final UCS strength will be. The geopolymer specimen series (FMS-0xa) with 0.27 of Liquid/Solid ratio has recorded the highest values in terms of UCS strength which vary between 1.7 and 14,075 MPa. The compressive strength also depends on the curing time. The UCS test of the geopolymer showed slight changes in compressive strength after 28 days, but no changes have been recorded after 56 days(Badur and Chaudhary 2008). When sodium silicate was utilized, the presence of silica retards the zeolite formation rate. As a result, first, greater strength values are gained at lower degrees of reaction. The fly ash activated by an alkaline solution can have a greater compressive strength with greater zeolite content. (Lloyd, 2009 ) 3.3.2.1 SEM Imaging Analysis The SEM imaging was carried out to figure out the effect of aging periods, NaOH concentration, and gypsum on the microstructure of geopolymers. The SEM micrographs of different geopolymer specimens are displayed in Figs. 7 - 10 . In order to understand the effect of aging time on the microstructure of the geopolymer specimens, SEM imaging of FGMSW-3b matrix was carried out and cured under room temperature condition after 7, 14, and 28 days with 100% F.A., 20g of Gy at 10 M of NaOH concentration (Fig. 7 ). Fig. 7 provides a comparative analysis of SEM micrographs of various geopolymers effectively treated at varying periods at a moderate optical zoom. According to this figure, there is very little modification in the microstructure of geopolymers after seven days, implying that curing time has little influence on the microstructure, as also stated by another study. (Zhang et al. 2011 ). To figure out the effect of sodium hydroxide (NaOH) on the microstructure of geopolymer specimens (FMS-02 and FMS-02a) cured under room temperature after 14 days curing period with 100% F.A. at different concentrations of NaOH (5M and 10M), the SEM imaging was investigated. Fig. 8 depicts the various modifications shown in the micro-structural of the geopolymers. Fig. 8 (a) showed the existence of F.A. in a negligible amount as the concentration of NaOH increases, discussing the function of NaOH in polymerization. Fig. 8 (b) indicates the existence of F.A. in a massive portion as the concentration of NaOH increases, which also clarifies the function of NaOH in geopolymers. Further analysis revealed that at 15M NaOH, the particles of F.A. have been almost non-existent, indicating that the increased the NaOH concentration, the faster the geopolymerization rate. At 15M, the geopolymer gel was much more cohesive and thicker than that at 5 and 10M, yet geopolymerization was quite substantial at 10M (Zhang et al. 2011 ). It also confirms the compressive strength (UCS) results (Fig. 12 (a)), which show that the maximum UCS value was acquired to 10M NaOH. The effect of sodium silicate (Na-silicate) on the microstructure was evaluated, by comparing the specimen FMS-01 activated with only NaOH and FMSW-01 activated with NaOH and Na-silicate both cured at ambient temperature, at 5M NaOH with 100% F.AAs shown in Fig. 9 (c) and (d), there is still a notable change in structural system between all these images; Fig. 9 (d) is more compact than Fig. 9 (c), attributed to the existence of sodium silicate in that sample at a 1.08:1 ratio. Once sodium hydroxide (NaOH) and sodium silicate (Na-Silicate) are mixed to make an alkali solution, the blending has superior mechanical properties than NaOH alone(Palomo et al. 1999 ); the very same research claimed that sample only with NaOH has a porous material compared to one provided both with NaOH and Na-Silicate, which has a higher density structure. To understand the effect of gypsum on the microstructure of the geopolymer matrixes (FMS-02, FGMS-02, and FGMS-02a) at low magnification, the SEM analysis was performed with 75% F.A. at 5M NaOH at different content of gypsum: (a) 0g, (b) and (c) 20g 10 g of gypsum cured for seven days curing under ambient air condition. The scanning electron microscopy (SEM) geopolymer matrixes (FMS-02, FGMS-02, and FGMS-02a) are displayed in Fig. 10 . This figure reveals that the opacity of these three geopolymers varies significantly. The sample of FGMS-02 with 10g of Gy in Fig. 10 (b) is much more condensed with low permeability than that of the other geopolymers; nevertheless, there is much more unreacted F.A. in the FMS-02 geopolymer with 0g of Gy in Fig. 10 (a) than the other geopolymers, which clarified the function which gypsum performed in terms of microstructures and mechanical properties by boosting the polymerization rate. In addition, these SEM imaging results justified the Unconfined Compressive Strength results (Fig. 12 . (c)) that the UCS values increased with the addition of 10g of Gy. This performance could be attributed to the combination of mine tailings (low reactivity) to fly ash (high reactivity) and gypsum, which concurred with the research finding of Xiaolong et al., which claimed that mine tailings are often crystalline, leading to low reactivity throughout geopolymerization therefore; as a result, products with minimal compressive performance. As a result, adding extra elements with higher reactivity to mine tailings-based geopolymers can efficiently tune and optimize their characteristics. (Xiaolong et al. 2021 ). Furthermore, because most of the chemicals included in this function are manufacturing wastes, its use has additional benefits for the environment. Strong-containing calcium compounds have such a higher favorable impact on geopolymer durability than lower-containing calcium. This is due to the development of extra CSH gels, which, when combined with NASH, increases structural integrity, as previously reported by Xiaolong et al.,.(Xiaolong et al. 2021 ) 3.3.2.2 XRD Analysis X-ray fluorescence spectrometry has been used to determine the elemental composition of the geopolymers using the XRD-6100 diffractometer and the XRD patterns have been analysed through JADE 6.0 Software. Because of its amorphous or nanocrystalline nature, the N-A-S-H gel formed during polymerization is difficult to characterize with XRD. Nonetheless, the XRD patterns of the specimens were used to determine the crystalline formation in the different mixture designs of the fly ash-based geopolymer presented with high compressive strength. (FMS-01a (100% F.A.), FGMS-02 (75% F.A.), FGMSW-02 (75% F.A.), FGMSW-01a (100% F.A.), FGMSW-03b (50% F.A.), synthesized under room temperature conditions cured at 7, 14 and 28 days is shown in Fig. 6 , where different phases have been obtained. Where C= Corundum Al 2 O 3 , Cc= Calcite CaCO 3 , G=Gypsum CaSO 4 2H 2 O, M= Mullite Al 6 Si 2 O 13 , Q= quartz SiO 2 , Ss=Sodium silicate Na 2 (SiO 3 ), Sh=Calcium Silicate hydritade Ca 1 .5Si 0.5 xH 2 O, Ch= Chabazite, J= Jadeite, A=Anhydrite CaSO 4 . Mullite and quartz, which have been discovered in raw fly ash, were observed throughout all samples. All of the enabled samples exhibited amorphous ridges focused around 220° to 30°, including all samples, confirmed the formation of a geopolymer gel. (Keyte et al., 2009a). Except for the FMSW-05 sample, that does not show the geopolymerization since mine tailing is the only element in its composition. Singh et al., in their research, found a similar observation (Singh et al., 2018). Numerous crystalline structures, including quartz and mullite, have been regarded as non-reactive, even though their reaction speed in alkali-silicate solutions is remarkably slower when compared to inorganic materials.(Keyte et al., 2009b) in some of the samples as FGMS-02 and FGMSW-03, could identify de chabazite, which is one of the crystal that can encapsulate the heavy metals such as Cu and Pb (Jun et al., 2015) . Calcite, CaCO3, is formed once calcium hydroxide reacts to carbon dioxide in the atmosphere; calcium solubility at elevated pHs has been well recognized to decrease due to the instability of calcium hydroxide forming(Komnitsas and Zaharaki 2009 ), his mineral was found in the majority of the samples. Crystallization amorphous gels were the subtler shown in fly ash-derived geopolymers. Compared to the fly ash instance, much less of the binder is gradually morphed into zeolite stages. Furthermore, variables that promote zeolite forming, like increasing the alkalis of the binder, increasing strength, and reducing any proclivity for strength loss, at least for the duration considered. The creation of zeolites, including chabazite, was recognized through XRD analysis in most specimens. Other minerals discovered included calcite and quartz, which were linked to the presence of zeolites. 3.3.2.3 FTIR Analysis The FTIR of the five best specimens in terms of compressive strength with various materials was investigated. The FTIR spectra of the five (5) geopolymers (FMS-01a (100% F.A.), FGMS-02a (75% F.A.), FGMSW-02(75% F.A.), FGMSW-02(75% F.A.), and FGMSW-03b (50% F.A.), containing a different proportion of Fly Ash and sodium hydroxide concentration (5M, 10M) cured at 7, 14 and 28 days are shown in Fig. 11 . Table 5 shows the Infrared characteristic bands identified in F.A. and geopolymers specimens. In-plane and bending vibrations of Al-O / Si-O, 460cm −1 , and 550 cm-1 are assigned. The existence of a 1456cm-1 band may be due to C= O vibrations, which indicate the presence of carbonate bands. In addition, the I.R. spectra studies show bands close to 1016 cm−1 and 1143 cm−1 due to asymmetric Si-O stretching while banding at 458 cm−1 to SiO4 bending in-plane Si-O. However, bands between 772, 579, 537, and 439 cm−1 correlate with Al-Si minerals. In addition, new bands emerging at 3423, 1638, and 1540 cm−1 are consistent with-OH, H 2 O bending and asymmetric carbonate stretching, respectively (Ismaiel Saraya and El-Fadaly 2017). The peak appeared at 1640 cm−1 as a result of bending H-O-H vibration, and the intensity of this peak increased with a rise in NaOH concentration, suggesting a rise in geopolymerization degree (Devi and Saroha 2016 ). 4. Conclusions From this study, it can be concluded that fly ash, mine tailings with gypsum as an additive by using Sodium hydroxide (NaOH) at (5-10M) and sodium silicate (water glass) as the alkali reagents can be used to study the feasibility of geopolymerization. In this work, eight geopolymer recipes were made based on fly ash. Both F.A. and M.T. were added in different proportions (0, 25, 50, 75, and 100%) of the total weight. The different dosages mentioned in the design section of the geopolymers gave rise to 40 recipes of geopolymers, which after being mixed and cured at room temperature after 7, 14, and 14 days curing time, showed slight physical changes compared to those without F.A. content could not maintain their shape and hardness. Furthermore, From this research, we remark that mine tailings could not be used alone in performing geopolymer products owing to their low reactivity. However, associating mine tailings with other binders with high reactivity, such as fly ash or high content in SiO 2 , would make mine tailings a suitable binder in geopolymerisation. In summary, the Unconfined Compressive Strength (UCS) of Geopolymers, the mechanical properties, and microstructure were influenced by curing time, temperature, and the chemical reactions. Furthermore, this study demonstrated that mine tailings could be successfully valorized through geopolymerization to generate eco-friendly products that would sustainably use in the building and construction materials industry. Declarations Acknowledgments The work was supported by the Postgraduate Research & Practice Innovation Program of Jiangsu Province (SJCX17-0261), NSFC (51002080, 41501197), SPITP (201610300273), Top-notch Academic Programs Project of Jiangsu Higher Education Institutions (PPZY2015C222), and the Priority Academic Program Development of Jiangsu Higher Education Institutions (PAPD). Conflicts of interest/Competing interests The authors declare that they have no known competing financial interests or personal relationships that could have appeared to influence the work reported in this paper. Funding (no) Availability of data and material (all data are included within the manuscript) Code availability (no) Consent for publication “Not applicable” References Badur, Smita, and Rubina Chaudhary. 2008. “Utilization of Hazardous Wastes and By-Products as a Green Concrete Material through S/S Process: A Review.” Reviews on Advanced Materials Science 17 (1–2): 42–61. Boonserm, Kornkanok, Vanchai Sata, Kedsarin Pimraksa, and Prinya Chindaprasirt. 2012. “Microstructure and Strength of Blended FBC-PCC Fly Ash Geopolymer Containing Gypsum as an Additive.” ScienceAsia 38 (2): 175–81. https://doi.org/10.2306/scienceasia1513-1874.2012.38.175. Choi, W. H., S. R. Lee, and J. Y. Park. 2009. “Cement Based Solidification/Stabilization of Arsenic-Contaminated Mine Tailings.” Waste Management 29 (5): 1766–71. https://doi.org/10.1016/j.wasman.2008.11.008. Csavina, Janae, Jason Field, Mark P. Taylor, Song Gao, Andrea Landázuri, Eric A. Betterton, and A. Eduardo Sáez. 2012. “A Review on the Importance of Metals and Metalloids in Atmospheric Dust and Aerosol from Mining Operations.” Science of the Total Environment 433 (September): 58–73. https://doi.org/10.1016/j.scitotenv.2012.06.013. Davidovits, J. 1991. “Geopolymers - Inorganic Polymeric New Materials.” Journal of Thermal Analysis 37 (8): 1633–56. https://doi.org/10.1007/BF01912193. Devi, Parmila, and Anil K. Saroha. 2016. “Risk Assessment and Technical Feasibility of Usage of Paper Mill Sludge Biochar-Based Exhausted Adsorbent for Geopolymeric Brick Formation.” Environmental Science and Pollution Research 23 (21): 21641–51. https://doi.org/10.1007/s11356-016-7343-4. Fernández-Jiménez, A., A. Palomo, I. Sobrados, and J. Sanz. 2006. “The Role Played by the Reactive Alumina Content in the Alkaline Activation of Fly Ashes.” Microporous and Mesoporous Materials 91 (1–3): 111–19. https://doi.org/10.1016/j.micromeso.2005.11.015. Hassan, Amer, Mohammed Arif, and M. Shariq. 2019. “Use of Geopolymer Concrete for a Cleaner and Sustainable Environment – A Review of Mechanical Properties and Microstructure.” Journal of Cleaner Production 223 (June): 704–28. https://doi.org/10.1016/j.jclepro.2019.03.051. Ismaiel Saraya, Mohamed El-Shahte, and Ezzat El-Fadaly. 2017. “Preliminary Study of Alkali Activation of Basalt: Effect of NaOH Concentration on Geopolymerization of Basalt.” Journal of Materials Science and Chemical Engineering 05 (11): 58–76. https://doi.org/10.4236/msce.2017.511006. Jaarsveld, J G S Van, J S J Van Deventer, and G C Lukey. 2002. “.” Chemical Engineering Journal 89: 63–73. Jun, Yubin, and Jae Eun Oh. 2015. “Use of Gypsum as a Preventive Measure for Strength Deterioration during Curing in Class F Fly Ash Geopolymer System.” Materials 8 (6): 3053–67. https://doi.org/10.3390/ma8063053. Keyte, L. M. 2009a. Fly Ash Glass Chemistry and Inorganic Polymer Cements . Geopolymers: Structures, Processing, Properties and Industrial Applications . Woodhead Publishing Limited. https://doi.org/10.1533/9781845696382.1.15. Keyte, L.M. 2009b. “Fly Ash Glass Chemistry and Inorganic Polymer Cements.” In Geopolymers , 15–36. Elsevier. https://doi.org/10.1533/9781845696382.1.15. Kinnunen, Paivo, Arnold Ismailov, Soili Solismaa, Harisankar Sreenivasan, Marja Liisa Räisänen, Erkki Levänen, and Mirja Illikainen. 2018. “Recycling Mine Tailings in Chemically Bonded Ceramics – A Review.” Journal of Cleaner Production 174 (February): 634–49. https://doi.org/10.1016/j.jclepro.2017.10.280. Kiventerä, Jenni, Priyadharshini Perumal, Juho Yliniemi, and Mirja Illikainen. 2020. “Mine Tailings as a Raw Material in Alkali Activation: A Review.” International Journal of Minerals, Metallurgy and Materials 27 (8): 1009–20. https://doi.org/10.1007/s12613-020-2129-6. Komnitsas, K., and D. Zaharaki. 2009. “Utilisation of Low-Calcium Slags to Improve the Strength and Durability of Geopolymers.” In Geopolymers , 343–75. Elsevier. https://doi.org/10.1533/9781845696382.2.343. Kossoff, D., W.E. Dubbin, M. Alfredsson, S.J. Edwards, M.G. Macklin, and K.A. Hudson-Edwards. 2014. “Mine Tailings Dams: Characteristics, Failure, Environmental Impacts, and Remediation.” Applied Geochemistry 51 (December): 229–45. https://doi.org/10.1016/j.apgeochem.2014.09.010. Krishna, R. S., Faiz Shaikh, Jyotirmoy Mishra, Georgy Lazorenko, and Anton Kasprzhitskii. 2021. “Mine Tailings-Based Geopolymers: Properties, Applications and Industrial Prospects.” Ceramics International 47 (13): 17826–43. https://doi.org/10.1016/j.ceramint.2021.03.180. Lazorenko, Georgy, Anton Kasprzhitskii, Alexander Kruglikov, Vasilii Mischinenko, and Victor Yavna. 2020. “Sustainable Geopolymer Composites Reinforced with Flax Tows.” Ceramics International 46 (8): 12870–75. https://doi.org/10.1016/j.ceramint.2020.01.184. Lloyd, R.R. 2009. “Accelerated Ageing of Geopolymers.” In Geopolymers , 139–66. Elsevier. https://doi.org/10.1533/9781845696382.2.139. Ma, Chau Khun, Abdullah Zawawi Awang, and Wahid Omar. 2018. “Structural and Material Performance of Geopolymer Concrete: A Review.” Construction and Building Materials 186 (October): 90–102. https://doi.org/10.1016/j.conbuildmat.2018.07.111. Moukannaa, S., A. Nazari, A. Bagheri, M. Loutou, J. G. Sanjayan, and R. Hakkou. 2019. “Alkaline Fused Phosphate Mine Tailings for Geopolymer Mortar Synthesis: Thermal Stability, Mechanical and Microstructural Properties.” Journal of Non-Crystalline Solids 511 (May): 76–85. https://doi.org/10.1016/j.jnoncrysol.2018.12.031. Ngole-Jeme, Veronica Mpode, and Peter Fantke. 2017. “Ecological and Human Health Risks Associated with Abandoned Gold Mine Tailings Contaminated Soil.” Edited by Jorge Paz-Ferreiro. PLoS ONE 12 (2): e0172517. https://doi.org/10.1371/journal.pone.0172517. Palomo, A., M. W. Grutzeck, and M. T. Blanco. 1999. “Alkali-Activated Fly Ashes: A Cement for the Future.” Cement and Concrete Research 29 (8): 1323–29. https://doi.org/10.1016/S0008-8846(98)00243-9. Rangan, B. Vijaya. 2014. “Geopolymer Concrete for Environmental Protection.” Indian Concrete Journal 88 (4): 41–59. Rao, Feng, and Qi Liu. 2015. “Geopolymerization and Its Potential Application in Mine Tailings Consolidation: A Review.” Mineral Processing and Extractive Metallurgy Review 36 (6): 399–409. https://doi.org/10.1080/08827508.2015.1055625. Rattanasak, Ubolluk, Kanokwan Pankhet, and Prinya Chindaprasirt. 2011. “Effect of Chemical Admixtures on Properties of High-Calcium Fly Ash Geopolymer.” International Journal of Minerals, Metallurgy and Materials 18 (3): 364–69. https://doi.org/10.1007/s12613-011-0448-3. Sheoran, A. S., and V. Sheoran. 2006. “Heavy Metal Removal Mechanism of Acid Mine Drainage in Wetlands: A Critical Review.” Minerals Engineering 19 (2): 105–16. https://doi.org/10.1016/j.mineng.2005.08.006. Singh, Nakshatra. 2018. “Fly Ash-Based Geopolymer Binder: A Future Construction Material.” Minerals 8 (7): 299. https://doi.org/10.3390/min8070299. Škvára, František, Tomás Jílek, and Lubomír Kopecký. 2005. “Geopolymer Materials Based on Fly Ash.” Ceramics - Silikaty 49 (3): 195–204. Wang, Shun-Cai, Zhi-cheng Wei, Yan Zhou, and Fang-Han Wang. 2015. “A Research on the Leaching Toxicity of the Solid Waste of a Pb-Zn Mine.” Journal of Residuals Science & Technology 12 (1): 25–30. https://doi.org/10.12783/issn.2376-578X/12/1/4. Wei, Yan, Liao Jun-Cheng, Wang Shu-Mei, Liang Sheng-Wang, and Yu Jiang-Yong. 2016. “The Ftir Fingerprint of Gypsum Fibrosum.” Acta Medica Mediterranea 32 (SpecialIssue1): 607–11. Xiaolong, Zhang, Zhang Shiyu, Liu Hui, and Zhao Yingliang. 2021. “Disposal of Mine Tailings via Geopolymerization.” Journal of Cleaner Production 284 (xxxx): 124756. https://doi.org/10.1016/j.jclepro.2020.124756. Xu, H., van Deventer, J. 2000. “The Geopolymerisation of Alumino-Silicate Minerals.” Int. J. Miner. Process. 59: 247–66. Xu, Hua, and Jannie S.J. Van Deventer. 2003. “Effect of Source Materials on Geopolymerization.” Industrial and Engineering Chemistry Research 42 (8): 1698–1706. https://doi.org/10.1021/ie0206958. Zhang, Lianyang, Saeed Ahmari, and Jinhong Zhang. 2011. “Synthesis and Characterization of Fly Ash Modified Mine Tailings-Based Geopolymers.” Construction and Building Materials 25 (9): 3773–81. https://doi.org/10.1016/j.conbuildmat.2011.04.005. Zhang, Wei, Jinghua Long, Xueru Zhang, Weining Shen, and Zhongyi Wei. 2020. “Pollution and Ecological Risk Evaluation of Heavy Metals in the Soil and Sediment around the HTM Tailings Pond, Northeastern China.” International Journal of Environmental Research and Public Health 17 (19): 1–10. https://doi.org/10.3390/ijerph17197072. Zhao, Shujie, Faheem Muhammad, Lin Yu, Ming Xia, Xiao Huang, Binquan Jiao, Ning Lu, and Dongwei Li. 2019. “Solidification/Stabilization of Municipal Solid Waste Incineration Fly Ash Using Uncalcined Coal Gangue–Based Alkali-Activated Cementitious Materials.” Environmental Science and Pollution Research 26 (25): 25609–20. https://doi.org/10.1007/s11356-019-05832-5. Zhuang, Xiao Yu, Liang Chen, Sridhar Komarneni, Chun Hui Zhou, Dong Shen Tong, Hui Min Yang, Wei Hua Yu, and Hao Wang. 2016. “Fly Ash-Based Geopolymer: Clean Production, Properties and Applications.” Journal of Cleaner Production 125 (July): 253–67. https://doi.org/10.1016/j.jclepro.2016.03.019. Tables Table.1 Chemical Compositions of class F fly ash and Lead-Zinc mine tailing Element (wt %) SiO 2 Al 2 O 3 Fe 2 O 3 MnO 2 CaO MgO K 2 O Na 2 O P 2 O 5 TiO 2 SO 3 LOI FA 40.15 35.50 7.57 0.11 8.33 1.21 1.48 1.10 0.37 1.51 0.70 1.64 MT 18.83 1.61 6.20 9.12 29.49 2.83 0.15 0.12 0.03 0.06 2.30 28.96 Table.2 Chemical Composition of FA and MT − Minor and Trace Elements (ppm) Element (ppm) As Mo Pb Rb Th U Y Zr Ga Cu Co Ni Cr V FA 21.3 14.4 101.4 47.2 32.3 12.5 64.5 433.8 67.4 75.1 25.4 45.5 61.7 182.1 MT 151.9 0.7 622.4 10.6 11.5 7.5 63.6 28.7 26.6 52.9 1.4 10.1 24.3 97 Table.3 Mixture Design for Geopolymerization of Mine Tailings S (NaOH) Specimen Code Waste materials (g) Ratios F G M Si/Al Na/Al Liquid/Solid W/S 5 M FMS-01 200 - 0 1.13 0.14 0.27 - FMS-02 150 - 50 1.29 0.18 0.27 - FMS-03 100 - 100 1.59 0.25 0.27 - FMS-04 50 - 150 2.39 0.43 0.27 - FMS-05 0 - 200 11.71 2.57 0.27 - 10 M FMS-01a 200 - 0 1.13 0.26 0.27 - FMS-02a 150 - 50 1.29 0.33 0.27 - FMS-03a 100 - 100 1.59 0.47 0.27 - FMS-04a 50 - 150 2.39 0.83 0.27 - FMS-05a 0 - 200 11.71 5.07 0.27 - 5 M FMSW-01 200 - 0 1.13 0.14 0.52 1.08:1 FMSW-02 150 - 50 1.29 0.18 0.52 1.08:1 FMSW-03 100 - 100 1.59 0.25 0.52 1.08:1 FMSW-04 50 - 150 2.39 0.43 0.52 1.08:1 FMSW-05 0 - 200 11.71 2.57 0.52 1.08:1 5 M FGMS-01 200 10 0 1.13 0.14 0.32 - FGMS-02 150 10 50 1.29 0.18 0.32 - FGMS-03 100 10 100 1.59 0.25 0.32 - FGMS-04 50 10 150 2.39 0.43 0.32 - FGMS-05 0 10 200 11.71 2.57 0.32 - 5 M FGMS-01a 200 20 0 1.13 0.14 0.37 - FGMS-02a 150 20 50 1.29 0.18 0.37 - FGMS-03a 100 20 100 1.59 0.25 0.37 - FGMS-04a 50 20 150 2.39 0.43 0.37 - FGMS-05a 0 20 200 11.71 2.57 0.37 - 5 M FGMSW-01 200 10 0 1.23 2.95 0.57 1.08:1 FGMSW-02 150 10 50 1.41 3.87 0.57 1.08:1 FGMSW-03 100 10 100 1.77 5.62 0.57 1.08:1 FGMSW-04 50 10 150 2.73 10.32 0.57 1.08:1 FGMSW-05 0 10 200 13.79 64.55 0.57 1.08:1 5 M FGMSW-01a 200 20 0 1.23 2.95 0.62 1.08:1 FGMSW-02a 150 20 50 1.41 3.87 0.62 1.08:1 FGMSW-03a 100 20 100 1.77 5.62 0.62 1.08:1 FGMSW-04a 50 20 150 2.73 10.32 0.62 1.08:1 FGMSW-05a 0 20 200 13.79 64.55 0.62 1.08:1 10 M FGMSW-01b 200 20 0 1.23 3.07 0.62 1.08:1 FGMSW-02b 150 20 50 1.41 4.02 0.62 1.08:1 FGMSW-03b 100 20 100 1.77 5.84 0.62 1.08:1 FGMSW-04b 50 20 150 2.73 10.72 0.62 1.08:1 FGMSW-05b 0 20 200 13.79 67.05056 0.62 1.08:1 Table 4. Table of the samples that have the higher values of UCS of the different series. Alkali activator content MT content/ other aggregates 0% 25% 50% 75% 100% NaOH 5M FMS-03a FMS-04 NaOH 10M FMS-01a FMS-02a FMS-03 FMS-04a WG/ NaOH 2N/ 5M FMSW-01 FMSW-02 FMSW-03 FMSW-04 FMSW-05 NaOH 5M Gypsum 10g FGMS-02 FGMS-03 NaOH 5M Gypsum 20g FGMS-02a FGMS-03a WG/ NaOH 2N/ 5M Gypsum 10g FGMSW-02 FGMSW-03 WG/ NaOH 2N/ 5M Gypsum 20g FGMSW-01a FGMSW-03a WG/ NaOH 2N/ 10M Gypsum 20g FGMSW-01b FGMSW-03b FGMSW-04b FGMSW-05b Table 5. Infrared Characteristic Bands Identified in FA and Geopolymers Specimens Wave number (cm -1 ) Characteristic bands 460 - 550 plane and bending vibrations of Al-O/Si-O 603-618 Functional group of AlO 2 817-878 -1456 -CO 3 vibrations in CaCO 3 970 Stretching vibration mode of SI-O in CSH gel 1420-1472 Si-O vibrations 1660-1782 Bending mode of H-O-H 2505-2519 C-O vibrations in CO 2 constrained in amorphous phase 3475 -3645 O-H stretching vibration of portlandite Cite Share Download PDF Status: Under Review Version 1 posted Reviews received at journal 21 Oct, 2021 Reviewers invited by journal 21 Oct, 2021 Editor assigned by journal 19 Oct, 2021 First submitted to journal 30 Sep, 2021 You are reading this latest preprint version Research Square lets you share your work early, gain feedback from the community, and start making changes to your manuscript prior to peer review in a journal. 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Also discoverable on Platform About Our Team In Review Editorial Policies Advisory Board Help Center Resources Author Services Accessibility API Access RSS feed Manage Cookie Preferences © Research Square 2026 | ISSN 2693-5015 (online) Privacy Policy Terms of Service Do Not Sell My Personal Information {"props":{"pageProps":{"initialData":{"identity":"rs-996321","acceptedTermsAndConditions":true,"allowDirectSubmit":false,"archivedVersions":[],"articleType":"Research Article","associatedPublications":[],"authors":[{"id":58196412,"identity":"9ee87764-9a84-4f4c-86a6-aa977364df6f","order_by":0,"name":"ALSENY BAH","email":"data:image/png;base64,iVBORw0KGgoAAAANSUhEUgAAAZAAAAAyAQMAAABI0h/eAAAABlBMVEX///8AAABVwtN+AAAACXBIWXMAAA7EAAAOxAGVKw4bAAABEUlEQVRIiWNgGAWjYDACdjB5gMGAvQHMSoAIs+HRwgzTwnOAsQGshY1oLRIJRGrhb2Z/+Liw7Y68ueTz5495GOrydOf3GDB8KDvMwD+7AasWicM8xsYz254Z7pydY9jMw3C42OwYjwHjjHOHGSTuHMBuzWEeNmnetsOMG27nMAK1HEjcBtTCDBQBORWrDvnD7M9/AxXYb7h5/CFQSx1Ey188WgwOM5iBzEzccIMB5DBmiBZGPFoMgX6R5jn3LHnDmRzDmXMMDgO1pBUc7DmXziNxA7sWuePtDz/zlN2x3XD8+IMPbyqADjt8eOODH2XWcvwzsGsBA0Z4LBhAqANAzINbPQj8wS89CkbBKBgFIxwAAIllYvB751slAAAAAElFTkSuQmCC","orcid":"https://orcid.org/0000-0002-8613-942X","institution":"Shanghai Maritime University","correspondingAuthor":true,"submittingAuthor":false,"prefix":"","firstName":"ALSENY","middleName":"","lastName":"BAH","suffix":""},{"id":58196413,"identity":"f4657393-7515-4eb6-8b8d-9be55e63cdd8","order_by":1,"name":"Andrea ORTIZ Ramos","email":"","orcid":"","institution":"Nanjing University of Information Science and Technology","correspondingAuthor":false,"submittingAuthor":false,"prefix":"","firstName":"Andrea","middleName":"ORTIZ","lastName":"Ramos","suffix":""},{"id":58196414,"identity":"97880e07-eb81-4585-a4f0-cc9957d33f55","order_by":2,"name":"Feng Daolun","email":"","orcid":"","institution":"Shanghai Maritime University","correspondingAuthor":false,"submittingAuthor":false,"prefix":"","firstName":"Feng","middleName":"","lastName":"Daolun","suffix":""},{"id":58196415,"identity":"feb3d9c6-6c2b-43e9-b1f3-81f996ecd63d","order_by":3,"name":"jie Jin","email":"","orcid":"","institution":"Nanjing University of Information Science and Technology","correspondingAuthor":false,"submittingAuthor":false,"prefix":"","firstName":"jie","middleName":"","lastName":"Jin","suffix":""},{"id":58196416,"identity":"82220dd1-aa97-4ebd-896b-9642bbd20a8d","order_by":4,"name":"Alhassane Bah","email":"","orcid":"","institution":"Kunming University of Science and Technology","correspondingAuthor":false,"submittingAuthor":false,"prefix":"","firstName":"Alhassane","middleName":"","lastName":"Bah","suffix":""},{"id":58196417,"identity":"85a98474-072c-481d-9c8e-e1740bf28e20","order_by":5,"name":"Feihu Li","email":"","orcid":"","institution":"Nanjing University of Information Science and Technology","correspondingAuthor":false,"submittingAuthor":false,"prefix":"","firstName":"Feihu","middleName":"","lastName":"Li","suffix":""}],"badges":[],"createdAt":"2021-10-19 17:11:49","currentVersionCode":1,"declarations":"","doi":"10.21203/rs.3.rs-996321/v1","doiUrl":"https://doi.org/10.21203/rs.3.rs-996321/v1","draftVersion":[],"editorialEvents":[],"editorialNote":"","failedWorkflow":false,"files":[{"id":14919970,"identity":"2b5cc61a-48a3-4649-8b8e-59a4062b6f19","added_by":"auto","created_at":"2021-10-26 20:04:08","extension":"png","order_by":1,"title":"Figure 1","display":"","copyAsset":false,"role":"figure","size":80035,"visible":true,"origin":"","legend":"XRD patterns of (a) fly ash, (b) mine tailing, and (c) FGD gypsum. Note: B − Brushite (JCPDS #09-0077), C − Calcite (JCPDS #05-0586), G − Gypsum (JCPDS #33-0311), H − Gehlenite (JCPDS #35-0755), M − Mullite (JCPDS #15-0776), Q − Quartz (JCPDS #46-1045), S − Sphalerite (JCPDS #05-0566).","description":"","filename":"fig1.png","url":"https://assets-eu.researchsquare.com/files/rs-996321/v1/15a25c3d634ca9336e99d2a0.png"},{"id":14920348,"identity":"8245ec50-0235-48fd-bcae-f7f73098abb0","added_by":"auto","created_at":"2021-10-26 20:07:08","extension":"png","order_by":2,"title":"Figure 2","display":"","copyAsset":false,"role":"figure","size":119793,"visible":true,"origin":"","legend":"FTIR spectra of FA, MT and GY","description":"","filename":"fig2.png","url":"https://assets-eu.researchsquare.com/files/rs-996321/v1/18fe699f269d3510af048086.png"},{"id":14920676,"identity":"6b785b4c-ad37-40cd-bb96-28e3769ba849","added_by":"auto","created_at":"2021-10-26 20:13:08","extension":"png","order_by":3,"title":"Figure 3","display":"","copyAsset":false,"role":"figure","size":428016,"visible":true,"origin":"","legend":"SEM Images of (a) Fly Ash, (b, c) Mine Tailing, And (d) Gypsum. ","description":"","filename":"fig3.png","url":"https://assets-eu.researchsquare.com/files/rs-996321/v1/58b5c7804438b01fa6867c7f.png"},{"id":14919973,"identity":"7e16f67e-18a4-4e53-be7d-a3bae7623d0c","added_by":"auto","created_at":"2021-10-26 20:04:08","extension":"png","order_by":4,"title":"Figure 4","display":"","copyAsset":false,"role":"figure","size":46393,"visible":true,"origin":"","legend":"Particle Size Distribution of Mine tailings\nNote: B − Brushite (JCPDS #09-0077), C − Calcite (JCPDS #05-0586), G − Gypsum (JCPDS #33-0311), H − Gehlenite (JCPDS #35-0755), M − Mullite (JCPDS #15-0776), Q − Quartz (JCPDS #46-1045), S − Sphalerite (JCPDS #05-0566). ","description":"","filename":"fig4.png","url":"https://assets-eu.researchsquare.com/files/rs-996321/v1/d5acb1ed6cdc191cc4e9f380.png"},{"id":14920473,"identity":"4881b4c8-dd5d-42ee-9712-1208c9d6e846","added_by":"auto","created_at":"2021-10-26 20:10:08","extension":"png","order_by":5,"title":"Figure 5","display":"","copyAsset":false,"role":"figure","size":164782,"visible":true,"origin":"","legend":"aging period of FMS-0xa geopolymer specimens at 10M NaOH with different proportion of FA","description":"","filename":"fig5.png","url":"https://assets-eu.researchsquare.com/files/rs-996321/v1/583916ad865014e600a74fb1.png"},{"id":14920474,"identity":"9fd233fb-88d0-4a64-b671-a8ce59545a2b","added_by":"auto","created_at":"2021-10-26 20:10:08","extension":"png","order_by":6,"title":"Figure 6","display":"","copyAsset":false,"role":"figure","size":945456,"visible":true,"origin":"","legend":"XRD patterns of the specimen a FMS-01a (100% FA) b) FGMS-02 (75% FA) c) FGMSW-02 (75% FA), d) FGMSW-01a (100% FA); d) FGMSW-03b (50% FA), which described data belongs to 7, 14 and 28 days after their activation with sodium hydroxide 5M and 10M. Where C= Corundum Al2O3, Cc= Calcite CaCO3, G=Gypsum CaSO4 2H2O, M= Mullite Al6Si2O13, Q= quartz SiO2, Ss=Sodium silicate Na2(SiO3), Sh=Calcium Silicate hydritade Ca1.5Si0.5 xH2O, Ch= Chabazite, J= Jadeite, A=Anhydrite CaSO4","description":"","filename":"fig6.png","url":"https://assets-eu.researchsquare.com/files/rs-996321/v1/7511213e51af303c77abf781.png"},{"id":14920350,"identity":"04d131f8-7a4e-4ff1-be1f-78ab54856cdb","added_by":"auto","created_at":"2021-10-26 20:07:08","extension":"png","order_by":7,"title":"Figure 7","display":"","copyAsset":false,"role":"figure","size":605419,"visible":true,"origin":"","legend":"Scanning Electron Microscopy of geopolymer specimens (FGMSW-3b) with 100% FA, 20g of Gy at 10 M of NaOH cured for: (a) 7 days, (b) 14 days and (c) 28 days curing.","description":"","filename":"fig7.png","url":"https://assets-eu.researchsquare.com/files/rs-996321/v1/fe231699a0ef72de82ff99b0.png"},{"id":14920351,"identity":"b73cf811-4811-4fca-b800-171210675aa1","added_by":"auto","created_at":"2021-10-26 20:07:08","extension":"png","order_by":8,"title":"Figure 8","display":"","copyAsset":false,"role":"figure","size":484136,"visible":true,"origin":"","legend":"Scanning Electron Microscopy of geopolymer specimens (FMS-02 and FMS-02a) at the same magnification with 100% FA at different concentration of NaOH (a) 5M and (b) 10 M of NaOH cured for 14 days curing. ","description":"","filename":"fig8.png","url":"https://assets-eu.researchsquare.com/files/rs-996321/v1/ee1132072b248845ddc63f61.png"},{"id":14920355,"identity":"53430654-69dc-4e7f-ac72-5c8c17895dee","added_by":"auto","created_at":"2021-10-26 20:07:08","extension":"png","order_by":9,"title":"Figure 9","display":"","copyAsset":false,"role":"figure","size":504497,"visible":true,"origin":"","legend":"SEM images of geopolymer specimens (FMS-01 and FMSW-01) at low magnification with 100% FA at 5M of NaOH cured for 7 days curing activated with (c) only NaOH and (d) both NaOH and Na-Silicate","description":"","filename":"fig9.png","url":"https://assets-eu.researchsquare.com/files/rs-996321/v1/91db735e70d8a542c146a804.png"},{"id":14920475,"identity":"61b4669e-5346-4879-9202-4bc394534ba4","added_by":"auto","created_at":"2021-10-26 20:10:08","extension":"png","order_by":10,"title":"Figure 10","display":"","copyAsset":false,"role":"figure","size":807818,"visible":true,"origin":"","legend":"Scanning Electron Microscopy of geopolymer specimens (FGMS-02 and FGMS-02a) with low magnification with 75% FA at 5M NaOH at different content of Gypsum: (a) 0g , (b) 10 g and (c) 20g of Gypsum cured for 7 days curing. ","description":"","filename":"fig10.png","url":"https://assets-eu.researchsquare.com/files/rs-996321/v1/3ab26cae89a01cc84b3acd35.png"},{"id":14919981,"identity":"6a76fd3b-8557-4c2c-bf9e-65435ffe0d9d","added_by":"auto","created_at":"2021-10-26 20:04:08","extension":"png","order_by":11,"title":"Figure 11","display":"","copyAsset":false,"role":"figure","size":1069537,"visible":true,"origin":"","legend":"FTIR of the recipe after 7, 14 and 28 days, where a) FMS-01a (100% FA), b) FGMS-02a (75% FA), c) FGMSW-02(75% FA), d) FGMSW-02(75% FA), e) FGMSW-03b (50% FA),","description":"","filename":"fig11.png","url":"https://assets-eu.researchsquare.com/files/rs-996321/v1/4220b3017121fb9b8b897f1c.png"},{"id":14919976,"identity":"cd7c1f29-4bf7-4fbe-bd70-b212ba0dad95","added_by":"auto","created_at":"2021-10-26 20:04:08","extension":"png","order_by":12,"title":"Figure 12","display":"","copyAsset":false,"role":"figure","size":410300,"visible":true,"origin":"","legend":"(a) the compressive strength with NaOH concentration (5 and 10M) at different proportion of FA and (b) compressive strength(UCS) with FA content at various NaOH concentration and (c) UCS vs Gypsum (0, 10 and 20g) at different FA content and at 5M NaOH cured for 7 days.","description":"","filename":"fig12.png","url":"https://assets-eu.researchsquare.com/files/rs-996321/v1/6a6087fb769c3b753f664e38.png"},{"id":14920353,"identity":"ebc97313-b4c8-41fa-8133-b4e5cd33ac11","added_by":"auto","created_at":"2021-10-26 20:07:08","extension":"png","order_by":13,"title":"Figure 13","display":"","copyAsset":false,"role":"figure","size":1896412,"visible":true,"origin":"","legend":"(a). Geopolymers FMS, FMSW and FMS-00a\n(b). Geopolymers FGMS and FGMS-00a\n(c). Geopolymers FGMSW, FGMSW-00a and FGMSW-00b","description":"","filename":"fig13.png","url":"https://assets-eu.researchsquare.com/files/rs-996321/v1/8f8b9728c23494b578b4d4b0.png"},{"id":14920677,"identity":"400dd894-aedb-45fb-9df8-1f9eaceb1990","added_by":"auto","created_at":"2021-10-26 20:13:17","extension":"pdf","order_by":0,"title":"","display":"","copyAsset":false,"role":"manuscript-pdf","size":5445197,"visible":true,"origin":"","legend":"","description":"","filename":"manuscript.pdf","url":"https://assets-eu.researchsquare.com/files/rs-996321/v1/a560fcb9-a503-4e1a-b635-a2d91193f5fd.pdf"}],"financialInterests":"","formattedTitle":"\u003cp\u003eLead-Zinc Mine Tailings Valorization Through Fly Ash-Based Geopolymer for Building Material: Synthesis, Microstructure, and Mechanical Properties\u003c/p\u003e","fulltext":[{"header":"1. Introduction","content":"\u003cp\u003eValorising mine tailings through geopolymerisation to meet construction demand is a sustainable and environmentally friendly approach. Environmental problems have become a worldwide concern. In addition, Heavy metals such as lead (Pb), zinc (Zn), Copper (Cu) are among the most dangerous pollutants which lead to the death of the living organism (Humans, animals) through environmental pollution that occurs by the exploitation of mineral resources. Crushed rocks, as well as effluents from mineral exploration, make up mine tailings. These are the byproducts left over from extracting products from mining ores that have never been a 100 percent effective system; not all agents and chemicals used are recoverable. Mine tailings are also discarded products that provide no economic advantage to the mineral miners at the time of manufacture. Hence they are often kept in the most cost-effective manner possible to meet obligations. (Xiaolong et al. \u003cspan citationid=\"CR33\" class=\"CitationRef\"\u003e2021\u003c/span\u003e). On the other side, Every year, the issue of long-term dumping of tailings (M.T.) that pile in tailing ponds and mining waste landfills becomes increasingly pressing.(Ngole-Jeme and Fantke 2017; Kinnunen et al. \u003cspan citationid=\"CR14\" class=\"CitationRef\"\u003e2018\u003c/span\u003e; Krishna et al. \u003cspan citationid=\"CR18\" class=\"CitationRef\"\u003e2021\u003c/span\u003e). Besides, it occurs as a result of higher manufacturing quantities in mining and metallurgical entities, as well as the absence of meaningful waste-handling techniques. However, also, it is stated, particularly in developed countries, tightening environmental regulations. The continuous inflow of toxic substances, radioactive elements, and other harmful substances into the ecosystem, polluting the soil, is indeed a serious outcome of tailings storage. (W. Zhang et al. \u003cspan citationid=\"CR37\" class=\"CitationRef\"\u003e2020\u003c/span\u003e), water (Sheoran and Sheoran \u003cspan citationid=\"CR28\" class=\"CitationRef\"\u003e2006\u003c/span\u003e)and air (Csavina et al. \u003cspan citationid=\"CR4\" class=\"CitationRef\"\u003e2012\u003c/span\u003e).\u003c/p\u003e \u003cp\u003eThe use of M.T. as a major contributor to alkali-activated materials and geopolymers represents an attractive trend for their application. (Kiventer\u0026auml; et al. \u003cspan citationid=\"CR15\" class=\"CitationRef\"\u003e2020\u003c/span\u003e). This process is an opportunity not just to reduce the dynamics of M.T. accretion and decrease the occurrence of industrial contamination, but it also integrates the benefits of geopolymer technology related to the diminution of carbon dioxide liberation into the atmosphere, the potential for utilizing certain technogenic aluminosilicate waste, and the adaptability of the characteristics of geopolymers as an overall building material (Ma, Awang, and Omar 2018; Hassan, Arif, and Shariq \u003cspan citationid=\"CR8\" class=\"CitationRef\"\u003e2019\u003c/span\u003e; Lazorenko et al. \u003cspan citationid=\"CR19\" class=\"CitationRef\"\u003e2020\u003c/span\u003e; Krishna et al. \u003cspan citationid=\"CR18\" class=\"CitationRef\"\u003e2021\u003c/span\u003e)\u003c/p\u003e \u003cp\u003eSustainable management of tailings through geopolymers has increasingly attracted the attention of a diverse group of experts, including general practitioners. Numerous research has indeed been reported, highlighting an attempt to improve understanding of the mechanics of tailings geopolymerization to control the characteristics of MT-based geopolymers for long-term development (Moukannaa et al. \u003cspan citationid=\"CR22\" class=\"CitationRef\"\u003e2019\u003c/span\u003e).\u003c/p\u003e \u003cp\u003eOwing to its appealing attributes like superior mechanical properties, enhanced heat resistance, prolonged durability, and reasonable manufacturing costs, geopolymers have indeed been extensively explored as a Portland cement replacement in recent years (Moukannaa et al. \u003cspan citationid=\"CR22\" class=\"CitationRef\"\u003e2019\u003c/span\u003e)\u003c/p\u003e \u003cp\u003eIn order to find sustainable solutions to address these issues, some environment materials such as \u0026laquo; Geopolymers \u0026raquo; by geopolymerization process that engages chemical reaction of aluminosilicates oxides with Alkali polysilicates yielding polymeric Si-O-Al bonds (Davidovits \u003cspan citationid=\"CR5\" class=\"CitationRef\"\u003e1991\u003c/span\u003e) and some techniques such as \u0026laquo; Solidification / Stabilization technology \u0026raquo; have been developed to encapsulate toxic chemical and radioactive waste. In order to diminish the quantity of fly ash from a power plant to be disposed of in the world such as the Czech Republic, the fly ash has to be added to cement and concretes(Škv\u0026aacute;ra, J\u0026iacute;lek, and Kopeck\u0026yacute; 2005; Zhao et al. \u003cspan citationid=\"CR38\" class=\"CitationRef\"\u003e2019\u003c/span\u003e), in addition, using alkaline solutions reagents such as NaOH, or Na\u003csub\u003e2\u003c/sub\u003eSiO\u003csub\u003e3\u003c/sub\u003e contribute strongly to geopolymerization process as said (Rattanasak et al. 2011), that geopolymerization happens in alkaline solution, especially in the sodium hydroxide/sodium silicate system.\u003c/p\u003e \u003cp\u003eGypsum has been utilized in some recent studies to ameliorate the mechanical strength of fly ash-based geopolymers when activating the fly ash by sodium hydroxide(NaOH) and Sodium silicate(Na-silicate) (Jun et al., 2015). CaSO\u003csub\u003e4\u003c/sub\u003e or gypsum is a suitable additive due to its availability in the market with acceptable cost (Boonserm et al., \u003cspan citationid=\"CR2\" class=\"CitationRef\"\u003e2012\u003c/span\u003e).\u003c/p\u003e \u003cp\u003eThis research, therefore, evaluates the performance of raw materials ( Fly Ash (F.A.), Mine Tailings(M.T.), and Gypsum(Gy)) and the Alkali reagents ( NaOH and Sodium Silicate) to study the mechanical property and microstructure of geopolymers. In order to achieve this research, the XRF, XRD diffractometer, FTIR, SEM imaging, and the Unconfined Compressive Strength (UCS) analysis were performed to investigate the Geopolymer-based solidification of Lead-Zinc mine tailings.\u003c/p\u003e"},{"header":"2. Materials And Methods","content":"\u003cdiv id=\"Sec3\" class=\"Section2\"\u003e \u003ch2\u003e2.1. Materials\u003c/h2\u003e \u003cp\u003eBased on the availability, affordability, and applicability, the following materials were chosen to conduct this research, including fly ash (F.A.), gypsum (G.Y.), and mine tailings (M.T.), Sodium hydroxide (NaOH), sodium silicate, and distilled water. Both the F.A. and the G.Y. were obtained from Jiangsu Nanre Power Generation Co., Ltd. (Nanjing, China), M.T. was achieved from Nanjing Yinmaoqianxin Mining Industry Co., Ltd. (Nanjing, China). 96% NaOH pellets were supplied by Shanghai Macklin Biochemical Co., Ltd., and sodium silicate solution (SiO\u003csub\u003e2\u003c/sub\u003e 13.36%; Na\u003csub\u003e2\u003c/sub\u003eO 29.84%) was obtained from Ganjiashan Yourui Refractories Co., Ltd. Sodium hydroxide and sodium silicate were selected as alkaline agents due to the sodium geopolymers had higher mechanical strength than potassium geopolymers ( Rao et al., 2015\u003cspan type=\"BoldItalic\" class=\"BoldItalic\" name=\"Emphasis\"\u003e)\u003c/span\u003e. The chemical compositions of both F.A. and M.T. were obtained by the fused X-ray fluorescence (XRF) method, and the results are shown in Tables 1 \u0026amp;2. The X-ray diffraction (XRD) analysis of the raw materials and geopolymers specimens was performed on an XRD-6100 diffractometer (Shimadzu, Japan), the Fourier Transform Infrared Spectroscopy (FTIR) data were collected on Is5 infrared spectrometer, and The scanning electron micrograph (SEM) of the raw materials and geopolymers specimens were measured by using a Hitachi japan SU1510 microscope.\u003c/p\u003e \u003c/div\u003e \u003cdiv id=\"Sec4\" class=\"Section2\"\u003e \u003ch2\u003e2.2. Synthesis of Geopolymer\u003c/h2\u003e \u003cp\u003eTo achieved the objective of this study, forty (40) geopolymer recipes were performed. Samples were prepared by blending the dry reagents about 7 min then gradually adding the alkaline liquid such as NaOH at 5 -10M and sodium silicate in the different recipes) and further mixing for 5 min. The alkaline solution was prepared by blending the sodium hydroxide solution to de-ionized water (DIW) at 5 M and 10 M with sodium hydroxide flakes and stirring for at least 5 min. Due to the heat generation, adequate time was required for the solution to cool down to room temperature one day before it was used; however, the NaOH solution and sodium silicate were injected into the dry mixture separately. The samples were cast in 20x 20 x 20 mm cubes at room temperature for 72 hours before being removed from the molds and kept for another four days at room temperature. Two measurements of the 12 cubes made to measure the compressive strength of 7, 14, and 28 days will be taken. Table (3) presents the mixture design of the different samples performed in the study to find the best recipe to encapsulate the toxic metals, where the labels will represent using letters which are represented by fly ash (F), gypsum (G), mine tailing (M), sodium hydroxide (S), water glass (W). Where W/S expresses the ratio between sodium hydroxide (S) with a water glass or sodium silicate soln (W) were added in some of the mixes. In addition, silica or quartz is the principal impurity in fly ashes. In geopolymerization, silicate is an important activator, so Si / Al ratios higher than 2.5 were commonly investigated in the literature. In this work, the Si / Al ratios of all specimens having in their composition fly ash vary from 1 to 2.54, coinciding with the work of Davidovits and his co-workers, where they concluded that the Si / Al ratio in fly ash-based geopolymers should be between 1 and 3( Rao et al., \u003cb\u003e2015\u003c/b\u003e).\u003c/p\u003e \u003cp\u003eOn the other hand, the specimens with a high Si/Al ratio that varies between 10.33 and 12.25 belong to the 100% of M.T. in the composition. In some works, gypsum applications can reduce porosity; however, an excess amount of gypsum may cause volume instability within the material. As fly ash is an industrial waste material, varying impurities of different chemical substances may be found within fly ash, which resultantly may cause significant changes in reactions; however, gypsum was also added with other ingredients such as calcium silicates and other types of sodium silicates(Jun et al., 2015), that is why in some recipes was added a portion of 10 or 20 grams of the gypsum.\u003c/p\u003e \u003cp\u003eThen the crystallization phase of geopolymers with the highest value of compressive strength\u003c/p\u003e \u003cp\u003ewas analyzed through FTIR and XRD machines.\u003c/p\u003e \u003c/div\u003e \u003cdiv id=\"Sec5\" class=\"Section2\"\u003e \u003ch2\u003e2.3. Mechanical Property Test\u003c/h2\u003e \u003cp\u003eThe unconfined compressive strength (UCS) test is known and utilized to measure geopolymers' solidification effectiveness. It is generally accepted that a UCS of 0.35 MPa (psi) is appropriate for the physical integrity of solidification/ stabilization waste type to withstand standards landfill overburden pressures. (Choi et al., \u003cspan citationid=\"CR3\" class=\"CitationRef\"\u003e2009\u003c/span\u003e).\u003c/p\u003e \u003cp\u003e20 x 20 x 20 mm cube specimens were cast for the strength test on mortar at 3, 7, and 28 days UCS. The mortar specimens were cast and cured at 25\u0026ndash;30\u0026deg;C room temperature. The molds have been covered with protective plastic sheets shortly after casting and de-molded after 24 hours. The compression tests were carried out using a load compression testing machine. At least three samples were tested for every age, as well as the average of the recorded UCS values is being used.\u003c/p\u003e \u003c/div\u003e \u003cdiv id=\"Sec6\" class=\"Section2\"\u003e \u003ch2\u003e2.4. Geopolymer Microstructure Analysis\u003c/h2\u003e \u003cp\u003eTo understand the geopolymers' properties, physical observation and Methods of mechanical detection were utilized upon selected geopolymers products based on their performance in terms of compressive strength results. FTIR test results were acquired and used an ASTM Standard (IS5 infrared spectrometer) from Thermo Fisher USA and a Shimadzu (Japan) XRD machine model (XRD-6100) with an objective function of (20-60KV and 2-80mA) for the phasing characteristics. Furthermore, morphological properties of geopolymer samples were studied using Hitachi (Japan) SU1510 SEM equipment.\u003c/p\u003e \u003c/div\u003e"},{"header":"3. Results And Discussion","content":"\u003cdiv id=\"Sec8\" class=\"Section2\"\u003e\n\u003ch2\u003e3.1. Characterization of Fly Ash, Mine Tailing, and Gypsum\u003c/h2\u003e\n\u003cp\u003eTo comprehend the effectiveness of raw resources, including mine tailings, fly ash, and gypsum, in forming a geopolymer, it is necessary to understand their physical and chemical properties, including chemical compositions, mineralogical composition, and size distribution.\u003c/p\u003e\n\u003cp\u003eTable 1\u0026amp;2 shows the chemical composition of fly ash (F.A.) and mine tailings (M.T.) that consisted mostly in a vitreous phase comprising 40.15% and 35.50% of SiO\u003csub\u003e2\u003c/sub\u003e and Al\u003csub\u003e2\u003c/sub\u003eO\u003csub\u003e3\u003c/sub\u003e, respectively. Also another oxide in lower percentages including CaO, Fe\u003csub\u003e2\u003c/sub\u003eO\u003csub\u003e3\u003c/sub\u003e, and MnO\u003csub\u003e2\u003c/sub\u003e to 8.33%, 7.57%, and 0.11%, respectively. The LOI limitations are 8% and 6% according to CSA A3001 for Type F fly ash and for Types CI and C.H. fly ashes, respectively; considering the acceptable limitations for LOI, the F.A. level is 1.64, allowing the specimen to be utilized for testing and obtaining a great outcome. Heavy metal quantities including Pb, Cu, Y, Cr, and As could also be found in F.A., as shown in Table 2. Fig.\u0026nbsp;\u003cspan class=\"InternalRef\"\u003e1\u003c/span\u003e shows the XRD patterns of fly ash composition that are utilized in this research. It is clear that the presence of the quartz is 7.9% and mullite 24.5%, which are the non-reactive crystalline phase, and the amorphous phase present in the F.A. is 67.6%. The distinctive shape of the original fly ash morphology is shown in Fig.\u0026nbsp;\u003cspan class=\"InternalRef\"\u003e3\u003c/span\u003e(a). It appears to be made up of nearly uniform spherical (cenospheres) vitreous fragments with diameters ranging from 2 to 14 m.\u003c/p\u003e\n\u003cp\u003eMine tailings mineralogy is largely dependent on the type of the original ore, minerals manufacturing techniques, as well as the level of deterioration during storing in tailings ponds. (Kossoff et al. \u003cspan class=\"CitationRef\"\u003e2014\u003c/span\u003e). Furthermore, The reactivity of prospective geopolymerization precursors is determined by the alkali solubility of silicon and aluminum, determined by their mineralogy. As a result, mine tailings' reactivity can be estimated based on their mineralogical features. (Xu, H., van Deventer \u003cspan class=\"CitationRef\"\u003e2000\u003c/span\u003e). Tables 1 \u0026amp; 2 display the mine tailings\u0026rsquo; chemical composition (major oxides and trace elements). It can be seen in these tables that M.T. consist mainly of Si, Fe, and Al, as shown by the major oxide composition of 18.83%, 29.49%, 9.12%, 6.20%, and 1.61% for SiO\u003csub\u003e2\u003c/sub\u003e, CaO, MnO\u003csub\u003e2,\u003c/sub\u003e Fe\u003csub\u003e2\u003c/sub\u003eO\u003csub\u003e3\u003c/sub\u003e, and Al\u003csub\u003e2\u003c/sub\u003eO\u003csub\u003e3\u003c/sub\u003e, respectively. The tailings also contain a lower concentration of heavy metal, which could confirm the results of the study \u0026ldquo;\u003cem\u003eA Research on the Leaching Toxicity of the Solid Waste of a Pb-Zn mine\u003c/em\u003e\u0026rdquo; of Wang et al. (Wang et al. \u003cspan class=\"CitationRef\"\u003e2015\u003c/span\u003e), in which the chemical study revealed that harmful component level in the mine tailings was low, indicating that there was no risk of pollution. As a result, it was determined that mine tailing specimens are not harmful substances. The predominant minerals included in mine tailings, according to XRD examination, are crystalline solids such as sphalerite, gehlenite, gypsum, calcite, brushite, and quartz, (Fig.\u0026nbsp;\u003cspan class=\"InternalRef\"\u003e1\u003c/span\u003e).For the last description of M.T., the bans around 3316cm-1 were attributed to loosely bound water (H-O-H), and the absorption band 1660 cm-1was induced by O-H stretching from adsorbed water. The band 1393 cm-1 is associated with symmetric stretching vibration from adsorbed CO2, and the band 1016 cm-1 was assigned to apical Si-O stretching and Si-O-Si stretching. The M.T particle size distribution is shown in Fig.\u0026nbsp;\u003cspan class=\"InternalRef\"\u003e4\u003c/span\u003e; roughly 42.50 percent of both the particulates are less than 60 m, with the remaining 5.56 to 9.41 wt percent having a size ranging from 60 to 200 m. Ultimately, the second-highest figure in size particle distribution is 13,02 wt percent of particles larger than 200 m. Fig.\u0026nbsp;\u003cspan class=\"InternalRef\"\u003e3\u003c/span\u003e(b,c) also depicts the M.T. amorphous crystals in various sizes. Because mine tailing particulates are angular, dried tailings have a higher strength angle. Since its magnitude is dependent on the mineral processing requirements, it is hard to extrapolate. (Xiaolong et al. \u003cspan class=\"CitationRef\"\u003e2021\u003c/span\u003e).\u003c/p\u003e\n\u003cp\u003eThe description of gypsum was compared with the band standards of the gypsum spectra, the peak around 3396 -3562 cm\u003csup\u003e\u0026minus;1\u003c/sup\u003e and 1623 cm\u003csup\u003e\u0026minus;1\u003c/sup\u003e own to the H-O *H. The S-O, which including the asymmetrical vibration, will be in the band 1139 cm-1; the bands 590 to 669 cm-1 represent the asymmetrical deformation vibration. (Wei et al. 2016). The SEM results of the gypsum and the varied forms and structures of both the particulates are shown in Fig.\u0026nbsp;\u003cspan class=\"InternalRef\"\u003e3\u003c/span\u003e (d).\u003c/p\u003e\n\u003cp\u003eThe FTIR spectra of F.A., G.Y., and M.T. are shown in Fig.\u0026nbsp;\u003cspan class=\"InternalRef\"\u003e2\u003c/span\u003e. At first, it will be described the bands of F.A. At 568 cm-1 is due to Al-O-Si symmetric stretching. For Si-O-Si asymmetric stretching is shown in the band at 1066 cm. The structural and geometric knowledge from SEM analysis of crystals helps us define the distinction between raw resources and geopolymers' crystallization.\u003c/p\u003e\n\u003c/div\u003e\n\u003cdiv id=\"Sec9\" class=\"Section2\"\u003e\n\u003ch2\u003e3.2. The Physical Characteristic of Geopolymers\u003c/h2\u003e\n\u003cp\u003eOnce the mixtures were done, bulks had different physical characteristics such as color, shape, and integrality. In Fig.\u0026nbsp;\u003cspan class=\"InternalRef\"\u003e13\u003c/span\u003e(a), (b), and (c), different series of geopolymers were shown, whose compositions are described in Table 3; all of them have a cubic shape with a dimension of 20 x 20 x 20 mm.\u003c/p\u003e\n\u003cp\u003eThe specimens labeled with the codes FMS-0x (x = 1, 2, 3, 4, and 5) have the following characteristics, the colors of these bulks vary from a gray color that little by little changes to a shade of brown by the increase in the amount of mine tailing respectively, the two last specimens of the series FMS-04 and FMS-05 do not conserve the initial cubic shape. The second series with the code FMSW-0x had the same variety of colors with the difference that are a little bit dark, as for its shapes are cubic but with a presence of cracking in the surface of all the series.\u003c/p\u003e\n\u003cp\u003eFinally, the series FMS-0xa, which were activated with NaOH at 10M, these series also presented a variety of color but little more intense compared to others, but that is caused by the increase of mine tailing in the mixture, but covered with a white layer that could be due to the interaction of sodium hydroxide with carbon dioxide. By simple observation, it was possible to determine the integrality order of this series of geopolymer specimens as follows:\u003c/p\u003e\n\u003cp\u003eFMS-01 \u0026gt; FMS-02 \u0026gt; FMS-03 \u0026gt; FMS-04 \u0026gt; FMS-05\u003c/p\u003e\n\u003cp\u003eFMSW-01 \u0026gt; FMSW -02 \u0026gt; FMSW -03 \u0026gt; FMSW -04 \u0026gt; FMSW -05\u003c/p\u003e\n\u003cp\u003eFMS-01a \u0026gt; FMS-02a \u0026gt; FMS-03a \u0026gt; FMS-04a \u0026gt; FMS-05a\u003c/p\u003e\n\u003cp\u003eThe specimen's codes FGMS-0x belong to the first line of Fig.\u0026nbsp;\u003cspan class=\"InternalRef\"\u003e12\u003c/span\u003e(a), the colors of these bulks vary from a gray to brown but FGMS-05, was covered with a white layer, cubic shapes with a presence of cracking in the surface of FGMS-03, -04 and -05, and also observed a light erosion at the corners of the cube in FGMS-05. In the second series with the code FGMS-0xa, the colors of the different bulks presented a grayscale and were observed a slight erosion in the cubic shapes. The integrality order of these series of geopolymer specimens are as follows:\u003c/p\u003e\n\u003cp\u003eFGMS-01 / FGMS-02 \u0026gt; FGMS-03 \u0026gt; FGMS-04 \u0026gt; FGMS-05\u003c/p\u003e\n\u003cp\u003eFGMS-01a \u0026gt; FGMS-02a \u0026gt; FGMS-03a \u0026gt; FGMS-04a \u0026gt; FGMS-05a\u003c/p\u003e\n\u003c/div\u003e\n\u003cdiv id=\"Sec10\" class=\"Section2\"\u003e\n\u003ch2\u003e3.3. Mechanical Property and Microstructure of Geopolymers\u003c/h2\u003e\n\u003cdiv id=\"Sec11\" class=\"Section3\"\u003e\n\u003ch2\u003e3.3.1 Mechanical Property of Geopolymers\u003c/h2\u003e\n\u003cp\u003eIn order to investigate and figure out the mechanical property of the geopolymer specimens, the effect of the curing time, sodium hydroxide (NaOH), Fly Ash (F.A.), and gypsum (Gy) on the Unconfined Compressive Strength (UCS) were performed based on some selected geopolymers matrix. Furthermore, Table \u003cspan class=\"InternalRef\"\u003e4\u003c/span\u003e summarizes the samples that have the higher values of UCS of the different series.\u003c/p\u003e\n\u003cdiv class=\"gridtable\"\u003e\u0026nbsp;\u003c/div\u003e\n\u003cdiv id=\"Sec12\" class=\"Section4\"\u003e\n\u003ch2\u003e3.3.1.1. Effect of Curing Time on Mechanical Strength\u003c/h2\u003e\n\u003cp\u003eThe role of curing time on the compressive strength (UCS) has been investigated with the proportion of F.A. (0%, 25%, 50%, 75%, 100%). Fig.\u0026nbsp;\u003cspan class=\"InternalRef\"\u003e5\u003c/span\u003e shows the result of curing time on the compressive strength for FMS-0xa geopolymer specimens at 10M NaOH. These mixtures were cured for different curing times, which are 7, 14, and 28 days. Only the FMS-05a mixture with 0% of F.A. decreased with the increase of curing time. The trends of FMS-04a with 25% of F.A. which to pass the days will decrease gradually with the increase of curing time but not completely to zero compared to the FMS-05a mixture. that showed the F.A. particles have high reactivity and play a great role in the mechanical properties. The lack of data in compressive strength of the geopolymer specimens with 100% mine tailing (M.T.) was reported in many research that there is no geopolymerization. Additives like fly ash, gypsum were utilized in geopolymerization processes to consolidate mine tailings (Rao and Liu 2015).\u003c/p\u003e\n\u003cp\u003eFigure\u0026nbsp;\u003cspan class=\"InternalRef\"\u003e5\u003c/span\u003e summarizes the specimens cured at room temperature whose compressive strength values increase with the cured time. A longer curing period increases the polymerization rate resulting in higher compressive strength. The results show that longer curing periods did not lower the compressive strength of geopolymer concrete as declared (Jaarsveld et al. \u003cspan class=\"CitationRef\"\u003e2002\u003c/span\u003e). These will be the best candidates to perform the toxicity study to determine the encapsulation capacity of toxic metals.\u003c/p\u003e\n\u003c/div\u003e\n\u003cdiv id=\"Sec13\" class=\"Section4\"\u003e\n\u003ch2\u003e3.3.1.2 Effect of Fly Ash and NaOH Concentration on Mechanical Strength\u003c/h2\u003e\n\u003cp\u003eFigure\u0026nbsp;\u003cspan class=\"InternalRef\"\u003e12\u003c/span\u003e(a-b) displays the result of Unconfined Compressive Strength (UCS) of fly ash-based geopolymer specimens cured at room temperature for seven days with various F.A. proportions (0%, 25%, 50%, 75%, 100%) and NaOH concentration at 5M and 10M. This figure shows that both F.A. and NaOH contribute strongly to the increase of strength. Higher the amount of F.A. and NaOH is greater than the UCS value, as demonstrated in another study (Zhang et al. \u003cspan class=\"CitationRef\"\u003e2011\u003c/span\u003e). This is due to higher O.H. or sodium oxide content during the geopolymerization reaction, as claimed by Zhuang et al. There are reactions and condensation between fly ash and alkaline reagents. The outcome, Si\u003csup\u003e4+\u003c/sup\u003e, and Al\u003csup\u003e3+\u003c/sup\u003e, combined with complex crystallization, oligomerization, and polymerization, yields a new aluminosilicate-based polymer with a novel amorphous three-dimensional network structure (Zhuang et al. \u003cspan class=\"CitationRef\"\u003e2016\u003c/span\u003e). The Si/Al ratio played a great role in the geopolymerization as the main precursor. Furthermore, as demonstrated by Zhang et al. (L. Zhang et al., \u003cspan class=\"CitationRef\"\u003e2011\u003c/span\u003e), the elevated of the Unconfined Compressive Strength (UCS) with the proportion of F.A. is owing to the Si/Al ratio of the MT/FA mixture and its reactivity. Generally, a low Si/Al ratio is preferable for a good geopolymerization (Rangan et al., 2014) and should be within 1-3 (Xu et al., \u003cspan class=\"CitationRef\"\u003e2003\u003c/span\u003e; Zhang et al. \u003cspan class=\"CitationRef\"\u003e2011\u003c/span\u003e; Rangan et al., 2014).\u003c/p\u003e\n\u003c/div\u003e\n\u003cdiv id=\"Sec14\" class=\"Section4\"\u003e\n\u003ch2\u003e3.3.1.3. Effect of Gypsum (G) on Mechanical Strength\u003c/h2\u003e\n\u003cp\u003eIn order to investigate the effect of gypsum (G) on the Unconfined Compressive Strength (UCS), three series of geopolymers specimens (FMS-0x, FGMS-0x, and FGMS-0xa) were performed with different proportions of F.A. (0%, 25%, 50%, 75%, and 100%) cured for seven days at 5M NaOH with Gypsum that range at 0g, 10g, and 20g. Fig.\u0026nbsp;\u003cspan class=\"InternalRef\"\u003e12\u003c/span\u003e (c) shows the role of gypsum with different proportions of fly ash on the compressive strength. It can be seen that the strength of the geopolymers with gypsum increase compare with those without G, which means adding gypsum can improve the geopolymerization as claimed (Boonserm et al., \u003cspan class=\"CitationRef\"\u003e2012\u003c/span\u003e). The highest peak of strength was gained by adding 10g of G. This increase happened because of the entering of Ca\u003csup\u003e2+\u003c/sup\u003e in the bond Si-O-Al-O and equilibrating the charge Al ions (Fern\u0026aacute;ndez-Jim\u0026eacute;nez et al. \u003cspan class=\"CitationRef\"\u003e2006\u003c/span\u003e), that contributes strongly to the formation of CSH, aluminosilicate structure and lead to the improvement of compressive strength (Boonserm et al. \u003cspan class=\"CitationRef\"\u003e2012\u003c/span\u003e). Further, the trend drops down with the increased amount of G (Rattanasak et al., \u003cstrong\u003e2011\u003c/strong\u003e).\u003c/p\u003e\n\u003c/div\u003e\n\u003c/div\u003e\n\u003cdiv id=\"Sec15\" class=\"Section3\"\u003e\n\u003ch2\u003e3.3.2 Microstructure and Microchemistry of Geopolymers\u003c/h2\u003e\n\u003cp\u003eIn order to characterize and evaluate the microstructure and microchemistry of fly ash-based-geopolymer matrix and figure out the connection between the microstructure and compressive strength of geopolymers, SEM imaging, XRD diffractometer, and FTIR spectra of selected geopolymers specimens were evaluated.\u003c/p\u003e\n\u003cp\u003eFinally, it can be noted that one of the most important factors that contribute to the mechanical strength is the water ratio used. Basically, the lower this ratio is, the greater the final UCS strength will be. The geopolymer specimen series (FMS-0xa) with 0.27 of Liquid/Solid ratio has recorded the highest values in terms of UCS strength which vary between 1.7 and 14,075 MPa. The compressive strength also depends on the curing time. The UCS test of the geopolymer showed slight changes in compressive strength after 28 days, but no changes have been recorded after 56 days(Badur and Chaudhary 2008). When sodium silicate was utilized, the presence of silica retards the zeolite formation rate. As a result, first, greater strength values are gained at lower degrees of reaction. The fly ash activated by an alkaline solution can have a greater compressive strength with greater zeolite content. (Lloyd, \u003cspan class=\"CitationRef\"\u003e2009\u003c/span\u003e)\u003c/p\u003e\n\u003cdiv id=\"Sec16\" class=\"Section4\"\u003e\n\u003ch2\u003e3.3.2.1 SEM Imaging Analysis\u003c/h2\u003e\n\u003cp\u003eThe SEM imaging was carried out to figure out the effect of aging periods, NaOH concentration, and gypsum on the microstructure of geopolymers. The SEM micrographs of different geopolymer specimens are displayed in Figs.\u0026nbsp;\u003cspan class=\"InternalRef\"\u003e7\u003c/span\u003e-\u003cspan class=\"InternalRef\"\u003e10\u003c/span\u003e.\u003c/p\u003e\n\u003cp\u003eIn order to understand the effect of aging time on the microstructure of the geopolymer specimens, SEM imaging of FGMSW-3b matrix was carried out and cured under room temperature condition after 7, 14, and 28 days with 100% F.A., 20g of Gy at 10 M of NaOH concentration (Fig.\u0026nbsp;\u003cspan class=\"InternalRef\"\u003e7\u003c/span\u003e). Fig.\u0026nbsp;\u003cspan class=\"InternalRef\"\u003e7\u003c/span\u003e provides a comparative analysis of SEM micrographs of various geopolymers effectively treated at varying periods at a moderate optical zoom. According to this figure, there is very little modification in the microstructure of geopolymers after seven days, implying that curing time has little influence on the microstructure, as also stated by another study. (Zhang et al. \u003cspan class=\"CitationRef\"\u003e2011\u003c/span\u003e).\u003c/p\u003e\n\u003cp\u003eTo figure out the effect of sodium hydroxide (NaOH) on the microstructure of geopolymer specimens (FMS-02 and FMS-02a) cured under room temperature after 14 days curing period with 100% F.A. at different concentrations of NaOH (5M and 10M), the SEM imaging was investigated. Fig.\u0026nbsp;\u003cspan class=\"InternalRef\"\u003e8\u003c/span\u003e depicts the various modifications shown in the micro-structural of the geopolymers. Fig.\u0026nbsp;\u003cspan class=\"InternalRef\"\u003e8\u003c/span\u003e (a) showed the existence of F.A. in a negligible amount as the concentration of NaOH increases, discussing the function of NaOH in polymerization. Fig.\u0026nbsp;\u003cspan class=\"InternalRef\"\u003e8\u003c/span\u003e (b) indicates the existence of F.A. in a massive portion as the concentration of NaOH increases, which also clarifies the function of NaOH in geopolymers. Further analysis revealed that at 15M NaOH, the particles of F.A. have been almost non-existent, indicating that the increased the NaOH concentration, the faster the geopolymerization rate. At 15M, the geopolymer gel was much more cohesive and thicker than that at 5 and 10M, yet geopolymerization was quite substantial at 10M (Zhang et al. \u003cspan class=\"CitationRef\"\u003e2011\u003c/span\u003e). It also confirms the compressive strength (UCS) results (Fig.\u0026nbsp;\u003cspan class=\"InternalRef\"\u003e12\u003c/span\u003e (a)), which show that the maximum UCS value was acquired to 10M NaOH.\u003c/p\u003e\n\u003cp\u003eThe effect of sodium silicate (Na-silicate) on the microstructure was evaluated, by comparing the specimen FMS-01 activated with only NaOH and FMSW-01 activated with NaOH and Na-silicate both cured at ambient temperature, at 5M NaOH with 100% F.AAs shown in Fig.\u0026nbsp;\u003cspan class=\"InternalRef\"\u003e9\u003c/span\u003e (c) and (d), there is still a notable change in structural system between all these images; Fig.\u0026nbsp;\u003cspan class=\"InternalRef\"\u003e9\u003c/span\u003e (d) is more compact than Fig.\u0026nbsp;\u003cspan class=\"InternalRef\"\u003e9\u003c/span\u003e (c), attributed to the existence of sodium silicate in that sample at a 1.08:1 ratio. Once sodium hydroxide (NaOH) and sodium silicate (Na-Silicate) are mixed to make an alkali solution, the blending has superior mechanical properties than NaOH alone(Palomo et al. \u003cspan class=\"CitationRef\"\u003e1999\u003c/span\u003e); the very same research claimed that sample only with NaOH has a porous material compared to one provided both with NaOH and Na-Silicate, which has a higher density structure.\u003c/p\u003e\n\u003cp\u003eTo understand the effect of gypsum on the microstructure of the geopolymer matrixes (FMS-02, FGMS-02, and FGMS-02a) at low magnification, the SEM analysis was performed with 75% F.A. at 5M NaOH at different content of gypsum: (a) 0g, (b) and (c) 20g 10 g of gypsum cured for seven days curing under ambient air condition. The scanning electron microscopy (SEM) geopolymer matrixes (FMS-02, FGMS-02, and FGMS-02a) are displayed in Fig.\u0026nbsp;\u003cspan class=\"InternalRef\"\u003e10\u003c/span\u003e. This figure reveals that the opacity of these three geopolymers varies significantly. The sample of FGMS-02 with 10g of Gy in Fig.\u0026nbsp;\u003cspan class=\"InternalRef\"\u003e10\u003c/span\u003e (b) is much more condensed with low permeability than that of the other geopolymers; nevertheless, there is much more unreacted F.A. in the FMS-02 geopolymer with 0g of Gy in Fig.\u0026nbsp;\u003cspan class=\"InternalRef\"\u003e10\u003c/span\u003e (a) than the other geopolymers, which clarified the function which gypsum performed in terms of microstructures and mechanical properties by boosting the polymerization rate. In addition, these SEM imaging results justified the Unconfined Compressive Strength results (Fig.\u0026nbsp;\u003cspan class=\"InternalRef\"\u003e12\u003c/span\u003e. (c)) that the UCS values increased with the addition of 10g of Gy. This performance could be attributed to the combination of mine tailings (low reactivity) to fly ash (high reactivity) and gypsum, which concurred with the research finding of Xiaolong et al., which claimed that mine tailings are often crystalline, leading to low reactivity throughout geopolymerization therefore; as a result, products with minimal compressive performance. As a result, adding extra elements with higher reactivity to mine tailings-based geopolymers can efficiently tune and optimize their characteristics. (Xiaolong et al. \u003cspan class=\"CitationRef\"\u003e2021\u003c/span\u003e). Furthermore, because most of the chemicals included in this function are manufacturing wastes, its use has additional benefits for the environment. Strong-containing calcium compounds have such a higher favorable impact on geopolymer durability than lower-containing calcium. This is due to the development of extra CSH gels, which, when combined with NASH, increases structural integrity, as previously reported by Xiaolong et al.,.(Xiaolong et al. \u003cspan class=\"CitationRef\"\u003e2021\u003c/span\u003e)\u003c/p\u003e\n\u003c/div\u003e\n\u003cdiv id=\"Sec17\" class=\"Section4\"\u003e\n\u003ch2\u003e3.3.2.2 XRD Analysis\u003c/h2\u003e\n\u003cp\u003eX-ray fluorescence spectrometry has been used to determine the elemental composition of the geopolymers using the XRD-6100 diffractometer and the XRD patterns have been analysed through JADE 6.0 Software. Because of its amorphous or nanocrystalline nature, the N-A-S-H gel formed during polymerization is difficult to characterize with XRD. Nonetheless, the XRD patterns of the specimens were used to determine the crystalline formation in the different mixture designs of the fly ash-based geopolymer presented with high compressive strength. (FMS-01a (100% F.A.), FGMS-02 (75% F.A.), FGMSW-02 (75% F.A.), FGMSW-01a (100% F.A.), FGMSW-03b (50% F.A.), synthesized under room temperature conditions cured at 7, 14 and 28 days is shown in Fig.\u0026nbsp;\u003cspan class=\"InternalRef\"\u003e6\u003c/span\u003e, where different phases have been obtained. Where C= Corundum Al\u003csub\u003e2\u003c/sub\u003eO\u003csub\u003e3\u003c/sub\u003e, Cc= Calcite CaCO\u003csub\u003e3\u003c/sub\u003e, G=Gypsum CaSO\u003csub\u003e4\u003c/sub\u003e 2H\u003csub\u003e2\u003c/sub\u003eO, M= Mullite Al\u003csub\u003e6\u003c/sub\u003eSi\u003csub\u003e2\u003c/sub\u003eO\u003csub\u003e13\u003c/sub\u003e, Q= quartz SiO\u003csub\u003e2\u003c/sub\u003e, Ss=Sodium silicate Na\u003csub\u003e2\u003c/sub\u003e(SiO\u003csub\u003e3\u003c/sub\u003e), Sh=Calcium Silicate hydritade Ca\u003csub\u003e1\u003c/sub\u003e.5Si\u003csub\u003e0.5\u003c/sub\u003e xH\u003csub\u003e2\u003c/sub\u003eO, Ch= Chabazite, J= Jadeite, A=Anhydrite CaSO\u003csub\u003e4\u003c/sub\u003e.\u003c/p\u003e\n\u003cp\u003eMullite and quartz, which have been discovered in raw fly ash, were observed throughout all samples. All of the enabled samples exhibited amorphous ridges focused around 220\u0026deg; to 30\u0026deg;, including all samples, confirmed the formation of a geopolymer gel. (Keyte et al., 2009a). Except for the FMSW-05 sample, that does not show the geopolymerization since mine tailing is the only element in its composition. Singh et al., in their research, found a similar observation (Singh et al., 2018). Numerous crystalline structures, including quartz and mullite, have been regarded as non-reactive, even though their reaction speed in alkali-silicate solutions is remarkably slower when compared to inorganic materials.(Keyte et al., 2009b) in some of the samples as FGMS-02 and FGMSW-03, could identify de chabazite, which is one of the crystal that can encapsulate the heavy metals such as Cu and Pb (Jun et al., \u003cstrong\u003e2015)\u003c/strong\u003e.\u003c/p\u003e\n\u003cp\u003eCalcite, CaCO3, is formed once calcium hydroxide reacts to carbon dioxide in the atmosphere; calcium solubility at elevated pHs has been well recognized to decrease due to the instability of calcium hydroxide forming(Komnitsas and Zaharaki \u003cspan class=\"CitationRef\"\u003e2009\u003c/span\u003e), his mineral was found in the majority of the samples.\u003c/p\u003e\n\u003cp\u003eCrystallization amorphous gels were the subtler shown in fly ash-derived geopolymers. Compared to the fly ash instance, much less of the binder is gradually morphed into zeolite stages. Furthermore, variables that promote zeolite forming, like increasing the alkalis of the binder, increasing strength, and reducing any proclivity for strength loss, at least for the duration considered. The creation of zeolites, including chabazite, was recognized through XRD analysis in most specimens. Other minerals discovered included calcite and quartz, which were linked to the presence of zeolites.\u003c/p\u003e\n\u003c/div\u003e\n\u003cdiv id=\"Sec18\" class=\"Section4\"\u003e\n\u003ch2\u003e3.3.2.3 FTIR Analysis\u003c/h2\u003e\n\u003cp\u003eThe FTIR of the five best specimens in terms of compressive strength with various materials was investigated. The FTIR spectra of the five (5) geopolymers (FMS-01a (100% F.A.), FGMS-02a (75% F.A.), FGMSW-02(75% F.A.), FGMSW-02(75% F.A.), and FGMSW-03b (50% F.A.), containing a different proportion of Fly Ash and sodium hydroxide concentration (5M, 10M) cured at 7, 14 and 28 days are shown in Fig.\u0026nbsp;\u003cspan class=\"InternalRef\"\u003e11\u003c/span\u003e. Table \u003cspan class=\"InternalRef\"\u003e5\u003c/span\u003e shows the Infrared characteristic bands identified in F.A. and geopolymers specimens. In-plane and bending vibrations of Al-O / Si-O, 460cm\u003csup\u003e\u0026minus;1\u003c/sup\u003e, and 550 cm-1 are assigned. The existence of a 1456cm-1 band may be due to C= O vibrations, which indicate the presence of carbonate bands. In addition, the I.R. spectra studies show bands close to 1016 cm\u0026minus;1 and 1143 cm\u0026minus;1 due to asymmetric Si-O stretching while banding at 458 cm\u0026minus;1 to SiO4 bending in-plane Si-O. However, bands between 772, 579, 537, and 439 cm\u0026minus;1 correlate with Al-Si minerals. In addition, new bands emerging at 3423, 1638, and 1540 cm\u0026minus;1 are consistent with-OH, H\u003csub\u003e2\u003c/sub\u003eO bending and asymmetric carbonate stretching, respectively (Ismaiel Saraya and El-Fadaly 2017). The peak appeared at 1640 cm\u0026minus;1 as a result of bending H-O-H vibration, and the intensity of this peak increased with a rise in NaOH concentration, suggesting a rise in geopolymerization degree (Devi and Saroha \u003cspan class=\"CitationRef\"\u003e2016\u003c/span\u003e).\u0026nbsp;\u003c/p\u003e\n\u003c/div\u003e\n\u003c/div\u003e\n\u003c/div\u003e"},{"header":"4. Conclusions","content":"\u003cp\u003eFrom this study, it can be concluded that fly ash, mine tailings with gypsum as an additive by using Sodium hydroxide (NaOH) at (5-10M) and sodium silicate (water glass) as the alkali reagents can be used to study the feasibility of geopolymerization. In this work, eight geopolymer recipes were made based on fly ash. Both F.A. and M.T. were added in different proportions (0, 25, 50, 75, and 100%) of the total weight. The different dosages mentioned in the design section of the geopolymers gave rise to 40 recipes of geopolymers, which after being mixed and cured at room temperature after 7, 14, and 14 days curing time, showed slight physical changes compared to those without F.A. content could not maintain their shape and hardness. Furthermore, From this research, we remark that mine tailings could not be used alone in performing geopolymer products owing to their low reactivity. However, associating mine tailings with other binders with high reactivity, such as fly ash or high content in SiO\u003csub\u003e2\u003c/sub\u003e, would make mine tailings a suitable binder in geopolymerisation. In summary, the Unconfined Compressive Strength (UCS) of Geopolymers, the mechanical properties, and microstructure were influenced by curing time, temperature, and the chemical reactions. Furthermore, this study demonstrated that mine tailings could be successfully valorized through geopolymerization to generate eco-friendly products that would sustainably use in the building and construction materials industry.\u003c/p\u003e"},{"header":"Declarations","content":"\u003ch4\u003eAcknowledgments\u003c/h4\u003e\n\u003cp\u003eThe work was supported by the Postgraduate Research \u0026amp; Practice Innovation Program of Jiangsu Province (SJCX17-0261), NSFC (51002080, 41501197), SPITP (201610300273), Top-notch Academic Programs Project of Jiangsu Higher Education Institutions (PPZY2015C222), and the Priority Academic Program Development of Jiangsu Higher Education Institutions (PAPD).\u003c/p\u003e\n\u003cp\u003e\u003cstrong\u003eConflicts of interest/Competing interests\u003c/strong\u003e The authors declare that they have no known competing financial interests or personal relationships that could have appeared to influence the work reported in this paper.\u003c/p\u003e\n\u003cp\u003e\u003cstrong\u003eFunding\u003c/strong\u003e\u0026nbsp;(no)\u003c/p\u003e\n\u003cp\u003e\u003cstrong\u003eAvailability of data and material\u003c/strong\u003e\u0026nbsp;(all data are included within the manuscript)\u003c/p\u003e\n\u003cp\u003e\u003cstrong\u003eCode availability\u003c/strong\u003e\u0026nbsp;(no)\u003c/p\u003e\n\u003ch4\u003e\u003cstrong\u003eConsent for publication\u003c/strong\u003e \u0026ldquo;Not applicable\u0026rdquo;\u0026nbsp;\u003c/h4\u003e"},{"header":"References","content":"\u003col\u003e\n\u003cli\u003eBadur, Smita, and Rubina Chaudhary. 2008. \u0026ldquo;Utilization of Hazardous Wastes and By-Products as a Green Concrete Material through S/S Process: A Review.\u0026rdquo; \u003cem\u003eReviews on Advanced Materials Science\u003c/em\u003e 17 (1\u0026ndash;2): 42\u0026ndash;61.\u003c/li\u003e\n\u003cli\u003eBoonserm, Kornkanok, Vanchai Sata, Kedsarin Pimraksa, and Prinya Chindaprasirt. 2012. \u0026ldquo;Microstructure and Strength of Blended FBC-PCC Fly Ash Geopolymer Containing Gypsum as an Additive.\u0026rdquo; \u003cem\u003eScienceAsia\u003c/em\u003e 38 (2): 175\u0026ndash;81. https://doi.org/10.2306/scienceasia1513-1874.2012.38.175.\u003c/li\u003e\n\u003cli\u003eChoi, W. H., S. R. Lee, and J. Y. Park. 2009. \u0026ldquo;Cement Based Solidification/Stabilization of Arsenic-Contaminated Mine Tailings.\u0026rdquo; \u003cem\u003eWaste Management\u003c/em\u003e 29 (5): 1766\u0026ndash;71. https://doi.org/10.1016/j.wasman.2008.11.008.\u003c/li\u003e\n\u003cli\u003eCsavina, Janae, Jason Field, Mark P. Taylor, Song Gao, Andrea Land\u0026aacute;zuri, Eric A. Betterton, and A. Eduardo S\u0026aacute;ez. 2012. \u0026ldquo;A Review on the Importance of Metals and Metalloids in Atmospheric Dust and Aerosol from Mining Operations.\u0026rdquo; \u003cem\u003eScience of the Total Environment\u003c/em\u003e 433 (September): 58\u0026ndash;73. https://doi.org/10.1016/j.scitotenv.2012.06.013.\u003c/li\u003e\n\u003cli\u003eDavidovits, J. 1991. \u0026ldquo;Geopolymers - Inorganic Polymeric New Materials.\u0026rdquo; \u003cem\u003eJournal of Thermal Analysis\u003c/em\u003e 37 (8): 1633\u0026ndash;56. https://doi.org/10.1007/BF01912193.\u003c/li\u003e\n\u003cli\u003eDevi, Parmila, and Anil K. Saroha. 2016. \u0026ldquo;Risk Assessment and Technical Feasibility of Usage of Paper Mill Sludge Biochar-Based Exhausted Adsorbent for Geopolymeric Brick Formation.\u0026rdquo; \u003cem\u003eEnvironmental Science and Pollution Research\u003c/em\u003e 23 (21): 21641\u0026ndash;51. https://doi.org/10.1007/s11356-016-7343-4.\u003c/li\u003e\n\u003cli\u003eFern\u0026aacute;ndez-Jim\u0026eacute;nez, A., A. Palomo, I. Sobrados, and J. Sanz. 2006. \u0026ldquo;The Role Played by the Reactive Alumina Content in the Alkaline Activation of Fly Ashes.\u0026rdquo; \u003cem\u003eMicroporous and Mesoporous Materials\u003c/em\u003e 91 (1\u0026ndash;3): 111\u0026ndash;19. https://doi.org/10.1016/j.micromeso.2005.11.015.\u003c/li\u003e\n\u003cli\u003eHassan, Amer, Mohammed Arif, and M. Shariq. 2019. \u0026ldquo;Use of Geopolymer Concrete for a Cleaner and Sustainable Environment \u0026ndash; A Review of Mechanical Properties and Microstructure.\u0026rdquo; \u003cem\u003eJournal of Cleaner Production\u003c/em\u003e 223 (June): 704\u0026ndash;28. https://doi.org/10.1016/j.jclepro.2019.03.051.\u003c/li\u003e\n\u003cli\u003eIsmaiel Saraya, Mohamed El-Shahte, and Ezzat El-Fadaly. 2017. \u0026ldquo;Preliminary Study of Alkali Activation of Basalt: Effect of NaOH Concentration on Geopolymerization of Basalt.\u0026rdquo; \u003cem\u003eJournal of Materials Science and Chemical Engineering\u003c/em\u003e 05 (11): 58\u0026ndash;76. https://doi.org/10.4236/msce.2017.511006.\u003c/li\u003e\n\u003cli\u003eJaarsveld, J G S Van, J S J Van Deventer, and G C Lukey. 2002. \u0026ldquo;\u0026lt;Vanjaarsveld2002.Pdf\u0026gt;.\u0026rdquo; \u003cem\u003eChemical Engineering Journal\u003c/em\u003e 89: 63\u0026ndash;73.\u003c/li\u003e\n\u003cli\u003eJun, Yubin, and Jae Eun Oh. 2015. \u0026ldquo;Use of Gypsum as a Preventive Measure for Strength Deterioration during Curing in Class F Fly Ash Geopolymer System.\u0026rdquo; \u003cem\u003eMaterials\u003c/em\u003e 8 (6): 3053\u0026ndash;67. https://doi.org/10.3390/ma8063053.\u003c/li\u003e\n\u003cli\u003eKeyte, L. M. 2009a. \u003cem\u003eFly Ash Glass Chemistry and Inorganic Polymer Cements\u003c/em\u003e. \u003cem\u003eGeopolymers: Structures, Processing, Properties and Industrial Applications\u003c/em\u003e. Woodhead Publishing Limited. https://doi.org/10.1533/9781845696382.1.15.\u003c/li\u003e\n\u003cli\u003eKeyte, L.M. 2009b. \u0026ldquo;Fly Ash Glass Chemistry and Inorganic Polymer Cements.\u0026rdquo; In \u003cem\u003eGeopolymers\u003c/em\u003e, 15\u0026ndash;36. Elsevier. https://doi.org/10.1533/9781845696382.1.15.\u003c/li\u003e\n\u003cli\u003eKinnunen, Paivo, Arnold Ismailov, Soili Solismaa, Harisankar Sreenivasan, Marja Liisa R\u0026auml;is\u0026auml;nen, Erkki Lev\u0026auml;nen, and Mirja Illikainen. 2018. \u0026ldquo;Recycling Mine Tailings in Chemically Bonded Ceramics \u0026ndash; A Review.\u0026rdquo; \u003cem\u003eJournal of Cleaner Production\u003c/em\u003e 174 (February): 634\u0026ndash;49. https://doi.org/10.1016/j.jclepro.2017.10.280.\u003c/li\u003e\n\u003cli\u003eKiventer\u0026auml;, Jenni, Priyadharshini Perumal, Juho Yliniemi, and Mirja Illikainen. 2020. \u0026ldquo;Mine Tailings as a Raw Material in Alkali Activation: A Review.\u0026rdquo; \u003cem\u003eInternational Journal of Minerals, Metallurgy and Materials\u003c/em\u003e 27 (8): 1009\u0026ndash;20. https://doi.org/10.1007/s12613-020-2129-6.\u003c/li\u003e\n\u003cli\u003eKomnitsas, K., and D. Zaharaki. 2009. \u0026ldquo;Utilisation of Low-Calcium Slags to Improve the Strength and Durability of Geopolymers.\u0026rdquo; In \u003cem\u003eGeopolymers\u003c/em\u003e, 343\u0026ndash;75. Elsevier. https://doi.org/10.1533/9781845696382.2.343.\u003c/li\u003e\n\u003cli\u003eKossoff, D., W.E. Dubbin, M. Alfredsson, S.J. Edwards, M.G. Macklin, and K.A. Hudson-Edwards. 2014. \u0026ldquo;Mine Tailings Dams: Characteristics, Failure, Environmental Impacts, and Remediation.\u0026rdquo; \u003cem\u003eApplied Geochemistry\u003c/em\u003e 51 (December): 229\u0026ndash;45. https://doi.org/10.1016/j.apgeochem.2014.09.010.\u003c/li\u003e\n\u003cli\u003eKrishna, R. S., Faiz Shaikh, Jyotirmoy Mishra, Georgy Lazorenko, and Anton Kasprzhitskii. 2021. \u0026ldquo;Mine Tailings-Based Geopolymers: Properties, Applications and Industrial Prospects.\u0026rdquo; \u003cem\u003eCeramics International\u003c/em\u003e 47 (13): 17826\u0026ndash;43. https://doi.org/10.1016/j.ceramint.2021.03.180.\u003c/li\u003e\n\u003cli\u003eLazorenko, Georgy, Anton Kasprzhitskii, Alexander Kruglikov, Vasilii Mischinenko, and Victor Yavna. 2020. \u0026ldquo;Sustainable Geopolymer Composites Reinforced with Flax Tows.\u0026rdquo; \u003cem\u003eCeramics International\u003c/em\u003e 46 (8): 12870\u0026ndash;75. https://doi.org/10.1016/j.ceramint.2020.01.184.\u003c/li\u003e\n\u003cli\u003eLloyd, R.R. 2009. \u0026ldquo;Accelerated Ageing of Geopolymers.\u0026rdquo; In \u003cem\u003eGeopolymers\u003c/em\u003e, 139\u0026ndash;66. Elsevier. https://doi.org/10.1533/9781845696382.2.139.\u003c/li\u003e\n\u003cli\u003eMa, Chau Khun, Abdullah Zawawi Awang, and Wahid Omar. 2018. \u0026ldquo;Structural and Material Performance of Geopolymer Concrete: A Review.\u0026rdquo; \u003cem\u003eConstruction and Building Materials\u003c/em\u003e 186 (October): 90\u0026ndash;102. https://doi.org/10.1016/j.conbuildmat.2018.07.111.\u003c/li\u003e\n\u003cli\u003eMoukannaa, S., A. Nazari, A. Bagheri, M. Loutou, J. G. Sanjayan, and R. Hakkou. 2019. \u0026ldquo;Alkaline Fused Phosphate Mine Tailings for Geopolymer Mortar Synthesis: Thermal Stability, Mechanical and Microstructural Properties.\u0026rdquo; \u003cem\u003eJournal of Non-Crystalline Solids\u003c/em\u003e 511 (May): 76\u0026ndash;85. https://doi.org/10.1016/j.jnoncrysol.2018.12.031.\u003c/li\u003e\n\u003cli\u003eNgole-Jeme, Veronica Mpode, and Peter Fantke. 2017. \u0026ldquo;Ecological and Human Health Risks Associated with Abandoned Gold Mine Tailings Contaminated Soil.\u0026rdquo; Edited by Jorge Paz-Ferreiro. \u003cem\u003ePLoS ONE\u003c/em\u003e 12 (2): e0172517. https://doi.org/10.1371/journal.pone.0172517.\u003c/li\u003e\n\u003cli\u003ePalomo, A., M. W. Grutzeck, and M. T. Blanco. 1999. \u0026ldquo;Alkali-Activated Fly Ashes: A Cement for the Future.\u0026rdquo; \u003cem\u003eCement and Concrete Research\u003c/em\u003e 29 (8): 1323\u0026ndash;29. https://doi.org/10.1016/S0008-8846(98)00243-9.\u003c/li\u003e\n\u003cli\u003eRangan, B. Vijaya. 2014. \u0026ldquo;Geopolymer Concrete for Environmental Protection.\u0026rdquo; \u003cem\u003eIndian Concrete Journal\u003c/em\u003e 88 (4): 41\u0026ndash;59.\u003c/li\u003e\n\u003cli\u003eRao, Feng, and Qi Liu. 2015. \u0026ldquo;Geopolymerization and Its Potential Application in Mine Tailings Consolidation: A Review.\u0026rdquo; \u003cem\u003eMineral Processing and Extractive Metallurgy Review\u003c/em\u003e 36 (6): 399\u0026ndash;409. https://doi.org/10.1080/08827508.2015.1055625.\u003c/li\u003e\n\u003cli\u003eRattanasak, Ubolluk, Kanokwan Pankhet, and Prinya Chindaprasirt. 2011. \u0026ldquo;Effect of Chemical Admixtures on Properties of High-Calcium Fly Ash Geopolymer.\u0026rdquo; \u003cem\u003eInternational Journal of Minerals, Metallurgy and Materials\u003c/em\u003e 18 (3): 364\u0026ndash;69. https://doi.org/10.1007/s12613-011-0448-3.\u003c/li\u003e\n\u003cli\u003eSheoran, A. S., and V. Sheoran. 2006. \u0026ldquo;Heavy Metal Removal Mechanism of Acid Mine Drainage in Wetlands: A Critical Review.\u0026rdquo; \u003cem\u003eMinerals Engineering\u003c/em\u003e 19 (2): 105\u0026ndash;16. https://doi.org/10.1016/j.mineng.2005.08.006.\u003c/li\u003e\n\u003cli\u003eSingh, Nakshatra. 2018. \u0026ldquo;Fly Ash-Based Geopolymer Binder: A Future Construction Material.\u0026rdquo; \u003cem\u003eMinerals\u003c/em\u003e 8 (7): 299. https://doi.org/10.3390/min8070299.\u003c/li\u003e\n\u003cli\u003e\u0026Scaron;kv\u0026aacute;ra, Franti\u0026scaron;ek, Tom\u0026aacute;s J\u0026iacute;lek, and Lubom\u0026iacute;r Kopeck\u0026yacute;. 2005. \u0026ldquo;Geopolymer Materials Based on Fly Ash.\u0026rdquo; \u003cem\u003eCeramics - Silikaty\u003c/em\u003e 49 (3): 195\u0026ndash;204.\u003c/li\u003e\n\u003cli\u003eWang, Shun-Cai, Zhi-cheng Wei, Yan Zhou, and Fang-Han Wang. 2015. \u0026ldquo;A Research on the Leaching Toxicity of the Solid Waste of a Pb-Zn Mine.\u0026rdquo; \u003cem\u003eJournal of Residuals Science \u0026amp; Technology\u003c/em\u003e 12 (1): 25\u0026ndash;30. https://doi.org/10.12783/issn.2376-578X/12/1/4.\u003c/li\u003e\n\u003cli\u003eWei, Yan, Liao Jun-Cheng, Wang Shu-Mei, Liang Sheng-Wang, and Yu Jiang-Yong. 2016. \u0026ldquo;The Ftir Fingerprint of Gypsum Fibrosum.\u0026rdquo; \u003cem\u003eActa Medica Mediterranea\u003c/em\u003e 32 (SpecialIssue1): 607\u0026ndash;11.\u003c/li\u003e\n\u003cli\u003eXiaolong, Zhang, Zhang Shiyu, Liu Hui, and Zhao Yingliang. 2021. \u0026ldquo;Disposal of Mine Tailings via Geopolymerization.\u0026rdquo; \u003cem\u003eJournal of Cleaner Production\u003c/em\u003e 284 (xxxx): 124756. https://doi.org/10.1016/j.jclepro.2020.124756.\u003c/li\u003e\n\u003cli\u003eXu, H., van Deventer, J. 2000. \u0026ldquo;The Geopolymerisation of Alumino-Silicate Minerals.\u0026rdquo; \u003cem\u003eInt. J. Miner. Process.\u003c/em\u003e 59: 247\u0026ndash;66.\u003c/li\u003e\n\u003cli\u003eXu, Hua, and Jannie S.J. Van Deventer. 2003. \u0026ldquo;Effect of Source Materials on Geopolymerization.\u0026rdquo; \u003cem\u003eIndustrial and Engineering Chemistry Research\u003c/em\u003e 42 (8): 1698\u0026ndash;1706. https://doi.org/10.1021/ie0206958.\u003c/li\u003e\n\u003cli\u003eZhang, Lianyang, Saeed Ahmari, and Jinhong Zhang. 2011. \u0026ldquo;Synthesis and Characterization of Fly Ash Modified Mine Tailings-Based Geopolymers.\u0026rdquo; \u003cem\u003eConstruction and Building Materials\u003c/em\u003e 25 (9): 3773\u0026ndash;81. https://doi.org/10.1016/j.conbuildmat.2011.04.005.\u003c/li\u003e\n\u003cli\u003eZhang, Wei, Jinghua Long, Xueru Zhang, Weining Shen, and Zhongyi Wei. 2020. \u0026ldquo;Pollution and Ecological Risk Evaluation of Heavy Metals in the Soil and Sediment around the HTM Tailings Pond, Northeastern China.\u0026rdquo; \u003cem\u003eInternational Journal of Environmental Research and Public Health\u003c/em\u003e 17 (19): 1\u0026ndash;10. https://doi.org/10.3390/ijerph17197072.\u003c/li\u003e\n\u003cli\u003eZhao, Shujie, Faheem Muhammad, Lin Yu, Ming Xia, Xiao Huang, Binquan Jiao, Ning Lu, and Dongwei Li. 2019. \u0026ldquo;Solidification/Stabilization of Municipal Solid Waste Incineration Fly Ash Using Uncalcined Coal Gangue\u0026ndash;Based Alkali-Activated Cementitious Materials.\u0026rdquo; \u003cem\u003eEnvironmental Science and Pollution Research\u003c/em\u003e 26 (25): 25609\u0026ndash;20. https://doi.org/10.1007/s11356-019-05832-5.\u003c/li\u003e\n\u003cli\u003eZhuang, Xiao Yu, Liang Chen, Sridhar Komarneni, Chun Hui Zhou, Dong Shen Tong, Hui Min Yang, Wei Hua Yu, and Hao Wang. 2016. \u0026ldquo;Fly Ash-Based Geopolymer: Clean Production, Properties and Applications.\u0026rdquo; \u003cem\u003eJournal of Cleaner Production\u003c/em\u003e 125 (July): 253\u0026ndash;67. https://doi.org/10.1016/j.jclepro.2016.03.019.\u003c/li\u003e\n\u003c/ol\u003e"},{"header":"Tables","content":"\u003ch2\u003e\u0026nbsp;\u003c/h2\u003e\n\u003cp\u003eTable.1 Chemical Compositions of class F fly ash and Lead-Zinc mine tailing\u003c/p\u003e\n\u003ctable border=\"1\" width=\"0\"\u003e\n\u003ctbody\u003e\n\u003ctr\u003e\n\u003ctd width=\"42\"\u003e\u0026nbsp;\u003c/td\u003e\n\u003ctd colspan=\"12\" width=\"615\"\u003e\n\u003cp\u003e\u003cstrong\u003eElement (wt %)\u003c/strong\u003e\u003c/p\u003e\n\u003c/td\u003e\n\u003c/tr\u003e\n\u003ctr\u003e\n\u003ctd width=\"42\"\u003e\u0026nbsp;\u003c/td\u003e\n\u003ctd width=\"53\"\u003e\n\u003cp\u003eSiO\u003csub\u003e2\u003c/sub\u003e\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd width=\"55\"\u003e\n\u003cp\u003eAl\u003csub\u003e2\u003c/sub\u003eO\u003csub\u003e3\u003c/sub\u003e\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd width=\"55\"\u003e\n\u003cp\u003eFe\u003csub\u003e2\u003c/sub\u003eO\u003csub\u003e3\u003c/sub\u003e\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd width=\"56\"\u003e\n\u003cp\u003eMnO\u003csub\u003e2\u003c/sub\u003e\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd width=\"53\"\u003e\n\u003cp\u003eCaO\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd width=\"51\"\u003e\n\u003cp\u003eMgO\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd width=\"45\"\u003e\n\u003cp\u003eK\u003csub\u003e2\u003c/sub\u003eO\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd width=\"53\"\u003e\n\u003cp\u003eNa\u003csub\u003e2\u003c/sub\u003eO\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd width=\"48\"\u003e\n\u003cp\u003eP\u003csub\u003e2\u003c/sub\u003eO\u003csub\u003e5\u003c/sub\u003e\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd width=\"48\"\u003e\n\u003cp\u003eTiO\u003csub\u003e2\u003c/sub\u003e\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd width=\"45\"\u003e\n\u003cp\u003eSO\u003csub\u003e3\u003c/sub\u003e\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd width=\"53\"\u003e\n\u003cp\u003eLOI\u003c/p\u003e\n\u003c/td\u003e\n\u003c/tr\u003e\n\u003ctr\u003e\n\u003ctd width=\"42\"\u003e\n\u003cp\u003e\u003cstrong\u003eFA\u003c/strong\u003e\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd width=\"53\"\u003e\n\u003cp\u003e40.15\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd width=\"55\"\u003e\n\u003cp\u003e35.50\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd width=\"55\"\u003e\n\u003cp\u003e7.57\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd width=\"56\"\u003e\n\u003cp\u003e0.11\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd width=\"53\"\u003e\n\u003cp\u003e8.33\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd width=\"51\"\u003e\n\u003cp\u003e1.21\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd width=\"45\"\u003e\n\u003cp\u003e1.48\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd width=\"53\"\u003e\n\u003cp\u003e1.10\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd width=\"48\"\u003e\n\u003cp\u003e0.37\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd width=\"48\"\u003e\n\u003cp\u003e1.51\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd width=\"45\"\u003e\n\u003cp\u003e0.70\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd width=\"53\"\u003e\n\u003cp\u003e1.64\u003c/p\u003e\n\u003c/td\u003e\n\u003c/tr\u003e\n\u003ctr\u003e\n\u003ctd width=\"42\"\u003e\n\u003cp\u003e\u003cstrong\u003eMT\u003c/strong\u003e\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd width=\"53\"\u003e\n\u003cp\u003e18.83\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd width=\"55\"\u003e\n\u003cp\u003e1.61\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd width=\"55\"\u003e\n\u003cp\u003e6.20\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd width=\"56\"\u003e\n\u003cp\u003e9.12\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd width=\"53\"\u003e\n\u003cp\u003e29.49\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd width=\"51\"\u003e\n\u003cp\u003e2.83\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd width=\"45\"\u003e\n\u003cp\u003e0.15\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd width=\"53\"\u003e\n\u003cp\u003e0.12\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd width=\"48\"\u003e\n\u003cp\u003e0.03\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd width=\"48\"\u003e\n\u003cp\u003e0.06\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd width=\"45\"\u003e\n\u003cp\u003e2.30\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd width=\"53\"\u003e\n\u003cp\u003e28.96\u003c/p\u003e\n\u003c/td\u003e\n\u003c/tr\u003e\n\u003c/tbody\u003e\n\u003c/table\u003e\n\u003cp\u003eTable.2 Chemical Composition of FA and MT \u0026minus; Minor and Trace Elements (ppm)\u003c/p\u003e\n\u003ctable border=\"1\" width=\"0\"\u003e\n\u003ctbody\u003e\n\u003ctr\u003e\n\u003ctd width=\"40\"\u003e\u0026nbsp;\u003c/td\u003e\n\u003ctd colspan=\"14\" width=\"615\"\u003e\n\u003cp\u003e\u003cstrong\u003eElement (ppm)\u003c/strong\u003e\u003c/p\u003e\n\u003c/td\u003e\n\u003c/tr\u003e\n\u003ctr\u003e\n\u003ctd width=\"40\"\u003e\n\u003cp\u003e\u003cstrong\u003e\u0026nbsp;\u003c/strong\u003e\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd width=\"50\"\u003e\n\u003cp\u003eAs\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd width=\"42\"\u003e\n\u003cp\u003eMo\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd width=\"50\"\u003e\n\u003cp\u003ePb\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd width=\"42\"\u003e\n\u003cp\u003eRb\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd width=\"42\"\u003e\n\u003cp\u003eTh\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd width=\"42\"\u003e\n\u003cp\u003eU\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd width=\"42\"\u003e\n\u003cp\u003eY\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd width=\"50\"\u003e\n\u003cp\u003eZr\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd width=\"42\"\u003e\n\u003cp\u003eGa\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd width=\"42\"\u003e\n\u003cp\u003eCu\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd width=\"42\"\u003e\n\u003cp\u003eCo\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd width=\"42\"\u003e\n\u003cp\u003eNi\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd width=\"42\"\u003e\n\u003cp\u003eCr\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd width=\"58\"\u003e\n\u003cp\u003eV\u003c/p\u003e\n\u003c/td\u003e\n\u003c/tr\u003e\n\u003ctr\u003e\n\u003ctd width=\"40\"\u003e\n\u003cp\u003e\u003cstrong\u003eFA \u003c/strong\u003e\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd width=\"50\"\u003e\n\u003cp\u003e21.3\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd width=\"42\"\u003e\n\u003cp\u003e14.4\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd width=\"50\"\u003e\n\u003cp\u003e101.4\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd width=\"42\"\u003e\n\u003cp\u003e47.2\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd width=\"42\"\u003e\n\u003cp\u003e32.3\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd width=\"42\"\u003e\n\u003cp\u003e12.5\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd width=\"42\"\u003e\n\u003cp\u003e64.5\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd width=\"50\"\u003e\n\u003cp\u003e433.8\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd width=\"42\"\u003e\n\u003cp\u003e67.4\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd width=\"42\"\u003e\n\u003cp\u003e75.1\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd width=\"42\"\u003e\n\u003cp\u003e25.4\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd width=\"42\"\u003e\n\u003cp\u003e45.5\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd width=\"42\"\u003e\n\u003cp\u003e61.7\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd width=\"58\"\u003e\n\u003cp\u003e182.1\u003c/p\u003e\n\u003c/td\u003e\n\u003c/tr\u003e\n\u003ctr\u003e\n\u003ctd width=\"40\"\u003e\n\u003cp\u003e\u003cstrong\u003eMT\u003c/strong\u003e\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd width=\"50\"\u003e\n\u003cp\u003e151.9\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd width=\"42\"\u003e\n\u003cp\u003e0.7\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd width=\"50\"\u003e\n\u003cp\u003e622.4\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd width=\"42\"\u003e\n\u003cp\u003e10.6\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd width=\"42\"\u003e\n\u003cp\u003e11.5\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd width=\"42\"\u003e\n\u003cp\u003e7.5\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd width=\"42\"\u003e\n\u003cp\u003e63.6\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd width=\"50\"\u003e\n\u003cp\u003e28.7\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd width=\"42\"\u003e\n\u003cp\u003e26.6\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd width=\"42\"\u003e\n\u003cp\u003e52.9\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd width=\"42\"\u003e\n\u003cp\u003e1.4\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd width=\"42\"\u003e\n\u003cp\u003e10.1\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd width=\"42\"\u003e\n\u003cp\u003e24.3\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd width=\"58\"\u003e\n\u003cp\u003e97\u003c/p\u003e\n\u003c/td\u003e\n\u003c/tr\u003e\n\u003c/tbody\u003e\n\u003c/table\u003e\n\u003cp\u003e\u003cem\u003eTable.3 Mixture Design for Geopolymerization of Mine Tailings\u003c/em\u003e\u003c/p\u003e\n\u003ctable border=\"1\" width=\"0\"\u003e\n\u003ctbody\u003e\n\u003ctr\u003e\n\u003ctd rowspan=\"2\" width=\"70\"\u003e\n\u003cp\u003e\u003cstrong\u003eS (NaOH)\u003c/strong\u003e\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd rowspan=\"2\" width=\"110\"\u003e\n\u003cp\u003e\u003cstrong\u003eSpecimen Code\u003c/strong\u003e\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd colspan=\"3\" width=\"169\"\u003e\n\u003cp\u003e\u003cstrong\u003eWaste materials (g)\u003c/strong\u003e\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd colspan=\"4\" width=\"303\"\u003e\n\u003cp\u003e\u003cstrong\u003eRatios\u003c/strong\u003e\u003c/p\u003e\n\u003c/td\u003e\n\u003c/tr\u003e\n\u003ctr\u003e\n\u003ctd width=\"56\"\u003e\n\u003cp\u003e\u003cstrong\u003eF\u003c/strong\u003e\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd width=\"56\"\u003e\n\u003cp\u003e\u003cstrong\u003eG\u003c/strong\u003e\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd width=\"56\"\u003e\n\u003cp\u003e\u003cstrong\u003eM\u003c/strong\u003e\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd width=\"70\"\u003e\n\u003cp\u003e\u003cstrong\u003eSi/Al\u003c/strong\u003e\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd width=\"70\"\u003e\n\u003cp\u003e\u003cstrong\u003eNa/Al\u003c/strong\u003e\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd width=\"100\"\u003e\n\u003cp\u003e\u003cstrong\u003eLiquid/Solid\u003c/strong\u003e\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd width=\"63\"\u003e\n\u003cp\u003e\u003cstrong\u003eW/S\u003c/strong\u003e\u003c/p\u003e\n\u003c/td\u003e\n\u003c/tr\u003e\n\u003ctr\u003e\n\u003ctd rowspan=\"5\" width=\"70\"\u003e\n\u003cp\u003e\u003cstrong\u003e5 M\u003c/strong\u003e\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd width=\"110\"\u003e\n\u003cp\u003eFMS-01\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd width=\"56\"\u003e\n\u003cp\u003e200\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd width=\"56\"\u003e\n\u003cp\u003e-\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd width=\"56\"\u003e\n\u003cp\u003e0\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd width=\"70\"\u003e\n\u003cp\u003e1.13\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd width=\"70\"\u003e\n\u003cp\u003e0.14\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd width=\"100\"\u003e\n\u003cp\u003e0.27\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd width=\"63\"\u003e\n\u003cp\u003e-\u003c/p\u003e\n\u003c/td\u003e\n\u003c/tr\u003e\n\u003ctr\u003e\n\u003ctd width=\"110\"\u003e\n\u003cp\u003eFMS-02\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd width=\"56\"\u003e\n\u003cp\u003e150\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd width=\"56\"\u003e\n\u003cp\u003e-\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd width=\"56\"\u003e\n\u003cp\u003e50\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd width=\"70\"\u003e\n\u003cp\u003e1.29\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd width=\"70\"\u003e\n\u003cp\u003e0.18\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd width=\"100\"\u003e\n\u003cp\u003e0.27\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd width=\"63\"\u003e\n\u003cp\u003e-\u003c/p\u003e\n\u003c/td\u003e\n\u003c/tr\u003e\n\u003ctr\u003e\n\u003ctd width=\"110\"\u003e\n\u003cp\u003eFMS-03\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd width=\"56\"\u003e\n\u003cp\u003e100\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd width=\"56\"\u003e\n\u003cp\u003e-\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd width=\"56\"\u003e\n\u003cp\u003e100\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd width=\"70\"\u003e\n\u003cp\u003e1.59\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd width=\"70\"\u003e\n\u003cp\u003e0.25\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd width=\"100\"\u003e\n\u003cp\u003e0.27\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd width=\"63\"\u003e\n\u003cp\u003e-\u003c/p\u003e\n\u003c/td\u003e\n\u003c/tr\u003e\n\u003ctr\u003e\n\u003ctd width=\"110\"\u003e\n\u003cp\u003eFMS-04\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd width=\"56\"\u003e\n\u003cp\u003e50\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd width=\"56\"\u003e\n\u003cp\u003e-\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd width=\"56\"\u003e\n\u003cp\u003e150\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd width=\"70\"\u003e\n\u003cp\u003e2.39\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd width=\"70\"\u003e\n\u003cp\u003e0.43\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd width=\"100\"\u003e\n\u003cp\u003e0.27\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd width=\"63\"\u003e\n\u003cp\u003e-\u003c/p\u003e\n\u003c/td\u003e\n\u003c/tr\u003e\n\u003ctr\u003e\n\u003ctd width=\"110\"\u003e\n\u003cp\u003eFMS-05\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd width=\"56\"\u003e\n\u003cp\u003e0\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd width=\"56\"\u003e\n\u003cp\u003e-\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd width=\"56\"\u003e\n\u003cp\u003e200\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd width=\"70\"\u003e\n\u003cp\u003e11.71\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd width=\"70\"\u003e\n\u003cp\u003e2.57\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd width=\"100\"\u003e\n\u003cp\u003e0.27\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd width=\"63\"\u003e\n\u003cp\u003e-\u003c/p\u003e\n\u003c/td\u003e\n\u003c/tr\u003e\n\u003ctr\u003e\n\u003ctd rowspan=\"5\" width=\"70\"\u003e\n\u003cp\u003e\u003cstrong\u003e10 M\u003c/strong\u003e\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd width=\"110\"\u003e\n\u003cp\u003eFMS-01a\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd width=\"56\"\u003e\n\u003cp\u003e200\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd width=\"56\"\u003e\n\u003cp\u003e-\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd width=\"56\"\u003e\n\u003cp\u003e0\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd width=\"70\"\u003e\n\u003cp\u003e1.13\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd width=\"70\"\u003e\n\u003cp\u003e0.26\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd width=\"100\"\u003e\n\u003cp\u003e0.27\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd width=\"63\"\u003e\n\u003cp\u003e-\u003c/p\u003e\n\u003c/td\u003e\n\u003c/tr\u003e\n\u003ctr\u003e\n\u003ctd width=\"110\"\u003e\n\u003cp\u003eFMS-02a\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd width=\"56\"\u003e\n\u003cp\u003e150\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd width=\"56\"\u003e\n\u003cp\u003e-\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd width=\"56\"\u003e\n\u003cp\u003e50\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd width=\"70\"\u003e\n\u003cp\u003e1.29\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd width=\"70\"\u003e\n\u003cp\u003e0.33\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd width=\"100\"\u003e\n\u003cp\u003e0.27\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd width=\"63\"\u003e\n\u003cp\u003e-\u003c/p\u003e\n\u003c/td\u003e\n\u003c/tr\u003e\n\u003ctr\u003e\n\u003ctd width=\"110\"\u003e\n\u003cp\u003eFMS-03a\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd width=\"56\"\u003e\n\u003cp\u003e100\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd width=\"56\"\u003e\n\u003cp\u003e-\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd width=\"56\"\u003e\n\u003cp\u003e100\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd width=\"70\"\u003e\n\u003cp\u003e1.59\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd width=\"70\"\u003e\n\u003cp\u003e0.47\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd width=\"100\"\u003e\n\u003cp\u003e0.27\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd width=\"63\"\u003e\n\u003cp\u003e-\u003c/p\u003e\n\u003c/td\u003e\n\u003c/tr\u003e\n\u003ctr\u003e\n\u003ctd width=\"110\"\u003e\n\u003cp\u003eFMS-04a\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd width=\"56\"\u003e\n\u003cp\u003e50\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd width=\"56\"\u003e\n\u003cp\u003e-\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd width=\"56\"\u003e\n\u003cp\u003e150\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd width=\"70\"\u003e\n\u003cp\u003e2.39\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd width=\"70\"\u003e\n\u003cp\u003e0.83\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd width=\"100\"\u003e\n\u003cp\u003e0.27\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd width=\"63\"\u003e\n\u003cp\u003e-\u003c/p\u003e\n\u003c/td\u003e\n\u003c/tr\u003e\n\u003ctr\u003e\n\u003ctd width=\"110\"\u003e\n\u003cp\u003eFMS-05a\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd width=\"56\"\u003e\n\u003cp\u003e0\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd width=\"56\"\u003e\n\u003cp\u003e-\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd width=\"56\"\u003e\n\u003cp\u003e200\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd width=\"70\"\u003e\n\u003cp\u003e11.71\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd width=\"70\"\u003e\n\u003cp\u003e5.07\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd width=\"100\"\u003e\n\u003cp\u003e0.27\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd width=\"63\"\u003e\n\u003cp\u003e-\u003c/p\u003e\n\u003c/td\u003e\n\u003c/tr\u003e\n\u003ctr\u003e\n\u003ctd rowspan=\"5\" width=\"70\"\u003e\n\u003cp\u003e\u003cstrong\u003e5 M\u003c/strong\u003e\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd width=\"110\"\u003e\n\u003cp\u003eFMSW-01\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd width=\"56\"\u003e\n\u003cp\u003e200\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd width=\"56\"\u003e\n\u003cp\u003e-\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd width=\"56\"\u003e\n\u003cp\u003e0\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd width=\"70\"\u003e\n\u003cp\u003e1.13\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd width=\"70\"\u003e\n\u003cp\u003e0.14\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd width=\"100\"\u003e\n\u003cp\u003e0.52\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd width=\"63\"\u003e\n\u003cp\u003e1.08:1\u003c/p\u003e\n\u003c/td\u003e\n\u003c/tr\u003e\n\u003ctr\u003e\n\u003ctd width=\"110\"\u003e\n\u003cp\u003eFMSW-02\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd width=\"56\"\u003e\n\u003cp\u003e150\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd width=\"56\"\u003e\n\u003cp\u003e-\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd width=\"56\"\u003e\n\u003cp\u003e50\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd width=\"70\"\u003e\n\u003cp\u003e1.29\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd width=\"70\"\u003e\n\u003cp\u003e0.18\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd width=\"100\"\u003e\n\u003cp\u003e0.52\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd width=\"63\"\u003e\n\u003cp\u003e1.08:1\u003c/p\u003e\n\u003c/td\u003e\n\u003c/tr\u003e\n\u003ctr\u003e\n\u003ctd width=\"110\"\u003e\n\u003cp\u003eFMSW-03\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd width=\"56\"\u003e\n\u003cp\u003e100\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd width=\"56\"\u003e\n\u003cp\u003e-\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd width=\"56\"\u003e\n\u003cp\u003e100\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd width=\"70\"\u003e\n\u003cp\u003e1.59\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd width=\"70\"\u003e\n\u003cp\u003e0.25\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd width=\"100\"\u003e\n\u003cp\u003e0.52\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd width=\"63\"\u003e\n\u003cp\u003e1.08:1\u003c/p\u003e\n\u003c/td\u003e\n\u003c/tr\u003e\n\u003ctr\u003e\n\u003ctd width=\"110\"\u003e\n\u003cp\u003eFMSW-04\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd width=\"56\"\u003e\n\u003cp\u003e50\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd width=\"56\"\u003e\n\u003cp\u003e-\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd width=\"56\"\u003e\n\u003cp\u003e150\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd width=\"70\"\u003e\n\u003cp\u003e2.39\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd width=\"70\"\u003e\n\u003cp\u003e0.43\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd width=\"100\"\u003e\n\u003cp\u003e0.52\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd width=\"63\"\u003e\n\u003cp\u003e1.08:1\u003c/p\u003e\n\u003c/td\u003e\n\u003c/tr\u003e\n\u003ctr\u003e\n\u003ctd width=\"110\"\u003e\n\u003cp\u003eFMSW-05\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd width=\"56\"\u003e\n\u003cp\u003e0\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd width=\"56\"\u003e\n\u003cp\u003e-\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd width=\"56\"\u003e\n\u003cp\u003e200\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd width=\"70\"\u003e\n\u003cp\u003e11.71\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd width=\"70\"\u003e\n\u003cp\u003e2.57\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd width=\"100\"\u003e\n\u003cp\u003e0.52\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd width=\"63\"\u003e\n\u003cp\u003e1.08:1\u003c/p\u003e\n\u003c/td\u003e\n\u003c/tr\u003e\n\u003ctr\u003e\n\u003ctd rowspan=\"5\" width=\"70\"\u003e\n\u003cp\u003e\u003cstrong\u003e5 M\u003c/strong\u003e\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd width=\"110\"\u003e\n\u003cp\u003eFGMS-01\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd width=\"56\"\u003e\n\u003cp\u003e200\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd width=\"56\"\u003e\n\u003cp\u003e10\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd width=\"56\"\u003e\n\u003cp\u003e0\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd width=\"70\"\u003e\n\u003cp\u003e1.13\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd width=\"70\"\u003e\n\u003cp\u003e0.14\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd width=\"100\"\u003e\n\u003cp\u003e0.32\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd width=\"63\"\u003e\n\u003cp\u003e-\u003c/p\u003e\n\u003c/td\u003e\n\u003c/tr\u003e\n\u003ctr\u003e\n\u003ctd width=\"110\"\u003e\n\u003cp\u003eFGMS-02\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd width=\"56\"\u003e\n\u003cp\u003e150\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd width=\"56\"\u003e\n\u003cp\u003e10\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd width=\"56\"\u003e\n\u003cp\u003e50\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd width=\"70\"\u003e\n\u003cp\u003e1.29\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd width=\"70\"\u003e\n\u003cp\u003e0.18\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd width=\"100\"\u003e\n\u003cp\u003e0.32\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd width=\"63\"\u003e\n\u003cp\u003e-\u003c/p\u003e\n\u003c/td\u003e\n\u003c/tr\u003e\n\u003ctr\u003e\n\u003ctd width=\"110\"\u003e\n\u003cp\u003eFGMS-03\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd width=\"56\"\u003e\n\u003cp\u003e100\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd width=\"56\"\u003e\n\u003cp\u003e10\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd width=\"56\"\u003e\n\u003cp\u003e100\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd width=\"70\"\u003e\n\u003cp\u003e1.59\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd width=\"70\"\u003e\n\u003cp\u003e0.25\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd width=\"100\"\u003e\n\u003cp\u003e0.32\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd width=\"63\"\u003e\n\u003cp\u003e-\u003c/p\u003e\n\u003c/td\u003e\n\u003c/tr\u003e\n\u003ctr\u003e\n\u003ctd width=\"110\"\u003e\n\u003cp\u003eFGMS-04\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd width=\"56\"\u003e\n\u003cp\u003e50\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd width=\"56\"\u003e\n\u003cp\u003e10\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd width=\"56\"\u003e\n\u003cp\u003e150\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd width=\"70\"\u003e\n\u003cp\u003e2.39\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd width=\"70\"\u003e\n\u003cp\u003e0.43\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd width=\"100\"\u003e\n\u003cp\u003e0.32\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd width=\"63\"\u003e\n\u003cp\u003e-\u003c/p\u003e\n\u003c/td\u003e\n\u003c/tr\u003e\n\u003ctr\u003e\n\u003ctd width=\"110\"\u003e\n\u003cp\u003eFGMS-05\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd width=\"56\"\u003e\n\u003cp\u003e0\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd width=\"56\"\u003e\n\u003cp\u003e10\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd width=\"56\"\u003e\n\u003cp\u003e200\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd width=\"70\"\u003e\n\u003cp\u003e11.71\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd width=\"70\"\u003e\n\u003cp\u003e2.57\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd width=\"100\"\u003e\n\u003cp\u003e0.32\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd width=\"63\"\u003e\n\u003cp\u003e-\u003c/p\u003e\n\u003c/td\u003e\n\u003c/tr\u003e\n\u003ctr\u003e\n\u003ctd rowspan=\"5\" width=\"70\"\u003e\n\u003cp\u003e\u003cstrong\u003e5 M\u003c/strong\u003e\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd width=\"110\"\u003e\n\u003cp\u003eFGMS-01a\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd width=\"56\"\u003e\n\u003cp\u003e200\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd width=\"56\"\u003e\n\u003cp\u003e20\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd width=\"56\"\u003e\n\u003cp\u003e0\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd width=\"70\"\u003e\n\u003cp\u003e1.13\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd width=\"70\"\u003e\n\u003cp\u003e0.14\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd width=\"100\"\u003e\n\u003cp\u003e0.37\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd width=\"63\"\u003e\n\u003cp\u003e-\u003c/p\u003e\n\u003c/td\u003e\n\u003c/tr\u003e\n\u003ctr\u003e\n\u003ctd width=\"110\"\u003e\n\u003cp\u003eFGMS-02a\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd width=\"56\"\u003e\n\u003cp\u003e150\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd width=\"56\"\u003e\n\u003cp\u003e20\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd width=\"56\"\u003e\n\u003cp\u003e50\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd width=\"70\"\u003e\n\u003cp\u003e1.29\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd width=\"70\"\u003e\n\u003cp\u003e0.18\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd width=\"100\"\u003e\n\u003cp\u003e0.37\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd width=\"63\"\u003e\n\u003cp\u003e-\u003c/p\u003e\n\u003c/td\u003e\n\u003c/tr\u003e\n\u003ctr\u003e\n\u003ctd width=\"110\"\u003e\n\u003cp\u003eFGMS-03a\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd width=\"56\"\u003e\n\u003cp\u003e100\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd width=\"56\"\u003e\n\u003cp\u003e20\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd width=\"56\"\u003e\n\u003cp\u003e100\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd width=\"70\"\u003e\n\u003cp\u003e1.59\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd width=\"70\"\u003e\n\u003cp\u003e0.25\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd width=\"100\"\u003e\n\u003cp\u003e0.37\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd width=\"63\"\u003e\n\u003cp\u003e-\u003c/p\u003e\n\u003c/td\u003e\n\u003c/tr\u003e\n\u003ctr\u003e\n\u003ctd width=\"110\"\u003e\n\u003cp\u003eFGMS-04a\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd width=\"56\"\u003e\n\u003cp\u003e50\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd width=\"56\"\u003e\n\u003cp\u003e20\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd width=\"56\"\u003e\n\u003cp\u003e150\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd width=\"70\"\u003e\n\u003cp\u003e2.39\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd width=\"70\"\u003e\n\u003cp\u003e0.43\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd width=\"100\"\u003e\n\u003cp\u003e0.37\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd width=\"63\"\u003e\n\u003cp\u003e-\u003c/p\u003e\n\u003c/td\u003e\n\u003c/tr\u003e\n\u003ctr\u003e\n\u003ctd width=\"110\"\u003e\n\u003cp\u003eFGMS-05a\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd width=\"56\"\u003e\n\u003cp\u003e0\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd width=\"56\"\u003e\n\u003cp\u003e20\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd width=\"56\"\u003e\n\u003cp\u003e200\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd width=\"70\"\u003e\n\u003cp\u003e11.71\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd width=\"70\"\u003e\n\u003cp\u003e2.57\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd width=\"100\"\u003e\n\u003cp\u003e0.37\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd width=\"63\"\u003e\n\u003cp\u003e-\u003c/p\u003e\n\u003c/td\u003e\n\u003c/tr\u003e\n\u003ctr\u003e\n\u003ctd rowspan=\"5\" width=\"70\"\u003e\n\u003cp\u003e\u003cstrong\u003e5 M\u003c/strong\u003e\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd width=\"110\"\u003e\n\u003cp\u003eFGMSW-01\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd width=\"56\"\u003e\n\u003cp\u003e200\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd width=\"56\"\u003e\n\u003cp\u003e10\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd width=\"56\"\u003e\n\u003cp\u003e0\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd width=\"70\"\u003e\n\u003cp\u003e1.23\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd width=\"70\"\u003e\n\u003cp\u003e2.95\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd width=\"100\"\u003e\n\u003cp\u003e0.57\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd width=\"63\"\u003e\n\u003cp\u003e1.08:1\u003c/p\u003e\n\u003c/td\u003e\n\u003c/tr\u003e\n\u003ctr\u003e\n\u003ctd width=\"110\"\u003e\n\u003cp\u003eFGMSW-02\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd width=\"56\"\u003e\n\u003cp\u003e150\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd width=\"56\"\u003e\n\u003cp\u003e10\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd width=\"56\"\u003e\n\u003cp\u003e50\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd width=\"70\"\u003e\n\u003cp\u003e1.41\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd width=\"70\"\u003e\n\u003cp\u003e3.87\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd width=\"100\"\u003e\n\u003cp\u003e0.57\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd width=\"63\"\u003e\n\u003cp\u003e1.08:1\u003c/p\u003e\n\u003c/td\u003e\n\u003c/tr\u003e\n\u003ctr\u003e\n\u003ctd width=\"110\"\u003e\n\u003cp\u003eFGMSW-03\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd width=\"56\"\u003e\n\u003cp\u003e100\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd width=\"56\"\u003e\n\u003cp\u003e10\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd width=\"56\"\u003e\n\u003cp\u003e100\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd width=\"70\"\u003e\n\u003cp\u003e1.77\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd width=\"70\"\u003e\n\u003cp\u003e5.62\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd width=\"100\"\u003e\n\u003cp\u003e0.57\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd width=\"63\"\u003e\n\u003cp\u003e1.08:1\u003c/p\u003e\n\u003c/td\u003e\n\u003c/tr\u003e\n\u003ctr\u003e\n\u003ctd width=\"110\"\u003e\n\u003cp\u003eFGMSW-04\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd width=\"56\"\u003e\n\u003cp\u003e50\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd width=\"56\"\u003e\n\u003cp\u003e10\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd width=\"56\"\u003e\n\u003cp\u003e150\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd width=\"70\"\u003e\n\u003cp\u003e2.73\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd width=\"70\"\u003e\n\u003cp\u003e10.32\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd width=\"100\"\u003e\n\u003cp\u003e0.57\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd width=\"63\"\u003e\n\u003cp\u003e1.08:1\u003c/p\u003e\n\u003c/td\u003e\n\u003c/tr\u003e\n\u003ctr\u003e\n\u003ctd width=\"110\"\u003e\n\u003cp\u003eFGMSW-05\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd width=\"56\"\u003e\n\u003cp\u003e0\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd width=\"56\"\u003e\n\u003cp\u003e10\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd width=\"56\"\u003e\n\u003cp\u003e200\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd width=\"70\"\u003e\n\u003cp\u003e13.79\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd width=\"70\"\u003e\n\u003cp\u003e64.55\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd width=\"100\"\u003e\n\u003cp\u003e0.57\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd width=\"63\"\u003e\n\u003cp\u003e1.08:1\u003c/p\u003e\n\u003c/td\u003e\n\u003c/tr\u003e\n\u003ctr\u003e\n\u003ctd rowspan=\"5\" width=\"70\"\u003e\n\u003cp\u003e\u003cstrong\u003e5 M\u003c/strong\u003e\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd width=\"110\"\u003e\n\u003cp\u003eFGMSW-01a\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd width=\"56\"\u003e\n\u003cp\u003e200\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd width=\"56\"\u003e\n\u003cp\u003e20\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd width=\"56\"\u003e\n\u003cp\u003e0\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd width=\"70\"\u003e\n\u003cp\u003e1.23\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd width=\"70\"\u003e\n\u003cp\u003e2.95\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd width=\"100\"\u003e\n\u003cp\u003e0.62\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd width=\"63\"\u003e\n\u003cp\u003e1.08:1\u003c/p\u003e\n\u003c/td\u003e\n\u003c/tr\u003e\n\u003ctr\u003e\n\u003ctd width=\"110\"\u003e\n\u003cp\u003eFGMSW-02a\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd width=\"56\"\u003e\n\u003cp\u003e150\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd width=\"56\"\u003e\n\u003cp\u003e20\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd width=\"56\"\u003e\n\u003cp\u003e50\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd width=\"70\"\u003e\n\u003cp\u003e1.41\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd width=\"70\"\u003e\n\u003cp\u003e3.87\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd width=\"100\"\u003e\n\u003cp\u003e0.62\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd width=\"63\"\u003e\n\u003cp\u003e1.08:1\u003c/p\u003e\n\u003c/td\u003e\n\u003c/tr\u003e\n\u003ctr\u003e\n\u003ctd width=\"110\"\u003e\n\u003cp\u003eFGMSW-03a\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd width=\"56\"\u003e\n\u003cp\u003e100\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd width=\"56\"\u003e\n\u003cp\u003e20\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd width=\"56\"\u003e\n\u003cp\u003e100\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd width=\"70\"\u003e\n\u003cp\u003e1.77\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd width=\"70\"\u003e\n\u003cp\u003e5.62\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd width=\"100\"\u003e\n\u003cp\u003e0.62\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd width=\"63\"\u003e\n\u003cp\u003e1.08:1\u003c/p\u003e\n\u003c/td\u003e\n\u003c/tr\u003e\n\u003ctr\u003e\n\u003ctd width=\"110\"\u003e\n\u003cp\u003eFGMSW-04a\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd width=\"56\"\u003e\n\u003cp\u003e50\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd width=\"56\"\u003e\n\u003cp\u003e20\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd width=\"56\"\u003e\n\u003cp\u003e150\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd width=\"70\"\u003e\n\u003cp\u003e2.73\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd width=\"70\"\u003e\n\u003cp\u003e10.32\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd width=\"100\"\u003e\n\u003cp\u003e0.62\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd width=\"63\"\u003e\n\u003cp\u003e1.08:1\u003c/p\u003e\n\u003c/td\u003e\n\u003c/tr\u003e\n\u003ctr\u003e\n\u003ctd width=\"110\"\u003e\n\u003cp\u003eFGMSW-05a\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd width=\"56\"\u003e\n\u003cp\u003e0\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd width=\"56\"\u003e\n\u003cp\u003e20\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd width=\"56\"\u003e\n\u003cp\u003e200\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd width=\"70\"\u003e\n\u003cp\u003e13.79\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd width=\"70\"\u003e\n\u003cp\u003e64.55\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd width=\"100\"\u003e\n\u003cp\u003e0.62\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd width=\"63\"\u003e\n\u003cp\u003e1.08:1\u003c/p\u003e\n\u003c/td\u003e\n\u003c/tr\u003e\n\u003ctr\u003e\n\u003ctd rowspan=\"5\" width=\"70\"\u003e\n\u003cp\u003e\u003cstrong\u003e10 M\u003c/strong\u003e\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd width=\"110\"\u003e\n\u003cp\u003eFGMSW-01b\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd width=\"56\"\u003e\n\u003cp\u003e200\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd width=\"56\"\u003e\n\u003cp\u003e20\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd width=\"56\"\u003e\n\u003cp\u003e0\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd width=\"70\"\u003e\n\u003cp\u003e1.23\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd width=\"70\"\u003e\n\u003cp\u003e3.07\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd width=\"100\"\u003e\n\u003cp\u003e0.62\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd width=\"63\"\u003e\n\u003cp\u003e1.08:1\u003c/p\u003e\n\u003c/td\u003e\n\u003c/tr\u003e\n\u003ctr\u003e\n\u003ctd width=\"110\"\u003e\n\u003cp\u003eFGMSW-02b\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd width=\"56\"\u003e\n\u003cp\u003e150\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd width=\"56\"\u003e\n\u003cp\u003e20\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd width=\"56\"\u003e\n\u003cp\u003e50\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd width=\"70\"\u003e\n\u003cp\u003e1.41\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd width=\"70\"\u003e\n\u003cp\u003e4.02\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd width=\"100\"\u003e\n\u003cp\u003e0.62\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd width=\"63\"\u003e\n\u003cp\u003e1.08:1\u003c/p\u003e\n\u003c/td\u003e\n\u003c/tr\u003e\n\u003ctr\u003e\n\u003ctd width=\"110\"\u003e\n\u003cp\u003eFGMSW-03b\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd width=\"56\"\u003e\n\u003cp\u003e100\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd width=\"56\"\u003e\n\u003cp\u003e20\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd width=\"56\"\u003e\n\u003cp\u003e100\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd width=\"70\"\u003e\n\u003cp\u003e1.77\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd width=\"70\"\u003e\n\u003cp\u003e5.84\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd width=\"100\"\u003e\n\u003cp\u003e0.62\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd width=\"63\"\u003e\n\u003cp\u003e1.08:1\u003c/p\u003e\n\u003c/td\u003e\n\u003c/tr\u003e\n\u003ctr\u003e\n\u003ctd width=\"110\"\u003e\n\u003cp\u003eFGMSW-04b\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd width=\"56\"\u003e\n\u003cp\u003e50\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd width=\"56\"\u003e\n\u003cp\u003e20\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd width=\"56\"\u003e\n\u003cp\u003e150\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd width=\"70\"\u003e\n\u003cp\u003e2.73\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd width=\"70\"\u003e\n\u003cp\u003e10.72\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd width=\"100\"\u003e\n\u003cp\u003e0.62\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd width=\"63\"\u003e\n\u003cp\u003e1.08:1\u003c/p\u003e\n\u003c/td\u003e\n\u003c/tr\u003e\n\u003ctr\u003e\n\u003ctd width=\"110\"\u003e\n\u003cp\u003eFGMSW-05b\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd width=\"56\"\u003e\n\u003cp\u003e0\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd width=\"56\"\u003e\n\u003cp\u003e20\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd width=\"56\"\u003e\n\u003cp\u003e200\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd width=\"70\"\u003e\n\u003cp\u003e13.79\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd width=\"70\"\u003e\n\u003cp\u003e67.05056\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd width=\"100\"\u003e\n\u003cp\u003e0.62\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd width=\"63\"\u003e\n\u003cp\u003e1.08:1\u003c/p\u003e\n\u003c/td\u003e\n\u003c/tr\u003e\n\u003c/tbody\u003e\n\u003c/table\u003e\n\u003cp\u003eTable 4. Table of the samples that have the higher values of UCS of the different series.\u003c/p\u003e\n\u003ctable style=\"width: 742px;\" border=\"1\"\u003e\n\u003ctbody\u003e\n\u003ctr\u003e\n\u003ctd style=\"width: 105px;\" colspan=\"2\"\u003e\n\u003cp\u003e\u0026nbsp;\u003c/p\u003e\n\u003cp\u003eAlkali activator content\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd style=\"width: 84px;\"\u003e\n\u003cp\u003eMT content/\u003c/p\u003e\n\u003cp\u003eother aggregates\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd style=\"width: 102px;\"\u003e\n\u003cp\u003e\u0026nbsp;\u003c/p\u003e\n\u003cp\u003e0%\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd style=\"width: 97.8125px;\"\u003e\n\u003cp\u003e\u0026nbsp;\u003c/p\u003e\n\u003cp\u003e25%\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd style=\"width: 102.188px;\"\u003e\n\u003cp\u003e\u0026nbsp;\u003c/p\u003e\n\u003cp\u003e50%\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd style=\"width: 104px;\"\u003e\n\u003cp\u003e\u0026nbsp;\u003c/p\u003e\n\u003cp\u003e75%\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd style=\"width: 96px;\"\u003e\n\u003cp\u003e\u0026nbsp;\u003c/p\u003e\n\u003cp\u003e100%\u003c/p\u003e\n\u003c/td\u003e\n\u003c/tr\u003e\n\u003ctr\u003e\n\u003ctd style=\"width: 64px;\"\u003e\n\u003cp\u003eNaOH\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd style=\"width: 41px;\"\u003e\n\u003cp\u003e5M\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd style=\"width: 84px;\"\u003e\n\u003cp\u003e\u0026nbsp;\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd style=\"width: 102px;\"\u003e\n\u003cp\u003e\u0026nbsp;\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd style=\"width: 97.8125px;\"\u003e\n\u003cp\u003e\u0026nbsp;\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd style=\"width: 102.188px;\"\u003e\n\u003cp\u003eFMS-03a\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd style=\"width: 104px;\"\u003e\n\u003cp\u003eFMS-04\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd style=\"width: 96px;\"\u003e\n\u003cp\u003e\u0026nbsp;\u003c/p\u003e\n\u003c/td\u003e\n\u003c/tr\u003e\n\u003ctr\u003e\n\u003ctd style=\"width: 64px;\"\u003e\n\u003cp\u003eNaOH\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd style=\"width: 41px;\"\u003e\n\u003cp\u003e10M\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd style=\"width: 84px;\"\u003e\n\u003cp\u003e\u0026nbsp;\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd style=\"width: 102px;\"\u003e\n\u003cp\u003eFMS-01a\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd style=\"width: 97.8125px;\"\u003e\n\u003cp\u003eFMS-02a\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd style=\"width: 102.188px;\"\u003e\n\u003cp\u003eFMS-03\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd style=\"width: 104px;\"\u003e\n\u003cp\u003eFMS-04a\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd style=\"width: 96px;\"\u003e\n\u003cp\u003e\u0026nbsp;\u003c/p\u003e\n\u003c/td\u003e\n\u003c/tr\u003e\n\u003ctr\u003e\n\u003ctd style=\"width: 64px;\"\u003e\n\u003cp\u003eWG/\u003c/p\u003e\n\u003cp\u003eNaOH\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd style=\"width: 41px;\"\u003e\n\u003cp\u003e2N/\u003c/p\u003e\n\u003cp\u003e5M\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd style=\"width: 84px;\"\u003e\n\u003cp\u003e\u0026nbsp;\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd style=\"width: 102px;\"\u003e\n\u003cp\u003eFMSW-01\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd style=\"width: 97.8125px;\"\u003e\n\u003cp\u003eFMSW-02\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd style=\"width: 102.188px;\"\u003e\n\u003cp\u003eFMSW-03\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd style=\"width: 104px;\"\u003e\n\u003cp\u003eFMSW-04\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd style=\"width: 96px;\"\u003e\n\u003cp\u003eFMSW-05\u003c/p\u003e\n\u003c/td\u003e\n\u003c/tr\u003e\n\u003ctr\u003e\n\u003ctd style=\"width: 64px;\"\u003e\n\u003cp\u003eNaOH\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd style=\"width: 41px;\"\u003e\n\u003cp\u003e5M\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd style=\"width: 84px;\"\u003e\n\u003cp\u003eGypsum 10g\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd style=\"width: 102px;\"\u003e\n\u003cp\u003e\u0026nbsp;\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd style=\"width: 97.8125px;\"\u003e\n\u003cp\u003eFGMS-02\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd style=\"width: 102.188px;\"\u003e\n\u003cp\u003eFGMS-03\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd style=\"width: 104px;\"\u003e\n\u003cp\u003e\u0026nbsp;\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd style=\"width: 96px;\"\u003e\n\u003cp\u003e\u0026nbsp;\u003c/p\u003e\n\u003c/td\u003e\n\u003c/tr\u003e\n\u003ctr\u003e\n\u003ctd style=\"width: 64px;\"\u003e\n\u003cp\u003eNaOH\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd style=\"width: 41px;\"\u003e\n\u003cp\u003e5M\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd style=\"width: 84px;\"\u003e\n\u003cp\u003eGypsum 20g\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd style=\"width: 102px;\"\u003e\n\u003cp\u003e\u0026nbsp;\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd style=\"width: 97.8125px;\"\u003e\n\u003cp\u003eFGMS-02a\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd style=\"width: 102.188px;\"\u003e\n\u003cp\u003eFGMS-03a\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd style=\"width: 104px;\"\u003e\n\u003cp\u003e\u0026nbsp;\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd style=\"width: 96px;\"\u003e\n\u003cp\u003e\u0026nbsp;\u003c/p\u003e\n\u003c/td\u003e\n\u003c/tr\u003e\n\u003ctr\u003e\n\u003ctd style=\"width: 64px;\"\u003e\n\u003cp\u003eWG/\u003c/p\u003e\n\u003cp\u003eNaOH\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd style=\"width: 41px;\"\u003e\n\u003cp\u003e2N/\u003c/p\u003e\n\u003cp\u003e5M\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd style=\"width: 84px;\"\u003e\n\u003cp\u003eGypsum 10g\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd style=\"width: 102px;\"\u003e\n\u003cp\u003e\u0026nbsp;\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd style=\"width: 97.8125px;\"\u003e\n\u003cp\u003eFGMSW-02\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd style=\"width: 102.188px;\"\u003e\n\u003cp\u003eFGMSW-03\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd style=\"width: 104px;\"\u003e\n\u003cp\u003e\u0026nbsp;\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd style=\"width: 96px;\"\u003e\n\u003cp\u003e\u0026nbsp;\u003c/p\u003e\n\u003c/td\u003e\n\u003c/tr\u003e\n\u003ctr\u003e\n\u003ctd style=\"width: 64px;\"\u003e\n\u003cp\u003eWG/\u003c/p\u003e\n\u003cp\u003eNaOH\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd style=\"width: 41px;\"\u003e\n\u003cp\u003e2N/\u003c/p\u003e\n\u003cp\u003e5M\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd style=\"width: 84px;\"\u003e\n\u003cp\u003eGypsum 20g\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd style=\"width: 102px;\"\u003e\n\u003cp\u003eFGMSW-01a\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd style=\"width: 97.8125px;\"\u003e\n\u003cp\u003e\u0026nbsp;\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd style=\"width: 102.188px;\"\u003e\n\u003cp\u003eFGMSW-03a\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd style=\"width: 104px;\"\u003e\n\u003cp\u003e\u0026nbsp;\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd style=\"width: 96px;\"\u003e\n\u003cp\u003e\u0026nbsp;\u003c/p\u003e\n\u003c/td\u003e\n\u003c/tr\u003e\n\u003ctr\u003e\n\u003ctd style=\"width: 64px;\"\u003e\n\u003cp\u003eWG/\u003c/p\u003e\n\u003cp\u003eNaOH\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd style=\"width: 41px;\"\u003e\n\u003cp\u003e2N/\u003c/p\u003e\n\u003cp\u003e10M\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd style=\"width: 84px;\"\u003e\n\u003cp\u003eGypsum 20g\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd style=\"width: 102px;\"\u003e\n\u003cp\u003eFGMSW-01b\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd style=\"width: 97.8125px;\"\u003e\n\u003cp\u003e\u0026nbsp;\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd style=\"width: 102.188px;\"\u003e\n\u003cp\u003eFGMSW-03b\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd style=\"width: 104px;\"\u003e\n\u003cp\u003eFGMSW-04b\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd style=\"width: 96px;\"\u003e\n\u003cp\u003eFGMSW-05b\u003c/p\u003e\n\u003c/td\u003e\n\u003c/tr\u003e\n\u003c/tbody\u003e\n\u003c/table\u003e\n\u003cp\u003eTable 5. Infrared Characteristic Bands Identified in FA and Geopolymers Specimens\u003c/p\u003e\n\u003ctable border=\"1\"\u003e\n\u003ctbody\u003e\n\u003ctr\u003e\n\u003ctd width=\"235\"\u003e\n\u003cp\u003e\u003cstrong\u003eWave number (cm\u003csup\u003e-1\u003c/sup\u003e)\u003c/strong\u003e\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd width=\"313\"\u003e\n\u003cp\u003e\u003cstrong\u003eCharacteristic bands\u003c/strong\u003e\u003c/p\u003e\n\u003c/td\u003e\n\u003c/tr\u003e\n\u003ctr\u003e\n\u003ctd width=\"235\"\u003e\n\u003cp\u003e460 - 550\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd width=\"313\"\u003e\n\u003cp\u003eplane and bending vibrations of Al-O/Si-O\u003c/p\u003e\n\u003c/td\u003e\n\u003c/tr\u003e\n\u003ctr\u003e\n\u003ctd width=\"235\"\u003e\n\u003cp\u003e603-618\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd width=\"313\"\u003e\n\u003cp\u003eFunctional group of AlO\u003csub\u003e2\u003c/sub\u003e\u003c/p\u003e\n\u003c/td\u003e\n\u003c/tr\u003e\n\u003ctr\u003e\n\u003ctd width=\"235\"\u003e\n\u003cp\u003e817-878 -1456\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd width=\"313\"\u003e\n\u003cp\u003e-CO\u003csub\u003e3\u003c/sub\u003e vibrations in CaCO\u003csub\u003e3\u003c/sub\u003e\u003c/p\u003e\n\u003c/td\u003e\n\u003c/tr\u003e\n\u003ctr\u003e\n\u003ctd width=\"235\"\u003e\n\u003cp\u003e970\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd width=\"313\"\u003e\n\u003cp\u003eStretching vibration mode of SI-O in CSH gel\u003c/p\u003e\n\u003c/td\u003e\n\u003c/tr\u003e\n\u003ctr\u003e\n\u003ctd width=\"235\"\u003e\n\u003cp\u003e1420-1472\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd width=\"313\"\u003e\n\u003cp\u003eSi-O vibrations\u003c/p\u003e\n\u003c/td\u003e\n\u003c/tr\u003e\n\u003ctr\u003e\n\u003ctd width=\"235\"\u003e\n\u003cp\u003e1660-1782\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd width=\"313\"\u003e\n\u003cp\u003eBending mode of H-O-H\u003c/p\u003e\n\u003c/td\u003e\n\u003c/tr\u003e\n\u003ctr\u003e\n\u003ctd width=\"235\"\u003e\n\u003cp\u003e2505-2519\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd width=\"313\"\u003e\n\u003cp\u003eC-O vibrations in CO\u003csub\u003e2\u003c/sub\u003e constrained in amorphous phase\u003c/p\u003e\n\u003c/td\u003e\n\u003c/tr\u003e\n\u003ctr\u003e\n\u003ctd width=\"235\"\u003e\n\u003cp\u003e3475 -3645\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd width=\"313\"\u003e\n\u003cp\u003eO-H stretching vibration of portlandite\u003c/p\u003e\n\u003c/td\u003e\n\u003c/tr\u003e\n\u003c/tbody\u003e\n\u003c/table\u003e"}],"fulltextSource":"","fullText":"","funders":[],"hasAdminPriorityOnWorkflow":false,"hasManuscriptDocX":true,"hasOptedInToPreprint":true,"hasPassedJournalQc":"","hasAnyPriority":false,"hideJournal":false,"highlight":"","institution":"","isAcceptedByJournal":false,"isAuthorSuppliedPdf":false,"isDeskRejected":"","isHiddenFromSearch":false,"isInQc":false,"isInWorkflow":false,"isPdf":false,"isPdfUpToDate":true,"isWithdrawnOrRetracted":false,"journal":{"display":true,"email":"
[email protected]","identity":"environmental-science-and-pollution-research","isNatureJournal":false,"hasQc":true,"allowDirectSubmit":false,"externalIdentity":"espr","sideBox":"Learn more about [Environmental Science and Pollution Research](https://www.springer.com/journal/11356)","snPcode":"11356","submissionUrl":"https://submission.nature.com/new-submission/11356/3","title":"Environmental Science and Pollution Research","twitterHandle":"","acdcEnabled":true,"dfaEnabled":true,"editorialSystem":"em","reportingPortfolio":"Springer Hybrid","inReviewEnabled":true,"inReviewRevisionsEnabled":false},"keywords":"Geopolymer, Solidification, Fly ash, Mine tailing, gypsum, mechanical strength, microstructure.","lastPublishedDoi":"10.21203/rs.3.rs-996321/v1","lastPublishedDoiUrl":"https://doi.org/10.21203/rs.3.rs-996321/v1","license":{"name":"CC BY 4.0","url":"https://creativecommons.org/licenses/by/4.0/"},"manuscriptAbstract":"\u003cp\u003eUsing geopolymerization to value mining wastes in order to meet construction demand is a sustainable and environmentally friendly strategy. Fly ash geopolymer materials have been developed to address environmental issues such as climate change caused by the emissions of CO\u003csub\u003e2\u003c/sub\u003e from coal fly ash plants, mining, and cement industry into the atmosphere. The main objective of this study is to study the feasibility of using mine tailings to produce environmentally friendly building materials (so-called geopolymer products) with excellent mechanical strength through fly-based geopolymer technology. Fly ash (F.A.) and mine tailings (M.T.) were utilized as raw materials and gypsum (G.Y.) as additives. Sodium hydroxide (NaOH) at (5-10M) and sodium silicate (water glass) constituted the alkaline solution and were added separately to the mixture. The mechanical property and microstructure of the geopolymers were assessed by performing the Unconfined Compressive Strength (UCS), Scanning Electron Microscopy (SEM), X-ray diffractions (XRD), and Fourier transforms infrared (FTIR). A 24 MPa was achieved at 10M NaOH with 100% F.A. Besides, low UCS values were obtained with only M.T. as a binder. The SEM imaging analysis confirmed similar results showing that the geopolymer specimens cured with 100% of F.A. at 10M NaOH with a moderate amount of gypsum are denser than those prepared without gypsum at 5M. The findings revealed that F.A., MT, and gypsum, together with the alkali reagents, influenced the geopolymerisation process. These factors responded effectively to the microstructural performance(increasing density), resulting in increased unconfined compressive strength.\u003c/p\u003e","manuscriptTitle":"Lead-Zinc Mine Tailings Valorization Through Fly Ash-Based Geopolymer for Building Material: Synthesis, Microstructure, and Mechanical Properties","msid":"","msnumber":"","nonDraftVersions":[{"code":1,"date":"2021-10-26 20:04:06","doi":"10.21203/rs.3.rs-996321/v1","editorialEvents":[{"type":"communityComments","content":0},{"type":"editorInvitedReview","content":"","date":"2021-10-21T19:27:02+00:00","index":0,"fulltext":""},{"type":"reviewersInvited","content":"","date":"2021-10-21T13:54:33+00:00","index":"","fulltext":""},{"type":"editorAssigned","content":"","date":"2021-10-19T17:11:39+00:00","index":"","fulltext":""},{"type":"submitted","content":"Environmental Science and Pollution Research","date":"2021-09-30T11:48:09+00:00","index":"","fulltext":""}],"status":"published","journal":{"display":true,"email":"
[email protected]","identity":"environmental-science-and-pollution-research","isNatureJournal":false,"hasQc":true,"allowDirectSubmit":false,"externalIdentity":"espr","sideBox":"Learn more about [Environmental Science and Pollution Research](https://www.springer.com/journal/11356)","snPcode":"11356","submissionUrl":"https://submission.nature.com/new-submission/11356/3","title":"Environmental Science and Pollution Research","twitterHandle":"","acdcEnabled":true,"dfaEnabled":true,"editorialSystem":"em","reportingPortfolio":"Springer Hybrid","inReviewEnabled":true,"inReviewRevisionsEnabled":false}}],"origin":"","ownerIdentity":"d330c2d9-f9d6-48ec-a205-e4acfe6cd8df","owner":[],"postedDate":"October 26th, 2021","published":true,"recentEditorialEvents":[],"rejectedJournal":[],"revision":"","amendment":"","status":"under-review","subjectAreas":[{"id":8101902,"name":"Environmental Chemistry"},{"id":8101903,"name":"Toxicology"}],"tags":[],"updatedAt":"2021-10-26T20:04:06+00:00","versionOfRecord":[],"versionCreatedAt":"2021-10-26 20:04:06","video":"","vorDoi":"","vorDoiUrl":"","workflowStages":[]},"version":"v1","identity":"rs-996321","journalConfig":"researchsquare"},"__N_SSP":true},"page":"/article/[identity]/[[...version]]","query":{"redirect":"/article/rs-996321","identity":"rs-996321","version":["v1"]},"buildId":"7rjqhiLT3MXkJMwkYKINL","isFallback":false,"isExperimentalCompile":false,"dynamicIds":[84888],"gssp":true,"scriptLoader":[]}
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