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ORIGINAL ARTICLE
Long-term behavior of lime-stabilized kaolinite clay
Aydın Kavak • Gokhan Baykal
Received: 22 August 2010 / Accepted: 8 October 2011 / Published online: 28 October 2011
� Springer-Verlag 2011
Abstract Clay soils create many problems for highway
construction and they have to be replaced or improved by
stabilization for satisfactory performance. Lime stabiliza-
tion is a well-established technique to improve the per-
formance of clays. Cementitious minerals form upon
mixing of clay with lime causing an improvement in
strength and durability. In the study, the changes in the
microfabric of long-term cured lime-stabilized kaolinite
clay using X-ray diffraction pattern, scanning electron
microscope and unconfined compressive strength (UCS) is
presented. Unconfined compression test samples at two
different lime contents (4 and 12% by weight) were pre-
pared and cured in a humidity room for long time curing.
The UCS of pure kaolinite was originally 125 kPa, which
increased to 1,015 kPa after 1 month and to 2,640 kPa (21
times the initial value) after 10 years for cured lime-sta-
bilized kaolinite samples. Similar long-term strength
increases were also observed for stabilized kaolinite with
12% lime. Calcium aluminate silicate hydrate minerals
were detected in the structure of the kaolinite. This sug-
gests pozzolanic reactions with lime stabilization may
continue in the long-term for up to 10 years.
Keywords Lime stabilization � Lime � Soil �Stabilization � Clay � Kaolinite
Introduction
Environmental impact of road construction on the ecology
is detrimental due to need for large volume of fill material.
When the performance in the site is not suitable for road
construction, borrow material is needed which is dredged
from nearby river or mined from surrounding pits. Instead
of using borrow material, it may be more economical to use
in situ soil provided that the performance criteria are met.
Lime stabilization of clay soil is widely done to improve
the performance of in situ soil to the level that, the required
performance criteria are satisfied. Improvement of the
existing soil reduces the need for cut and fills works,
minimizing the environmental impacts.
Soil stabilization by lime refers to the admixture of this
material in the form of calcium hydroxide to the soil and
the compaction of the mixture at the optimum water con-
tent. These chemical processes modify the soil structure
whereby larger grain aggregates are formed (Broderick and
Daniel 1990), leading to several advantages in the suit-
ability of the soil for road construction. Lime stabilization
is widely used, both to make clay-bearing soils suitable as
base, sub-bases and sub-grades to increase the strength, and
to produce other properties of useful infrastructure mate-
rials that contain clay. The stabilization process occurs
because calcium hydroxide (lime CaOH2) reacts favorably
with some but not all of the clay. The reaction causes the
clay’s properties to change substantially (Clare and
Crunchley 1957). Plasticity and the tendency to expand
with added moisture are immediately reduced, as the
troublesome cations of sodium and potassium are replaced
by those of calcium or magnesium. Also, lime causes
flocculation, a lumping together of clay particles, which
increase particle size (Sides and Barden 1971). The addi-
tion of lime to soil causes an immediate increase in soil pH
A. Kavak (&)
Department of Civil Engineering, Kocaeli University,
Umuttepe Camp., Kocaeli, Turkey
e-mail: [email protected]
G. Baykal
Department of Civil Engineering,
Bogazici University, Bebek/Istanbul, Turkey
e-mail: [email protected]
123
Environ Earth Sci (2012) 66:1943–1955
DOI 10.1007/s12665-011-1419-8
due to partial disassociation of the calcium hydroxide
(Ladd et al. 1960). The calcium ions in turn combine with
the reactive hydrous silica and/or aluminates, which harden
with time to affect stabilization of the soil. The relatively
high pH of the pore water facilitates the formation of this
cementitious gel by increasing the reactivity of the surface
silica. Over a longer period, there can be a substantial
strength gain through a pozzolanic reaction with any
available silica or alumina.
When stabilizing soil with lime, the amount of calcium
required depends on the eventual use of the mix, and the
objectives of stabilization. As indicated, lime stabilization
of natural materials for bases and sub-bases is intended both
to reduce plasticity and the accompanying volume changes
with moisture content, and to increase strength. The com-
mon test for reduction in plasticity and volume change is the
plasticity index (PI). Results with one group of clays
showed that values reduced by one-third to two-thirds with
3% lime and to a non-plastic condition with 5%. Strength
increases are often measured by standard tests such as
unconfined or triaxial compression, California bearing ratio
(CBR), or flexure test. The strength of lime-stabilized soils
usually increases not only in the short time but also con-
tinues over time since pozzolanic action takes place (Kavak
1996). Solanki et al. (2009) showed the variation of mod-
ulus of elasticity (ME) and unconfined compressive strength
(UCS) values with lime content. Similar to resilient mod-
ulus (Mr), the modulus of elasticity and UCS essentially
showed the same trend. It is evident that there is a signifi-
cant increase in ME and UCS with increasing lime content.
Eades and Grim (1963) studied kaolinite and lime
reactions. They concluded that the reaction of lime and
kaolinite causes the formation of new crystalline phases,
which are tentatively identified as calcium silicate
hydrates. This reaction seems to take place by the lime
reacting with kaolinite particles around the edges, with a
new phase forming around a core of kaolinite.
Croft (1964) examined kaolinite samples by X-ray dif-
fraction method. The preliminary examinations revealed a
rapid attack uniformly distributed over all surfaces of the
clay minerals. The intensity and sharpness of all kaolinite
lines, as well as those of calcium hydroxide, had dimin-
ished considerably after reaction for 1 week. Croft (1964)
also observed the mixture by electron microscopy; the
particles revealed a tendency towards pseudohexagonal
shape; most were, however, irregular and ragged. Glenn
and Handy (1963) cured kaolinite and lime mixtures for
2 years. X-ray diffraction shows a reduction in kaolinite
peak intensities after reaction with lime. However, much
unreacted Ca(OH)2 remains in the calcitic lime mix after
2 years. Small amounts of Ca(OH)2 and much Mg(OH)2
remain in the dolomitic lime mixes. There is an evidence of
12.6-A material from reaction with dolomitic limes, and a
7.6-A product, which appears strongest from reaction with
calcitic lime but is also present in the other mixes.
The in situ performance of lime-stabilized soils
depending on time is also a very important issue for sta-
bilization. As an example, lime stabilization, soil replace-
ment and soil reinforcement by geosynthetics methods
were used to improve the soil when widening old railway
lines to double track in the Czech Republic. After 5 years
in service, the slab section was causing permanent prob-
lems for the track maintenance and had to be reconstructed,
while the lime-improved section behaved very well. Herle
(2005) investigated the subsoil anomalies in this research
on a radar record and also conducted unconfined com-
pression tests on samples taken from test pits. Following
this study, the use of small quantities of lime such as 1, to
2% for rail track subgrade improvement has been widely
accepted as a very efficient and economic method for
reconstructing old rail corridors. In comparisons with other
methods (e.g. soil replacement, soil reinforcement), it is
also environmentally friendly, as it is not necessary to shift
large quantities of soil to and from the site. Another
important example was the construction, in 1969, of a test
section with base and sub-base layers of lateritic soil sta-
bilized with calcitic lime near the town of Cruz Alta, in
Brazil. Despite the lack of major rehabilitation works,
35 years later the road retained an acceptable serviceability
level. Nunez et al. (2005) studied cored samples and new
samples prepared in the laboratory. Cored specimens
showed higher strength and modulus than those compacted
in the laboratory, due to the longer curing time of the cured
samples and to some that of carbonation that took place in
the laboratory samples.
While long-term stabilization data exists in the litera-
ture, virtually all of this is from field scale projects and not
from a controlled laboratory environment. Although it is
known that pozzolanic reactions continue for many years,
there is limited available laboratory data in the literature
for the long time curing and in many studies, curing time
for this process is less than 1 year. In the following table, a
list of similar studies with the maximum curing time in the
laboratory environment are listed.
As it can be seen from the Table 1, there are many
researches related to investigate the effect of curing time
on lime stabilization but, the curing time under controlled
conditions in these researches is less than 1 year. Locat
et al. (1990) studied shear strength development of sensi-
tive clays on lime stabilization under controlled environ-
ment as much as 300 days curing time. Uddin et al. (1997)
(cross reference Little 1999), cured a plastic clay for
180 days at lime contents between 2.5 and 15%. Very
substantial strength gains occurred between 60 and
180 days. Strength gains were maximal at 10% lime and
decreased by 15%. Evans (1998) stabilized highly plastic
1944 Environ Earth Sci (2012) 66:1943–1955
123
Queensland Black clays with 8% lime, which were cured
for 28 days and 26 weeks. As in previous reports, the
strength gain between 28 days and 26 weeks was very
substantial, demonstrating the long-term pozzolanic
process. Baykal (1989) studied the effect of micro mor-
phological development on the elastic moduli of lime-
stabilized bentonite samples cured for 180 days. The
improvements in the lime-stabilized bentonite were shown
by unconfined compression tests, chemical analysis, and
micro morphological investigation using X-ray diffrac-
tometer (XRD) and scanning electron microscope (SEM)
techniques.
The objective of this study was to investigate the long-
term behavior of lime-stabilized kaolinite clay. The study
examined the changes in the microstructure of lime-stabi-
lized kaolinite using X-ray diffraction pattern, SEM elec-
tron microscope images and the changes in strength for
long time cured kaolinite samples under controlled condi-
tions. In the present study, two groups of work were mat-
ched and a full dataset was obtained for a period of
10 years. The first group tests were conducted on lime-
stabilized kaolinite. During this study, many samples were
also left for long-time curing in a temperature and humidity
controlled curing room. Unconfined compression tests
were conducted at various curing times, and the micro
fabric of lime stabilized kaolinite was investigated using
XRD, SEM and EDS methods for 10 years cured
specimens.
Table 1 Literature studies related to UCS tests of lime stabilized soils
References Titles Tests Curing time
Locat et al. (1990) Laboratory investigations on the lime stabilization of
sensitive clays: shear strength development (Clays)
Proctor test, shear strength, SEM 0, 1, 3, 10, 30, 100 and
300 day(s)
Ladd et al. (1960) Recent soil-lime research at the Massachusetts Institute
of Technology (Kaolinite/Montmorillanite)
Dynamic compaction test,
classification tests, unconfined
compression test, CBR tests
0, 7 and 28 day(s)
Hilt and Davidson
(1960)
Lime fixation in clayey soils (Kaolinite/
Montmorillonite)
Classification tests, chemical
analysis, pH test, unconfined
compression test
28 days
Croft (1964) The processes involved in the lime-stabilization of clay
soil (Kaolinite/Montmorillonite)
Classification tests, chemical
analysis, pH test, X-ray
analysis, SEM
60 days for X-ray
Hilt and Davidson
(1961)
Isolation and investigation of a lime-montmorillonite
crystalline reaction product (Bentonite/Kaolinite)
Classification tests, chemical
analysis, pH test, X-ray
analysis, SEM
30 days
Taylor and Arman
(1960)
Lime stabilization using preconditioned soils
(Kaolinite/Montmorillanite)
Classification tests, Proctor test,
Tri-axial test
40 days
Mitchell and El Jack
(1964)
The fabric of soil-cement and its formation (Kaolinite/
Montmorillonite)
Classification tests, chemical
analysis, Proctor test,
unconfined compression tests
240 days
TRB State of the Art
Report-5 (1987)
(Little 1999)
Lime stabilization of Illinois soil, Field evidences
indicates some soil-lime mixtures can continue to gain
strength for excess of 10 years
Unconfined compression tests,
field evidences
75 days for laboratory
works, field
evidences for
10 years
Baykal (1989) The Effect of Micromorphological Development on the
elastic moduli of Fly-ash, Lime Stabilized Bentonite
Classification tests, chemical
analysis, unconfined
compression tests, XRD, SEM
1, 28, 90 and 180 days
Shackelford and Daniel
(1991)
Diffusion in saturated soil II : results for compacted
clay (Kaolinite)
Classification tests, Proctor tests,
diffusion test
30 and 109 days
Doty and Alexander
(1968)
The time-dependent behavior of pozzolanic strength
development of 12 different soils cured at 23 C and 38
C. Significant strength increases are observed between
180 and 360 days
Classification tests, PI
comparisons
From 7 days to
360 days
Uddin et al. (1997)
(Little 1999)
The time-dependent behavior of pozzolanic strength
development of a plastic clay
Unconfined compression tests Between 60 days and
180 days
Evans (1998) Soils highly plastic Queensland Black clays, the
strength gain between 28 days and 26 weeks was very
substantial demonstrating the long-term pozzolanic
process
Classification tests, PI
comparisons, unconfined
compressive strength
Between 28 days and
26 weeks
Environ Earth Sci (2012) 66:1943–1955 1945
123
Materials and methods
Methodology
In the study, the geotechnical properties of natural kaolinite
were determined at the beginning. The optimum lime
quantity for kaolinite clay was selected as the minimum
lime percentage in weight that produced the maximum
UCS. Atterberg limit tests and pH tests were also con-
ducted at various lime contents between 2 and 10% to
determine the optimum lime content of the kaolinite clay.
In order to determine the short- and long-term effects of
excessive lime amount in the clay soil, studies have been
made also with 12% of lime percentage. Kaolinite with 4
and 12% lime by weight are denoted as K4 and K12,
respectively.
Kaolinite was air-dried and stored in plastic containers
in the laboratory. Kaolinite was taken from the container
and the required weight was mixed with a predetermined
amount of lime by using a hand mixer with speed control.
Thorough mixing was essential to evenly distribute the
moisture. During the mixing period, the rate of the mixer
was held constant. After 5 min of mixing, water was slowly
added to the mixture. The amount of water added corre-
sponds to the optimum moisture content of the soil and
lime mixture. The Harvard miniature compaction apparatus
was used to compact the samples for unconfined com-
pression tests with a specially designed hammer. The
standard Proctor energy level was used for unconfined
compressive strength tests conducted in the study. In order
to obtain comparable stress–strain curves between samples,
equal compaction energy per blow per unit compacted
volume was used and the hammer-to-mold diameter ratio
was maintained. After compaction, the specimens were
carefully trimmed. The specimens were first sealed in
plastic containers and then the same samples were sealed in
aluminum foil and have been kept in a humidity room at a
temperature of 21�C and humidity of more than 95%.
Keeping the moisture content constant is essential for the
development of cementitious products. The weights of
specimens with and without the cover were recorded and
the specimens were checked to determine whether they had
lost water content during curing.
To determine the mineralogical characteristics of the
kaolinite chemical analysis, XRD and SEM analyses and
environmental scanning electron microscope (ESEM)
analyses were made of natural samples and samples to
which lime was added. Chemical analyses were conducted
with added 4% lime by weight and the ratios of the
structure that forms the components were determined.
XRD analyses were conducted on natural and long-term
cured lime-stabilized kaolinite samples. Small sub-samples
were taken from the unconfined compression test samples
and were powdered and dried in a sterilizer. Copper K-aradiation with wavelength B1.54 A was used. Diffraction
patterns showing two theta angles with respect to intensity
values were plotted. The samples used for SEM images
were kept in a low temperature sterilizer for 24 h. Before
being placed under the microscope, the samples, which
have a non-conductive surface, were coated with a very
thin conductive carbon layer. The samples analyzed by
ESEM scanning electron microscope were not coated.
The Kaolinite clay used in the present study is mainly
composed of silica (61.6%) and alumina (13.31%). Iron
oxide, magnesium oxide and Calcium oxide also are
present (4–5%) (Table 2).
To determine the geotechnical properties of the Kao-
linite sieve analysis, Atterberg limit tests, Specific gravity
and standard and modified Proctor tests were conducted.
Tests were conducted in accordance with ASTM
D421&422, ASTM D4318, ASTM D 854, ASTM D
698-78 and ASTM D 1557-78 (Bowles 1992). The geo-
technical characteristics of the natural kaolinite are shown
below, in Table 3.
Physical and chemical properties of the lime used in the
study are given in Table 4 (Nuh Cement and Lime Fac-
tory). The lime is stored in the laboratory within a plastic
cover, which is inside a sealed glass container to prevent
the carbonation effect of the CO2 present in the air.
The hydrated calcium lime used in the studies was
manufactured by Nuh Company. Calcium hydroxide con-
tent varies between 80 and 86%.
Results
Determination of the optimum lime content
Optimum lime content can be defined as the lowest lime
content giving the maximum unconfined compressive
Table 2 Chemical analysis of
kaolinite (%)SiO2 61.60
Al2O3 13.31
Fe2O3 5.27
TiO2 0.75
CaO 4.31
MgO 4.52
Na2O 0.57
K2O 1.76
Cr2O3 0.026
BaO 0.03
SO3 0.08
P2O5 0.08
MnO 0.138
L.O.I. (loss of ign.) 6.27
1946 Environ Earth Sci (2012) 66:1943–1955
123
strength of lime-stabilized soils, by also taking into con-
sideration PI and pH values. In order to find the optimum
lime percentage for the kaolinite clay, unconfined com-
pression tests at various lime contents and pH tests using
the Eades and Grim (1963) procedure and Atterberg limit
were conducted.
Atterberg limits
After adding lime, structural transformation and floccula-
tion begins immediately. Kaolinite was initially mixed with
lime and was then kept under curing conditions for one
hour (Kavak and Akyarli 2007) before Atterberg limit tests
were performed. The tests were conducted in accordance
with ASTM 4318. The experiments were done by adding
lime at weight percentages of 0, 2, 4, 5, 6, 8, 10%
accordingly.
The liquid limit value for pure kaolinite was found to be
37.5, which increased to 42.5 by the addition of 2% lime.
The liquid limit is around 41–42 for higher lime percent-
ages. The plastic limit also increased from 29.8 to 34.2
percent with the addition of 2% of lime and remained
relatively constant at higher percentages of lime. The
results of liquid and plastic limit and PI values for kaolinite
with different lime percentages are presented in Table 5.
At 4% lime content, the PI decreased from 7.7 to 6.5,
compared with the original specimen. This percent was
almost the lowest value and this lime content was chosen as
the design lime content for the kaolinite, Atterberg limit
tests give similar design lime content, at 4%. The PI value
drops to 7.5 and does not change much for higher lime
percentages.
UCS tests
The unconfined compressive strength was conducted from
0 to 12% of lime at 2% increments using 0–28 days cured
specimens. A summary of the tests is shown in the Fig. 1,
below. The UCS tests showed that the lowest lime content
that produced maximum soil strength was 4% lime.
In the Fig. 1, the effect of curing and of lime content can
be seen clearly. The UCS of natural kaolinite is 125 kPa,
reaching to 1,000 kPa at 4% lime content after 28 days
curing. For almost all cured specimens, lime content of
more than 4% had little effect on the UCS. Based on Fig. 1,
the optimum lime content can be taken as 4%, taking into
economic factors of the stabilization work.
Table 3 Geotechnical properties of kaolinite clay
Property
Soil classification
Classification-USCS ML
Classification-AASHTO A-4
Atterberg limits
LL (%) 38
PL (%) 30
PI (%) 8
Sieve analysis USCS
Sand (75–2,000 lm) (%) 0
Silt (2–75 lm) (%) 42
Clay (\2 lm) (%) 58
Specific gravity 2.62
Organic material (%) 0
Compac. param. (standard proctor)
Dry unit weight (kN/m3) 15.3
Optimum moist. cont. (%) 21.5
Comp. param. (modified proctor)
Dry unit weight (kN/m3) 15.6
Optimum moist. cont. (%) 18.6
Natural water content (%) 6–8
Activity 0.15
Table 4 Physical and chemical properties of lime
Chemical name Calcium hydroxide
Physical appearance Dry white powder
Boiling temperature (�C) 100
Heat of fusion (�C) 580
Bulk density ( kg/m3) Max. 500
Specific gravity 2.21
Over 90 l (%) 3–6
Over 63 l (%) 7–10
pH (25�C) 12.4
Ca(OH)2 (%) 80–86
Active CaO (%) 60.6–65.15
CaO ? MgO (%) 83–93
MgO 1–2
Insoluble material (%) max. 1
Bounded H2O (%) 19.4–20.85
S max. 0.5
R2O3 (Al2O3 ? Fe2O3) (%) max. 1
Table 5 Atterberg limits of kaolinite at different lime contents
Lime cont. (%) LL (%) PL (%) PI (%)
0 37.5 29.8 7.7
2 42.5 34.2 8.3
3 41.2 33.8 7.4
4 41.1 34.3 6.5
5 40.8 33.9 6.9
6 40.9 34.2 6.7
8 41.1 32.8 7.3
10 41.7 33.6 8.1
Environ Earth Sci (2012) 66:1943–1955 1947
123
pH tests
The pH level is an indicator of the reaction between lime
and soil. The pH of the soil increases to 12.4, with optimum
amount of lime (Eades and Grim 1963). At this pH, the soil
alumina and soil silica (pozzolans) become soluble and
combine with free calcium and water to form cementitious
products: calcium aluminate silicate hydrates (CASH) and
calcium-aluminate-hydrates (CAH) (Little 1999).
The pH tests were also conducted according to the
method of Eades and Grims (1963) using lime contents
from 1 to 10 at 1% increments. In Fig. 2, the variation of
pH with lime for kaolinite samples is shown. The pH value
increases to a maximum of almost 12.4 at 4% lime.
Based on the Atterberg limit, UCS and pH test results, the
optimum lime for the research content was chosen as 4%.
Standard and modified proctor tests
Moisture and density relations of the kaolinite were deter-
mined using standard and modified Proctor compaction
tests. The tests were conducted according to the ASTM D
698-78 and D 1557-78 (Bowles 1992). Following these
tests, comparisons were made of the behavior of the lime-
stabilized kaolinite between standard and modified Proctor
tests. The soil and lime mixtures were prepared for com-
paction test as described above in the section on sample
preparation. First, Proctor tests were conducted using the
natural kaolinite and then the kaolinite was mixed with the
chosen optimum lime content and the tests were repeated
for this case. A summary of the maximum dry unit weight
and optimum water content of kaolinite with and without
lime is shown in the Table 6. The Proctor curves are shown
in the Fig. 3.
Optimum water content and dry unit weight for kaolinite
samples was found to be 21.5% and 15.3 kN/m3, respec-
tively, for standard Proctor tests. In the light of the standard
Proctor test results, the optimum water content increases to
25% and maximum dry unit weight decreases to 14.6 kN/m3
with 4% lime. The trend is also similar for modified
Proctor tests, while optimum water content increases to
24.5%, the maximum dry unit weight drops to 14.7 kN/m3
with 4% of lime. Optimum water content of kaolinite
0
200
400
600
800
1000
1200
0 2 4 6 8 10 12
Unc
. Com
p. S
tr. (
kPa)
Lime Content %
0 Day0 Day0 Day avg.1 Day1 Day1 Day avg.7 Days7 Days7 Days avg.28 Days28 Days28 days avg.
Fig. 1 UCS tests of kaolinite at
different lime contents
Fig. 2 Kaolinite pH values with respect to lime content %
Table 6 Maximum dry unit weight and optimum water content
values of kaolinite with and without lime
Maximum dry unit
weight cd (kN/m3)
Optimum moisture
content wt (%)
Kaolinite (standard) 15.3 21.5
Kaolinite (modified) 15.6 18.6
Kaolinite ? 4% by
weight lime (standard)
14.6 25.0
Kaolinite ? 4% by
weight lime
(modified)
14.7 24.5
Kaolinite ? 12% by
weight lime (standard)
14.5 26.5
1948 Environ Earth Sci (2012) 66:1943–1955
123
sample and dry unit weight for kaolinite samples were
found as 26.5% and 14.5 kN/m3, respectively, for K12
samples. It is clear that, optimum water content increases
with the increases of lime content and maximum dry unit
weight decreases with increasing lime.
According to the compaction test results, it is observed
that for lime-stabilized kaolinite samples, the results are
similar for both of standard and modified tests. The vari-
ation in the optimum water content and maximum dry unit
weight is less than 3 and 1%, respectively, between stan-
dard and modified Proctor tests. As a result of compaction
tests, it can be said that optimum water content values
increase and maximum dry unit weight values decrease
with lime stabilization. The Proctor curves become flatter
for lime-stabilized samples and smoother curves are
obtained. The results are similar to those reported in pre-
vious studies by Neubauer and Thompson (1972) and
Solanki et al. (2009).
According to the results of standard and modified
Proctor tests for natural and lime-stabilized kaolinite clay,
it can be said that although the compaction energy values
are very different for standard and modified Proctor tests,
the moisture versus dry unit weight graphs of kaolinite
clays with lime are very similar. Kaolinite behaves similar
to that of a granular material in micro fabric after lime
stabilization.
Unconfined compression tests
Unconfined compression tests were conducted on kaolinite
samples prepared with standard energy at the 4% optimum
lime content and cured at different periods ranging from
0 days to 123 months. The samples were prepared for UCS
tests using a Harvard miniature compaction set according
to the defined methodology described above in the section
on sample preparation. The specimens were cured at 21�C
in a room with greater than 95% humidity. The maximum
curing time used in the study is more than 10 years. The
unconfined compressive strength of natural kaolinite was
125 kPa, reaching 1,015 kPa for lime-stabilized kaolinite
specimens with 4% lime that were cured for 28 days. In the
long-term, for a period of 123 months curing UCS reached
2,640 kPa. The increase of strength was 21 times higher
than the original strength. Three typical unconfined com-
pression tests for natural kaolinite K4, cured for 28 days
and K4 cured for 123 months are shown in Fig. 4.
The behavior of the lime-stabilized kaolinite was very
different from that of natural kaolinite. The modulus of
elasticity, which is the slope of the stress–strain curve
changes sharply for lime-stabilized kaolinite, and the soil
shows brittle behavior with lime. The unit strains at failure
decreases to around 1% for lime-stabilized and cured
specimens, compared to 2.3% for natural kaolinite samples.
UCS test results for K4 samples at different curing periods
up to 123 months are shown in the Fig. 5 below.
In Fig. 5, it is clearly seen that, the UCS of lime-stabi-
lized kaolinite increases with time. Each UCS value in the
bar graph is the average value of three UCS tests and the
maximum variation in these three tests was found to be
10% at maximum variation. The UCS increased from the
reference value of 125 kPa to 1,000 kPa in 1 month, to
2,064 kPa after 96 months and finally reached to 2,640 kPa
at 123 months curing time.
In order to see the changes in strength and behavior in
the short- and long-term, a series of UCS control tests were
conducted with 12% content, which was the maximum
value used for the lime determination studies. The stress–
strain curve for unconfined compression tests of kaolinite
with 12% lime are shown in Fig. 6 below. The unconfined
compression strength increases with curing time and
reaches to 2,507 kPa in 123 months. The strength increase
was very high like K4 samples which is approximately 20
times higher than the initial kaolinite’s unconfined com-
pression strength.
10
11
12
13
14
15
16
17
18
14 16 18 20 22 24 26 28 30 32 34 36
Max
imum
Dry
Uni
t W
eigh
t , k
N/m
3
Water Content , %
Kaolinite (Standard)
Kaolinite + 4% Lime (Standard)
Kaolinite (Modified)
Kaolinite + 4% Lime (Modified)
Fig. 3 Standard and modified Proctor test results for kaolinite Fig. 4 UCS tests for K4 samples
Environ Earth Sci (2012) 66:1943–1955 1949
123
Elastic modulus values are determined from UCS tests
by using the slopes of the stress–strain curve between 20
and 50% of the failure stress. The increase in UCS values is
in the range of 20 times the original strength but the
increase in elastic moduli is approximately 50 times
compared to original one for K4 samples. The elastic
modulus values are calculated and presented in the Figs. 4
and 6.
Similar to the results of the K4 samples, the behavior of
the K12 lime-stabilized kaolinite was very different to that
of natural kaolinite. The modulus of elasticity which is the
slope of the stress–strain curve changes sharply for lime-
stabilized kaolinite, the soil shows brittle behavior with
lime. The unit strain at failure decreases to 1.3% for lime
stabilized and cured specimens compared to 2.3% for
Fig. 5 UCS tests conducted in
123 months for K4 at various
curing periods
0
500
1000
1500
2000
2500
3000
0 0.5 1 1.5 2 2.5 3
UC
S(k
Pa)
Strain (%)
Natural
1 day
7 days
28 days
6 months
123 months
Fig. 6 UCS tests, stress–strain curves for K12 samples
Fig. 7 Unconfined
Compressive Strength Values
for K12
1950 Environ Earth Sci (2012) 66:1943–1955
123
natural kaolinite samples. In Fig. 7, it is clearly seen that,
similar to K4 samples, the UCS of K12 lime-stabilized
kaolinite increases with time.
Each UCS value in the bar graph is the average value of
three UCS tests and the maximum variation between these
three tests was found to be 10%. UCS increased from the
reference value of 125 kPa to 1,000 kPa in 1 month,
1,550 kPa at 115 months and finally reached 2,507 at
123 months curing time.
The strength gain of the lime-stabilized samples is very
high in the long-term. Many design methods for lime-sta-
bilized soils use the unconfined compressive strength of
28-day or 3-month cured samples as design strength. In
Fig. 7, the long-term increase in strength at 123 months is
2.9 times for K4 samples and 3.5 times for K12 samples
compared to their respective 28-day cured values. The very
significant strength increases further illustrate the impor-
tance of maintaining enough lime and high enough pH to
continue pozzolanic reactivity in a reactive clay soil. As
long as this maintained strength gain in the long-term is
possible (Little 1999). Laboratory data indicate that, under
suitable conditions, strength gain can continue for in excess
of 10 years.
Typical basic characteristics of lime-stabilized kaolinite
samples were calculated and final values are shown in
Table 7. The water content and drying effect might be very
important in the long-term.
The drying is less than 1% compared to original values.
The void ratio is 0.83 for K4 samples and 0.92 for K12
samples. Although, voids in K12 are more than K4 sam-
ples, saturation is higher in K4 samples compared to K12
samples.
CBR experiments
California bearing ratio tests are conducted to lime stabi-
lized kaolinite samples for both of standard and soaked
cases. The tests are conducted according to the ASTM D
1883-87. Experiments have been done on both of samples
K4 and kaolinite. The samples have been prepared first by
mixing at optimum water content and leaving an hour in
the laboratory for initial reactions then compacted in CBR
moulds. The samples are compacted and left in the
laboratory in a humidity room at 21�C. The tests are con-
ducted on samples cured for 1, 7 and 28 days. The varia-
tion in CBR values are shown in Fig. 8. CBR values for
many cured lime-soil mixtures are very high and indicate
the extensive development of pozzolanic cementing
products.
California bearing ratio values increased sharply with
lime for both of standard and soaked CBR tests. For
standard CBR, the CBR of natural kaolinite was found as
15, this value reached to 89 with 4% of lime in 28 days,
which one is 5.9 times higher than the original value. The
similar sharp increases are also observed for the soaked
CBR tests. The soaked CBR value of kaolinite was found
as 2, the value increased with 4% lime to 58 in 28 days.
The value is 29 times higher than the initial value. The
swelling for lime stabilized kaolinite is found less than 1%.
Micro analysis
XRD analysis
X-ray diffractometer analyses were conducted of the K4
and K12 samples, which were cured for long-term
(10 years). The tests were conducted at Bogazici Univer-
sity Advance Technologies R&D center in Istanbul Turkey.
40 kV and 40 mA Copper K-a radiation was used in XRD
analysis. The samples were supplied to the laboratory in
powdered form and were dried in a sterilizer prior to
analysis. XRD analyses were made for kaolinite, K4 and
K12 samples.
D-spacings obtained by XRD patterns belong to the
hydrated calcium aluminum silicate (CASH) mineral
named laumontite. Chemical formula of Laumontite is
CaAl2Si4O12–4H2O. Since this mineral belongs to the
silicate group, this is probably one of the reasons for the
long-term strength gain observed in the samples.
Table 7 Basic characteristics of the lime stabilized UCS samples
K4, 10 years K12, 10 years
Water cont. (%) 25.2 24.4
Unit wt (kN/m3) 17.51 16.6
Dry unit wt (kN/m3) 13.99 13.3
Weight (g) 112.5 106.6
Void ratio 0.83 0.92
Saturation (%) 79.0 69.3
Fig. 8 Standard and soaked CBR values
Environ Earth Sci (2012) 66:1943–1955 1951
123
Energy dispersive X-ray spectroscopy
Energy dispersive X-ray spectroscopy (EDS) was used for
the elemental analysis and chemical characterization of K4
samples cured for 10 years. As a type of spectroscopy,
EDS relies on the investigation of a sample through
interactions between electromagnetic radiation and matter,
analyzing X-rays emitted by the matter in response to
impacts from charged particles. The EDS analysis of the
samples was conducted by the micro analysis group at the
Sisecam company research laboratories, using a Thermo
Noran system six X-ray microanalysis system.
Table 8 shows the constituents of K4 kaolinite clay
specimens cured for 10 years determined by EDS.
The stabilized K4 samples consist mainly of Silicon
dioxide (63%), aluminum oxide (24%), sulfur trioxide
(9%) and lime (4%).
SEM analysis
Scanning electron microscopy studies were carried out at
two institutions. The samples examined with Jeol JSM
6360 LV scanning electron microscope at Sisecam
research laboratory, were coated with carbon. The envi-
ronmental scanning electron microscope at Bogazici Uni-
versity does not need coating for nonconductive specimens
(The XL 30 Philips ESEM scanning electron microscope).
The specimens studied at Bogazici University were not
coated (Fig. 9).
In the studies, images of kaolinite clay at 2,500, 5,000
and 10,000 magnifications were compared with K4 sam-
ples cured for 10 years. The images are shown in Figs. 10,
11, 12, 13, 14 and 15.
In the figures above, images from untreated soil indicate
crumbled and flaked arrangement of soil particles. Higher
magnified views (5,0009 and 10,0009) of the treated K4
samples indicate the presence of cubic cementitious crys-
tals. As lime reacts with the clay particles, an agglomera-
tion effect takes place which forms bigger particles, with a
consequent increase in pore size area, resulting in well-
aggregated crumbs.
In the following images in Figs. 16 and 17, K4 kaolinite
clay at 350 magnifications were compared with K12 sam-
ples cured 10 years.
The images show that increased lime in K12 samples
creates porous fabric compared to that of K4 samples. The
higher void ratios calculated and presented in Table 7 are
in competence with the visual observations.
The SEM and XRD images of the long-term K4 samples
show that the original platy structure of the kaolinite
mineral is still preserved.
Furthermore, SEM images of the K12 samples show
quartz, calcite and kaolinite minerals within the structure.
Microfabric evaluation of stabilized clays is a challenging
process. It is very difficult to determine the reaction prod-
ucts due to their low concentration. However, microfabric
Table 8 EDS analysis of K4 kaolinite clay cured for 10 years
Element Net counts Weight (%) Formula Compound (%)
O 18,067 51.34 –
Al 5,327 12.50 Al2O3 23.62
Si 11,641 29.33 SiO2 62.75
S 1,182 3.64 SO3 9.1
Ca 602 2.62 CaO 3.66
Ti 36 0.23 TiO2 0.38
Cr 38 0.33 Cr2O3 0.48
Total 100.00 100.00
Fig. 9 XRD analysis of natural
kaolinite and samples with 4
and 12% lime (Bogazici Univ.,
2004)
1952 Environ Earth Sci (2012) 66:1943–1955
123
Fig. 10 Kaolinite natural clay 92,500
Fig. 11 K4, 92,500 (10 years cured)
Fig. 12 Kaolinite natural clay 95,000
Fig. 13 K4, 95,000 (10 years cured)
Fig. 14 Kaolinite natural clay 910,000
Fig. 15 K4, 910,000 (10 years cured)
Environ Earth Sci (2012) 66:1943–1955 1953
123
development of K4 and K12 samples was evident at 10,000
and 2,000 magnification after 123 months.
To determine the relationships between mineralogy and
macroscopic geotechnical parameters, Chryssochoou
(2010) completed a detailed mineralogical analyses of
dredged material (DM) stabilized with lime, cement kiln
dust (CKD), class F fly ash and two cements that was cured
for 6 months. A direct correlation between mineralogy and
engineering parameters was not found, largely due to the
complexity of the system involved. Rajasekaran and Nar-
asimha (1996) showed crumbs of floccules associated with
soil–lime reaction products of the images of the samples
treated with lime.
Although, it is very hard to correlate microfabric to
engineering behavior quantitatively, some qualitative
comments can be made. Addition of lime results in an open
microfabric due to flocculation. The pozzolanic reactions
cause formation of cementitious crystals which in term
densify the fabric causing an increase in strength and a
decrease in strain at failure values. The densification of
microfabric is supported by the results of UCS tests with
nearly 50 times increase in elastic modulus values while
the UCS increase is in the range of 20 times.
X-ray diffractometer and ESEM analysis offered min-
eralogical proof of the changes which occur in kaolinite
clays when treated with lime. This mineralogical proof was
supported by changes in physical properties such as
Atterberg limits, compressive strength measured on the
same soil.
Conclusions
The present study used three methods, UCS tests, pH
method and Atterberg limits to determine the optimum
lime content for the kaolinite samples. All the methods
used in the study gave expected and consistent results. The
performance and behavior of the lime-stabilized kaolinite
with 4% lime is similar to that of with 12% lime in both
short- and long-term tests. The long-term behavior of the
samples also supports the validity of the methods over
longer periods.
In the long-term, the unconfined compressive strength of
lime-stabilized kaolinite increases continuously although
the rate of increase is less in later years. The increase in
strength of lime-stabilized samples is very high compared
to that of the natural kaolinite clay samples. The uncon-
fined compressive strength of natural kaolinite was
125 kPa; this increased to 2,640 kPa for lime-stabilized
kaolinite samples cured for 123 months, which is 21 times
the original value. Since ion exchange, flocculation and
carbonation reactions between lime and clay samples occur
in a short time, the reason for the strength increase lime-
stabilized kaolinite even at 123 months is probably due to
pozzolanic reactions. Tests on long-term cured kaolinite
samples with 12% of lime showed similar results, with a
UCS value around 20 times higher than the initial strength
of natural kaolinite. Increasing lime content to a value of
three times of optimum did not improve the long-term
strength behavior. These increases can also be explained by
pozzolanic reactions. XRD and ESEM studies also showed
that laumontite minerals are present in both K4 and K12
samples. A typical CASH named Laumontite has been
detected in K4 and K12 samples after 10 years of curing.
The fabric and structure of cementation minerals did not
change after 10 years curing under the controlled labora-
tory conditions.
The strength improvement of nearly 2.5 times with
respect to 28 days curing is attributed to maturity of
cementitious minerals. The strength increases after
1 month and 3 months are very important because many
lime stabilization design methods uses the 28-day strength’
Fig. 16 K4, 9350 (10 years cured)
Fig. 17 K12, 9350 (10 years cured)
1954 Environ Earth Sci (2012) 66:1943–1955
123
as a design value. The strength in the long-term is found to
be around 3 times higher compared to that of 28-day
strength for both K4 and K12 samples. This suggests that
classical design parameters are very conservative in terms
of long-term lime stabilization behavior.
Chemical stabilization of clay soils with lime is an
environmentally friendly, economical and technically fea-
sible method for road construction. The present study has
demonstrated the fact that the cementitious minerals, which
contributed to strength, formed in the short-term are still
available and maintain their original fabric and structure
without deterioration.
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