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ABSTRACT
Utilisation of waste plastic materials as aggregates in concrete manufacturing could be partial
solution to the environmental and ecological challenges associated with the use of plastics.
This study examines the possibility of using waste High Density Polyethylene (HDPE) as a
partial replacement for coarse aggregate in concrete formulation at various plastic
compositions (0%, 2%, 4%, 6% and 8% by weight of the coarse aggregate). Particle size
distribution (PSD) and specific gravity tests were conducted for the plastic aggregates. The
influence of the waste HDPE on the fresh and hardened state properties of the concrete, the
workability, compressive and flexural strengths were investigated in comparism to the
control. The effect of water on the compressive strength of the composite was also
determined for the various compositions. Results of various tests suggest that workability of
the fresh concrete decreased with increasing plastic content. The compressive strength of the
concrete decreased appreciably with increase in the plastic content and was found to also be
lower than normal concrete. The 28th
day flexural strength decrease marginally with increase
in plastic content in the concrete. Also the mass of water absorbed by the concrete samples
increased with the increasing plastic content. Despite the effects of waste HDPE on the
various properties of the composite, results were all found to be within acceptable limits.
Thus the use of waste plastic materials could be considered for use in formulation of
concrete.
1. INTRODUCTION
In Ghana lack of sustainable waste management techniques by our local authorities has led to
most of the plastic waste not collected or disposed of properly in an appropriate manner. In
most towns and cities the waste plastics are thrown into municipal waste collection centers
from where it is collected by the local authorities for further disposal into landfills and
dumpsites. However, not all of these wastes gets collected and transported to the final
dumpsites. As a result the waste plastic can pose serious problems which include contributing
to blockage of drains and gutters which can cause flooding, release of toxic gas into
atmosphere when they are burnt, choking of livestock and aquatic species when they mistake
them for food, breeding ground for mosquitoes when the plastic materials are filled with
rainwater and pose disposal and ecological problems as plastics take several years to degrade.
Available options for dealing with plastic waste are recycling, reduction, reuse of plastics and
recovering of waste plastic which cannot be reduced, reused or recycled. In the developed
countries, recycling technology has been the solution of choice but in developing countries,
like Ghana it may not be economically viable since it is heavily capital intensive (UNEP,
2009).
Waste Low Density Polyethylene (LDPE) can be converted into high energy hydrocarbon
fuels by a thermal degradation process (Sarker et al., 2011). The fuel produced by recycling
of waste plastic can be alternative to petrol, diesel etc. Ghana and many developing countries
are currently experiencing rapid urbanization and industrialization and as a result a lot of
infrastructure developments are going on in these countries. However, infrastructure
developments are plagued with problems such as acute shortage of construction materials,
sky rocketing prices of construction materials and increased generation of waste. Plastic is
one major component of Municipal Solid Waste (MSW) which is becoming a major research
issue for its possible use in concrete. There have been successful replacement or partial
replacement of aggregates or filler components of concrete with industrial waste such as fly
ash and wood chips in concrete (Bignozzi et al., 2000). Waste plastics of various types can be
used as partial replacements of aggregates in the manufacturing of concrete (Mostafizur et
al., 2012). For instance Expanded polystyrene (EPS) based waste, High Density Polyethylene
(HDPE), Polyethylene Terephthalate (PET) waste bottles, Polypropylene fibers and
Polyethylene bags have all been used in different forms by researchers in concrete. In this
study high density polyethylene bottles which forms 19% of waste plastic in municipal solid
waste (Sarker, 2010) was shredded into flakes and used as a partial replacement of coarse
aggregate in concrete.
2. EXPERIMENTAL DETAILS
2.1 Materials
2.1.1Cement
Ordinary Portland limestone cement manufactured by Ghacem CEM II/BL 33.5R was used
for casting the cubes and beams for all the concrete mixes. The cement was of uniform grey
colour and free from any hard lumps and was bought from a local vendor.
2.1.2 Fine Aggregates
Ordinary pit sand used for the experimental program was procured locally from Fumesua, a
town in the Ejisu Municipality. The sand was first dried, passed through a 5mm sieve to
remove any particles greater than 5mm including roots and debris. Sieve analysis was
conducted to determine the particle size distribution using Malest Auto sieve shaker.
2.1.3 Coarse Aggregates
Locally available coarse aggregates/granite supplied by local supplier having maximum size
of 19mm was used in this work. Particle size distribution of the coarse aggregate was also
obtained using Malest Auto sieve shaker.
2.1.4 Polymeric Material
High density Polyethylene (HDPE) bottles identified using its recycled code was collected
from the environment and used in the work. The labels on the bottles were removed and the
bottles were then washed, cleaned, dried and cut or shreded into smaller flake sizes manually
using table knife and scissors. The recycled plastic wastes were used to replace coarse
aggregate for making the concrete specimens. The specific gravity test was conducted on the
plastic aggregates and the Malest Auto sieve shaker was also used for the particle size
distribution of the plastic aggregates.
2.1.5 Water
Generally water that is satisfactory for drinking is also suitable for use in concrete. In this
work portable water suitable for human consumption was employed in the experimental
procedures.
2.2 Particle Size Distribution
The aggregates were weighed and then placed on the first sieve of the arranged series of
sieves of the Malest Auto sieve shaker and the machine was turned on. The sieve shaker
shakes the aggregates with some aggregates passing through some sieves and others retained.
After 10 minutes the sieve shaker automatically stops and aggregates retained in the
respective sieves were weighed for their masses. The particle size distribution curve for all
the aggregates are displayed in figure 1.0.
Figure 1.0 Particle Distribution curve for all aggregates
2.3 Mixing, Casting, Curing
The control mix has a mix ratio of 1:2:3 (cement: fine aggregate: coarse aggregate) which
was adapted for this work with a constant water- cement ratio of 0.55. For making mixes
containing plastics, the amount of plastic were calculated as 2%, 4%, 6% and 8% by weight
of the coarse aggregate in the control concrete. The aggregates were mixed with water under
the standard practice of mixing them in a concrete mixer and mixing ceased as soon as a
homogenous mixture was obtained. A total of 64 cubes and 10 beams specimen were cast for
this experiment.
Cement
(kg)
Fine
aggregate
(kg)
Coarse
aggregate
(kg)
Plastic
aggregate
(kg)
Water
(litres)
CONTROL 4.5 9.0 13.5 0.0 2.475
2% HDPE 4.5 9.0 13.23 0.27 2.475
4% HDPE 4.5 9.0 12.96 0.54 2.475
6% HDPE 4.5 9.0 12.69 0.81 2.475
8% HDPE 4.5 9.0 12.42 1.08 2.475
Table 1.0 Mix proportion for cube samples
3.0 RESULTS AND DISCUSSION
3.1 Workability (Slump test)
The ease of flow or workability of the freshly prepared concrete was observed to have zero
slump at 6% and 8% HDPE replacement. It was observed generally that the slump height
decreases as the percentage replacement of coarse aggregate with waste HDPE increases.
Figure 2.0 shows the results obtained for the slump height at various HDPE percentage
replacement.
Figure 2.0 Slump Height of various percentage replacement
3.2 Compressive Strength
It was observed that the compressive strength increased with increasing curing age for all
percentage replacement, a trend which is similar to that of the control. However it can be
deduced that incorporation of waste content in the concrete lowers compressive strength of
the hardened concrete and reduces further as the percentage replacement increases
Figure 3.0 Compressive strength for all concrete samples
3.3 Flexural Strength
Results of flexural strength indicates that the strength decreased systematically with
increasing percentage of plastic content but however the flexural strength remained the same
with 2% and 4% replacement of coarse aggregate with waste HDPE.
Figure 4.0 Flexural strength for all percentage replacements
3.4 Water Absorption
Air dried cubes specimens were weighed for their masses and then the dried samples were
placed in an oven at a constant temperature of 107o
C for 24 hours to ensure the samples were
completely dried with a constant mass. After 24 hours the cube specimens were removed and
their masses noted and recorded. The samples were allowed to cool in the laboratory and then
immersed in clean water for 24 hours. After 24 hours of immersion in water the specimens
were removed and their masses weighed.
The percentage absorption of water was then calculated using the formula.
2 1
2
% 100%
W W
Waterabsorption
W
−
= ×
Where W1 is the oven dry mass of the test specimen
W2 is the wet mass of the test specimen
It was observed that the percentage mass of water absorbed by the concrete specimens
increased linearly with the increase in waste plastic content with the control concrete
absorbing 2.507% whiles 8% HDPE replacement absorbed the most with 3.391%
Figure 5.0 Percentage mass of water absorbed by concrete samples
.
4.0 CONCLUSION
After the preliminary test on the concrete samples the following conclusions were made on
the HDPE modified concrete
• There was decrease in the workability of the concrete with increase in the percentage
of waste plastic content in the concrete.
• The compressive strength of all the concrete samples increased with increasing curing
days.
• The compressive strength for the normal concrete was higher than the compressive
strength of concrete samples containing HDPE plastic and also decreased with
increasing plastic content in concrete.
• The flexural strength of the specimens after 28 days decreased marginally with
increase in waste plastic content.
• The percentage mass of water absorbed by the concrete samples also increased with
increasing plastic content.
It has been identified that the use of waste HDPE as partial replacement of aggregate in
concrete has some effect on the properties of the concrete but the results are all within the
acceptable strength development properties. Waste HDPE could therefore be used as a
cheap alternative to replace aggregate partially in construction especially in the
formulation of concrete.
REFERENCES
Bignozzi M.,Saccani A.,Sandrolini F.,(2000). “New polymer mortars containing polymeric
waste.Part 1: microstructure and mechanical properties”, Composites: Part A 31,p. 97-
98.
Mostafizur R., Akhtarul I., and Mainuddin A., (2012). “Recycling of waste polymeric
materials as partial replacement for aggregates in concrete” International Conference
on Chemical, Environmental and Biological Sciences, Penang, Malaysia, p. 99-101.
Sam R., Bamford A., Fletcher J., Ofosu G., Fuseini A.,(2013). “Assessment of quality of the
various brands of Portland cement products available on the Ghanaian market”,
International Journal of Science and Technology, Vol. 2, No 3.p. 254-258.
Sarker M.,Momunor R.,Rahman S.,(2011). “Agricultural waste plastics conversion into high
energy liquid hydrocarbon fuel by thermal degradation process”, Journal of Petroleum
Technology and Alternative Fuels, Vol. 2(8), p. 141-142.
United Nations Environmental Program (UNEP), Division of Technology, Industry and
Economics (2009).“Converting waste plastic into a resource”, p.14-16.
Sam R., Bamford A., Fletcher J., Ofosu G., Fuseini A.,(2013). “Assessment of quality of the
various brands of Portland cement products available on the Ghanaian market”,
International Journal of Science and Technology, Vol. 2, No 3.p. 254-258.
Sarker M.,Momunor R.,Rahman S.,(2011). “Agricultural waste plastics conversion into high
energy liquid hydrocarbon fuel by thermal degradation process”, Journal of Petroleum
Technology and Alternative Fuels, Vol. 2(8), p. 141-142.
United Nations Environmental Program (UNEP), Division of Technology, Industry and
Economics (2009).“Converting waste plastic into a resource”, p.14-16.

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Influence of recycled Waste High Density Polyethylene Plastic aggregate on mechanical properties of concrete

  • 1. ABSTRACT Utilisation of waste plastic materials as aggregates in concrete manufacturing could be partial solution to the environmental and ecological challenges associated with the use of plastics. This study examines the possibility of using waste High Density Polyethylene (HDPE) as a partial replacement for coarse aggregate in concrete formulation at various plastic compositions (0%, 2%, 4%, 6% and 8% by weight of the coarse aggregate). Particle size distribution (PSD) and specific gravity tests were conducted for the plastic aggregates. The influence of the waste HDPE on the fresh and hardened state properties of the concrete, the workability, compressive and flexural strengths were investigated in comparism to the control. The effect of water on the compressive strength of the composite was also determined for the various compositions. Results of various tests suggest that workability of the fresh concrete decreased with increasing plastic content. The compressive strength of the concrete decreased appreciably with increase in the plastic content and was found to also be lower than normal concrete. The 28th day flexural strength decrease marginally with increase in plastic content in the concrete. Also the mass of water absorbed by the concrete samples increased with the increasing plastic content. Despite the effects of waste HDPE on the various properties of the composite, results were all found to be within acceptable limits. Thus the use of waste plastic materials could be considered for use in formulation of concrete. 1. INTRODUCTION In Ghana lack of sustainable waste management techniques by our local authorities has led to most of the plastic waste not collected or disposed of properly in an appropriate manner. In most towns and cities the waste plastics are thrown into municipal waste collection centers from where it is collected by the local authorities for further disposal into landfills and dumpsites. However, not all of these wastes gets collected and transported to the final dumpsites. As a result the waste plastic can pose serious problems which include contributing to blockage of drains and gutters which can cause flooding, release of toxic gas into atmosphere when they are burnt, choking of livestock and aquatic species when they mistake them for food, breeding ground for mosquitoes when the plastic materials are filled with rainwater and pose disposal and ecological problems as plastics take several years to degrade.
  • 2. Available options for dealing with plastic waste are recycling, reduction, reuse of plastics and recovering of waste plastic which cannot be reduced, reused or recycled. In the developed countries, recycling technology has been the solution of choice but in developing countries, like Ghana it may not be economically viable since it is heavily capital intensive (UNEP, 2009). Waste Low Density Polyethylene (LDPE) can be converted into high energy hydrocarbon fuels by a thermal degradation process (Sarker et al., 2011). The fuel produced by recycling of waste plastic can be alternative to petrol, diesel etc. Ghana and many developing countries are currently experiencing rapid urbanization and industrialization and as a result a lot of infrastructure developments are going on in these countries. However, infrastructure developments are plagued with problems such as acute shortage of construction materials, sky rocketing prices of construction materials and increased generation of waste. Plastic is one major component of Municipal Solid Waste (MSW) which is becoming a major research issue for its possible use in concrete. There have been successful replacement or partial replacement of aggregates or filler components of concrete with industrial waste such as fly ash and wood chips in concrete (Bignozzi et al., 2000). Waste plastics of various types can be used as partial replacements of aggregates in the manufacturing of concrete (Mostafizur et al., 2012). For instance Expanded polystyrene (EPS) based waste, High Density Polyethylene (HDPE), Polyethylene Terephthalate (PET) waste bottles, Polypropylene fibers and Polyethylene bags have all been used in different forms by researchers in concrete. In this study high density polyethylene bottles which forms 19% of waste plastic in municipal solid waste (Sarker, 2010) was shredded into flakes and used as a partial replacement of coarse aggregate in concrete. 2. EXPERIMENTAL DETAILS 2.1 Materials 2.1.1Cement
  • 3. Ordinary Portland limestone cement manufactured by Ghacem CEM II/BL 33.5R was used for casting the cubes and beams for all the concrete mixes. The cement was of uniform grey colour and free from any hard lumps and was bought from a local vendor. 2.1.2 Fine Aggregates Ordinary pit sand used for the experimental program was procured locally from Fumesua, a town in the Ejisu Municipality. The sand was first dried, passed through a 5mm sieve to remove any particles greater than 5mm including roots and debris. Sieve analysis was conducted to determine the particle size distribution using Malest Auto sieve shaker. 2.1.3 Coarse Aggregates Locally available coarse aggregates/granite supplied by local supplier having maximum size of 19mm was used in this work. Particle size distribution of the coarse aggregate was also obtained using Malest Auto sieve shaker. 2.1.4 Polymeric Material High density Polyethylene (HDPE) bottles identified using its recycled code was collected from the environment and used in the work. The labels on the bottles were removed and the bottles were then washed, cleaned, dried and cut or shreded into smaller flake sizes manually using table knife and scissors. The recycled plastic wastes were used to replace coarse aggregate for making the concrete specimens. The specific gravity test was conducted on the plastic aggregates and the Malest Auto sieve shaker was also used for the particle size distribution of the plastic aggregates. 2.1.5 Water Generally water that is satisfactory for drinking is also suitable for use in concrete. In this work portable water suitable for human consumption was employed in the experimental procedures. 2.2 Particle Size Distribution
  • 4. The aggregates were weighed and then placed on the first sieve of the arranged series of sieves of the Malest Auto sieve shaker and the machine was turned on. The sieve shaker shakes the aggregates with some aggregates passing through some sieves and others retained. After 10 minutes the sieve shaker automatically stops and aggregates retained in the respective sieves were weighed for their masses. The particle size distribution curve for all the aggregates are displayed in figure 1.0. Figure 1.0 Particle Distribution curve for all aggregates 2.3 Mixing, Casting, Curing The control mix has a mix ratio of 1:2:3 (cement: fine aggregate: coarse aggregate) which was adapted for this work with a constant water- cement ratio of 0.55. For making mixes containing plastics, the amount of plastic were calculated as 2%, 4%, 6% and 8% by weight of the coarse aggregate in the control concrete. The aggregates were mixed with water under the standard practice of mixing them in a concrete mixer and mixing ceased as soon as a homogenous mixture was obtained. A total of 64 cubes and 10 beams specimen were cast for this experiment. Cement (kg) Fine aggregate (kg) Coarse aggregate (kg) Plastic aggregate (kg) Water (litres) CONTROL 4.5 9.0 13.5 0.0 2.475 2% HDPE 4.5 9.0 13.23 0.27 2.475 4% HDPE 4.5 9.0 12.96 0.54 2.475 6% HDPE 4.5 9.0 12.69 0.81 2.475
  • 5. 8% HDPE 4.5 9.0 12.42 1.08 2.475 Table 1.0 Mix proportion for cube samples 3.0 RESULTS AND DISCUSSION 3.1 Workability (Slump test) The ease of flow or workability of the freshly prepared concrete was observed to have zero slump at 6% and 8% HDPE replacement. It was observed generally that the slump height decreases as the percentage replacement of coarse aggregate with waste HDPE increases. Figure 2.0 shows the results obtained for the slump height at various HDPE percentage replacement. Figure 2.0 Slump Height of various percentage replacement 3.2 Compressive Strength It was observed that the compressive strength increased with increasing curing age for all percentage replacement, a trend which is similar to that of the control. However it can be deduced that incorporation of waste content in the concrete lowers compressive strength of the hardened concrete and reduces further as the percentage replacement increases
  • 6. Figure 3.0 Compressive strength for all concrete samples 3.3 Flexural Strength Results of flexural strength indicates that the strength decreased systematically with increasing percentage of plastic content but however the flexural strength remained the same with 2% and 4% replacement of coarse aggregate with waste HDPE. Figure 4.0 Flexural strength for all percentage replacements 3.4 Water Absorption Air dried cubes specimens were weighed for their masses and then the dried samples were placed in an oven at a constant temperature of 107o C for 24 hours to ensure the samples were completely dried with a constant mass. After 24 hours the cube specimens were removed and their masses noted and recorded. The samples were allowed to cool in the laboratory and then
  • 7. immersed in clean water for 24 hours. After 24 hours of immersion in water the specimens were removed and their masses weighed. The percentage absorption of water was then calculated using the formula. 2 1 2 % 100% W W Waterabsorption W − = × Where W1 is the oven dry mass of the test specimen W2 is the wet mass of the test specimen It was observed that the percentage mass of water absorbed by the concrete specimens increased linearly with the increase in waste plastic content with the control concrete absorbing 2.507% whiles 8% HDPE replacement absorbed the most with 3.391% Figure 5.0 Percentage mass of water absorbed by concrete samples . 4.0 CONCLUSION After the preliminary test on the concrete samples the following conclusions were made on the HDPE modified concrete
  • 8. • There was decrease in the workability of the concrete with increase in the percentage of waste plastic content in the concrete. • The compressive strength of all the concrete samples increased with increasing curing days. • The compressive strength for the normal concrete was higher than the compressive strength of concrete samples containing HDPE plastic and also decreased with increasing plastic content in concrete. • The flexural strength of the specimens after 28 days decreased marginally with increase in waste plastic content. • The percentage mass of water absorbed by the concrete samples also increased with increasing plastic content. It has been identified that the use of waste HDPE as partial replacement of aggregate in concrete has some effect on the properties of the concrete but the results are all within the acceptable strength development properties. Waste HDPE could therefore be used as a cheap alternative to replace aggregate partially in construction especially in the formulation of concrete. REFERENCES Bignozzi M.,Saccani A.,Sandrolini F.,(2000). “New polymer mortars containing polymeric waste.Part 1: microstructure and mechanical properties”, Composites: Part A 31,p. 97- 98. Mostafizur R., Akhtarul I., and Mainuddin A., (2012). “Recycling of waste polymeric materials as partial replacement for aggregates in concrete” International Conference on Chemical, Environmental and Biological Sciences, Penang, Malaysia, p. 99-101.
  • 9. Sam R., Bamford A., Fletcher J., Ofosu G., Fuseini A.,(2013). “Assessment of quality of the various brands of Portland cement products available on the Ghanaian market”, International Journal of Science and Technology, Vol. 2, No 3.p. 254-258. Sarker M.,Momunor R.,Rahman S.,(2011). “Agricultural waste plastics conversion into high energy liquid hydrocarbon fuel by thermal degradation process”, Journal of Petroleum Technology and Alternative Fuels, Vol. 2(8), p. 141-142. United Nations Environmental Program (UNEP), Division of Technology, Industry and Economics (2009).“Converting waste plastic into a resource”, p.14-16.
  • 10. Sam R., Bamford A., Fletcher J., Ofosu G., Fuseini A.,(2013). “Assessment of quality of the various brands of Portland cement products available on the Ghanaian market”, International Journal of Science and Technology, Vol. 2, No 3.p. 254-258. Sarker M.,Momunor R.,Rahman S.,(2011). “Agricultural waste plastics conversion into high energy liquid hydrocarbon fuel by thermal degradation process”, Journal of Petroleum Technology and Alternative Fuels, Vol. 2(8), p. 141-142. United Nations Environmental Program (UNEP), Division of Technology, Industry and Economics (2009).“Converting waste plastic into a resource”, p.14-16.