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<front>
<journal-meta>
<journal-id journal-id-type="publisher-id">Front. Mater.</journal-id>
<journal-title>Frontiers in Materials</journal-title>
<abbrev-journal-title abbrev-type="pubmed">Front. Mater.</abbrev-journal-title>
<issn pub-type="epub">2296-8016</issn>
<publisher>
<publisher-name>Frontiers Media S.A.</publisher-name>
</publisher>
</journal-meta>
<article-meta>
<article-id pub-id-type="doi">10.3389/fmats.2016.00043</article-id>
<article-categories>
<subj-group subj-group-type="heading">
<subject>Materials</subject>
<subj-group>
<subject>Original Research</subject>
</subj-group>
</subj-group>
</article-categories>
<title-group>
<article-title>Microstructural Changes Induced by CO<sub>2</sub> Exposure in Alkali-Activated Slag/Metakaolin Pastes</article-title>
</title-group>
<contrib-group>
<contrib contrib-type="author" corresp="yes">
<name><surname>Bernal</surname> <given-names>Susan A.</given-names></name>
<xref ref-type="aff" rid="aff1"><sup>1</sup></xref>
<xref ref-type="corresp" rid="cor1">&#x0002A;</xref>
<uri xlink:href="http://frontiersin.org/people/u/360774"/>
</contrib>
</contrib-group>
<aff id="aff1"><sup>1</sup><institution>Department of Civil and Structural Engineering, The University of Sheffield</institution>, <addr-line>Sheffield</addr-line>, <country>UK</country></aff>
<author-notes>
<fn fn-type="edited-by"><p>Edited by: Wenhui Duan, Monash University, Australia</p></fn>
<fn fn-type="edited-by"><p>Reviewed by: Denvid Lau, City University of Hong Kong, Hong Kong; Jiafei Jiang, Tongji University, China</p></fn>
<corresp content-type="corresp" id="cor1">&#x0002A;Correspondence: Susan A. Bernal, <email>s.bernal&#x00040;sheffield.ac.uk</email></corresp>
<fn fn-type="other" id="fn001"><p>Specialty section: This article was submitted to Structural Materials, a section of the journal Frontiers in Materials</p></fn>
</author-notes>
<pub-date pub-type="epub">
<day>16</day>
<month>09</month>
<year>2016</year>
</pub-date>
<pub-date pub-type="collection">
<year>2016</year>
</pub-date>
<volume>3</volume>
<elocation-id>43</elocation-id>
<history>
<date date-type="received">
<day>11</day>
<month>07</month>
<year>2016</year>
</date>
<date date-type="accepted">
<day>02</day>
<month>09</month>
<year>2016</year>
</date>
</history>
<permissions>
<copyright-statement>Copyright &#x000A9; 2016 Bernal.</copyright-statement>
<copyright-year>2016</copyright-year>
<copyright-holder>Bernal</copyright-holder>
<license xlink:href="http://creativecommons.org/licenses/by/4.0/"><p>This is an open-access article distributed under the terms of the Creative Commons Attribution License (CC BY). The use, distribution or reproduction in other forums is permitted, provided the original author(s) or licensor are credited and that the original publication in this journal is cited, in accordance with accepted academic practice. No use, distribution or reproduction is permitted which does not comply with these terms.</p></license>
</permissions>
<abstract>
<p>The structural changes induced by accelerated carbonation in alkali-activated slag/metakaolin (MK) cements were determined. The specimens were carbonated for 540&#x02009;h in an environmental chamber with a CO<sub>2</sub> concentration of 1.0&#x02009;&#x000B1;&#x02009;0.2%, a temperature of 20&#x02009;&#x000B1;&#x02009;2&#x000B0;C, and relative humidity of 65&#x02009;&#x000B1;&#x02009;5%. Accelerated carbonation led to decalcification of the main binding phase of these cements, which is an aluminum substituted calcium silicate hydrate (C-(N-)A-S-H) type gel, and the consequent formation of calcium carbonate. The sodium-rich carbonates trona (Na<sub>2</sub>CO<sub>3</sub>&#x000B7;NaHCO<sub>3</sub>&#x000B7;2H<sub>2</sub>O) and gaylussite (Na<sub>2</sub>Ca(CO<sub>3</sub>)<sub>2</sub>&#x000B7;5H<sub>2</sub>O) were identified in cements containing up to 10 wt.% MK as carbonation products. The formation of these carbonates is mainly associated with the chemical reaction between the CO<sub>2</sub> and the free alkalis present in the pore solution. The structure of the carbonated cements is dominated by an aluminosilicate hydrate (N-A-S-H) type gel, independent of the MK content. The N-A-S-H type gels identified are likely to be derived both from the activation reaction of the MK, forming a low-calcium gel product that does not seem to undergo structural changes upon CO<sub>2</sub> exposure, and the decalcification of C-(N-)A-S-H type gel. The carbonated pastes present a highly porous microstructure, more notable as the content of MK content in the cement increases, which might have a negative impact on the durability of these materials in service.</p>
</abstract>
<kwd-group>
<kwd>alkali-activation</kwd>
<kwd>blast furnace slag</kwd>
<kwd>metakaolin</kwd>
<kwd>accelerated carbonation</kwd>
</kwd-group>
<contract-num rid="cn01">EP/M003272/1</contract-num>
<contract-sponsor id="cn01">Engineering and Physical Sciences Research Council<named-content content-type="fundref-id">10.13039/501100000266</named-content></contract-sponsor>
<counts>
<fig-count count="5"/>
<table-count count="2"/>
<equation-count count="2"/>
<ref-count count="40"/>
<page-count count="10"/>
<word-count count="6062"/>
</counts>
</article-meta>
</front>
<body>
<sec id="S1" sec-type="introduction">
<title>Introduction</title>
<p>Alkali-activated cements are a class of cements produced at room temperature via a chemical reaction between a poorly crystalline aluminosilicate material (termed the <italic>precursor</italic>) and a highly alkaline solution (the <italic>activator</italic>) to form hardened solids, if properly formulated and cured (Provis and Bernal, <xref ref-type="bibr" rid="B32">2014</xref>). Alkali-activated cements based on Ca-rich precursors, such as granulated blast furnace slag (GBFS), a by-product of the iron manufacturing industry, are currently used for production of mortars and concretes for structural and non-structural applications (Juenger et al., <xref ref-type="bibr" rid="B26">2011</xref>; Buchwald et al., <xref ref-type="bibr" rid="B15">2015</xref>). Alkali-activated cements are considered to be an environmentally sustainable construction material, and so research in this area has for several years been driven by the Greenhouse and economic benefits that can be gained from a more sustainable construction materials industry (Habert et al., <xref ref-type="bibr" rid="B22">2011</xref>). There is a general consensus that alkali-activated cements can offer cradle-to-gate Greenhouse emissions savings approaching 40&#x02013;80% compared to Portland cement for a performance-equivalent material. However, the question of whether mortars and concretes produced with these alternative binders can withstand the test of time during their service life requires further analysis. These materials do not yet have the long-term performance record of conventional Portland cement, and there is not yet a full understanding of the factors governing their durability.</p>
<p>Carbonation is understood as an acid&#x02013;base reaction between the hydrated products formed in a cement, and the carbonic acid formed by dissolution of atmospheric CO<sub>2</sub> in the pore solution, leading to the formation of carbonates (Hobbs, <xref ref-type="bibr" rid="B23">2001</xref>; Sanju&#x000E1;n et al., <xref ref-type="bibr" rid="B35">2003</xref>; Fern&#x000E1;ndez-Bertos et al., <xref ref-type="bibr" rid="B18">2004</xref>). In addition to causing matrix degradation, carbonation is also one of the key processes that can cause corrosion of steel rebar within concretes in service environments that do not involve chloride attack. Therefore, if alkali-activated slag cements and concretes are going to play an important role in future infrastructure development, they need to perform as well as, or better than, Portland cements under service conditions.</p>
<p>The susceptibility to carbonation of alkali-activated slag cements has been identified as one of their potential disadvantages, compared with Portland cement, as earlier studies assessing the degradation of these materials under exposure to high CO<sub>2</sub> concentrations showed notable structural changes that might compromise mechanical performance (Deja, <xref ref-type="bibr" rid="B16">2002</xref>; Palacios and Puertas, <xref ref-type="bibr" rid="B31">2006</xref>; Puertas et al., <xref ref-type="bibr" rid="B33">2006</xref>). The accelerated carbonation of alkali-activated binders is mainly a chemically controlled mechanism (Bernal, <xref ref-type="bibr" rid="B3">2014</xref>), and its extent is governed by similar parameters to those which promote specific microstructural characteristics in these materials, such as the type of the precursor used (aluminosilicate or GBFS) (Bernal et al., <xref ref-type="bibr" rid="B8">2013a</xref>, <xref ref-type="bibr" rid="B12">2014a</xref>), and the nature of the activator (Palacios and Puertas, <xref ref-type="bibr" rid="B31">2006</xref>). The testing conditions, such as relative humidity and CO<sub>2</sub> concentration, also have a significant impact on the rate and extent of carbonation of alkali-activated materials. This is mainly associated with the nature of the products derived from the pore solution carbonation, and also the desiccation and consequent cracking these materials undergo during the usual conditioning (involving exposure to a drying atmosphere) prior to accelerated carbonation testing (Bernal, <xref ref-type="bibr" rid="B3">2014</xref>; Yang et al., <xref ref-type="bibr" rid="B39">2016</xref>). Despite the apparent high susceptibility to carbonation, which has been reported for alkali-activated cements under laboratory conditions, no correlation has been identified between results obtained when exposing these materials to a high CO<sub>2</sub> concentration via accelerated testing methods, and under exposure to atmospheric carbonation conditions for several years (Bernal et al., <xref ref-type="bibr" rid="B13">2014b</xref>). This elucidates that the use of accelerated testing methods to assess carbonation of alkali-activated slags can underestimate the real performance these materials will have during service life.</p>
<p>The addition of a small amount of metakaolin (MK) (up to 20 wt.%) to slag-rich silicate-activated binders promotes the formation of a structure mainly composed of coexisting alkali aluminosilicate and Al-substituted calcium silicate hydrate (C-A-S-H) type gels (Bernal et al., <xref ref-type="bibr" rid="B5">2012a</xref>). The addition of up to 20 wt.% MK to alkali-activated slag cements does not have a notable impact in their mechanical performance, but in the case of highly reactive slags, it contributes to the ability to control the setting time (Bernal et al., <xref ref-type="bibr" rid="B7">2010</xref>). When using high doses of activator (&#x0003E;5% Na<sub>2</sub>O by mass of GBFS&#x02009;&#x0002B;&#x02009;MK), a C-A-S-H type gel is formed as the main binding phase (Bernal et al., <xref ref-type="bibr" rid="B9">2013b</xref>). Concretes and mortars produced with these high activator dose slag/MK blends developed high compressive strengths when compared to reference alkali-activated slag systems (Bernal et al., <xref ref-type="bibr" rid="B5">2012a</xref>; Bernal, <xref ref-type="bibr" rid="B4">2015</xref>). The inclusion of MK induced negligible changes in the compressive strength of mortars post-carbonation, although reductions in porosity were observed (Bernal, <xref ref-type="bibr" rid="B4">2015</xref>). Conversely, in concretes, exposure to high CO<sub>2</sub> concentrations led to a reduction of loading capacity, and increased porosity (Bernal et al., <xref ref-type="bibr" rid="B13">2014b</xref>). These divergent results are most likely a consequence of the changes in permeable voids between mortars and concretes, leading to different rates of carbonation and extents of microstructural changes for a given time of CO<sub>2</sub> exposure.</p>
<p>To further elucidate the role of the microstructural features of these carbonated binders in determining the performance of mortars and concretes produced with alkali-activated slag/MK binders, this study focusses on assessing the structural changes induced by high CO<sub>2</sub> exposure of alkali-activated slag/MK pastes, under controlled environmental conditions, using high-resolution X-ray diffraction (XRD), thermogravimetry, Fourier transform infrared (FTIR) spectroscopy, and scanning electron microscopy (SEM).</p>
</sec>
<sec id="S2">
<title>Experimental Program</title>
<sec id="S2-1">
<title>Materials</title>
<p>The primary raw material used was a blast furnace slag with a specific gravity of 2900&#x02009;kg/m<sup>3</sup> and Blaine fineness 399&#x02009;m<sup>2</sup>/kg. The particle size range, determined through laser diffraction, was 0.1&#x02013;74&#x02009;&#x003BC;m, with an average particle size, d<sub>50</sub>, of 15&#x02009;&#x003BC;m. The chemical composition of this slag is shown in Table <xref ref-type="table" rid="T1">1</xref>.</p>
<table-wrap position="float" id="T1">
<label>Table 1</label>
<caption><p><bold>Composition of the GBFS and MK used, determined through X-ray fluorescence analysis</bold>.</p></caption>
<table frame="hsides" rules="groups">
<thead>
<tr>
<th valign="top" align="left" rowspan="2">Precursor</th>
<th valign="top" align="center" colspan="7">Component (mass% as oxide)<hr/></th>
</tr>
<tr>
<th valign="top" align="center">SiO<sub>2</sub></th>
<th valign="top" align="center">Al<sub>2</sub>O<sub>3</sub></th>
<th valign="top" align="center">CaO</th>
<th valign="top" align="center">Fe<sub>2</sub>O<sub>3</sub></th>
<th valign="top" align="center">MgO</th>
<th valign="top" align="center">Other</th>
<th valign="top" align="center">LOI</th>
</tr>
</thead>
<tbody>
<tr>
<td align="left" valign="top">GBFS</td>
<td align="center" valign="top">32.3</td>
<td align="center" valign="top">16.3</td>
<td align="center" valign="top">42.5</td>
<td align="center" valign="top">2.4</td>
<td align="center" valign="top">2.9</td>
<td align="center" valign="top">1.7</td>
<td align="center" valign="top">1.9</td>
</tr>
<tr>
<td align="left" valign="top">MK</td>
<td align="center" valign="top">50.7</td>
<td align="center" valign="top">44.6</td>
<td align="center" valign="top">2.7</td>
<td align="center" valign="top">&#x02013;</td>
<td align="center" valign="top">&#x02013;</td>
<td align="center" valign="top">1.0</td>
<td align="center" valign="top">1.0</td>
</tr>
</tbody>
</table>
<table-wrap-foot>
<p><italic>LOI is loss on ignition at 1000&#x000B0;C</italic>.</p>
</table-wrap-foot>
</table-wrap>
<p>The MK used was produced in the laboratory by calcination of a kaolin containing minor quartz and dickite impurities, at 700&#x000B0;C in air, for 2&#x02009;h. The particle size range of the MK was 1.8&#x02013;100&#x02009;&#x003BC;m, with a d<sub>50</sub> of 13.2&#x02009;&#x003BC;m and 10% of particles finer than 4&#x02009;&#x003BC;m. Alkaline activating solutions were formulated by blending a commercial sodium silicate solution with 32.4 wt.% SiO<sub>2</sub>, 13.5 wt.% Na<sub>2</sub>O, and 54.1 wt.% H<sub>2</sub>O, together with 50 wt.% NaOH solution, to reach the specified activator compositions.</p>
</sec>
<sec id="S2-2">
<title>Sample Synthesis and Test Procedure</title>
<p>Pastes with different GBFS/(GBFS&#x02009;&#x0002B;&#x02009;MK) ratios and with a constant water/solids ratio of 0.23 (where &#x0201C;solids&#x0201D; is defined as GBFS&#x02009;&#x0002B;&#x02009;MK&#x02009;&#x0002B;&#x02009;anhydrous activator) were produced using the activation conditions described in Table <xref ref-type="table" rid="T2">2</xref>. The specimens were cast in a cylindrical mold and stored in hermetically sealed containers with a relative humidity of 90% and a temperature of 25&#x02009;&#x000B1;&#x02009;2&#x000B0;C for 28&#x02009;days.</p>
<table-wrap position="float" id="T2">
<label>Table 2</label>
<caption><p><bold>Mix designs of the pastes studied</bold>.</p></caption>
<table frame="hsides" rules="groups">
<thead>
<tr>
<th valign="top" align="left" rowspan="2">Component</th>
<th valign="top" align="center" colspan="3">Overall SiO<sub>2</sub>/Al<sub>2</sub>O<sub>3</sub> molar ratio<hr/></th>
</tr>
<tr>
<th valign="top" align="center">4.4</th>
<th valign="top" align="center">4.0</th>
<th valign="top" align="center">3.6</th>
</tr>
</thead>
<tbody>
<tr>
<td align="left" valign="top">GBFS</td>
<td align="center" valign="top">1</td>
<td align="center" valign="top">0.9</td>
<td align="center" valign="top">0.8</td>
</tr>
<tr>
<td align="left" valign="top">MK</td>
<td align="center" valign="top">&#x02013;</td>
<td align="center" valign="top">0.1</td>
<td align="center" valign="top">0.2</td>
</tr>
<tr>
<td align="left" valign="top">Sodium silicate solution</td>
<td align="center" valign="top">0.3</td>
<td align="center" valign="top">0.3</td>
<td align="center" valign="top">0.3</td>
</tr>
<tr>
<td align="left" valign="top">NaOH (50 wt.% solution)</td>
<td align="center" valign="top">0.2</td>
<td align="center" valign="top">0.2</td>
<td align="center" valign="top">0.2</td>
</tr>
<tr>
<td align="left" valign="top">Water</td>
<td align="center" valign="top">0.3</td>
<td align="center" valign="top">0.3</td>
<td align="center" valign="top">0.3</td>
</tr>
<tr>
<td align="left" valign="top">Activator concentration (% Na<sub>2</sub>O by mass of GBFS&#x02009;&#x0002B;&#x02009;MK)</td>
<td align="center" valign="top">10.6</td>
<td align="center" valign="top">11.6</td>
<td align="center" valign="top">12</td>
</tr>
</tbody>
</table>
</table-wrap>
<p>Pastes were then crushed and sieved to a particle size of 0.074&#x02009;mm, and exposed to CO<sub>2</sub> using an accelerated carbonation chamber with a CO<sub>2</sub> concentration of 1.0&#x02009;&#x000B1;&#x02009;0.2%, a temperature of 20&#x02009;&#x000B1;&#x02009;2&#x000B0;C, and RH&#x02009;&#x0003D;&#x02009;65&#x02009;&#x000B1;&#x02009;5%. These accelerated carbonation conditions were selected based on a previous study (Bernal et al., <xref ref-type="bibr" rid="B6">2012b</xref>), where it was demonstrated that comparable carbonation reaction products to those forming after several years of atmospheric exposure are identified in samples carbonated under these conditions. Non-carbonated samples, and samples exposed to CO<sub>2</sub> for 540&#x02009;h (referred to as carbonated throughout the document) were analyzed through:
<list list-type="bullet">
<list-item><p>X-ray diffraction was carried out using a high-resolution high-throughput synchrotron powder X-ray diffractometer with a system of 12 simultaneous analyzer/detectors, at beamline 11-BM at the Advanced Photon Source (APS), Argonne National Laboratory (USA). The tests were conducted according to the standard protocols for automated data acquisition on the 11-BM beamline. The conditions for the data collection were: continuous scanning of a detector covering an angular range of 20&#x000B0; with a step rate of 0.01&#x000B0;/s, a step size of 0.001&#x000B0; and wavelengths of &#x003BB;&#x02009;&#x0003D;&#x02009;0.401738&#x02009;&#x000C5; for non-carbonated samples, and 0.458879&#x02009;&#x000C5; for carbonated samples. Data have been converted to Q units (Q&#x02009;&#x0003D;&#x02009;4&#x003C0; sin&#x003B8;/&#x003BB;) for presentation here, to enable comparison between data sets collected at different wavelengths.</p></list-item>
<list-item><p>Fourier transform infrared spectrometry was conducted via the KBr pellet technique, using a Shimadzu FTIR 8400 instrument, scanning from 4000 to 400&#x02009;cm<sup>&#x02212;1</sup>.</p></list-item>
<list-item><p>Thermogravimetry was carried out in a SDT-Q600 TGA/DSC from TA Instruments. Samples were tested from 25 to 1100&#x000B0;C, in a nitrogen atmosphere, at a heating rate of 10&#x000B0;C/min.</p></list-item>
<list-item><p>Scanning electron microscopy of non-carbonated samples was carried out in a Philips XL30F Field Emission SEM, with an accelerating voltage of 15&#x02009;kV, and a working distance of 10&#x02009;mm.</p></list-item>
<list-item><p>Environmental scanning electron microscopy (ESEM) of unpolished carbonated samples was conducted using an FEI Quanta instrument with a 15&#x02009;kV accelerating voltage and a working distance of 10&#x02009;mm, in low vacuum mode.</p></list-item>
</list></p>
</sec>
</sec>
<sec id="S3" sec-type="discussion">
<title>Results and Discussion</title>
<sec id="S3-1">
<title>High-Resolution Synchrotron X-Ray Diffraction</title>
<p>High-resolution X-ray diffractograms of non-carbonated pastes of the compositions studied here, as a function of the curing time, were previously reported by Bernal et al. (<xref ref-type="bibr" rid="B9">2013b</xref>). As the main partially crystalline reaction products, tobermorite-type phases with three different basal spacings (9, 11, and 14&#x02009;&#x000C5;) were observed in these cements, most likely with some Al substitution (Myers et al., <xref ref-type="bibr" rid="B30">2013</xref>). A sodium calcium silicate hydrate (Na<sub>2</sub>Ca<sub>2</sub>Si<sub>2</sub>O<sub>7</sub>&#x000B7;H<sub>2</sub>O; Powder Diffraction File (PDF) &#x00023; 00-022-0891), and two aluminosilicate zeolite products, gismondine (CaAl<sub>2</sub>Si<sub>2</sub>O<sub>8</sub>&#x000B7;4H<sub>2</sub>O; PDF &#x00023; 00-020-0452), and garronite (NaCa<sub>2.5</sub>(Si<sub>10</sub>Al<sub>6</sub>)O<sub>32</sub>&#x000B7;13H<sub>2</sub>O; PDF &#x00023; 99-000-1300), the last of which was solely identified in specimens containing MK. Variations in the intensities of the reflections of some of these phases were observed as a function of the MK content, which is discussed in detail by Bernal et al. (<xref ref-type="bibr" rid="B9">2013b</xref>). Other crystalline phases, including gehlenite (Ca<sub>2</sub>Al<sub>2</sub>SiO<sub>7</sub>, PDF &#x00023; 00-035-0755), quartz (SiO<sub>2</sub>) (PDF &#x00023;01-078-2315), and calcite (CaCO<sub>3</sub>) (PDF&#x00023; 01-072-1214), attributed to the unreacted slag, were also observed.</p>
<p>Upon CO<sub>2</sub> exposure, samples with GBFS/(GBFS&#x02009;&#x0002B;&#x02009;MK)&#x02009;&#x0003D;&#x02009;1.0 (Figure <xref ref-type="fig" rid="F1">1</xref>A) showed the formation of the sodium carbonate trona (Na<sub>2</sub>CO<sub>3</sub>&#x000B7;NaHCO<sub>3</sub>&#x000B7;2H<sub>2</sub>O) (PDF &#x00023;00-029-1447), associated with the carbonation of the pore solution present in the sample (Bernal et al., <xref ref-type="bibr" rid="B6">2012b</xref>), along with minor traces of the sodium-calcium carbonate gaylussite (Na<sub>2</sub>Ca(CO<sub>3</sub>)<sub>2</sub>&#x000B7;5H<sub>2</sub>O, PDF&#x00023; 00-012-0255). This double salt has been identified as a carbonation product in some alkali-activated slag cements (Bernal et al., <xref ref-type="bibr" rid="B6">2012b</xref>, <xref ref-type="bibr" rid="B8">2013a</xref>), although was not observed in a study of carbonated samples produced with a similar slag to that used in this study, but activated with a lower activator dose (Bernal et al., <xref ref-type="bibr" rid="B7">2010</xref>). A notable increase in the intensity of the reflections assigned to calcite was observed, along with reduction in the intensities of the reflections assigned to the Al-substituted C-S-H and C-(N-)S-H type phases. This demonstrates that the exposure of these cements to high concentrations of CO<sub>2</sub> is leading to decalcification of the main binding reaction products, toward formation of calcium carbonates, as has been reported for Ca-rich alkali-activated cements (Palacios and Puertas, <xref ref-type="bibr" rid="B31">2006</xref>). Changes in the reflection assigned to the zeolites gismondine and garronite were not observed upon CO<sub>2</sub> exposure. The fact that traces of C-S-H type phases are still identifiable in the diffraction data for the carbonated samples indicates that the pastes are not yet fully carbonated after 540&#x02009;h of CO<sub>2</sub> exposure.</p>
<fig id="F1" position="float">
<label>Figure 1</label>
<caption><p><bold>High-resolution synchrotron X-ray diffraction patterns of non-carbonated from Bernal et al. (<xref ref-type="bibr" rid="B9">2013b</xref>) and accelerated-carbonated alkali-activated pasted with a GBFS/(GBFS&#x02009;&#x0002B;&#x02009;MK) of (A) 1.0, (B) 0.9, and (C) 0.8</bold>. Peaks marked as CS are assigned to tobermorite-type phases with the three different basal spacings as well as the Na-containing C-S-H.</p></caption>
<graphic xlink:href="fmats-03-00043-g001a.tif"/>
<graphic xlink:href="fmats-03-00043-g001b.tif"/>
</fig>
<p>Similar results to those observed in samples solely based on slag (Figure <xref ref-type="fig" rid="F1">1</xref>A) were identified in carbonated samples with GBFS/(GBFS&#x02009;&#x0002B;&#x02009;MK)&#x02009;&#x0003D;&#x02009;0.9 (Figure <xref ref-type="fig" rid="F1">1</xref>B). This suggests that the substitution of slag by MK in a low quantity (&#x02265;10 wt.%) does not induce notable changes in the phase assemblages of these alkali-activated cements. Conversely, in samples with GBFS/(GBFS&#x02009;&#x0002B;&#x02009;MK)&#x02009;&#x0003D;&#x02009;0.8, neither trona nor gaylussite were identified as carbonation products, although these pastes were produced with the highest activator Na<sub>2</sub>O concentration among the cements studied (Table <xref ref-type="table" rid="T2">2</xref>). This might be associated with the higher degree of consumption of alkalis via the activation reaction of MK, reducing the amount of free alkalis in the pore solution of these cements, and consequently supressing the formation of Na-rich carbonates.</p>
</sec>
<sec id="S3-2">
<title>Thermogravimetry</title>
<p>In non-carbonated pastes (Figure <xref ref-type="fig" rid="F2">2</xref>A), the main weight loss is identified below 250&#x000B0;C, and is more notable in pastes with higher MK contents. The weight loss in this temperature range is attributed to the evaporation of loosely bound water in the system, and dehydration of the substituted tobermorite-type (C-(N-)A-S-H) gel (Alarcon-Ru&#x000ED;z et al., <xref ref-type="bibr" rid="B1">2005</xref>) present in these pastes. The temperature at which the weight loss is most rapid (i.e., the minimum in the differential thermograms plotted in Figure <xref ref-type="fig" rid="F2">2</xref>) is similar for the three samples at 62&#x000B0;C, in good agreement with results previously identified for alkali-activated GBFS/MK systems with high slag content, where the structure of the binders is dominated by the activation of the slag (Buchwald et al., <xref ref-type="bibr" rid="B14">2007</xref>; Bernal et al., <xref ref-type="bibr" rid="B10">2011a</xref>). The fact that more weight is lost by samples with GBFS/(GBFS&#x02009;&#x0002B;&#x02009;MK)&#x02009;&#x0003D;&#x02009;0.8 might indicate that water is more loosely bound in the reaction products forming in this paste. The small peak observed at 107&#x000B0;C in the data for samples with GBFS/(GBFS&#x02009;&#x0002B;&#x02009;MK)&#x02009;&#x0003D;&#x02009;1.0 and 0.9 is attributed to the dehydration of the zeolite gismondine (Bernal et al., <xref ref-type="bibr" rid="B10">2011a</xref>), identified as one of the main crystalline reaction products in activated GBFS/MK under the activation conditions used in this study (Bernal et al., <xref ref-type="bibr" rid="B9">2013b</xref>). Gismondine was not observed as a reaction product in pastes with 20 wt.% MK (Bernal et al., <xref ref-type="bibr" rid="B9">2013b</xref>), consistent with the thermogravimetry results presented here.</p>
<fig id="F2" position="float">
<label>Figure 2</label>
<caption><p><bold>Thermogravimetry curves and differential thermograms of (A) non-carbonated and (B) accelerated-carbonated alkali-activated pasted with a GBFS/(GBFS&#x02009;&#x0002B;&#x02009;MK) of (i) 1.0, (ii) 0.9, and (iii) 0.8</bold>.</p></caption>
<graphic xlink:href="fmats-03-00043-g002.tif"/>
</fig>
<p>The peaks between 400&#x000B0;C and 418&#x000B0;C cannot be assigned to any crystalline phase present in these systems. The recent results of L&#x02019;H&#x000F4;pital et al. (<xref ref-type="bibr" rid="B27">2016</xref>) suggest that a weight loss in this temperature range most likely corresponds to dehydration of alkali-containing C-A-S-H type gels, such as those forming in the pastes assessed here. The peak at 640&#x000B0;C is assigned to calcium carbonate present in the anhydrous GBFS as a result of weathering prior to sample synthesis (Bernal et al., <xref ref-type="bibr" rid="B7">2010</xref>). Negligible weight changes were observed above 700&#x000B0;C.</p>
<p>In carbonated samples (Figure <xref ref-type="fig" rid="F2">2</xref>B), an initial weight loss band centered at 52&#x000B0;C is identified in all of the samples. Carbonation of alkali-activated slags leads to decalcification of the C-(N-)A-S-H type gels forming in these systems, resulting in the formation of an aluminosilicate hydrate type gel (Bernal et al., <xref ref-type="bibr" rid="B8">2013a</xref>, <xref ref-type="bibr" rid="B12">2014a</xref>), whose water is more loosely bound than in the original C-(N-)A-S-H. This might be inducing the shift toward lower temperatures of this weight loss peak compared to the uncarbonated samples. In specimens with GBFS/(GBFS&#x02009;&#x0002B;&#x02009;MK) ratios of 1.0 and 0.9 a peak at 112&#x000B0;C was observed, and assigned to trona, which is one of the main carbonate product forming in these binders as identified by XRD (Figure <xref ref-type="fig" rid="F1">1</xref>). Barall and Rogers (<xref ref-type="bibr" rid="B2">1966</xref>) identified that the thermal decomposition of trona takes place in two stages, as shown in Eqs <xref ref-type="disp-formula" rid="E1">1</xref> and <xref ref-type="disp-formula" rid="E2">2</xref>. The first decomposition stage leads to weight losses at &#x0007E;110&#x000B0;C, while decomposition of the sodium bicarbonate leads to weight losses at slightly higher temperatures (&#x0007E;123&#x000B0;C).</p>
<disp-formula id="E1"><label>(1)</label><mml:math id="M1"><mml:mrow><mml:msub><mml:mrow><mml:mtext>Na</mml:mtext></mml:mrow><mml:mtext>2</mml:mtext></mml:msub><mml:msub><mml:mrow><mml:mtext>CO</mml:mtext></mml:mrow><mml:mtext>3</mml:mtext></mml:msub><mml:mo>&#x022C5;</mml:mo><mml:msub><mml:mrow><mml:mtext>NaHCO</mml:mtext></mml:mrow><mml:mtext>3</mml:mtext></mml:msub><mml:mo>&#x022C5;</mml:mo><mml:msub><mml:mrow><mml:mtext>2H</mml:mtext></mml:mrow><mml:mtext>2</mml:mtext></mml:msub><mml:mtext>O</mml:mtext><mml:mo>&#x02192;</mml:mo><mml:msub><mml:mrow><mml:mtext>Na</mml:mtext></mml:mrow><mml:mtext>2</mml:mtext></mml:msub><mml:msub><mml:mrow><mml:mtext>CO</mml:mtext></mml:mrow><mml:mtext>3</mml:mtext></mml:msub><mml:mo>+</mml:mo><mml:msub><mml:mrow><mml:mtext>NaHCO</mml:mtext></mml:mrow><mml:mtext>3</mml:mtext></mml:msub><mml:mo>+</mml:mo><mml:msub><mml:mrow><mml:mtext>2H</mml:mtext></mml:mrow><mml:mtext>2</mml:mtext></mml:msub><mml:mtext>O</mml:mtext></mml:mrow></mml:math></disp-formula>
<disp-formula id="E2"><label>(2)</label><mml:math id="M2"><mml:mrow><mml:msub><mml:mrow><mml:mtext>2NaHCO</mml:mtext></mml:mrow><mml:mtext>3</mml:mtext></mml:msub><mml:mo>&#x02192;</mml:mo><mml:msub><mml:mrow><mml:mtext>Na</mml:mtext></mml:mrow><mml:mtext>2</mml:mtext></mml:msub><mml:msub><mml:mrow><mml:mtext>CO</mml:mtext></mml:mrow><mml:mtext>3</mml:mtext></mml:msub><mml:mo>+</mml:mo><mml:msub><mml:mrow><mml:mtext>CO</mml:mtext></mml:mrow><mml:mtext>2</mml:mtext></mml:msub><mml:mo>+</mml:mo><mml:msub><mml:mtext>H</mml:mtext><mml:mo>2</mml:mo></mml:msub><mml:mtext>O</mml:mtext></mml:mrow></mml:math></disp-formula>
<p>A peak centered at 168&#x000B0;C is also identified in pastes with a GBFS/(GBFS&#x02009;&#x0002B;&#x02009;MK) of 1.0 and 0.9, whose intensity reduced with the inclusion of MK in the binders. A less resolved peak has been identified at a similar temperatures in accelerated-carbonated alkali-activated slag cements (Bernal et al., <xref ref-type="bibr" rid="B8">2013a</xref>), and assigned to decomposition of hydrous sodium&#x02013;calcium carbonates [e.g., gaylussite or pirssonite (Johnson and Robb, <xref ref-type="bibr" rid="B25">1973</xref>)]. In the samples assessed, traces of gaylussite were identified by high-resolution XRD (Figure <xref ref-type="fig" rid="F1">1</xref>) and, therefore, this weight loss is assigned to decomposition of this phase. In samples with GBFS/(GBFS&#x02009;&#x0002B;&#x02009;MK)&#x02009;&#x0003D;&#x02009;0.8, peaks associated with decomposition of the sodium carbonate products were not observed, in accordance with the high-resolution XRD results (Figure <xref ref-type="fig" rid="F1">1</xref>).</p>
</sec>
<sec id="S3-3">
<title>Fourier Transform Infrared Spectroscopy</title>
<p>In non-carbonated samples solely based on slag (Figure <xref ref-type="fig" rid="F3">3</xref>A), a band at 1645cm<sup>&#x02212;1</sup> is observed, assigned to the bending vibration mode of the H-OH bonds in the reaction products forming. The band centered at 1414&#x02009;cm<sup>&#x02212;1</sup> is attributed to the asymmetric stretching mode of the O-C-O bonds of <inline-formula><mml:math id="M3"><mml:mrow><mml:msubsup><mml:mtext>CO</mml:mtext><mml:mn>3</mml:mn><mml:mrow><mml:mn>2</mml:mn><mml:mo>&#x02212;</mml:mo></mml:mrow></mml:msubsup></mml:mrow></mml:math></inline-formula> ions of the calcite present in the unreacted slag. The asymmetric stretching resonance of the Si-O-T bonds (where T can be Si or Al) was observed at 968&#x02009;cm<sup>&#x02212;1</sup>, along with a shoulder at 866&#x02009;cm<sup>&#x02212;1</sup> assigned to the vibration mode of the Al-O bonds of the <inline-formula><mml:math id="M4"><mml:mrow><mml:msubsup><mml:mtext>AlO</mml:mtext><mml:mn>4</mml:mn><mml:mrow><mml:mo>&#x02212;</mml:mo></mml:mrow></mml:msubsup></mml:mrow></mml:math></inline-formula> groups in the reaction products. The Si-O-T band position is characteristic of the environments of silicon tetrahedra (SiO<sub>4</sub>) in the chain structure of C-S-H type gels (Garc&#x000ED;a Lodeiro et al., <xref ref-type="bibr" rid="B20">2009</xref>). The band centered at 714&#x02009;cm<sup>&#x02212;1</sup> corresponds to the bending vibration mode of the Al-O-Si bonds, and the band at 648&#x02009;cm<sup>&#x02212;1</sup> is attributed to the symmetric vibration mode of the Si-O-Si or Al-O-Si bonds. This band corresponds to C-A-S-H type phases, and the zeolites gismondine and garronite forming in these systems, as identified by XRD (Figure <xref ref-type="fig" rid="F1">1</xref>). This band has also been observed in unreacted slag (Bernal et al., <xref ref-type="bibr" rid="B11">2011b</xref>), and has been attributed to gehlenite. All infrared band assignments follow references (Huang and Kerr, <xref ref-type="bibr" rid="B24">1960</xref>; Farmer, <xref ref-type="bibr" rid="B17">1974</xref>; Gadsden, <xref ref-type="bibr" rid="B19">1975</xref>; Sitarz et al., <xref ref-type="bibr" rid="B36">2000a</xref>,<xref ref-type="bibr" rid="B37">b</xref>).</p>
<fig id="F3" position="float">
<label>Figure 3</label>
<caption><p><bold>FTIR spectra of non-carbonated and accelerated-carbonated alkali-silicate-activated slag/metakaolin pastes with GBFS/(GBFS&#x02009;&#x0002B;&#x02009;MK) ratios of (A) 1.0, (B) 0.9, and (C) 0.8</bold>.</p></caption>
<graphic xlink:href="fmats-03-00043-g003.tif"/>
</fig>
<p>The addition of 10 wt.% MK [i.e., GBFS/(GBFS&#x02009;&#x0002B;&#x02009;MK)&#x02009;&#x0003D;&#x02009;0.9] led to a reduction in intensity of the O-C-O band centered at 1418&#x02009;cm<sup>&#x02212;1</sup>, consistent with the lower content of slag in these cements. In the region of the Si-O-T vibration modes, two overlapping bands at 1026 and 957&#x02009;cm<sup>&#x02212;1</sup> were identified. A higher wavenumber for the asymmetric stretching Si-O-T bonds is related to increased polymerization degree of the C-S-H type gels (Yu et al., <xref ref-type="bibr" rid="B40">1999</xref>), but this effect is counteracted when the Al supplied by MK is incorporated into this gel, which shifts the Si-O-T band toward lower wavenumbers (Bernal et al., <xref ref-type="bibr" rid="B11">2011b</xref>). Myers et al. (<xref ref-type="bibr" rid="B29">2015</xref>) identified highly polymerized silicate sites Q<sup>4</sup>(3Al) and Q<sup>4</sup>(4Al) in alkali-activated slags via high-resolution NMR spectroscopy, indicating the formation of a disordered aluminosilicate product resembling an alkali aluminosilicate (hydrate) (N&#x02013;A&#x02013;S(&#x02013;H)) type gel, typically observed in MK geopolymers (Williams et al., <xref ref-type="bibr" rid="B38">2011</xref>), along with the C-(N-)A-S-H type gels. Therefore, the two peaks identified in the Si-O-T region of the slag/MK cement spectrum (Figure <xref ref-type="fig" rid="F3">3</xref>B) cannot be assigned to a specific phase, but most likely correspond to the highly crosslinked C-(N-)A-S-H type gels typically identified in alkali-activated slag cements (Myers et al., <xref ref-type="bibr" rid="B29">2015</xref>), and potentially to a secondary N-A-S-H type gel derived from the activation of both slag and MK, and structurally related to the zeolites present in the samples. The shoulder at 887&#x02009;cm<sup>&#x02212;1</sup> along with a peak at 706&#x02009;cm<sup>&#x02212;1</sup> are assigned to the Al-O and Al-O-Si bonds that can be present in C-(N-)A-S-H and/or N-A-S-H type gels.</p>
<p>The addition of 20 wt.% MK [i.e., GBFS/(GBFS/MK)&#x02009;&#x0003D;&#x02009;0.8], Figure <xref ref-type="fig" rid="F3">3</xref>C, also led to the shifting of the T-O-T band, which is more symmetric than in samples with lower MK content and observed at 989&#x02009;cm<sup>&#x02212;1</sup>, along with the formation of a well-resolved peak at 875&#x02009;cm<sup>&#x02212;1</sup> assigned to calcite. The fact that a sole band is identified in this spectrum might suggest that there are less differences either in chemistry and/or structure (e.g., degree of crosslinking) of the C-(N-)A-S-H and N-A-S-H type gels forming in these cements as the MK content increases.</p>
<p>Upon accelerated carbonation (Figure <xref ref-type="fig" rid="F3">3</xref>A), in cements solely based on slag, a shoulder centered at 1475&#x02009;cm<sup>&#x02212;1</sup> is identified along with the asymmetric stretching vibration band of the <inline-formula><mml:math id="M5"><mml:mrow><mml:msubsup><mml:mtext>CO</mml:mtext><mml:mn>3</mml:mn><mml:mrow><mml:mn>2</mml:mn><mml:mo>&#x02212;</mml:mo></mml:mrow></mml:msubsup></mml:mrow></mml:math></inline-formula> groups at 1414&#x02009;cm<sup>&#x02212;1</sup>. This secondary carbonate band is assigned to trona (Huang and Kerr, <xref ref-type="bibr" rid="B24">1960</xref>), which was identified by XRD (Figure <xref ref-type="fig" rid="F1">1</xref>). Between 1100 and 900&#x02009;cm<sup>&#x02212;1</sup>, formation of a secondary band centered at 1130&#x02009;cm<sup>&#x02212;1</sup> is observed, along with a slight sift of the T-O-T band from 1014 to 1003&#x02009;cm<sup>&#x02212;1</sup>. Accelerated carbonation of alkali-activated slags cements leads to decalcification of the C-A-S-H type gels (Palacios and Puertas, <xref ref-type="bibr" rid="B31">2006</xref>), and higher wavenumbers can be associated with a high degree of polymerization of silicates. This is consistent with the formation of aluminosilicate hydrate type gels, which present bands at similar wavenumbers (Garc&#x000ED;a-Lodeiro et al., <xref ref-type="bibr" rid="B21">2008</xref>) to those identified in the carbonated pastes. The sharp peak identified at 871&#x02009;cm<sup>&#x02212;1</sup> is assigned to calcite, also identified by XRD (Figure <xref ref-type="fig" rid="F1">1</xref>). A slight increase in the intensity of the band at 714&#x02009;cm<sup>&#x02212;1</sup>, associated with the bending vibration mode of the Al-O-Si bonds, was also observed. This suggests an increase in the fraction of Al-O-Si bonds within this paste, consistent with the formation of N-A-S-H type gel in this cement upon CO<sub>2</sub> exposure (Bernal et al., <xref ref-type="bibr" rid="B8">2013a</xref>).</p>
<p>In carbonated pastes containing 10 wt.% MK (Figure <xref ref-type="fig" rid="F3">3</xref>B), similar bands to those identified in the formulation solely based on slag were observed. In this case, the T-O-T band shifted from 946&#x02009;cm<sup>&#x02212;1</sup> in non-carbonated samples to 1008&#x02009;cm<sup>&#x02212;1</sup> in carbonated specimens, along with the formation of a distinct shoulder at 1140&#x02009;cm<sup>&#x02212;1</sup>. Upon accelerated carbonation of Ca-free alkali-activated cements, changes in the structure of the N-A-S-H type gel have not been identified (Bernal et al., <xref ref-type="bibr" rid="B8">2013a</xref>); therefore, the changes in the position of the T-O-T band are assigned to the decalcification of the C-(N-)A-S-H type gel. The two distinct peaks correspond to N-A-S-H type gels (Garc&#x000ED;a-Lodeiro et al., <xref ref-type="bibr" rid="B21">2008</xref>) and the vibration mode identified at 642&#x02009;cm<sup>&#x02212;1</sup> is assigned to vibrations of rings present in this type of gel (Mozgawa et al., <xref ref-type="bibr" rid="B28">2002</xref>).</p>
<p>In carbonated pastes with a GBFS/(GBFS&#x02009;&#x0002B;&#x02009;MK) ratio of 0.8 (Figure <xref ref-type="fig" rid="F3">3</xref>C), the band at 1475&#x02009;cm<sup>&#x02212;1</sup> assigned to trona was not identified, consistent with the XRD (Figure <xref ref-type="fig" rid="F1">1</xref>C) and TGA (Figure <xref ref-type="fig" rid="F2">2</xref>B) results. Similar to the pastes with 10 wt.% MK (Figure <xref ref-type="fig" rid="F3">3</xref>B), two bands at 1001 and 1115&#x02009;cm<sup>&#x02212;1</sup> are observed in the carbonated samples, consistent with the formation of N-A-S-H type gels. A slight increase in the intensity of the peak at 875&#x02009;cm<sup>&#x02212;1</sup> assigned to calcite is observed in the carbonated sample.</p>
</sec>
<sec id="S3-4">
<title>Scanning Electron Microscopy</title>
<p>Non-carbonated samples based solely on slag present a highly dense, smooth, and continuous microstructure (Figure <xref ref-type="fig" rid="F4">4</xref>A), consistent with the results typically reported for these materials (San Nicolas et al., <xref ref-type="bibr" rid="B34">2014</xref>). Similar features are identified in samples with 10 wt.% MK (Figure <xref ref-type="fig" rid="F4">4</xref>B), although the surface of this cement seems rougher than that of the slag-only binders.</p>
<fig id="F4" position="float">
<label>Figure 4</label>
<caption><p><bold>Secondary electron micrographs of fractured sections of non-carbonated alkali-activated slag/metakaolin binders with GBFS/(GBFS&#x02009;&#x0002B;&#x02009;MK) ratios of (A) 1.0 and (B) 0.9</bold>.</p></caption>
<graphic xlink:href="fmats-03-00043-g004.tif"/>
</fig>
<p>Carbonation induces notable changes in the microstructures of the binders assessed. In pastes solely based on slag (Figures <xref ref-type="fig" rid="F5">5</xref>A1,A2), the continuity of the matrix is lost upon accelerated carbonation, so that highly fragmented laminar type structures are identified throughout the sample. A clear separation between each laminar type structure is observed, which might induce an increase of the microporosity in carbonated pastes, favoring the ingress of aggressive agents through the fragmented matrix. In pastes with 10 wt.% MK (Figures <xref ref-type="fig" rid="F5">5</xref>B1,B2) the formation of laminar type structures throughout the matrix, along with formation of large and continuous particles, is observed. The laminar structures seem more continuous than those observed in cements without MK.</p>
<fig id="F5" position="float">
<label>Figure 5</label>
<caption><p><bold>Secondary electron micrographs of fractured carbonated alkali-activated slag/metakaolin binders with GBFS/(GBFS&#x02009;&#x0002B;&#x02009;MK) ratios of (A1,A2) 1.0, (B1,B2) 0.9, and (C1,C2) 0.8</bold>.</p></caption>
<graphic xlink:href="fmats-03-00043-g005.tif"/>
</fig>
<p>The most notable changes are identified in the carbonated pastes with 20 wt.% (Figures <xref ref-type="fig" rid="F5">5</xref>C1,C2). This binder shows a continuous and highly porous microstructure, with a mesh type structure, where formation of distinctive crystalline phases was not identified.</p>
</sec>
</sec>
<sec id="S4">
<title>Implications for Durability of Alkali-Activated Slag/Metakaolin Pastes</title>
<p>One of the main threats posed by carbonation of alkali-activated reinforced concretes is a potential reduction of the alkalinity in the system, so that the pH drops to values that may induce depassivation of the steel rebars, leaving the materials vulnerable to development of corrosion processes. The carbonation of alkali-activated materials can be described as a two-step mechanism initiating with the carbonation of alkalis present in the pore solution, followed by the carbonation of the hydrated reaction products in the cementitious binder (Bernal, <xref ref-type="bibr" rid="B3">2014</xref>). The type and amount of carbonation products derived from the carbonation of the pore solution in particular will significantly impact the potential extent of damage to these materials.</p>
<p>The inclusion of 10 wt.% MK in these cements does not seem to have a marked impact on the sodium carbonates derived from the carbonation of the pore solution. Conversely, in samples with 20 wt.% MK, formation of sodium carbonates is not identified, indicating that most of the alkalis have been consumed upon reaction with MK, modifying the chemistry of the pore solution. It could be then expected that the carbonation of the hydrated reaction products forming in 20 wt.% MK-containing cements will occur faster than that of cements with lower MK contents, inducing more notable microstructural changes for similar times of exposure to high CO<sub>2</sub> concentrations.</p>
<p>The continuously porous microstructure identified in the carbonated 20 wt.% MK-containing cements will aid the ingress of aggressive agents within the material, facilitating any degradation process that might take place. However, considering the reduced size of the pores identified in this cement, it might be possible that the formation and precipitation of a large amount of carbonation products could plug some of the voids, reducing the permeability of the carbonated samples, as was identified in carbonated mortar specimens produced with the same formulations as the cements assessed (Bernal, <xref ref-type="bibr" rid="B4">2015</xref>). Further investigation of the physicochemical and microstructural impact of carbonation on alkali-activated slag-MK binders is required, but this paper has highlighted the importance of free alkali content in determining the mechanism and products of their carbonation.</p>
</sec>
<sec id="S5">
<title>Conclusion</title>
<p>The addition of minor fractions of MK to alkali-activated slag cements induces notable changes in the microstructure of these binders when exposed to high CO<sub>2</sub> concentrations. Independent of the MK content in the binders, CO<sub>2</sub> exposure induced decalcification of the C-(N-)A-S-H type phases present in these cements, leading to the formation of N-A-S-H type gels as the main reaction products. Similar sodium carbonates, derived from the carbonation reaction between the free alkalis in the pore solution and CO<sub>2</sub>, are identified in pastes with up to 10 wt.% MK. The fact that alkali-rich carbonate salts, such as trona or gaylussite are not identified when higher contents of MK are added to these cements indicates that there is a reduced content of free alkalis in the pore solution, most likely as a consequence of alkali binding through reaction with MK. The reduced concentration of free alkalis in the pore solution in MK-blended alkali-activated slag cements makes these cements more vulnerable to carbonation, as the dissolved CO<sub>2</sub> in pore solution will react with the hydrated binding phases, inducing a notable increase in their microporosity.</p>
</sec>
<sec id="S6">
<title>Author Contributions</title>
<p>SB is the sole author of this paper. She produced all the samples, analyzed them using the analytical techniques described in this manuscript, processed the information, and wrote the paper.</p>
</sec>
<sec id="S7">
<title>Conflict of Interest Statement</title>
<p>The author declares that the research was conducted in the absence of any commercial or financial relationships that could be construed as a potential conflict of interest.</p>
</sec>
</body>
<back>
<ack>
<p>This work was supported in part by the UK Engineering and Physical Sciences Research Council through grant EP/M003272/1. Use of the Advanced Photon Source at Argonne National Laboratory (ANL) was supported by the US Department of Energy, Office of Science, Office of Basic Energy Sciences, under Contract No. DE-AC02-06CH11357. Prof. Ruby Mej&#x000ED;a de Gutierrez (U. del Valle, Colombia), Prof. John Provis (U. Sheffield, UK), and Dr. Volker Rose (ANL, USA) are greatly acknowledged for the valuable discussions and support during the execution of this study.</p>
</ack>
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