1. Introduction
Plastics, whilst commonly utilised in human life, have been identified as long-lasting pollutants in the environment [
1]. Plastics are utilised in several aspects of life, such as clothes, electronics, toys, healthcare supplies, and food packaging [
2]. The widespread use of plastics has led to their presence not only on Mount Everest but also at depths in the ocean. In 2022, the worldwide plastic production reached approximately 400 million tons [
3]. A significant share of crude oil is used to produce this plastic. The majority of current polymer and plastic materials are derived from non-renewable petrochemical resources. However, this is not a sustainable solution in the long term, as these non-renewable resources will eventually be depleted. The continued increase in plastic production will increase the scarcity of fossil fuels, which will affect the economy and human livelihoods. The growing number of plastic products has had a profound impact on the environment, particularly in terms of pollution. The manufacturing process and disposal of plastic materials through incineration release greenhouse gases, contributing to global warming [
4]. The decomposition of plastics in landfills takes 10-450 years, and this prolonged process contributes significantly to water and environmental pollution [
5,
6]. Furthermore, the production and disposal of plastics consumes a considerable amount of energy [
6].
Proper management of plastic waste in daily life is crucial for environmental conservation and the ecological well-being of future generations. Reusing plastic products and recycling them into new items can significantly contribute to achieving a circular economy [
7]. Sustainable engineering strategies that have been considered to date include industrial symbiosis, remanufacturing, design for the environment, life cycle engineering, green engineering, and cleaner production with a focus on sustainable consumption and production [
8,
9]. Under these circumstances, post-consumer plastic waste has drawn considerable attention from researchers, governments, and industries. Therefore, recycling post-consumer waste could play a significant role in enhancing the efficiency of natural resource utilisation and mitigating the detrimental environmental impact of plastics [
10,
11,
12].
Various methods have been used to recycle plastic waste with an aim to decrease greenhouse gas (GHG) emissions, enhance waste management, minimise the reliance on fossil fuels, and to protect the bio-geo-physical environment. These processes include bioconversion [
13], dissolution recycling, injection moulding [
14], mechanical recycling [
15], additive manufacturing (3D printing) [
16], and other similar methods. These solutions have significantly enhanced the ability to manage plastic waste to help achieve a viable and environment-friendly future [
1].
Among the aforementioned technologies, 3D printing has gained widespread acceptance as the optimal solution for eco-efficiently producing functional components in a wide range of industries, including unmanned aerial vehicles (UAVs), aerospace, civil engineering, agriculture, bioprinting, biomedical engineering, biomedicine, membrane technology, multi-material components, metal matrix composites, and food production [
17,
18]. Consequently, the use of recycled polymers in additive manufacturing (AM) has been identified as a potential solution to extend the lifespan of plastic items [
7]. Many additive manufacturing techniques have been developed, and the most popular method is fused deposition modelling (FDM) additive technology. This involves continuous feeding of a thermoplastic filament into the printer, heating it until it melts, extruding the material through a heated nozzle, and depositing it on a printing platform [
19].
Recently, acrylonitrile butadiene styrene (ABS), polylactic acid (PLA), polyethylene terephthalate (PET) and polycarbonate (PC) have emerged as the most commonly used polymer materials for FDM [
20,
21]. Among these, PLA has gained widespread prominence due to its biodegradable nature, utilisation of renewable resources, and significantly reduced greenhouse gas emissions [
22,
23]. Specifically, PLA production requires 65% less energy and generates 68% fewer greenhouse gases than for traditional plastics. Moreover, it is a highly recyclable thermoplastic that contains no toxins [
24]. Therefore, it is considered a potential candidate for replacing traditional plastics [
23]. Consequently, the global production capacity of PLA has reached approximately 677,000 metric tons by 2023, reflecting its growing popularity as a sustainable alternative to conventional oil-based plastics [
25]. The rising demand for PLA is largely attributed to the growing awareness of environmental issues and the dwindling reserves of crude oil, leading various industrial sectors to consider PLA as a sustainable alternative. Consequently, the amount of PLA in conventional post-consumer plastic waste streams is expected to increase [
25]. Despite its biodegradable nature, PLA does have some adverse environmental consequences. PLA takes several years to degrade in the environment (between 3-5 years) presenting a challenge for its appropriate disposal [
12,
26]. PLA that is made from corn and sugarcane can cause "food vs filament" issue as it not only creates pressure on cultivable land but could affect food scarcity unless this biobased filament is recycled. In addition, the weaknesses of pure PLA polymers including poor mechanical strength, brittleness, low ductility, poor thermal stability, and a narrow processing window, have limited its application [
27].
Some of these weaknesses can be overcome by selecting optimum printing parameters to obtain the required mechanical properties [
28,
29]. This is important as the growing market volume of PLA has prompted ongoing efforts to reprocess and recycle post-consumer PLA. Beltran et al. [
30] observed a minor influence of mechanical recycling on the thermal, structural, and mechanical properties of PLA, indicating the reusing capability of recycled PLA in low value-added applications such as packaging. However, the repeated extrusion cycling of virgin PLA could steadily increase the melt flow rate (MFR) of the reprocessed samples, resulting in a decrease in the tensile and impact strengths [
31]. Similarly, Pillin et al. [
32] found a notable reduction in tensile strength upon repeated injection moulding of PLA. In addition, Zhao et al. [
33] examined the recyclability of PLA in 3D printing and observed significant deterioration in polymer properties and viscosity after just two reprocessing cycles.
Therefore, blending recycled plastics with virgin plastics could be one of the most straightforward approaches to recover the properties of recycled polymers [
29]. This initiative will not only reduce plastic waste, but also save fossil fuels for future generations by reducing the conversion of petroleum products to produce virgin plastic [
1,
8,
21]. The strength of the filament decreased with an increase in the recycled material [
34,
35], but Bergaliyeva et al. [
36] found that the blend specimens strength increased with an increase in the recycled content. However, these studies did not analyse the impact of the process parameters on blend-printed specimens. Therefore, a detailed study of post-consumer PLA (PC-PLA) is necessary to fill this research gap.
The preparation of blend filaments is a fundamental step in FDM 3D printing. However, the fabrication of blend materials often requires adjustment of various process parameters to ensure high accuracy in the final printed products. The quality and processability of the fabricated filaments are largely influenced by extrusion parameters, such as the screw speed (RPM) and extrusion temperature [
36]. These extruder parameters are experimentally fine-tuned and may vary accordingly. In addition, design of experiments (DoE) has been commonly used to optimise the process parameters in FDM and enhance one or more physical properties [
37,
38,
39,
40]. Studies in this field commonly employ the Taguchi method to optimise process parameters, identify key influencing factors, and conduct experiments and analyses accordingly. Using this method, researchers have been able to obtain the desired performance through an optimal combination of factors, demonstrating the reliability and maturity of this approach [
27].
The existing literature has primarily focused on a restricted range of production orientations, thereby limiting the understanding of the anisotropic behaviour of fabricated parts. Furthermore, these investigations have offered limited insight into understanding the degradation behaviour and inherent modification of material properties that occur during the selection of a material for part manufacturing. Therefore, a detailed study on the implementation of blended PLA filaments in 3D printing is necessary. This study aimed to bridge the existing gap by using post-consumer recycled PLA (PC-PLA), focusing on the incorporation of virgin PLA (vPLA) into PC-PLA. The resulting physical and mechanical characteristics of 3D printed components at various printing temperatures were carefully determined. It is noteworthy that relatively few investigations have been carried out regarding the effects of printing temperature on the 3D printability of vPLA/PC-PLA blends. This study, however, aimed to contribute to the existing body of knowledge by examining the effects of printing temperature on the quality of 3D printed parts produced using 50:50 wt.% blend of 100% virgin commercial PLA pellets and PC-PLA waste. This research provides in-depth information on material fabrication and characterisation, which will offer additional knowledge for the manufacturing of blended PLA filaments.
5. Conclusions and Future Work
This study explored the processing and characterisation of 3D printed vPLA/PC-PLA blended samples. Sustainable 3D printer feedstock filaments of 1.7 ± 0.05 mm diameter were made using a vPLA:PC-PLA (50:50) blend. Utilising the Taguchi OA, the samples were subjected to a 3D printing process with three distinct parameters: layer height, infill, and nozzle temperature. These parameters were optimised to generate the desired outcome. The physical and mechanical properties of the printed specimens were evaluated and investigated thoroughly. According to the results of this study, the addition of vPLA in PC-PLA to fabricate blended filament significantly enhanced the mechanical properties. Compared to 100% recycled PLA, the tensile strength, flexural strength, impact, and hardness of the blended samples showed an improvement of 18.40%, 8%, 9.15%, and 5%, respectively. Fractography analysis revealed that the blended samples had better layer and inter-layer adhesion, contributing to the increase in mechanical properties. The driving agents for this improvement were increased layer height and nozzle temperature. Experimental run 7 (LH: 0.3 mm, I: 60%, and NT: 215 °C) demonstrated high tensile and flexural properties. This suggests that a large layer height and nozzle temperature can lead to increased strength, even with a low infill percentage. On the other hand, experimental run 9 (LH: 0.3 mm, I: 100%, and NT: 205 °C) showed that a high infill percentage can improve impact and hardness properties. Optimisation of the printing parameters showed that for a large layer height (0.3 mm), high infill (100%), and high nozzle temperature (215 °C), the S/N ratio was high. The ANOVA table reveals that the layer height had the most significant influence on the mechanical properties of the three printing parameters. The experimental results of the 3D printed specimens using optimal printing parameters showed a high tensile strength of 51.81 MPa, which demonstrates the potential of using blended filaments in 3D printing. Future research should concentrate on blending various percentages of vPLA and PC-PLA. Future research could also include value-added product development using blended filaments for industrial applications and testing of upcycled rPLA based products. The estimation of the fatigue life and service life of PC-PLA could also be included in future research that would provide valuable insights into its formulation durability, longevity, and sustainability. Also, it is crucial to consider the sustainability of PC-PLA for various applications. A comprehensive life-cycle assessment (LCA) of PC-PLA could provide valuable information on the environmental impacts of this material. Research in this area can lead to the development of more sustainable and environmentally friendly manufacturing materials.
Author Contributions
Conceptualisation, M.R.H., I.J.D., A.P., M.J. and W.K.B.; methodology, M.R.H., I.J.D., A.P., M.J. and W.K.B.; validation, M.R.H., I.J.D., A.P., M.J. and W.K.B.; formal analysis, M.R.H.; investigation, M.R.H.; data curation M.R.H.; writing—original draft preparation, M.R.H.; writing—review and editing, M.R.H., I.J.D., A.P., M.J. and W.K.B.; supervision, I.J.D., A.P., M.J. and W.K.B. All authors have read and agreed to the published version of the manuscript.
Figure 1.
Flow chart of the research methodology.
Figure 1.
Flow chart of the research methodology.
Figure 2.
Processing of household post-consumer PLA waste.
Figure 2.
Processing of household post-consumer PLA waste.
Figure 3.
Flowchart of post-consumer PLA filament production.
Figure 3.
Flowchart of post-consumer PLA filament production.
Figure 5.
Schematic of (
a) tensile and (
b) flexural test specimens [
46].
Figure 5.
Schematic of (
a) tensile and (
b) flexural test specimens [
46].
Figure 6.
Schematic of (
a) impact and (
b) hardness test specimens [
46].
Figure 6.
Schematic of (
a) impact and (
b) hardness test specimens [
46].
Figure 7.
Surface roughness measurement on the selected five-point of the top surface of tensile specimens [
46].
Figure 7.
Surface roughness measurement on the selected five-point of the top surface of tensile specimens [
46].
Figure 8.
(a) Surface roughness of vPLA:PC-PLA (50:50) blended filament specimens and (b) comparison of surface roughness of vPLA, rPLA, and vPLA:PC-PLA (50:50) blended specimens (where LH is the layer height, I is the infill percentage, and NT is the nozzle temperature).
Figure 8.
(a) Surface roughness of vPLA:PC-PLA (50:50) blended filament specimens and (b) comparison of surface roughness of vPLA, rPLA, and vPLA:PC-PLA (50:50) blended specimens (where LH is the layer height, I is the infill percentage, and NT is the nozzle temperature).
Figure 10.
Tensile stress vs. tensile strain curves for vPLA:PC-PLA (50:50) blended filament printed specimens (where LH is the layer height, I is the infill percentage, and NT is the nozzle temperature).
Figure 10.
Tensile stress vs. tensile strain curves for vPLA:PC-PLA (50:50) blended filament printed specimens (where LH is the layer height, I is the infill percentage, and NT is the nozzle temperature).
Figure 11.
Comparison of UTS for vPLA, rPLA, and vPLA:PC-PLA (50:50) blended filament 3D printed specimens (where LH is the layer height, I is the infill percentage, and NT is the nozzle temperature).
Figure 11.
Comparison of UTS for vPLA, rPLA, and vPLA:PC-PLA (50:50) blended filament 3D printed specimens (where LH is the layer height, I is the infill percentage, and NT is the nozzle temperature).
Figure 12.
Flexural stress–strain curves for vPLA: PC-PLA (50:50) blended filament-printed specimens (where LH is the layer height, I is the infill percentage, and NT is the nozzle temperature).
Figure 12.
Flexural stress–strain curves for vPLA: PC-PLA (50:50) blended filament-printed specimens (where LH is the layer height, I is the infill percentage, and NT is the nozzle temperature).
Figure 13.
Comparison of flexural strength for vPLA, rPLA, and vPLA:PC-PLA (50:50) blended filament specimens (where LH is the layer height, I is the infill percentage, and NT is the nozzle temperature).
Figure 13.
Comparison of flexural strength for vPLA, rPLA, and vPLA:PC-PLA (50:50) blended filament specimens (where LH is the layer height, I is the infill percentage, and NT is the nozzle temperature).
Figure 14.
Charpy impact strength of vPLA:PC-PLA (50:50) blended 3D printed specimens (where LH is the layer height, I is the infill percentage, and NT is the nozzle temperature).
Figure 14.
Charpy impact strength of vPLA:PC-PLA (50:50) blended 3D printed specimens (where LH is the layer height, I is the infill percentage, and NT is the nozzle temperature).
Figure 15.
Comparison of the impact strengths of vPLA, rPLA, and vPLA:PC-PLA (50:50) blended filament specimens (where LH is the layer height, I is the infill percentage, and NT is the nozzle temperature).
Figure 15.
Comparison of the impact strengths of vPLA, rPLA, and vPLA:PC-PLA (50:50) blended filament specimens (where LH is the layer height, I is the infill percentage, and NT is the nozzle temperature).
Figure 20.
Main effects plot of S/N ratios for surface roughness of blended specimen (a) Ra, (b) Rq.
Figure 20.
Main effects plot of S/N ratios for surface roughness of blended specimen (a) Ra, (b) Rq.
Figure 21.
(a) Stress-strain diagram of 100% PC-PLA 3D printed tensile sample, and (b) comparison of UTS for vPLA, rPLA, vPLA:PC-PLA (50:50) blended specimens, and 100% PC-PLA tensile samples.
Figure 21.
(a) Stress-strain diagram of 100% PC-PLA 3D printed tensile sample, and (b) comparison of UTS for vPLA, rPLA, vPLA:PC-PLA (50:50) blended specimens, and 100% PC-PLA tensile samples.
Table 3.
Tensile properties of the vPLA:PC-PLA (50:50) blended filament-printed specimens.
Table 3.
Tensile properties of the vPLA:PC-PLA (50:50) blended filament-printed specimens.
Experimental Run |
Yield Strength (MPa) |
Ultimate tensile Strength (UTS) (MPa) |
Strain at UTS (%) |
Fracture Strength (MPa) |
Strain at Fracture (%) |
Elastic Modulus (GPa) |
Work until UTS (kJ/m2) |
Work until Fracture (kJ/m2) |
Run 1 (LH: 0.1, I: 60, NT: 195) |
25.35 ± 1.98 |
26.15 ± 2.95 |
2.09 ± 2.31 |
25.25 ± 1.56 |
2.90 ± 1.86 |
1.98 ± 1.15 |
21.97 ± 1.58 |
35.81 ± 1.51 |
Run 2 (LH: 0.1, I: 80, NT: 205) |
28.72 ± 2.25 |
29.40 ± 2.85 |
2.13 ± 2.10 |
27.51 ± 1.85 |
3.15 ± 2.85 |
2.02 ± 1.17 |
23.36 ± 1.02 |
46.61 ± 1.92 |
Run 3 (LH: 0.1, I: 100, NT: 215) |
28.12 ± 2.10 |
36.01 ± 1.85 |
2.14 ± 2.25 |
34.33 ± 1.93 |
3.05 ± 2.53 |
2.33 ± 1.02 |
28.62 ± 1.09 |
49.06 ± 1.52 |
Run 4 (LH: 0.2, I: 60, NT: 205) |
31.24 ± 2.05 |
40.41 ± 1.12 |
2.12 ± 1.25 |
37.66 ± 1.83 |
3.03 ± 2.14 |
2.65 ± 1.05 |
32.25 ± 1.19 |
67.50 ± 1.38 |
Run 5 (LH: 0.2, I: 80, NT: 215) |
41.85 ± 1.95 |
46.67 ± 1.98 |
2.20 ± 1.45 |
44.95 ± 1.84 |
3.41 ± 1.97 |
2.85 ± 1.14 |
39.74 ± 1.14 |
75.52 ± 1.52 |
Run 6 (LH: 0.2, I: 100, NT: 195) |
32.37 ± 1.91 |
42.22 ± 2.25 |
2.17 ± 1.58 |
38.83 ± 1.79 |
3.42 ± 2.05 |
2.70 ± 1.54 |
34.18 ± 1.27 |
66.98 ± 1.24 |
Run 7 (LH: 0.3, I: 60, NT: 215) |
43.64 ± 1.68 |
48.88 ± 1.56 |
2.37 ± 1.87 |
46.05 ± 1.89 |
3.35 ± 2.61 |
3.20 ± 1.32 |
42.31 ± 1.34 |
77.66 ± 1.34 |
Run 8 (LH: 0.3, I: 80, NT: 195) |
34.01 ± 1.81 |
43.62 ± 2.10 |
2.14 ± 2.37 |
38.92 ± 1.87 |
3.69 ± 2.13 |
2.75 ± 1.29 |
34.524± 1.51 |
75.36 ± 1.05 |
Run 9 (LH: 0.3, I: 100, NT: 205) |
43.47 ± 1.88 |
47.78 ± 2.54 |
2.28 ± 2.21 |
47.35 ± 1.94 |
3.54 ± 2.10 |
3.40 ± 1.18 |
42.51 ± 1.24 |
77.74 ± 1.19 |
Table 4.
Flexural test results of the vPLA: PC-PLA (50:50) blended filament-printed specimens.
Table 4.
Flexural test results of the vPLA: PC-PLA (50:50) blended filament-printed specimens.
Experimental Run |
Yield Stress (MPa) |
Flexural Stress (MPa) |
Flexural Strain (%) |
Elastic Modulus (GPa) |
Work until Maximum Flexural Stress (kJ/m2) |
Run 1 (LH: 0.1, I: 60, NT: 195) |
43.76 ± 3.21 |
51.01 ± 1.86 |
6.69 ± 1.89 |
1.97 ± 1.26 |
19.09 ± 2.83 |
Run 2 (LH: 0.1, I: 80, NT: 205) |
54.04 ± 2.56 |
63.81 ± 2.10 |
7.69 ± 2.67 |
2.15 ± 2.57 |
25.86 ± 2.01 |
Run 3 (LH: 0.1, I: 100, NT: 215) |
59.32 ± 2.21 |
67.23 ± 2.92 |
6.71 ± 2.15 |
2.29 ± 2.93 |
28.78 ± 2.12 |
Run 4 (LH: 0.2, I: 60, NT: 205) |
63.80 ± 2.21 |
77.20 ± 2.04 |
6.25 ± 2.65 |
2.52 ± 2.34 |
33.49 ± 2.05 |
Run 5 (LH: 0.2, I: 80, NT: 215) |
71.13 ± 2.14 |
84.23 ± 2.09 |
8.40 ± 2.39 |
2.65 ± 2.01 |
42.34 ± 2.45 |
Run 6 (LH: 0.2, I: 100, NT: 195) |
69.19 ± 2.76 |
77.18 ± 1.67 |
7.64 ± 2.95 |
2.44 ± 1.85 |
36.30 ± 1.54 |
Run 7 (LH: 0.3, I: 60, NT: 215) |
77.34 ± 2.89 |
88.36 ± 1.47 |
7.07 ± 2.28 |
2.89 ± 2.01 |
37.92 ± 2.31 |
Run 8 (LH: 0.3, I: 80, NT: 195) |
70.87 ± 3.90 |
81.37 ± 1.85 |
6.92 ± 1.12 |
2.50 ± 1.45 |
37.19 ± 1.41 |
Run 9 (LH: 0.3, I: 100, NT: 205) |
78.11 ± 2.29 |
88.29 ± 2.17 |
7.82 ± 2.56 |
2.67 ± 2.20 |
45.19 ± 2.07 |
Table 6.
Summary of optimum printing parameters for vPLA:PC-PLA (50:50) blended specimens.
Table 6.
Summary of optimum printing parameters for vPLA:PC-PLA (50:50) blended specimens.
Factors |
Tensile Strength |
Flexural Strength |
Impact Strength |
Shore D hardness |
Surface Roughness |
Level |
Description |
Level |
Description |
Level |
Description |
Level |
Description |
Level |
Description |
Layer Height (mm) |
3 |
0.3 |
3 |
0.3 |
3 |
0.3 |
3 |
0.3 |
1 |
0.1 |
Infill (%) |
3 |
100 |
3 |
100 |
3 |
100 |
3 |
100 |
1 |
60 |
Nozzle Temperature (°C) |
3 |
215 |
3 |
215 |
2 |
205 |
3 |
215 |
2 |
205 |