1. Introduction
The amount of waste generated by various industrial sectors is steadily increasing, posing a major environmental problem. It is a common objective of sustainable global development goals to fight the climate crisis by recycling waste materials to reduce the volume of solid waste at disposal sites [
1,
2,
3,
4,
5,
6,
7]. Currently, about 8.3 billion metric tons of plastic are generated globally and this is expected to increase to 12 billion by 2050. However, only 9% of these are recycled, and 6.3 billion are accumulated in landfills or sloughing off in the natural environment. Moreover, as of 2018, the glass industry reported recycling around 27 million metric tons globally, accounting for about 21% of total glass production [
8]. Therefore, solid waste reuse in the construction industry is gaining attention in developed countries. Currently, the scarcity of construction materials and excessive disposal of waste products are the difficulties experienced globally that need a rapid and permanent solution [
9,
10]. Notably, this process has led scholars to tackle the issue of finding suitable eco-friendly construction materials and handle environmental matters simultaneously [
11]. Recently, there has been some evidence of waste materials and by-products used in construction materials. However, recycling waste as an alternative construction material is used significantly less in developing countries [
12]. The usage of these materials aids in their integration into cement, concrete, and other construction materials but also assists in lowering the cost of cement production by reducing energy consumption and improving environmental protection from potential carbon emissions [
13,
14,
15,
16].
Recycling waste glass and plastic has always been an issue globally, even though the recycling rate of glass is relatively high compared with plastics [
17]. A lot of research has been conducted on recycling plastic waste in mortar [
18,
19,
20,
21,
22] and concrete [
23,
24,
25,
26]. Other studies have been conducted on the recycling of waste glass in concrete as a fine aggregate replacement [
1,
17,
27], coarse aggregates as an additive [
27,
28,
29,
30,
31], partial replacement of cement [
32,
33,
34,
35], and as fine aggregates [
36] in mortar. In other studies, fine aggregates used in concrete mixtures are substituted in proportions by shredded plastics and glass, and the optimal amount is determined at which greater strength is attained [
37,
38,
39]. Concrete from plastic and glass wastes has several benefits including being lightweight, robust, simple to shape, and customized to various customer needs [
40].
The use of glass wastes as fine aggregates improves the physical and mechanical properties of concrete by reducing the density, and they are effective in controlling the structure’s weight for stability purposes [
41]. On the other hand, crushed glass contains engineering characteristics of an angular and somewhat elongated shape. This situation creates a higher internal friction angle, improving the interlocking between different ingredients of concrete particles. Partial replacement of waste glass does not significantly affect the workability of the concrete [
42]. However, it has been shown that the compressive strength decreases by almost 49% with a 60% of WG [
42].
On the other hand, the addition of waste glass as fine aggregates increases the mechanical properties of mortar [
36]. Replacing the natural sand with recycled high-density polyethylene (HDPE) aggregates increased the axial deformation capability of mortar and reduced the density [
21]. Waste plastic as coarse aggregates in the concrete also increases the workability of concrete [
43]. The rise in slump indicates that more water was available from the mix due to decreased absorption by reducing the percentage volume of natural aggregates and low water absorption by recycled plastics [
44,
45]. Many authors reported a gradual decrease in the compressive strength by increasing the percentage of waste plastic [
46,
47,
48]. Their findings show that the addition or partial replacement of WG and WP has positive and negative effects on the concrete’s fresh and hardened properties. However, limited research is available on the combination of WG and WP in concrete as a partial replacement for fine aggregates. The primary aim of this research is to investigate the properties and performance of concrete produced using waste glass (WG) and waste plastic (WP) as partial replacements for fine aggregate. This study seeks to evaluate the potential benefits and challenges of incorporating these waste materials into concrete mixtures, including their impact on the mechanical properties. By exploring these factors, the research aims to contribute to more sustainable construction practices and the effective utilization of waste materials.
2. Materials and Methods
Comprehensive experimental tests were conducted to study the characteristics and strength properties of the partial replacement of fine aggregates with plastic and glass waste on concrete’s fresh and hardened properties. Potential waste glass quantities were collected from empty glass containers and various building and construction remnant materials commonly used for laboratory procedures. The waste glass was crushed into fine pieces that resembled the size of sand. On the other hand, samples of granulated plastic waste, mostly soda and water bottles, were collected from a dumpsite. Waste plastics should be cleaned before use to remove debris and impurities that could alter the hydration and bonding of the cement paste. The plastic samples were selected to fit the sieve’s size requirements at the laboratory.
The proportion by weight of all constituents (aggregates, cement, plastics, glass, and water) was kept constant in all the mixes. The ACI mix design method arrived at the right combination of cement, fine aggregate, coarse aggregate, and water for C-25 grade concrete. Finally, different experiments were conducted on concrete properties with various mixing and curing parameters. For this study, the ratios of the weight of waste plastics to glass used were 3:7, 6:14, and 10:20. The optimum mix ratio was determined.
2.1. Cement
Ordinary Portland cement (OPC) with a grade of 42.5 N manufactured by the Derba Midroc Cement PLC in Salale Zone, Oromia Regional State, Ethiopia was selected for this study. The physical and mechanical properties were studied using the requirements specified by ASTM and are presented in
Table 1. Cement pastes with different water–cement ratios generally have other setting times. Therefore, it does not seem apparent at first which setting time to use. The setting time of a cement paste with a typical consistency is referred to as the setting time of cement paste by convention [
49]. The initial setting time is the duration of cement paste related to 25 mm penetration of the Vicat needle into the paste 30 s after it is released.
In contrast, the final setting time is related to zero penetration of the Vicat needle into the paste [
49]. The standard consistency for hydraulic cement refers to the amount of water required to make a neat paste of satisfactory workability. The Vicat apparatus was used to assess the paste’s resistance to penetration by applying a 300-gram plunger to its surface. The mechanical property of the cement used in this study is shown in
Table 2.
2.2. Aggregate
The fine aggregate (river sand) used for this research work was brought from suppliers of Jimma town, Ethiopia, and was originally from Gambela, Ethiopia, and crushed coarse aggregate was bought from the crusher site located in Jimma town. Aggregate grain size distribution or gradation is one of the properties of aggregates that influences the quality of concrete. Therefore, fine aggregates and coarse aggregates with gradation satisfying the grading requirement of the ASTM standard [
51], shown in
Figure 1 and
Figure 2, were used throughout the experiment.
Therefore, the grain size distribution curve exhibits a fine aggregate sample employed for this research task as a well-graded type of aggregate. The percentage passing of fine aggregate runs in the lower and upper limit of the standard requirement gradation curve.
2.3. Waste Plastics
Forty-three (43) kg samples of the waste plastic particles, mostly soda and water bottles, were collected from plastic disposed in the Jimma town bore dumping site in Ethiopia. high-density polyethylene (HDPE) and Polyethylene Terephthalate (PET) are two types of commonly used plastics made for everyday use. For this study, PET types of plastics were selected since they can be found in high volumes in dumpsites relative to others. The collected plastics were cleaned from impurities with tap water and then air-dried. The air-dried sample was melted at 130 °C, cooled to make it suitable for crushing, and converted to a fine-sized aggregate. The production process of the fine waste plastic is illustrated in
Figure 3. Finally, a sieve analysis was conducted and the required size of the plastic aggregate was determined, as illustrated in
Figure 3.
The physical properties of the plastic and glass waste are summarized in
Table 3.
The grain size distribution curve of fine waste plastics is illustrated in
Figure 4.
2.4. Waste Glass
Seventy-two (72) kg of waste glass materials was used throughout this experimental study, gathered from the disposals of reconstruction and building demolition projects in the Jimma town bore solid-waste dumping site. Soda-lime-type glass was used for the investigation throughout this research study among different glasses. For this task, the collection of waste and glass focused on a ‘bore’ dumping site in Jimma town. The collected waste glass was contaminated with impurities that could have altered the glass’s chemical and physical properties. Therefore, the waste glass was cleaned with pure water to remove impurities. Then, the cleaned waste glass was ground into a fine aggregate size manually using a hammer.
Finally, the crushed waste glass was sieved, and the required size was obtained, as shown in
Figure 5.
The grain size distribution curve of the fine waste glass is illustrated in
Figure 6.
2.5. Mix Designing and Proportioning
The material properties (cement, aggregate, shredded plastics, and waste glass) and concrete characteristics containing the waste glass and plastic were examined. In addition, the mathematical approach to the volume-based analysis of materials was considered for the concrete mix production to evaluate the physical and mechanical properties (workability, compressive strength, flexural strength, and splitting tensile strength).
The appropriate quantities of cement, sand, aggregates, waste plastics, and glass were used to create a concrete mix. The main purpose here was to find the optimum replacement of waste plastics and glass that could be utilized to manufacture concrete that meets the performance standards of concrete under loads and in diverse environments.
2.5.1. Mix Design for Waste Plastics to Glass
Different trial mixes were proportioned by observing concrete’s workability and compressive strength to obtain the appropriate waste plastic and glass ratio. As a result, the optimum ratio of WP to WG was determined.
Table 4 summarizes the mix properties of the concrete mix without any waste glass and plastics content for three various water–cement ratios. These ratios cover the most widely applicable engineering practices, from 0.4 to 0.6. The mixes conform to the standards and specifications of ASTM C136 [
51] and ASTM C 33-03 [
52]. Finally, the mix proportion for the C-25 concrete grade is tabulated in
Table 5 with different water–cement ratios.
With different controlling factors, such as water–cement ratio, waste plastics, and glass proportions, four mixes and 72 standard compressive sample specimens were used in the experiments. For comparison purposes, the reference testing samples were plain concrete with no WG and WP content.
Table 5 summarizes the complete experimental plan.
2.5.2. Mix Design for Fine Aggregate, Waste Plastic, and Glass
The testing program continued focusing only on the two mixes with optimal output results, i.e., sample WPG-0 at a water–cement ratio of 0.4 and 20% of the fine aggregate replaced by WG and WP. We used a w/c ratio of 0.40 because the concrete workability was stable compared to the control mixture. However, the workability and strength of the concrete are affected when using a w/c ratio above 0.50. Based on these results, an extra series of 12 tests were conducted to determine the flexural strength and the splitting resistance of the two optimal concrete mixes. The trial mix for WP and WG using a water–cement ratio of 0.4 is described in
Table 6.
The mix proportions for compressive strength at the 7th and 28th days with different water–cement ratio are summarized in
Table 7.
2.6. Concrete Specimens Preparation
Initially, a certain amount of water was added to the aggregates and left for a short while to bring the aggregates to the saturated surface dry condition (SSD). Next, the fine aggregate, coarse aggregate, and cement were dry mixed for about a minute. Next, the fine glass and plastic wastes were carefully added to the dry mix to avoid segregation, followed by the addition of two-thirds of the total mixing water.
Twelve 150 mm cubes, three 150 × 300 mm cylinders, and three 100 × 100 × 500 mm beams were cast for each mix. Cubes were used to measure the compressive strength on the 7th and 28th days. In addition, the 28th day’s tensile strength and flexural tensile strength were evaluated using cylinder specimens and beam specimens, as shown in
Figure 7.
3. Results and Discussions
3.1. The Test Program for Concrete Mix Design
For the laboratory procedures, the concrete grade C-25 compressive strength was used to understand the effect of compressive strength.
The ratios of plastics to glass in the mix were determined by using the estimated quantity of waste with a water-to-cement ratio of 0.4 and observing the effect on the compressive strength of the concrete on the 7th day (
Table 8).
As shown in
Table 8, the compressive strength increases as the ratio of plastics in the mix decreases and the glass increases. It shows that the added glass has positive effect by improving the compressive strength of the concrete, compared with the waste plastic.
The mean concrete compressive strength on the 7th day for the ratio of WP to WG (1:1, 1:1.5, 1:2, 1:2.5 and 1:3) was compared with the control mix concrete’s compressive strength. From the proportions of the plastics to glass, a ratio of 1:2 was selected because in the first two ratios the compressive strength decreased, while in the 1:2.5 ratio and 1:3 ratio, the amount of glass was high and amount of plastic was low, but the strength met the standard. However, these ratios were not selected since the quantity of glass in the mix was significantly higher than the combined plastic quantity.
When the ratios of plastic to glass were 1:2, 1:2.5, and 1:3, the mean compressive strength of the concrete was almost equal with the control mix, as shown in
Table 8. Thus, for practical purposes in terms of the proportions of the plastics to glass, a ratio of 1:2I was selected due to the fact that the volume of the plastic waste is much greater than that of glass wastes in the study area of this research. However, from a scientific point of view, a ratio of 1:3 is recommended since the maximum compressive strength was observed at this mix ratio.
Thus, it is inferred that the replacement of sand with plastic waste up to 15% can be adopted so that the disposal of used plastic can be reduced and the lack of natural aggregates can be managed effectively [
53].
When 30% of the fine aggregate was replaced by waste glass, the strength was only about 1% lower than that of the control, which is a promising result [
35]. Therefore, the 1:2 ratio was selected as the optimum ratio of plastics to glass in the mix during the investigation.
3.2. Effect of Waste Plastics and Glass on the Workability of Concrete
As shown in
Table 9, the fresh concrete workability was inversely affected by the increase in water–cement ratio and decreased as the percentage of fine WP and WG was increased.
Clearly, fine WP and WG in concrete significantly decreased the workability. Specifically, for a w/c ratio of 0.4 replacing 10% of the fine aggregate with fine WP and WG, the change was negligible. However, it significantly decreased the workability for a w/c ratio of 0.5 and above the fine WP and WG introduced to the concrete.
Generally, the water to cement ratio affected the concrete workability, rather than the introduction of waste plastics and glass to the mix. The slump tests with and without the wastes are shown in
Figure 8.
3.3. Unit Weight Test Results
The results for different sample groups regarding the unit weight for hardened concrete are listed in
Table 10.
It was shown that the concrete unit weight decreased as the water–cement ratio increased. For example, at a water–cement ratio of 0.4, the maximum reduction was 1.7%; at a water–cement ratio of 0.5, the maximum reduction in unit weight was 5.5%; and at a water–cement ratio of 0.6, the maximum reduction was 8.67%. According to ASTM C 33, the concrete unit weight at w/c = 0.4 fulfills the requirements of normal weight concrete: it must be between 2.2 and 2.4 (g/cm3). Therefore, a water–cement ratio of 0.4 was selected for the investigation since the percentage of reduction in unit weight was minimal.
3.4. Effect of Waste Plastics and Glass on Compressive Strength of Concrete
As shown in
Table 11, at water–cement ratios of 0.4 and 10% WP and WG, the compressive strength at 7 and 28 days was increased by 12.55% and 6.44%, respectively. Nevertheless, at w/c = 0.5 and 0.6 and all introductions of WP to WG, the compressive strength at 7 and 28 days was decreased. On the other hand, at 20% replacement, a reduction was observed by 14.35% and 0.73% on the 7th and 28th day, respectively. In this case, the concrete designs for C-25, on the 28th day, the compressive strength was 26.9 MPa. Therefore, if the impact of the WG and WP on the environment was considered a primary issue, it is possible to use up to 20% replacement for fine aggregate for simple structures where lightweight concrete is required.
A summary of the effect of the water–cement ratio on compressive strength is shown in
Figure 9. It can be observed that the compressive strength decreases as the water–cement ratio increases across all tested percentages of waste materials used as fine aggregate replacements.
3.5. Optimal Waste Plastic and Glass Contents in Concrete Mixes
As shown in
Table 12, the optimum compressive strength was obtained with a 10% replacement of fine aggregate by WG and WP. However, as discussed earlier, utilizing a 20% replacement is also feasible, as the mean compressive strength on the 28th day remains sufficient. This approach will help increase the percentage of waste materials being recycled.
3.6. Effect of Waste Plastic and Glass on Flexural Strength
The prepared beam samples were tested after 28 days of standard curing, and the results of the flexural strength tests for the control concrete and the waste plastics and glass concretes are illustrated in
Figure 9. The bending strength of the concrete (
σ) in MPa was obtained based on Equation (1).
where
σ—bending strength,
M—maximum moment,
I—moment of inertia, and
C—centroid depth.
The results demonstrate the effect of fine waste plastic (WP) and waste glass (WG) contents in concrete mixes on the flexural strength of the concrete. As illustrated in
Figure 10, when 20% of the fine aggregate is replaced by WG and WP, the flexural strength increases by 19.7%, from 12.46 MPa to 15.52 MPa.
This significant improvement in flexural strength suggests that incorporating WG and WP as partial replacements for traditional fine aggregates can enhance the mechanical properties of concrete. The increase in flexural strength can be attributed to the improved bonding and distribution of stress within the concrete matrix provided by the WG particles. In contrast, the presence of WP might contribute to a lesser extent, indicating that WG has a more pronounced effect on the flexural performance. These findings highlight the potential of utilizing waste materials in concrete production, promoting sustainable construction practices while enhancing material properties.
3.7. Effect of Waste Plastics and Glass on Splitting Tensile Strength
The results show that the use of optimal fine aggregate WP and WG contents in the concrete mix reduced the splitting tensile strength of the mixture slightly.
Equation (2) gives the horizontal stress to which the element is subjected.
where
P—the applied compressive load,
L—the cylinder length, and
D—the cylinder diameter.
The split tensile strength of the control mix was 4.65 MPa, and the inclusion of waste plastics and glass into the concrete resulted in a 4.3 MPa splitting tensile strength on the 28th day of curing, as shown in
Figure 11. Therefore, the introduction of WP and WG slightly decreased the splitting tensile strength compared to a plain concrete mix. The study conducted in [
54] concludes that concrete mortar could be made completely sustainable by using recycled materials like glass, plastic, and recycled concrete, as well as micro-silica and fly ash, and that only 20% of the weight of cement could be used without lowering the compressive and flexural strength of the concrete.
4. Conclusions
The experimental study on concrete samples incorporating plastic and glass wastes as partial replacements for fine aggregate yielded the following key findings. Based on these findings, the following conclusions can be drawn:
The optimal mix ratio of plastics to glass waste was determined to be 1:2.3. This ratio was found to provide the best balance between the structural integrity and recyclability of the resulting material. Using this specific proportion ensures that the composite material benefits from the desirable properties of both plastic and glass, making it suitable for various practical applications.
Incorporating waste plastics and glass into the concrete mix slightly reduced the workability at water–cement ratios of 0.5 and 0.6. However, the workability remained unaffected when the water–cement ratio was 0.4. Therefore, a water–cement ratio of 0.4 is recommended to produce sustainable concrete from waste plastics and glass.
The investigation determined that the optimal replacement of fine aggregate with waste materials was 10%, comprising 7% waste glass and 3% waste plastic. However, to effectively utilize the waste materials, a 20% replacement—comprising 14% waste glass and 6% waste plastic—is a better option, as the mean compressive strength is almost 25 MPa. This finding highlights a balanced approach to enhancing the sustainability of concrete production.
The compressive strength of concrete increases as the proportion of plastics in the mix decreases and the amount of glass increases. This indicates that glass exerts a more significant influence on the compressive strength compared to plastics.
In concrete mixes containing the optimal proportion of fine waste plastics and glass, there was a significant enhancement observed in the flexural strength. However, there was a slight decrease noted in the splitting tensile strength.
Overall, these findings highlight the potential for sustainable construction practices by effectively integrating waste materials into concrete production processes.
Author Contributions
Conceptualization, A.M.L.; Formal analysis, A.M.L. and D.M.; Investigation, A.M.L., D.M. and F.F.F.; Methodology, A.L and D.M.; Writing—original draft, A.M.L., D.M., F.F.F., G.U. and Y.T.B.; Writing—review and editing, A.M.L., F.F.F., G.U. and Y.T.B. All authors have read and agreed to the published version of the manuscript.
Funding
This research received no external funding.
Data Availability Statement
The original contributions presented in the study are included in the article, further inquiries can be directed to the corresponding author.
Conflicts of Interest
The authors declare no conflicts of interest.
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Figure 1.
Grain size distribution curve of fine aggregate.
Figure 1.
Grain size distribution curve of fine aggregate.
Figure 2.
Grain size distribution curve of coarse aggregate.
Figure 2.
Grain size distribution curve of coarse aggregate.
Figure 3.
Fine waste plastic preparation process: (a) collection, (b) cleaning, (c) crushing, (d) melted and grinded.
Figure 3.
Fine waste plastic preparation process: (a) collection, (b) cleaning, (c) crushing, (d) melted and grinded.
Figure 4.
Grain size distribution curve of fine- waste plastics.
Figure 4.
Grain size distribution curve of fine- waste plastics.
Figure 5.
Granulated glass particles used for testing: (a) collected sample, (b) cleaned, crushed, and sieved waste glass.
Figure 5.
Granulated glass particles used for testing: (a) collected sample, (b) cleaned, crushed, and sieved waste glass.
Figure 6.
Grain size distribution curve of fine waste glass.
Figure 6.
Grain size distribution curve of fine waste glass.
Figure 7.
Sample under test: (a) flexural strength, (b) tensile strength, (c) failure under tensile test.
Figure 7.
Sample under test: (a) flexural strength, (b) tensile strength, (c) failure under tensile test.
Figure 8.
Example of slump test (a) for plain concrete and (b) for waste plastic and glass.
Figure 8.
Example of slump test (a) for plain concrete and (b) for waste plastic and glass.
Figure 9.
Compressive strength at different percentages of waste materials and various water–cement ratios.
Figure 9.
Compressive strength at different percentages of waste materials and various water–cement ratios.
Figure 10.
Example of mean flexural strength of C-25 concretes on day 28 with a water–cement ratio of 0.4.
Figure 10.
Example of mean flexural strength of C-25 concretes on day 28 with a water–cement ratio of 0.4.
Figure 11.
Example of tensile strength of C-25 concretes on day 28 with a water–cement ratio of 0.4.
Figure 11.
Example of tensile strength of C-25 concretes on day 28 with a water–cement ratio of 0.4.
Table 1.
Physical properties of Derba cement.
Table 1.
Physical properties of Derba cement.
Physical Properties | Test Results | Recommended Value |
---|
Consistency (%) | 31 | 26–33 [49] |
Initial Setting Time (min) | 52 | more than 45 min [50] |
Final Setting Time (min) | 320 | not more than 375 [50] |
Table 2.
Mechanical property of Derba cement.
Table 2.
Mechanical property of Derba cement.
Mechanical Property | Test Results |
---|
3rd day compressive strength (MPa) | 23.20 |
7th day compressive strength (MPa) | 33.40 |
28th day compressive strength (MPa) | 45.70 |
Table 3.
Physical properties of plastic and glass waste.
Table 3.
Physical properties of plastic and glass waste.
Properties | Test Results | ASTM Code Standards [52] |
---|
- | Plastic Waste | Glass Waste | Recommended |
---|
Fineness modulus (FM) | 2.52 | 2.56 | - |
The nominal maximum size, (mm) | 0.075–4.00 | 0.075–4.00 | - |
Specific gravity (SSD basis) | 1.09 | 2.62 | 2.3–2.9 |
Unit weight, (kg/m3) | 65 | 2450 | 1280–1920 |
Water absorption capacity, (%) | 0.00 | 0.01 | 0.4–4.0 |
Table 4.
Mix proportioning for one m3 of concrete.
Table 4.
Mix proportioning for one m3 of concrete.
Type of Mix | w/c | Cement (kg/m3) | Water (kg/m3) | Fine Agg (kg/m3) | Coarse Agg (kg/m3) | Plastic Waste (kg/m3) | Glass Waste (kg/m3) |
---|
Control | 0.4 | 475 | 165 | 768 | 1007 | 0.0 | 0.0 |
Control | 0.5 | 380 | 162 | 850 | 1007 | 0.0 | 0.0 |
Control | 0.6 | 316.67 | 160 | 905 | 1007 | 0.0 | 0.0 |
Table 5.
Design of concrete mixtures and number of test specimens for compressive strength at each test age.
Table 5.
Design of concrete mixtures and number of test specimens for compressive strength at each test age.
Group No | w/c Ratio | % of WP and WG | WP: WG Ratio | Number of Compressive Strength Tests |
---|
7th Day | 28th Day |
---|
WPG-0 | 0.4 | 0 | 0:0 | 3 | 3 |
WPG-1 | 10 | 3:7 | 3 | 3 |
WPG-2 | 20 | 6:14 | 3 | 3 |
WPG-3 | 30 | 10:20 | 3 | 3 |
WPG-0 | 0.5 | 0 | 0:0 | 3 | 3 |
WPG-1 | 10 | 3:7 | 3 | 3 |
WPG-2 | 20 | 6:14 | 3 | 3 |
WPG-3 | 30 | 10:20 | 3 | 3 |
WPG-0 | 0.6 | 0 | 0:0 | 3 | 3 |
WPG-1 | 10 | 3:7 | 3 | 3 |
WPG-2 | 20 | 6:14 | 3 | 3 |
WPG-3 | 30 | 10:20 | 3 | 3 |
Table 6.
Trial mix for waste plastic and glass ratio for water–cement ratio of 0.4.
Table 6.
Trial mix for waste plastic and glass ratio for water–cement ratio of 0.4.
Type of Mix | Mix Ratio of WP to WG | Cement (kg/m3) | Water (kg/m3) | Fine Agg (kg/m3) | Coarse Agg (kg/m3) | Plastic Waste (kg/m3) | Glass Waste (kg/m3) |
---|
Control (WPG-0) | N/A | 38.475 | 13.65 | 62.20 | 81.57 | 0.00 | 0.0 |
WPG-1 | 1:1 | 38.475 | 13.65 | 49.76 | 81.57 | 6.22 | 6.22 |
WPG-2 | 1:1.5 | 38.475 | 13.65 | 49.7664 | 81.57 | 4.976 | 7.46 |
WPG-3 | 1:2 | 38.475 | 13.65 | 49.76 | 81.57 | 4.15 | 8.29 |
WPG-4 | 1:2.5 | 38.475 | 13.65 | 49.76 | 81.57 | 3.55 | 8.88 |
WPG-5 | 1:3 | 38.475 | 13.65 | 49.76 | 81.57 | 3.11 | 9.33 |
Table 7.
Mix proportions for 0.081 m3 of concrete.
Table 7.
Mix proportions for 0.081 m3 of concrete.
Type of Mix | w/c | Cement (kg/m3) | Water (kg/m3) | Fine Agg (kg/m3) | Coarse Agg (kg/m3) | Plastic Agg (kg/m3) | Glass Agg (kg/m3) |
---|
Plain (PG-0) | 0.4 | 38.475 | 13.65 | 62.20 | 81.57 | 0.00 | 0.0 |
WPG-1 | 0.4 | 38.475 | 13.65 | 55.9872 | 81.57 | 2.0736 | 4.1472 |
WPG-2 | 0.4 | 38.475 | 13.65 | 49.7664 | 81.57 | 4.1472 | 8.2944 |
WPG-3 | 0.4 | 38.475 | 13.65 | 43.5456 | 81.57 | 6.2208 | 12.4416 |
Plain (PG-0) | 0.5 | 30.78 | 13.12 | 68.85 | 81.57 | 0.0 | 0.0 |
WPG-1 | 0.5 | 30.78 | 13.12 | 61.965 | 81.57 | 2.295 | 4.59 |
WPG-2 | 0.5 | 30.78 | 13.12 | 55.08 | 81.57 | 4.59 | 9.18 |
WPG-3 | 0.5 | 30.78 | 13.12 | 48.195 | 81.57 | 6.885 | 13.77 |
Plain (XPG-0) | 0.6 | 32.7 | 25.65 | 73.305 | 81.57 | 0.0 | 0.0 |
WPG-1 | 0.6 | 32.7 | 25.65 | 65.9745 | 81.57 | 2.4435 | 4.887 |
WPG-2 | 0.6 | 32.7 | 25.65 | 58.644 | 81.57 | 4.887 | 9.774 |
WPG-3 | 0.6 | 32.7 | 25.65 | 51.3135 | 81.57 | 7.3305 | 14.661 |
Table 8.
Compressive strength of concrete at 7 days for varying ratios of waste plastics to waste glass (WP:WG).
Table 8.
Compressive strength of concrete at 7 days for varying ratios of waste plastics to waste glass (WP:WG).
Group Number | WP:WG | - | 7th-Day Compressive Strength (MPa) |
---|
(Control) | 0:0 | Mean | 20.6 |
Standard deviation | 0.20 |
M2-PG-2 | 1:1.5 | Mean | 16.2 |
Standard deviation | 0.30 |
M2-PG-2 | 1:1.5 | Mean | 19.27 |
Standard deviation | 0.152 |
M4-PG-4 | 1:2.5 | Mean | 20.46 |
Standard deviation | 0.155 |
M5-PG-5 | 1:3 | Mean | 20.8 |
Standard deviation | 0.10 |
Table 9.
Slump test results.
Table 9.
Slump test results.
Grade | w/c | Sample | Slump Test (mm) | Grade | w/c | Sample | Slump Test (mm) | Grade | w/c | Sample | Slump Test (mm) |
---|
C-25 | 0.4 | PG-0 | 10 | C-25 | 0.5 | PG-0 | 95 | C-25 | 0.6 | PG-0 | 240 |
0.4 | PG-1 | 9.5 | 0.5 | PG-1 | 90 | 0.6 | PG-1 | 230 |
0.4 | PG-2 | 7 | 0.5 | PG-2 | 80 | 0.6 | PG-2 | 220 |
0.4 | PG-3 | 7 | 0.5 | PG-3 | 30 | 0.6 | PG-3 | 210 |
Table 10.
Unit weight of concrete with series of proportions of fine waste plastics and glass contents.
Table 10.
Unit weight of concrete with series of proportions of fine waste plastics and glass contents.
Specimen | w/c | Waste (%) | WP:WG | Unit wt. (g/cm3) | Reduction (%) |
---|
WPG-0 | 0.4 | 0 | 0 | 2.35 | 0.00 |
WPG-1 | 0.4 | 10 | 3:7 | 2.39 | 1.70 |
WPG-2 | 0.4 | 20 | 6:14 | 2.33 | 0.85 |
WPG-3 | 0.4 | 30 | 10:20 | 2.37 | 0.85 |
WPG-0 | 0.5 | 0 | 0 | 2.36 | 0.00 |
WPG-1 | 0.5 | 10 | 3:7 | 2.49 | 5.5 |
WPG-2 | 0.5 | 20 | 6:14 | 2.24 | 5.08 |
WPG-3 | 0.5 | 30 | 10:20 | 2.29 | 2.97 |
WPG-0 | 0.6 | 0 | 0 | 2.19 | 0.00 |
WPG-1 | 0.6 | 10 | 3:7 | 2.05 | 6.40 |
WPG-2 | 0.6 | 20 | 6:14 | 2.01 | 8.22 |
WPG-3 | 0.6 | 30 | 10:20 | 2.0 | 8.67 |
Table 11.
The 7- and 28-day compressive strengths of concrete with several fine waste plastic to glass contents at different water–cement ratios.
Table 11.
The 7- and 28-day compressive strengths of concrete with several fine waste plastic to glass contents at different water–cement ratios.
Samples | w/c | WP and WG (%) | WP:WG | Compressive Strength (MPa) | Strength Change (%) |
---|
7 Days | 28 Days | 7 Days | 28 Days |
---|
WPG-0 | 0.4 | 0 | 0 | 22.3 | 27.1 | 0.00 | 0.00 |
WPG-1 | 10 | 3:7 | 25.1 | 28.9 | +12.55 | +6.64 |
WPG-2 | 20 | 6:14 | 19.1 | 26.9 | −14.35 | −0.73 |
WPG-3 | 30 | 10:20 | 15.0 | 25.4 | −32.74 | −6.27 |
WPG-0 | 0.5 | 0 | 0 | 20.7 | 27.3 | 0.00 | 0.00 |
WPG-1 | 10 | 3:7 | 19.1 | 26.8 | −7.73 | −1.83 |
WPG-2 | 20 | 6:14 | 18.3 | 25.2 | −11.59 | −7.70 |
WPG-3 | 30 | 10:20 | 16.8 | 25.0 | −18.84 | −8.82 |
WPG-0 | 0.6 | 0 | 0 | 20.5 | 27.0 | 0.00 | 0.00 |
WPG-1 | 10 | 3:7 | 15.5 | 22.5 | −24.39 | −16.67 |
WPG-2 | 20 | 6:14 | 16.2 | 21.5 | −20.97 | −20.37 |
WPG-3 | 30 | 10:20 | 14.3 | 19.2 | −30.92 | −28.89 |
Table 12.
The 7- and 28-day compressive strength of concrete at w/c = 0.4.
Table 12.
The 7- and 28-day compressive strength of concrete at w/c = 0.4.
Group No. | WP and WG (%) | 7-Days Compressive Strength (MPa) | 28-Days Compressive Strength (MPa) |
---|
WPG-0 | 0 | 22.3 | 27.1 |
WPG-1 | 10 | 25.1 | 28.9 |
WPG-2 | 20 | 19.1 | 24.9 |
WPG-3 | 30 | 15.0 | 24.4 |
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