Jalal 2020
Jalal 2020
Review Article
On the Recent Trends in Expansive Soil Stabilization
Using Calcium-Based Stabilizer Materials (CSMs):
A Comprehensive Review
Fazal-E- Jalal ,1,2 Yongfu Xu ,1,2,3 Babak Jamhiri ,1 and Shazim Ali Memon 4
          1
            State Key Laboratory of Ocean Engineering, Shanghai Jiao Tong University, Shanghai 200240, China
          2
            Department of Civil Engineering, Shanghai Jiao Tong University, Shanghai 200240, China
          3
            Wentian College of Hohai University, Ma’anshan 243000, China
          4
            Department of Civil and Environmental Engineering, Nazarbayev University, Nur-Sultan 010000, Kazakhstan
Correspondence should be addressed to Yongfu Xu; yongfuxu@sjtu.edu.cn and Shazim Ali Memon; shazim.memon@nu.edu.kz
Received 15 October 2019; Revised 12 December 2019; Accepted 27 January 2020; Published 9 March 2020
          Copyright © 2020 Fazal-E- Jalal et al. This is an open access article distributed under the Creative Commons Attribution License,
          which permits unrestricted use, distribution, and reproduction in any medium, provided the original work is properly cited.
          Calcium-based stabilizer materials (CSMs) exhibit pozzolanic properties which improve the properties of clayey soils by hy-
          dration, cation exchange, flocculation, pozzolanic reaction, and carbonation. In this comprehensive review, comprising over past
          three decades from 1990 to 2019, a mechanistic literature of expansive soil stabilization by incorporating CSMs is presented by
          reviewing 183 published research articles. The advantages and disadvantages of CSMs as the ground stabilizing agent are
          succinctly presented, and the major outcomes of physicochemical effects on soil properties are discussed in detail. After blending
          with CSM, the main and interaction effects on soil properties with focus on chemical processes such as X-ray fluorescence, X-ray
          diffraction analyses, and microstructure interaction by using scanning electron microscopy and thermogravimetric analysis have
          been reviewed in light of findings of past researchers. This work will help geotechnical engineers to opt for suitable CSM in the field
          of geoenvironmental engineering in committing to sustainable construction of civil engineering structures over expansive soils.
discussions on techniques and challenges in soil modi-              the particle face is known as “particle edge.” Diffuse double
fication. According to Godenzoni [13], the cementing                 layers are produced around particle faces with the attached
materials (CMs) are produced by the most conventional               water called “double-layer water.” The water other than
stabilizing materials, that is, lime, cement, and their mixes       the diffuse double layers is shown by the “equilibrium
along with other pozzolanic materials. Today, a detailed            solution.”
literature is available, and a worldwide research on ex-                The role of diffused double layer theory comes into play
pansive soil stabilization using a wide array of classical          while evaluating the expansivity of clay minerals. Accord-
and emergent materials is still in progress [14–22]. Al-            ingly, the repulsive and attractive forces generated by
though well-documented studies on the use of numerous               physicochemical effects are quantified on the particle scale
stabilizers are available, to these authors’, knowledge, no         level [26]. This theory is applicable to smectite particles
study made between 1990 and 2019 that explains the main             present in monovalent electrolytes with lesser concentration.
and interaction effects of CSMs on the expansive soils, has          The thickness of the double layer is shown in the following
been found. Also, the standardization for various addi-             “Poisson–Boltzmann equation”:
tives is unavailable in the field of geotechnical engineering
                                                                                                ��������
which leads to geoenvironmental issues and affects the                                     1        Dk T
environment. This comprehensive review serves three                                         �               ,                  (1)
                                                                                          K      8πη0 ε2 V2
main objectives on the following subjects: (1) gain insights
about the history, mechanism, damages associated, and
prevalence of expansive soils over last 30 years, (2) review        where 1/K � DL, i.e., thickness of double layer (cm),
the practice of efficacious stabilization using Ca-based              D � dielectric constant, k � Boltzmann constant � 1.38 ∗
stabilizer materials for civil engineering structures and           10− 23 J/K, η0 � bulk solution of the electrolyte concentration
road pavements, and (3) serve a guideline for researchers           (ions/cm3), ε � unit electronic charge (esu), T � absolute
and practitioners to select materials under the domain of           temperature (K), and v � cation valence. Note that DL is
this study.                                                         directly proportional to the cation exchange capacity (CEC)
                                                                    and specific surface area (SSA) of clay minerals and has
2. Fundamental Knowledge about                                      pronounced effect on these entities [27–29].
   Stabilization of Expansive Soils                                     The clay minerals belong to “phyllosilicates” family
                                                                    and carry a net residual negative charge. The mechanism
2.1. Mechanism. Improvement in properties of an ex-                 of clay modification by calcium-rich stabilizers involves
pansive or problematic soil means increase in the com-              dissociation of higher calcium content into calcium ions
pressive strength and permeability, reduction in plasticity         that react with both silica and alumina leading to the ion
and compressibility, and improvement in durability of               exchange, flocculation, and pozzolanic reactions. This
these soils. More concisely, “soil stabilization” is mainly         process is expressed in equations (2)–(5). Also, the Cal-
the addition of chemical admixtures to soil which results           ifornia bearing ratio (CBR) is increased, and the forma-
in chemical improvement [23]. Swelling in expansive soils           tion of two main components takes place, calcium silicate
deals mainly with prevalence of type and amount of pore             hydrates (C-S-H) gel, represented by chemical formula
spaces and their interaction with water. The phenomenon             [5Ca2SiO4: 6H2O], and calcium aluminate hydrate (C-A-
of swelling may comprise over a relatively long time                H) gel, with chemical formula [Ca5Si5Al (OH)O17·5H2O].
ranging between 5 to 8 years during early service life of           As shown in equations (4) and (5), it is due to this
foundations and pavements [24]. Figure 1 illustrates the            pozzolanic reaction that soil durability is largely improved
pore spaces between the unit layers of clays, also known as         [30]. It is also notable that, in some cases, calcium alu-
interlayer space, which represent the “microporosity,”              minate silicate hydrate (C-A-S-H) may form which also
whereas pore spaces between adjacent particles or ag-               adds to the soil strength. The pozzolanic reactions occur in
gregates, called the interparticle pores or interaggregate          a highly alkaline environment gradually dissolving the
pore spaces, respectively, represent the “macroporosity”            aluminosilicates which also contributes to the long-term
in the compacted smectite particles. The water present in           strength gain [31]. The presence of clay mineral type and
both these regions differ in terms of their physical states.         calcium (Ca2+) ions governs the effectiveness of these
Swelling takes place when the water enters into the in-             reactions. The volumetric stability of the soil matrix is
terlayers. Petry and Little [10] outlined the empirical             enhanced as Ca2+ tends to replace monovalent Na+ or H+
methods to determine the volume change resulted from                ions. Production of C-S-H and C-A-H gels in this way is
swelling in expansive soils.                                        called “polymerization process” [32, 33]:
    Figure 2 depicts the process of water entry inside clay
plates at extended microlevel. The “clay particle” represents                                280 cal/g ⟶ CaO
                                                                                CaO + H2 O �������������������→ Ca(OH)2        (2)
an interconnected stack of clay layers with a maximum
four layers of crystalline water. The “clay aggregates” are                        Ca(OH)2 ⟶ Ca2+ + 2(OH)−                     (3)
the assembly of “clay particles” forming unit of a compacted
clay double structure. The portion of the clay particle              Ca2+ + 2(OH)− + SiO2 ⟶ C − S − H                          (4)
surface parallel to that of “clay layers” is called the “particle
face.” However, the part of the clay particle surface normal to     Ca2+ + 2(OH)− + Al2 O3 ⟶ C − A − H                         (5)
Advances in Materials Science and Engineering                                                                                             3
Basal spacing
                                          Unit layer
                                                                                                           Macroporosity
                                                                                    Macroporosity
                                                                                 between the particles between the aggregates
Figure 1: Effect of water entry on micro- and macroplates of compacted smectite with classification of “microporosity” and “macro-
porosity,” reproduced with permission from [12].
                    Equlibrium
                     solution
                                                                                                                   Particle face
                                                                                                   Particle edge
                                           Macro voids, filled with air     Double-layer water
                                           at higher matric suctions
Figure 2: Compacted clay structure depicting the process of water entry inside clay plates at the extended microlevel, adapted from [25].
2.2. Identification and Characterization. It is essential to                  limits contribute very least statistical significance to esti-
quantify the amount of swell pressure (Ps) exerted by                        mation of Ps as evidenced by conducting tests on 38
expansive soil upon water uptake. Expansive soils below the                  samples obtained from database of material parameters.
ground surface level extending to a depth of approximately                   “Free Swell Index” (FSI), a measure of FS, is the increase in
1.5 meters are more susceptible to swelling pressure in the                  soil volume without any external constraints when sub-
particular zone called “active zone depth.” However, the                     merged in water. “Ps” is defined as the pressure exerted by
region beyond the active zone depth is termed as “zone of                    clay when it absorbs water in a confined space. “Activity”
constant volume” experiencing lesser volume change with                      (A), the ratio of plasticity index (PI) to the percent of clay
moisture entry [28]. The susceptibility of such soils to                     fraction, represents the water holding capacity of clay soil
volumetric swelling makes them highly unsuitable for use                     and is function of type and amount of clay mineral. Activity
in supporting foundations. Shi et al. [29] presented the                     of Mt (commonly greater than 4) is highest than for ka-
common methods to evaluate the swell intensity, i.e., free                   olinite and illite. The FS and Ps [28, 36] are calculated using
swell (FS) [34] and Ps, which were determined using simple                   oedometer in accordance with ASTM standards [37].
tests such as Atterberg limits (liquid limit (LL), plastic limit             Moreover, to determine the Ps, the zero swell test and
(PL), and shrinkage limit (SL)), contents of colloids, and                   oedometer test methods are preferable because of their ease
activity (A) value of clay. The LL, PL, and SL are index                     and simple procedure [38, 39]. For a variety of expansive
properties used for classification of fine-grained soils and                   soils in Egypt, it was revealed by Mehmood et al. [40] that,
determine the mechanical behavior, i.e., shear strength,                     for highly plastic clays with activity between 0.8 and 1.5, the
compressibility, and swell potential [27]. According to the                  swell potential parameters were calculated using the fol-
experimental study by Cantillo et al. [35], the Atterberg                    lowing equations:
4                                                                               Advances in Materials Science and Engineering
Table 1: Various classification and characterization criteria available in the literature for expansive soils using basic geotechnical tests.
#1 on the basis of swelling [41]
                                                                             Swell pressure
Swell potential           Total expansion                                                                               Degree of expansion
                                                     US customary (tsf )    SI units (kPa)    Metric units (kg/cm2)
0–1.5                        0–10                           <2.05               <196                   <2                 Low
1.5–5                       10–20                         2.05–4.1             196–392                2–4               Medium
5–25                        20–35                          4.1–7.2             392–687                4–7                 High
>25                          >35                            >7.2                >687                   >7              Very high
#2 on the basis of Atterberg limits [42]
Linear shrinkage      Shrinkage index               PI                  LL                     SL                  Expansivity index
0–8%                        <25%                  <18%                 <35%                  <14%                         Low
8–13%                      25–35%                18–25%              35–45%                 12–14%                      Medium
13–18%                     35–50%                25–35%              45–60%                 10–12%                        High
>18%                        >50%                  >35%                 >60%                  <10%                      Very high
#3 on basis of free swell ratio (FSR) [43]
FSR                    Soil expansivity                   Clay type                               Dominant clay mineral
<1                        Negligible                     Nonswelling                                     Kaolinite
1–5                          Low                  Swelling and nonswelling                    Kaolinite and montmorillonite
1.5–2                     Moderate                        Swelling                                   Montmorillonite
2–4                          High                         Swelling                                   Montmorillonite
>4                        Very high                       Swelling                                   Montmorillonite
#4 on the basis of liquid limit (LL)
LL                      Classification
0–20%                      No swell
20–35%                    Low swell
35–50%                  Medium swell
50–70%                    High swell
70–90%                 Very high swell
#5 U.S. Army Waterways Experiment Station (WES 1983)
Classification of potential swell           Swell potential (%)        LL (%)                 PI (%)                Soil suction (kPa)
Low                                                <0.5                 <50                   <25                         <160
Marginal                                         0.5–1.5              50–60                  25–35                      160–430
High                                               >1.5                 >60                   >35                         >430
#6 China Ministry of Construction (CMC 2004) [44]
Standard absorption M.C (%)                       PI (%)                    Free swell value (%)                 Swell potential class
<2.5                                               <15                              <40                              Nonexpansive
2.5–4.8                                           15–28                            40–60                                  Low
4.8–6.8                                           28–40                            60–90                                Medium
>6.8                                               >40                              >90                                   High
                        Table 2: Mineralogical properties of basic clay minerals (kaolinite, illite, and montmorillonite).
                                                         Interlayer bond/    Isomorphous       Shrink-       CEC
Clay mineral                       Structure                                                                                 LL (%)    K (m/s)
                                                             intensity        substitution      swell     (meq/100 g)
                               Alternating sheets
                              of silica tetrahedron
Kaolinite (1 : 1 clay                Alumina
                                                         Hydrogen, strong         Low         Very low        3–15           30–75    10− 5–10− 7
mineral)                             Silica
                                  and alumina
                                octahedral sheets
Illite (2 : 1 clay             Alternating sheets
                                   of alumina
                                                         K-ion, moderate       Moderate          Low         10–40           60–120 10− 6–10− 8
mineral)
                               octahedral sheets
                                     Silica
Ground heave at Al Kod, Oman King Abdul Aziz road, Saudi Arabia
Figure 4: Morphology of cracks in expansive soil (LL � 77.6%, PI � 40.7%, MDD � 1.47 g/cm3, and OMC � 28%) after blending with several
mixtures of calcium carbide residue (CCR) and rice husk (RHA) and cured for 28 days [72].
employ CSM are as follows: (1) the replacement with coarse                      [74]. The stabilizing materials with Ca2+ lower down the Ps
grained materials may be uneconomical because the ex-                           by two mechanisms: (1) by stabilizing the structure of clay
pansive soil layers are extended deep and in irregular pat-                     particles using cation exchange and (2) by increasing the
tern, (2) the presence of Ca2+ ions speeds up the pozzolanic                    concentration of cations held between soil within water and
reactions [63] and tends to decrease the Ps, (3) it is a hot                    thus depleting the double layer thickness [72].
topic and is widely practiced in field nowadays, (4) the
prewetting technique among other takes higher time (several
years) for soils with low hydraulic conductivity [73], and (5)                  4.2. Characteristics of CSM. A large number of CSMs, for
recycling gains environmental and economic benefits by                           instance, lime, cement, fly ash (FA), ground-granulated blast
reducing the usage of natural resources which leads to                          furnace slag (GGBS), bagasse ash (BA), cement kiln dust
development of low-emission and low-energy technologies                         (CKD), rice husk ash (RHA), silica fume [64], steel slag (SS),
Advances in Materials Science and Engineering                                                                                                 7
           Table 3: Summary of oxide composition of traditional Ca-based stabilizer materials (CSMs) from previous studies.
Popular Ca-based stabilizers         CaO (C)       SiO2 (S)      Al2O3 (A)       SO3    Fe2O3   MgO      K2O     TiO2    LOI     Gs    LL (%)
Hydrated lime [84]                     70.9          1.20           0.70          —      0.10   0.50     0.10    0.10    26.1   2.32
Extinct lime [85]                      83.3          2.50           1.50         2.50    2.00   0.50      —       —       —      —        —
Lime [86]                              45.0          12.0           1.20         0.00    0.50   0.70     0.80     —      40.0    —        —
Lime sludge [87]                       48.0          6.50           1.15          —      1.20    —        —       —       —      —        —
Cement [88]                            44.7          27.4           13.1         3.96    3.30   1.19     1.14     —      4.01    —        —
Cement [89]                            65.2          20.4           4.10                 3.20   4.50     0.59     —       —      —        —
Cement [90]                            63.0          20.0           6.00         2.00    3.00    —       1.00     —       —      —        —
CKD [91]                               63.9          11.9           9.90         0.00    3.40   1.70     0.10     —      4.70   2.80
FA [92]                                1.60          54.4           28.6          —      3.20   1.40     1.70    1.80    5.00   2.15     32
FA [93]                                2.40          58.5           27.8         0.03    8.10   0.70     0.01     —      2.10    —       —
FA [94]                                6.70          55.6           26.4          —      3.90   0.60     2.10    1.00    3.68   2.13     46
FA [95]                                1.60          54.4           28.6          —      3.20   1.40     1.70    1.80    5.00   2.15     32
FA [96]                                48.9          19.9           9.30         7.30    5.70   3.70     0.50     —      3.01    —       —
Class C FA [97]                        29.1          31.9           17.5         2.0     5.10    —        —       —      1.00    2.6     NP
Class F FA [98]                        14.3          41.3           16.3         0.70    6.30   4.70     2.60     —      0.10   2.53     NP
GGBS [99]                              34.0          34.3           17.9         1.64    1.00   6.02     0.64     —      2.66    —       —
GGBS [100]                             44.9          29.2           13.8          —      5.50   6.20     1.00    2.10     —     2.84     40
Steel slag [100]                       25.8          16.4           2.40          —      26.0   10.0      —      0.80     —      —       —
BA [91]                                11.7          47.8           10.2          —      5.70   2.80     2.60    0.80    16.1    —       —
BA [95]                                3.20          57.1           29.7         0.02    2.75    —        —      1.13     —      —       —
BA [101]                               4.30          67.8           6.90          —      3.84    —        —       —       —      —       —
Coal waste ash (CWA) [102]             2.30          55.7           23.3          —      3.40   0.90     3.50    1.20    38.7   1.94     —
GSA [93]                               10.9          33.4            6.8         6.40    2.16   4.72     25.4     —       —      —       —
GSA [103]                              15.5          23.9            8.9          5.7     5.2    6.9     22.9    1.02     —      —       —
LOI: loss on ignition; Gs: specific gravity; NP: nonplastic; —, “no available data.”
sewage sludge ash (SSA), palm oil fuel ash (POFA), fuel oil                     5. Effect on Geotechnical Properties with
fly ash (FOFA), groundnut shell ash (GSA) [12, 34, 75–78],                          Emphasis on Chemical Processes and
are employed in geotechnical engineering. Some “nano-
                                                                                   Microstructure Interaction
materials” rich in Ca content [79] also act as CSM, and Sabat
[80] suggested these could be used for strength enhance-                        5.1. Main Effect of Lime Stabilization. Lime stabilization
ment, plasticity reduction, and limiting swell and shrinkage                    improves the geotechnical properties by changing the mi-
strains. Also, the mixture of cement, emulsion, and water                       crostructure and fabric of expansive clays [112] through four
forms evolutive materials such as cold recycled mixtures                        important reactions [113], i.e., (1) cation exchange, (2)
(CRMs), which are responsible for the long-term properties                      flocculation-agglomeration, (3) carbonation, and (4) poz-
in the pavement construction [81–83].                                           zolanic reaction. It is mainly due to the flocculation-ag-
     The different CSMs with chemical compositions deter-                        glomeration reaction that the geotechnical properties of high
mined using X-ray fluorescence (XRF) are listed in Table 3.                      plasticity clay soils are improved. Because of flocculation, the
The widely used CSMs are lime (CaO≈40-50% and 70-80%),                          PI and FSI lower down, whereas compression strength and
cement (≈40-50% and 60-70%), FA (<10% and 30%–50%),                             permeability go up [23, 114–116]. Figure 5 shows that, with
GGBS (≈30–50%), and BA (<5% and 10-20%). The avail-                             lime treatment, the PI reduces by six times the original and
ability of surplus Ca2+ tends to replace the monovalent so-                     transforms from CH to ML showing the efficacy of lime
dium or hydrogen ions rapidly especially in a high pH                           stabilization. The presence of kaolinite, illite, and Mt affects
environment, which gives a higher volumetric stability to                       the final stabilization and highly governs the stabilizer
expansive soils through ion exchange. This leads to the                         characteristics, such as dosage methodology, strength gain,
flocculation reaction, which in turn improves the physical and                   engineering conditions, and curing condition effect [23].
mechanical behavior of the soil and increases the soil strength.                    The period of curing is an important parameter in
     However, calcium carbonate (CaCO3) is produced due                         achieving long-term compressive (qu) and split tensile
to carbonation of lime which is a source of weakness due to                     strength (qt), as the pozzolanic reaction progresses to-
its plastic nature which increases the plasticity of expansive                  wards completion [54, 63, 117]. The strength gain with 4%
soils [23]. Modarres and Nosoudy [87] stated that CaCO3                         lime and curing at 28 days for quartz, kaolinite, and Mt
formation is related to presence of excess lime and the                         were recorded as 330%, 230%, and 130%, respectively, in
unavailability of the reactive SiO2 and Al2O3.                                  contrast to samples with 4% lime and tested after one day
     The advantages and disadvantages of CSMs are briefly                        curing [118]. Increased curing duration is an effective
summarized in Table 4, which serves as a guide to deal with                     approach in reducing the swell potential of expansive soils
CSM stabilization of expansive clays, on-site commercially                      treated with lime. At same water content in the modified
and in the laboratory for research.                                             compaction test, an increase of 133% in UCS is observed
8                                                                                                                             Advances in Materials Science and Engineering
                                                                                        e
                                                                                      in
                                                                    ”l
                                                                                    ”l
                                                                  “U
                            40
                                                                            O
                            30
                                                                                                                      It is important to determine how efficient lime acts when
                                                                                                                 it is used as a potential CSM. The suitability of lime in silica-
                                                                                                                 rich soils, soil containing gypsum, sulfate-rich soils, and
                                                           L
                            20
                                                          O
SEM micrographs
                                     Untreated clayey soil paste                         8% lime-treated clayey soil paste                  20% natural pozzolana and 8% lime-treated
                                          (7 days cured)                                         (7 days cured)                                  clayey soil paste (7 days cured)
Figure 6: Microstructural comparison of clay soil paste cured at 7 days (untreated sample, treated with 8% lime, treated with 20%
pozzolan + 8% lime) (modified after [54]).
                                   3500                                                                                          350
                                                                                                          Cement (million ton)
                                                                                                                                 300
                                   3000                                                                                          250
   Cement production (×106 tons)
                                                                                                                                 200
                                   2500                                                                                          150
                                                                                                                                 100
                                   2000
                                                                                                                                  50
                                                                                                                                   0
                                   1500
                                                                                                                                           Saudi Arabia
                                                                                                                                                   China
                                                                                                                                                    India
                                                                                                                                                       EU
                                                                                                                                                       US
                                                                                                                                                   Brazil
                                                                                                                                            South Korea
                                                                                                                                               Indonesia
                                                                                                                                       Russia Federation
                                                                                                                                                   Japan
Mexico
                                                                                                                                                  France
                                                                                                                                                 Canada
                                                                                                                                               Argentina
                                                                                                                                            South Africa
                                                                                                                                                      UK
                                                                                                                                                  Turkey
                                                                                                                                                Germany
                                                                                                                                                     Italy
                                   1000
500
                                     0                                                                                                             Country
                                      1920       1940        1960               1980   2000      2020
                                                                         Year
                                                                   (a)                                                                            (b)
Figure 7: Global annual cement production: (a) between 1925–2009 [124]; (b) in different countries [125].
somehow restrained since global warming and rapidly                                                                   The effect of cement alone on the geotechnical properties
changing climate are challenging global issues of today’s                                                         and engineering characteristics is reviewed first. Cement
world [22, 123]. Figure 7 indicates the global annual cement                                                      modifies the physical properties of certain waste materials
production between 1925 and 2009 and the cement pro-                                                              (e.g., marble industrial waste and bottom ash) and decreases
duction in various countries with China taking the lead as it                                                     their toxicity level [128–130]. The plasticity and swell indices
plans to construct 40 billion square meters of floor space                                                         lower down, thereby increasing the shear strength param-
until 2036.                                                                                                       eters and permeability characteristics. Based on results from
    Cement stabilization is specifically recommended and                                                           past literature, it is illustrated from Figure 8 that, up to 10%
significantly increases the cohesion, strength, and durability                                                     addition of cement and lime each, both Ps and FS values are
of coarse-graded mixtures having a low PI [126]. Zaimoglu                                                         reduced considerably. The Ps is necessary to evaluate the
[127] refrained the use of cement owing to its high cost and                                                      nature of problem associated with expansive problems. So,
hazardous nature. Cement and lime stabilization are more or                                                       in order to study the effect of stabilizers on Ps, almost all
less identical in yielding results with respect to mechanism of                                                   curves record to follow similar declining trend, from 500 to
modification since the formation of C-S-H and C-A-H takes                                                          700 kPa, for untreated soil to 170 to 300 kPa, for both lime
place in both cases which form cementitious links with the                                                        and cement (10% dosage each), with the least amount of
untreated clay particles. Lime and cement have their own                                                          variance between lime and cement [71]. The significant
benefits and ill effects regarding the viewpoint of stabilizing                                                     reduction in maximum Ps is observed in the data of
materials.                                                                                                        Vijayvergiya and Ghazzallay in contrast to almost identical
10                                                                                                                                                        Advances in Materials Science and Engineering
800 35
700 30
                            600
                                                                                                                                        25
                            500
     Swell pressure (kPa)
20
                              0                                                                                                          0
                                  0              2              4                  6            8                 10                         0              2              4                  6            8                 10
                                                               Stabilizer content (%)                                                                                     Stabilizer content (%)
                    –100                                                                                                                –5
Figure 8: Main effect of both cement and lime on the plot of swelling pressure and free swell, from past literature.
values reported by Turkoz and Tuson [131], when consid-                                                                           cement alone treatment [116]. The PI decreases by 60%, and
ering the initial and final Ps values on each curve. On the                                                                        the Ps drops by 82% when (5% lime + 3% cement) blend is
contrary, the treatment of lime and cement within range of 2                                                                      used to modify medium expansive soil extracted from depth
to 10% dosage level indicates that FS curves experience wide                                                                      [71]. The Ps value is recorded to decrease from 249 kPa for
variance. The trend shown by Komornik and David is most                                                                           untreated soil to 45 kPa for (5% lime + 3% cement) blend.
significant, witnessing almost 6 times reduction among                                                                             Their combined effect on geotechnical properties is also
untreated and highest dosage values, in contrast to results                                                                       summarized succinctly in Table 5.
obtained by Turkoz and Tuson which changes from 20% to                                                                                 Recently, it is found that recycled cement can be yielded
merely 15%. Moreover, the remaining three curves for lime                                                                         by burning old OPC pastes at elevated temperatures of 450°C
and cement are seen to follow a similar trend which illus-                                                                        (RC-450), which will lower down the CO2 emission by 94%,
trates an intermediate effect on the reduction of FS values.                                                                       attaining an equivalent strength of OPC. It is obvious from
Lastly, it can be seen in Figure 8 that the stabilization                                                                         surface morphology studies by SEM that CO2 is reduced by
mechanism of lime and cement for each specified treatment                                                                          (1) formation of calcium carboaluminate and (2) C-S-H gels
resembles each other, with cement proving to be more ef-                                                                          containing calcite, as both are evidenced in the SEM mi-
fective in terms of minimizing the swell. Note that, by using                                                                     crographs in Figures 9(a) and 9(b), and in the EDX analyses
9% lime alone, the Ps becomes zero and the effect on                                                                               in Figures 9(c) and 9(d), respectively. In the plots between
plasticity value is almost the same as recorded for the case of                                                                   energy on abscissa and counts on ordinate, the peaks for only
lime-cement mix [132].                                                                                                            calcite, silica, and alumina are shown with almost no traces
    The CKD is fine-grained powder-like dust material                                                                              of other problematic clay minerals [94, 144]. Figures 9(a)
obtained as a by-product from the manufacturing of cement                                                                         and 9(b) also reveal the formation of portlandite and
[133]. It contains traces of reactive CaO and alkaline                                                                            ettringite with a honey-combed structure in the micrograph
compounds and is therefore highly fine to be used as the                                                                           of OPC being transformed into a denser structure with
effective soil stabilizing agent. However, the properties of                                                                       newly formed carboaluminate at 4 μm magnification level. It
CKD largely differ depending upon the manufacturing plant,                                                                         is therefore to say that RC-450 (1) is richer in calcium
cement kiln type, and the characteristics of raw materials                                                                        carbonate amount, (2) has densely arranged nanoparticles,
employed in cement production [12, 134, 135]. Its pro-                                                                            and (3) has no portlandite content. Kolias et al. [99] de-
duction is estimated to be approximately 30 million tons per                                                                      lineated that tobermorite formation leads to a denser and
year, across the globe, of which 80% causes an environ-                                                                           stable soil structure.
mental threat and is not safely disposed [97]. Many re-                                                                                The thermogravimetric analysis (TGA) measures change
searchers have suggested its use as potential stabilizer for                                                                      in mass of a material as a function of either temperature or
clayey soils. The (volcanic ash + 20% CKD) stabilizer mix                                                                         time and is capable to quantify phase compositions in
will yield a significant improvement in mechanical prop-                                                                           ettringite, portlandite, gehlenite, and calcite [145]. The re-
erties [136] and pronounced increase in CBR values (above                                                                         sults of TGA in Figure 9(e) show that CO2 fixation (that is to
80%); therefore, Yu et al. [91] found it suitable for the                                                                         combat the challenge of global warming [146]) in case of RC-
construction of economical building units and small-scale                                                                         450 is low (75%) in contrast with that of a higher value for
roadways.                                                                                                                         OPC (87%) at same temperature. The trend of reducing
    In terms of the final stabilization effects, the interaction                                                                    weight loss with temperature thus signals a low CO2 fixation
effect of cement with lime is more efficacious than lime or                                                                          value for RC-450. This shows the significant effect of recycled
Advances in Materials Science and Engineering                                                                                               11
     Table 5: A succinct list of research conducted on Ca-based stabilizer materials for different expansive soils across the world.
                                   Expansive soil properties                                    Stabilizer
Location of
                             LL PL PI                        MDD OMC                                    Optimum          Properties improved
expansive soil        Gs                 Activity USCS                                  Type
                            (%) (%) (%)                    (kN/m3) (%)                                    amount
                                                                                                      5% L + 3% C.
                                                                                                     Other studies:
                                                                                                      2% L + 1% C
                                                                                                            [94]
                                                                                      Lime (L),                           Ps↓ � 249 to 45 kPa
Oman, Al-                                                                                           4% L + 30% red
                     2.80   50   29.5 20.5      1.03      MH        17.5       21   cement (C),                               PI↓ � 20 to 8%
Khoud [71]                                                                                              mud [137]
                                                                                   pozzolan (P)                               Ps↓ � by 840%
                                                                                                      8% L + 4% C
                                                                                                             [71]
                                                                                                      8% L + 20% P
                                                                                                            [84]
                                                                                    Fly ash (F),
                                                                                                                          LL↓, PI↓, PL↑ UCS
China, Hefei,                                                                         sand (S),        10% F + 8%
                     2.71 42.8    22    20.8     —        MH        17.3     18.9                                     ↑ � 345 to 900 kPa (with
Anhui [138]                                                                         basalt fiber         S + 0.4% B
                                                                                                                             0.4% Ba fibers)
                                                                                         (B)
                                                                                   Lime (L) and 5, 10, 15, and
USA, Idabel,                                                                                                           Shrinkage↓ � maximum
                      —     79    25     54     1.30      CH         —         —     Class C fly          20% [54]
Oklahoma [121]                                                                                                                 at 20% lime
                                                                                     ash (CFA) L and CFA each
India, Calcutta                                                                                     20% mixture of UCS↑ � 270 to 450 kPa
                                                                                    Fly ash (F)
(80% BC + 20%                                                                                        F and G [121]          (28 days curing)
                     2.66   78    45     33       3       CH         —         —     and GGBS
Na-bentonite)                                                                                            (F:G 70 :           Addition of 1%
                                                                                         (G)
[95]                                                                                                    30) + 1% L      Lime: 270 to 875 kPa
                                                                                                    25% B (modest
                                                                                    Bagasse ash          effect on          MDD↓, swelling↓
Australia,
                2.65        86    37     49     1.66      CH       12.65     36.5 (B) and lime           strength)    UCS↑ (0–25% BA + lime
Queensland [68]
                                                                                          (L)        10%B + 10% L                  mix)
                                                                                                            [95]
                                                                                                          4-6 % B
                                                                                    Bagasse ash                           B: swelling↓, UCS↑
                                                                                                    8–10% M [140]
Pakistan, Kohat                                                                        (B) and                            till 5% B, MDD5%↑
                     2.71   43    41     22      0.6       CL       18.1     14.9                   Combined effect:
city, KPK [139]                                                                     marble dust                          M: swelling↓, UCS↑
                                                                                                    8% B + 16% lime
                                                                                      (M) [68]                          At 10% M, MDD4%↑
                                                                                                       sludge [139]
                                                                                                                      UCS↑ (strength of cured
India, Dadri
                                                                                                                           sample > uncured
(100%                                                                              Dadri fly ash 10–15% [141]
                 2.71 412         60    352      3.5      CH        12.6      41.0                                               samples)
bentonite) Dadri                                                                   and lime (L)        (with 3% L)
                                                                                                                      Ps � ↓(as F and L content
[96]
                                                                                                                                increases)
                                                                                                                      Models developed which
                                                                                    Ps versus ω,
China, Guangxi                                                                                                        needs to be validated due
               2.73         77    34     43      —        CH        17.2       —        MDD                   —
province [14]                                                                                                          to lack of experimental
                                                                                       relation
                                                                                                                                  results
                                                                                                      12% P and L
                                                                                      Portland                           PI:↓, methylane blue
Algeria, S-H                                                                                        each. (lime is a
                      —     84    33     51     1.98      CH        19.7     19.43 cement (P)                           values↑, CBR↓, shear
clay, M’sila [142]                                                                                     much better
                                                                                   and lime (L)                                 strength↑
                                                                                                          option)
                                                                                                                      With coal: less effect on
                                                                                   Coal ash (C)
Iran, taleghan                                                                                                                  properties
                      —     47    21     26      <1        CL       16.4     18.0 and hydrated 9% C + 6% HL
city [87]                                                                                                                coal + h. lime, UCS↑
                                                                                     lime (HL)
                                                                                                                                PI↓, CBR↑
                                                                                       Sewage
Taiwan, taipei                                                                                       8% admixture
                      —     30    20     10      >1        CL       16.6     16.8 sludge ash (S)                           CBR↑, UCS↑, PI↓
[137]                                                                                                    (S:L 4 : 1)
                                                                                   and lime (L)
                                                                                                    10% F (F: SiO2 is
                                                                                                                           Ps↓ (50% to 70%),
Sudan,                                                                                                54%, alumina
               2.64         76    24     52      1.3      CH        1.49     26.0   Fly ash (F)                          at 25% F, Ps↓ (90%),
Khartoum [123]                                                                                         34%, CaO is
                                                                                                                        UCS↑ (almost 100%)
                                                                                                           3.6%)
Brazil, curitiba                                                                                                              UCS (by 75%)
                     2.71   53    32     21      <1       MH        13.8     28.5     Lime (L)              9% L
city [143]                                                                                                                 Porosity↓, MDD↑
                                                                                                       Dolomite L
                                                                                                                            Increase in pH↑
Spain, Granada                                                                        Lime (L),        (effective as
                            69    48     21      1.4      CH        15.7       40                                          Increase in CO3↑
[21]                                                                               steel slag (S) commercial L) S:
                                                                                                                           UCS↑, plasticity↓
                                                                                                         also good
↑ represents an increase; ↓ represents a decrease, in the corresponding property.
12                                                                                                                 Advances in Materials Science and Engineering
                          SEM micrographs                                                                                Thermogravimetric analysis results
                                                                                                  100
90
                                                                                          Weight (%)
                                                                                                       80
                                                                                                                 Higher CO2
                                                                                                       70        fixation in RC-450°C paste
60
                                                                                                       50
                                                                                                                     200          400    600       800                      1000
                                                                                                                                  Temperature (°C)
                                                                                                                      OPC paste
                                                                                                                      RC-450°C paste
                                (a)                                                                                                       (e)
                                                                                                                                    EDX analysis 
                                  EDX position (d)                           50                                                            50
                                                                                      O                                                                        O
                                                                             40                                                                   40
                                                                             30                             Si                                    30
                                                                                                                                                                                     Ca
                                                                    Counts
                                                                                                                                         Counts
                                                                                                                           Ca
                                                                                                                                                           C           Si
                                                                             20 C                      Al                                         20
                                                                             10                                              Ca                   10
             EDX position (c)
                                                                              0                                                                   0
                                                                                  0        1                  2     3     4          5                 0           1     2     3     4    5
                                                                                                             Energy (KeV)                                               Energy (KeV)
                                (b)                                                                                (c)                                                         (d)
Figure 9: Comparison of SEM micrographs and TGA along with EDX analysis on specified locations for OPC and recycled cement (RC)
450°C (modified after [129]).
cement at an elevated temperature on the microstructure of                            Fly ash is a geopolymer, i.e., a cementitious additive
expansive clay soil. So, cement proves to be more efficacious                       capable of reacting with H2O in the presence of alkaline
in controlling swell potential, and it is obvious that the                        activators [96]. Activation of FA prior to stabilization
mechanism of cement and lime stabilization of soils follows                       using different activators (such as NaOH, Na2SO4, and
a similar pattern and yields identical results.                                   K2SO4) is necessary for their performance. In order to
                                                                                  elevate the pH environment, generally 1% CaO is in-
                                                                                  corporated in the industrial wastes for initiating the
5.3. Main Effect of Fly Ash and Interaction with Lime and                          chemical reaction. The cementitious nature lacks because
Cement. Fly ash (FA) controls the swell potential in ex-                          the CaO content in FA is less than 10% although the Al2O3
pansive soils [24, 137] and is classified into several types                       and SiO2 contents are generally high. Therefore, lime,
based on the source of extraction and nature of pozzolanic                        cement, or GGBS are incorporated to enhance the poz-
behavior. The ASTM categorizes the noncrystalline FA into                         zolanic behavior of FA [149].
Class N, Class F, and Class C [71], represented here as NFA,                          Of all ASTM types of FA, the CFA proves to significantly
FFA, and CFA, respectively. One advantage inherent to FA is                       improve the expansivity. This results in decreasing perme-
its pozzolanic nature. CFA is obtained when subbituminous                         ability, PI, FS, and Ps of soft clays [12, 95, 150]. The ce-
coal is burnt in plants, while generating electricity [129]. This                 mentation in expansive clays stabilized with lime, lime-FA,
form of CFA is being considered as an additive with high-                         and OPC is associated with formation, setting, and inter-
calcium fly ash (HCFA) in conjunction with other catalytic                         growth of gelatinous reaction products (such as crystalline,
binders and a waste material rich in silica-alumina to de-                        hydrous calcium silicates, and aluminates). Figure 10
velop a new cold mixture for asphalt binders and emulsion                         highlights the particulate characteristics of four types of
mixtures in pavement design and practice [147]. In India                          pozzolan. The environmental scanning electron microscopy
alone, as of 2005, according to Dahale [97] the total pro-                        (ESEM) is an advanced form of SEM [151]. It is shown in
duction of FA reached 75M tons/year, 92% of which would                           Figure 10 that trass pozzolan (T) has the capability to absorb
go useless in contrast with findings of He et al. [129] for the                    large amount of water in contrast to tuff pozzolan (A)
western countries, stating the effective utilization of 70% of                     exhibiting roundish and rough surface which witnesses a
total FA produced. In the Table 3, Kate reported the FA with                      lower water uptake, owing to their mineral shape, size, and
CaO approximately equals to 49% [96]. It can be observed                          orientation. The subsequent increase in angularities of
from the table that all FA types have silica + alumina + iron                     pozzolan K (sharp edged, split-like grains, more even, and
oxide content exceeding 80% and is therefore defined as                            dense structural surface) and P (sharp-edged, split-like
“pozzolan”, according to ASTM [148].                                              grains, glassy-like, and even more even and dense surface)
Advances in Materials Science and Engineering                                                                                          13
(a) (b)
(c) (d)
Figure 10: Environmental scanning electron microscope (ESEM) images of various types of pozzolans providing an insight to particulate
characteristics (reproduced from research study by [121] with some modifications).
(Figures 10(c) and 10(d), respectively) also leads to reduced              increasing OMC whereas accounts for a reduction in MDD
water penetration [121].                                                   in the presence of sand, which acts as the filler material to
    In addition, the indirect tensile strength of specimen                 improve compaction characteristics due to capillary bridge.
stabilized with FA can be calculated, which is helpful for soils           Also, by keeping FA content constant and increasing the
subjected to traffic load, differential temperature, and/or                   amount of sand, the results were inversed. In terms of
nonuniform settlement, and an equation is employed on the                  strength characteristics evaluation, a highest UCS value is
basis of which a correlation (25% FA treatment) has been                   attained with an addition of 10% FA and 8% sand in the
developed to determine the Brazilian tensile strength (BTS),               expansive soil sample, which is attributed to C-S-H gel and
using the unconfined compression strength (UCS) value, in                   AFt phase formation because of FA hydration and thus
equation (8) [152]. For a given value of LL, the PI can be                 significantly improving cohesion between clayey particles.
directly evaluated using correlation suggested in equation                     The CFA has been used in conjunction with cement and
(9) and can further be used to determine BTS from the                      waste gypsum [97], and the maximum UCS is achieved at 28
derived equation (10), after original equations by past                    days (0.36 MPa to 3.49 MPa) with strength reporting to be
researchers:                                                               decreased by 36% at 56 days. While dealing with coal ash, the
                                                                           probable chromium (Cr) and lead [97] concentration is to be
                   BTS � 0.026 × UCS1.116 ,                         (8)
                                                                           kept in limits [154]. According to Kolias et al. [99], the FA
                                                                           increases the tobermorite formation which enhances the
                     PI � 0.11 × LL2 ,                              (9)    strength, while further addition of cement provides im-
                                                                           proved setting and hardening. The mixture of cement-FA
                   BTS � 0.0012 × PI0.558 .                       (10)     yields high early and final strength for treated soils. The FA
                                                                           less than 50% is optimum and. achieves the highest UCS and
   The main and interaction effects of FA are briefly dis-                   shear strength values. However, the strength drops beyond
cussed. According to Kommu et al. [153], the FA aids in                    this threshold.
14                                                                                       Advances in Materials Science and Engineering
     Table 6: Comparison of lime-activated GGBS (LAS) and lime-activated Portland cement (LPC), in perspective of stabilization.
                          Soaked in Na2SO4 for 120 days C-S-H formation C-S-H formation              Compressive strength
LAS∼LPC-treated clay
                                (durability check)        (before soaking) (after soaking)             (start till soaking)
LAS-treated clays            No cracks, more durable           More              Less          Steady drop (775 kPa to 625 kPa)
LPC-treated clays          Extensive cracks, less durable       Less            More       Sharp loss in strength gain (after 28 days)
LAS: lightweight alkali-activated GGBS; LPC: lightweight Portland cement.
5.4. Main Effect of GGBS and Interaction Effect with Lime and                 prices and/or unavailability of lime in some places, the
Cement. The ground granulated blast furnace slag (GGBS) is                  GGBS-FA mix binder is cost-effective and significantly re-
a prominent industrial waste that helps in giving long-term                 duces the burden on environment [161].
strength to problematic soils [155, 156], and sometimes, it is
also used as a replacement of cement due to its high ce-
mentitious nature. Unlike lime, the GGBS is far more ef-                    5.5. Main Effect of Bagasse Ash and Interaction Effect with
ficacious to stabilize the sulfate bearing soils. Much has been              Lime and Cement. The bagasse ash is a waste in the form of
learnt about the physical, mechanical, and hydraulic be-                    agricultural byproducts which is obtained from sugarcane
havior of clayey soils stabilized using GGBS and their ac-                  industry. The juice extracted from sugarcane forms a mass
tivation with lightweight alkalis (lightweight alkali-activated             resembling fiber called “bagasse.” When bagasse is burnt, an
GGBS (LAS)). As shown in Table 6, use of this particular                    ash is produced in the form of fine residue, with coarse-
CSM experiences no cracks visible to naked eye when dipped                  grained structure and lower Gs value than that of soil, termed
in sodium sulfate solution for four months, thereby yielding                as “bagasse ash [95].” The BA is a serious issue and is usually
a higher compressive strength [157, 158]. It can also be                    dumped without any economic value. Being rich in SiO2
observed that C-S-H formation before soaking in case of                     content, it is used as a pozzolanic material because the
LAS-treated clays is in more quantity than that of LPC-                     amount of alumina, silica, and calcium oxide exceeds 70%.
treated clays, and after soaking, it is vice versa. The LAS-                ASTM defines such materials as Class N or Class F pozzolan,
treated clays are more durable and experience fewer number                  while if the accumulated percentage exceeds 50%, then it is
of cracks when dipped in sodium sulfate solution for 120                    categorized as Class C pozzolan [149]. In addition, it has
days, in contrast with LPC-treated clays which are less                     been confirmed from leaching tests on expansive soil sta-
durable and witness more cracks.                                            bilized with bagasse ash that it is suitable for stabilization of
    The role of GGBS, alone and in combination with FA and                  road subgrades owing to its nonhazardous nature [162, 163].
lime, in affecting the engineering characteristics is of vital               The addition of BA reduces the PI, swell, alkalinity of soil
importance to soil engineers, practitioners, and scientists.                matrix, and cation exchange value while increases the
According to Sivapullaiah [159], the slags with a larger                    CaCO3 content and the total soluble solids [3].
amount of Ca2+ ions (such as in the case of GGBS) than Na2+                     The improvement mechanism of BA is identical to the
ions, such as Cu slags, tend to minimize swell potential more               chemical reaction involved in cement stabilization. The clay
effectively. It suggests that suitability of stabilizer is highly            reacts with lime and BA resulting in flocculation and the
dependent on its chemical composition. In addition, Sharma                  cation exchange phenomenon that is a “short-term reac-
and Sivapullaiah [95] and Jiang et al. [160] employed GGBS                  tion.” Then, the formation of C-S-H and C-A-H gels takes
for investigating effects on expansive soils to control the                  place, due to the pozzolanic reaction, giving “long-term
uncontrollable swelling, mainly occurring in sulfate-rich                   strength” to the soils [164, 165]. However, the strength gain
soils upon CaO or cement addition, concluding that GGBS is                  and durability are quite low when BA is used alone for
a suitable material for pavement stabilization, owing to its                purpose of stabilization. However, it effectively lowers the
high wear resistance. The use of GGBS in combination with                   PI, FS, and Ps values [68]. The UCS of high expansive soil,
lime and RHA (20%, 5%, and 10%, respectively) is effective,                  when treated with 0.5% BA + 6.25% lime mix and cured for
as plasticity reduces drastically by 67% and the strength                   three days, witnessed a dramatic increase of almost 96% as
increases by 95% in contrast to that of virgin soil [98].                   compared to when no lime treatment was done. Similarly,
Moreover, considering the wide variation in properties of                   for the same dosage levels of stabilizer contents cured for 28
GGBS and FA, for instance, the deficiency of CaO in FA and                   days, the percentage increase in strength was about 150%,
the excess of CaO in GGBS make their “interaction effect” as                 reflecting the effectiveness of curing in the strength gain
superadvantageous, in terms of treating expansive soil. With                process [166]. The MDD drops, and the OMC rises when
using almost 10% steel slag, the MDD is expected to rise and                (8% BA + 16% lime sludge) mix is incorporated in expansive
the UCS also increases by 50%. However, beyond this                         soil (LL � 60%, PI � 28%, Ps � 128 kN/m2) [167]. In Fig-
amount, the strength loss is reported at a much slower rate.                ure 11, the increase in RHA from 0 to 7.5% indicates a
Also, the reduction of 70% in PI is recorded at 30% steel slag              gradual increase in the UCS and later drops when further
content. Moreover, by using 20% optimum blend of GGBS                       increased up to 12.5%. The trend of CDA is almost similar to
and FA for stabilization of high plastic clays along with 1%                that of SCBA. In contrast, following the same pattern, RHA
lime, the test results indicate reduction in LL and PI, whereas             experiences a sharp rate of strength gain and strength loss.
shrinkage limit, MDD, UCS, and amount of C-S-H gel                          Therefore, it can be concluded that BA is a less effective
produced are significantly increased. Despite high cement                    stabilizer and its performance is highly improved when lime
Advances in Materials Science and Engineering                                                                                           15
2.5
21
                      UCS (g/cc)
                                   1.5
0.5
                                    0
                                          0      2.5             5              7.5              10        12.5
                                                       Percentage replacement of soil with ash
                                         RHA
                                         SCBA
                                         CDA
Figure 11: Stabilization of subgrade soil in India using indigenous nonplastic materials such as rice husk ash (RHA), sugarcane bagasse ash
(SCBA), and cow dung ash (CDA). The in situ soil (depth of 1.5 m–2.5 m was intermediate plastic clay (figure taken from [168]).
is added to it, and the curing period is increased up to 28              avoid polluting the environment [93]. Addition of GSA to
days.                                                                    black cotton soil (LL � 83.36% and PI � 89.32%) significantly
                                                                         improved the compaction and strength characteristics.
                                                                         However, it cannot be used as standalone stabilizer for road
5.6. Efficacy of Other Eco-Friendly Stabilizer Materials.                  construction owing to the smaller value of CBR after sta-
The extent of other CSMs cannot comprehensively be                       bilization [175]. Venkatraman et al. [176] concluded from
enclosed in one research paper; however, few eminent                     his study on the settlement behavior of clayey soil using the
materials are presented in this section, for instance, calcium           plate load test that the GSA stabilization enhances the ul-
carbon residue (CCR), groundnut shell ash (GSA), and                     timate bearing capacity. GSA and cement increased the
sewage sludge ash (SSA).                                                 optimum moisture content [177] whereas slightly decreased
    When acetylene is burnt, calcium carbon residue (CCR)                the dry density as well as the modulus of elasticity of soil. The
is produced. It is deleterious in nature but rich in lime [138]          (2% GSA + 0.1% cement) blend may be used as a feasible
content; therefore, it can be used to modify the properties of           alternative in pavement construction and for stabilizing soil
expansive soils [169]. The stabilization with CCR achieves               where load is emplaced [103]. The GSA with dosage levels
better results than with lime from the viewpoint of economy              increased from 4% to 6% was applied to low plasticity clay
and environment [170]. Horpibulsuk categorized the                       and a rise of 15% in UCS at 7 days was recorded, which fell
strength development of CCR-stabilized soils into three                  short of standard requirement for stabilization of base
zones, namely, active, inert, and deterioration zones. Only              materials [178]. Behnood [12] enumerated that 8% GSA is
the first two zones are beneficial with respect to strength                helpful in mitigating the swell by effectively lowering down
improvement. In the first zone (i.e., CCR less than 7%), the              the PI value.
natural pozzolanic material is sufficient for the pozzolanic                   SSA resembles FA in terms of cementitious nature has a
reaction. Hence, the FA is not required to further improve               higher percentage of Ca2+ in SSA (8%) than in FA (3 to 5%)
the strength. But, in the inert zone (i.e., CCR between 7%               [162] and acts as an efficient stabilizer. Sewage sludge
and 11%), the strength gain is achieved by adding FA which               blended with coal fly ash (CFA) can lower the availability of
helps in densification and speeding up the pozzolanic re-                 heavy metals such as Cu, Zn, and Cd in the sludge [179].
action [78]. Moreover, Somna et al. [171] utilized CCR-RHA               Behnood [12] outlined that SSA effectively modifies the
mix and recorded 22% increase in the UCS upon curing                     properties of CL soil by increasing their UCS, CBR, cohe-
from 28 days to 180 days. These materials are also employed              sion, and shear strength while reducing the swelling and
for yielding high strength concrete in construction. In ad-              angle of internal friction [180]. The UCS of specimens was
dition, BA and CCR are mixed in combination for making                   improved 3–7 times by using incinerated sewage sludge ash
the stabilized mix more ductile. In the stabilization of soft            (ISSA) and cement. Also, the swelling behavior was reduced
Bangkok clay, the pozzolanic reaction intensified as the                  by 10–60%, and the improvement in the CBR values was up
amorphous Si from BA was dissolved in alkaline environ-                  to 30 times [181]. 8% SSA + lime can change untreated
ment and reacted with the CCR [172]. With 8% CCR                         expansive from weak subgrade soil to better subgrade soil in
treatment, for no BA content and with 9% BA after 36 days                road construction [137].
curing, the change in UCS was as high as 400% [173].
    Ground nuts are grown in abundance in different re-
                                                                         6. Discussion
gions of the world approximately 20,000,000 hectares per
annum [174]. The use of GSA, a form of agricultural waste, is            It has been evolved to this day that the evaluation of
useful in waste management. It needs to be safely disposed to            stabilization of expansive soils is well documented in a
16                                                                               Advances in Materials Science and Engineering
series of diverse philosophies laid down, wherein a variety         structure [122] and (2) increase in calcium to silica ratio.
of CSM have been employed for stabilizing low to high               According to Dash and Hussain [115], these studies are in
range expansive soils. However, one significant short-               good agreement with those observed for microstructural
coming associated with the use of CSM is the increased              behavior of expansive soils. Thus, lime stabilization is fea-
brittleness; therefore, several stabilized elements are in-         sible for SiO2-rich soils, soils having gypsum, and the soils
corporated to overcome this problem [173]. The two                  containing iron with varying optimum percentage of lime
prominent and conventional CSMs, lime and cement,                   for each, depending on presence of respective ingredient.
witness brittle failure in the modified soil matrix system.          However, in SO4-rich soils, the use of lime is not recom-
Lime stabilization is commonly and widely used for road             mended since there is no hydrated calcium oxide available.
pavements. According to findings of Bell [117] and                   Because when in absence of sulfates, the CEC of the soil
Mukhtar et al. [118], the optimum percentage of lime (for           greatly depends on its negatively charged particles [182].
pH � 12.4) ranges between 4% and 8%, depending upon                 Thus, it can be inferred that lime stabilization of expansive
the soil conditions and type of soil. However, if used in           soils is mainly function of environment of lime-soil reactions
excess that is 6% and more, Tran et al. [119] emphasized            and type of clay minerals.
that lime treatment may undergo significant reduction in                 For cement versus lime stabilization, it is often mis-
compressive and shear strength (of up to 30%, or even               interpreted that both stabilizers are identical in yielding
more) because of requirement of large amount of water               results in terms of C-S-H and C-A-H formation, but cement
and higher initial porosity. As a result, the unconsumed            proves to be a relatively better choice. Few common char-
hydrated lime becomes unreactive in the strength gain               acteristics related to the cement stabilization are briefly
process [120]. Cement provides the highest strength                 discussed. Cement assists in minimizing the toxicity level
among other CSMs, whereas lime containing excess of free            from certain wastes, for instance, agricultural or industrial
lime is suitable for materials with PI > 10% as the free lime       waste, and causes reduction in PI and swell potential.
reacts with clay particles to reduce the plasticity. Lime           Generally, 10% cement is considered as optimum for
cement blends are usually limited to stabilize materials            treating medium to high expansive soils, whereas the var-
with PI < 10%. The strength achieved depends on amount              iation in improvement widely varies when it is used between
of stabilizing agent incorporated and the type of material          2–10% because of varying soil type, weathering effects, and
treated. However, excessive cement may be detrimental               period of curing. Cement is not used for soils with PI higher
for the subgrade performance as it could form semibrittle           than 30%. Therefore, lime is usually added to the soil prior to
materials [13].                                                     cement mixing for workability. Cement reduces swell more
    The results of XRD and XRF of lime-treated soils                effectively than lime does. It can be inferred that (i) the rate
revealed the significant mineralogical changes upon treat-           of decrease for both FS and Ps with the addition of 2%
ment. The long-term strength is improved when curing is             cement is significant. An increase up to 12% cement causes
done, and the strength increase upon treatment of 4% lime           uniform and gradual reduction in Ps and a relatively non-
in low swelling clays (i.e., kaolinite) is the highest in           uniform but a gradual decrease in FS. Also, the modification
comparison to the lowest strength for the case of high              mechanism of cement and lime is more or less similar
swelling clay minerals (e.g., Mt). This is associated with the      because C-S-H and C-A-H gels formation leads to ce-
replacement of calcium hydroxide with calcium oxide at the          mentitious links with the untreated expansive soil particles
early stages of lime mixing with the soil. According to             particularly containing organic matter. [183] A general in-
Behnood [12], soil stabilization with lime in the regions           creasing trend is observed in UCS values with higher CKD
exposed to severe weathering is less effective (at low lime          content along with the curing time for problematic soil (with
content) because the beneficial effect of lime stabilization in       a potential for a time-dependent increase in strength). So,
reducing the swell potential of lime-treated soil is reduced in     strength increases with more curing. Therefore, further
this condition. However, for many other scenarios, lime             studies on longer curing times and possibly increased CKD
stabilization of expansive soils is still regarded as an effective   contents are required. CKD, volcanic ash, and their mixes
approach to minimize the swelling potential. According to           are helpful in reducing cost of construction of small-scale
Dafalla et al. [104], when laminated clay is stabilized using       houses and pavements, in terms of strength and durability
lime, the PI value reduces more effectively for soils con-           aspects [171]. It is important to mention here that blend of
taining calcic Mt or sodic Mt than clays with kaolinite.            5% lime and 3% cement will effectively reduce the PI by 60%
However, Al-Rawas [71] argue that lime modification may              and Ps by 82%. Thus, cement is more efficacious in con-
be unsuitable for soils with content of Mt in excess of 40%,        trolling swell potential although the mechanism behind
which is having 8% as the optimum lime dosage level. It is          stabilizing soils by cement and lime follows a similar pattern
explained by the notion that, with increase in Mt percentage        and results in general.
in the clay fraction, a simultaneous increase in volumetric             Fly ash less than 50% is suffice for increasing the OMC
strain is also accompanied, depicting the effect of miner-           and reducing the MDD in expansive soils, thereby achieving
alogical properties of expansive clay on long-term charac-          higher UCS and shear strength values. But a successful
teristics of chemical stabilizer materials. The microstructural     treatment requires an alkali activator due to the inherent
characteristics indicate that PI is significantly increased with     lack of calcium oxide (less than 10%) in FA. It is said that 1%
8% lime due to [50] formation of C-S-H and C-A-H gels               lime is suited for compensation, but the rate of increase of
[117], which fill the pores in clays with discontinuous              OMC and MDD is still important. While modifying the
Advances in Materials Science and Engineering                                                                                   17
capacity against expansion, FA is also proven to increase the         (2) Along with the microstructure effects, the rate of
strength of expansive soils, such as adding 10%. But an                   hydration and pozzolanic reactions in the poly-
optimized dosage for a joint application, for example, both               merization process and cementation play a major
increasing UCS while reducing expansion is still open for                 role in the required duration and condition of soil
further investigation leading to introduction of multipur-                curing. Before soil stabilization with the selected
pose FAs. To this end, modified FAs, such as CFA, FA-sand-                 CSM, an optimum dosage and methodology of
marble dust, and variety of similar materials are incorpo-                practical application on the host soil should be
rated to reduce the PI, FS, and Ps of soils as feasible mixtures          characterized.
in practice as, for example, in flexible pavement where both           (3) In accordance with the past literature, Table 5 is
strength and expansion are significant.                                    created with the knowledge of the variety of ex-
    The ground-granulated blast furnace slag is another                   pansive soils across the globe using different CSMs in
highly cementitious one, and it also needs an activator,                  order to quantify the main and interaction effects of
generally with lightweight alkali. GGBS lacks binder leading              the type of stabilizers in terms of the applicable host
to a more CaO presence compared with lime which due to                    soil, optimum CSM dosage incorporated, and the
less cementitious nature has less CaO content. As a result,               associated improved properties.
both GGBS and lime are used in conjunction, and it is
                                                                      (4) Despite cement being the widely used CSM, con-
established that 20% GGBS and 1% lime will effectively
                                                                          sidering the expenses and challenge of CO2 emission
reduce LL and PI and increase the MDD, UCS, and C-S-H
                                                                          and associated toxicity levels in treated soils, lime
formation. The ground basic oxygen furnace slag (GBOFS)
                                                                          alongside other pozzolans (FA, BA, GGBS, CCR,
performs better than the GGBS. In a study by Goodarzi and
                                                                          GSA, and SSA in order of their practical efficiency) is
Salimi [109], 10% GBOFS is sufficient to eliminate disper-
                                                                          more beneficial option for stabilizing expansive soils.
sion in soil, whereas a greater percentage of GGBS (i.e.,
20–25%) is required for achieving the same impact. It is               In addition, this study identifies research needs for future
attributed to the lower activity (crystalline nature) of GGBS      including energy perspectives with respect to sustainable
in contrast to that of GBOFS. One associated shortcoming is        local construction and developing a satisfactory protocol
that the ultimate improvement in engineering properties            explaining the stabilization mechanisms. The search for
requires still a higher percentage (15–20%) of GBOFS along         choosing environmentally friendly biomaterials and nu-
with increased curing time [12].                                   merous waste materials is still under investigation and is
    Owing to its nonhazardous nature and suitability for           needed to maintain global sustainability standards.
road subgrades, bagasse ash alone used for stabilizing soil
affects the durability. The improvement mechanism of BA
resembles with that of cement stabilization. For better re-
                                                                   Conflicts of Interest
sults, lime should be added to the BA. It is observed that         The authors declare that they have no conflicts of interest.
0.6% BA and 6.25% lime will increase the strength by 96%
after curing for three days, suggesting that curing plays a
major role. Indicating the fact that BA is a less effective         Acknowledgments
stabilizer, its performance is highly improved when lime is
                                                                   The key project of the National Natural Science Foundation
added to it with increased curing.
                                                                   of China (Grant no. 41630633) is acknowledged for the fi-
                                                                   nancial support. The authors would like thank Professor
7. Conclusions and Recommendations                                 Shui Long Shen for his motivation in writing this manuscript
                                                                   and Engr. Aminul Haque and Engr. Farjad Iqbal for their
This study reviews the trends in stabilization of low to high      valuable comments in finalizing this review article. The
expansive soils with Ca-based materials (CSMs). The in-            authors also wish to thank the esteemed referees for pro-
fluence of the effectively proven CSMs on the engineering,           viding insightful suggestions to improve this manuscript.
geotechnical, and microstructural properties of expansive
soils used in soil stabilization has been evaluated. In addi-
tion, the recent studies stressing the use of more environ-        References
mentally friendly and nonconventional stabilization
                                                                     [1] L. C. Dang, B. Fatahi, and H. Khabbaz, “Behaviour of ex-
materials and techniques have also been discussed. In the                pansive soils stabilized with hydrated lime and bagasse fi-
light of discussions in this study, the main conclusions and             bres,” Procedia Engineering, vol. 143, pp. 658–665, 2016.
findings are stated as follows:                                       [2] H. King: Expansive Soils and Expansive Clay: The Hidden
    (1) The microstructure of expansive soil is a key pa-                Force behind Basement and Foundation Problems, 2015,
        rameter in evaluating the swell-shrink properties,               http://www.coinspection.com/uploads/1/1/2/4/11243167/
        compressive strength behavior, and the environ-                  geology.com_articles_expansive-soil.pdf.
        mental potential in various soil stabilization projects.     [3] C. Rajakumar and T. Meenambal, “Experimental study of
        A successful and reliable choice of stabilizers should           bagasse ash utilisation for road application on expansive
        be on the basis of their subsequent effect on the                 soil,” Nature Environment & Pollution Technology, vol. 14,
        microstructure.                                                  no. 4, 2015.
18                                                                                  Advances in Materials Science and Engineering
 [4] S. A. Aiban, “Compressibility and swelling characteristics of     [20] E. Celik and Z. Nalbantoglu, “Effects of ground granulated
     Al-Khobar Palygorskite, eastern Saudi Arabia,” Engineering             blastfurnace slag (GGBS) on the swelling properties of lime-
     Geology, vol. 87, no. 3-4, pp. 205–219, 2006.                          stabilized sulfate-bearing soils,” Engineering Geology,
 [5] B. Zhang, W. Shen, J. Wang, W. Zhang, W. Zhu, and Y. Liu,              vol. 163, pp. 20–25, 2013.
     “Slight-expansive road base course binder: properties, hy-        [21] M. Sol-Sánchez, J. Castro, C. G. Ureña, and J. M. Azañón,
     dration and performance,” Construction and Building Ma-                “Stabilisation of clayey and marly soils using industrial
     terials, vol. 150, pp. 626–633, 2017.                                  wastes: pH and laser granulometry indicators,” Engineering
 [6] G. M. S. Abdullah and H. I. Al-Abdul Wahhab, “Evaluation               Geology, vol. 200, pp. 10–17, 2016.
     of foamed sulfur asphalt stabilized soils for road applica-       [22] M. F. Iqbal, Q.-F. Liu, I. Azim et al., “Prediction of me-
     tions,” Construction and Building Materials, vol. 88,                  chanical properties of green concrete incorporating waste
     pp. 149–158, 2015.                                                     foundry sand based on gene expression programming,”
 [7] P. K. Gautam, P. Kalla, A. S. Jethoo, R. Agrawal, and                  Journal of Hazardous Materials, vol. 384, p. 121322, 2020.
     H. Singh, “Sustainable use of waste in flexible pavement: a        [23] J. K. Mitchell and K. Soga, “Fundamentals of soil behavior,”
     review,” Construction and Building Materials, vol. 180,                Fundamentals of Soil Behavior, Vol. 3, John Wiley & Sons,
     pp. 239–253, 2018.                                                     New York, NY, USA, 2005.
 [8] H. Jiang, B. Wang, H. I. Inyang, J. Liu, K. Gu, and B. Shi,       [24] J. Nelson and D. J. Miller, Expansive Soils: Problems and
     “Role of expansive soil and topography on slope failure and            Practice in Foundation and Pavement Engineering, John
     its countermeasures, Yun County, China,” Engineering Ge-               Wiley & Sons, Hoboken, NJ, USA, 1997.
     ology, vol. 152, no. 1, pp. 155–161, 2013.                        [25] D. Mašı́n and N. Khalili, “Swelling phenomena and effective
 [9] M. Gougazeh and A. Al-Shabatat, “Geological and geo-                   stress in compacted expansive clays,” Canadian Geotechnical
     technical properties of soil materials at Tannur dam, Wadi Al          Journal, vol. 53, no. 1, pp. 134–147, 2015.
     Hasa, South Jordan,” Journal of Taibah University for Science,    [26] Y. Xu, “Fractal model for the correlation relating total
     vol. 7, no. 4, pp. 216–224, 2013.                                      suction to water content of bentonites,” Fractals, vol. 26,
[10] T. M. Petry and D. N. Little, “Review of stabilization of clays        no. 3, Article ID 1850028, 2018.
     and expansive soils in pavements and lightly loaded struc-        [27] V. Ouhadi and R. Yong, “The role of clay fractions of marly
     tures-history, practice, and future,” Journal of Materials in          soils on their post stabilization failure,” Engineering Geology,
     Civil Engineering, vol. 14, no. 6, pp. 447–460, 2002.                  vol. 70, no. 3-4, pp. 365–375, 2003.
[11] K. B. Simons, “Limitations of residential structures on ex-       [28] R. Katti, U. Kulkarni, A. Katti, and R. Kulkarni, “Stabilization
     pansive soils,” Journal of Performance of Constructed Fa-
                                                                            of embankment on expansive soil—a case study,” in Pro-
     cilities, vol. 5, no. 4, pp. 258–270, 1991.
                                                                            ceedings of the Experimental and Applied Modeling of Un-
[12] A. Behnood, “Soil and clay stabilization with calcium- and
                                                                            saturated Soils GeoShanghai International Conference,
     non-calcium-based additives: a state-of-the-art review of
                                                                            pp. 181–189, Shanghai, China, June 2010.
     challenges, approaches and techniques,” Transportation
                                                                       [29] C. Shi, Y. Wu, C. Riefler, and H. Wang, “Characteristics and
     Geotechnics, vol. 17, pp. 14–32, 2018.
                                                                            pozzolanic reactivity of glass powders,” Cement and Concrete
[13] C. Godenzoni: Multiscale Rheological and Mechanical
                                                                            Research, vol. 35, no. 5, pp. 987–993, 2005.
     Characterization of Cold Mixtures, 2017, https://scholar.
                                                                       [30] L. Liu, “Prediction of swelling pressures of different types of
     google.com/scholar?hl=en&as_sdt=0%2C5&q=Multiscale+
                                                                            bentonite in dilute solutions,” Colloids and Surfaces A:
     Rheological+and+Mechanical+Characterization+of+Cold+
     Mixtures&btnG=.                                                        Physicochemical and Engineering Aspects, vol. 434, pp. 303–
[14] K. Yan and L. Wu, “Swelling behavior of compacted ex-                  318, 2013.
     pansive soils, recent advancement in soil behavior,” in           [31] A. M. Awad, S. M. Shaikh, R. Jalab et al., “Adsorption of
     Proceedings of the Situ Test Methods, Pile Foundations, and            organic pollutants by natural and modified clays: a com-
     Tunneling: Selected Papers from the 2009 GeoHunan Inter-               prehensive review,” Separation and Purification Technology,
     national Conference, pp. 1–6, Changsha, China, August 2009.            vol. 228, Article ID 115719, 2019.
[15] C. C. Ikeagwuani and D. C. Nwonu, “Emerging trends in             [32] Y.-J. Cui, “On the hydro-mechanical behaviour of MX80
     expansive soil stabilisation: a review,” Journal of Rock Me-           bentonite-based materials,” Journal of Rock Mechanics and
     chanics and Geotechnical Engineering, vol. 11, no. 2,                  Geotechnical Engineering, vol. 9, no. 3, pp. 565–574, 2017.
     pp. 423–440, 2019.                                                [33] A. A. Boateng and D. A. Skeete, “Incineration of rice hull for
[16] I. Yilmaz and B. Civelekoglu, “Gypsum: an additive for                 use as a cementitious material: the Guyana experience,”
     stabilization of swelling clay soils,” Applied Clay Science,           Cement and Concrete Research, vol. 20, no. 5, pp. 795–802,
     vol. 44, no. 1-2, pp. 166–172, 2009.                                   1990.
[17] C. Kurtulus, F. Sertcelik, M. M. Canbay, and İ. Sertcelik,       [34] S. Pourakbar, A. Asadi, B. B. K. Huat, and
     “Estimation of Atterberg limits and bulk mass density of an            M. H. Fasihnikoutalab, “Stabilization of clayey soil using
     expansive soil from P-wave velocity measurements,” Bulletin            ultrafine palm oil fuel ash (POFA) and cement,” Trans-
     of Engineering Geology and the Environment, vol. 69, no. 1,            portation Geotechnics, vol. 3, pp. 24–35, 2015.
     pp. 153-154, 2010.                                                [35] V. Cantillo, V. Mercado, and C. Pájaro, “Empirical corre-
[18] P. Priyadharshini, K. Ramamurthy, and R. G. Robinson,                  lations for the swelling pressure of expansive clays in the city
     “Reuse potential of stabilized excavation soil as fine aggregate        of Barranquilla, Colombia,” Earth Sciences Research Journal,
     in cement mortar,” Construction and Building Materials,                vol. 21, no. 1, pp. 45–49, 2017.
     vol. 192, pp. 141–152, 2018.                                      [36] H. Elbadry, “Simplified reliable prediction method for de-
[19] M. L. Nehdi, “Clay in cement-based materials: critical                 termining the volume change of expansive soils based on
     overview of state-of-the-art,” Construction and Building               simply physical tests,” HBRC Journal, vol. 13, no. 3,
     Materials, vol. 51, pp. 372–382, 2014.                                 pp. 353–360, 2017.
Advances in Materials Science and Engineering                                                                                            19
[37] N. Huvaj and E. Uyeturk, “Effects of drying on atterberg           [55] S. I. Cetiner, Stabilization of Expansive Soils by Çayirhan Fly
     limits of pyroclastic soils of northern Turkey,” Applied Clay          Ash and Desulphogypsum, Middle East Technical University,
     Science, vol. 162, pp. 46–56, 2018.                                    Ankara, Turkey, 2004.
[38] A. A. Basma, A. S. Al-Homoud, and A. Husein, “Laboratory          [56] D. W. Smith, G. A. Narsilio, and P. Pivonka, “Numerical
     assessment of swelling pressure of expansive soils,” Applied           particle-scale study of swelling pressure in clays,” KSCE
     Clay Science, vol. 9, no. 5, pp. 355–368, 1995.                        Journal of Civil Engineering, vol. 13, no. 4, pp. 273–279, 2009.
[39] H. Akgün, A. Günal Türkmenoğlu, A. Arslan Kelam,              [57] Y. S. Wibowo, “Perilaku Sifat Fisik dan Keteknikan Tanah
     K. Yousefi-Bavil, G. Öner, and M. K. Koçkar, “Assessment of            residual Batuan Volkanik Kuarter Di Daerah Cikijing,
     the effect of mineralogy on the geotechnical parameters of              Majalengka, Jawa Barat,” RISET Geologi Dan Pertambangan,
     clayey soils: a case study for the Orta County, Çankırı,               vol. 21, no. 2, pp. 131–139, 2011.
     Turkey,” Applied Clay Science, vol. 164, pp. 44–53, 2018.         [58] P. V. Muthyalu, K. Ramu, and G. P. Raju, “Study on per-
[40] E. Mehmood, M. Ilyas, and K. Farooq, “Effect of initial                 formance of chemically stabilized expansive soil,” Interna-
     placement conditions on swelling characteristics of expan-             tional Journal of Advances in Engineering & Technology,
     sive soils,” in Proceedings of the Geo-Frontiers 2011: Advances        vol. 2, no. 1, p. 139, 2012.
     in Geotechnical Engineering, pp. 2397–2403, Dallas, TX,           [59] M. Malekzadeh and H. Bilsel, “Hydro-mechanical behavior
     USA, March 2011.                                                       of polypropylene fiber reinforced expansive soils,” KSCE
[41] B. Shi, H. Jiang, Z. Liu, and H. Fang, “Engineering geological         Journal of Civil Engineering, vol. 18, no. 7, pp. 2028–2033,
     characteristics of expansive soils in China,” Engineering              2014.
     Geology, vol. 67, no. 1-2, pp. 63–71, 2002.                       [60] F. Mousavi, E. Abdi, and H. Rahimi, “Effect of polymer
[42] A. A. Al-Rawas, “The factors controlling the expansive na-             stabilizer on swelling potential and CBR of forest road
     ture of the soils and rocks of northern Oman,” Engineering             material,” KSCE Journal of Civil Engineering, vol. 18, no. 7,
     Geology, vol. 53, no. 3-4, pp. 327–350, 1999.                          pp. 2064–2071, 2014.
[43] D. R. Katti, M. I. Matar, K. S. Katti, and P. M. Amarasinghe,     [61] H. Zhao, L. Ge, T. M. Petry, and Y.-Z. Sun, “Effects of
     “Multiscale modeling of swelling clays: a computational and            chemical stabilizers on an expansive clay,” KSCE Journal of
     experimental approach,” KSCE Journal of Civil Engineering,             Civil Engineering, vol. 18, no. 4, pp. 1009–1017, 2014.
                                                                       [62] M. Dafalla and M. Shamrani, “Road damage due to expansive
     vol. 13, no. 4, pp. 243–255, 2009.
                                                                            soils: survey of the phenomenon and measures for im-
[44] K. Prakash and A. Sridharan, “Free swell ratio and clay
                                                                            provement,” in Proceedings of the Design, Construction,
     mineralogy of fine-grained soils,” Geotechnical Testing
                                                                            Rehabilitation, and Maintenance of Bridges, pp. 73–80,
     Journal, vol. 27, no. 2, pp. 220–225, 2004.
                                                                            Hunan, China, 2011.
[45] Y. Xu, “Peak shear strength of compacted GMZ bentonites in
                                                                       [63] A. J. Puppala and A. Pedarla, “Innovative ground im-
     saline solution,” Engineering Geology, vol. 251, pp. 93–99,
                                                                            provement techniques for expansive soils,” Innovative In-
     2019.
                                                                            frastructure Solutions, vol. 2, no. 1, p. 24, 2017.
[46] ASTM, Standard Test Methods for One-Dimensional Swell or
                                                                       [64] A. Al-Taie, M. M. Disfani, R. Evans, A. Arulrajah, and
     Settlement Potential of Cohesive Soils, ASTM, West Con-
                                                                            S. Horpibulsuk, “Swell-shrink cycles of lime stabilized ex-
     shohocken, PA, USA, 2003.
                                                                            pansive subgrade,” Procedia Engineering, vol. 143, pp. 615–
[47] J. D. Nelson, K. C. Chao, D. D. Overton, and E. J. Nelson,
                                                                            622, 2016.
     Foundation Engineering for Expansive Soils, John Wiley &          [65] W. D. Lawson, A Survey of Geotechnical Practice for Ex-
     Sons, Hoboken, NJ, USA, 2015.                                          pansive Soils in Texas, Unsaturated Soils 2006, American
[48] A. Aqeel, “Investigation of expansive soils in Obhor Sabkha,           Society of Civil Engineers, Reston, VA, USA, 2006.
     Jeddah-Saudi Arabia,” Arabian Journal of Geosciences, vol. 9,     [66] M. Iqbal, Q. Liu, and I. Azim, “Experimental study on the
     no. 4, p. 314, 2016.                                                   utilization of waste foundry sand as embankment and
[49] B. A. Hakami and E.-S. S. A. Seif, “Expansive potentiality of          structural fill,” in Proceedings of the IOP Conference Series:
     Sabkha soils of Rabigh Lagoon, Saudi Arabia: a case study,”            Materials Science and Engineering, Article ID 012042,
     Arabian Journal of Geosciences, vol. 12, no. 4, p. 107, 2019.          Bangkok, Thailand, May 2019.
[50] I. M. Idriss and R. W. Boulanger, “SPT-based liquefaction         [67] M. De Beer, Aspects of the Design and Behaviour of Road
     triggering procedures,” Report UCD/CGM-10/02, Depart-                  Structures Incorporating Lightly Cementitious Layers, Uni-
     ment of Civil and Environmental Engineering, University of             versity of Pretoria, Pretoria, South Africa, 2008.
     California, Davis, CA, USA, p. 259, 2010.                         [68] H. Hasan, L. Dang, H. Khabbaz, B. Fatahi, and S. Terzaghi,
[51] M. Labib and A. Nashed, “GIS and geotechnical mapping of               “Remediation of expansive soils using agricultural waste
     expansive soil in Toshka region,” Ain Shams Engineering                bagasse ash,” Procedia Engineering, vol. 143, pp. 1368–1375,
     Journal, vol. 4, no. 3, pp. 423–433, 2013.                             2016.
[52] A. Puppala, L. Hoyos, C. Viyanant, and C. Musenda, “Fiber         [69] R. N. Yong and V. R. Ouhadi, “Experimental study on in-
     and fly ash stabilization methods to treat soft expansive               stability of bases on natural and lime/cement-stabilized
     soils,” in Proceedings of the Soft Ground Technology,                  clayey soils,” Applied Clay Science, vol. 35, no. 3-4,
     pp. 136–145, Noordwijkerhout, Netherlands, May 2001.                   pp. 238–249, 2007.
[53] M. M. Zumrawi, “Construction problems of light structures         [70] H. H. Adem and S. K. Vanapalli, “Review of methods for
     founded on expansive soils in Sudan,” International Journal            predicting in situ volume change movement of expansive soil
     of Science and Research (IJSR), vol. 4, no. 8, pp. 896–902,            over time,” Journal of Rock Mechanics and Geotechnical
     2015.                                                                  Engineering, vol. 7, no. 1, pp. 73–86, 2015.
[54] A. Al-Swaidani, I. Hammoud, and A. Meziab, “Effect of              [71] A. A. Al-Rawas, A. W. Hago, and H. Al-Sarmi, “Effect of
     adding natural pozzolana on geotechnical properties of lime-           lime, cement and Sarooj (artificial pozzolan) on the swelling
     stabilized clayey soil,” Journal of Rock Mechanics and Geo-            potential of an expansive soil from Oman,” Building and
     technical Engineering, vol. 8, no. 5, pp. 714–725, 2016.               Environment, vol. 40, no. 5, pp. 681–687, 2005.
20                                                                                        Advances in Materials Science and Engineering
[72] Y. Liu, Y. Su, A. Namdar et al., “Utilization of cementitious                resources of Papua New Guinea,” Resources, Conservation
     material from residual rice husk ash and lime in stabilization               and Recycling, vol. 51, no. 4, pp. 711–731, 2007.
     of expansive soil,” Advances in Civil Engineering, vol. 2019,         [90]   A. K. Sabat, “Engineering properties of an expansive soil
     pp. 1–17, 2019.                                                              stabilized with rice husk ash and lime sludge,” International
[73] M. M. Zumrawi, “Geotechnical aspects for roads on ex-                        Journal of Engineering and Technology, vol. 5, no. 6,
     pansive soils,” International Journal of Scientific Research,                 pp. 4826–4833, 2013.
     vol. 4, pp. 896–902, 2015.                                            [91]   B.-W. Yu, Y.-J. Du, F. Jin, and C.-Y. Liu, “Multiscale study of
[74] C. Godenzoni, A. Graziani, E. Bocci, and M. Bocci, “The                      sodium sulfate soaking durability of low plastic clay stabi-
     evolution of the mechanical behaviour of cold recycled                       lized by reactive magnesia-activated ground granulated
     mixtures stabilised with cement and bitumen: field and                        blast-furnace slag,” Journal of Materials in Civil Engineering,
     laboratory study,” Road Materials and Pavement Design,                       vol. 28, no. 6, Article ID 04016016, 2016.
     vol. 19, no. 4, pp. 856–877, 2018.                                    [92]   A. Rana, P. Kalla, and L. J. Csetenyi, “Sustainable use of
[75] M. A. Rahgozar, M. Saberian, and J. Li, “Soil stabilization                  marble slurry in concrete,” Journal of Cleaner Production,
     with non-conventional eco-friendly agricultural waste ma-                    vol. 94, pp. 304–311, 2015.
     terials: an experimental study,” Transportation Geotechnics,          [93]   F. Oriola and G. Moses, “Groundnut shell ash stabilization of
     vol. 14, pp. 52–60, 2018.                                                    black cotton soil,” Electronic Journal of Geotechnical Engi-
[76] A. Kumar and D. Gupta, “Behavior of cement-stabilized                        neering, vol. 15, no. 1, pp. 415–428, 2010.
     fiber-reinforced pond ash, rice husk ash-soil mixtures,”               [94]   K. M. A. Hossain and L. Mol, “Some engineering properties
     Geotextiles and Geomembranes, vol. 44, no. 3, pp. 466–474,                   of stabilized clayey soils incorporating natural pozzolans and
     2016.                                                                        industrial wastes,” Construction and Building Materials,
[77] V. Ortega-López, J. M. Manso, I. I. Cuesta, and J. J. González,            vol. 25, no. 8, pp. 3495–3501, 2011.
     “The long-term accelerated expansion of various ladle-fur-            [95]   A. K. Sharma and P. V. Sivapullaiah, “Ground granulated
     nace basic slags and their soil-stabilization applications,”                 blast furnace slag amended fly ash as an expansive soil
     Construction and Building Materials, vol. 68, pp. 455–464,                   stabilizer,” Soils and Foundations, vol. 56, no. 2, pp. 205–212,
     2014.                                                                        2016.
[78] S. Horpibulsuk, C. Phetchuay, A. Chinkulkijniwat, and                 [96]   J. M. Kate, “Strength and Volume Change Behavior of Ex-
     A. Cholaphatsorn, “Strength development in silty clay sta-                   pansive Soils Treated with Fly Ash,” Innovations in Grouting
     bilized with calcium carbide residue and fly ash,” Soils and                  and Soil Improvement, American Society of Civil Engineers,
     Foundations, vol. 53, no. 4, pp. 477–486, 2013.                              Reston, VA, USA, pp. 1–15, 2005.
[79] Y. Shang and Y. Fu, “Experimental study of the mechanical             [97]   P. Dahale, P. Nagarnaik, and A. Gajbhiye, “Effect OF flyash
     properties of expansive soil with added nanomaterials,”                      and lime on stabilization of expansive soil,” Journal on Civil
     Arabian Journal of Geosciences, vol. 11, no. 8, p. 180, 2018.                Engineering, vol. 6, no. 2, p. 8, 2016.
[80] A. K. Sabat, “Statistical models for prediction of swelling           [98]   A. A. Al-Rawas, “Microfabric and mineralogical studies on
     pressure of a stabilized expansive soil,” Electronic Journal of              the stabilization of an expansive soil using cement by-pass
     Geotechnical Engineering, vol. 17, pp. 837–846, 2012.                        dust and some types of slags,” Canadian Geotechnical
[81] A. Graziani, C. Iafelice, S. Raschia, D. Perraton, and                       Journal, vol. 39, no. 5, pp. 1150–1167, 2002.
     A. Carter, “A procedure for characterizing the curing process         [99]   S. Kolias, V. Kasselouri-Rigopoulou, and A. Karahalios,
     of cold recycled bitumen emulsion mixtures,” Construction                    “Stabilisation of clayey soils with high calcium fly ash and
     and Building Materials, vol. 173, pp. 754–762, 2018.                         cement,” Cement and Concrete Composites, vol. 27, no. 2,
[82] A. Graziani, C. Iafelice, S. Raschia, A. Carter, and                         pp. 301–313, 2005.
     D. Perraton, A Laboratory Approach for Characterizing the            [100]   M. Dayioglu, B. Cetin, and S. Nam, “Stabilization of ex-
     Evolutive Behavior of Cold Recycled Mixtures, 2018.                          pansive Belle Fourche shale clay with different chemical
[83] E. Otte, A Structural Design Procedure for Cement-Treated                    additives,” Applied Clay Science, vol. 146, pp. 56–69, 2017.
     Layers in Pavements, University of Pretoria, Pretoria, South         [101]   I. Akinwumi, “Soil modification by the application of steel
     Africa, 2013.                                                                slag,” Periodica Polytechnica Civil Engineering, vol. 58, no. 4,
[84] A. Seco, F. Ramı́rez, L. Miqueleiz, and B. Garcı́a, “Stabili-                pp. 371–377, 2014.
     zation of expansive soils for use in construction,” Applied          [102]   L.-W. Kong and A.-G. Guo, “Bearing strength and swelling
     Clay Science, vol. 51, no. 3, pp. 348–352, 2011.                             behavior of jingmen expansive soil,” in Proceedings of the
[85] M. R. Taha, “Geotechnical properties of soil-ball milled soil                GeoFlorida 2010: Advances in Analysis, Modeling & Design,
     mixtures,” in Nanotechnology in Construction 3, Z. Bittnar,                  pp. 2571–2580, Palm Beach, FL, USA, February 2010.
     P. J. M. Bartos, J. Němeček et al., Eds., pp. 377–382, Springer,   [103]   E. R. Sujatha, K. Dharini, and V. Bharathi, “Influence of
     Berlin, Germany, 2009.                                                       groundnut shell ash on strength and durability properties of
[86] R. P. Freitas, V. S. Felix, M. O. Pereira et al., “Micro-XRF                 clay,” Geomechanics and Geoengineering, vol. 11, no. 1,
     analysis of a Brazilian polychrome sculpture,” Microchemical                 pp. 20–27, 2016.
     Journal, vol. 149, p. 104020, 2019.                                  [104]   M. Dafalla, E. Mutaz, and M. Al-Shamrani, “Compressive
[87] A. Modarres and Y. M. Nosoudy, “Clay stabilization using                     strength variations of lime-treated expansive soils,” in Pro-
     coal waste and lime—technical and environmental impacts,”                    ceedings of the International Foundations Congress and
     Applied Clay Science, vol. 116-117, pp. 281–288, 2015.                       Equipment Expo, pp. 1402–1409, San Antonio, TX, USA,
[88] M. Khemissa and A. Mahamedi, “Cement and lime mixture                        March 2015.
     stabilization of an expansive overconsolidated clay,” Applied        [105]   T. Y. Elkady, “The effect of curing conditions on the un-
     Clay Science, vol. 95, pp. 104–110, 2014.                                    confined compression strength of lime-treated expansive
[89] K. M. A. Hossain, M. Lachemi, and S. Easa, “Stabilized soils                 soils,” Road Materials and Pavement Design, vol. 17, no. 1,
     for construction applications incorporating natural                          pp. 52–69, 2016.
Advances in Materials Science and Engineering                                                                                               21
[106] A. A. B. Moghal, B. C. S. Chittoori, and B. M. Basha, “Effect        [124] G. Constantinides, “Nanoscience and nanoengineering of
      of fibre reinforcement on CBR behaviour of lime-blended                    cement-based materials,” in Nanotechnology in Eco-Efficient
      expansive soils: reliability approach,” Road Materials and                Construction, Elsevier, Amsterdam, Netherlands, 2013.
      Pavement Design, vol. 19, no. 3, pp. 690–709, 2018.                 [125] A. Jamshidi, K. Kurumisawa, T. Nawa, and T. Igarashi,
[107] M. R. Hausmann, Engineering Principles of Ground Modi-                    “Performance of pavements incorporating waste glass: the
      fication, McGraw-Hill, New York, Ny, USA, 1990.                            current state of the art,” Renewable and Sustainable Energy
[108] D. Bergado, L. Anderson, N. Miura, and A. Balasubramaniam,                Reviews, vol. 64, pp. 211–236, 2016.
      Soft Ground Improvement in Lowland and Other Environ-               [126] A. Grilli, E. Bocci, and A. Graziani, “Influence of reclaimed
      ments, ASCE, Reston, VA, USA, 1996.                                       asphalt content on the mechanical behaviour of cement-
[109] A. R. Goodarzi and M. Salimi, “Stabilization treatment of a               treated mixtures,” Road Materials and Pavement Design,
      dispersive clayey soil using granulated blast furnace slag and            vol. 14, no. 3, pp. 666–678, 2013.
      basic oxygen furnace slag,” Applied Clay Science, vol. 108,         [127] A. S. Zaimoglu, “Optimization of unconfined compressive
      pp. 61–69, 2015.                                                          strength of fine-grained soils modified with polypropylene
[110] F. G. Bell, Engineering Treatment of Soils, CRC Press, Boca               fibers and additive materials,” KSCE Journal of Civil Engi-
      Raton, FL, USA, 2014.                                                     neering, vol. 19, no. 3, pp. 578–582, 2015.
[111] M. F. Javed, N. H. Ramli Sulong, S. A. Memon,                       [128] M. Schneider, M. Romer, M. Tschudin, and H. Bolio,
      S. K.-u. Rehman, and N. B. Khan, “Experimental and nu-                    “Sustainable cement production-present and future,” Ce-
      merical study of flexural behavior of novel oil palm concrete              ment and Concrete Research, vol. 41, no. 7, pp. 642–650, 2011.
      filled steel tube exposed to elevated temperature,” Journal of       [129] Z. He, X. Zhu, J. Wang, M. Mu, and Y. Wang, “Comparison
      Cleaner Production, vol. 205, pp. 95–114, 2018.                           of CO2 emissions from OPC and recycled cement pro-
[112] T. Thyagaraj, S. M. Rao, P. Sai Suresh, and U. Salini,                    duction,” Construction and Building Materials, vol. 211,
      “Laboratory studies on stabilization of an expansive soil by              pp. 965–973, 2019.
      lime precipitation technique,” Journal of Materials in Civil        [130] S. Saride, S. R. Chikyala, A. J. Puppala, and P. J. Harris,
      Engineering, vol. 24, no. 8, pp. 1067–1075, 2012.                         “Effects of organics on stabilized expansive subgrade soils,”
[113] T. Olinic and E. Olinic, “The effect of quicklime stabilization            in Proceedings of the Ground Improvement and Geosynthetics,
      on soil properties,” Agriculture and Agricultural Science                 pp. 155–164, Conshohocken, PA, USA, 2010.
      Procedia, vol. 10, pp. 444–451, 2016.                               [131] M. Turkoz and H. Tosun, “The use of methylene blue test for
[114] L. Ali and Z. Zafar, “Construction on expansive soils in semi             predicting swell parameters of natural clay soils,” Scientific
      arid zone,” in Proceedings of the Instrumentation, Testing,               Research and Essays, vol. 6, no. 8, pp. 1780–1792, 2011.
      and Modeling of Soil and Rock Behavior, American Society of         [132] M. Rahman, S. Rehman, and O. Al-Amoudi, “Literature
      Civil Engineers, Hunan, China, June 2011.                                 review on cement kiln dust usage in soil and waste stabili-
[115] S. K. Dash and M. Hussain, “Lime stabilization of soils:                  zation and experimental investigation,” International Jour-
      reappraisal,” Journal of Materials in Civil Engineering,                  nal of Research and Reviews in Applied Sciences, vol. 7, no. 1,
      vol. 24, no. 6, pp. 707–714, 2011.                                        pp. 77–87, 2011.
[116] Y. Cheng, S. Wang, J. Li, X. Huang, C. Li, and J. Wu,               [133] R. A. Shawabkeh, “Solidification and stabilization of cad-
      “Engineering and mineralogical properties of stabilized ex-               mium ions in sand–cement–clay mixture,” Journal of Haz-
      pansive soil compositing lime and natural pozzolans,”                     ardous Materials, vol. 125, no. 1–3, pp. 237–243, 2005.
      Construction and Building Materials, vol. 187, pp. 1031–1038,       [134] S. Peethamparan and J. Olek, “Study of the effectiveness of
      2018.                                                                     cement kiln dusts in stabilizing Na-Montmorillonite clay,”
[117] F. G. Bell, “Lime stabilization of clay minerals and soils,”              Journal of Materials in Civil Engineering, vol. 20, no. 2,
      Engineering Geology, vol. 42, no. 4, pp. 223–237, 1996.                   pp. 137–146, 2008.
[118] M. Al-Mukhtar, S. Khattab, and J.-F. Alcover, “Micro-               [135] S. Peethamparan, J. Olek, and J. Lovell, “Influence of
      structure and geotechnical properties of lime-treated ex-                 chemical and physical characteristics of cement kiln dusts
      pansive clayey soil,” Engineering Geology, vol. 139-140,                  (CKDs) on their hydration behavior and potential suitability
      pp. 17–27, 2012.                                                          for soil stabilization,” Cement and Concrete Research, vol. 38,
[119] S. Horpibulsuk, R. Rachan, A. Chinkulkijniwat,                            no. 6, pp. 803–815, 2008.
      Y. Raksachon, and A. Suddeepong, “Analysis of strength              [136] S. L. Cui, J. D. Wang, X. D. Wang, Y. F. Du, and X. P. Wang,
      development in cement-stabilized silty clay from micro-                   “Mechanical behavior and micro-structure of cement kiln
      structural considerations,” Construction and Building Ma-                 dust-stabilized expensive soil,” Arabian Journal of Geo-
      terials, vol. 24, no. 10, pp. 2011–2021, 2010.                            sciences, vol. 11, no. 17, p. 521, 2018.
[120] A. M. Idris and A. A. El-Zahhar, “Indicative properties             [137] D.-F. Lin, K.-L. Lin, M.-J. Hung, and H.-L. Luo, “Sludge ash/
      measurements by SEM, SEM-EDX and XRD for initial                          hydrated lime on the geotechnical properties of soft soil,”
      homogeneity tests of new certified reference materials,”                   Journal of Hazardous Materials, vol. 145, no. 1-2, pp. 58–64,
      Microchemical Journal, vol. 146, pp. 429–433, 2019.                       2007.
[121] R. L. Buhler and A. B. Cerato, “Stabilization of Oklahoma           [138] Q.-Y. Ma, Z.-M. Cao, and P. Yuan, “Experimental research
      expansive soils using lime and class C FLY ash,” in Pro-                  on microstructure and physical-mechanical properties of
      ceedings of the Problematic Soils and Rocks and in Situ                   expansive soil stabilized with fly ash, sand, and basalt fiber,”
      Characterization, pp. 1–10, Denver, Co, USA, February 2007.               Advances in Materials Science and Engineering, vol. 2018,
[122] C. Shi, “Studies on several factors affecting hydration and                Article ID 9125127, 13 pages, 2018.
      properties of lime-pozzolan cements,” Journal of Materials in       [139] F. E. Jalal, K. Shahzada, S. Saeed, I. Ahmad, and K. Khan,
      Civil Engineering, vol. 13, no. 6, pp. 441–445, 2001.                     “Stabalization of medium expansive soils in Pakistan using
[123] M. M. Zumrawi and A. A.-A. A. Babikir, “Laboratory study                  marble industrial waste and bagasse ash,” International
      of steel slag used for stabilizing expansive soil,” University Of         Journal of Earth Sciences and Engineering, vol. 10, no. 4,
      Khartoum Engineering Journal, vol. 6, no. 2, 2017.                        pp. 885–891, 2017.
22                                                                                      Advances in Materials Science and Engineering
[140] R. Alavéz-Ramı́rez, P. Montes-Garcı́a, J. Martı́nez-Reyes,                stabilized earth blocks,” Construction and Building Materials,
      D. C. Altamirano-Juárez, and Y. Gochi-Ponce, “The use of                  vol. 166, pp. 531–536, 2018.
      sugarcane bagasse ash and lime to improve the durability and       [157]   M. Temimi, M. A. Rahal, M. Yahiaoui, and R. Jauberthie,
      mechanical properties of compacted soil blocks,” Con-                      “Recycling of fly ash in the consolidation of clay soils,”
      struction and Building Materials, vol. 34, pp. 296–305, 2012.              Resources, Conservation and Recycling, vol. 24, no. 1, pp. 1–6,
[141] C. Okagbue and T. Onyeobi, “Potential of marble dust to                    1998.
      stabilise red tropical soils for road construction,” Engineering   [158]   I. Azim, J. Yang, S. Bhatta, F. Wang, and Q.-f. Liu, “Factors
      Geology, vol. 53, no. 3-4, pp. 371–380, 1999.                              influencing the progressive collapse resistance of RC frame
[142] A. Mahamedi and M. Khemissa, “Stabilization of an ex-                      structures,” Journal of Building Engineering, p. 100986, 2019.
      pansive overconsolidated clay using hydraulic binders,”            [159]   P. Sivapullaiah, Use of Solid Waste to Enhance Properties of
      HBRC Journal, vol. 11, no. 1, pp. 82–90, 2015.                             Problematic Soil of Karnataka, Indian Institute of Science,
[143] J. D. J. A. Baldovino, R. L. D. S. Izzo, E. B. Moreira, and                Bangalore, India, 2014.
      J. L. Rose, “Optimizing the evolution of strength for lime-        [160]   N.-J. Jiang, Y.-J. Du, and K. Liu, “Durability of lightweight
      stabilized rammed soil,” Journal of Rock Mechanics and                     alkali-activated ground granulated blast furnace slag (GGBS)
      Geotechnical Engineering, vol. 11, no. 4, pp. 882–891, 2019.               stabilized clayey soils subjected to sulfate attack,” Applied
[144] L.-X. Mao, Z. Hu, J. Xia et al., “Multi-phase modelling of                 Clay Science, vol. 161, pp. 70–75, 2018.
      electrochemical rehabilitation for ASR and chloride affected        [161]   A. A. Ashango and N. R. Patra, “Behavior of expansive soil
      concrete composites,” Composite Structures, vol. 207,                      treated with steel slag, rice husk ash, and lime,” Journal of
      pp. 176–189, 2019.                                                         Materials in Civil Engineering, vol. 28, no. 7, Article ID
[145] Q. T. Phung, N. Maes, and S. Seetharam, “Pitfalls in the use               06016008, 2016.
      and interpretation of TGA and MIP techniques for Ca-               [162]   J. T. Hatmoko and H. Suryadharma, “Shear behavior of
      leached cementitious materials,” Materials & Design,                       calcium carbide residue - bagasse ash stabilized expansive
      vol. 182, p. 108041, 2019.                                                 soil,” Procedia Engineering, vol. 171, pp. 476–483, 2017.
[146] F. S. Pereira, E. R. deAzevedo, E. F. da Silva et al., “Study of   [163]   M. De Beer, Behaviour of Cementitious Subbase Layers in
      the carbon dioxide chemical fixation-activation by guani-                   Bitumen Base Road Structures, University of Pretoria, Pre-
      dines,” Tetrahedron, vol. 64, no. 43, pp. 10097–10106, 2008.               toria, South Africa, 2009.
[147] A. Dulaimi, H. A. Nageim, F. Ruddock, and L. Seton,                [164]   K. Ganesan, K. Rajagopal, and K. Thangavel, “Evaluation of
      “Performance analysis of a cold asphalt concrete binder                    bagasse ash as supplementary cementitious material,” Ce-
      course containing high-calcium fly ash utilizing waste ma-                  ment and Concrete Composites, vol. 29, no. 6, pp. 515–524,
      terial,” Journal of Materials in Civil Engineering, vol. 29,
                                                                                 2007.
      no. 7, Article ID 04017048, 2017.
                                                                         [165]   W. Fedrigo, A. T. Visser, W. J. Steyn, and W. P. Núñez,
[148] S.-G. Lu, F.-F. Sun, and Y.-T. Zong, “Effect of rice husk
                                                                                 “Flexural behaviour of lightly Cement stabilised materials:
      biochar and coal fly ash on some physical properties of
                                                                                 South Africa and Brazil,” Road Materials and Pavement
      expansive clayey soil (Vertisol),” Catena, vol. 114, pp. 37–44,
                                                                                 Design, pp. 1–26, 2019.
      2014.
                                                                         [166]   K. C. P. Faria, R. F. Gurgel, and J. N. F. Holanda, “Recycling
[149] ASTM, Standard Specification for Coal Fly Ash and Raw or
                                                                                 of sugarcane bagasse ash waste in the production of clay
      Calcined Natural Pozzolan for Use in Concrete, ASTM, West
                                                                                 bricks,” Journal of Environmental Management, vol. 101,
      Conshohocken, PA, USA, 2012.
[150] Q. Zeng, K. Li, T. Fen-chong, and P. Dangla, “Determination                pp. 7–12, 2012.
                                                                         [167]   L. D. Nguyen, B. Fatahi, and H. Khabbaz, “A constitutive
      of cement hydration and pozzolanic reaction extents for fly-
      ash cement pastes,” Construction and Building Materials,                   model for cemented clays capturing cementation degrada-
      vol. 27, no. 1, pp. 560–569, 2012.                                         tion,” International Journal of Plasticity, vol. 56, pp. 1–18,
[151] B. Lin and A. B. Cerato, “Applications of SEM and ESEM in                  2014.
      microstructural investigation of shale-weathered expansive         [168]   A. K. Yadav, K. Gaurav, R. Kishor, and S. Suman, “Stabi-
      soils along swelling-shrinkage cycles,” Engineering Geology,               lization of alluvial soil for subgrade using rice husk ash,
      vol. 177, pp. 66–74, 2014.                                                 sugarcane bagasse ash and cow dung ash for rural roads,”
[152] B. R. Phani Kumar and R. S. Sharma, “Effect of fly ash on                    International Journal of Pavement Research and Technology,
      engineering properties of expansive soils,” Journal of Geo-                vol. 10, no. 3, pp. 254–261, 2017.
      technical and Geoenvironmental Engineering, vol. 130, no. 7,       [169]   S. Horpibulsuk, C. Phetchuay, and A. Chinkulkijniwat, “Soil
      pp. 764–767, 2004.                                                         stabilization by calcium carbide residue and fly ash,” Journal
[153] S. Kommu, S. S. Asadi, and A. V. S. Prasad, “Leaching be-                  of Materials in Civil Engineering, vol. 24, no. 2, pp. 184–193,
      havior and strength characteristics of black cotton soil sta-              2011.
      bilized with fly ash,” Materials Today: Proceedings, vol. 5,        [170]   C. Subhacini, M. Ranjitha, S. Dhanapal, and K. A. Prakash,
      no. 9, pp. 17974–17981, 2018.                                              “Expansive soil stabilization using waste from sugarcane
[154] A. R. Pourkhorshidi, M. Najimi, T. Parhizkar, F. Jafarpour,                Industry,” Journal for Studies in Management and Planning,
      and B. Hillemeier, “Applicability of the standard specifica-                vol. 1, no. 3, pp. 345–352, 2015.
      tions of ASTM C618 for evaluation of natural pozzolans,”           [171]   K. Somna, C. Jaturapitakkul, and P. Kajitvichyanukul,
      Cement and Concrete Composites, vol. 32, no. 10, pp. 794–                  “Microstructure of calcium carbide residue–ground fly ash
      800, 2010.                                                                 paste,” Journal of Materials in Civil Engineering, vol. 23,
[155] C. Gupta and R. K. Sharma, “Influence of marble dust, fly ash                no. 3, pp. 298–304, 2010.
      and beas sand on sub grade characteristics of expansive soil,”     [172]   S. Vichan and R. Rachan, “Chemical stabilization of soft
      Journal of Mechanical and Civil Engineering, pp. 13–18, 2014.              Bangkok clay using the blend of calcium carbide residue and
[156] D. C. Sekhar and S. Nayak, “Utilization of granulated blast                biomass ash,” Soils and Foundations, vol. 53, no. 2,
      furnace slag and cement in the manufacture of compressed                   pp. 272–281, 2013.
Advances in Materials Science and Engineering                           23