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RESEARCH ARTICLE (Open Access)

Bio-based plastics – a sustainable solution to plastic pollution

Arturo Aburto Medina A * , Soulayma Hassan A , Chaitali Dekiwadia B , Chengrong Chen C D and Andrew S. Ball A D
+ Author Affiliations
- Author Affiliations

A Department of Biology, School of Science, RMIT University, Bundoora, Vic. 3083, Australia.

B RMIT Microscopy and Microanalysis Facility, RMIT University, Melbourne, Vic. 3001, Australia.

C School of Environment and Sciences, Griffith University, Nathan Campus, Nathan, Qld 4111, Australia.

D Solving Plastic Waste Cooperative Research Centre Research Centre, Griffith University, Nathan Campus, Nathan, Qld 4111, Australia.




Dr Arturo Aburto Medina obtained his PhD from the University of Essex, UK, and has more than 10 years’ experience conducting research and consulting on diverse bioremediation and environmental projects. He has conducted postdoctoral studies at the University of California—Irvine, Flinders University and RMIT University. His research interests include bioremediation of contaminated sites, antimicrobial surfaces, conservation of the environment and indoor air quality. ORCID: https://orcid.org/0000-0002-2871-609X.



Soulayma Hassan is a PhD candidate at RMIT University, Australia. Her research focuses on the sustainable production of polyhydroxyalkanoates (PHAs) from lignocellulosic biomass, particularly sugarcane bagasse, aiming to develop cost-effective and eco-friendly bioplastics. Her research interests include the circular economy, sustainable resource management and waste valourisation. Soulayma’s research experience also extends to the anaerobic digestion of organic waste, further promoting waste-to-resource technologies. ORCID: https://orcid.org/0009-0009-8839-2611.



Dr Chaitali Dekiwadia is a platform scientist at RMIT’s Microscopy & Microanalysis Facility. She has conducted postdoctoral studies at The University of Melbourne and Peter MacCallum Cancer Centre. She specialises in life sciences, cryo and X-ray CT, with a passion for advancing research through cutting-edge technology. Her deep knowledge of electron microscopy as a core facility staff for cross discipline collaboration has significantly contributed to produce good research outcomes, fostering technical excellence and enhancing scientific collaboration. ORCID: https://orcid.org/0000-0002-0928-4420.



Prof. Chengrong Chen is distinguished professor in environmental biogeochemistry and waste recycling at Griffith University and research director of the Solving Plastic Waste CRC. Over the past 30 years, Prof. Chen has worked in the areas of environmental biogeochemistry, with a broad interest in waste recycling, climate change, decarbonation and environmental pollution and sustainability. He has published over 200 peer-reviewed journal papers. ORCID: https://orcid.org/0000-0001-6377-4001.



Andrew S. Ball is the director of the ARC Training Centre for the Transformation of Australia’s Biosolids Resource, a distinguished professor at RMIT University, Melbourne, and Solving Plastic Waste CRC program leader. He has worked in the areas of soil microbiology, environmental pollution and biogeochemical cycling for 40 years, publishing over 300 peer-reviewed articles. ORCID: https://orcid.org/0000-0003-2387-968X.

* Correspondence to: a.arturo1309@gmail.com

Microbiology Australia https://doi.org/10.1071/MA25027
Submitted: 10 April 2025  Accepted: 9 May 2025  Published: 26 May 2025

© 2025 The Author(s) (or their employer(s)). Published by CSIRO Publishing on behalf of the ASM. This is an open access article distributed under the Creative Commons Attribution-NonCommercial-NoDerivatives 4.0 International License (CC BY-NC-ND)

Abstract

Global annual plastic production is >410 × 106 tonnes with an annual rate increase of 4%; most of this plastic is non-biodegradable. Bio-based plastics (also known as bioplastics) are formed from polymers created from renewable or recycled raw materials, making them part of a sustainable plastic life cycle and part of a circular economy. Their production uses carbon-neutral energy and products are recycled at their end of life (EOL). Thus, they stand as an alternative to the current global plastic waste problem (>80% goes to landfill). Bio-based plastics can have a lower carbon footprint than conventional plastics, their materials properties can be advantageous, they are compatible with current recycling streams and biodegradation as EOL is also an option for some. Some challenges include having a larger production of bio-based plastics by gene-edited microorganisms and an improvement in the chemical and biological methods of recycling (upcycling) to process larger volumes and create higher-quality materials. Also, policy is important for the clear identification of bio-based plastics and their acceptance by creating financial incentives for their upscaling.

Keywords: bio-based plastics, biological recycling, carbon-neutral energy, circular economy, PHAs, polyhydroxyalkanoates, polyhydroxylalkanoic acids, renewable sources.

Introduction

Global annual plastic production is >410 × 106 tonnes with an annual rate increase of 4%.1 Thus, plastic constitutes the third highest waste source globally making it a huge human health and environmental concern.2 Most of this plastic is non-biodegradable. Polyethylene terephthalate (PET) is the dominant material (production of 70%) in the global fibres market, whereas polyethylene (PE; 36%), polypropylene (PP; 21%) and polyvinylchloride (PVC; 12%) are the main non-fibre plastics produced.3 The largest global plastic volumes are used in the following commercial sectors: packaging (35%), construction (16%), textiles (14.5%), consumer goods (10.3%), automotive (10.1%), electronics (6.2%) and agricultural industries (3.4%). Packaging is the main source of waste, with 141 × 106 tonnes produced in 2015 alone, of which 96.6% was unrecycled.3 A significant portion of non-biodegradable plastic end up in the environment. It is estimated that up to 80% of plastics found in oceans comes from the land4 and ~2 × 106 tonnes of plastic debris leach into rivers annually3 in both developing and developed nations. Moreover, wealthier nations ship their waste to developing countries with inferior regulations and waste management infrastructure.5 Malaysia has been the world’s largest importer of plastic waste2 and also has one of the largest plastic production industries globally; however, along with other developing nations in South-east Asia, Malaysia lacks appropriate waste management systems.6 Up to 85% of the plastic waste ends up in landfill and the marine environment.7 This waste is harmful because microplastics (<1–5 mm) are generated and consumed by marine organisms resulting in bioaccumulation and biomagnification. Today, microplastics has been reported to be detected in air, tap water, fish and salt.8 Microplastics can also absorb and carry contaminants (e.g. hydrophobic organic chemicals).9 In addition, plastic can leach oestrogenic-like chemicals (e.g. bisphenol A) when exposed to sunlight or certain temperatures that may result in metabolic disorders in mammals such as obesity and type-2 diabetes.10

Plastic pollution is also very costly; the impact on tourism, fishing and shipping industries is estimated to be US$1.3 × 109 year–1 in the Asia–Pacific region alone.11 The Malaysian government has established a roadmap to zero single-use plastic 2018–3012 joining other nations with similar measures such as New Zealand, Thailand, India and the European Union.

Bio-based plastics and the circular economy

Not all bio-based plastics are environmentally degradable; however, bio-polybutylene succinate (bioPBS), polylactic acid (PLA), polyglycolic acid (PGA) and polyhydroxyalkanoates (PHAs) are, with low carbon, biodegradable and compostable (industrial composting) options available (Table 1).

Table 1.Types of plastics currently available, biodegradability, cost and global production.

PolymerBiodegradation (industrial)Biodegradation (ocean)Price (US$ kg–1)Global production (%)
Fossil-based and durable
 HDPENon-biodegradableNon-biodegradable1.4–1.612.5
 LDPENon-biodegradableNon-biodegradable1.3614.4
 PPNon-biodegradableNon-biodegradable1.119.3
 PSNon-biodegradableNon-biodegradable0.7–1.55.3
 PETNon-biodegradableNon-biodegradable1.2–1.46.2
 PVCNon-biodegradableNon-biodegradable1.912.9
Fossil-based and degradable
 PBAT2–3 months>1 year4.17.1
 PBS2–5 months>1 year4.5
 PVA1–2 weeks4 months2
 PCL4–6 weeks6 weeksNA
Bio-based and durable
 PEF9 monthsNANA1.5
 bioPETNoNANA
 bioPENoNA1.8–2.4
Bio-based and degradable
 bioPBS>3 months>1 yearNA
 PLA6–9 weeks>1.5 years2–3
 PGA2–3 months1–2 monthsNA
 P3HB1–4 months1–6 months3–8
 P4HB4–6 weeks1–6 months3–8

Global production data are from Plastics Europe.13 HDPE, high-density polyethylene; LDPE, low-density polyethylene; NA, not available; P3HB, poly(3-hydroxybutyrate); P4HB, poly(4-hydroxybutyrate); PBAT, polybutylene adipate-co-terephthalate; PBS, polybutylene succinate; PCL, polycaprolactone; PE, polyethylene; PEF, polyethylene furanoate; PET, polyethylene terephthalate; PGA, polyglycolic acid; PLA, polylactic acid; PP, polypropylene; PS, polystyrene; PVA, polyvinyl alcohol; PVC, polyvinylchloride.

Global plastic production is dominated by fossil-based and durable plastics, PP being the largest produced (Table 1). Such plastics are largely responsible for the global plastic and microplastic problem. Research has been conducted on their degradation by microorganisms.14 A recent review has listed bacteria, fungi, engineered microorganisms, microbial consortia, algae and animals capable of degrading conventional plastics.15 However, such an approach is likely to represent just one alternative among several to the microplastic problem considering the increasing volume of conventional plastics produced every year (>410 × 106 tonnes).

Ideally, bio-based plastics should be made from renewable or recycled sources to comply for a circular economy and be part of a sustainable plastic life cycle (where waste becomes raw material). In the current linear economy, only 9% are recycled, 12% incinerated, with the remainder sent to landfill.3 A circular economy approach has been proposed to be able to reduce greenhouse gas emissions by ~62%.16 Some of the renewable sources include lignocellulosic biomass such as wheat straw and sugarcane bagasse,17 which are cheap, although they do require a pretreatment to obtain the fermentable cellulose and hemicellulose sugars.18

Bio-based plastic production

Global bio-based plastic production has more than doubled since 2010.19 Close to half of the 2.18 × 106 tonnes of bioplastics manufactured in 2023 was for packaging, the most prevalent type of plastic pollution. The uptake of bioplastics (~1%) used in Australia is currently limited by high production costs, with most bioplastics in Australia imported from Thailand and Brazil. However, the commercial market of PHAs has been estimated to reach annual volumes of 100,000 tonnes in future years.3 Bio-based and degradable polyesters are PLA, bioPBS and PHAs (Fig. 1); all have the advantage of being able to be cleaved by enzymatic activity or hydrolysis.

Fig. 1.

Chemical structures of polylactic acid (PLA), polybutylene succinate (PBS) and polyhydroxyalkanoate (PHA).


MA25027_F1.gif

PHAs can be produced by a range of different bacteria (Fig. 2a) including Bacillus safensis,20 Cupriavidus necator,21 and archaeal strains Haloferax mediterranei22 and Halogeometricum borinquense.23

Fig. 2.

(a) Fluorescent Nile red staining of cells accumulating polyhydroxylalkanoic acids (PHAs) on agar plates. (b) Transmission Electron Microscopy image showing intracellular PHA production (white granules) by one of RMIT University’s isolates from rotted sugar cane bagasse.


MA25027_F2.gif

PHA is stored intracellularly, representing up to 80% of their cell volume (Fig. 2b). PHA can be synthesised from biomass compounds, e.g. sugar cane bagasse or liquefied plastic wastes24 (Fig. 1). The most common monomers consist of the rigid poly-3-hydroxybutyrate (P3HB) and the softer and more flexible poly-(3-hydroxybutyrate-co-3-hydroxyhexanoate) (PHBH), making them good substitutes for PE and PP.25 The key enzymes and steps involved in PHA production are 3-ketothiolase: acetyl coenzyme A (CoA) to acetoacetyl CoA and PHA synthases that polymerise hydroxyacyl-CoA monomers to form polymeric PHA chains. Research is currently aimed at enhancing PHA yields by increasing the cell size (Fig. 3) along with improving stress tolerance26 through the application of CRISPR-Cas9 approaches. Further, more environmentally friendly processes for cell extraction are also being developed.26,27

Fig. 3.

Key enzymes in the production of PHAs and schematic of CRISPR-Cas9 gene editing.


MA25027_F3.gif

Recycling of plastics

To be part of a complete circular economy, bioplastics should undergo biological recycling through aerobic composting or anaerobic degradation at their end of life (EOL), whereas fossil-based plastics should be upcycled by chemical or biological depolymerisation or by undergoing thermolysis for those with functional (PET) and non-functional backbones (PE and PP) respectively (Fig. 4).

Fig. 4.

A circular plastic economy. Plastic waste becomes raw material to be recycled. Composting or incineration of captured methane from anaerobic digestion is a net-zero addition to the carbon cycle since it is captured by photosynthesis to create new biomass.


MA25027_F4.gif

Fate of bioplastics at EOL

Composting and biodegradation involve the microbial digestion of the polymeric material in oxic conditions into CO2 and H2O by known strains.28 The process can be aided by fragmentation and the reduction of particle size making it more susceptible to enzymatic degradation.29 Hydrolysis and photodegradation can also help, but oxo-degradation (oxidation) is not recommended due to microplastic formation. Biodegradation is not guaranteed because it is highly dependent on the polymer’s chemical structure, the environment and the microorganisms available30 and all these conditions may not be met even in industrial composters. Composting times vary according to the polymer composition and can go up to 9 months for polyethylene furanoate (PEF) (Table 1).

The advantage of anaerobic digestion is the net-zero carbon balance for the bioplastic waste while producing energy from the capture and burning of the produced methane and when water is circulated to promote microbial activities, a bioreactor landfill can be created increasing its efficiency. This EOL is ideal for PHAs and would be recommended over other EOLs such as biodegradation, chemical or biological recycling.

Fate of fossil-based plastics at EOL

Mechanical recycling

The cheapest form and most common form of recycling and requires sorting the polymer types, washing, mechanical shredding, melting and forming new plastic shapes. The new plastics are generally of lower quality due to thermal and mechanical stress and virgin polymers may be added to increase the product quality.31 Some non-recyclable items include medical contaminants, coloured or low-density materials. The environmental impact of mechanical recycling is lower than producing virgin plastics but only 10% of PET and high-density PE is recycled globally.32 The recycling rate can be increased with deposit-refund schemes for post-consumer plastics as is the case in Norway and Germany where >97% of PET bottles are recycled.

Chemical recycling

Chemical recycling has also been termed upcycling and can generate high-quality polymers from waste as opposed to mechanical recycling. Depolymerisation is performed by solvolysis and thermolysis, and it can convert the polymers into materials of high quality.31 However, it is more expensive and only accounts for <1% of all recycled plastics. Thus, a challenge for chemical companies is to make this process cost competitive with virgin polymers. Although the thermolysis of polystyrene can recover >90% of liquid hydrocarbon oil,33 there is the risk of potential toxic gases production due to additives.

Biological recycling

Microorganisms are used to depolymerase polymers into monomers but do not digest them to CO2. Although aromatic polyesters are more resistant to enzymatic hydrolysis, the bacterium Ideonella sakaiensis can depolymerise PET at ambient temperatures in just 40 days.29 Genetic modification has also been used to improve the depolymerisation of PET and PEF.14,34

Policy

The plastic waste pollution is one of current three most pressing global environmental crises. Solving plastic waste problem cannot be achieved without evidence-based government policy intervention. The circular economy of plastic is being prioritised by governments and international bodies. The United Nations has made it a priority since 2018. The Ellen McArthur Foundation promotes science-based policies for a circular economy.35 The European Union aims to recycle 50% of plastic packaging by 2030 and certain items of single-use plastic have been banned. The adoption of extended producer responsibility (EPR) schemes has helped local governments deal with packaging materials, but the scope needs to include other plastic industries. Household waste management systems should be implemented globally as has been initiated in some European countries and Japan.36 China has plans to increase their bioplastics production, specifically PLA and ban all non-recyclables whereas Japan, Malaysia, Singapore and South Korea have created bioplastic subsidies.37 Recent discussion of introduction of recycled content in plastic products is encouraging and adoption of government policy shift will certainly enhance the recycling of plastic and reduce the problem of plastic pollution in the environment.

Conclusions

Bio-based plastics have the potential to create a circular economy and gene editing is very promising not only to increase bioplastic polymerisation (especially for PHAs), but also for biological depolymerisation during recycling. Moreover, public education on bioplastics needs to increase and labels need to be standardised for local and global scales to prevent confusion and avoid ‘greenwashing’. Deposit-refund systems for plastic bottles should be implemented globally and mimic the successful EU cases. Policies such as taxation of non-bio-based plastics should increase the demand for bioplastics and promote a more circular economy.

Data availability

The data that support this study are available in the article.

Conflicts of interest

The authors declare that they have no conflicts of interest.

Declaration of funding

This research did not receive any specific funding.

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Biographies

MA25027_B1.gif

Dr Arturo Aburto Medina obtained his PhD from the University of Essex, UK, and has more than 10 years’ experience conducting research and consulting on diverse bioremediation and environmental projects. He has conducted postdoctoral studies at the University of California—Irvine, Flinders University and RMIT University. His research interests include bioremediation of contaminated sites, antimicrobial surfaces, conservation of the environment and indoor air quality. ORCID: https://orcid.org/0000-0002-2871-609X.

MA25027_B2.gif

Soulayma Hassan is a PhD candidate at RMIT University, Australia. Her research focuses on the sustainable production of polyhydroxyalkanoates (PHAs) from lignocellulosic biomass, particularly sugarcane bagasse, aiming to develop cost-effective and eco-friendly bioplastics. Her research interests include the circular economy, sustainable resource management and waste valourisation. Soulayma’s research experience also extends to the anaerobic digestion of organic waste, further promoting waste-to-resource technologies. ORCID: https://orcid.org/0009-0009-8839-2611.

MA25027_B3.gif

Dr Chaitali Dekiwadia is a platform scientist at RMIT’s Microscopy & Microanalysis Facility. She has conducted postdoctoral studies at The University of Melbourne and Peter MacCallum Cancer Centre. She specialises in life sciences, cryo and X-ray CT, with a passion for advancing research through cutting-edge technology. Her deep knowledge of electron microscopy as a core facility staff for cross discipline collaboration has significantly contributed to produce good research outcomes, fostering technical excellence and enhancing scientific collaboration. ORCID: https://orcid.org/0000-0002-0928-4420.

MA25027_B4.gif

Prof. Chengrong Chen is distinguished professor in environmental biogeochemistry and waste recycling at Griffith University and research director of the Solving Plastic Waste CRC. Over the past 30 years, Prof. Chen has worked in the areas of environmental biogeochemistry, with a broad interest in waste recycling, climate change, decarbonation and environmental pollution and sustainability. He has published over 200 peer-reviewed journal papers. ORCID: https://orcid.org/0000-0001-6377-4001.

MA25027_B5.gif

Andrew S. Ball is the director of the ARC Training Centre for the Transformation of Australia’s Biosolids Resource, a distinguished professor at RMIT University, Melbourne, and Solving Plastic Waste CRC program leader. He has worked in the areas of soil microbiology, environmental pollution and biogeochemical cycling for 40 years, publishing over 300 peer-reviewed articles. ORCID: https://orcid.org/0000-0003-2387-968X.