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Production Process of an Eco-Friendly One-Part Alkali-Activated Binder

Abstract

One-part alkali-activated binder (AAB) is a product with lower environmental impact than Portland cement, and can be a feasible commercial alternative. The main objective of this study was to propose and test a method of obtaining one-part AAB with metakaolin and an alternative powder sodium silicate from rice husk ash (RHA). To evaluate the AAB properties, mortars were produced with different SiO2/Al2O3 molar ratios (2.7, 3.1, and 3.3), and tests were conducted to characterize the binder. The results indicated that the process was efficient in generating a non-crystalline sodium silicate powdered material. With high SiO2/Al2O3 molar ratio the mortars achieved high compressive strength and it increased with age, had low permeability, and capillary water absorption. Compressive strength results varied from 6 MPa to 12 MPa at 28 days, indicating the possibility of using the proposed method for one-part AAB production. AAB produced can be applied in different building materials.

Keywords
: One-part alkali-activated binder ; production process; cement; alternative binder; cleaner production; sustainability

1. Introduction

Alkali-activated binder (AAB) can be considered one of the breakthroughs in concrete technology of the last century11 Nematollahi B, Sanjayan J, Shaikh FUA. Synthesis of heat and ambient cured one-part geopolymer mixes with different grades of sodium silicate. Ceram Int. 2015;41(4):5696-704. http://dx.doi.org/10.1016/j.ceramint.2014.12.154.
http://dx.doi.org/10.1016/j.ceramint.201...
. AAB is an alternative to Portland cement (PC), and it is formed by a chemical reaction between an alkali-activator with an aluminosilicate precursor22 Bernal SA, Provis JL. Durability of alkali-activated materials: progress and perspectives. J Am Ceram Soc. 2014;97(4):997-1008. http://dx.doi.org/10.1111/jace.12831.
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The environmental benefits of AAB have driven the interest in this cement. AAB production does not demand high calcination temperatures and the chemical reaction does not release CO233 McNulty E. Geopolymers: an environmental alternative to carbon dioxide producing ordinary Portland cement [Internet]. 2009 [cited 2021 Aug 28]. Available from: http://citeseerx.ist.psu.edu/viewdoc/download?doi=10.1.1.474.1240&rep=rep1&type=pdf
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,44 Provis JL. Geopolymers and other alkali activated materials: why, how, and what? Mater Struct. 2014;47(1–2):11-25. http://dx.doi.org/10.1617/s11527-013-0211-5.
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. According to Carreño-Gallardo et al.55 Carreño-Gallardo C, Tejeda-Ochoa A, Perez-Ordonez OI, Ledezma-Sillas JE, Lardizabal-Gutierrez D, Prieto-Gomez C, et al. In the CO2 emission remediation by means of alternative geopolymers as substitutes for cements. J Environ Chem Eng. 2018;6(4):4878-84. http://dx.doi.org/10.1016/j.jece.2018.07.033.
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, the replacement of PC by AAB can provide a reduction of up to 1480 million tons of CO2 per year. Accordingly, the reduction of CO2 emissions when compared to PC is one of the main facts that direct the researchers to pay attention to AAB66 Aiken TA, Kwasny J, Sha W, Soutsos MN. Effect of slag content and activator dosage on the resistance of fly ash geopolymer binders to sulfuric acid attack. Cement Concr Res. 2018;111:23-40. http://dx.doi.org/10.1016/j.cemconres.2018.06.011.
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There are two methods to AAB production. The two-part mixing is more usual in the literature, but the one-part mixing is a recent proposal of growing interest because of the commercialization feasibility and facility of using77 Provis JL. Alkali-activated materials. Cement Concr Res. 2018;114:40-8. http://dx.doi.org/10.1016/j.cemconres.2017.02.009.
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,88 Luukkonen T, Abdollahnejad Z, Yliniemi J, Kinnunen P, Illikainen M. One-part alkali-activated materials: a review. Cement Concr Res. 2018;103:21-34. http://dx.doi.org/10.1016/j.cemconres.2017.10.001.
http://dx.doi.org/10.1016/j.cemconres.20...
. In two-part mixing, the aluminosilicate precursor is a solid material, and the alkali-activator is an aqueous solution. These two parts are mixed to form the AAB. Differently, in one-part AAB the aluminosilicate source and the alkali activator are powders. One-part AAB is used in the same way of conventional PC: the dry materials are mixed with water, starting the binding reaction77 Provis JL. Alkali-activated materials. Cement Concr Res. 2018;114:40-8. http://dx.doi.org/10.1016/j.cemconres.2017.02.009.
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8 Luukkonen T, Abdollahnejad Z, Yliniemi J, Kinnunen P, Illikainen M. One-part alkali-activated materials: a review. Cement Concr Res. 2018;103:21-34. http://dx.doi.org/10.1016/j.cemconres.2017.10.001.
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9 Tigue AAS, Malenab RAJ, Dungca JR, Yu DEC, Promentilla MAB. Chemical stability and leaching behavior of one-part geopolymer from soil and coal fly ash mixtures. Minerals. 2018;8(9):411. http://dx.doi.org/10.3390/min8090411.
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-1010 Ma C, Zhao B, Guo S, Long G, Xie Y. Properties and characterization of green one-part geopolymer activated by composite activators. J Clean Prod. 2019;220:188-99. http://dx.doi.org/10.1016/j.jclepro.2019.02.159.
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The discovery of one-part AAB was a significant event in the development of eco-friendly cement1111 Abdollahnejad Z, Hlavacek P, Miraldo S, Pacheco-Torgal F, Aguiar JLB. Compressive strength, microstructure and hydration products of hybrid alkaline cements. Mater Res. 2014;17(4):829-37. http://dx.doi.org/10.1590/S1516-14392014005000091.
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. The one-part AAB does not need storage, management, and use of highly corrosive alkali-solutions in the worksite, which are very dangerous to the workers involved. This favors the commercialization and application of AAB in civil construction activities11 Nematollahi B, Sanjayan J, Shaikh FUA. Synthesis of heat and ambient cured one-part geopolymer mixes with different grades of sodium silicate. Ceram Int. 2015;41(4):5696-704. http://dx.doi.org/10.1016/j.ceramint.2014.12.154.
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,1212 Yu J, Chen Y, Chen G, Wang L. Experimental study of the feasibility of using anhydrous sodium metasilicate as a geopolymer activator for soil stabilization. Eng Geol. 2020;264:105316. http://dx.doi.org/10.1016/j.enggeo.2019.105316.
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,1313 Hajimohammadi A, Ngo T, Mendis P, Kashani A, van Deventer JSJ. Alkali activated slag foams: the effect of the alkali reaction on foam characteristics. J Clean Prod. 2017;147:330-9. http://dx.doi.org/10.1016/j.jclepro.2017.01.134.
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One-part AAB made with anhydrous sodium metasilicate as activator presented high compressive strength; however, the production of this chemical product has environmental impacts1212 Yu J, Chen Y, Chen G, Wang L. Experimental study of the feasibility of using anhydrous sodium metasilicate as a geopolymer activator for soil stabilization. Eng Geol. 2020;264:105316. http://dx.doi.org/10.1016/j.enggeo.2019.105316.
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,1414 Dong M, Elchalakani M, Karrech A. Development of high strength one-part geopolymer mortar using sodium metasilicate. Constr Build Mater. 2020;236:117611. http://dx.doi.org/10.1016/j.conbuildmat.2019.117611.
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,1515 Ma C, Zhao B, Wang L, Long G, Xie Y. Clean and low-alkalinity one-part geopolymeric cement: effects of sodium sulfate on microstructure and properties. J Clean Prod. 2020;252:119279. http://dx.doi.org/10.1016/j.jclepro.2019.119279.
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. The extra energy necessary to produce the solid activators makes one-part AAB more environmentally impacting than a two-part binder1616 Abdulkareem M, Havukainen J, Horttanainen M. Environmental assessment of alkali-activated mortars using different activators. In: 17th International Waste Management and Landfill Symposium [Internet]; 2019; Cagliari, Italy. Proceedings. Padova: EWA; 2019 [cited 2021 Aug 28]. Available from: http://urn.fi/URN:NBN:fi-fe2019120345430
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Within this scenario, researches have been conducted on alternative activators. Abdel-Gawwad et al.1717 Abdel-Gawwad HA, Mohammed MS, Ads EN. A novel eco-sustainable approach for the cleaner production of ready-mix alkali activated cement using industrial solid wastes and organic-based activator powder. J Clean Prod. 2020;256:120705. http://dx.doi.org/10.1016/j.jclepro.2020.120705.
http://dx.doi.org/10.1016/j.jclepro.2020...
proposed a new user-friendly activator powder obtained by thermal treatment at 60 °C of a mixture of sodium hydroxide and ethylene glycol. Granulated blast-furnace slag or slag-lead bearing sludge was mixed with the activator to originate one-part AAB. Pastes achieved considerable mechanical strength, with one-part AAB presenting a compressive strength 157% higher than two-part AAB at 180 days. In another research, Ma et al.1515 Ma C, Zhao B, Wang L, Long G, Xie Y. Clean and low-alkalinity one-part geopolymeric cement: effects of sodium sulfate on microstructure and properties. J Clean Prod. 2020;252:119279. http://dx.doi.org/10.1016/j.jclepro.2019.119279.
http://dx.doi.org/10.1016/j.jclepro.2019...
evaluated the partial replacement of sodium silicate anhydrous by sodium sulfate, aiming to achieve a cleaner one-part AAB. They found the use of sodium sulfate generated material with compressive strength higher than 15 MPa at 1 day and reduced the carbon footprint of AAB. Samarakoon et al.1818 Samarakoon MH, Ranjith PG, Duan WH, Silva VRS. Properties of one-part fly ash/slag-based binders activated by thermally-treated waste glass/NaOH blends: a comparative study. Cement Concr Compos. 2020;112:103679. http://dx.doi.org/10.1016/j.cemconcomp.2020.103679.
http://dx.doi.org/10.1016/j.cemconcomp.2...
obtained an alternative activator to commercial sodium silicate by mixing soda-lime glass powder and sodium hydroxide. They tested the solid activator with fly ash/ground granulated blast-furnace slag precursors in mortar production, and the results indicated compressive strength higher than 30 MPa at 28 days. The alternative solid activator showed to be cheaper and more environmentally friendly than commercial options.

The use of agro-industrial wastes, such as rice husk ash (RHA) due to the high volume generated and high reactive silica content, has a growing interest recently1919 Passuello A, Rodríguez ED, Hirt E, Longhi M, Bernal SA, Provis JL, et al. Evaluation of the potential improvement in the environmental footprint of geopolymers using waste-derived activators. J Clean Prod. 2017;166:680-9. http://dx.doi.org/10.1016/j.jclepro.2017.08.007.
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20 Abdulkareem M, Havukainen J, Nuortila-Jokinen J, Horttanainen M. Environmental and economic perspective of waste-derived activators on alkali-activated mortars. J Clean Prod. 2021;280:124651. http://dx.doi.org/10.1016/j.jclepro.2020.124651.
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-2121 Adesanya E, Perumal P, Luukkonen T, Yliniemi J, Ohenoja K, Kinnunen P, et al. Opportunities to improve sustainability of alkali-activated materials: a review of side-stream based activators. J Clean Prod. 2021;286:125558. http://dx.doi.org/10.1016/j.jclepro.2020.125558.
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. RHA has been applied in civil construction as supplementary cementitious material, and it has also been used to obtain alternative sodium silicate solutions to AAB production1919 Passuello A, Rodríguez ED, Hirt E, Longhi M, Bernal SA, Provis JL, et al. Evaluation of the potential improvement in the environmental footprint of geopolymers using waste-derived activators. J Clean Prod. 2017;166:680-9. http://dx.doi.org/10.1016/j.jclepro.2017.08.007.
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,2222 Sandhu RK, Siddique R. Influence of rice husk ash (RHA) on the properties of self-compacting concrete: a review. Constr Build Mater. 2017;153:751-64. http://dx.doi.org/10.1016/j.conbuildmat.2017.07.165.
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23 Tchakouté HK, Rüscher CH, Kong S, Kamseu E, Leonelli C. Geopolymer binders from metakaolin using sodium waterglass from waste glass and rice husk ash as alternative activators: a comparative study. Constr Build Mater. 2016;114:276-89. http://dx.doi.org/10.1016/j.conbuildmat.2016.03.184.
http://dx.doi.org/10.1016/j.conbuildmat....

24 Tchakouté HK, Rüscher CH, Kong S, Ranjbar N. Synthesis of sodium waterglass from white rice husk ash as an activator to produce metakaolin-based geopolymer cements. J Build Eng. 2016;6:252-61. http://dx.doi.org/10.1016/j.jobe.2016.04.007.
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25 Bernal SA, Rodríguez ED, Mejia De Gutiérrez R, Provis JL, Delvasto S. Activation of metakaolin/slag blends using alkaline solutions based on chemically modified silica fume and rice husk ash. Waste Biomass Valoriz. 2012;3(1):99-108. http://dx.doi.org/10.1007/s12649-011-9093-3.
http://dx.doi.org/10.1007/s12649-011-909...

26 Bouzón N, Payá J, Borrachero MV, Soriano L, Tashima MM, Monzó J. Refluxed rice husk ash/NaOH suspension for preparing alkali activated binders. Mater Lett. 2014;115:72-4. http://dx.doi.org/10.1016/j.matlet.2013.10.001.
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27 Mellado A, Catalán C, Bouzón N, Borrachero MV, Monzó JM, Payá J. Carbon footprint of geopolymeric mortar: study of the contribution of the alkaline activating solution and assessment of an alternative route. RSC Advances. 2014;4(45):23846-52. http://dx.doi.org/10.1039/C4RA03375B.
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28 Mejía JM, Mejía de Gutiérrez R, Montes C. Rice husk ash and spent diatomaceous earth as a source of silica to fabricate a geopolymeric binary binder. J Clean Prod. 2016;118:133-9. http://dx.doi.org/10.1016/j.jclepro.2016.01.057.
http://dx.doi.org/10.1016/j.jclepro.2016...

29 Kamseu E, Beleuk à Moungam LM, Cannio M, Billong N, Chaysuwan D, Melo UC, et al. Substitution of sodium silicate with rice husk ash-NaOH solution in metakaolin based geopolymer cement concerning reduction in global warming. J Clean Prod. 2017;142:3050-60. http://dx.doi.org/10.1016/j.jclepro.2016.10.164.
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30 Geraldo RH, Fernandes LFR, Camarini G. Water treatment sludge and rice husk ash to sustainable geopolymer production. J Clean Prod. 2017;149:146-55. http://dx.doi.org/10.1016/j.jclepro.2017.02.076.
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31 Teixeira OG, Geraldo RH, da Silva FG, Gonçalves JP, Camarini G. Mortar type influence on mechanical performance of repaired reinforced concrete beams. Constr Build Mater. 2019;217:372-83. http://dx.doi.org/10.1016/j.conbuildmat.2019.05.035.
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-3232 Tong KT, Vinai R, Soutsos MN. Use of Vietnamese rice husk ash for the production of sodium silicate as the activator for alkali-activated binders. J Clean Prod. 2018;201:272-86. http://dx.doi.org/10.1016/j.jclepro.2018.08.025.
http://dx.doi.org/10.1016/j.jclepro.2018...
. Commercial sodium silicate has a high carbon footprint and the use of alternative dissolved silica sources is important in environmental aspects2121 Adesanya E, Perumal P, Luukkonen T, Yliniemi J, Ohenoja K, Kinnunen P, et al. Opportunities to improve sustainability of alkali-activated materials: a review of side-stream based activators. J Clean Prod. 2021;286:125558. http://dx.doi.org/10.1016/j.jclepro.2020.125558.
http://dx.doi.org/10.1016/j.jclepro.2020...
. The activators are considered as the main problem related to AAB production because they are produced using expensive and polluting processes3333 Marvila MT, de Azevedo ARG, Vieira CMF. Reaction mechanisms of alkali-activated materials. IBRACON Struct Mater J. 2021;14(3):1-26. http://dx.doi.org/10.1590/S1983-41952021000300009.
http://dx.doi.org/10.1590/S1983-41952021...
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In this study, an alternative sodium silicate powder from RHA was proposed to make one-part AAB. The research aimed to test an innovative production method to produce a binder with cleaner production.

2. Materials and Methods

2.1. Materials

In the present investigation, it was used the precursor materials to make the AAB (metakaolin – MK, rice husk ash – RHA, and sodium hydroxide – NaOH) and natural river quartz sand to make the mortar to evaluate the AAB properties to building components.

Metakaolin (MK = “HP ultra” from Metacaulim do Brasil Indústria e Comércio Ltd.) and rice husk ash (RHA = “Silcca Nobre” from Sílica Verde do Arroz Ltd.) were the aluminosilicate sources. The two solid precursors are commercial products, and they were employed without any additional processing.

Chemical composition, physical characteristics, and particle size distribution of the MK and RHA are shown in Table 1 and Figure 1. The chemical compositions were determined using X-ray fluorescence (XRF) (equipment: Bruker FRX S8-Tiger). Particle size distribution was carried out with a laser diffraction particle size analyzer (Malvern Mastersizer 3000).

Table 1
Chemical composition and physical properties of metakaolin (MK) and rice husk ash (RHA).
Figure 1
Frequency (a) and cumulative (b) distribution of the solid precursor.

MK is mainly composed of SiO2 and Al2O3, which represent more than 90% of the total composition. According to Poon et al.3434 Poon CS, Lam L, Kou SC, Wong YL, Wong R. Rate of pozzolanic reaction of metakaolin in high-performance cement pastes. Cement Concr Res. 2001;31(9):1301-6. http://dx.doi.org/10.1016/S0008-8846(01)00581-6.
http://dx.doi.org/10.1016/S0008-8846(01)...
, MK is typically composed of 50–55% SiO2 and 40–45% Al2O3. TiO2 is a common impurity presented in MK and the content found was similar to other researches3535 Kriven WM, Bell JL, Mallicoat SW, Gordon M. Intrinsic microstructure and properties of metakaolin-based geoolymers. In: International Worshop on Geopolymer Binders: Interdependence of Composition, Structure and Properties; 2007; Weimar, Germany. Proceedings. Germany: Shaker; 2007. p. 71-86.,3636 Rocha TS, Dias DP, França FCC, Guerra RRS, Marques LRCO. Metakaolin-based geopolymer mortars with different alkaline activators (Na+ and K+). Constr Build Mater. 2018;178:453-61. http://dx.doi.org/10.1016/j.conbuildmat.2018.05.172.
http://dx.doi.org/10.1016/j.conbuildmat....
. Considering the physical properties, Rashad3737 Rashad AM. Metakaolin as cementitious material: History, scours, production and composition: a comprehensive overview. Constr Build Mater. 2013;41:303-18. http://dx.doi.org/10.1016/j.conbuildmat.2012.12.001.
http://dx.doi.org/10.1016/j.conbuildmat....
presented that typical values of bulk density and specific mass of MK are 2600 kg/m3 and 300-400 kg/m3, respectively. The obtained results indicated that MK used in the present study is slightly denser. The high content of SiO2 in RHA (> 90%) was also observed by Tong et al.3232 Tong KT, Vinai R, Soutsos MN. Use of Vietnamese rice husk ash for the production of sodium silicate as the activator for alkali-activated binders. J Clean Prod. 2018;201:272-86. http://dx.doi.org/10.1016/j.jclepro.2018.08.025.
http://dx.doi.org/10.1016/j.jclepro.2018...
and indicates the feasibility of using it as a silica source, which tends to be reactive and suitable to AAB production3838 Darsanasiri AGND, Matalkah F, Ramli S, Al-Jalode K, Balachandra A, Soroushian P. Ternary alkali aluminosilicate cement based on rice husk ash, slag and coal fly ash. J Build Eng. 2018;19:36-41. http://dx.doi.org/10.1016/j.jobe.2018.04.020.
http://dx.doi.org/10.1016/j.jobe.2018.04...
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X-ray diffraction (XRD) patterns of MK and RHA are shown in Figure 2. Equipment Bruker – S8 x-ray diffractometer with CuKα radiation at 40 kV and 40 mA, from 5-60° 2θ by scanning at 0.02° seg-1 was employed for XRD measurements. The identification of phases was carried out with X'Pert HighScore Plus version 3.0.5 and GSAS II version 3913 software. Inorganic Crystal Structure Database (ICSD) and Crystallography Open Database (COD) were used to identify the crystalline peaks.

Figure 2
XRD patterns of MK (a) and RHA (b).

XRD patterns indicate the mineral composition of MK (Figure 2a) is kaolinite (Al2O3·2SiO2·2H2O, COD ID: 9009234), muscovite (KAl3Si3O10(OH)2, COD ID: 9005014), and quartz (SiO2, ICSD PDF: 01-085-0457). The range between 18° and 35° 2θ is related to non-crystalline phases with some peaks attributed to impurities as quartz2323 Tchakouté HK, Rüscher CH, Kong S, Kamseu E, Leonelli C. Geopolymer binders from metakaolin using sodium waterglass from waste glass and rice husk ash as alternative activators: a comparative study. Constr Build Mater. 2016;114:276-89. http://dx.doi.org/10.1016/j.conbuildmat.2016.03.184.
http://dx.doi.org/10.1016/j.conbuildmat....
. RHA (Figure 2b) had a peak at 21.8° 2θ attributed to cristobalite (SiO2, COD ID: 9008225), a quartz polymorph formed during combustion2828 Mejía JM, Mejía de Gutiérrez R, Montes C. Rice husk ash and spent diatomaceous earth as a source of silica to fabricate a geopolymeric binary binder. J Clean Prod. 2016;118:133-9. http://dx.doi.org/10.1016/j.jclepro.2016.01.057.
http://dx.doi.org/10.1016/j.jclepro.2016...
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Sodium hydroxide (NaOH) in flakes (Unipar Carbocloro S.A., 97.5% purity) was employed as activator, and water from the municipal supply was used for its dissolution.

Natural river quartz sand locally available was used as fine aggregate with specific mass of 2609 kg/m3, bulk density of 1890 kg/m3, fineness modulus of 2.38, and maximum particle size of 2.4 mm. Figure 3 shows the particle size distribution of the sand.

Figure 3
Particle size distribution of sand.

2.2. Mortars: mix design, production, and curing method

The mortar mix proportions are presented in Table 2.

Table 2
Mix design (in weight).

The theoretical SiO2/Al2O3 molar ratio was varied to compare the influence of chemical composition on the properties of one-part AAB. In the literature, one-part AAB has been produced with SiO2/Al2O3 molar ratios ranging between 0.75 – 6.0288 Luukkonen T, Abdollahnejad Z, Yliniemi J, Kinnunen P, Illikainen M. One-part alkali-activated materials: a review. Cement Concr Res. 2018;103:21-34. http://dx.doi.org/10.1016/j.cemconres.2017.10.001.
http://dx.doi.org/10.1016/j.cemconres.20...
. In the present study, SiO2/Al2O3 molar ratios of 2.7, 3.1, and 3.3 (considering total solubility of raw materials) were used. The range employed was close to 3.0, considering the results of Bernal et al.2525 Bernal SA, Rodríguez ED, Mejia De Gutiérrez R, Provis JL, Delvasto S. Activation of metakaolin/slag blends using alkaline solutions based on chemically modified silica fume and rice husk ash. Waste Biomass Valoriz. 2012;3(1):99-108. http://dx.doi.org/10.1007/s12649-011-9093-3.
http://dx.doi.org/10.1007/s12649-011-909...
, which used MK and RHA to produce AAB. Na2O/Al2O3 and H2O/Na2O molar ratios were kept constant in all the specimens by using extra NaOH or RHA in some mixtures to adjust the initial chemical composition. The binder/sand ratio was equal to 1:2.

To prepare the mortars, the solid one-part AAB and sand were put in a mechanical mixer (equipment: Perfecta; capacity: 20 L) for 2 min at slow speed until homogenization. Thereafter, water was gradually put in the mixture followed by continuous mixing (medium speed) for more 5 min. The homogenized fresh mortar was immediately transferred to the molds, which were subjected to vibration (vibrating table) for 1 min to eliminate the entrapped air.

After casting, the molds were placed in a laboratory room with temperature of 25 °C ± 2 °C and relative humidity of 60% ± 5%. The specimens were demolded after 3 days of curing and stored in a sealed container in laboratory conditions until testing.

2.3 Methods

2.3.1. Thermogravimetry (TG), derivative thermogravimetry (DTG), and differential thermal analysis (DTA)

Thermal analysis (TG/DTG/DTA) was carried out in a DTG 60H Shimadzu simultaneous TG/DTA apparatus using about 10 g of the sample in a platinum crucible. The heating rate of 10 °C min-1 was used from 25 °C to 1000 °C under a nitrogen flow of 50 mL min-1.

2.3.2. Specific mass, bulk density, and pH

Specific mass (Le Chatelier flask) and bulk density of the powders were determined by adapting Brazilian Standards NBR 166053939 ABNT: Associação Brasileira de Normas Técnicas. ABNT NBR 16605: Portland cement and other powdered material: determination of the specific gravity. Rio de Janeiro: ABNT; 2017. 4 p. used for PC and NBR 121274040 ABNT: Associação Brasileira de Normas Técnicas. ABNT NBR 12127: gypsum for buildings: determination of physical properties of powder. Rio de Janeiro: ABNT; 2019. 6 p. used for gypsum plaster.

The pH of the powdered materials was estimated employing the method described to determine soil pH4141 EMBRAPA: Empresa Brasileira de Pesquisa Agropecuária. Manual de métodos de análise de solo. 2. ed. Rio de Janeiro: EMBRAPA; 1997. 212 p.. A 10 mL sample was mixed with 25 mL of distilled water. The mixture remained to stand for 1 h, before determining the pH (equipment: Thermo Orion 410).

2.3.3. Flow and heat release

A flow table test was used to determine the workability of the mortars. The test was made following NBR 132764242 ABNT: Associação Brasileira de Normas Técnicas. ABNT NBR 13276: mortars applied on walls and ceilings: determination of the consistence index. Rio de Janeiro: ABNT; 2016. 2 p..

The heat released was registered immediately after the addition of water in the mortar. The specimens were molded in expanded polystyrene (EPS) thermal cup of 120 mL. The material was placed inside an EPS container filled with expansive polyurethane foam, aiming to achieve higher temperature insulation from the internal environment. In the central part of the specimens was inserted a thermocouple (K-type) to register the temperature through a data acquisition system (equipment: datalogger Testo 177-T4). The container with the mortars was kept in ambient conditions (average temperature registered during all the test time of 20.9 °C ± 2 °C). Data were saved each 22 s during the total time of 2000 min.

2.3.4. Mechanical properties and statistical analysis

To evaluate the importance of RHA dissolution (step 1 of one-part AAB synthesis, as presented in results), cubic mortars (40 mm × 40 mm × 40 mm) were molded (mix proportion in grams = 42 alternative powder sodium silicate (APSS); 80 MK; 244 sand; and 66.3 water) and subjected to compressive strength test. Specimens were prepared with and without the previously RHA dissolution system proposed (heating and stirring) and the test was carried out in a Versa Tester machine (maximum load of 150 kN) at the ages of 3, 7, 28, 90, and 180 days.

Mechanical properties of mortars were evaluated by flexural and compressive strength tests at the ages of 3, 7, 28, 90, and 180 days (compressive strength) or 3, 28, and 90 days (flexural strength). The specimens were tested in a Versa Tester machine (maximum load of 150 kN). Cubic samples (40 mm × 40 mm × 40 mm) were molded to the compressive strength test, which was obtained by the maximum load divided by the sample area4343 ABNT: Associação Brasileira de Normas Técnicas. ABNT NBR 15961-2: structural masonry: concrete blocks part 2: execution and site control. Rio de Janeiro: ABNT; 2011. 35 p.. Prismatic samples (40 mm × 40 mm × 160 mm) were molded to flexural strength test, obtained by the three-point-bending test4444 ABNT: Associação Brasileira de Normas Técnicas. ABNT NBR 13279: mortars applied on walls and ceilings: determination of the flexural and the compressive strength in the hardened stage. Rio de Janeiro: ABNT; 2005. 9 p..

Analysis of variance (ANOVA) (Microsoft Excel® software) and Least Square Difference (LSD) (Statgraphics Centurion® software) were made with a 95% confidence limit to compare the treatments.

2.3.5. Air permeability and capillary water absorption

Air permeability of the mortars was evaluated according to Thenoz method, such as presented by Geraldo et al.3030 Geraldo RH, Fernandes LFR, Camarini G. Water treatment sludge and rice husk ash to sustainable geopolymer production. J Clean Prod. 2017;149:146-55. http://dx.doi.org/10.1016/j.jclepro.2017.02.076.
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.

Cylindrical specimens (50 mm diameter and 100 mm height) were prepared and cured at room temperature for 25 days (average temperature of 25 °C ± 2 °C and relative humidity of 60% ± 5%). At this age, the specimens were cut into three parts and the central part slice (50 mm height) was oven-dried (60 °C ± 2 °C) for 48 h and after cooling they had their lateral surfaces sealed to guarantee the flow was uniaxial and perpendicular to the cross-sectional area. The test was developed at 28 days in a varying charge apparatus. The average values of three specimens of each mortar composition were reported. Air permeability was calculated with Equation 1, which is based on Darcy’s law.

k = μ . s .1 / ρ . g . t . S . l n h 0 / h 1 (1)

Where: k = air permeability coefficient (m2); μ = air viscosity at the test temperature (Pa.s); ρ = density of water (kg/m3); g = gravity acceleration (m/s2); S = cross-sectional area of the sample (m2); s = cross-sectional area of capillary tube (m2); h0 = start water level (m); h1 = final water level (m); 1 = sample height (m); and t = testing time (s) (time to water pass from h0 to h1).

A capillary water absorption test was performed on cylindrical specimens (50 mm diameter and 100 mm height) at 28 days. The average values of three specimens for each mortar composition were reported and the test was based on NBR 97794545 ABNT: Associação Brasileira de Normas Técnicas. ABNT NBR 9779: mortar and hardened concrete: determination of water absorption by capillarity. Rio de Janeiro: ABNT; 2012. 3 p. with some modifications, as follows.

The specimens were oven-dried (60 °C ± 2 °C) for 48 h. Thereafter, the samples were weighed and had their lateral surfaces sealed before testing to have the water flow perpendicular to the cross-sectional area. The specimens were partially immersed in water (5 mm ± 1 mm) and the water uptake into the specimens was evaluated at 5 min, 10 min, 15 min, 30 min, 1 h, 2 h, 4 h, 6 h, 8 h, and 24 h. Capillary water absorption was calculated with Equation 2.

C w a = H m D m / S (2)

Where: Cwa = capillary water absorption (kg/m2); Hm = humid mass (kg); Dm = oven-dried mass (kg); and S = cross-sectional area of the specimen (m2).

2.3.6. Scanning electron microscopy (SEM) observations

Scanning electron microscopy (SEM) by secondary electron images were obtained on fractured surfaces from compressive strength test specimens. The images were observed on LEO Electron Microscopy/Oxford 440i with 20 kV and 100 pA. The equipment contained X-ray dispersive energy detector (EDS) and chemical analysis was performed. The samples were coated with gold before SEM observations.

3. Results and Discussions

3.1. Synthesis of one-part AAB

The method to one-part AAB obtaining was divided into steps as shown in Figure 4 and described, as follows.

Figure 4
Steps to production of one-part AAB proposed.

3.1.1. Alternative powder sodium silicate (APSS) production

The APSS production comprises steps 1 to 3 (Figure 4).

Step 1-RHA silica dissolution: RHA was blended into a NaOH solution. The mix proportion employed was equal to (in mass) 1 NaOH : 1.605 water : 1.284 RHA. The mixture was put in a magnetic stirrer (equipment: Fisatom 752A) with heating (90 °C ± 5 °C) for 30 min, following the process described by Geraldo et al.3030 Geraldo RH, Fernandes LFR, Camarini G. Water treatment sludge and rice husk ash to sustainable geopolymer production. J Clean Prod. 2017;149:146-55. http://dx.doi.org/10.1016/j.jclepro.2017.02.076.
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to produce two-part AAB. Due to the high viscosity of the material, it was used another mechanical stirrer (equipment: Fisatom 713D, rotation range: 500-600 rpm) equipped with a stainless-steel stem to maintain the mixing.

The liquid material originated in this step had high viscosity and density = 1600 kg/m3, pH = 14, total solid content = 65%, and humidity content = 35%.

The main objective of this step is to use RHA as a source of silica to synthesis an alternative sodium silicate (ASS)2121 Adesanya E, Perumal P, Luukkonen T, Yliniemi J, Ohenoja K, Kinnunen P, et al. Opportunities to improve sustainability of alkali-activated materials: a review of side-stream based activators. J Clean Prod. 2021;286:125558. http://dx.doi.org/10.1016/j.jclepro.2020.125558.
http://dx.doi.org/10.1016/j.jclepro.2020...
,2727 Mellado A, Catalán C, Bouzón N, Borrachero MV, Monzó JM, Payá J. Carbon footprint of geopolymeric mortar: study of the contribution of the alkaline activating solution and assessment of an alternative route. RSC Advances. 2014;4(45):23846-52. http://dx.doi.org/10.1039/C4RA03375B.
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, first in liquid phase (ASS) and in powder (APSS) in this work. Different results in the literature indicate the suitability of using RHA to obtain an ASS3232 Tong KT, Vinai R, Soutsos MN. Use of Vietnamese rice husk ash for the production of sodium silicate as the activator for alkali-activated binders. J Clean Prod. 2018;201:272-86. http://dx.doi.org/10.1016/j.jclepro.2018.08.025.
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.

Step 2-Oven-drying: The material from step 1 was collected and spread in a rectangular aluminum tray (thickness = ~5 mm). This viscous liquid was oven-dried (temperature of 200 °C ± 10 °C for 3 h) in a stationary kiln with air circulation. Different preliminary trials were carried out with lower drying temperatures (50 °C, 100°, 150 °C); however, during this process, a film was formed over the material layer, which prevented water evaporation. Because of it, a temperature of 200 °C was employed. To compare, Vinai and Soutsos4646 Vinai R, Soutsos M. Production of sodium silicate powder from waste glass cullet for alkali activation of alternative binders. Cement Concr Res. 2019;116:45-56. http://dx.doi.org/10.1016/j.cemconres.2018.11.008.
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made the oven-dry process to obtain a reactive powder using the temperature of 330 °C for 2 h, revealing higher temperatures may decrease the total dry time.

Step 3-Grinding and homogenization: during this process, the dried material from step 2 was grounded in a porcelain ball mill until reaching a fineness to pass through a 0.075 mm sieve opening. The resultant material was manually homogenized using a plastic container, and it was designed as APSS.

Table 3 and Figure 5 show the chemical composition of APSS obtained by XRF and the XRD pattern of APSS, respectively.

Table 3
Chemical composition of alternative sodium silicate (APSS) in powder.
Figure 5
XRD results of APSS (a) and XRD of RHA and APSS (b).

XRF revealed that APSS is predominantly composed of silica, derived from RHA, and sodium, derived from NaOH. SiO2 and Na2O represent more than 85% of the APSS total chemical composition. The APSS silica modulus Ms SiO2/Na2O molar ratio was equal to 1.69, a value higher than the silica modulus of 1.25 stated by Gado et al.4747 Gado RA, Hebda M, Lach M, Mikula J. Alkali activation of waste clay bricks: Influence of the silica modulus, SiO2/Na2O, H2O/Na2O molar ratio, and liquid/solid ratio. Materials . 2020;13(2):383. http://dx.doi.org/10.3390/ma13020383.
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as an optimum condition to alkali-activation of waste clay bricks. APSS had a pH of 13.26.

XRD shows a low-crystalline material, indicating a reactive powder. Step 1 (dissolution of NaOH + RHA) was efficient in breaking the cristobalite peak, as indicated by Mejía et al.2828 Mejía JM, Mejía de Gutiérrez R, Montes C. Rice husk ash and spent diatomaceous earth as a source of silica to fabricate a geopolymeric binary binder. J Clean Prod. 2016;118:133-9. http://dx.doi.org/10.1016/j.jclepro.2016.01.057.
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. This crystal has a high dissolution susceptibility to being removed by an alkaline source. The crystalline phases in APSS revealed by XRD peaks were identified as NaOH(H2O) (COD ID: 1532133), Na2(Si2O5) (COD ID: 1533028), and Na2SiO3 (COD ID: 2310858). Considering the chemical stoichiometry and the products identified by XRD, the products were formed following the overall chemical reactions in solution (Reactions 1 to 4).

2 N a O H N a 2 O + H 2 O (1)
N a 2 O + H 2 O + S i O 2 N a 2 S i O 3 + H 2 O (2)
N a 2 S i O 3 + S i O 2 N a 2 S i 2 O 5 (3)
N a 2 O + 2 H 2 O 2 N a O H H 2 O (4)

Reaction 1 represents NaOH in flakes dissolved in water4848 Hardjito D, Wallah SE, Sumajouw DMJ, Rangan BV. Factors influencing the compressive strength of fly ash-based geopolymer concrete. Civ Eng Dimension [serial on the Internet]. 2004 [cited 2021 Aug 28];6(2):88-93. Available from: https://ced.petra.ac.id/index.php/civ/article/download/16116/16108
https://ced.petra.ac.id/index.php/civ/ar...
. NaOH solution dissolves the RHA silica to form sodium silicate, as shown in Reaction 22121 Adesanya E, Perumal P, Luukkonen T, Yliniemi J, Ohenoja K, Kinnunen P, et al. Opportunities to improve sustainability of alkali-activated materials: a review of side-stream based activators. J Clean Prod. 2021;286:125558. http://dx.doi.org/10.1016/j.jclepro.2020.125558.
http://dx.doi.org/10.1016/j.jclepro.2020...
,4646 Vinai R, Soutsos M. Production of sodium silicate powder from waste glass cullet for alkali activation of alternative binders. Cement Concr Res. 2019;116:45-56. http://dx.doi.org/10.1016/j.cemconres.2018.11.008.
http://dx.doi.org/10.1016/j.cemconres.20...
. The Na2SiO3 and Na2(Si2O5) phases are sodium silicate from RHA and NaOH. It indicates that the procedure for RHA silica dissolution was efficient.

TG curves (Figure 6) indicated a continuous mass loss, more pronounced at 200 °C – 350 °C, with a DTG peak at 282 °C, due to the water loss. There was a low endothermic DTA peak at 800 °C, which can be attributed to calcium carbonate decomposition4949 Fernandes IJ, Sánchez FAL, Jurado JR, Kieling AG, Rocha TLAC, Moraes CAM, et al. Physical, chemical and electric characterization of thermally treated rice husk ash and its potential application as ceramic raw material. Adv Powder Technol. 2017;28(4):1228-36. http://dx.doi.org/10.1016/j.apt.2017.02.009.
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. Another exothermic DTA peak at 858 °C can be related to the β-tridymite formation derived from the silica heating at the range of 870 °C5050 Pagliari L, Dapiaggi M, Pavese A, Francescon F. A kinetic study of the quartz-cristobalite phase transition. J Eur Ceram Soc. 2013;33(15-16):3403-10. http://dx.doi.org/10.1016/j.jeurceramsoc.2013.06.014.
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.

Figure 6
TG/DTG/DTA curves of APSS.

3.1.2. One-part AAB

The production of one-part AAB, after the APSS production, comprises steps 4 and 5.

Step 4-MK addition and homogenization: MK was added to APSS in determined proportions, and the powders were manually mixed in a sealed container until complete homogenization.

Step 5-One-part AAB: after the process described, the one-part AAB was obtained, and it was ready to be used only with the water addition. Considering the three different SiO2/Al2O3 molar ratios tested in this study and Table 4 shows some characteristics of the obtained binders.

Table 4
Characteristics of the one-part AAB produced considering the theoretical SiO2/Al2O3 molar ratio.

The results indicated that the physical properties of the binders B_3.1 and C_3.3 were similar. A_2.7 presented a slightly higher pH due to the incorporation of extra NaOH, used to correct the molar Na2O/Al2O3 ratio. The values of pH are very close to that presented by PC, which is around 135151 Bertolini L, Carsana M, Cassago D, Quadrio Curzio A, Collepardi M. MSWI ashes as mineral additions in concrete. Cement Concr Res. 2004;34(10):1899-906. http://dx.doi.org/10.1016/j.cemconres.2004.02.001.
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.

3.2. Importance of RHA silica dissolution (step 1)

Figure 7 shows the effect of step 1 (RHA silica dissolution with heating and stirring) on compressive strength of mortars, comparing results with mortars made with an equivalent system, but just adding RHA into NaOH solution and going on with other processes.

Figure 7
Influence of RHA dissolution step in the compressive strength of mortars made with one-part AAB.

The results indicated that the RHA dissolution by heating and mixing is important in strength development. The mortar made with one-part AAB produced with RHA dissolution (step 1) achieved a compressive strength 2.8 times higher than the mortar made just by mixing RHA into NaOH solution and following the next steps. The difference is because the steps (heating and mixing) to prepare APSS supplied a higher amount of amorphous silicate, which contributed to the mechanical strength development, as explained by Autef et al.5252 Autef A, Joussein E, Gasgnier G, Rossignol S. Role of the silica source on the geopolymerization rate ALL or. J Non-Cryst Solids. 2012;358(21):2886-93. http://dx.doi.org/10.1016/j.jnoncrysol.2012.07.015.
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.

RHA dissolution also provided a higher strength increases over time. The chemical mechanism of APSS to dissolve the aluminosilicate precursor (metakaolin) is expected to be similar to the activator containing only NaOH, the difference is that APSS accelerates the reaction by supplying soluble silicate from the activator2121 Adesanya E, Perumal P, Luukkonen T, Yliniemi J, Ohenoja K, Kinnunen P, et al. Opportunities to improve sustainability of alkali-activated materials: a review of side-stream based activators. J Clean Prod. 2021;286:125558. http://dx.doi.org/10.1016/j.jclepro.2020.125558.
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.

3.3 Mortars made with one-part AAB containing different SiO2/Al2O3 molar ratios

The flow table test indicated A_2.7, B_3.1, and C_3.3 with flows of 130 mm, 129 mm, and 124 mm, respectively. The results indicated that all mortars had low workability. The workability of mortars was similar, with a low spread diameter. This can be explained by the physical characteristics of the powder binder used (e.g. water absorption, grain size) and the water content that was not sufficient to reach good workability.

Figure 8 shows the results of heat evolution curves of mortars immediately after water addition.

Figure 8
Heat evolution curves of the mortars made with the one-part AAB immediately after water addition (a) with magnification from 21 °C to 33 °C (b) (average ambient temperature during the test = 20.9 °C ± 2 °C).

The temperature registered with time indicated an exothermic chemical reaction (heat release). The heat curves of B_3.1 and C_3.3 presented a similar pattern and reached the maximum temperatures registered after about 1 h. The use of additional NaOH in A_2.7 did not result in an acceleration of chemical reactions, differently, the curves indicated that in this sample there was a lower heat releasing and the reaction occurred slower, where the maximum temperature delayed 4 times more than the other AAB mix designs.

Each curve presented only one maximum temperature peak, a result similar to that obtained by Longhi et al.5353 Longhi MA, Rodríguez ED, Bernal SA, Provis JL, Kirchheim AP. Valorisation of a kaolin mining waste for the production of geopolymers. J Clean Prod. 2016;115:265-72. http://dx.doi.org/10.1016/j.jclepro.2015.12.011.
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and Geraldo et al.3030 Geraldo RH, Fernandes LFR, Camarini G. Water treatment sludge and rice husk ash to sustainable geopolymer production. J Clean Prod. 2017;149:146-55. http://dx.doi.org/10.1016/j.jclepro.2017.02.076.
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with two-part AAB. The peak presented in the curves is related to the chemical reactions of dissolution and polycondensation from alkaline activation, which happen almost at the same time5353 Longhi MA, Rodríguez ED, Bernal SA, Provis JL, Kirchheim AP. Valorisation of a kaolin mining waste for the production of geopolymers. J Clean Prod. 2016;115:265-72. http://dx.doi.org/10.1016/j.jclepro.2015.12.011.
http://dx.doi.org/10.1016/j.jclepro.2015...
,5454 Sagoe-Crentsil K, Weng L. Dissolution processes, hydrolysis and condensation reactions during geopolymer synthesis: part II. High Si/Al ratio systems. J Mater Sci. 2007;42(9):3007-14. http://dx.doi.org/10.1007/s10853-006-0818-9.
http://dx.doi.org/10.1007/s10853-006-081...
.

Figure 9 shows the results of compressive strength (Figure 9a) and flexural strength (Figure 9b) of the mortars, respectively. ANOVA indicated there was a significant difference among the data set considering flexural or compressive strength results (p-value ≤ 0.05 and Fcrit < F). Table 5 shows the analysis obtained by the Least Square Difference (LDS) to compare the treatments.

Figure 9
Compressive (a) and flexural (b) strengths of mortars made with the one-part AAB.
Table 5
LSD test with a 95% confidence limit.

The results indicated that compressive strengths increased with time. The increase was more evidenced in B_3.1 and C_3.3, while A_2.7 did not obtain a significant increase after 28 days. The compressive strength from 3 to 90 days of A_2.7, B_3.1, and C_3.3 increased in the order of 2.4, 2.6, and 2.2 times, respectively. The strength development may be related to the slow RHA silica dissolution when the binder is mixed with water. As showed by Luukkonen et al.5555 Luukkonen T, Abdollahnejad Z, Yliniemi J, Kinnunen P, Illikainen M. Comparison of alkali and silica sources in one-part alkali-activated blast furnace slag mortar. J Clean Prod. 2018;187:171-9. http://dx.doi.org/10.1016/j.jclepro.2018.03.202.
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, the slow silica availability results in continuous gain strength by increasing the degree of reaction.

The mechanical strength of the mortars also increased with the higher SiO2/Al2O3 molar ratios used, indicating the importance of the initial composition. Statistics indicate a significant difference in compressive strength according to SiO2/Al2O3 molar ratio in most of the curing times. Considering flexural strength, the specimens B_3.1 and C_3.3 did not present significant differences.

In the literature, other authors reported strength increasing with higher SiO2/Al2O3 molar ratio to AAB production5656 Silva PD, Sagoe-Crenstil K, Sirivivatnanon V. Kinetics of geopolymerization: role of Al2O3 and SiO2. Cement Concr Res. 2007;37(4):512-8. http://dx.doi.org/10.1016/j.cemconres.2007.01.003.
http://dx.doi.org/10.1016/j.cemconres.20...
,5757 Çetintaş R, Soyer-Uzun S. Relations between structural characteristics and compressive strength in volcanic ash based one-part geopolymer systems. J Build Eng. 2018;20:130-6. http://dx.doi.org/10.1016/j.jobe.2018.07.011.
http://dx.doi.org/10.1016/j.jobe.2018.07...
. The strength increase is associated with higher Si-O-Si bonds and lower Si-O-Al bonds formation, derived from the more significant degree of SiO2 available. The three-dimensional networks Si-O-Si bonds have more strength than Si-O-Al bonds, resulting in a material with improved mechanical strength with denser and more homogeneous microstructures5656 Silva PD, Sagoe-Crenstil K, Sirivivatnanon V. Kinetics of geopolymerization: role of Al2O3 and SiO2. Cement Concr Res. 2007;37(4):512-8. http://dx.doi.org/10.1016/j.cemconres.2007.01.003.
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57 Çetintaş R, Soyer-Uzun S. Relations between structural characteristics and compressive strength in volcanic ash based one-part geopolymer systems. J Build Eng. 2018;20:130-6. http://dx.doi.org/10.1016/j.jobe.2018.07.011.
http://dx.doi.org/10.1016/j.jobe.2018.07...
-5858 Duxson P, Provis JL, Lukey GC, Mallicoat SW, Kriven WM, Van Deventer JSJ. Understanding the relationship between geopolymer composition, microstructure and mechanical properties. Colloids Surf A Physicochem Eng Asp. 2005;269(1-3):47-58. http://dx.doi.org/10.1016/j.colsurfa.2005.06.060.
http://dx.doi.org/10.1016/j.colsurfa.200...
.

The maximum compressive strength achieved was ~18 MPa at 180 days, which was lower than other literature values about one-part AAB. Mortars produced with AAB achieved lower compressive strength than mortars in a two-part method produced by Geraldo et al.3030 Geraldo RH, Fernandes LFR, Camarini G. Water treatment sludge and rice husk ash to sustainable geopolymer production. J Clean Prod. 2017;149:146-55. http://dx.doi.org/10.1016/j.jclepro.2017.02.076.
http://dx.doi.org/10.1016/j.jclepro.2017...
and Teixeira et al.3131 Teixeira OG, Geraldo RH, da Silva FG, Gonçalves JP, Camarini G. Mortar type influence on mechanical performance of repaired reinforced concrete beams. Constr Build Mater. 2019;217:372-83. http://dx.doi.org/10.1016/j.conbuildmat.2019.05.035.
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using similar materials. The authors reported compressive strength in the range of 29 MPa – 40 MPa at 28 days. Nevertheless, the data indicate that the one-part AAB proposed generated material with binding properties and compressive strength higher than required for non-structural applications, such as mortars for components and rendering5959 Maddalena R, Roberts JJ, Hamilton A. Can Portland cement be replaced by low-carbon alternative materials? A study on the thermal properties and carbon emissions of innovative cements. J Clean Prod. 2018;186:933-42. http://dx.doi.org/10.1016/j.jclepro.2018.02.138.
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. According to Brazilian standards, the minimum compressive strengths for some applications are: ceramic bricks = higher than 1.5 MPa, soil cement brick = higher than 2.0 MPa, concrete blocks for sealing = higher than 2.5 MPa, ceramic blocks for structural masonry = higher than 3 MPa, and hollow concrete blocks of C category = higher than 4 MPa.

The use of more reactive precursors and a thinner APSS could improve the AAB reactivity and, as a result, the mechanical strength.

Figure 10 exhibits the results of air permeability (Figure 10a) and water absorption (Figure 10b) of the hardened mortars.

Figure 10
Air permeability (a) and capillary water absorption (b) of the AAB mortars.

The results indicated that A_2.7 was a more permeable mortar. The additional water used to dissolve the extra NaOH and to adjust the molar ratio H2O/Na2O contributes to the porosity increasing in hardened mortar, as reported by Cheng et al.6060 Cheng H, Lin KL, Cui R, Hwang CL, Chang YM, Cheng TW. The effects of SiO2/Na2O molar ratio on the characteristics of alkali-activated waste catalyst-metakaolin based geopolymers. Constr Build Mater. 2015;95:710-20. http://dx.doi.org/10.1016/j.conbuildmat.2015.07.028.
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.

Air permeability results obtained in a two-part AAB mortar made with APSS from RHA were 1 x 10-13 m230, while the results obtained in this research with one-part AAB made with APSS were 10 times higher. The high permeability can be related to entrapped air in the mortars, which is derived mainly by the difficulty of mixing and molding the mortars in the fresh state due to the low workability.

The capillary water absorption results indicated that within the first 480 min the differences between the capillarity of A_2.7 and other specimens increased with time. After 24 h, A_2.7 had capillary water absorption 30% higher than the other mortars. The specimens B_3.1 and C_3.3 presented similar behavior during all tests, which indicates that they have a similar internal capillary pores network1111 Abdollahnejad Z, Hlavacek P, Miraldo S, Pacheco-Torgal F, Aguiar JLB. Compressive strength, microstructure and hydration products of hybrid alkaline cements. Mater Res. 2014;17(4):829-37. http://dx.doi.org/10.1590/S1516-14392014005000091.
http://dx.doi.org/10.1590/S1516-14392014...
.

The results suggest that in sample A_2.7 there was a broader number and connection of pores, resulting in a higher capillary suction6161 Pavía S, Treacy E. A comparative study of the durability and behaviour of fat lime and feebly-hydraulic lime mortars. Mater Struct. 2007;39(3):391-8. http://dx.doi.org/10.1617/s11527-005-9033-4.
http://dx.doi.org/10.1617/s11527-005-903...
. The data are in accordance with the air permeability tests that indicated A_2.7 was a more permeable material. B_3.1 and C_3.3 provided lower internal water transport by capillary forces, indicating they are materials of higher durability than A_2.76262 Albitar M, Mohamed Ali MS, Visintin P, Drechsler M. Durability evaluation of geopolymer and conventional concretes. Constr Build Mater. 2017;136:374-85. http://dx.doi.org/10.1016/j.conbuildmat.2017.01.056.
http://dx.doi.org/10.1016/j.conbuildmat....
.

Figure 11 shows the morphology of the mortars obtained by SEM. The numbers 1, 2, 3, and 4 presented in the images indicated the EDS point of detection. Table 6 presents the results of the chemical composition obtained by EDS (average value obtained at least two reading points in diverse regions of specimens).

Figure 11
Microstructure of mortars obtained by SEM.
Table 6
Elemental composition of mortars (obtained by EDS).

Figure 11 revealed that the specimen microstructures were homogeneous, dense, and presented micro-cracks and voids usually with spherical shapes distributed by the matrix (porosity).

The observed samples were fractured from the specimens of compressive strength test. This can cause some microcracks observed in the microstructure. In the literature, other studies reported microcracks in one-part AAB which may also be due to some expansive reactions in the hardened material1010 Ma C, Zhao B, Guo S, Long G, Xie Y. Properties and characterization of green one-part geopolymer activated by composite activators. J Clean Prod. 2019;220:188-99. http://dx.doi.org/10.1016/j.jclepro.2019.02.159.
http://dx.doi.org/10.1016/j.jclepro.2019...
. Spherical voids reveal the presence of trapped air bubbles that contribute to total porosity3636 Rocha TS, Dias DP, França FCC, Guerra RRS, Marques LRCO. Metakaolin-based geopolymer mortars with different alkaline activators (Na+ and K+). Constr Build Mater. 2018;178:453-61. http://dx.doi.org/10.1016/j.conbuildmat.2018.05.172.
http://dx.doi.org/10.1016/j.conbuildmat....
.

Mortar matrix A_2.7 microstructure revealed the presence of elongated needle-shaped crystals. This is due to the additional NaOH and water in the mixture, necessary to keep a constant Na2O/Al2O3 and H2O/Na2O molar ratios, resulting in unreacted and free alkalis. The unreacted and free alkalis react with CO2 to form efflorescence6363 Najafi Kani E, Allahverdi A, Provis JL. Efflorescence control in geopolymer binders based on natural pozzolan. Cement Concr Compos. 2012;34(1):25-33. http://dx.doi.org/10.1016/j.cemconcomp.2011.07.007.
http://dx.doi.org/10.1016/j.cemconcomp.2...
. Temuujin et al.6464 Temuujin J, van Riessen A, Williams R. Influence of calcium compounds on the mechanical properties of fly ash geopolymer pastes. J Hazard Mater. 2009;167(1-3):82-8. http://dx.doi.org/10.1016/j.jhazmat.2008.12.121.
http://dx.doi.org/10.1016/j.jhazmat.2008...
stated that efflorescence is mainly composed of Na and O, with a chemical composition ranging in according to the precursor employed.

The high Na/Si and Na/Al ratios obtained from EDS point 1 (Figure 11 – A_2.7, images C and D) revealed the concentration of sodium in the needle-like crystals, while the concentrations were considerably lower in the A_2.7 matrix indicated by EDS point 2 (Figure 11 – A_2.7, image D). During the crystal formations, internal pressure can be generated ranging according to pore diameter and, in some cases, it causes cracking6565 Longhi MA, Zhang Z, Rodríguez ED, Kirchheim AP, Wang H. Efflorescence of alkali-activated cements (geopolymers) and the impacts on material structures: a critical analysis. Front Mater. 2019;6:89. http://dx.doi.org/10.3389/fmats.2019.00089.
http://dx.doi.org/10.3389/fmats.2019.000...
.

Mortar matrix B_3.1 presented a continuous and dense microstructure with pores and cracks. Figure 11 – B_3.1, images B and C showed small zeolite crystals formed on the matrix surface as secondary products in the reaction process (on the N-A-S-H gel) which is the precursor of zeolites formation6666 Alehyen S, Achouri MEL, Taibi M. Characterization, microstructure and properties of fly ash-based geopolymer. J Mater Environ Sci [serial on the Internet]. 2017 [cited 2021 Aug 28];8(5):1783-96. Available from: https://jmaterenvironsci.com/Document/vol8/vol8_N5/190-JMES-2930-Alehyen.pdf
https://jmaterenvironsci.com/Document/vo...
,6767 Hajimohammadi A, van Deventer JSJ. Characterisation of one-part geopolymer binders made from fly ash. Waste Biomass Valoriz. 2017;8(1):225-33. http://dx.doi.org/10.1007/s12649-016-9582-5.
http://dx.doi.org/10.1007/s12649-016-958...
. Sample B_3.1 had a Si/Al molar ratio lower than 0.3. Ma et al.6868 Ma C, Long G, Shi Y, Xie Y. Preparation of cleaner one-part geopolymer by investigating different types of commercial sodium metasilicate in China. J Clean Prod. 2018;201:636-47. http://dx.doi.org/10.1016/j.jclepro.2018.08.060.
http://dx.doi.org/10.1016/j.jclepro.2018...
results showed that in these cases the N-A-S-H gels may have been few geopolimerized which results in the formation of the zeolitic phase.

Mortar matrix C_3.3 presented a continuous and dense microstructure. Figure 11 – C_3.3, image C, present crystals similar to the zeolitic phase, but EDS measurements were not made on these surfaces, and it makes difficult to confirm this phase formation. Mortar C_3.3 presented the Na/Si and Si/Al molar ratios very close to the results available in the literature.

The elemental compositions obtained by EDS showed the molar ratios: Na/Al varying from 0.48 to 0.61; Na/Si varying from 0.25 to 0.32; and Si/Al varying from 1.51 to 2.03. The EDS results in point 1 were not considered because it was made on the alkaline crystal. Guo et al.6969 Guo S, Ma C, Long G, Xie Y. Cleaner one-part geopolymer prepared by introducing fly ash sinking spherical beads: properties and geopolymerization mechanism. J Clean Prod. 2019;219:686-97. http://dx.doi.org/10.1016/j.jclepro.2019.02.116.
http://dx.doi.org/10.1016/j.jclepro.2019...
reported Na/Si molar ratios between 0.28 and 0.51, and stated that the best ratio was close to 0.5 where occurred the greatest formation of N-A-S-H gel. Duxon et al.5858 Duxson P, Provis JL, Lukey GC, Mallicoat SW, Kriven WM, Van Deventer JSJ. Understanding the relationship between geopolymer composition, microstructure and mechanical properties. Colloids Surf A Physicochem Eng Asp. 2005;269(1-3):47-58. http://dx.doi.org/10.1016/j.colsurfa.2005.06.060.
http://dx.doi.org/10.1016/j.colsurfa.200...
studied the Si/Al molar ratio between 1.15 and 2.15, and reported that the higher mechanical properties were achieved with Si/Al molar ratio of 1.90. The mechanical properties of B_3.1 and C_3.3 mortars had better results.

The results of one-part AAB obtained in this work confirm that the process to obtain this one-part binder is a viable economic alternative in diverse applications, such as fire-proof building materials, protective coatings, renderings, and building components.

4. Conclusions

A method to produce one-part alkali-activated binder (AAB) was carried out by the following steps: 1- production of alternative powder sodium silicate solution; 2- oven-drying the solution; 3- grinding to obtain a sodium silicate as a thin powder (APSS); 4- addition of metakaolin to the APSS; and 5- the binder is ready (one-part AAB).

The SiO2/Al2O3 molar ratio used in mortar production affected the final properties. The increase in SiO2 content generated mortar with higher strength and lower porosity.

The highest compressive strength (~18 MPa) was achieved at 180 days by mortar produced with a theoretical SiO2/Al2O3 molar ratio of 3.3. Despite the relatively low mechanical results, the mortars achieved enough compressive strength for different applications in civil construction (renderings and components).

Data indicated the effectiveness of the proposed method of production one-part AAB. The use of a solid silicate soluble source from rice husk ash (agricultural waste) dissolution makes the AAB production cleaner when compared with other commercial activators, resulting in environmental benefits.

5. Acknowledgments

This work was supported by the Coordination for the Improvement of Higher Education Personnel - Brazil (CAPES, Finance code: 001), PROCAD/CAPES, and National Council for Scientific and Technological Development - Brazil (CNPq).

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Publication Dates

  • Publication in this collection
    06 Dec 2021
  • Date of issue
    2022

History

  • Received
    28 Aug 2021
  • Reviewed
    19 Oct 2021
  • Accepted
    04 Nov 2021
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