Engineering Characterisation of Wearing Course Materials Modified with Waste Plastic
Abstract
:1. Introduction
2. Background on Road Engineering
- A.
- Hot mix asphalt (HMA) is a mixture of aggregate and bitumen blended through heating. For paving and compaction, the mixture must be hot enough to form the HMA. In cold countries, paving is limited to warm seasons due to the cold weather during winter or autumn, which causes the compacted base to cool down the asphalt mixture too much before it is packed to the desired air void content. Hot mix asphalt is the most common bituminous mix around the world for road pavements with heavy traffic, such as roads and expressways or airport lanes.
- B.
- Warm mix asphalt concrete (WMA) is a mixture created by adding waxes, zeolites, or asphalt emulsions, which are added to the mixture in different stages. This allows a significant reduction in temperature for mixing and laying, which, in turn, leads to more savings in fossil fuels and a reduction in the air pollution and environmental contamination resulting from the emission of CO2, vapours and aerosols. The lower laying temperature not only helps in improving working conditions, but also makes the surface availability faster for utilisation, especially in construction projects with critical tasks and time schedules. Furthermore, the application of such additives in HMA can yield more easily compacted mixes, specifically in cold climates for which the length of the hauls is limited by the temperature.
- C.
- Cold mix asphalt concrete is created by emulsifying the bitumen in water with soap, before being mixed with aggregate, since the viscosity of bitumen emulsion is lower, which renders the mixture easy to work and compact. After the evaporation of a sufficient amount of water, the emulsion breaks, allowing the cold mix to take on the cold HMA properties. Cold mix asphalt concrete is usually used to patch cracked or dug up asphalt parts on roads with lighter traffic services.
- D.
- Cut-back asphalt concrete (CBMA) is created by the dissolution of the binder within kerosene or any other lighter petroleum products before being blended with aggregate. Since the dissolved binder is less viscous, the mixture can be handled and compacted more easily. After the mixture is laid, the lighter petroleum fraction evaporates.
- E.
- Mastic asphalt concrete, sometimes called sheet asphalt, is a mixture of hard grade blown bitumen (oxidised), which is blended in a green cooker while heating to make a liquid of high viscosity, and then the aggregate is added in the mixture. The resulting bitumen aggregate mix is matured through cooking (heating) for approximately 7 h. The thickness of mastic asphalt concrete usually needs to be about 20–30 mm for road, sidewalks, and walker’s lanes and about 10 mm for roof and flooring applications [1,3].
Hot Mix Asphalt (HMA)
3. Stone Mastic Asphalt
3.1. Advantages and Disadvantages of SMA
3.2. Characteristics of Materials Used in SMA Mixtures
3.3. SMA Mixtures Design Methods
3.4. Marshall Method
4. Road Pavement and Modification
5. Polymer-Modified Asphalt
6. General Studies on Using Additives in Road Construction
7. Waste Materials
7.1. Waste Materials and Environment
- i.
- Fire or explosion, which is a threat to the living areas adjacent to middens and landfills, especially with organic (biodegradable) waste materials, since they can easily generate a highly flammable combination of various gases, such as methane, which is known as landfill gas.
- ii.
- Contamination of the ground and surface water neighbouring the landfills and middens as a result of decomposition of waste materials in the landfills, which leads to landfill leachates that are highly risky and dangerous for hygienic purposes.
- iii.
- Pollution of the local amenities available in those areas.
- iv.
- Other environmental pollution brought about by odour, dust, noise, aesthetics, and the like, which result from dumping and landfilling operations [47].
7.2. Recycling of Waste Materials
7.3. Typical Kinds of Waste Materials
- a.
- Solid waste materials: any kind of disposed of household or office furniture, kitchen utensils, harmless industrial waste materials, construction and renovation debris, municipality and agricultural trash, and discarded materials; many other nontoxic/non-hazardous solid waste materials are grouped into this category.
- b.
- Special waste materials: hazardous household or office waste, such as chemicals, paints, and paint thinners, rechargeable batteries used in different devices at home or office, lead-acid batteries used in vehicles, oil, worn-out tyres, etc.
- c.
- Hazardous waste materials: any liquid, solid, gaseous, or hybrid material disposed of by hospitals, clinics, and health centres. These materials, if left uncontrolled, can threaten the health of the residents of that area in which they are discarded.
8. Waste Plastic
- a.
- Preservation of limited fossil resources, such as oil, of which at least 8% is consumed to produce plastic items in the world, 4% for petrochemical feedstock, and 4% during manufacture, respectively;
- b.
- Reduction in energy consumption;
- c.
- Reduction in disposed and discarded solid materials;
- d.
- Reduction in carbon dioxide (CO2), sulphur dioxide (SO2), and nitrogen oxide (NO) emissions.
Application of Polyethylene Plastic in Asphalt
9. Conclusions
- The advance of utilising waste plastic as an ecological environmentally friendly modifier in asphalt was performed and examined. The results show the possibility to use waste plastic in modifying bitumen.
- The large and uncontrolled amount of PET bottles produced in recent decades has contributed to the creation of serious environmental problems, mostly because of the hygienic consideration, in that they are not reusable for refilling. Considering the points discussed above, recycling plastic waste materials contributes to a significant reduction in disposed plastic materials in the environment, as well as helping to preserve the natural fossil resources.
- The report emphasises that the 6% and 8% waste PET are the idealistic contents projected to modify and improve the strength, stiffness, durability, elasticity properties, and rutting resistance of asphalt mixtures. However, most of the previous studies show no description of the compositional differences in the PET used; as such, the ideal content could be below or above the 6–8% based on the materials and mixing process. Generally, polyethylene terephthalate (PET, also known as PETE, PETP, or PET-P) belongs to the polyester family and is made of a thermoplastic resin (Mashaan et al. 2021a). PET is one of the most essential raw materials used in making synthesised fibres. The structure of PET is formed of linear saturated thermoplastic polyesters, which have been in use since 1966 (Modarres and Hamedi 2014). The procedure for making these kinds of polymers consists of two phases: (a) esterification of dimethyl terephthalate with ethylene glycol; (b) polycondensation.
- In addition, the rutting and fatigue properties of SMA mixture using waste high-density polyethylene (HDPE) have been enhanced at 2–4%. Another report shows that SMA mixtures modified with 4% HDPE have the best fatigue resistance at a fatigue life of 157,090 cycles; however, the 8% HDPE has the better rutting resistance at a rut depth of 1.05 mm.
- Based on the above results, it can be concluded that PET, as a recycled polymer, can significantly improve the engineering properties of the asphalt mixture. In addition, higher contents, of 6% and 8%, could make the SMA mixtures more stable and durable.
- Results of aging display that nearly all waste plastic samples had longer fatigue life, lower aging index, and, as such, higher resistance to fatigue and cracking in comparison with nonmodified bitumen.
- Considering more research on using different sizes of waste plastic, different shapes of waste plastic, different bitumen types, different blending conditions of time, temperature, and shear velocity are recommended for future research. In addition, using high-advance technology to examine the chemical development and change in plastic–bitumen interaction phase is required for better understanding of the engineering properties.
Funding
Institutional Review Board Statement
Informed Consent Statement
Data Availability Statement
Acknowledgments
Conflicts of Interest
References
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Type of Additive | Authors and Studies | Findings |
---|---|---|
Crumb rubber and waste tyre rubber | [32]; [17]; [3]; [33]; [4]; [34]; [35]; [27] |
|
Elastomers:
| [36]; [24]; [25]; [31]; [37] |
|
Fibre:
| [38]; [39]; [40] |
|
Plastomers: HDPE, LDPE, PE, PET | [13]; [30]; [41]; [42]; [43] |
|
Reference | Type of Plastic Waste | Shape | Size (mm) | Melting Point °C | Specific Gravity/Density (g/cm3) |
---|---|---|---|---|---|
[58] | LDPE | Pellet | 5.00–2.36 | 140 °C | 0.92 |
[41] | HDPE | powder | 2 mm | 0.935 g/cm3 | |
[13] | HDPE & LDPE | Grinded and Not grinded | 2–3 mm | HDPE = 125 °C LDPE = 110 °C | HDPE = 0.035 LDPE = 0.033 |
[59] | PP (virgin) | Powder | Not given | Not given | 0.82 gm/cm3 |
[60] | PE LDPE wastes | PE: wax LDPE: pellet and shredded | Not given | Not given | Not given |
[61] | LDPE (virgin) | Grinding to powder | Not given | 113.2 C | 0.9205 gm/cm3 |
[18] | Wastes PP HDPE LDPE | Mulch and powder\ powder | Not given | LDPE: 110 °C HDPE: 131 °C | Not given |
[62] | PE PP PS | Foam, powder | Not given | Not given | Not given |
[63] | HDPE (virgin) | Pellet | Not given | 149 °C | 0.9430 gm/cc (density) |
[16] | PET | PET chips were crushed and sieved | 0.425–1.18 | Not given | Not given |
[64] | PET | PET chips were crushed and sieved | 2.36 mm | Not given | Not given |
[65] | LDPE/HDPE + CR | powder | 0.15–0.75 mm | Not given | Density LDPE: 922 kg/m3 HDPE: 961 kg/m3 |
Authors | Type of Waste Plastic | Plastic % | Type of Bitumen and Asphalt Mix | Mix Conditions | Properties | Major Finding |
---|---|---|---|---|---|---|
[41] | HDPE | 4%, 6% and 8% by weigh of bitumen | AC- 20 (4.2% OBC) | Temperature: 145, 155, and 165 °C Time: 5, 15, 30 min. Speed mix: 200 rpm | Marshall stability, Marshall quotient (MQ). | 4% HDPE is recommended mix at 165 °C, 30 min. -Increase in MQ ↑ 50% Compared to control mix. |
[13] | HDPE & LDPE | 6, 8, 10, 12, 14, 16% by weigh of bitumen | PG 60/70 (5.4% OBC) | Temperature: 180–190 °C | Marshall test stability and flow | 12% HDPE grinded provide better engineering properties |
[31] | PE (virgin) | 2, 4, 6, 8, 10 and 12% | PG 40/50 | Mix Temperature: 145–155 °C | Marshall test stability and flow | 10% PE shows high stability |
[59] | PP (virgin) Powder | 1, 3, 5 and 7 wt.% | SMA mix (5.82% OBC) PG 50/60 | Time = 160 °C Time = 5 min | Rheological test (penetration, ductility, softening point). Marshall test stability and flow; tensile and compressive strength; | 5% PP is recommended. |
[60] | PE LDPE wastes | PE: 4% LDPE: 1–4% | PG 52-34 | PE mix (1 h, 160 °C, low shear mixer) LDPE mix (1 h, 185 °C, high shear mixer) | Superpave tests Aging Stiffness | LDPE with low molecular weight is recommended in asphalt modification. |
[18] | Wastes HDPE LDPE | 2, 3, 4, 5% | Not given | Not given | Binder tests (viscosity, penetration, softening point) Asphalt tests (rutting and fatigue) | 4% HDPE was optimised. |
[61] | LDPE & (virgin) | 0, 2, 4, 6, 8% | PG 50/60 14 mm SMA | Not given | Binder tests (penetration, ductility, softening point) Asphalt tests (Marshal test stability and flow) | 6% HDPE was optimised. |
[62] | Waste PE PP PS | 5, 10, 15–25% | Dry mix PG 80/100 | Not given | Binder and asphalt tests | Use high % of plastic. |
[63] | HDPE | 1, 3, 5, 7% | PG 80/100 | 170 °C, 2 h, 3000 rpm. | Binder tests (penetration, ductility, softening point) Asphalt tests (Marshal test stability and flow; MQ) | 5% HDPE results in higher stability and MQ by about 50–55%. |
[64] | PET | 0.1%, 0.2%, 0.3%, 0.4%, 0.5%, 0.6%, 0.7%, 0.8%, 0.9%, and 1% | PG 80/100 Dry mix | Not given | Marshall test stability and flow; ITSM Creep | PET-modified mixtures showed acceptable creep performance in both static and dynamic method |
[65] | LDPE/HDPE + CR | 2, 4, 8, 10% | PG 64-10 | Not given | DSR tests | 8–10% LDPE improved the rheological properties |
[66] | devulcanized waste PET | 0, 2.5, 5, 7.5, 10, 12.5 and 15% | PG 60/70 | Shear mix of 4000 rpm; Time of 60 min and Temperature of 160 °C. | Indirect tensile strength, rutting wheel track tests and Marshall stability | Ideal content of PET 7.5–10%. PET increases stability, decreases moisture susceptibility, improve rutting resistance. |
[67] | Waste HDPE and crumb rubber | 3, 4, 5, 6, 7% | polymer-modified bitumen (PMB 45/80-60 SMA 14 | 4600–7200 rpm; 20 min. 170–180 °C | Binder tests (penetration, softening point, DSR) Asphalt tests (rutting and fatigue) | Using HDPE 5–6% improved water sensitivity resistance and rutting resistance. |
[44] | Waste HDPE and waste EVA | 5% | PG 30/50 | 600 m rpm; 60 min; 180 °C | Binder tests (penetration, softening point, DSR) Asphalt tests (rutting and fatigue). | HDPE shows better rutting resistance, EVA shows better fatigue life. |
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Mashaan, N. Engineering Characterisation of Wearing Course Materials Modified with Waste Plastic. Recycling 2022, 7, 61. https://doi.org/10.3390/recycling7040061
Mashaan N. Engineering Characterisation of Wearing Course Materials Modified with Waste Plastic. Recycling. 2022; 7(4):61. https://doi.org/10.3390/recycling7040061
Chicago/Turabian StyleMashaan, Nuha. 2022. "Engineering Characterisation of Wearing Course Materials Modified with Waste Plastic" Recycling 7, no. 4: 61. https://doi.org/10.3390/recycling7040061
APA StyleMashaan, N. (2022). Engineering Characterisation of Wearing Course Materials Modified with Waste Plastic. Recycling, 7(4), 61. https://doi.org/10.3390/recycling7040061