<?xml version="1.0" encoding="UTF-8"?><!DOCTYPE article  PUBLIC "-//NLM//DTD Journal Publishing DTD v3.0 20080202//EN" "http://dtd.nlm.nih.gov/publishing/3.0/journalpublishing3.dtd"><article xmlns:mml="http://www.w3.org/1998/Math/MathML" xmlns:xlink="http://www.w3.org/1999/xlink" dtd-version="3.0" xml:lang="en" article-type="research article"><front><journal-meta><journal-id journal-id-type="publisher-id">GM</journal-id><journal-title-group><journal-title>Geomaterials</journal-title></journal-title-group><issn pub-type="epub">2161-7538</issn><publisher><publisher-name>Scientific Research Publishing</publisher-name></publisher></journal-meta><article-meta><article-id pub-id-type="doi">10.4236/gm.2019.92005</article-id><article-id pub-id-type="publisher-id">GM-93815</article-id><article-categories><subj-group subj-group-type="heading"><subject>Articles</subject></subj-group><subj-group subj-group-type="Discipline-v2"><subject>Earth&amp;Environmental Sciences</subject></subj-group></article-categories><title-group><article-title>
 
 
  NaOH Activation of Raw Soils: Effect of NaOH Content on the Drying Kinetic and Its Modelling
 
</article-title></title-group><contrib-group><contrib contrib-type="author" xlink:type="simple"><name name-style="western"><surname>Stevina</surname><given-names>Bouyila</given-names></name><xref ref-type="aff" rid="aff1"><sup>1</sup></xref></contrib><contrib contrib-type="author" xlink:type="simple"><name name-style="western"><surname>Raymond</surname><given-names>Gentil Elenga</given-names></name><xref ref-type="aff" rid="aff1"><sup>1</sup></xref><xref ref-type="corresp" rid="cor1"><sup>*</sup></xref></contrib><contrib contrib-type="author" xlink:type="simple"><name name-style="western"><surname>Louis</surname><given-names>Ahouet</given-names></name><xref ref-type="aff" rid="aff2"><sup>2</sup></xref></contrib><contrib contrib-type="author" xlink:type="simple"><name name-style="western"><surname>Mondésir</surname><given-names>Ngoulou</given-names></name><xref ref-type="aff" rid="aff1"><sup>1</sup></xref></contrib><contrib contrib-type="author" xlink:type="simple"><name name-style="western"><surname>Serge</surname><given-names>Konda</given-names></name><xref ref-type="aff" rid="aff2"><sup>2</sup></xref></contrib></contrib-group><aff id="aff2"><addr-line>Bureau de Contr&amp;amp;#244;le du Batiment et Travaux Publics (BCBTP), Brazzaville, Congo</addr-line></aff><aff id="aff1"><addr-line>Laboratoire des Matériaux et Energies (LME), Faculty of Sciences and Technics, Marien Ngouabi University, Brazzaville, Congo</addr-line></aff><pub-date pub-type="epub"><day>30</day><month>04</month><year>2019</year></pub-date><volume>09</volume><issue>02</issue><fpage>55</fpage><lpage>66</lpage><history><date date-type="received"><day>15,</day>	<month>February</month>	<year>2019</year></date><date date-type="rev-recd"><day>27,</day>	<month>April</month>	<year>2019</year>	</date><date date-type="accepted"><day>30,</day>	<month>April</month>	<year>2019</year></date></history><permissions><copyright-statement>&#169; Copyright  2014 by authors and Scientific Research Publishing Inc. </copyright-statement><copyright-year>2014</copyright-year><license><license-p>This work is licensed under the Creative Commons Attribution International License (CC BY). http://creativecommons.org/licenses/by/4.0/</license-p></license></permissions><abstract><p>
 
 
  NaOH activation of soils is an affordable and promising way to improve mechanical properties of earthen bricks. If for well-activated geopolymers, the hard polymeric network limits the influence of water on mechanical properties, for the weakly activated one, as non-calcined raw clayey soils, the influence of water on these properties would be more critical. This work aims to determine the effect of sodium hydroxide concentration on the drying kinetics of bricks made with raw clayey soils, and to model this kinetics. The results show that the drying kinetics is governed by the diffusion of water due to the absence of free water. The drying duration increases linearly with the increasing of NaOH content, while the volumetric shrinkage decreases, probably thanks to the reduction of the material porosity during the formation of the zeolitic structures. Besides, the drying duration is strongly and negatively correlated with the initial drying rate (
  &amp;#8722;0.97) and bricks did not show visible cracks. Among the five parametric models tested, the Khazaei’s model is the best in terms of all statistical criteria considered. For all models used, the coefficient of determination is ranged from 0.993 to 0.999, and the evolution of the models’ parameters is in accordance with that of the drying kinetics observed.
 
</p></abstract><kwd-group><kwd>Earthen Brick</kwd><kwd> Stabilization</kwd><kwd> Alkaline Activation</kwd><kwd> Modeling</kwd><kwd> Geopolymer</kwd><kwd> Drying Kinetics</kwd></kwd-group></article-meta></front><body><sec id="s1"><title>1. Introduction</title><p>Access to decent housing remains a significant challenge for many people, especially in developing countries [<xref ref-type="bibr" rid="scirp.93815-ref1">1</xref>] . In Sub-Saharan African villages, for example, the earthen dwellings remain the most numerous because they are low cost and easy to build. Indeed, for these constructions, the soil is usually taken from the immediate vicinity of the future house and used without stabilizer or with plant products (fibers, kernels) as reinforcement. Besides, the owners manufacture themselves or participate in the manufacture of the materials. In addition to be inexpensive, these houses are eco-friendly and have excellent thermal behavior [<xref ref-type="bibr" rid="scirp.93815-ref2">2</xref>] . However, they have the drawback to require frequent repairs due to the weak strength of the soils used. Indeed, unfortunately, only a few raw soils are suitable for construction without stabilization. For instance, for most standards, the suitable clay content to manufacture earthen bricks is ranged from 10 to 30% [<xref ref-type="bibr" rid="scirp.93815-ref3">3</xref>] [<xref ref-type="bibr" rid="scirp.93815-ref4">4</xref>] . For less and more clay contents, it is necessary to add a stabilizer as cement [<xref ref-type="bibr" rid="scirp.93815-ref5">5</xref>] , lime [<xref ref-type="bibr" rid="scirp.93815-ref6">6</xref>] , ash [<xref ref-type="bibr" rid="scirp.93815-ref7">7</xref>] [<xref ref-type="bibr" rid="scirp.93815-ref8">8</xref>] [<xref ref-type="bibr" rid="scirp.93815-ref9">9</xref>] or to use the improved technique as firing, geo-polymerization or soil activation [<xref ref-type="bibr" rid="scirp.93815-ref10">10</xref>] [<xref ref-type="bibr" rid="scirp.93815-ref11">11</xref>] [<xref ref-type="bibr" rid="scirp.93815-ref12">12</xref>] [<xref ref-type="bibr" rid="scirp.93815-ref13">13</xref>] [<xref ref-type="bibr" rid="scirp.93815-ref14">14</xref>] . The choice of the stabilizer depends on several factors, including its cost and availability, the nature of the soil, and the complexity of the technique [<xref ref-type="bibr" rid="scirp.93815-ref5">5</xref>] [<xref ref-type="bibr" rid="scirp.93815-ref6">6</xref>] .</p><p>The geopolymer compressive strength depends notably on the nature of the aluminosilicate source, the type and concentration of the alkaline activator used, and the duration and the temperature of the curing [<xref ref-type="bibr" rid="scirp.93815-ref13">13</xref>] [<xref ref-type="bibr" rid="scirp.93815-ref14">14</xref>] [<xref ref-type="bibr" rid="scirp.93815-ref15">15</xref>] . It varies from 1 MPa for geopolymers made in solid-state to 110 MPa for fly ash activated with the mixture of sodium silicate and sodium hydroxide solution. Although the mixture of the sodium silicate and hydroxide sodium is better than the hydroxide sodium alone [<xref ref-type="bibr" rid="scirp.93815-ref13">13</xref>] [<xref ref-type="bibr" rid="scirp.93815-ref14">14</xref>] [<xref ref-type="bibr" rid="scirp.93815-ref15">15</xref>] [<xref ref-type="bibr" rid="scirp.93815-ref16">16</xref>] , this last activator is the most used because it is the cheapest, and the most available [<xref ref-type="bibr" rid="scirp.93815-ref13">13</xref>] . Most studies on geopolymers are focused on their mechanical properties and the chemical reactions, while information on their drying kinetics is scarce. If for well-activated geopolymers, the hard polymeric network limits the influence of water on mechanical properties, for the weakly activated one, as non-calcined raw clayey soils [<xref ref-type="bibr" rid="scirp.93815-ref14">14</xref>] [<xref ref-type="bibr" rid="scirp.93815-ref16">16</xref>] [<xref ref-type="bibr" rid="scirp.93815-ref17">17</xref>] , the influence of water on these properties would be more critical. Besides, it is well known that during their drying, clayey materials often shrink and crack due to the evaporation of water. The purpose of this work is to determine the effect of sodium hydroxide concentration on the drying kinetics of earth bricks, on the one hand, and to model this kinetics, on the other hand.</p></sec><sec id="s2"><title>2. Materials and Methods</title><sec id="s2_1"><title>2.1. Soils and Manufacture of Bricks</title><p>Two raw clayey soils were used for the manufacture of bricks. The first one was obtained by crushing termite Cubitermes spp. mounds (CMS) collected in the savanna around NGO (2˚29'14&quot;S; 15˚45'20&quot;E). They are at most 50 cm high and 30 cm large and are usually used to build floors in traditional houses or as rural road pavement. The crushed soil was sieved and only grains smaller than 2 mm were retained to manufacture bricks. The characteristics of this soil have been published [<xref ref-type="bibr" rid="scirp.93815-ref18">18</xref>] and are recalled in <xref ref-type="table" rid="table1">Table 1</xref>.</p><p>The second soil used is the lateritic soil (LS) from Mouyami (4˚27'34&quot;S; 14˚42'48&quot;E). It has been sieved to retain only the grains smaller than 2 mm. Its</p><table-wrap id="table1" ><label><xref ref-type="table" rid="table1">Table 1</xref></label><caption><title> Characteristics of the lateritic soil (LS) and the Cubitermes mound soil (CMS) used to manufacture earth bricks. W<sub>L</sub> = Liquid limit; W<sub>p</sub> = Plastic limit; ω<sub>omc</sub> = Optimum moisture content; γ = apparent density; OM = organic matter</title></caption><table><tbody><thead><tr><th align="center" valign="middle" >Soil characteristics</th><th align="center" valign="middle" >LS</th><th align="center" valign="middle" >CMS</th></tr></thead><tr><td align="center" valign="middle" >Clay (%)</td><td align="center" valign="middle" >31</td><td align="center" valign="middle" >25</td></tr><tr><td align="center" valign="middle" >Silt (%)</td><td align="center" valign="middle" >19</td><td align="center" valign="middle" >25</td></tr><tr><td align="center" valign="middle" >Sand (%)</td><td align="center" valign="middle" >50</td><td align="center" valign="middle" >50</td></tr><tr><td align="center" valign="middle" >W<sub>L</sub> (%)</td><td align="center" valign="middle" >27.9</td><td align="center" valign="middle" >11.6</td></tr><tr><td align="center" valign="middle" >W<sub>p</sub> (%)</td><td align="center" valign="middle" >9.9</td><td align="center" valign="middle" >2.1</td></tr><tr><td align="center" valign="middle" >PI (%)</td><td align="center" valign="middle" >18</td><td align="center" valign="middle" >9.5</td></tr><tr><td align="center" valign="middle" >ω<sub>omc</sub> (%)</td><td align="center" valign="middle" >10</td><td align="center" valign="middle" >15.2</td></tr><tr><td align="center" valign="middle" >γ (t/m<sup>3</sup>)</td><td align="center" valign="middle" >2.1</td><td align="center" valign="middle" >1.72</td></tr><tr><td align="center" valign="middle" >OM (%)</td><td align="center" valign="middle" >0.54</td><td align="center" valign="middle" >5.00</td></tr></tbody></table></table-wrap><p>geotechnical characteristics have been determined as described in [<xref ref-type="bibr" rid="scirp.93815-ref18">18</xref>] , that is, the particle size analysis was carried out in accordance with the NF 94 056 [<xref ref-type="bibr" rid="scirp.93815-ref19">19</xref>] and NF 94 057 [<xref ref-type="bibr" rid="scirp.93815-ref20">20</xref>] standards, and the Atterberg limits, the dry density, and the optimal moisture content were measured in accordance with the NF 94 051 [<xref ref-type="bibr" rid="scirp.93815-ref21">21</xref>] and NF P94-093 [<xref ref-type="bibr" rid="scirp.93815-ref22">22</xref>] standards, respectively. The organic matter content was determined by chemical route using the Walkley and Black method [<xref ref-type="bibr" rid="scirp.93815-ref23">23</xref>] . The results of these analyses are reported in <xref ref-type="table" rid="table1">Table 1</xref>.</p><p>For the stabilization of the bricks, five alkaline solutions were prepared (1.5%; 2.5%; 5%; 7.5% and 10% by weight) by dissolving sodium hydroxide pellets with a purity of 98% in distilled water. These NaOH solutions were used instead of the usual tap water for the manufacture of the bricks, at the content of the optimum moisture content determined through the Proctor test. The bricks have been molded by using a mechanical press with a pressure of 6 MPa. A whitish powder appeared on the surface of the stabilized bricks for 7.5% and 10% NaOH solutions. This powder is probably due to the reaction of sodium hydroxide with the air carbonic gas [<xref ref-type="bibr" rid="scirp.93815-ref13">13</xref>] .</p><p>The volumetric shrinkage rate of bricks at the instant t, λ(t), is equal to the difference between the initial volume V(0) and the volume at the instant t, V(t) divided by the initial volume.</p></sec><sec id="s2_2"><title>2.2. Monitoring and Modeling of the Drying Kinetics</title><p>The monitoring of the drying kinetics of the bricks was carried out as described in [<xref ref-type="bibr" rid="scirp.93815-ref18">18</xref>] , i.e., the mass of the bricks was recorded until its stabilization. The brick is assumed dry when its mass variation during three consecutive days is less than 2%. For each NaOH solution and soil type, three tests were conducted to check the reproducibility of the results.</p><p>Five parametric models have been tested to simulate the drying kinetics of the bricks: the Page-Avrami model [<xref ref-type="bibr" rid="scirp.93815-ref24">24</xref>] [<xref ref-type="bibr" rid="scirp.93815-ref25">25</xref>] , the diffusion model [<xref ref-type="bibr" rid="scirp.93815-ref18">18</xref>] [<xref ref-type="bibr" rid="scirp.93815-ref26">26</xref>] , the Khazaei’s model [<xref ref-type="bibr" rid="scirp.93815-ref27">27</xref>] [<xref ref-type="bibr" rid="scirp.93815-ref28">28</xref>] , the Peleg’s model [<xref ref-type="bibr" rid="scirp.93815-ref29">29</xref>] [<xref ref-type="bibr" rid="scirp.93815-ref30">30</xref>] and the Yong’s model [<xref ref-type="bibr" rid="scirp.93815-ref18">18</xref>] [<xref ref-type="bibr" rid="scirp.93815-ref31">31</xref>] . The meaning of their parameters has been recalled in [<xref ref-type="bibr" rid="scirp.93815-ref18">18</xref>] and their values are determined by minimizing the reduced chi-square using the origin Pro 8 software. The goodness of the fit is estimated through the value of its coefficient of determination R<sup>2</sup>, the root mean square of the error (RMSE) and the Akaike’s Information Criterion (AIC). The models’ expressions are reported in <xref ref-type="table" rid="table2">Table 2</xref>.</p><p>The evaporable water content of the brick at the time t (the reduced mass) M<sub>r</sub>(t) is calculated according to the formula:</p><p>M r ( t ) = M ( 0 ) − M ( t ) M ( 0 ) − M f</p><p>where M(t) is the brick’s mass at the time t and M<sub>f</sub> the mass at the end of the drying.</p></sec></sec><sec id="s3"><title>3. Results and Discussion</title><sec id="s3_1"><title>3.1. Effect of the NaOH Content on the Drying Kinetics and Shrinkage of Bricks</title><p>The drying kinetics curves of earthen bricks made with Cubitermes spp. mound soil and lateritic soil activated with hydroxide sodium solutions are reported in <xref ref-type="fig" rid="fig1">Figure 1</xref>(a) and <xref ref-type="fig" rid="fig1">Figure 1</xref>(b), respectively.</p><p>These curves did not show the constant drying rate phase (a straight line at the start of the curve), but a steady variation of the drying rate, that is, there is almost no free water in the bricks. In other words, these drying kinetics are governed by the diffusion of moisture from the interior to the surface of bricks [<xref ref-type="bibr" rid="scirp.93815-ref25">25</xref>] . This behavior could be linked to the fact that the moisture content used to make bricks is the optimum moisture content (OMC) of the soil determined by the Proctor test. Indeed, the OMC diminishes the friction between soil grains, allowing the soil to have the highest density during its compaction, without being liquid [<xref ref-type="bibr" rid="scirp.93815-ref22">22</xref>] . The drying duration and the initial drying rate deduced from these curves are represented versus the activator content in <xref ref-type="fig" rid="fig2">Figure 2</xref>(a) and <xref ref-type="fig" rid="fig2">Figure 2</xref>(b), respectively. It appears that the difference between the clay contents of the two soils used has not a significant effect on the drying kinetics of the bricks. On the other hand, the activation of soils with NaOH increases the drying duration from about 23 days for non-stabilized bricks to about 28 days for the stabilized</p><table-wrap id="table2" ><label><xref ref-type="table" rid="table2">Table 2</xref></label><caption><title> Expressions of the models with their parameters. M<sub>r</sub>(t) is the evaporable water content of the brick at the time t</title></caption><table><tbody><thead><tr><th align="center" valign="middle" >Model</th><th align="center" valign="middle" >M r ( t )</th><th align="center" valign="middle" >Parameters</th><th align="center" valign="middle" >References</th></tr></thead><tr><td align="center" valign="middle" >Page-Avrami</td><td align="center" valign="middle" >exp ( − k t n )</td><td align="center" valign="middle" >k, n</td><td align="center" valign="middle" >[<xref ref-type="bibr" rid="scirp.93815-ref24">24</xref>] [<xref ref-type="bibr" rid="scirp.93815-ref25">25</xref>]</td></tr><tr><td align="center" valign="middle" >Diffusion</td><td align="center" valign="middle" >a exp ( − k t ) + ( 1 − a ) exp ( − k b t )</td><td align="center" valign="middle" >a, k, b</td><td align="center" valign="middle" >[<xref ref-type="bibr" rid="scirp.93815-ref18">18</xref>] [<xref ref-type="bibr" rid="scirp.93815-ref26">26</xref>]</td></tr><tr><td align="center" valign="middle" >Khazaei</td><td align="center" valign="middle" >1 − a ( 1 − exp ( − t / T ) ) − b t</td><td align="center" valign="middle" >a, T, b</td><td align="center" valign="middle" >[<xref ref-type="bibr" rid="scirp.93815-ref27">27</xref>] [<xref ref-type="bibr" rid="scirp.93815-ref28">28</xref>]</td></tr><tr><td align="center" valign="middle" >Peleg</td><td align="center" valign="middle" >1 − t / ( a + b t )</td><td align="center" valign="middle" >a, b</td><td align="center" valign="middle" >[<xref ref-type="bibr" rid="scirp.93815-ref29">29</xref>] [<xref ref-type="bibr" rid="scirp.93815-ref30">30</xref>]</td></tr><tr><td align="center" valign="middle" >Yong</td><td align="center" valign="middle" >c t − μ exp ( − t / T )</td><td align="center" valign="middle" >c, &#181;, T</td><td align="center" valign="middle" >[<xref ref-type="bibr" rid="scirp.93815-ref18">18</xref>] [<xref ref-type="bibr" rid="scirp.93815-ref31">31</xref>]</td></tr></tbody></table></table-wrap><p>bricks with the 10% NaOH solution. For the means values and by linear regression, the following relationship was found between the drying duration (D) and the NaOH content (α):</p><p>D = 24 + 0.8 α − 0.04 α 2 ; R 2 = 0.91</p><p>This lengthening of the drying duration by the NaOH activation could be explained by the tendency of NaOH to form compounds with water, and/or by the formation of the zeolitic structure between the initial soil grains [<xref ref-type="bibr" rid="scirp.93815-ref13">13</xref>] [<xref ref-type="bibr" rid="scirp.93815-ref16">16</xref>] [<xref ref-type="bibr" rid="scirp.93815-ref17">17</xref>] . Indeed, for an alkaline activated mortar made with a natural soil, Kim and al. observed that the formation of zeolitic structure is coupled with the reduction of the mortar porosity [<xref ref-type="bibr" rid="scirp.93815-ref16">16</xref>] . For their part, Diop and Grutzeck reported microstructure transformations during the alkaline activation of a clayey soil [<xref ref-type="bibr" rid="scirp.93815-ref17">17</xref>] . Besides, the drying duration has a strong and negative correlation with the initial drying rate (−0.97). Thus, NaOH activation of soil and stabilization of soil with cassava starch or amylopectin have opposite effects on the drying duration [<xref ref-type="bibr" rid="scirp.93815-ref18">18</xref>] . This variation of the effect of stabilizers on the brick behavior justifies the necessity to evaluate each process to optimize it.</p><p>As for the drying kinetics, there is no significant difference between the volumetric shrinkage rate of Cubitermes spp. soil bricks and that of lateritic soil bricks (<xref ref-type="fig" rid="fig3">Figure 3</xref>(a) and <xref ref-type="fig" rid="fig3">Figure 3</xref>(b)), despite the difference in clay content. The NaOH activation reduces significantly the shrinkage rate of bricks from about 5% for non-activated soils to 3% for soil activated with the 10% NaOH solution. This reduction of the shrinkage rate could be due to the formation of the zeolitic structure [<xref ref-type="bibr" rid="scirp.93815-ref13">13</xref>] [<xref ref-type="bibr" rid="scirp.93815-ref16">16</xref>] [<xref ref-type="bibr" rid="scirp.93815-ref17">17</xref>] that reduces the brick porosity as above mentioned. Besides, manufactured earth bricks did not show visible cracks. In fact, the increasing of the drying duration combined with the shrinkage reduction would reduce the appearance of cracks in bricks, and therefore would contribute to the increase of their strength. Indeed, slower lost of water, and weaker shrinkage generate less internal stresses, and thus the appearance of cracks in the bricks.</p><p>The shrinkage decrease observed here is lower than that induced by the addition of lime [<xref ref-type="bibr" rid="scirp.93815-ref6">6</xref>] and plant fibers [<xref ref-type="bibr" rid="scirp.93815-ref32">32</xref>] [<xref ref-type="bibr" rid="scirp.93815-ref33">33</xref>] , while it is higher than that produced by the addition of cement [<xref ref-type="bibr" rid="scirp.93815-ref34">34</xref>] or polyethylene strap [<xref ref-type="bibr" rid="scirp.93815-ref35">35</xref>] . However, in average, the improvement of the earthen brick strength due to the addition of lime [<xref ref-type="bibr" rid="scirp.93815-ref6">6</xref>] [<xref ref-type="bibr" rid="scirp.93815-ref36">36</xref>] , or plant fibers [<xref ref-type="bibr" rid="scirp.93815-ref32">32</xref>] [<xref ref-type="bibr" rid="scirp.93815-ref33">33</xref>] is lower than that reported for the NaOH activated soils [<xref ref-type="bibr" rid="scirp.93815-ref16">16</xref>] [<xref ref-type="bibr" rid="scirp.93815-ref17">17</xref>] .</p></sec><sec id="s3_2"><title>3.2. Evaluation of the Models</title><p>The reduced water contents predicted by the models are represented as functions of those measured in <xref ref-type="fig" rid="fig4">Figure 4</xref>. To evaluate the quality of these predictions,</p><p>the mean values of the coefficient of determination (R<sup>2</sup>), the root mean square error (RMSE), and the Aike’s information criterion (AIC) for all models tested are also reported on these figures. For each model and any drying kinetics curve, the coefficient of determination is greater than 0.992, and the RMSE is less than 0.03. Therefore, all these models could be considered suitable to simulate this drying kinetics. However, the Khazaei model has better results than the others (<xref ref-type="table" rid="table3">Table 3</xref>), for all statistical criteria. As it has already proved to be the best for simulating the drying kinetics of earthen bricks stabilized with other binders [<xref ref-type="bibr" rid="scirp.93815-ref18">18</xref>] , it seems very suitable for modeling the drying kinetics of compressed earth bricks.</p><p>The values of the parameter n (the exponent of the time) of the Page-Avrami model and those of the khazaei’s model (<xref ref-type="table" rid="table4">Table 4</xref> and <xref ref-type="table" rid="table5">Table 5</xref>) are on average equal to 1. These values are consistent with the shape of the drying curves which shows a steady decrease of the drying rate. However, there is a slight increase in the value of n with the increase of NaOH content. All factors affecting negatively the drying rate could contribute to this increase, and in particular, the decrease of porosity by the formation of zeolitic structure, the appearance of the flour on the brick surface due to the NaOH-CO<sub>2</sub> reaction. Indeed, as we have already reported in the material and methods part, for the bricks activated with 7.5 and 10% NaOH solution, a whitish powder appeared on the surface of the bricks.</p><table-wrap id="table3" ><label><xref ref-type="table" rid="table3">Table 3</xref></label><caption><title> The ranking of the goodness of fit of the different models according to the statistical criteria</title></caption><table><tbody><thead><tr><th align="center" valign="middle" ></th><th align="center" valign="middle"  colspan="3"  >CMS bricks</th><th align="center" valign="middle"  colspan="3"  >LS bricks</th></tr></thead><tr><td align="center" valign="middle" >Rank</td><td align="center" valign="middle" >R<sup>2</sup></td><td align="center" valign="middle" >X<sup>2</sup></td><td align="center" valign="middle" >AIC</td><td align="center" valign="middle" >R<sup>2</sup></td><td align="center" valign="middle" >X<sup>2</sup></td><td align="center" valign="middle" >AIC</td></tr><tr><td align="center" valign="middle" >1</td><td align="center" valign="middle" >Kharzaei</td><td align="center" valign="middle" >Kharzaei</td><td align="center" valign="middle" >Kharzaei</td><td align="center" valign="middle" >Kharzaei</td><td align="center" valign="middle" >Kharzaei</td><td align="center" valign="middle" >Kharzaei</td></tr><tr><td align="center" valign="middle" >2</td><td align="center" valign="middle" >Diffusion</td><td align="center" valign="middle" >Diffusion</td><td align="center" valign="middle" >Avrami</td><td align="center" valign="middle" >Diffusion</td><td align="center" valign="middle" >Diffusion</td><td align="center" valign="middle" >Diffusion</td></tr><tr><td align="center" valign="middle" >3</td><td align="center" valign="middle" >Avrami</td><td align="center" valign="middle" >Avrami</td><td align="center" valign="middle" >Diffusion</td><td align="center" valign="middle" >Avrami</td><td align="center" valign="middle" >Avrami</td><td align="center" valign="middle" >Avrami</td></tr><tr><td align="center" valign="middle" >4</td><td align="center" valign="middle" >Yong</td><td align="center" valign="middle" >Yong</td><td align="center" valign="middle" >Yong</td><td align="center" valign="middle" >Peleg</td><td align="center" valign="middle" >Peleg</td><td align="center" valign="middle" >Peleg</td></tr><tr><td align="center" valign="middle" >5</td><td align="center" valign="middle" >Peleg</td><td align="center" valign="middle" >Peleg</td><td align="center" valign="middle" >Peleg</td><td align="center" valign="middle" >Yong</td><td align="center" valign="middle" >Yong</td><td align="center" valign="middle" >Yong</td></tr></tbody></table></table-wrap><table-wrap id="table4" ><label><xref ref-type="table" rid="table4">Table 4</xref></label><caption><title> Values of the models’ parameters applied to drying kinetics of Cubitermes spp. mound soil bricks activated with NaOH solutions</title></caption><table><tbody><thead><tr><th align="center" valign="middle" ></th><th align="center" valign="middle"  colspan="2"  >Page-Avrami</th><th align="center" valign="middle"  colspan="3"  >Diffusion</th><th align="center" valign="middle"  colspan="3"  >Yong</th><th align="center" valign="middle"  colspan="4"  >Khazaei</th><th align="center" valign="middle"  colspan="2"  >Peleg</th></tr></thead><tr><td align="center" valign="middle" >NaOH (%)</td><td align="center" valign="middle" >k</td><td align="center" valign="middle" >n</td><td align="center" valign="middle" >a</td><td align="center" valign="middle" >b</td><td align="center" valign="middle" >k</td><td align="center" valign="middle" >c</td><td align="center" valign="middle" >T</td><td align="center" valign="middle" >u</td><td align="center" valign="middle" >a</td><td align="center" valign="middle" >b</td><td align="center" valign="middle" >n</td><td align="center" valign="middle" >T</td><td align="center" valign="middle" >a</td><td align="center" valign="middle" >b</td></tr><tr><td align="center" valign="middle" >0</td><td align="center" valign="middle" >0.28</td><td align="center" valign="middle" >0.92</td><td align="center" valign="middle" >0.8</td><td align="center" valign="middle" >3.3</td><td align="center" valign="middle" >0.21</td><td align="center" valign="middle" >0.94</td><td align="center" valign="middle" >4.40</td><td align="center" valign="middle" >0.01</td><td align="center" valign="middle" >1.02</td><td align="center" valign="middle" >−0.001</td><td align="center" valign="middle" >0.90</td><td align="center" valign="middle" >4.2</td><td align="center" valign="middle" >2.7</td><td align="center" valign="middle" >0.87</td></tr><tr><td align="center" valign="middle" >1.5</td><td align="center" valign="middle" >0.22</td><td align="center" valign="middle" >0.97</td><td align="center" valign="middle" >1</td><td align="center" valign="middle" >4.5</td><td align="center" valign="middle" >0.21</td><td align="center" valign="middle" >0.98</td><td align="center" valign="middle" >4.90</td><td align="center" valign="middle" >0.01</td><td align="center" valign="middle" >1.03</td><td align="center" valign="middle" >−0.001</td><td align="center" valign="middle" >0.95</td><td align="center" valign="middle" >4.9</td><td align="center" valign="middle" >3.5</td><td align="center" valign="middle" >0.84</td></tr><tr><td align="center" valign="middle" >2.5</td><td align="center" valign="middle" >0.17</td><td align="center" valign="middle" >1.04</td><td align="center" valign="middle" >−13</td><td align="center" valign="middle" >1</td><td align="center" valign="middle" >0.14</td><td align="center" valign="middle" >1.03</td><td align="center" valign="middle" >5.40</td><td align="center" valign="middle" >−0.01</td><td align="center" valign="middle" >1.02</td><td align="center" valign="middle" >−0.001</td><td align="center" valign="middle" >1.03</td><td align="center" valign="middle" >5.8</td><td align="center" valign="middle" >4.4</td><td align="center" valign="middle" >0.80</td></tr><tr><td align="center" valign="middle" >5</td><td align="center" valign="middle" >0.15</td><td align="center" valign="middle" >1.06</td><td align="center" valign="middle" >0</td><td align="center" valign="middle" >22</td><td align="center" valign="middle" >0.01</td><td align="center" valign="middle" >1.04</td><td align="center" valign="middle" >5.89</td><td align="center" valign="middle" >−0.01</td><td align="center" valign="middle" >0.96</td><td align="center" valign="middle" >0.002</td><td align="center" valign="middle" >1.06</td><td align="center" valign="middle" >6</td><td align="center" valign="middle" >5</td><td align="center" valign="middle" >0.79</td></tr><tr><td align="center" valign="middle" >7.5</td><td align="center" valign="middle" >0.12</td><td align="center" valign="middle" >1.08</td><td align="center" valign="middle" >−5</td><td align="center" valign="middle" >1.1</td><td align="center" valign="middle" >0.10</td><td align="center" valign="middle" >1.04</td><td align="center" valign="middle" >6.50</td><td align="center" valign="middle" >−0.01</td><td align="center" valign="middle" >0.98</td><td align="center" valign="middle" >0.001</td><td align="center" valign="middle" >1.05</td><td align="center" valign="middle" >7</td><td align="center" valign="middle" >5.9</td><td align="center" valign="middle" >0.76</td></tr><tr><td align="center" valign="middle" >10</td><td align="center" valign="middle" >0.08</td><td align="center" valign="middle" >1.18</td><td align="center" valign="middle" >−29</td><td align="center" valign="middle" >1</td><td align="center" valign="middle" >0.07</td><td align="center" valign="middle" >1.09</td><td align="center" valign="middle" >7.15</td><td align="center" valign="middle" >−0.02</td><td align="center" valign="middle" >1.07</td><td align="center" valign="middle" >−0.001</td><td align="center" valign="middle" >1.10</td><td align="center" valign="middle" >9.1</td><td align="center" valign="middle" >7.8</td><td align="center" valign="middle" >0.67</td></tr></tbody></table></table-wrap><table-wrap id="table5" ><label><xref ref-type="table" rid="table5">Table 5</xref></label><caption><title> Values of the models’ parameters applied to drying kinetics of lateritic soil bricks activated with NaOH solutions</title></caption><table><tbody><thead><tr><th align="center" valign="middle" ></th><th align="center" valign="middle"  colspan="2"  >Page-Avrami</th><th align="center" valign="middle"  colspan="3"  >Diffusion</th><th align="center" valign="middle"  colspan="3"  >Yong</th><th align="center" valign="middle"  colspan="4"  >Khazaei</th><th align="center" valign="middle"  colspan="2"  >Peleg</th></tr></thead><tr><td align="center" valign="middle" >NaOH (%)</td><td align="center" valign="middle" >k</td><td align="center" valign="middle" >n</td><td align="center" valign="middle" >a</td><td align="center" valign="middle" >b</td><td align="center" valign="middle" >k</td><td align="center" valign="middle" >c</td><td align="center" valign="middle" >T</td><td align="center" valign="middle" >u</td><td align="center" valign="middle" >a</td><td align="center" valign="middle" >b</td><td align="center" valign="middle" >n</td><td align="center" valign="middle" >T</td><td align="center" valign="middle" >a</td><td align="center" valign="middle" >b</td></tr><tr><td align="center" valign="middle" >0</td><td align="center" valign="middle" >0.39</td><td align="center" valign="middle" >0.76</td><td align="center" valign="middle" >0.7</td><td align="center" valign="middle" >8.3</td><td align="center" valign="middle" >0.19</td><td align="center" valign="middle" >0.78</td><td align="center" valign="middle" >5.30</td><td align="center" valign="middle" >0.04</td><td align="center" valign="middle" >1.1</td><td align="center" valign="middle" >−0.003</td><td align="center" valign="middle" >0.67</td><td align="center" valign="middle" >4.7</td><td align="center" valign="middle" >2.7</td><td align="center" valign="middle" >0.87</td></tr><tr><td align="center" valign="middle" >1.5</td><td align="center" valign="middle" >0.25</td><td align="center" valign="middle" >0.84</td><td align="center" valign="middle" >0.8</td><td align="center" valign="middle" >5.4</td><td align="center" valign="middle" >0.16</td><td align="center" valign="middle" >0.87</td><td align="center" valign="middle" >6.00</td><td align="center" valign="middle" >0.03</td><td align="center" valign="middle" >1.0</td><td align="center" valign="middle" >0.000</td><td align="center" valign="middle" >0.80</td><td align="center" valign="middle" >4.9</td><td align="center" valign="middle" >3.5</td><td align="center" valign="middle" >0.84</td></tr><tr><td align="center" valign="middle" >2.5</td><td align="center" valign="middle" >0.22</td><td align="center" valign="middle" >0.88</td><td align="center" valign="middle" >0.9</td><td align="center" valign="middle" >7</td><td align="center" valign="middle" >0.14</td><td align="center" valign="middle" >0.91</td><td align="center" valign="middle" >6.76</td><td align="center" valign="middle" >0.02</td><td align="center" valign="middle" >1.1</td><td align="center" valign="middle" >−0.002</td><td align="center" valign="middle" >0.80</td><td align="center" valign="middle" >6.9</td><td align="center" valign="middle" >4.4</td><td align="center" valign="middle" >0.80</td></tr><tr><td align="center" valign="middle" >5</td><td align="center" valign="middle" >0.14</td><td align="center" valign="middle" >1.00</td><td align="center" valign="middle" >−0.1</td><td align="center" valign="middle" >54</td><td align="center" valign="middle" >0.01</td><td align="center" valign="middle" >0.98</td><td align="center" valign="middle" >7.35</td><td align="center" valign="middle" >0.01</td><td align="center" valign="middle" >1.4</td><td align="center" valign="middle" >−0.007</td><td align="center" valign="middle" >0.87</td><td align="center" valign="middle" >10.9</td><td align="center" valign="middle" >5</td><td align="center" valign="middle" >0.79</td></tr><tr><td align="center" valign="middle" >7.5</td><td align="center" valign="middle" >0.09</td><td align="center" valign="middle" >1.14</td><td align="center" valign="middle" >−14</td><td align="center" valign="middle" >1.1</td><td align="center" valign="middle" >0.07</td><td align="center" valign="middle" >1.06</td><td align="center" valign="middle" >7.78</td><td align="center" valign="middle" >−0.01</td><td align="center" valign="middle" >1.1</td><td align="center" valign="middle" >−0.001</td><td align="center" valign="middle" >1.04</td><td align="center" valign="middle" >9.7</td><td align="center" valign="middle" >5.9</td><td align="center" valign="middle" >0.76</td></tr><tr><td align="center" valign="middle" >10</td><td align="center" valign="middle" >0.05</td><td align="center" valign="middle" >1.28</td><td align="center" valign="middle" >−29</td><td align="center" valign="middle" >1.1</td><td align="center" valign="middle" >0.05</td><td align="center" valign="middle" >1.12</td><td align="center" valign="middle" >8.42</td><td align="center" valign="middle" >−0.03</td><td align="center" valign="middle" >1.0</td><td align="center" valign="middle" >0.003</td><td align="center" valign="middle" >1.19</td><td align="center" valign="middle" >10.7</td><td align="center" valign="middle" >7.8</td><td align="center" valign="middle" >0.67</td></tr></tbody></table></table-wrap><p>The values of the parameter k of the Page-Avrami model, those of 1/T of the Khazaei’s model, and the inverse of the parameter a of the Peleg’s model decrease when the NaOH content increases. This result is consistent with the fact that the first two parameters are directly related to the time after which 63.2% of water is evaporated, and the third with the initial drying speed.</p><p>The values of the parameter K of the diffusion model obtained here are larger than those obtained earlier [<xref ref-type="bibr" rid="scirp.93815-ref18">18</xref>] because the drying durations measured here are shorter than the previous ones.</p></sec></sec><sec id="s4"><title>4. Conclusions</title><p>The objective of this work was to study the effect of NaOH activation on the drying kinetics of earthen bricks and to test five parametric models on this kinetics.</p><p>The results obtained show that:</p><p>1) There is not a drying rate constant phase during the drying, and therefore the drying kinetics is governed mainly by the diffusion of water from the interior to the surface of the brick. The drying duration increases almost linearly with the NaOH content. It varies from about 23 days for non-activated bricks to 28 days for activated bricks with a 10% NaOH solution. This increase could be explained by the formation of the zeolite structure that reduces the soil porosity, the NaOH-H<sub>2</sub>O affinity, and the NaOH-CO<sub>2</sub> reaction;</p><p>2) NaOH activation reduces the volumetric shrinkage rate of bricks for the soils studied. It varies from about 5% for non-activated bricks to about 3% for the activated bricks with 10% NaOH solution. The reduction of the porosity due to the formation of a zeolitic structure could explain this shrinkage decrease. Manufactured bricks did not show visible cracks;</p><p>3) The coefficients of determination of the five models range from 0.993 to 0.999. The Kazaei’s model is the best of all. The parameter n of Avrami-Page and Khazaei models is about equal to 1, in accordance with the absence of free water in the bricks. This parameter increases slightly with the NaOH content. The evolution of the parameters k of the Page-Avrami and diffusion models, that of the parameters T and a of the Kharzaei and Peleg models, respectively, are in agreement with the variation of the drying duration due to the NaOH content.</p></sec><sec id="s5"><title>Conflicts of Interest</title><p>The authors declare no conflicts of interest regarding the publication of this paper.</p></sec><sec id="s6"><title>Cite this paper</title><p>Bouyila, S., Elenga, R.G., Ahouet, L., Ngoulou, M. and Konda, S. (2019) NaOH Activation of Raw Soils: Effect of NaOH Content on the Drying Kinetic and Its Modelling. Geomaterials, 9, 55-66. https://doi.org/10.4236/gm.2019.92005</p></sec></body><back><ref-list><title>References</title><ref id="scirp.93815-ref1"><label>1</label><mixed-citation publication-type="other" xlink:type="simple">UN-Habitat (2008) The State of African Cities: A Framework for Addressing Urban Challenges in Africa. United Nations Human Settlements Programme (UN-HABITAT).</mixed-citation></ref><ref id="scirp.93815-ref2"><label>2</label><mixed-citation publication-type="other" xlink:type="simple">Van Damme, H. and Houben, H. (2017) Earth Concrete. Stabilization Revisited. Cement and Concrete Research, 114, 90-102.  
https://doi.org/10.1016/j.cemconres.2017.02.035</mixed-citation></ref><ref id="scirp.93815-ref3"><label>3</label><mixed-citation publication-type="other" xlink:type="simple">Delgado, M.C.J. and Guerrero, I.C. (2007) The Selection of Soils for Unstabilised Earth Building: A Normative Review. Construction and Building Materials, 21, 237-251. https://doi.org/10.1016/j.conbuildmat.2005.08.006</mixed-citation></ref><ref id="scirp.93815-ref4"><label>4</label><mixed-citation publication-type="other" xlink:type="simple">Millogo, Y., Hajjaji, M. and Ouedraogo, R. (2008) Microstructure and Physical Properties of Lime-Clayey Adobe Bricks. Construction and Building Materials, 22, 2386-2392. https://doi.org/10.1016/j.conbuildmat.2007.09.002</mixed-citation></ref><ref id="scirp.93815-ref5"><label>5</label><mixed-citation publication-type="other" xlink:type="simple">Elenga, R.G., Mabiala, B., Ahouet, L., Goma-Maniongui, J. and Dirras, G.F. (2011) Characterization of Clayey Soils from Congo and Physical Properties of Their Compressed Earth Blocks Reinforced with Post-Consumer Plastic Wastes. Geomaterials, 1, 88-94. https://doi.org/10.4236/gm.2011.13013</mixed-citation></ref><ref id="scirp.93815-ref6"><label>6</label><mixed-citation publication-type="other" xlink:type="simple">Bahar, R., Benazzoug, M. and Kenai, S. (2004) Performance of Compacted Cement-Stabilised Soil. Cement &amp; Concrete Composites, 26, 811-820.  
https://doi.org/10.1016/j.cemconcomp.2004.01.003</mixed-citation></ref><ref id="scirp.93815-ref7"><label>7</label><mixed-citation publication-type="other" xlink:type="simple">Yetgin, S., Cavdar, O. and Cavdar, A. (2008) The Effects of the Fiber Contents on the Mechanic Properties of the Adobes. Construction and Building Materials, 22, 222-227. https://doi.org/10.1016/j.conbuildmat.2006.08.022</mixed-citation></ref><ref id="scirp.93815-ref8"><label>8</label><mixed-citation publication-type="other" xlink:type="simple">Hejazi, S.M., Sheikhzadeh, M., Abtahi, S.M. and Zadhoush, A. (2012) A Simple Review of Soil Reinforcement by Using Natural and Synthetic Fibers. Construction and Building Materials, 30, 100-116.  
https://doi.org/10.1016/j.conbuildmat.2011.11.045</mixed-citation></ref><ref id="scirp.93815-ref9"><label>9</label><mixed-citation publication-type="other" xlink:type="simple">Li, Y., et al. (2017) A Unified Expression for Grain Size Distribution of Soils. Geoderma, 288, 105-119. https://doi.org/10.1016/j.geoderma.2016.11.011</mixed-citation></ref><ref id="scirp.93815-ref10"><label>10</label><mixed-citation publication-type="other" xlink:type="simple">Elenga, R.G., Dirras, G.F., Goma Maniongui, J. and Mabiala, B. (2011) Drying of Raffia Fiber. BioRessources, 6, 4135-4144.</mixed-citation></ref><ref id="scirp.93815-ref11"><label>11</label><mixed-citation publication-type="other" xlink:type="simple">Peleg, M. (1988) An Empirical Model for Description of Moisture Sorption Curves. Journal of Food Science, 53, 1216-1217.  
https://doi.org/10.1111/j.1365-2621.1988.tb13565.x</mixed-citation></ref><ref id="scirp.93815-ref12"><label>12</label><mixed-citation publication-type="other" xlink:type="simple">Elenga, R.G., Massamba, D., Niéré, R.R., Goma Maniongui, J. and Dirras, G.F. (2013) Convective and Microwave Dryings of Raffia Fruit: Modeling and Effects on Color and Hardness. Research Journal of Applied Sciences, Engineering and Technology, 6, 2715-2723. https://doi.org/10.19026/rjaset.6.3776</mixed-citation></ref><ref id="scirp.93815-ref13"><label>13</label><mixed-citation publication-type="other" xlink:type="simple">Khazaei, J. and Daneshmandi, S. (2007) Modeling of Thin-Layer Drying Kinetics of Sesame Seeds: Mathematical and Neural Networks Modeling. International Agrophysics, 21, 335-348.</mixed-citation></ref><ref id="scirp.93815-ref14"><label>14</label><mixed-citation publication-type="other" xlink:type="simple">Crank, J. (1975) The Mathematics of Diffusion. Oxford University Press, Oxford.</mixed-citation></ref><ref id="scirp.93815-ref15"><label>15</label><mixed-citation publication-type="other" xlink:type="simple">Erbay, Z. and Icier, F. (2009) A Review of Thin Layer Drying of Foods: Theory, Modeling and Experimental Results. Critical Reviews in Food Science and Nutrition, 505, 441-464. https://doi.org/10.1080/10408390802437063</mixed-citation></ref><ref id="scirp.93815-ref16"><label>16</label><mixed-citation publication-type="other" xlink:type="simple">Avrami, M. (1940) Kinetics of Phase Change. II Transformation-Time Relations for Random Distribution of Nuclei. The Journal of Chemical Physics, 8, 212-224.  
https://doi.org/10.1063/1.1750631</mixed-citation></ref><ref id="scirp.93815-ref17"><label>17</label><mixed-citation publication-type="other" xlink:type="simple">Pauwels, J.M., Van Rants, E. and Verloom, M.A. (1992) Mannuel de laboratoire de pédologie Méthode d’analyse des sols et plantes; équipements, gestion des stocks, de verrerie et de produits chimiques. Place du champ de Mars 5, 1050 Bruxelles, Royaume de Belgique, 33-34.</mixed-citation></ref><ref id="scirp.93815-ref18"><label>18</label><mixed-citation publication-type="other" xlink:type="simple">NF P94-093 (1999) Soils: Investigations and Testing—Determination of Compaction Characteristics of Soil—Standard Proctor Test—Modified Proctor Test. Association Francaise de Normalisation (AFNOR), Paris. http://www.afnor.fr</mixed-citation></ref><ref id="scirp.93815-ref19"><label>19</label><mixed-citation publication-type="other" xlink:type="simple">NF P94-051 (1993) Soils: Investigation and Testing—Determination of Atterberg Limits—Liquid Limit Test Using Casagrande Apparatus—Plastic Limit Test on Rolled Thread. Association Francaise de Normalisation (AFNOR), Paris.  
http://www.afnor.fr</mixed-citation></ref><ref id="scirp.93815-ref20"><label>20</label><mixed-citation publication-type="other" xlink:type="simple">NF P94-057 (1992) Analyse granulometrique des sols. Methode par sedimentation. Association Francaise de Normalisation (AFNOR), Paris. http://www.afnor.fr</mixed-citation></ref><ref id="scirp.93815-ref21"><label>21</label><mixed-citation publication-type="other" xlink:type="simple">NF P94-056 (1996) Soil: Investigation and Testing—Granulometric Analysis—Dry Sieving Method Washing. Association Francaise de Normalisation (AFNOR), Paris.  
http://www.afnor.fr</mixed-citation></ref><ref id="scirp.93815-ref22"><label>22</label><mixed-citation publication-type="other" xlink:type="simple">Ngoulou, M., Elenga, R.G., Ahouet, L., Bouyila, S. and Konda, S. (2019) Modeling the Drying Kinetics of Earth Bricks Stabilized with Cassava Flour Gel and Amylopectin. Geomaterials, 9, 40-53. https://doi.org/10.4236/gm.2019.91004</mixed-citation></ref><ref id="scirp.93815-ref23"><label>23</label><mixed-citation publication-type="other" xlink:type="simple">Diop, M.B. and Michael, G.W. (2008) Sodium Silicate Activated Clay Brick. Bulletin of Engineering Geology and the Environment, 67, 499-505.  
https://doi.org/10.1007/s10064-008-0160-3</mixed-citation></ref><ref id="scirp.93815-ref24"><label>24</label><mixed-citation publication-type="other" xlink:type="simple">Kim, B., Yi, C. and Kang, K. (2014) Development of Alkali-Activated Binder Using Hwangtoh without Calcination. Construction and Building Materials, 58, 206-213.  
https://doi.org/10.1016/j.conbuildmat.2014.02.003</mixed-citation></ref><ref id="scirp.93815-ref25"><label>25</label><mixed-citation publication-type="other" xlink:type="simple">Rattanasak, U. and Chindaprasirt, P. (2009) Influence of NaOH Solution on the Synthesis of Fly Ash Geopolymer. Mineral Engineering, 22, 1073-1078.  
https://doi.org/10.1016/j.mineng.2009.03.022</mixed-citation></ref><ref id="scirp.93815-ref26"><label>26</label><mixed-citation publication-type="other" xlink:type="simple">Panagiotopoulou, Ch., Kontori, E., Perraki, Th. and Kakali, G. (2007) Dissolution of Aluminosilicate Minerals and By-Products in Alkaline Media. Journal of Materials Science, 42, 2967-2973. https://doi.org/10.1007/s10853-006-0531-8</mixed-citation></ref><ref id="scirp.93815-ref27"><label>27</label><mixed-citation publication-type="book" xlink:type="simple">Provis, J.L. (2009) Activating Solutions for Geopolymers. In: Provis, J.L. and Van Deventer, J.S.J., Eds., Geopolymers: Structure, Processing and Properties and Industrial Applications, Woodhead Publishing Limited, Cambridge, 50-71.  
https://doi.org/10.1533/9781845696382.2.294</mixed-citation></ref><ref id="scirp.93815-ref28"><label>28</label><mixed-citation publication-type="book" xlink:type="simple">Mackenzie, K.J.D. (2009) Utilisation of Non-Thermally Activated Clays in the Production of Geopolymers. In: Provis, J.L. and Van Deventer, J.S.J., Eds., Geopolymers: Structure, Processing and Properties and Industrial Applications, Woodhead Publishing Limited, Cambridge, 294-314.  
https://doi.org/10.1533/9781845696382.2.294</mixed-citation></ref><ref id="scirp.93815-ref29"><label>29</label><mixed-citation publication-type="other" xlink:type="simple">Somna, K., Jaturapitakkul, C., Kajitvichyanukul, P. and Chindaprasirt, P. (2011) NaOH-Activated Ground Fly Ash Geopolymer Cured at Ambient Temperature. Fuel, 90, 2118-2124. https://doi.org/10.1016/j.fuel.2011.01.018</mixed-citation></ref><ref id="scirp.93815-ref30"><label>30</label><mixed-citation publication-type="other" xlink:type="simple">MacKenzie, K.J.D., Brew, D.R.M., Fletcher, R.A. and Vagana, R. (2007) Formation of Aluminosilicate Geopolymers from 1:1 Layer-Lattice Minerals Pre-Treated by Various Methods: A Comparative Study. Journal of Materials Science, 42, 4667-4674. https://doi.org/10.1007/s10853-006-0173-x</mixed-citation></ref><ref id="scirp.93815-ref31"><label>31</label><mixed-citation publication-type="other" xlink:type="simple">Sofia, A., Lima, S.A., Humberto, V.H., Almir, S.A. and Neto, F.V. (2012) Analysis of the Mechanical Properties of Compressed Earth Block Masonry Using the Sugarcane Bagasse Ash. Construction and Building Materials, 35, 829-837.  
https://doi.org/10.1016/j.conbuildmat.2012.04.127</mixed-citation></ref><ref id="scirp.93815-ref32"><label>32</label><mixed-citation publication-type="other" xlink:type="simple">Shon, C.-S., Saylak, D. and Zollinger, D.G. (2009) Potential Use of Stockpiled Circulating Fluidized Bed Combustion Ashes in Manufacturing Compressed Earth Bricks. Construction and Building Materials, 23, 2062-2071.  
https://doi.org/10.1016/j.conbuildmat.2008.08.025</mixed-citation></ref><ref id="scirp.93815-ref33"><label>33</label><mixed-citation publication-type="other" xlink:type="simple">Fernández-Pereira, C., de la Casa, J.A., Gómez-Barea, A., Arroyo, F., Leiva, C. and Luna, Y. (2011) Application of Biomass Gasification Fly Ash for Brick Manufacturing. Fuel, 90, 220-232. https://doi.org/10.1016/j.fuel.2010.07.057</mixed-citation></ref><ref id="scirp.93815-ref34"><label>34</label><mixed-citation publication-type="other" xlink:type="simple">Bell, F.G. (1996) Lime Stabilization of Clay Minerals and Soils Engineering. Geology, 42, 223-237. https://doi.org/10.1016/0013-7952(96)00028-2</mixed-citation></ref><ref id="scirp.93815-ref35"><label>35</label><mixed-citation publication-type="other" xlink:type="simple">Bryan, A.J. (1988) Criteria for the Suitability of Soil for Cement Stabilization. Building and Environment, 23, 309-319.  
https://doi.org/10.1016/0360-1323(88)90037-6</mixed-citation></ref><ref id="scirp.93815-ref36"><label>36</label><mixed-citation publication-type="other" xlink:type="simple">Houben, H. and Guillaud, H. (1994) Earth Construction: A Comprehensive Guide. Intermediate Technology Publications, London.</mixed-citation></ref></ref-list></back></article>