Construction and Building Materials 188 (2018) 1025–1034
Contents lists available at ScienceDirect
Construction and Building Materials
journal homepage: www.elsevier.com/locate/conbuildmat
Use of crushed clay brick and pumice aggregates in lightweight
geopolymer concrete
Ampol Wongsa a, Vanchai Sata a,⇑, Peem Nuaklong a, Prinya Chindaprasirt a,b
a
b
Sustainable Infrastructure Research and Development Center, Department of Civil Engineering, Faculty of Engineering, Khon Kaen University, Khon Kaen 40002, Thailand
The Academy of Science, The Royal Society of Thailand, Dusit, Bangkok, Thailand
h i g h l i g h t s
Lightweight fly ash geopolymer concrete (LWGC) was studied.
Crushed clay brick (CA) and pumice aggregates (PA) were used for LWGC aggregate.
The results of natural aggregate (NA) LWGC were compared.
3
CA and PA LWGC yielded 2.7–18.3 MPa compressive strength with 1011–1749 kg/m .
And theirs exhibit better thermal insulation and fire resistance than that of NA.
a r t i c l e
i n f o
Article history:
Received 9 April 2018
Received in revised form 17 August 2018
Accepted 27 August 2018
Keywords:
Crushed clay brick
Pumice
Fly ash
Geopolymer
Lightweight concrete
a b s t r a c t
The study aimed to examine the properties of lightweight high-calcium fly ash geopolymer concrete
(LWGC) containing crushed clay brick and pumice aggregates. A high-calcium fly ash activated by sodium
silicate and sodium hydroxide solutions was used as the geopolymer binder. The properties of LWGCs
including workability, compressive strength, splitting tensile strength, surface abrasion resistance, density, thermal conductivity, ultrasonic pulse velocity, and fire resistance were investigated and compared
with those of the normal density control geopolymer concrete. Temperatures corresponding to 400 °C,
600 °C, and 800 °C were used to test the fire resistance of the concretes. The results indicated that both
crushed clay brick and pumice LWGCs exhibited better thermal insulation and fire resistance characteristics when compared to that of the geopolymer containing natural aggregates (CGCs). The results suggested that the LWGCs produced with crushed clay brick aggregate are suitable for structural
lightweight concrete. With respect to LWGCs produced with pumice aggregate, the compressive strength
was significantly lower, and is sutiable for the manufacture of concrete blocks.
Ó 2018 Elsevier Ltd. All rights reserved.
1. Introduction
Lightweight aggregate concrete is available in several parts of
the world due to its high strength to weight ratio, good sound insulation characteristics, and low thermal conductivity coefficient
given the present of voids in the lightweight aggregate. It can be
used in a wide range of densities and suitable strengths for various
concrete product applications such as roof decks, wall panels,
masonry blocks or brick, and precast concrete units [1]. The use
of lightweight aggregate concrete reduces the dead load of structure to produce lighter and smaller structures and also reduces
the cost of construction [2,3]. The use of lightweight aggregate
⇑ Corresponding author.
E-mail address: vancsa@kku.ac.th (V. Sata).
https://doi.org/10.1016/j.conbuildmat.2018.08.176
0950-0618/Ó 2018 Elsevier Ltd. All rights reserved.
concrete is also preferred, especially for structures built in seismic
zones due to its reduced weight [1].
Several researchers indicated that lightweight aggregate from
natural sources (for e.g., perlite, diatomite [4], and pumice [3,5])
or from manufactured and recycled materials (for e.g., coal bottom
ash, lightweight waste-based geopolymer aggregates [6], recycled
crushed clay brick [7,8], and recycled lightweight concrete aggregate [3]) are used to produce lightweight Portland cement-based
concrete. The lightweight aggregate concrete is also investigated
with a new binder, namely geopolymer. Geopolymer is an alternative cement binder synthesised by mixing aluminosilicate material
and high alkaline solutions [9] and is generally expected to provide
good fire resistance due to its ceramic-like properties. It utilizes
by-products including coal fly ash [10,11] or bottom ash [12,13],
rice husk ash [14,15], and ground granulated blast-furnace slag
[16–18] as aluminosilicate sources to react with high alkaline
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A. Wongsa et al. / Construction and Building Materials 188 (2018) 1025–1034
solutions such as sodium silicate and sodium hydroxide [19,20].
The utilisation of geopolymer binder in the production of lightweight aggregate concrete offers an alternative environment
friendly material and also reduces carbon dioxide emissions due
to the elimination of cement. An earlier study [21] indicated that
coal bottom ash is used to produce lightweight geopolymer concretes (LWGCs) with compressive strengths of 14.3–18.1 MPa and
densities of 1660–1690 kg/m3 that are used as thermal insulation
and moderate-strength concrete. Furthermore, Wongsa et al. [21]
examined the effect of alkaline solution to fly ash ratios (0.70,
0.75, and 0.80) and SS/SH ratios (0.5, 1.0, and 1.5) on the workability of LWGCs containing bottom ash as fine and coarse aggregate
and reported that the lowest alkaline solution to fly ash ratio of
0.70 corresponded to a suitable and sufficient ratio for workability
of LWGCs with high SS/SH ratio of 1.5. Zaetang et al. [22] also indicated that pervious high-calcium fly ash geopolymer concrete containing coal bottom ash as aggregate exhibited density of 1470–
1500 kg/m3, compressive strength of 5.7–8.6 MPa, and thermal
conductivity of 0.30–0.33 W/m K, and thus it is suitable as an environment friendly concrete. Posi et al. [23] reported that recycled
lightweight concrete aggregate from waste lightweight concrete
can be used as a lightweight aggregate to produce LWGCs with
compressive strengths of 4.5–17.5 MPa and densities of 1200–
1500 kg/m3. Colangelo et al. [24] investigated the use of expanded
polystyrene waste as a lightweight aggregate in metakaolin-based
geopolymer and reported that the LWGC mixed with expanded
polystyrene exhibited lower thermal conductivity and higher
strengths when compared to that of Portland cement-based
materials.
Volcanic pumice is a natural lightweight aggregate with a
sponge-like structure and is observed in the granulated form that
is produced from the rapid cooling of molten lava [1]. It is used
as an aggregate in the production of lightweight concrete in several
countries [5]. Specifically, it is found in United States, Italy, Turkey,
Greece, and Spain [1,25]. With respect to Thailand, it is found in
Rayong, Buriram, and Lopburi provinces. Crushed bricks as aggregates are of particular interest since their use reduces the problem
of waste storage and also aids in the preservation of natural aggregate resources [7]. Recent successful studies on the use of crushed
clay bricks as aggregates in concrete are reported in several parts of
the world including Algeria [7], Egypt [8], Hong Kong [26,27], United States [28,29], United Kingdom [30], and China [31]. In Thailand, several old constructions and buildings typically consume
large quantities of clay brick/block and reach the end of their service life facing demolition. This results in large quantities of wasted
clay bricks in several parts of country. Waste bricks generated from
construction and demolition sites are generally transported to
landfills for disposal. With the limited landfill space in Thailand,
it is necessary to discover the possible use of crushed clay brick
as a new civil engineering material. There are many published
studies on the use of recycled crushed clay brick aggregate (CA)
and pumice aggregate (PA) with geopolymer-based material. Previous studies [32,33] reported that CA can be used as coarse aggregate to produce pervious geopolymer concrete. However, there is a
paucity of studies that reported on the use of CA and PA as fine and
coarse aggregates in fly ash-based geopolymer binder to produce
LWGC. This study aims to fill the aforementioned knowledge gap.
Therefore, we focus on the use of CA and PA as fine and coarse
aggregates in lightweight high-calcium fly ash geopolymer concrete. In the experiment part, the effects of the sodium silicate to
sodium hydroxide solution (SS/SH) ratio and elevated temperature
exposure on the properties of LWGCs containing CA and PA as fine
and coarse aggregates including workability, compressive strength,
splitting tensile strength, surface abrasion resistance, density, thermal conductivity, and ultrasonic pulse velocity were investigated.
The results were also compared to theose of control geopolymer
concrete (CGC) produced with crushed limestone and river sand.
2. Materials and preparation of sample
2.1. Materials
The materials used in the study are crushed clay brick aggregate (CA), pumice
aggregate (PA), crushed natural limestone aggregate and river sand (NA), and lignite
coal fly ash. The CA was obtained from crushed broken clay brick from a construction site in Khon Kaen province, north-eastern Thailand. Commercially available
acidic pumice in Bangkok, Thailand was used as the PA. The coarse aggregates were
crushed and/or sieved into similar particles in the size range of 4.8 to 9.5 mm while
fine aggregates ranged from 75 mm to 4.8 mm. The fineness modulus of fine CA
(3.73), fine PA (3.72), and river sand (3.30) slightly exceeded the range (2.3–3.1)
based on ASTM C33/C33M-18 [34]. The CA and river sand were sieved to achieve
as-received PA grain size and to avoid any effects due to the aggregate size. The
grain size distributions of the aggregates relative to the upper and lower limits
based on ASTM C33/C33M-18 [34] are shown in Fig. 1.
The visual observation of all aggregates clearly indicated that the particle shape
of coarse PA was round while those of coarse CA and crushed limestone were angular. The surface texture of coarse PA was slightly rougher and more porous than
those of coarse CA and crushed limestone. Table 1 shows the physical properties
of all fine and coarse aggregates used in the study. The bulk density and specific
Fig. 1. Grain size distributions of aggregates.
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A. Wongsa et al. / Construction and Building Materials 188 (2018) 1025–1034
Table 1
Physical properties of coarse and fine aggregates.
Properties
3
Bulk density (kg/m )
Specific gravity (SSD)
Water absorption (%)
Fineness modulus
Los Angeles abrasion loss (%)
Crushed limestone
Coarse CA
Coarse PA
River sand
Fine CA
Fine PA
Testing standard
1576
2.70
0.54
6.00
26.0
1008
2.03
15.34
6.13
45.3
395
1.07
66.11
6.08
71.3
1671
2.63
0.35
3.30
–
1040
2.09
13.04
3.73
–
601
1.40
34.88
3.72
–
ASTM
ASTM
ASTM
ASTM
ASTM
Table 2
Chemical composition of fly ash, CA, and PA.
Oxides (%)
Fly ash
CA
PA
SiO2
Al2O3
Fe2O3
CaO
K2O
MgO
MnO
Na2O
P2O5
TiO2
SO3
Loss on Ignition (LOI)
39.4
20.8
11.5
14.5
2.4
2.2
–
1.4
0.2
0.5
4.2
1.5
67.9
15.2
5.1
0.6
1.5
1.2
0.1
0.8
–
0.8
–
–
60.4
16.7
4.0
2.4
3.4
0.9
0.1
4.0
0.2
0.5
–
–
gravity in saturated surface dry (SSD) condition of PA and CA were lower than those
of crushed limestone and river sand while the water absorptions were higher as
expected. The aggregates were fabricated in the SSD condition prior to the mixing
of concrete. The Los Angeles abrasion test of coarse aggregates was presented in
terms of the percent weight loss. The weight losses of CA and PA exceeded those
of crushed limestone. The results indicated that CA and PA exhibited lower abrasion
resistance than crushed limestone and were consistent in terms of bulk density and
specific gravity. Although, the Los Angeles abrasion loss value and water absorption
of PA exceeded the tolerated threshold. However, PA can be used as a lightweight
aggregate prepared by processing natural materials (pumice, scoria or tuff) for
structural concrete based on ACI Committee 213 [35].
Fly ash with specific gravity of 2.17 and 44% (by weight) retained on sieve no.
325 (45 mm) was obtained from Lampang province in the North of Thailand and
used as the primary source material to prepare a geopolymer binder. The chemical
compositions of the materials are given in Table 2. Specifically, 10 mol/L (Molar)
sodium hydroxide (SH) and sodium silicate (SS) solution were used as alkaline activators to produce geopolymer binder. Additionally, 10 M SH was prepared by dissolving 400 gm of sodium hydroxide pellets with distilled water in a final volume
of 1 L and left for 24 h prior to use. The commercial grade SS with 12.53% Na2O,
30.24% SiO2, and 57.23% H2O by weight was used without any modification.
2.2. Mix proportions
Given the low bulk densities of CA and PA, they were used as complete replacement (100%) of natural aggregate (NA) to produce lightweight aggregate geopolymer concrete. The proportions in all mixtures were maintained as constant and
consisted of 51%, 15%, and 34% by volume of bulk coarse aggregate, fine aggregate,
and geopolymer paste, respectively. Their mix proportions are shown in Table 3.
The parameters of the study corresponded to the types of fine and coarse aggregates
(NA, CA, and PA) and the SS/SH ratios by mass (0.5, 1.0, and 1.5). The alkaline
C29/C29M-17 [36]
C127-15 [37]
C127-15 [37]
C136/C136M-14 [38]
C131/C131M-14 [39]
solution to fly ash ratio by mass and concentration of SH were maintained as constant at 0.70 and 10 M, respectively [21]. The proportions in the mixture depended
on volumetric bases. The ratio of volume of bulk coarse aggregate to fine aggregate
and geopolymer paste volume was carefully maintained. The names of the mixtures
were based on the aggregate type and SS/SH ratio. For example, PA-1.0 denotes concrete with fine and coarse pumice aggregates and an SS/SH ratio of 1.0.
2.3. Mixing, casting, and curing
The mixing of LWGCs and CGCs was performed in a controlled room at 25 °C.
The fly ash and SH were mixed in a pan-type mixer for 5 min, and the fine and
coarse aggregates were then added and mixed for 2 min. Finally, SS was added to
the mixture and mixed for 1 min. After mixing, fresh mixtures were placed in
moulds and compacted on a vibrating table for 10 s. Two sizes of the samples were
cast. Cylindrical samples with a diameter of 10 cm and height of 20 cm were prepared for compressive and splitting tensile strength tests. Additionally, 10-cm cube
samples were used for surface abrasion resistance, density, ultrasonic pulse velocity, and thermal conductivity tests. The specimens were covered with a plastic sheet
to prevent moisture loss and were allowed to stand for 1 h at 25 °C. Subsequently,
the specimens were cured at 60 °C for 48 h. Following the heat curing, the specimens were placed in the laboratory for cooling, and they were demoulded on the
following day. The specimens were then covered with a plastic sheet and stored
in a controlled room at 25 °C until testing commenced.
3. Testing
The workability of fresh LWGCs and CGCs mixes was examined
by conducting slump tests as per ASTM C143/C143M-15a [40]. The
compressive strength, splitting tensile strength, and surface abrasion resistance were tested at the age of 7 d as per ASTM C39/
C39M [41], ASTM C496/C496M-17 [42], and ASTM C944/C944M
[43], respectively. The reported results corresponded to the average of three samples. The surface abrasion resistance was tested
by the rotating–cutting method. The samples were abraded with
a load of 98 N on the surface for 2 min following contact between
the cutter and sample surfaces. The abrasion resistance of each
sample was tested on the three sides of the sample. The densities
of the samples were measured as per ASTM C1754/C1754M-12
[44]. The ultrasonic pulse velocity on concretes was determined
as per ASTM C597-16 [45]. The transducers that were used exhibited a diameter of 50 mm with a frequency of 50 kHz. The thermal
conductivities were measured using a direct measuring instrument
with a surface probe (ISOMET2114). The measurement ranges of
the device corresponded to 0.04–6.0 W/m K.
Table 3
Mix proportions per m3 of LWGCs and CGCs.
Mix
NA-0.5
NA-1.0
NA-1.5
CA-0.5
CA-1.0
CA-1.5
PA-0.5
PA-1.0
PA-1.5
Aggregate
Geopolymer binder
Coarse
(kg)
Fine
(kg)
Fly ash
(kg)
SS
(kg)
SH
(kg)
1385
1385
1385
1049
1049
1049
536
536
536
383
383
383
354
354
354
215
215
215
350
354
357
350
354
357
350
354
357
82
124
150
82
124
150
82
124
150
163
124
100
163
124
100
163
124
100
Note: NA = crushed limestone and river sand, CA = crushed clay brick, PA = pumice aggregate.
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A. Wongsa et al. / Construction and Building Materials 188 (2018) 1025–1034
In order to examine the fire resistance properties of LWGCs,
only the SS/SH = 1.0 mixture was selected to expose at temperatures of 400 °C, 600 °C, and 800 °C. At the age of 7 d, the specimens
were subjected to target temperatures at a gradual incremental
rate of 3–5 °C/min. Immediately after the target temperature was
attained, it was maintained for 1 h before the furnace was shut
down to allow the specimens in the furnace to cool to room temperature. Following the temperature exposure, the compressive
strength, density, ultrasonic pulse velocity, and thermal conductivity were tested.
Figs. 3–5. The mechanical properties of LWGC containing CA and
PA were lower than those of NA due to its looser texture that
was also indicated by the decreases in the density and Los Angeles
abrasion resistance. Similar results were reported in previous studies [5,7] with respect to the negative effect of using crushed brick
and volcanic pumice as an aggregate on the mechanical properties
of the Portland cement-based concrete. Based on Khandaker and
Anwar [5], the compressive strength and modulus of elasticity
decreased with increases in the volcanic PA content due to the
4. Results and discussion
4.1. Slump value
As shown in Fig. 2, the slump value of lightweight geopolymer
concretes (LWGCs) containing PA is in the range of 201–263 mm,
and this exceeds that of LWGCs containing recycled CA by approximately 15–24% and by 5–22% for control geopolymer concrete
(CGCs) containing crushed limestone and river sand (NA). This
was reasonable due to the particle shapes of aggregates, i.e. PA
was round, while CA and NA were angular. Additionally, the high
water absorption of fine and coarse PA was potentially because
the volume of water at the SSD condition of PA particles exceeded
those of CA and NA particles. Part of the water inside PA particles
was available and improved the workability of the mixture and led
to increases in slump values of concrete. However, the slump value
of LWGCs containing CA was slightly lower than that of CGCs containing NA. This was due to the rounder particle shape of river sand
than that of fine CA although the crushed limestone and coarse CA
exhibited similar particle shapes.
Additionally, the results clearly indicated that the slump value
of LWGCs also depended on the SS/SH ratio. The increases in the
SS/SH ratio decreased the slump value of LWGCs. This was due to
the high viscosity of SS that reduced the flow of mixtures. For
example, slump values of 263, 235, and 201 mm were obtained
with PA mixes with SS/SH ratios of 0.5, 1.0, and 1.5, respectively.
A previous study [21] reported a similar finding wherein the slump
values of fresh lightweight geopolymer concrete containing bottom ash as aggregates and high-calcium fly ash as geopolymer binder decreased with increases in the SS/SH ratio.
Fig. 3. Compressive strength and SS/SH ratios for various types of aggregates.
4.2. Compressive strength, splitting tensile strength and weight losses
from surface abrasion test
A summary of mechanical properties of LWGCs and CGCs
including compressive strengths, splitting tensile strengths, and
weight losses from the surface abrasion test at 7 d are given in
Fig. 2. Slump value and SS/SH ratios for various types of aggregates.
Fig. 4. Splitting tensile strength and SS/SH ratios for various types of aggregates.
Fig. 5. Weight losses from surface abrasion test and SS/SH ratios for various types
of aggregates.
A. Wongsa et al. / Construction and Building Materials 188 (2018) 1025–1034
replacement of normal strong crushed gravel aggregate with relatively weak PA. Debieb and Kenai [7] also reported that the compressive strength, flexural strength, and modulus of elasticity of
Portland cement-based concrete containing 100% fine and coarse
crushed brick were observed as lower than those of comparable
ordinary concrete. However, the maximum compressive strength
of LWGCs containing CA (18.3 MPa) and PA (7.0 MPa) in the study
was in the range of the compressive strength requirement for
structural lightweight concrete (17.0–41.0 MPa) and lightweight
moderate-strength concrete (2.0–14.0 MPa), respectively, based
on ACI Committee 213 [35]. Furthermore, the average ratios of
the splitting tensile strengths to compressive strengths of LWGCs
containing CA of 7.7% and PA of 10.3% slightly exceeded those of
CGCs containing crushed limestone and river sand (6.6%). It should
be noted that that the use of CA and PA as aggregates to produce
LWGCs resulted in significant improvements in the splitting tensile
strength for geopolymer concrete with similar compressive
strength. This is because the surface roughness and angular shape
of the crushed material were advantageous in terms of a good bond
between the geopolymer paste and the aggregates, and this
increased the splitting tensile strength performances [7].
1029
With respect to the effect of SS/SH ratio, the mechanical properties including compressive strength, splitting tensile strength, and
surface abrasion resistance of LWGCs containing CA and PA tended
to increase with increases in the SS/SH ratios as shown in Figs. 3–5.
For example, the SS/SH ratios of LWGC containing CA increased
from 0.5 to 1.5, compressive strength increased from 8.2 to
18.3 MPa, splitting tensile strength increased from 0.6 to 1.6 MPa,
and weight losses from the abrasion surface test decreased from
4.17 to 2.63 g. Visual observation of the fracture surfaces of LWGCs
specimens after the splitting tensile strength test are shown in
Figs. 6 and 7 and clearly indicated that the majority of failure of
LWGCs with SS/SH ratio of 0.5 occurred at the interface between
aggregate and geopolymer paste. Conversely, the failure surface
of LWGCs with SS/SH ratio of 1.0 and 1.5 exhibited several fractures through the aggregate particles. It should be noted that that
the increases in the SS/SH ratio increased the geopolymer paste
and bonding between aggregate and geopolymer paste. When
the LWGC approached the ultimate load, the cracks passed though
the zones as opposed to the interface between aggregate and
geopolymer paste. The result confirmed the findings in a previous
study by Eiamwijit et al. [46] who investigated the properties of
Fig. 6. Fracture surface of LWGCs containing CA as aggregates.
Fig. 7. Fracture surface of LWGCs containing PA as aggregates.
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A. Wongsa et al. / Construction and Building Materials 188 (2018) 1025–1034
fluidised bed coal combustion fly ash geopolymers with different
SS/SH mass ratios (1.0, 1.5, 2.0, and 2.5) and indicated that the high
SS/SH ratio mixes with increased water glass content led to dense
and homogeneous composites. Abdullah et al. [47] and Risdanareni
et al. [48] investigated the effect of SS/SH ratios (0.5, 1.0, 1.5, 2.0,
2.5, and 3.0) on the properties and morphology of geopolymer synthesis using low-calcium fly ash and indicated that geopolymers
gel with optimum SS/SH ratios exhibited a continuous matrix
and homogeneous and less porous microstructure. This was due
to the increases in the sodium oxide content in the system, which
was mainly required for the geopolymerisation reaction since
sodium oxide was used to balance the charges and formed the aluminosilicate network [49]. However, previous studies [21,50] also
reported that the compressive strength decreased when increased
silicate was added into the system because an excess of sodium silicate hindered water evaporation and structure formation. Furthermore, increases in SS/SH ratio also decreased the dosage of SH. At a
high SS/SH ratio, the leaching of alumina and silica decreased, and
this resulted in a low level of geopolymerisation, and thereby
decreased the strength. A similar effect was reported by El-Sayed
et al. [51] wherein geopolymer-based mortar with a dosage of 6%
SH achieved higher gains in compressive strength when compared
with a dosage of 2% SH, thereby clearly indicating the effect of the
SH dosage on the early compressive strength gain and on the
degree of geopolymerisation. As shown in the study, the compressive strength and splitting tensile strength of CGCs tended to
decrease with increases in the SS/SH ratios as shown in Figs. 3
and 4.
4.3. Density, thermal conductivity, and ultrasonic pulse velocity
The measured density, thermal conductivity, and ultrasonic
pulse velocity of LWGCs and CGCs are shown in Table 4. The results
indicated that the use of CA and PA as fine and coarse aggregates in
LWGC reduced the density and thermal conductivity. This was due
to the high porosity and low density of CA and PA and low density
of LWGCs. The densities of LWGCs containing CA (1685–1749 kg/m3)
and PA (1011–1111 kg/m3) were approximately 25% and 50%
lower than those of CGCs containing crushed limestone and river
sand (2258–2299 kg/m3). Furthermore, the densities of LWGCs
containing CA and PA were within the range of 1440–1850 and
1000–1400 kg/m3 for structural lightweight concrete and lightweight moderate-strength concrete as per ACI Committee 213 [35].
Previous studies reported that the ultrasonic pulse velocity and
the thermal conductivity are affected by the density of concrete
[52,53]. The thermal conductivity of LWGCs containing CA (0.62–
0.65 W/m K) and PA (0.20–0.22 W/m K) were approximately
3 and 7 times lower than those of CGCs containing crushed limestone and river sand due to the low density of aggregates and concretes. It was noted that the use of CA and PA as fine and coarse
aggregate to produce LWGCs exhibited good density and excellent
thermal insulation and were suitable for insulating purposes. The
Fig. 8. Relationship between thermal conductivity and density of LWGCs and CGCs.
relationship between the thermal conductivity and the density of
LWGCs and CGCs is plotted in Fig. 8. The correlation coefficient
of the results was high with R2 = 0.9972. As shown in the figure,
the thermal conductivity increased with increases in the concrete
density. The density and thermal conductivity are expressed as
follows:
T ¼ 0:037e0:0016D
ð1Þ
where T denotes the thermal conductivity (W/m K)
D denotes the dry density (kg/m3)
With respect to ultrasonic pulse velocity, the ultrasonic pulse
velocity is also directly related to porosity of concrete since discontinuities of pores in aggregate and concrete cause a delay in the
wave propagation [54]. A previous study [55] also reported that
the ultrasonic pulse velocity in concrete is significantly influenced
by the types and unit weight of aggregate and density of concrete.
In the study, the ultrasonic pulse velocities of the LWGCs containing CA (1985–2285 m/s) and PA (1586–1858 m/s) were significantly lower than that of CGCs containing NA (3089–3419 m/s).
This was due to the lower densities of CA and PA when compared
with that of NA as shown in Tables 1. The relationship between the
density and the ultrasonic pulse velocity of LWGCs and CGCs is
shown in Fig. 9. In a manner similar to the thermal conductivity
results, the ultrasonic pulse velocity increased with increases in
the concrete density and is expressed as follows:
U ¼ 957:16e0:0005D
ð2Þ
where U denotes the ultrasonic pulse velocity (m/s)
D denotes the dry density (kg/m3)
With respect to the ratio of alkali activators, the SS/SH ratios
slightly affected the density, thermal conductivity, and ultrasonic
pulse velocity of LWGCs and CGCs. For example, with respect to
the densities of 1111, 1011, and 1079 kg/m3, thermal conductivities
Table 4
Density, thermal conductivity, and ultrasonic pulse velocity of LWGCs and CGCs.
Mix
Density
(kg/m3)
Thermal conductivity
(W/m K)
Ultrasonic pulse velocity
(m/s)
NA-0.5
NA-1.0
NA-1.5
CA-0.5
CA-1.0
CA-1.5
PA-0.5
PA-1.0
PA-1.5
2258
2299
2272
1731
1685
1749
1111
1011
1079
1.41
1.58
1.58
0.62
0.62
0.65
0.21
0.20
0.22
3089
3419
3303
1985
2285
2173
1586
1745
1858
Fig. 9. Relationship between ultrasonic pulse velocity and density of LWGCs and
CGCs.
A. Wongsa et al. / Construction and Building Materials 188 (2018) 1025–1034
of 0.21, 0.20, and 0.22 W/m K and ultrasonic pulse velocities of
1586, 1745, and 1858 m/s, respectively, were obtained for LWGC
containing PA with SS/SH ratios of 0.5, 1.0, and 1.5, respectively. A
similar effect was reported in an earlier study [21] wherein the
effects of SS/SH ratios on the density, thermal conductivity, and
ultrasonic pulse velocity of high-calcium fly ash lightweight
geopolymer concrete containing bottom ash as aggregate were
not significant.
4.4. Change in appearance of the specimens after temperature
exposure
The changes in the physical appearance of CGCs and LWGCs
containing CA and PA cylinders at different temperature exposures
are shown in Figs. 10–12. The original colour of CGCs containing
NA and LWGCs containing PA was dark grey while that of CA
exhibited a red colour. All the concrete cylinders did not exhibit
a significant change in colour when exposed to various temperatures. The only visible difference was that the original colour
became lighter after exposure to higher temperatures at 400 °C,
600 °C, and 800 °C due to the high moisture loss at high
temperatures.
1031
Physical observations after the fire exposures also indicated
that the LWGCs suffered less damage in terms of spalling and
cracking when compared to the CGC. As shown in Figs. 10–12,
the CGC specimens suffer severe spalling and cracking at 600 °C
and 800 °C exposures, while the LWGCs containing CA and PA at
800 °C exposure contained a number of small cracks at the surface.
Based on Sarker et al. [56], the surface spalling and cracking of
geopolymer concrete occurred due to the temperature differential
between the surface and centre of the specimens. This also
occurred as a result of the differential strain that is caused by a
temperature gradient through the cross section of the concrete
[56]. Thus, the results indicated that the LWGCs containing CA
and PA in the study exhibited excellent fire resistance that is essential for its use as a building material.
4.5. Residual strength of geopolymer concretes after temperature
exposure
A summary of results of compressive strengths before and after
temperature exposure at 400 °C, 600 °C, and 800 °C are given in
Table 5. The LWGCs containing CA and PA gained some strength with
a residual strength of 146% and 104%, respectively, after exposure at
Fig. 10. CGCs containing NA as aggregate after exposure at 25 °C, 400 °C, 600 °C, and 800 °C.
Fig. 11. LWGCs containing CA as aggregate after exposure at 25 °C, 400 °C, 600 °C, and 800 °C.
1032
A. Wongsa et al. / Construction and Building Materials 188 (2018) 1025–1034
Fig. 12. LWGCs containing PA as aggregate after exposure at 25 °C, 400 °C, 600 °C, and 800 °C.
Table 5
Compressive strength and percentage residual strength of geopolymer concretes.
Temperature
(°C)
25
400
600
800
NA-1.0
CA-1.0
PA-1.0
Comp. strength (MPa)
(STD. dev)
Residual strength
(%)
Comp. strength (MPa)
(STD. dev)
Residual strength
(%)
Comp. strength (MPa)
(STD. dev)
Residual strength
(%)
36.0 (1.3)
13.7 (0.9)
4.1 (0.4)
3.0 (0.6)
100
38
12
8
17.5 (0.1)
25.6 (0.6)
14.5 (0.4)
6.9 (0.1)
100
146
83
39
7.0
7.4
3.3
2.0
100
104
47
29
400 °C. This was potentially due to the loss of water in the system
due to sintering at the aforementioned temperature and a combination of geopolymer matrix and aggregates (CA and PA). This was the
main factor that contributed to the higher bonding and residual
strength following exposure at 400 °C. This is consistent with the
visual observations of the failure characteristics after the compressive strength test as shown in Fig. 13. The CGCs specimen showed
complete disintegration, and the LWGCs specimens containing CA
and PA exhibited large fragments of specimens. After the exposure
at 600 °C and 800 °C, the LWGCs exhibited residual strengths of
83% and 39% for CA-1.0 and 47% and 29% for PA-1.0, respectively.
(0.3)
(0.3)
(0.1)
(0.0)
With respect to the residual strength of CGC, CGCs containing
NA suffered from significant strength loss following exposure to
high temperature. The residual strength of CGCs after temperature
exposure at 400 °C, 600 °C, and 800 °C decreased by 38%, 12%, and
8%, respectively. The trends of strength reduction in the CGC specimens were similar to those observed by Sarker et al. [56] and
Abdulkareem et al. [57]. Based on Sarker et al. [56], the strength
loss in the geopolymer concrete specimens after exposure at
400 °C, 650 °C, 800 °C, and 1000 °C was attributed to the difference
between the thermal expansions of geopolymer matrix and aggregates [57]. However, the results also indicated that the LWGCs
Fig. 13. Failure characteristics of compressive strength test specimens after exposure at 400 °C.
A. Wongsa et al. / Construction and Building Materials 188 (2018) 1025–1034
containing CA and PA exhibited higher residual strength relative to
that of CGCs at all three exposure temperatures. When compared
with CGCs, LWGC exhibited less cracking and spalling and higher
residual compressive strength, and thus the performance of LWGCs
exceeded that of CGCs.
4.6. Density, thermal conductivity, and ultrasonic pulse velocity after
temperature exposure
Table 6 summarises the results of density, thermal conductivity,
and ultrasonic pulse velocity of LWGCs and CGCs after the temperature exposure at 400 °C, 600 °C, and 800 °C. The results indicated
that the densities of LWGCs and CGCs decreased with increases in
the exposure at elevated temperatures. This was due to the loss of
moisture in aggregates and alkaline solution contents in concrete
and surface spalling of specimens. The density losses of the LWGCs
containing PA significantly exceeded those of CA and NA. Following
the temperature exposure at 400 °C, 600 °C, and 800 °C, the densities of the PA-1.0 decreased by 24%, 29%, and 31%, the densities of
the CA-1.0 decreased by 14%, 17%, and 18%, and the densities of the
NA-1.0 decreased by 5%, 6%, and 7%, respectively. This was because
the water absorption of PA exceeded those of CA and NA. There is
generally a complete loss of mass due to elevated temperature
exposure in concrete that significantly impacts the compressive
strength of the sample [56]. However, the mass losses at 400 °C
temperature exposure in the study did not adversely affect the
compressive strength of the LWGCs containing CA and PA.
The thermal conductivity measured after the temperature
exposure was also directly related to the density of concrete as
shown in Table 6. The increase in high temperature exposure contributed to increases in the loss of moisture and alkali solution and
specimen porosity, thereby leading to decreases in the density and
thermal conductivity of the concrete. For example, when the exposure to elevated temperatures increased from 25 °C to 800 °C, the
density decreased from 2339 to 2099 kg/m3 for CGCs containing
NA, 1961 to 1638 kg/m3 for LWGCs containing CA, and 1357 to
1016 kg/m3 for LWGCs containing PA. Similarly, the thermal conductivity decreased from 1.75 to 0.91 W/m K for CGCs containing
NA, 0.70 to 0.57 W/m K for LWGCs containing CA, and 0.26 to
0.23 W/m K for LWGCs containing PA.
With respect to the ultrasonic pulse velocity results after the
temperature exposure, the ultrasonic pulse velocity values were
consistent with the density and the residual strength results of
concrete. This is consistent with the results obtained in a study
by Ghosh et al. [58]. The study explained the ultrasonic pulse
velocity in situ test for assuring the quality of concrete and
reported that the fly ash-based geopolymer concrete ultrasonic
pulse velocity value increased with increases in the compressive
Table 6
Density, thermal conductivity, and ultrasonic pulse velocity of geopolymer concretes
after temperature exposure.
Mix
Density
(kg/m3)
Thermal conductivity
(W/m K)
Ultrasonic pulse velocity
(m/s)
NA-1.0-25
NA-1.0-400
NA-1.0-600
NA-1.0-800
CA-1.0-25
CA-1.0-400
CA-1.0-600
CA-1.0-800
PA-1.0-25
PA-1.0-400
PA-1.0-600
PA-1.0-800
2339
2212
2162
2099
1961
1700
1652
1638
1357
1079
1023
1016
1.75
1.32
1.04
0.91
0.70
0.58
0.57
0.57
0.26
0.23
0.22
0.23
3419
1480
393
–
2285
2306
1299
1296
1745
1832
1108
1081
1033
strength [59]. Furthermore, Mohammed and Rahman [55] also
observed that the ultrasonic pulse travelled faster in dense concretes when compared to that in poor quality concretes. In the
study, the compressive strength and the ultrasonic pulse velocity
of LWGCs containing CA and PA with exposure at 400 °C exhibited
higher values than those exposed to 25 °C, 600 °C, and 800 °C,
respectively. It should be noted that that a high temperature exposure up to 400 °C can be used to improve the quality of LWGCs containing CA and PA. However, the precise values of ultrasonic pulse
velocity in the NA-1.0–800 specimens with the lowest residual
strength are not determined due the surface spalling and cracking
of the specimens as shown in Fig. 10(d).
5. Conclusions
In the study, the results indicated that the use of crushed clay
brick (CA) and PA to produce lightweight geopolymer concretes
(LWGCs) exhibited lower compressive strength, splitting tensile
strength, surface abrasion resistance, density, thermal conductivity, and ultrasonic pulse velocity when compared to those of
geopolymer concrete containing natural aggregate (CGCs). However, the compressive strength and density of LWGCs containing
CA (8.2–18.3 MPa and 1685–1749 kg/m3) and PA (2.7–7.0 MPa
and 1011–1111 kg/m3) revealed that the mixes with highest compressive strength was in the range of the required values for structural lightweight concrete and lightweight moderate-strength
concrete as per ACI Committee 213. Furthermore, the LWGCs containing CA and PA exhibited thermal insulation and residual
strength exceeding those of CGCs at exposure temperatures corresponding to 400 °C, 600 °C, and 800 °C.
Conflict of interest
None declared.
Acknowledgements
The authors would like to acknowledge the financial supports
from the Post-Doctoral Training Program from Research Affairs
and Graduate School, Khon Kaen University, Thailand (Grant No.
59254); the Thailand Research Fund (TRF) and Khon Kaen University under the Royal Golden Jubilee Ph.D. Program (Grant No. PHD
0083/2556), the TRF Basic Research Grant (Grant No. BRG6080010)
and the TRF Distinguished Research Professor (Grant No.
DPG6180002).
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