CLAY-02588; No of Pages 6
Applied Clay Science xxx (2013) xxx–xxx
Contents lists available at SciVerse ScienceDirect
Applied Clay Science
journal homepage: www.elsevier.com/locate/clay
Research paper
Characterization of alkali activated kaolinitic clay
Faten Slaty a, Hani Khoury a, Jan Wastiels b, Hubert Rahier c,⁎
a
b
c
Department of Geology, University of Jordan, Jordan
Department of Mechanics of Materials and Constructions, Vrije Universiteit Brussel, Belgium
Department of Physical Chemistry and Polymer Science, Vrije Universiteit Brussel, Belgium
a r t i c l e
i n f o
Article history:
Received 3 October 2011
Received in revised form 6 February 2013
Accepted 12 February 2013
Available online xxxx
Keywords:
Characterization
Compressive strength
Alkali activated cement
Kaolinite
a b s t r a c t
Low cost building materials have been developed by chemical activation of Jordanian Hiswa kaolinite with a
sodium hydroxide solution. The effect of the main parameters of synthesis and processing on the development of compressive strength was studied. An investigation of the physical, thermal, mineralogical and microstructural properties was performed. A compressive strength of 32 MPa was obtained for a mixture
cured at 80 °C for 24 h. The mineralogical and microstructural results on the hardened material indicate
the formation of sodium zeolite phases and feldspathoids with a Na/Al ratio of one. The high compressive
strength observed is directly related to the formation of the new phases that fill the pore spaces and bind
the matrix.
© 2013 Published by Elsevier B.V.
1. Introduction
The production of cement clinker produces a high amount of CO2: its
main raw material is calcium carbonate which releases CO2 upon
heating, while the heating to elevated temperatures consumes important amounts of fuel. The enormous amount of concrete used worldwide leads to the figure that the production of cement contributes
more than 5% to the global anthropogenic emission of carbon dioxide
(Habert et al., 2011). It is known that geopolymers, among other alternatives, can replace Portland cement while having a smaller ecological
footprint (Habert et al., 2011; Steveson and Sagoe-Crentsil, 2005). The
CO2 production during calcination of clay minerals is much smaller
than what is obtained from Portland cement as the calcination of clay
minerals is a dehydroxylation instead of a decarbonation.
The dehydroxylation occurs at a lower temperature, thus, costing
less energy (Gartner, 2011). Geopolymerization is the reaction of a
solid aluminosilicate with a liquid alkali component as an activator
agent, forming an inorganic polymeric network of alkali aluminosilicates (Ingles, 1970; Rahier et al, 2007; Rovnanik, 2010; Rowels and
O'Connor, 2003; Van Jaarsveld et al., 2002; Xu and Van Deventer,
2000). The solid aluminosilicates normally used are metakaolinite
(calcined clay mineral), fly ash (dust from coal incineration), blast
furnace slag (quenched slag from iron making), or other waste products from power stations and mining processes: their amorphous
structure can be transformed under the action of the alkaline
⁎ Corresponding author. Tel.: +32 26293277.
E-mail addresses:
[email protected] (F. Slaty),
[email protected]
(J. Wastiels),
[email protected],
[email protected] (H. Rahier).
activator. Several names are given to the materials obtained via alkali
activation (Xu et al., 2008). Besides geopolymers, inorganic polymers
(Rahier et al., 1996) and mineral polymers (Patfoort et al., 1989;
Theys et al., 1991) are also used although they are considered to be
of the same class of materials. The materials produced at lowtemperature by activation using an alkaline liquid component can
range from completely amorphous to crystalline products (analogues
of natural zeolites); the alkaline liquids contain group 1 metal ions
usually sodium and/or potassium. The water in the geopolymer mixtur
provides a reaction medium and assures the workability of the mixture
during mixing and handling. Filler materials may be used to enhance desired properties including mechanical strength and density.
An environmental drawback of geopolymers is the use of silicate
solutions. These are prepared by dissolution of a glass that is formed
at elevated temperature, thus with a considerable emission of greenhouse gasses (Habert et al., 2011; Steveson and Sagoe-Crentsil, 2005).
Using a NaOH solution instead of a silicate solution and kaolinite instead of metakaolinite would thus greatly reduce the environmental
impact of the construction material produced. The term alkali activation will be used here instead of geopolymerization. The reason is that
the raw material (kaolinite) and the product are (partly) crystalline,
contrary to the nature of geopolymers. Another difference with the
above consists in the fact that no thermal treatment has to be
performed on the solid aluminosilicate; it can be used in its naturally
occurring state and transformed by simple technological means,
which allows the method to fit into the appropriate technology for
building as defined by Schumacher (1973). The elements stated
above contribute to the economic viability of the alkali activation of
kaolinite, with respect to cement.
0169-1317/$ – see front matter © 2013 Published by Elsevier B.V.
http://dx.doi.org/10.1016/j.clay.2013.02.005
Please cite this article as: Slaty, F., et al., Characterization of alkali activated kaolinitic clay, Applied Clay Science (2013), http://dx.doi.org/10.1016/
j.clay.2013.02.005
2
F. Slaty et al. / Applied Clay Science xxx (2013) xxx–xxx
Alkali activation of clay soils has been known for a long time, for
instance road stabilization in developing countries (Cuisinier et al.,
2009; Gera and Volkov, 2000; Hossain and Mol, 2011; Xeidakis,
1996). The fact that zeolites can be formed from kaolinite and NaOH
solutions is also known (Breck, 1974). The literature on this topic is
however scarce and few studies have been carried out to improve
these materials in order to obtain a quality that is good enough to
use as construction materials, which can replace fired bricks, tiles or
cementitious products (Shi et al., 2006; Yousef et al., 2012). The
same technology has also been used to consolidate earthen architectural remains (Elert et al., 2008). Currently, an increasing number of
investigations are undertaken to search for a sustainable replacement
of ordinary Portland cement. A recent development by Lemougna et
al. (2011) used volcanic ash in combination with alkaline solutions.
The main goal of this research is to characterize the material
resulting from alkali activated kaolinite as is found in the Hiswa
area in South Jordan. The clay deposits in Jordan are widely used
and the extracted clays have a low price (Khoury, 2002). In this
paper the optimal composition and cure conditions will be discussed.
A structural characterization with XRD, SEM and NMR is carried out.
2. Experimental procedure
A kaolinite (Kaol) from Jordanian Hiswa is used as aluminosilicate
source. A silica sand (SiSand) from south Jordan is used as a filler material and NaOH purchased from Merck with 99% purity is used to
prepare the alkali solution with distilled water. The SiSand has a particle size distribution between 90 and 250 μm. Preparation of the
samples was performed in three steps:
1- Mixing: the amount of Kaol and SiSand were mixed using a laboratory mechanical overhead mixer. The alkali solution was prepared
by mixing NaOH and distilled water in a closed plastic bottle to
avoid evaporation. The cooled NaOH solution was added gradually
to the Kaol/SiSand mixture and mixed for 2 min at 100 rpm and
10 min at 200 rpm to get an optimum homogeneity.
2- Molding: the mixture was put into a stainless steel cylinder mold
(50 ∗ 25 mm) and compacted with a pressure of 16 MPa by using
a hydraulic compressor; the mold was then removed and the sample weighed. With each mixture at least 3 samples were prepared.
3- Curing: the uncovered samples were placed in a ventilated oven at
80 °C for 24 h, unless specified otherwise.
The compressive strength of the samples was measured by using a
CONTROLS testing machine (Model T106 modified to suit standard
testing), where the load was applied and increased by a displacement
rate of 3 mm/min. An average of three samples per measurement was
taken.
2.1. Optimization of ratio
The optimal component ratio was studied by preparing two series of
samples with different ratios of NaOH and SiSand. In this work, the
amount of distilled water added was taken as the plasticity limit for
the mixture of Kaol and SiSand. As a result the mixture does not flow
and must be compressed. The optimal ratio of the other components
in the mixture was determined depending on the best compressive
strength as will be highlighted in the Results and discussion section.
Two series were prepared: One with six samples with different NaOH
ratios and a second series with four samples with different SiSand ratios. The mass ratios of NaOH vary from 8, 12, 14, 16, 18, to 20 with respect to 100 Kaol mass%, 50 SiSand mass% and 22 H2O mass%. The
samples were cured at 80 °C for 24 h. The second series had different
SiSand ratios of 25, 50, 100, and 150 with respect to 100 Kaol mass%,
16 NaOH mass% and 22 H2O mass% and also cured under the same
conditions.
2.2. Optimization of curing conditions
The effect of curing time on compressive strength was studied by
preparing one series cured at 80 °C at six different times for 6, 12, 18,
24, 48 and 72 h. Another series was cured 24 h at four different temperatures at 50, 60, 70, and 80 °C for 24 h to check the influence of
temperature.
Four series of the optimized samples without SiSand filler and
with sand filler were prepared to get an idea of the influence of
sand on the difference between wet and dry samples. The samples
without sand also served for structural and molecular analyses. One
series was left under lab conditions and another series was immersed
in de-mineralized water to test the stability of samples in wet conditions. Unconfined compressive strength was measured for all series
after three days.
The compressive strength of the samples was measured by using a
modified motorized CBR device, at a displacement rate of 3 mm/min.
Three similar samples are tested and the average of the three measurements is taken.
2.3. Characterization of the raw materials and optimized material
In order to identify the major elements of Kaol and SiSand, X-ray
fluorescence spectroscopy was done on powdered samples using a
Bruker System S4 Pioneer.
The mineralogical components of raw Kaol and optimized samples
were investigated by X-ray diffraction (XRD), using a Siemens 500
Kristalloflex instrument, with Cu Kα radiation (λ = 1.5418 Å) and a
scan rate of 2°/min.
The thermal behavior was determined by TG/DTA analysis. The
analysis was done by using a Netzsch STA 409 thermal analyzer. The
samples (approximately 36 mg, size b 425 μm) were heated in an alumina cup at a rate of 20 °C/min, starting from 50 °C up to a maximum
temperature of 1000 °C using N2 as a purge gas.
The structural details were studied by SEM/EDX and NMR. The
platinum coated samples of raw Kaol and the optimized samples
were scanned using a high-energy beam of primary electrons in a raster scan pattern using model FEI-INSPECT-F50. 29Si and 27Al spectra
were obtained using a Bruker AC250 spectrometer that operates at
49.70 MHz and 65.18 MHz for the 29Si and 27Al resonance frequencies,
respectively. For more details on the MAS NMR conditions see Ref.
(Rahier et al., 1997).
3. Results and discussion
3.1. Characterization of the raw material
The composition, expressed in oxides, for the Kaol and SiSand is
given in Table 1. Silica (SiO2) and alumina (Al2O3) are the major components for Kaol, representing 74% from the total content. For SiSand,
the results show that SiO2 forms about 99% from the total content,
which was expected as the sand was expected to be almost pure.
The presence of 0.5% Al2O3 is attributed to an insignificant amount
of clay impurities.
Fig. 1 shows the X-ray diffractogram of the raw Kaol. The chart indicates that the mineralogical components of Kaol are mainly kaolinite
(Al2Si2O5(OH)4) and quartz (SiO2). Muscovite/illite (KAl2Si3AlO10(OH)2)
and hematite (Fe2O3) are present as minor components with traces of alunite (KAl3(SiO4)2(OH)6). Gypsum (CaSO4·2H2O) is present as a filler
material in joints and fractures of the deposit (Al-Momani, 2000).
Under the supposition that Al2O3 is only present in kaolinite, the amount
of kaolinite in Kaol would be 64 m% based on the results in Table 1.
The Kaol has a very fine particle size (picture not shown). Quartz
appears as colorless particles, medium to fine grained, subrounded
to angular shaped, and fractured pattern. Iron oxides (brown patches
Please cite this article as: Slaty, F., et al., Characterization of alkali activated kaolinitic clay, Applied Clay Science (2013), http://dx.doi.org/10.1016/
j.clay.2013.02.005
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F. Slaty et al. / Applied Clay Science xxx (2013) xxx–xxx
Table 1
Major element composition of Jordanian Hiswa Kaol and SiSand.
Major oxides
Al2O3
CaO
Fe2O3
K2O
L.O.I
MgO
MnO
Na2O
P2O5
SiO2
SO3
TiO2
Kaol
(wt.%)
SiSand
(wt.%)
25
0.7
7.5
1.4
12
0.2
0.0
0.2
0.2
49
2.9
0.9
0.1
0.0
0.00
0.00
0.0
0.1
0.0
99
0.0
0.1
0.5
0.2
of hematite) are present as a cement material. Some black spots could
not be identified.
Fig. 2 shows the TG/DTA curves of the Kaol sample. The TG curve
indicates that the sample has lost about 1% of water as moisture content. The next mass loss step around 500–600 °C accounting for 9.4%
is due to the removal of the OH groups of kaolinite resulting in
metakaolinite. From this mass loss the amount of kaolinite can be calculated being 67%. This is somewhat higher than the amount deduced
from XRF. The DTA curve shows three endothermic peaks: the first
one appears in the range of 100–150 °C, corresponding to the moisture loss also seen with TGA. The second peak appears at about
565 °C and is mainly attributed to the dehydroxylation of kaolinite
transforming into metakaolinite (Caglar et al., 2007; Kakali et al.,
2001; Zuhua et al., 2009). This dehydroxylation is the removal of hydroxyl groups from Al\OH bonds (Rocha and Klinowski, 1990). The
third endothermic peak appears at about 970 °C. At this temperature
the dehydroxylation goes to the end and new more stable phases are
formed. The new phases are a mixture of amorphous materials such as
mullite, silica–alumina and a small amount of unreacted metakaolinite.
3.2. Optimization of mixing ratios
NaOH is used as an activator for the aluminosilicate material. The
OH − concentration of the activator is an important parameter. The alkalinity is primarily necessary for the disintegration of the strong aluminosilicate layer (Sathia et al., 2008). As the reactivity of kaolinite is
much lower than for thermally activated clays, such strong alkaline
solutions need to be used (Fernandez et al., 2011). On the other
hand, Na + serves as the counter ion for the negative charge introduced by each AlO4 tetrahedron formed (see section 3.4). Fig. 3
shows that the compressive strength increases almost linearly with
the NaOH content. The highest compressive strength value obtained
was 33 MPa, for the series that contains 16 parts of NaOH. At higher
NaOH content the compressive strength again decreases.
Filler materials like sand reduce cracking and decrease the porosity of the composite. Fillers also reduce the quantity of binder paste
making the resultant material less expensive. The effect of adding
sand grains to the reaction mixture on the compressive strength is
shown in Fig. 4. Increasing the sand content improves the workability
of the mixture. The best compressive strength values are obtained for
3.3. Optimization of curing conditions
The effect of the curing temperature on compressive strength is
shown in Fig. 5. The maximum compressive strength value was
32 MPa, for the series cured at 80 °C for 24 h. The increase in curing
temperature from 60 °C to 80 °C more than doubles the compressive
strength. In general, temperature substantially increases the reaction
rate.
The effect of curing time on compressive strength is shown in
Fig. 6. The compressive strength increases with the increase of curing
time. A maximum compressive strength of 48 MPa was attained after
48 h of thermal curing. After 48 h, no further gain in strength was observed. Therefore, heat-curing time needs not to be more than 48 h at
80 °C in practical applications.
To check the stability of the samples under wet conditions some
optimized samples with and without sand filler were tested under
dry and wet conditions 7 days after curing for 24 h at 80 °C. The average compressive strength value of the samples without SiSand
was 23 MPa in dry conditions and 13 MPa in wet conditions; whereas
the average compressive strength value for the samples with SiSand
was 41 MPa in dry conditions and 24 MPa in wet conditions. Note
that the compressive strength still increased from 32 to 41 MPa during storage for 7 days at room temperature after the curing.
As a general rule, the samples made with SiSand exhibited higher
strength values than the samples made without SiSand. The strength
of all mixtures has decreased by half under wet conditions. This can
be partly attributed to the absorption of water by the remaining kaolinite (Reddy and Kumar, 2009), and partly by the hydrolysis of the
Si\O\Si bonds in the newly formed structure. However, this drop
in strength is not caused by degradation of the material; since repeated drying–wetting cycles do not further diminish the strength, this
observation however, will be discussed at greater length in a subsequent paper.
Q:Quartz
K:Kaolinite
M/I:Muscovite/Illite
G:Gypsum
H:Hematite
A:Alunite
Q
K
a SiSand:Kaol ratio of 0.5 to 1. Remark that the sample in Fig. 3 with
16 parts of NaOH has the same composition as the sample one in
Fig. 4 with 50 parts of SiSand. They were however made from a different batch. This shows the deviations between several batches (compressive strength of 28 compared to 33 MPa).
K
Q
M/I
G
M/I
10
A
M/I
20
H
A
M/I Q K Q
H
H
G G H
30
40
Q
H
Q
QH K
50
Q K
H
Q
60
2-Theta (°)
Fig. 1. XRD spectrum of the raw Kaol.
Fig. 2. TG/DTA curves of the raw Kaol.
Please cite this article as: Slaty, F., et al., Characterization of alkali activated kaolinitic clay, Applied Clay Science (2013), http://dx.doi.org/10.1016/
j.clay.2013.02.005
4
40
40
35
35
Compressive strength (MPa)
Compressive strength (MPa)
F. Slaty et al. / Applied Clay Science xxx (2013) xxx–xxx
30
25
20
15
10
5
30
25
20
15
10
5
0
0
5
10
15
20
0
25
0
NaOH (in parts)
20
40
60
80
100
Temperature (°C)
Fig. 3. NaOH ratio vs. compressive strength. Samples with composition 100 Kaol, 50
SiSand and 22 H2O and cured for 24 h at 80 °C.
Fig. 5. Curing temperature vs. compressive strength. Samples with composition 100
Kaol, 100 SiSand, 16 NaOH, and 22 H2O and cured for 24 h.
3.4. Structural characterization of the optimized material
Fig. 7 shows the X-ray diffractogram of the optimized alkaliactivated material. The chart indicates that the reaction of kaolinite
with NaOH results mainly in new alkaline sodium aluminosilicate
phases. These phases are Na-zeolitic minerals namely: phillipsite
((Na,K,Ca)1–2(Si,Al)8O16·6H2O) and natrolite (Na2Al2Si3O8.2H2O). A
feldspathoid phase of hydroxysodalite (Na2Si2Al2O5(H2O)6) is also
identified. Quartz occurs as a major phase in the sample due to the
added SiSand filler along with the remains of kaolinite, muscovite/illite, and hematite from the raw material. Remark that in these minerals the ratio Na +/Al 3+ = 1 as is the case for geopolymers (Rahier
et al., 1996). If the ratio of Na/Al = 1 is valid for all the reaction products formed, including any amorphous products, then the amount of
kaolinite consumed can be calculated since 2 mol of NaOH will react
with 1 mol of kaolinite (Al2O3·2SiO2·2H2O). In our samples 16
parts of NaOH were used to 100 parts of Kaol. Taking account of the
molar mass 16 parts of NaOH are only enough for to react with 52
parts of Kaol. From the characterization of the clay an amount of
64% (XRF) to 67% (TGA) of kaolinite is present in the Kaol while
only 52% can react. As a consequence, some kaolinite will remain
unreacted.
Fig. 8 shows the TG/DTA curves of the optimized sample. The TG
curve indicates that the sample loses about 1.45% water between 80
and 340 °C. This is accompanied by an endothermic signal in DTA. The
second step shows the transformation of kaolinite to metakaolinite as
the remaining OH groups are eliminated. This can be observed in the
mass loss as well as in the heat flow signal. An attempt was made to determine the amount of unreacted kaolinite via the mass loss by
dehydroxylation of unreacted kaolinite. However, the mass loss in Fig.
8 shows that this step is higher than expected. This is explained by an
overlap with some newly formed phase. As such the amount of residual
kaolinite cannot be measured accurately. The loss of this chemically
bound water will make the material less suited for elevated temperature applications.
The third endothermic peak appears at about 970 °C and does not
finish below 1000 °C. It is likely this corresponds to the transformation of metakaolinite into more stable phases, but also to the decomposition of other minerals that are present such as carbonates and
sulfates (Rocha and Klinowski, 1990).
Fig. 9 shows the SEM micrograph and EDX microanalysis for the
new sodium aluminosilicate phase that grows as a result of the reaction. The new phase occurs mainly as rosettes of spherulitic aggregates filling the pore spaces and binding with the other particles.
The relicts of kaolinite indicate that the reaction is not complete,
confirming the XRD and TG/DTA results. EDX microanalysis (arrow
in Fig. 9) of a new phase indicates the presence of aluminum (Al),
40
70
60
Compressive strength (MPa)
Compressive strength (MPa)
35
30
25
20
15
10
50
40
30
20
10
5
0
0
0
25
50
75
100
125
150
Sand ratio
Fig. 4. Sand ratio vs. compressive strength. Samples with composition 100 Kaol, 16
NaOH and 22 H2O and cured for 24 h at 80 °C.
0
20
40
60
80
Time (hours)
Fig. 6. Curing time vs. compressive strength. Samples with composition 100 Kaol, 100
SiSand, 16 NaOH, and 22 H2O and cured at 80 °C.
Please cite this article as: Slaty, F., et al., Characterization of alkali activated kaolinitic clay, Applied Clay Science (2013), http://dx.doi.org/10.1016/
j.clay.2013.02.005
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F. Slaty et al. / Applied Clay Science xxx (2013) xxx–xxx
Q: Quartz
K: Kaolinite
H: Hematite
M/I: Muscovite/ Illite
P: Phillipsite
S: Hydroxysodalite
N: Natrolite
A: Alunite
Q
a
Raw kaolinite
Geopolymer
Q
M/I
2
10
S
K+
P
M/I
+ K
N +
N
20
Q
+
Q N
K
S
+ S
N
M/I
+
S
H H
P
30
Q
Q
Q
Q
Q
Q
Q
H
40
50
K
H
AH
60
70
2-Theta (°)
Fig. 7. XRD spectrum of the optimized sample. Samples with composition 100 Kaol,
100 SiSand, 16 NaOH, and 22 H2O and cured at 80 °C for 24 h.
-20
-60
-100
ppm
b
Raw kaolinite
Geopolymer
Fig. 8. TG/DTA curves of the optimized sample. Samples with composition 100 Kaol,
100 SiSand, 16 NaOH, and 22 H2O and cured at 80 °C for 24 h.
silicon (Si), potassium (K) and sulfur (S) originating from Kaol, while
the presence of sodium (Na) is due to the addition of alkali activator
(NaOH).
Fig. 10a describes the chemical shifts of 29Si MAS NMR for a sample without SiSand compared to the raw Kaol. The 29Si spectrum
shows that Kaol shows a single resonance at − 91 ppm characteristic
150
50
-50
ppm
Fig. 10. a) 29Si MAS NMR spectrum and b) 27Al MAS NMR of Kaol and optimized sample. Samples with composition 100 Kaol, 100 SiSand, 16 NaOH, and 22 H2O and cured
at 80 °C for 24 h.
Fig. 9. SEM/EDX of the optimized sample. Samples with composition 100 Kaol, 100 SiSand, 16 NaOH, and 22 H2O and cured at 80 °C for 24 h.
Please cite this article as: Slaty, F., et al., Characterization of alkali activated kaolinitic clay, Applied Clay Science (2013), http://dx.doi.org/10.1016/
j.clay.2013.02.005
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F. Slaty et al. / Applied Clay Science xxx (2013) xxx–xxx
for the Si in the SiO4 layer of kaolinite (Rocha and Klinowski, 1990).
This Si is linked over an oxygen bridge to three other Si atoms with
mainly covalent bonds. The resonance at −108 ppm which is characteristic of Si covalently linked to four other Si atoms is related to the quartz
in the raw material. In the reacted sample, there is a new separate resonance observed at −87 ppm. This resonance is related to newly formed
sodium aluminosilicate phases. The 27Al spectrum in Fig. 10b shows a
broad resonance at −5 ppm assigned to 6-coordinated Al in Kaol (Xu
and Van Deventer, 2000). This again shows that the kaolinite is not
completely consumed. The new phases show a resonance at 57 ppm attributed to 4-coordinated Al. This transformation to tetrahedral Al is
comparable to the geopolymerization process.
4. Conclusions
The Jordanian clay from the south Hiswa area is predominantly
composed of kaolinite and quartz, in addition to a considerable
amount of muscovite/illite, hematite and possibly alunite and gypsum. Alkali activation of the raw kaolinite with an aqueous solution
of sodium hydroxide was studied. The compressive strength and the
workability of the formed samples are influenced by the proportions
and properties of the components of the reaction mixture. An increase of silica sand content up to a one to one ratio with respect to
kaolinite has led to improvements in the workability of the mixture
and an increase in the compressive strength. By optimizing the ratios
and curing conditions a compressive strength of up to 48 MPa under
dry conditions and 23 MPa under wet conditions was obtained. This
loss of compressive strength under wet conditions is acceptable. A
major decline in the kaolinite content was confirmed by several
analytical techniques. However, it was not possible to obtain a quantitative measurement for the amount of kaolinite remaining. The
crystalline reaction products were found to be sodium aluminosilicate phases from the zeolitic group, namely phillipsite, atrolite and
hydroxysodalite. These phases fill the pore spaces and bind the matrix, this differs from many geopolymers, as these phases contain
chemically bound water. In a following paper the durability of this
material will be studied.
Acknowledgments
The authors are indebted to VLIR-UOS for the financial support via
the project Chemical stabilization of natural geomaterials for construction and industrial applications, number ZEIN2006PR33.
References
Al-Momani, T., 2000. Characterization, Industrial Utilization And Environmental Impact Of The Hiswa Clay Deposits, South Jordan, Ph.D. Thesis, University of Jordan,
Amman.
Breck, D.W., 1974. Zeolite Molecular Sieves. J. Wiley, New York.
Caglar, B., Afsin, B., Tabak, A., 2007. Benzamide species retained by DMSO composites at
a kaolinite surface. Journal of Thermal Analysis and Calorimetry 87, 429–432.
Cuisinier, O., Deneele, D., Masrouri, F., 2009. Shear strength behaviour of compacted
clayey soils percolated with an alkaline solution. Engineering Geology 108,
177–188.
Elert, K., Sebastián, E., Valverde, I., Rodriguez-Navarro, C., 2008. Alkaline treatment of
clay minerals from the Alhambra formation: implications for the conservation of
earthen architecture. Applied Clay Science 39, 122–132.
Fernandez, R., Martirena, F., Scrivener, K.L., 2011. The origin of the pozzolanic activity
of calcined clay minerals: a comparison between kaolinite, illite and montmorillonite. Cement and Concrete Research 41, 113–122.
Gartner, E., 2011. Industrially interesting approaches to “low-CO2” cements. Cement
and Concrete Research 34, 1489–1498.
Gera, L.N., Volkov, F.E., 2000. Effect of alkaline-earth metal cations on stabilization of
loessial and clayey soil using alkalizing. In: Nakase, A., Tsuchida, T. (Eds.), Coastal
Geotechnical Engineering in Practice, Vol. 1, pp. 593–597.
Habert, G., d'Espinose de Lacaillerie, J.B., Roussel, N., 2011. An environmental evaluation of geopolymer based concrete production: reviewing current research trends.
Journal of Cleaner Production 19, 1229–1238.
Hossain, K.M.A., Mol, L., 2011. Some engineering properties of stabilized clayey soils incorporating natural pozzolans and industrial wastes. Construction and Building
Materials 25, 3495–3501.
Ingles, O.G., 1970. Mechanism of clay stabilization with inorganic acids and alkalis.
Australian Journal of Soil Research 8, 81–95.
Kakali, T., Perraki, S., Sivilis, T., Badogiannis, E., 2001. Thermal treatment of kaolin: the
effect of mineralogy on the pozzolanic activity. Applied Clay Science 20, 73–80.
Khoury, H., 2002. Clays and Clay Minerals in Jordan. Publications of University of
Jordan, Amman.
Lemougna, N.P., MacKenzie, K.J.D., Melo, U.F.C., 2011. Synthesis and thermal properties of
inorganic polymers (geopolymers) for structural and refractory applications from volcanic ash. Ceramics International. http://dx.doi.org/10.1016/j. ceramint.2011.05.002.
Patfoort, G., Wastiels, J., Bruggeman, P., Stuyck, L., 1989. Mineral polymer matrix composites. In: Brandt, A.M., Marshall, I.H. (Eds.), Brittle Matrix Composites, 2, pp.
587–592.
Rahier, H., Van Mele, B., Biesemans, M., Wastiels, J., Wu, X., 1996. Low-temperature
synthesized aluminosilicate glasses.1. Low-temperature reaction stoichiometry
and structure of a model compound. Journal of Materials Science 31, 71–79.
Rahier, H., Simons, W., Van Mele, B., Biesemans, M., 1997. Low-temperature synthesized aluminosilicate glasses. Part III: influence of the composition of the silicate
solution on production, structure and properties. Journal of Materials Science 32,
2237–2247.
Rahier, H., Wastiels, J., Biesemans, M., Willlem, R., Van Assche, G., Van Mele, B., 2007. Reaction mechanism, kinetics and high temperature transformations of geopolymers.
Journal of Materials Science 42, 2982–2996.
Reddy, V., Kumar, P., 2009. Role of clay content and moisture on characteristics of cement stabilized rammed earth. Proc. 11th Int. Conference Non-Conventional Materials and Technologies. Indian institute of science, Bangalore, India, Bath, UK.
Rocha, J., Klinowski, J., 1990. 29Si and 27Al magic-angle-spinning NMR studies of the thermal transformation of kaolinite. Physics and Chemistry of Minerals 17, 179–186.
Rovnanik, P., 2010. Effect of curing temperature on the development of hard structure of
metakaolin-based geopolymer. Construction and Building Materials 24, 1176–1183.
Rowels, M., O'Connor, B., 2003. Chemical optimization of the compressive strength of aluminosilicate geopolymers synthesized by sodium silicate activation of metakaolinite.
Journal of Materials Chemistry 13, 1161–1165.
Sathia, R., Ganesh Babu, K., Santhanam, M., 2008. Durability study of low calcium fly
ash geopolymer concrete. The 3rd ACF International Conference-ACF/VCA. Indian
Institute of Technology Madras, Chennai, India.
Schumacher, E.T., 1973. Small Is Beautiful, Economics As If People Mattered.
Shi, C., Krivenko, P.V., Roy, D., 2006. Alkali Activated Cements and Concretes. Taylor &
Francis, New York.
Steveson, M., Sagoe-Crentsil, K.K., 2005. Relationships between composition, structure
and strength of inorganic polymers: Part 2 — fly ash-derived inorganic polymers.
Journal of Materials Science 16, 4247–4259.
Theys, F., Faignet, S., Patfoort, G., Wastiels, J., 1991. In: Brandt, A.M., Marshall, I.H.
(Eds.), Fracture mechanical characterization of mineral polymer matrix composites: Brittle Matrix Composites, 3, pp. 383–392.
Van Jaarsveld, J.G.S., Van Deventer, J.S.J., Lukey, G.C., 2002. The effect of composition
and temperature on the properties of fly ash- and kaolinite-based geopolymers.
Chemical Engineering Journal 89, 63–73.
Xeidakis, G.S., 1996. Stabilization of swelling clays by Mg(OH)2. Factors affecting
hydroxy-Mg-interlayering in swelling clays. Engineering Geology 44, 93–106.
Xu, H., van Deventer, J.S.J., 2000. The geopolymerisation of alumino-silicate minerals.
International Journal of Mineral Processing 59, 247–266.
Xu, H., Provis, J.L., van Deventer, J.S.J., Krivenko, P.V., 2008. Characterization of aged slag
concretes. ACI Materials Journal 105, 131–139.
Yousef, R.I., El-Eswed, B., Alshaaer, M., Khalili, F., Rahier, H., 2012. Incomplete
geopolymerization of kaoline in alkali solution using zeolitic tuff or silica sand filler. Ceramics International 38, 5061–5067.
Zuhua, Z., Xiao, X., Huajun, H., Sudong, H., Yue, C., 2009. Activating process of
geopolymer. Kaolinite Materials Science 24, 132–136.
Please cite this article as: Slaty, F., et al., Characterization of alkali activated kaolinitic clay, Applied Clay Science (2013), http://dx.doi.org/10.1016/
j.clay.2013.02.005