properties of partition wall blocks prepared with high percentages of recycled clay brick after...
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Original citation:
Xiao, Z, Ling, T.-C., Poon, C.-S., Kou, S.-C., Wang, Q, Huang, R. (2013) Properties of
partition wall blocks prepared with high percentages of recycled clay brick after
exposure to elevated temperatures. Construction and Building Materials; 49:56-61.
http://www.sciencedirect.com/science/article/pii/S0950061813007344
Properties of partition wall blocks prepared with high percentages of
recycled clay brick after exposure to elevated temperatures
Xiao, Z, Ling, T.-C., Poon, C.-S., Kou, S.-C., Wang, Q, Huang, R.
Research Highlights
• High temperature properties of concrete blocks made with clay brick aggregate
(CBA) were examined.
• At 300°C, the nature of CBA origin made the concrete blocks stronger/more stiff.
• At 800°C, a higher percentage of CBA used enabled a higher residual flexural
strength.
• At 800°C, CBA blocks retained about 48-91% of their original (20°C) compressive
strength.
Abstract
High temperature properties of partition wall concrete blocks prepared with recycled
clay brick aggregate derived from construction and demolition (C&D) waste streams
(e.g. collapsed masonry after an earthquake) were studied. For this purpose three series
of concrete block mixes were designed using coarse and fine clay brick aggregate to
replace recycled concrete aggregate and sand at ratios percentages of 25%, 50% 75%
and 100%. The residual density, mass loss, compressive and flexural strengths after
exposure to elevated temperatures of 300°C, 500°C and 800°C were determined. The
results demonstrated that selection of an appropriate replacement for both coarse and
fine clay brick aggregates can lead to better performance of the blocks at elevated
temperatures. It is expected therefore that there will be significant advantages in terms
of sustainability and fire safety by adopting this inherent fire-resistant material in
concrete blocks especially for low rise residential developments.
Keywords: Clay brick aggregate, recycled concrete aggregate, elevated temperatures,
concrete blocks, compressive strength, flexural strength
1. Introduction
A huge quantity of construction and demolition (C&D) waste, which constitutes a
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major portion of the total solid waste stream, is generated every day [1]. The C&D
waste includes, but is not limited to, demolished concrete, bricks, masonry, wood, steel,
plaster, etc. According to a study by Xiao et al. [2] who reported that in the 2008
Sichuan earthquake about 382 million tonnes of construction waste derived mainly
from collapsed buildings was generated. Most recently, a 6.6-magnitude earthquake hit
Ya’an city, Sichuan Province on 2013 April 20, killing at least 192 people and injuring
thousands [3]. It has been estimated that 90% of all houses in the Ya’an area collapsed
due to this earthquake [3], resulting in huge quantities of waste. The nature of waste
generated by earthquakes in China has created a great challenge in its disposal and its
impact on the environment has also drawn considerable attention.
For the past few decades, systematic management systems and methods of recycling
the C&D waste have been extensively discussed in the literature [4-7]. Among them, it
is commonly accepted that recycling and reuse of C&D waste as an alternative
aggregate in construction is one of the most economic and environmentally friendly
ways of managing the waste. In addition to the environmental benefits in reducing the
demand for land in which to dispose of the C&D waste, the recycled aggregates derived
from the waste can also help to conserve natural materials.
A large number of studies has focused on reusing recycled concrete aggregate (RCA) to
produce new concrete. The potential benefits and shortcomings of using RCA have
been well researched [8-12]. Partial replacements of natural aggregates by RCA (30%
or less) in concrete do not jeopardize the mechanical properties [9]. However, it is
generally agreed that the compressive strength of concrete gradually decreases as the
amount of RCA increases [10]. Furthermore, the high water absorption properties of
recycled fine aggregate significantly affect durability by inducing excessive shrinkage
problems in concrete [11,12]. The above mentioned drawbacks therefore restrict the use
of recycled fine aggregate in concrete and limit the amount of RCA that can be used for
structural concrete.
In comparison to wet-mixed conventional concrete, a number of studies [13-16] has
demonstrated that it is feasible to incorporate up to 100% RCA as coarse and fine
aggregates for the production of non-structural precast concrete blocks using a
dry-mixed approach. This is probably due to the use of a combination of vibration and
compaction forces in the dry-mixed production process that could improve the density
(packing) and the quality of the concrete products produced.
A preliminary study was conducted to investigate the influence of the incorporation of
crushed clay brick as a replacement for coarse RCA and natural sand on the properties
of dry-mixed masonry partition wall blocks [16]. It was found that the hardened density
and drying shrinkage of the blocks decreased with increase in the clay brick aggregate
content. The overall results suggested that the replacement percentage of coarse
aggregates by crushed clay brick should be controlled at less than 25%, while the
replacement of natural sand by fine crushed clay brick should be within 50-75%.
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As for building applications, masonry partition wall blocks prepared with recycled
aggregates (RCA and clay brick aggregates) may be affected by fire. The aim of the
present work is to study the properties of partition wall concrete blocks after being
subjected to elevated temperatures of 300°C, 500°C and 800°C. The residual high
temperature properties (compressive and flexural strengths) and the total mass loss of
concrete blocks prepared with coarse and fine crushed clay brick to replace recycled
concrete aggregate and natural river sand at different (25%, 50%, 75% and 100%)
ratios were examined.
2. Experimental details
2.1. Materials
The cementitious material used in this work was an ASTM type 1 ordinary Portland
cement (OPC) with a density of 3160 kg/m3. The recycled concrete aggregate (RCA)
used was obtained from a recycling facility located in Hong Kong. At the facility,
crushed concrete rubble (from demolition projects) was crushed and processed to
produce coarse recycled aggregate with particle sizes between 5 and 10 mm. Crushed
clay brick originally from red bricks were produced by crushing and sieving them into
two different particle sizes: 5-10 mm (coarse brick aggregate CBA) and <5 mm (fine
brick aggregate FBA). River sand with a maximum size of 2.36 mm was used as the
fine natural aggregate in this study. The physical properties of all coarse and fine
aggregates were tested according to BS 882 (1992) and ASTM C128 and the results are
presented in Table 1. The photographs and grading curves of these aggregates are
shown in Figs. 1 and 2.
2.2. Partition wall block mix proportions
A total of three series of partition wall block mixtures were designed (see Table 2) and
fabricated in the laboratory using a dry-mixed method described in our previous studies
[16,17]. The block specimens produced aimed to meet the requirements stipulated by
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the BS 6073 (1981) specification for partition wall blocks. All the mixtures were
proportioned with a fixed total aggregate/cement ratio of 11.5, and 65% of the total
aggregate was fine aggregates (<5 mm). In each of the mix series, five different mix
proportions were prepared.
In Series 1 and 2, the influence of using crushed clay brick for sand replacement (fine
aggregate) at 25%, 50%, 75% and 100% was examined. The coarse aggregates with
RCA/CBA ratios of 3 and 1 were fixed in Series 1 and 2 respectively. For Series 3, the
effect of using crushed clay brick as coarse aggregate was investigated with RCA being
replaced by CBA at 25%, 50%, 75% and 100% by weight, while a fixed sand/FBA ratio
of 1 was used (in fine aggregate). The details of the mix proportions are shown in Table
2.
Each concrete block was fabricated by applying a compaction stress of 25 N/mm2 on
the materials in steel moulds with internal dimensions of 200×100×60 mm. The
fabricated block specimens were then covered with a plastic sheet and left at room
temperature of 23±3 °C and 75±5% relative humidity (RH). After one day, they were
demoulded and further cured (covered by a hemp bag to maintain a RH of over 90%) at
room temperature of 23±3 °C for at least 28 days before testing.
2.3. Heating temperature and testing
The specimens were heated to 300°C, 500°C and 800°C separately. The heating rate
was set at 2.5°C per minute until the target temperature was reached and the respective
maximum temperature was maintained for 4 h to ensure uniform temperature
distribution throughout the specimens. The specimens were allowed to cool naturally to
room temperature prior to testing.
The mass of the concrete blocks before and after each heating cycle was determined
using an electronic digital balance with an accuracy of ±0.1 g. The mass loss values
were calculated according to Mloss = (Minitial - Mheated)/ Minitial, where Minitial and Mheated
are the initial mass (before heating) and the heated mass (after heating) respectively.
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The compressive strength was determined by using a universal testing machine with a
maximum capacity of 3000 kN. A loading rate of 450 kN/min was applied to the
nominal area of the block specimen. Prior to the loading test, the block was soft capped
with two pieces of plywood. Three samples were tested after heating to each
temperature and the average values are reported.
The flexural strength of the block specimens was determined by a three-point bending
test with a supporting span of 180 mm. For this test, a test machine with a maximum
load capacity of 50 kN was used and a displacement of 0.10 mm/min was set. Two
samples were tested for each group of specimens.
3. Results and discussion
3.1. Initial density and mass loss
The dry hardened densities of fabricated concrete blocks before being exposed to the
elevated temperatures are shown in Fig. 3. The density of the concrete blocks decreased
with increase in clay brick content. These results can be explained by the lower density
of the recycled brick aggregate as compared to both sand and RCA (see Table 1).
The mass loss of the heated specimens at 300°C, 500°C and 800°C are shown in Figs.
4-6 respectively. In general, the data show that the percentage of mass loss for Series 1
and 2 block specimens increased with increase of FBA content. It is clear that the
replacement of sand with clay brick with a much higher water absorption capacity
somewhat increased the mass loss. This was particularly noticeable at 300°C because
the mass loss at this temperature was mainly accounted for by the loss of the absorbed
water in the aggregates and the free water in the cement matrix. Beyond this
temperature, the effect of aggregate types on mass loss appeared to be less significant.
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On the contrary, the mass loss value of the block specimens in Series 3 decreased when
the CBA content in the mixtures increased. In this case, it seems that the water
absorption capacity of the aggregates was not the only reason affecting the mass loss of
the heated blocks. Loss of bound water from the dehydrated old-cement paste attached
to the RCA might have contributed to the additional mass loss as the temperature
reached 500°C and above.
3.2. Compressive strength
The effects of using coarse and fine clay brick for RCA and sand replacements on the
compressive strength at ambient temperature (20°C) have been previously discussed
[16]. Figs. 7-9 show the trend of compressive strength at the elevated temperatures for
Series 1-3 block specimens.
Regardless of the aggregate type, all the heated concrete blocks at 300°C and 500°C
exhibited higher compressive strength than that at 20°C. The increases in compressive
strengths of the concrete blocks with clay brick aggregates at these temperatures can be
attributed to a few reasons. First, the nature of the clay brick made them stronger/more
stiff under these temperatures as Nguyen et al. [18] reported that the compressive
strength of a pure clay brick is twice the original strength after exposure to 400°C.
Second, some of the unhydrated cement paste might undergo additional hydration at
these temperatures [19] as the high temperature could increase the degree of
crystallinity of originally formed hydrates [20] which helps to improve their cementing
ability and the concrete’s strength.
It can be seen that the influence of FBA content was very similar at 300°C and 500°C
(see Figs. 7 and 8), where the blocks with 25-50% and 50-75% of FBA content
displayed the highest strength in Series 1 and 2 respectively. In Series 3 (Fig. 9), an
increase in the CBA content resulted in a decrease in the compressive strength at
ambient temperature. However, above this temperature the CBA concrete blocks had
more or less similar residual strengths as compared to that of the reference mixture
(with 100% of RCA). This reveals that the coarse brick aggregate performed better at
high temperatures than the recycled concrete aggregate.
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It can be seen from the above figures and Table 3 that all the compressive strengths
obtained at 800°C were lower than the initial strength (at ambient temperature). Such
results were not unexpected due to the decomposition of the new calcium silicate
hydrates (CSH) of the cement paste and the old cement mortar adhering to the RCA. In
comparison, Series 1 concrete blocks with a higher RCA/CBA ratio experienced a
slightly higher reduction of strength as compared to the concrete blocks in Series 2. It is
worth noticing that at this temperature, the Series 1-3 concrete blocks maintained
48-73%, 62-75% and 48-91% of their respective initial strengths, depending on the
content of clay brick aggregate used. This shows that the higher the clay brick
aggregate content is, the higher the strength that can be retained. This points to a
potential application of the blocks containing clay brick in high temperature conditions
(compared to normal concrete only 10-30% of its original strength can be retained after
exposure to high temperature at 800°C [21-23]).
3.3. Flexural strength
Figs. 10-12 show the effects of high temperature on flexural strength. It can be clearly
seen that the content and type of aggregate used had a similar influence at 20°C and
300°C. This is particularly noticeable when the replacement level of sand by clay brick
was up to 100%. For instance, the flexural strength of S1-100, S2-100 and S3-100
mixes at 300°C were enhanced by 27%, 24% and 15% respectively when compared to
their original strength obtained at the ambient temperature. The improvement in
flexural strength can be partly accounted for by the better bonding behaviour of the clay
brick aggregates at this temperature. This is in agreement with the finding by Lea and
Straddling [24], who indicated that the higher gain in flexural strength of concrete at
temperatures up to 300°C was mainly attributed to the increase of bond strength
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between the aggregate and the paste.
Unlike compressive strength, at the temperature of 500°C the flexural strength suffered
higher losses ranging from 20-54%, regardless of the content and type of aggregate
used. Apart from the dehydroxylation of calcium hydroxide (CH) occurring at
300-500°C [25,26], it seems that the microcracking which occurred at this temperature
affected flexural strength (further weakening the bond and the interfacial transition
zone in the cement matrix) more than it did the compressive strength. This is because
generally the flexural strength is more sensitive to the presence of such cracks than
compressive strength.
Beyond 500°C, a continuous drop in the flexural strength was observed and only a
small part of the initial strength was left at 800°C. This is particularly obvious for
control mixes, as S1-0, S2-0 and S3-0 only retained 8%, 10% and 12% of their initial
strength respectively. The decrease in flexural strength at this temperature is known to
be affected mainly by the dehydration of CSH gels as well as the transformation of
quartz (silica sand) occurring early at 570°C [27]. This also explains why the control
(reference blocks containing 100% of sand as fine aggregates) had the highest loss in
strength than those blocks made with clay brick aggregate (see Table 4).
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4. Conclusion
This study focused on the behaviour of partition wall concrete blocks after exposure to
elevated temperatures. The residual density, mass loss, and evolution of compressive
and flexural strengths of the block specimens prepared with recycled concrete and brick
aggregate were determined after heating cycles up to 300°C, 500°C and 800°C.
At 300°C, all the concrete blocks show better compressive and flexural strengths than
that at room temperature due to the natures of the clay brick making the blocks
stronger/more stiff. A decrease in both the compressive and flexural strengths was
observed between 300°C and 500°C which was mainly attributed to the
dehydroxylation of calcium hydration and the development of microcracks. The
microcracking at this temperature seemed to have a more detrimental effect on the
flexural strength than on compressive strength. Up to 800°C, the dehydration of CSH
gels caused a greater degree of strength loss. Only a small part (8-41%) of the initial
flexural strength was retained in all the concrete blocks. However the blocks were still
able to retain about 48-91% of their original compressive strength.
As far as compressive strength at elevated temperatures is concerned, the optimum
replacement level of sand by fine clay brick aggregate were determined to be 25-50%
for Series 1 and 50-75% for Series 2. As for Series 3, the incorporation of coarse clay
brick aggregate seemed to offset the detrimental effect observed at ambient temperature.
Also, it was found that the use of clay brick aggregate had more favourable effects on
flexural strength than on compressive strength. At all the maximum temperatures tested,
particularly at 800°C, a higher percentage of brick aggregate used enabled a higher
residual flexural strength.
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Acknowledgements
The authors wish to acknowledge the State Key Laboratory of Geohazard Prevention
and Geoenvironment Protection (SKLGP2012K002) and The Hong Kong Polytechnic
University for funding support.
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