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Comparison of alkali and silica sources in one-part alkali-activated blast furnace slag mortar Tero Luukkonen * , Zahra Abdollahnejad, Juho Yliniemi, Paivo Kinnunen, Mirja Illikainen University of Oulu, Fibre and Particle Engineering Research Unit, P.O. Box 8000, FI 90014, University of Oulu, Finland article info Article history: Received 28 December 2017 Received in revised form 28 February 2018 Accepted 20 March 2018 Available online 21 March 2018 Keywords: Alkali activation Blast furnace slag Geopolymer Microsilica Rice husk ash abstract Alkali-activated materials (AAMs) are one of the alternative low-CO 2 binders. One-part AAMs, (that is, mixing a solid precursor with a solid alkali activator and adding water) have recently attracted increasing interest. The purpose of this study is to examine if fast-dissolving solid synthetic sodium metasilicate could be replaced by a combination of sodium hydroxide and slow-dissolving silica derived from rice husk ash or microsilica in the preparation of one-part alkali-activated blast furnace slag mortar. The replacement would improve the carbon footprint and the cost efciency of the binder. The results demonstrate that silica availability signicantly affects compressive strength development as a function of time or mixture composition. The highest compressive strength (107 MPa, 28 d) was obtained with fast-dissolving silica. Furthermore, setting times could be adjusted based on the mix composition, and the durability of mortar remained good after 120 freezeethaw cycles. The results highlight the overall effect of silica availability on the fresh and hardened properties of one-part AAMs. © 2018 The Authors. Published by Elsevier Ltd. This is an open access article under the CC BY-NC-ND license (http://creativecommons.org/licenses/by-nc-nd/4.0/). 1. Introduction Alkali-activated materials (AAMs) (and geopolymers as their sub-group (Provis, 2014)) are recognized as one of the alternative low-CO 2 binders (Scrivener et al., 2016) and as a way to beneciate several kinds of industrial wastes into higher-value products (Mehta and Siddique, 2016). Ground granulated blast-furnace slag (GGBFS), an amorphous by-product of pig iron production, is one of the most widely studied precursors in alkali activation. It mainly consists of a CaOeMgOeAl 2 O 3 eSiO 2 system (Li et al., 2010) and forms calcium-aluminum-silicate-hydrate (C-A-S-H in cement chemist notation) gel as the result of alkali activation (Bernal et al., 2014a). The rst patent regarding the alkali activation of GGBFS was published as early as 1895 (Whiting, 1895) and these binders have been studied extensively since then and also used in construction (Palomo et al., 2014). The historical development of AAMs is dis- cussed, for example, in a recent review by Krivenko (2017). However, one major practical shortcoming of alkali-activation technology is the use of alkali-activator solutions (frequently concentrated sodium silicate and/or hydroxide), which are corro- sive, viscous, and cause occupational hazards. Consequently, there has recently been a pronounced interest in one-part (or just add water) AAMs, as documented in a review by Luukkonen et al. (2018). In one-part alkali-activation, precursors are mixed with solid alkali activator and water is added to initiate the reaction. Pioneering work with one-part alkali-activated GGBFS was carried out in Australia in the late 1990s and early 2000s as summarized by Collins and Sanjayan (2002) and the references therein. Later studies with one-part alkali-activated GGBFS have further devel- oped the mechanical properties and focused on, for instance, using bers (Luukkonen et al., 2018). Synthetic alkali silicates have been deemed to be the most suitable solid (or liquid) activators for GGBFS in the aforementioned studies. However, of the raw mate- rials, alkali silicates are the most expensive and have the highest environmental impact (Heath et al., 2014). Consequently, efforts are underway to nd alternative alkali activators and/or reactive silica sources. Regarding conventional AAMs, sodium hydroxide solution and rice husk ash (RHA) (Kamseu et al., 2017; Passuello et al., 2017), mold cleaning solution waste from the aluminum industry (Fern andez-Jim enez et al., 2017), and waste glass dissolved in NaOH/Na 2 CO 3 solution (Puertas and Torres-Carrasco, 2014; Torres- Carrasco and Puertas, 2015a; Torres-Carrasco et al., 2015b, 2015c) have been studied. Regarding one-part AAMs, the use of red mud (Choo et al., 2016), maize cob ash (Peys et al., 2016, 2017), RHA (Hajimohammadi et al., 2016a; Sturm et al., 2016a), silica fume (Kovtun et al., 2015), silica residue from chlorosilane production * Corresponding author. E-mail address: [email protected] (T. Luukkonen). Contents lists available at ScienceDirect Journal of Cleaner Production journal homepage: www.elsevier.com/locate/jclepro https://doi.org/10.1016/j.jclepro.2018.03.202 0959-6526/© 2018 The Authors. Published by Elsevier Ltd. This is an open access article under the CC BY-NC-ND license (http://creativecommons.org/licenses/by-nc-nd/4.0/). Journal of Cleaner Production 187 (2018) 171e179

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Page 1: Journal of Cleaner Production - University of Oulujultika.oulu.fi/files/nbnfi-fe201804176564.pdf · 2018-04-17 · (Sturm et al., 2016b), and geothermal silica (Hajimohammadi et al.,

lable at ScienceDirect

Journal of Cleaner Production 187 (2018) 171e179

Contents lists avai

Journal of Cleaner Production

journal homepage: www.elsevier .com/locate/ jc lepro

Comparison of alkali and silica sources in one-part alkali-activatedblast furnace slag mortar

Tero Luukkonen*, Zahra Abdollahnejad, Juho Yliniemi, Paivo Kinnunen, Mirja IllikainenUniversity of Oulu, Fibre and Particle Engineering Research Unit, P.O. Box 8000, FI 90014, University of Oulu, Finland

a r t i c l e i n f o

Article history:Received 28 December 2017Received in revised form28 February 2018Accepted 20 March 2018Available online 21 March 2018

Keywords:Alkali activationBlast furnace slagGeopolymerMicrosilicaRice husk ash

* Corresponding author.E-mail address: [email protected] (T. Luukkone

https://doi.org/10.1016/j.jclepro.2018.03.2020959-6526/© 2018 The Authors. Published by Elsevier

a b s t r a c t

Alkali-activated materials (AAMs) are one of the alternative low-CO2 binders. One-part AAMs, (that is,mixing a solid precursor with a solid alkali activator and adding water) have recently attracted increasinginterest. The purpose of this study is to examine if fast-dissolving solid synthetic sodium metasilicatecould be replaced by a combination of sodium hydroxide and slow-dissolving silica derived from ricehusk ash or microsilica in the preparation of one-part alkali-activated blast furnace slag mortar. Thereplacement would improve the carbon footprint and the cost efficiency of the binder. The resultsdemonstrate that silica availability significantly affects compressive strength development as a functionof time or mixture composition. The highest compressive strength (107MPa, 28 d) was obtained withfast-dissolving silica. Furthermore, setting times could be adjusted based on the mix composition, andthe durability of mortar remained good after 120 freezeethaw cycles. The results highlight the overalleffect of silica availability on the fresh and hardened properties of one-part AAMs.© 2018 The Authors. Published by Elsevier Ltd. This is an open access article under the CC BY-NC-ND

license (http://creativecommons.org/licenses/by-nc-nd/4.0/).

1. Introduction

Alkali-activated materials (AAMs) (and geopolymers as theirsub-group (Provis, 2014)) are recognized as one of the alternativelow-CO2 binders (Scrivener et al., 2016) and as a way to beneficiateseveral kinds of industrial wastes into higher-value products(Mehta and Siddique, 2016). Ground granulated blast-furnace slag(GGBFS), an amorphous by-product of pig iron production, is one ofthe most widely studied precursors in alkali activation. It mainlyconsists of a CaOeMgOeAl2O3eSiO2 system (Li et al., 2010) andforms calcium-aluminum-silicate-hydrate (C-A-S-H in cementchemist notation) gel as the result of alkali activation (Bernal et al.,2014a). The first patent regarding the alkali activation of GGBFSwaspublished as early as 1895 (Whiting, 1895) and these binders havebeen studied extensively since then and also used in construction(Palomo et al., 2014). The historical development of AAMs is dis-cussed, for example, in a recent review by Krivenko (2017).

However, one major practical shortcoming of alkali-activationtechnology is the use of alkali-activator solutions (frequentlyconcentrated sodium silicate and/or hydroxide), which are corro-sive, viscous, and cause occupational hazards. Consequently, there

n).

Ltd. This is an open access article u

has recently been a pronounced interest in one-part (or “just addwater”) AAMs, as documented in a review by Luukkonen et al.(2018). In one-part alkali-activation, precursors are mixed withsolid alkali activator and water is added to initiate the reaction.Pioneering work with one-part alkali-activated GGBFS was carriedout in Australia in the late 1990s and early 2000s as summarized byCollins and Sanjayan (2002) and the references therein. Laterstudies with one-part alkali-activated GGBFS have further devel-oped the mechanical properties and focused on, for instance, usingfibers (Luukkonen et al., 2018). Synthetic alkali silicates have beendeemed to be the most suitable solid (or liquid) activators forGGBFS in the aforementioned studies. However, of the raw mate-rials, alkali silicates are the most expensive and have the highestenvironmental impact (Heath et al., 2014). Consequently, efforts areunderway to find alternative alkali activators and/or reactive silicasources. Regarding conventional AAMs, sodium hydroxide solutionand rice husk ash (RHA) (Kamseu et al., 2017; Passuello et al., 2017),mold cleaning solution waste from the aluminum industry(Fern�andez-Jim�enez et al., 2017), and waste glass dissolved inNaOH/Na2CO3 solution (Puertas and Torres-Carrasco, 2014; Torres-Carrasco and Puertas, 2015a; Torres-Carrasco et al., 2015b, 2015c)have been studied. Regarding one-part AAMs, the use of red mud(Choo et al., 2016), maize cob ash (Peys et al., 2016, 2017), RHA(Hajimohammadi et al., 2016a; Sturm et al., 2016a), silica fume(Kovtun et al., 2015), silica residue from chlorosilane production

nder the CC BY-NC-ND license (http://creativecommons.org/licenses/by-nc-nd/4.0/).

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T. Luukkonen et al. / Journal of Cleaner Production 187 (2018) 171e179172

(Sturm et al., 2016b), and geothermal silica (Hajimohammadi et al.,2008) as activators or additional reactive silica sources has beenattempted. However, the effect of the silica dissolution rate on thefresh and hardened properties of the resulting binder has not beensystematically studied.

In the present paper, three different solid silica and alkalisources are compared: 1) synthetic anhydrous sodiummetasilicate,2) microsilica (MS) and sodium hydroxide, and 3) RHA and sodiumhydroxide. MS and RHA are commercially available industrial sideproducts already used by the concrete industry. RHA is a high-reactive-silica-content residue from the combustion of rice husk(estimated total global output 80Mt/a) (Chandrasekhar et al., 2003;Della et al., 2002; Armesto et al., 2002). MS, on the other hand, is aby-product from silicon and ferrosilicon alloy production with anequally high reactive silica amount (Khan and Siddique, 2011).Sodium hydroxide is required with these silica sources to providesufficient alkalinity and sodium ions. The aluminosilicate precursorwas GGBFS in all cases. The aim is to study the effect of the silicadissolution rate on the fresh and hardened properties of mortars. Asan outcome, the unit cost and environmental footprint of one-partalkali-activated GGBFS would be reduced if the use of MS or RHAwith sodium hydroxide was possible instead of sodium silicate.

2. Materials and methods

2.1. Materials

GGBFS (obtained from Finnsementti, Finland) had the d50 valueand density of 10.8 mmand 2.93 g/cm3, respectively. MS (tradenameParmix-silika) was obtained from Fescon Ltd. (Finland) as looselygranulated particles. It had the following specifications as reportedby the manufacturer: SiO2 > 85%, Cl < 0.10%, Na2O equivalent <3.0%, specific surface area 15e35m2/g, and activity index > 100%.MS and RHA (also from Fescon Ltd.) were milled for 10min with aRetschmortar grinder RM 200 before use. Their d50 values were 199and 172 mm before milling and 23 and 30 mm after milling,respectively, as determined with a Beckman Coulter LS 13320 laserdiffraction particle size analyzer. The chemical compositions of rawmaterials were determined with X-ray fluorescence (XRF) spec-troscopy (see section 2.3 for details) and are shown in Table 1. Ac-cording to the X-ray diffraction (XRD) analysis (see section 2.3 fordetails), GGBFS and MS were completely amorphous, whereas RHAcontained cristobalite (SiO2) and sodium phosphorus silicon oxide(Na2Si2PO8) in addition to amorphous material. Synthetic activatorchemicals were reagent grade sodium hydroxide powder (� 97%purity; Honeywell) and technical grade anhydrous sodium meta-silicate (molar ratio of SiO2/Na2O¼ 0.9; Alfa Aesar). Anhydrous

Table 1The chemical composition of GGBFS, microsilica, and rice husk ash.

Oxide [%, w/w] GGBFS Microsilica Rice husk ash

Na2O 0.51 0.18 0.22MgO 10.24 0.35 0.47Al2O3 9.58 0.23 0.17SiO2 32.33 94.25 88.46P2O5 0.01 0.01 0.69SO3 4.00 0.13 0.05K2O 0.53 0.56 1.69CaO 38.51 0.78 0.75Fe2O3 1.23 0.84 0.31TiO2 2.21 e e

LOI (525 �C) n.d. 1.69 8.88LOI (950 �C) n.d. 2.31 9.22

GGBFS¼ ground granulated blast furnace slag, LOI¼ loss on ignition, n.d.¼ notdetermined.

sodiummetasilicatewas obtained as 1mmgranules andwasmilledbefore use for 10min similarly as other materials. The aggregateused throughout the experiments was CEN standard sand (EN196e1:2016, 2016) with particle size distribution between 0.08and 2mm.

2.2. Preparation of alkali-activated mortars

Three series of mortars were prepared (Table 2). The first serieswas constructed by increasing the amount of sodium silicate (SS),and in the subsequent two series, synthetic sodium silicate wasreplaced by sodium hydroxide and alternative silica source, that is,RHA or MS. The compositions were selected based on earlierliterature (Yang et al., 2008) and preliminary experiments (notshown). The water/binder and aggregate/binder weight ratios wereconstant at 0.35 and 2.00, respectively. The series were formulatedto have similar (or as close as possible) SiO2/Al2O3, Na2O/SiO2,Na2O/Al2O3, CaO/SiO2, H2O/Na2O, and H2O/Al2O3 molar ratios. Thisallowed a comparison of the effect of reactive silica and alkalinitysources while keeping the calculated chemical composition con-stant across the series.

The preparation of specimens took place as follows: raw mate-rials and solid activators were mixed for 3min, tap water wasadded, and mixing was continued for a further 3min. The preparedmortars were cast in prismatic molds with dimensions of40� 40� 160mm. Specimens in the molds were compacted usinga jolting table (2� 60 shocks, 1 shock/s) and were then wrapped inplastic for approximately 24 h, demolded, and allowed to cure at23 �C and 60% relative humidity until testing. Each specimen wasprepared in triplicate. For X-ray diffraction analysis, specimenswere prepared without aggregate.

2.3. Chemical characterization

The chemical compositions were determined with a 4 kVwavelength dispersive XRF spectrometer (PANalytical AxiosmAX).XRF analyses were performed from fused samples: 1.5 g of samplewas melted at 1150 �C with 7.5 g of X-ray Flux Type 66:34 (66%Li2B4O7 and 34% LiBO2) to obtain melt-fused tablets. Moisture-%and loss-on-ignition (at 525 �C and 950 �C, respectively) weredetermined using a thermo-gravimeter (PrepAsh, Precisa).

Identification and quantification of crystalline phases was per-formed with XRD using a Rigaku Smartlab diffractometer (9 kW CuX-ray source) in the range of 5e120 �2q using 6 �2q/min scan speed.XRD analyses were performed from samples prepared without theaddition of aggregates (to exclude quartz signal) at the age of 28 d.Before analysis, samples were pulverized using a Retsch RS200mill.Quantification of crystalline phases was performed using theRietveld refinement method.

A field emission scanning electronmicroscope equippedwith anenergy dispersive spectrometer (SEM-EDS, Zeiss Ultra Plus) wasused to take micrographs of raw materials and hardened specimenintersections and to provide semi-quantitative information aboutthe chemical composition. Analyses were conducted using a back-scatter electron detector with 15 kV acceleration voltage andapproximately 8.5mm working distance. The samples were pre-pared by casting specimens in epoxy resin (Buehler). They werethen polished with Struers MD Piano 500, 1200, and 2000 grindingdiscs to reveal cross-sections. The samples were coatedwith carbonprior to measurement.

The evolution of heat during curing to assess ongoing chemicalprocesses was determined with a semi-adiabatic calorimeter (F-Cal8000, Calmetrix). Approximately 280 g of mortars SS1, RHA1, andMS1 (see Table 1) were prepared and placed inside plastic bags inthe calorimeter.

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Table 2Composition of prepared one-part alkali-activated mortars as weight fractions of the binder and as calculatedmolar ratios assuming complete solubility. Thewater/binder andaggregate/binder weight ratios were 0.35 and 2.00, respectively, in all cases.

Exp Name Weight fraction of binder Calculated molar ratios a

GGBFS SS NaOH RHA MS SiO2/Al2O3 Na2O/SiO2

Na2O/Al2O3

CaO/SiO2

H2O/ Na2O H2O/ Al2O3

SS1 0.90 0.10 e e e 6.64 0.16 1.05 1.10 21.86 22.98SS2 0.91 0.09 e e e 6.54 0.14 0.95 1.12 24.04 22.73SS3 0.92 0.08 e e e 6.44 0.13 0.84 1.13 26.71 22.48SS4 0.93 0.07 e e e 6.34 0.12 0.74 1.15 30.04 22.24SS5 0.94 0.06 e e e 6.25 0.10 0.64 1.17 34.32 22.00SS6 0.95 0.05 e e e 6.16 0.09 0.54 1.19 40.02 21.77SS7 0.96 0.04 e e e 6.07 0.07 0.45 1.20 48.00 21.54RHA1 0.88 e 0.06 0.05 e 6.64 0.16 1.05 1.10 21.87 22.96RHA2 0.90 e 0.06 0.05 e 6.54 0.14 0.95 1.12 24.06 22.76RHA3 0.91 e 0.05 0.04 e 6.44 0.13 0.84 1.13 26.73 22.51RHA4 0.92 e 0.04 0.04 e 6.34 0.12 0.74 1.15 30.06 22.22RHA5 0.93 e 0.04 0.03 e 6.25 0.10 0.64 1.17 34.34 21.99RHA6 0.94 e 0.03 0.03 e 6.16 0.09 0.54 1.19 40.04 21.76RHA7 0.95 e 0.03 0.02 e 6.07 0.07 0.45 1.20 48.02 21.54MS1 0.89 e 0.06 e 0.05 6.64 0.16 0.94 1.10 24.31 22.95MS2 0.90 e 0.05 e 0.04 6.54 0.14 0.83 1.12 27.28 22.70MS3 0.91 e 0.05 e 0.04 6.44 0.13 0.77 1.13 29.26 22.51MS4 0.92 e 0.04 e 0.03 6.34 0.12 0.71 1.15 31.28 22.22MS5 0.93 e 0.04 e 0.03 6.25 0.10 0.60 1.17 36.62 21.99MS6 0.94 e 0.03 e 0.02 6.16 0.09 0.54 1.19 40.06 21.76MS7 0.96 e 0.02 e 0.02 6.07 0.07 0.43 1.20 50.21 21.53

GGBFS¼ ground granulated blast furnace slag, SS¼ sodium silicate, RHA¼ rice husk ash, MS¼microsilica.a ¼ complete dissolution of raw materials was assumed.

T. Luukkonen et al. / Journal of Cleaner Production 187 (2018) 171e179 173

The solubility experiments were performed by placing 2 g ofsilica source (sodium metasilicate, RHA, or MS) in 1.0 L of 0.1, 1, or10M NaOH solution and mixing up to 4 h with a magnetic stirrertaking triplicate samples periodically. The samples were centri-fuged, and silicon concentration was determined with an opticalemission spectrometer (Thermo Electron IRIS Intrepid II XDL Duo).Each silica source was tested as received and after milling (10minwith a Retsch RM 200).

2.4. Fresh and hardened properties of mortars

Initial and final setting times of mortars were determined with aVicat apparatus (Vicatronic Matest) according to the standard EN196e3:2016 (2016). Compressive and flexural strengths weredetermined using a Zwick/Roell Z100 testing machine (with a loadcell of 100 kN) or a Toni Technik 3000 kN testing machine (whenover 100 kN force was required). Initially, the prismatic beamswereassessed under the flexural loading, and the broken half-specimenswere used to evaluate the compressive strength. Loading rates were50 N/s and 2.4 kN/s during the flexural and compressive strengthtests, respectively, according to the standard EN 196e1:2016(2016).

2.5. Durability properties of mortars

Freezeethaw resistance was tested according to the standardASTM C666/C666M-15 (2015). Three prismatic beams(40� 40� 160mm) were prepared according to the compositionsSS1, MS1, and RHA 1 (see Table 1). Specimens were measured forlength, weight, and time for an ultrasonic pulse to pass through thebeam (with Matest ultrasonic concrete tester C369N) and placed ina climate chamber half exposed to water and half exposed to air.The freezeethaw cycles were from þ20 to �15 �C with one cyclelasting 6 h. Samples were taken from the chamber after 60 and 120cycles, allowed to dry (at 23 �C and 60% relative humidity) for 1 d,and measured again for length, weight, and ultrasonic pulse spantime. The relative dynamic modulus of elasticity (Pc) was calculated

as the ratio of fundamental transverse frequency after c cycles (nl)and at 0 cycles (n):

Pc ¼ n2ln2

!� 100: (1)

3. Results and discussion

3.1. Silicon solubility from silica sources

Themost striking feature regarding the Si solubility (Fig.1) is theinsignificant difference between MS and RHA as received(d50¼172e199 mm) and after milling (d50¼ 23e30 mm). The silicasolubility is an important feature affecting, for instance, the rate ofconversion of the solid aluminosilicate source into the (C,N)-A-S-Hgel (Lee and Van Deventer, 2002; Rees et al., 2007). The apparentlack of improvement in solubility from milling might be explainedby the microstructure of silica sources (Fig. 2). RHA particles arehighly porous, which indicates good solubility. MS, however, is notexplicitly porous but according to the manufacturer's informationis “loosely granulated” and therefore likely to be easily soluble.Another explanation for the lack of improvement after millingcould be reaggregation of particles as suggested byHajimohammadi and van Deventer (2016b) who studied thedissolution of RHA (d50¼ 8 mm) and other (alumino)silicate sourcesin 0.05e0.3M NaOH solutions (liquid/solid¼ 200:1). The secondimportant feature that can be seen from Fig. 1 is that solubility ismarkedly increased when the NaOH concentration increases from1M to 10M, whereas the difference between 0.1 and 1M NaOH issmall. Finally, MS is clearly faster dissolving compared to RHA; up toapproximately 35% and 10% of Si was dissolved from MS and RHAafter 240min, respectively. The synthetic sodium silicate employedin this study dissolves almost completelywithin the first minutes indeionized water. Hajimohammadi et al. (2011) observed that aslow-releasing silica source (solid geothermal silica) led to the

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Fig. 1. Solubility of silicon from as received (d50¼172e199 mm) and milled (d50¼ 23e30 mm) rice husk ash and microsilica. Milling does not affect solubility, and 10M NaOH is themost efficient in dissolving Si.

Fig. 2. Scanning electron microscope micrographs of rice husk ash and microsilica particle intersections (300� magnification).

T. Luukkonen et al. / Journal of Cleaner Production 187 (2018) 171e179174

formation of a high silica content crystalline phase, analcime(NaAlSi2O6$H2O); nucleation took place near the unreacted silicaparticles; and the structure was more heterogeneous compared tothe quick-releasing silica source (sodium silicate solution). In thepresent study, however, no difference in crystalline phases or het-erogeneity was observed betweenmixes. Finally, it should be notedthat the water to binder weight ratio is much lower in the mortarformulations (0.35) compared to the water to solid weight ratio inthe solubility experiments (500); therefore, much lower solubility(than indicated in Fig. 1) in binder preparation could be expected.However, the solubility experiments were used to assess the

relative solubility of silica sources. The calculated sodium hydrox-ide molarity in the mortar mixtures (Table 1) is in the range of1.8e4.6M.

3.2. Fresh and hardened properties of mortars prepared withdifferent silica sources

3.2.1. Setting timeInitial and final setting times (Fig. 3) were found to be readily

adjustable according to the mix design (e.g., Na2O/SiO2 ratio or theactivator amount). The trend with setting times is

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Fig. 3. Initial and final setting times of one-part alkali-activated blast furnace slag mortars using different sodium and silica sources. The fastest setting occurs with the sodiumsilicate series, while microsilica with NaOH has the slowest setting.

T. Luukkonen et al. / Journal of Cleaner Production 187 (2018) 171e179 175

MS þ NaOH > RHA þ NaOH > sodium silicate, and the differencesbetween series are more marked with initial than final settingtimes. In practice, the mortars were no longer castable after theinitial setting was exceeded. One-part AAMs have frequently beenreported to set too rapidly due to the heat generation from thedissolution of solid activators, such as sodium hydroxide (Suwanand Fan, 2017). Our results demonstrate that this issue could beat least partially resolved by adjusting the amount of activator (i.e.alkali to silica ratio), as shown in Fig. 3. while keeping in mind thatsuch adjustment also affects the extent of reaction and subsequentcompressive strength (see section 3.3). The required initial settingtime for normal concrete has been specified as more than45e75min depending on the strength class (EN 197e1:2000,2000). This requirement can be largely met with the reportedmixtures, as the initial setting times were 19e72min. As a finalnote, the results agree with previous reported initial and finalsetting times for one-part AAMs, which have varied between23e150 and 69e230min, respectively (Abdel-Gawwad and Abo-El-Enein, 2016; Hajimohammadi et al., 2017; Matalkah et al., 2017;Wang et al., 2017).

3.2.2. Mechanical propertiesThe compressive strength (Fig. 4A) of the sodium silicate series

increases linearly when the calculated Na2O/SiO2 was over 0.09 andthe highest obtained valuewas 107MPa (at 28 d). This is, in fact, thefirst time one-part AAMs have been documented to exceed100MPa compressive strength, with earlier reported strengthsbeing up to 80MPa at 28 d (an analysis of the existing literaturewasperformed in earlier work (Luukkonen et al., 2018)). In terms ofstrength evolution as a function of time (Fig. 4B), the majority ofstrength development already occurred within 1 d. When curingwas continued up to 90 d, there was a slight decrease in thecompressive strength of mortar activated with sodium silicatewhile mortars activated with slower releasing silicate sourcescontinued to gain strength. This is in agreement with earlier resultsby Collins and Sanjayan (1999, 2001) who also observed retro-gression of one-part alkali-activated GGBFS compressive strengthwhen cured at 50% RH and 23 �C (whereas sealed or bath-curedspecimen continued to gain strength). The decrease of strengthwas explained as a result of microcracking. Nevertheless, even after

the slight decrease, the compressive strength of sodium silicaactivated mortar remains high (98MPa). MS or RHA with NaOHresulted in considerably lower and almost constant compressivestrength regardless of the mixture composition in the studiedrange. The compressive strength of the MS series was slightlyhigher thanwith RHAwith the same composition, which was likelydue to the lower silica availability of RHA (see Fig. 1) and approx-imately 6 weight-%-units higher silica content (see Table 1).Although the compressive strengths of slower-releasing silicasources were considerably lower in comparison with sodium sili-cate, they are still sufficient for certain structural uses as specified,for instance, in the standard ACI 318-11 (2011). Interestingly, thehigher strength indicated faster setting time (Fig. 3) in the sodiumsilicate series (SS1eSS7), whereas in the MS (MS1eMS7) and RHA(RHA1eRHA7) series there was no such correlation. The resultsindicate that the faster silica availability is indeed one of the keyfeatures for high strength development. The flexural strength ofmixes exhibited a similar trend as compressive strength, but thedifferences between series were not as marked (see supplementarymaterials).

3.2.3. Semi-adiabatic calorimetryTwo peaks were observed in the semi-adiabatic calorimetry

measurements (Fig. 5); the first appeared approximately 60minafter the addition of water for all studied mixtures, and the secondafter approximately 200e230min in the case of the MS1 and RHA1mixtures and after approximately 330min for SS1. However, thefirst peak is a barely visible shoulder of the second peak in the caseof theMS1 and RHA1mixtures. Heat evolution fromMS1 and RHA1is faster than from SS1. However, the temperature increase is quitesimilar in all mixes (10e11 �C), which is surprising because the heatof solution for anhydrous sodium metasilicate and sodium hy-droxide is different at �31.17 and �44.51 kJ/mol, respectively(Hazardous Substances Data Bank, 2003; Lide, 2003). The heat ofsolution for sodium metasilicate has been reported to varydepending on the concentration of other species in the solution(lower heat release when dissolving into a concentrated solution ofNaOH, for instance) (Provis and Van Deventer, 2009) and mostlikely also on the silica modulus. Compared to the published liter-ature (Alonso and Palomo, 2001; Bernal et al., 2011; Kumar et al.,

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Fig. 4. Compressive strength development as A) a function of the molar ratio of the mixture Na2O/SiO2 (see Table 1 for mixture compositions) and B) a function of time for SS1, MS1,and RHA1 mixtures. The error bars represent ±1 standard error (based on six measurements).

Fig. 5. Temperature increase as a function of time from one-part alkali-activated blastfurnace slag mortars using different silica and sodium sources.

T. Luukkonen et al. / Journal of Cleaner Production 187 (2018) 171e179176

2010), the results depicted in Fig. 5 indicate faster reaction thanwith conventional two-part AAMs. In addition, the temperatureincrease is higher than that reported elsewhere, for instance byPuligilla and Mondal (2013). The first peak in Fig. 5 is a result ofdissolution of raw materials and the second corresponds to thepolymerization and condensation (both exothermic reactions) ofC-A-S-H gel (Alonso and Palomo, 2001; Kumar et al., 2010; Puligillaand Mondal, 2013; Sun and Vollpracht, 2018). Frequently, the firstpeak is followed by a dormant (or induction) period during whichthe concentration of soluble alumina and silica species increases upto a certain threshold value (Sun and Vollpracht, 2018). However, inthe present study, the dormant period was visible only in the caseof sodium silicate-activated GGBFS. In fact, the lack of a dormantperiod indicates a rapid precipitate formation on the surface ofprecursor grains, which hinders subsequent reactions and a highstrength development (Sun and Vollpracht, 2018). These earlierfindings support the observed results in this study: MS1 and RHA1(no dormant period) had clearly lower strength compared to SS1(observable dormant period). When comparing calorimetry resultsto the setting times, the initial setting time of MS1 and RHA1 isreached approximately at the same time as the first peak occurred

in Fig. 5. However, the SS1 mixture has the initial setting time of19min, which could be too short to be observable with the semi-adiabatic calorimeter used.

3.3. Microstructure

The microstructure of binders was examined to gain furtherinsight regarding the differences resulting from the use of alkaliactivators and silica sources. The micrographs of specimen (onlySS1, MS1, and RHA1were studied) intersections are shown in Fig. 6.There are three distinguishable phases seen in the micrographs:aggregate particles (smooth grey areas), unreacted GGBFS particles(light grey areas), and C-A-S-H gel between the particles (texturedgrey area). There are more microcracks present in the SS1 binder,which might be an indication water escaping during curing; alonger curing at higher relative humidity might decrease the ten-dency for microcracks to appear (Collins and Sanjayan, 2001). Thepresence of a large amount of GGBFS particles is an indication ofincomplete dissolution. Consequently, the undissolved GGBFSparticles act as microfillers in the studied system.

The semi-quantitative X-ray microanalyses (Table 3) indicatethat the dissolution of GGBFS, MS, and RHAwere incomplete, whichwas also supported by the dissolution experiments (Fig. 1) and themortar micrographs (Fig. 6). Regarding the SiO2/Al2O3 molar ratio,the SS1 mortar has the highest value, indicating higher incorpo-ration of silica from the readily dissolving sodium silicate. However,the values are only 27e38% of the calculated value (assumingcomplete dissolution). As the source of aluminum was the same inall cases (i.e., GGBFS), the difference might be explained by thesilica source. The Na2O/SiO2, however, was 3e4 times higher thanthe calculated value, indicating a lower silica incorporation thancould be assumed from calculated value: again, this could be aresult of incomplete reaction of GGBFS. Interestingly though, SS1(high silica availability from Na2SiO3) had a similar Na2O/SiO2 ratioas MS1 and RHA1 (low silica availability from MS and RHA). Thiscould be a reason of approximately 0.5 units higher pH with MS1and RHA1 in comparison to SS1 (pHz 11.5), which increases SiO2solubility from GGBFS. In terms of Na2O/Al2O3, the MS and RHAspecimens have approximately the calculated composition. How-ever, the sodium silicate specimen (SS1) clearly has a higher Na2O/

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Fig. 6. Micrographs of hardened mortar intersections (1000� magnification).

Table 3Comparison of experimental and calculatedmolar ratios of selected binder mixtures(see Table 1 for complete mixture compositions).

Experimental Calculated a

SS1 (N¼ 50) MS1 (N¼ 40) RHA1 (N¼ 56)

SiO2/Al2O3 2.54 1.81 1.90 6.64Na2O/SiO2 0.62 0.60 0.52 0.16Na2O/Al2O3 1.57 1.09 0.98 1.05CaO/SiO2 0.99 1.02 1.15 1.10

N¼ number of point analyses.a calculated value assumes 100% solubility of raw materials.

Fig. 7. Diffractograms of specimens with numbers 1, 4, and 7 (see Table 1).CeSeH¼ calcium silicate hydrate, HT¼ hydrotalcite (Mg6Al2CO3(OH)16$4(H2O)),

T. Luukkonen et al. / Journal of Cleaner Production 187 (2018) 171e179 177

Al2O3 ratio, which indicates lower availability of alumina. Again, theslightly higher pH of MS1 and RHA1 could have enhanced Al2O3solubility from GGBFS. Finally, the CaO/SiO2 ratio is quite close tothe calculated value.

The presence of crystalline phases was determined by means ofXRD for selected hardened pastes (i.e., prepared without aggre-gate). As can be seen from Fig. 7, the formation of hydrotalcite(Mg6Al2CO3(OH)16$4(H2O)) took place in all pastes, which has beensuggested to occur particularly when GGBFS has MgO content over5 weight-%. The presence of hydrotalcite causes a greater reactionextent, lower aluminum incorporation in the formed gel, and betterresistance against carbonation (Bernal et al., 2014b). The broadpeak at approximately 25e35 �2q was assigned as calcium car-bonate (CaCO3), but also poorly crystalline CeSeH gel phases resultsignal in this region (Taylor, 1990). In RHA-containing pastes, therewas also a separate crystalline CeSeH-type phase at approximately7 �2q. The CaO/SiO2 ratio reported in Table 3 indicates that it couldbe the CeSeH (I) phase (CaO/SiO2 in the range 0.8e1.5) (Taylor,1990). Cristobalite (SiO2) originates from RHA. The intensity ofpeaks is clearly lower in the sodium silicate series, and thereforethe material is more amorphous than in the MS or RHA series. Thiscould be explained by the faster setting of the sodium silicate series.

3.4. Durability against freezeethaw cycles

The durability of selected hardened mortars was evaluated byexposing them to rapid freezeethaw cycles (Table 4). Ultrasonicpulse velocity (UPV) is an indirect indication of strength, theoccurrence of cracks or voids, and the uniformity of concrete ormortar. UPV values of 3.5e4.5 km/s are considered “good” fornormal concrete (IS: 13311 (Part-1), 1992) and all hardenedmortarsfall within this range, even after 120 freezeethaw cycles. In fact,there is a slight increase in UPV with all samples, indicatingcontinuing strength development and hardening (Shariq et al.,2013), even when exposed to rapid freezing and thawing. Therelative dynamic modulus of < 60% compared to the initial valueindicates a failed specimen (ASTM C666/C666M-15, 2015); there-fore, it can be concluded that all samples clearly passed 120freezeethaw cycles without failure. However, the RHA1 and MS1mixtures suffered some visible disintegration (see supplementarymaterial) on the surface and consequently some weight loss.With SS1, there was some weight loss after 120 cycles but no clearvisible damage. Nevertheless, UPV was not affected by disintegra-tion or weight loss.

CB¼ cristobalite (SiO2), CC¼ calcite (CaCO3) or CeSeH.

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Table 4Results of freezeethaw tests for selected mortar mixtures.

Number of cycles Weight [g] Ultrasonic pulse velocity [km/s] Relative dynamic modulus of elasticity [%]

SS1 0 595 4.18 10060 602 4.23 103120 591 4.28 105

RHA1 0 578 3.92 10060 577 4.02 105120 566 4.00 104

MS1 0 581 4.07 10060 577 4.02 97120 580 4.24 108

T. Luukkonen et al. / Journal of Cleaner Production 187 (2018) 171e179178

4. Conclusions

This study aimed to replace solid synthetic sodium metasilicatewith a combination of RHA or MS and sodium hydroxide in thepreparation of one-part alkali-activated blast-furnace slag mortar.The motivation for the replacement is the high cost and environ-mental impact of synthetic sodium silicate, which could bedecreased by using industrial side-products.

The results show that RHA and MS exhibited much lower siliconsolubility compared to synthetic sodium metasilicate whenexposed to 0e10M NaOH solutions. The particle size of RHA andMS had a negligible effect on solubility in the range of approxi-mately 20e200 mm. The low silica availability of RHA and MS wasconfirmed by X-ray microanalysis, but the lower-than-expectedsolubility of blast furnace slag was also evident.

The silica source has a significant effect on the fresh and hard-ened properties of one-part alkali-activated slag mortar. Settingtime can be readily adjusted by the silica source and activatoramount. The shortest setting times were observed for the sodiummetasilicate series, followed by the RHA þ NaOH and MS þ NaOHseries. The initial and final setting times varied in the ranges of20e70 and 30e220 min, respectively. It is possible to achievecompressive strength of more than 100 MPa at 28 d for one-partalkali-activated slag mortar prepared with sodium metasilicate.Increasing the activator amount resulted in an approximately linearincrease in compressive strength. With MS or RHA and NaOH,however, compressive strength remained much lower(32e34MPa at 28 d) and was unaffected by the activator amount inthe studied range. Flexural strength followed the same trend ascompressive strength. Nevertheless, MS and RHA-based mortarsstill exhibited sufficient strengths for certain structural uses.

The freezeethaw resistance of the tested mortar specimensproved to be promising, as the specimens could withstand 120cycles. In fact, the strength development seemed to continue evenunder these harsh conditions, as indicated by ultrasonic pulse ve-locity measurements. However, mortars exhibited some weightloss, and samples containing MS or RHA suffered visible disinte-gration, although ultrasonic pulse velocity indicated good qualityafter 120 cycles.

Acknowledgements

This work was supported by the Finnish Funding Agency forTechnology and Innovation (Tekes) (project GEOBIZ, grant number1105/31/2016). Authors wish to thank Mr. Jarno Karvonen and Mr.Tun Nyo for performing analysis.

Appendix A. Supplementary data

Supplementary data related to this article can be found athttps://doi.org/10.1016/j.jclepro.2018.03.202.

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