Abstract
Bioplastics are emerging as a promising alternative to traditional plastics, driven by the need for more sustainable options. This review article offers an in-depth analysis of the entire life cycle of bioplastics, from raw material cultivation to manufacturing and disposal, with a focus on environmental impacts at each stage. It emphasizes the significance of adopting sustainable agricultural practices and selecting appropriate feedstock to improve environmental outcomes. The review highlights the detrimental effects of unsustainable farming methods, such as pesticide use and deforestation, which can lead to soil erosion, water pollution, habitat destruction, and increased greenhouse gas emissions. To address these challenges, the article advocates for the use of efficient extraction techniques and renewable energy sources, prioritizing environmental considerations throughout the production process. Furthermore, the methods for reducing energy consumption, water usage, and chemical inputs during manufacturing by implementing eco-friendly technologies. It stresses the importance of developing robust disposal systems for biodegradable materials and supports recycling initiatives to minimize the need for new resources. The holistic approach to sustainability, including responsible feedstock cultivation, efficient production practices, and effective end-of-life management. It underscores the need to evaluate the potential of bioplastics to reduce plastic pollution, considering technological advancements, infrastructure development, and increased consumer awareness. Future research should focus on enhancing production sustainability, understanding long-term ecological impacts, and advancing bioplastics technology for better performance and environmental compatibility. This comprehensive analysis of bioplastics’ ecological footprint highlights the urgent need for sustainable solutions in plastic production.
Keywords: Bioplastic, Biodiversity, Environmental impact, Recycling, Mitigation
Introduction
Bioplastics are materials made from renewable sources like plants, biomass, or microorganisms, offering a more sustainable alternative to traditional plastics (Rosenboom, Langer & Traverso, 2022). They can be bio-based, biodegradable, or both (Cywar et al., 2022). The goal of bioplastics is to address the environmental issues linked with conventional plastics, which are made from fossil fuels and have harmful effects throughout their life cycle, from extraction and production to use and disposal (Atiwesh et al., 2021). Bioplastics aim to reduce environmental impact by offering several benefits: lower carbon footprints, better resource conservation, less waste, and support for a circular economy (Degli Esposti et al., 2021). Bio-based bioplastics often use crops or forestry by-products, which helps cut carbon emissions and reduces reliance on fossil fuels (Mongkoldhumrongkul & Sukkanta, 2022; Rosenboom, Langer & Traverso, 2022). They also offer a way to use fewer finite resources, such as petroleum, which is the base material for traditional plastics (Zhao et al., 2023). Bioplastics can potentially improve waste management. Being biodegradable, they break down into natural elements, reducing plastic waste in landfills and oceans (Folino et al., 2020). Some can be recycled or composted, supporting circular economy practices by promoting reuse and recycling. With an annual production of around two million tonnes, 100% bio-based bioplastics are seen as crucial for future circular economies and for achieving United Nations Sustainable Development Goals (SDGs) (Kumar et al., 2021). These goals include using less toxic substances, developing new recycling methods, and reducing dependence on fossil fuels (Rosenboom, Langer & Traverso, 2022). Bioplastics generally have a lower environmental impact than traditional plastics and offer sustainable alternatives (Altalhi, 2022). Their adoption drives research and innovation in sustainable materials (Palsra & Chauhan, 2020). This review examines various methods for assessing bioplastics’ popularity and adoption, including life cycle assessments from production to disposal. It also explores production methods, advancements, waste management strategies, and their effects on biodiversity and ecosystems. The review concludes with practices to reduce environmental impact and promote the sustainable use of bioplastics. Ongoing advancements in bioplastics technology continue to improve their performance, durability, and affordability, increasing their potential for widespread use.
Survey methodology
The study used a detailed questionnaire to explore awareness and perceptions of bioplastics. The sample included people from 42 countries, mainly in Europe and Asia (Filho et al., 2022). The survey was designed to gather a range of insights through self-directed responses. It covered demographics, knowledge of bioplastics, consumption habits, concerns, and opinions. The questionnaire used various answer formats, including multiple-choice and frequency scales, and was carefully reviewed for clarity and relevance. The survey was conducted online via the LimeSurvey platform over 5 months, gathering 384 responses. The data was analyzed using SPSS V.26, with frequency analyses and Chi-square tests examining the relationships between education, age, and gender, using a significance level of 5% (Filho et al., 2022).
Our research aimed to understand the environmental impact of bioplastics, motivated by the growing importance of sustainable materials in addressing environmental issues. We used a carefully designed survey to gather detailed insights from consumers, industry professionals, and environmental experts. A preliminary test of the survey with a small group was conducted to refine the questions and ensure clarity and objectivity (Bishop, Styles & Lens, 2021). To investigate the environmental effects of bioplastics, we performed an extensive literature review using the PubMed database. We started with search terms like “bioplastics environmental impact” and “sustainable materials footprint” and refined our search to include terms such as “biodegradable plastics life cycle assessment” and “renewable materials carbon footprint.” We also explored terms like “bioplastic manufacturing environmental effects” and “biodegradable polymer waste management.” This thorough search strategy aimed to provide a comprehensive understanding of the ecological impacts of bioplastics, forming the basis for our research into their environmental footprint. The data collection process involved a detailed review of recent publications and relevant literature. This careful approach ensured data accuracy and adherence to established methods. The collected data was thoroughly analysed to provide a clear and meaningful understanding of various research findings on bioplastics. Ethical considerations were crucial throughout the survey process. The review clearly explained the study’s purpose and maintained transparency. In summary, this survey methodology was carefully crafted to offer a thorough and reliable examination of the ecological impact of bioplastics. By systematically gathering diverse perspectives and maintaining high ethical standards, the study aimed to provide valuable insights into sustainable materials and environmental conservation. The goal was to significantly advance understanding of bioplastics’ environmental effects and support the development of sustainable practices and policies.
Emerging trends in bioplastic adoption
In recent years, bioplastics have gained popularity as a sustainable alternative to traditional plastics. Growing global concern about environmental issues has increased interest in bioplastics among individuals, businesses, and governments (Moshood et al., 2021). Bioplastics are favoured for their reduced carbon footprint, renewable sources, and potential biodegradability (Coppola et al., 2021, Fig. S1). Governments around the world are enacting regulations to promote sustainable materials and reduce plastic waste through bans, taxes, and incentives (Adam et al., 2020; Kiessling et al., 2023). These policies support the growth of bioplastics. Companies are incorporating sustainability into their strategies, using bioplastics in packaging, manufacturing, and product innovation to meet the rising consumer demand for eco-friendly alternatives (Ashrafi et al., 2019; Westlake et al., 2023). Consumers increasingly prefer brands that use bioplastics, seeing them as responsible and sustainable options (Filho et al., 2022; Galati et al., 2022). Technological advancements have improved bioplastic manufacturing, research, and material development (Andreeßen & Steinbüchel, 2019). These innovations have made bioplastics more appealing across various industries. Collaboration between governments, industry, and NGOs has driven progress and created sustainable supply chains (Maione, Lapko & Trucco, 2022). Increased production has made bioplastics more accessible and affordable (Gong et al., 2023). The rise of bioplastics is supported by environmental awareness, regulations, corporate sustainability, consumer demand, technological advancements, and collaborative efforts (Wydra et al., 2021), ensuring their continued growth as a sustainable solution. Evaluating the environmental impact of bioplastics throughout their life cycle—from production to disposal—is essential. While bioplastics are often seen as more eco-friendly than traditional plastics, it is important to assess their specific environmental effects (Atiwesh et al., 2021). Key concerns include the environmental footprint of feedstock production. Large-scale monoculture farming can lead to deforestation, habitat loss, soil erosion, water pollution from pesticides and fertilizers, and depletion of water resources (Shaheen & Sabir, 2017; Van Roijen & Miller, 2022). The production of bioplastics involves energy-intensive processes like fermentation, chemical synthesis, and polymerization. The greenhouse gas (GHG) emissions from these processes can vary based on the feedstock and production methods used (Chong et al., 2022; Jin et al., 2023). The impact is also affected by the type of energy used in manufacturing.
Addressing excessive carbon dioxide emissions, which contribute to global warming, highlights the need for improved methods of converting carbon dioxide into useful products such as biomethane, bioethanol, polyhydroxybutyrate, and succinic acid. Microorganisms like bacteria, algae, and yeast play a crucial role in this process. Advances in genetic engineering and machine learning are improving the efficiency of capturing and converting carbon dioxide through various methods including photoautotrophic biosynthesis, dark fermentation, and biodegradation. For instance, Chlorella vulgaris and Cyanobacteria can capture over 90% of carbon dioxide and produce approximately 0.45 g/L/day of biomass in a standard photobioreactor (Akash et al., 2023). The production of bioplastics can require significant amounts of water for feedstock irrigation, processing, and cooling (Morão & De Bie, 2019). The impact on local water resources depends on regional water availability, so it is important to manage water use sustainably. Another concern is the competition for feedstock crops, which could affect food security and land use if these crops are grown instead of food crops (Bishop, Styles & Lens, 2022). The water footprint of bioplastics ranges from 1.4 to 9.5 cubic meters per kilogram, while the land footprint ranges from 0.7 to 13.75 square meters per kilogram. If bioplastics were to replace all fossil-based plastics, the annual water footprint could range from 307 billion to 1,652 billion cubic meters, representing 3% to 18% of the global annual average. Similarly, the land footprint could range from 30 million to 219 million hectares per year, potentially using 8% to 61% of available arable land (Putri, 2018). To reduce environmental impact and ensure responsible resource use, it is crucial to adopt sustainable sourcing and land management practices for bioplastics production. Effective waste management is also important for biodegradable bioplastics to fully realize their environmental benefits. In landfills without proper conditions for degradation, biodegradable bioplastics can release methane, a potent greenhouse gas (Atiwesh et al., 2021). If bioplastics are not sorted from conventional plastics, they can contaminate recycling streams and reduce the quality of recycled materials. Poor waste disposal can lead to bioplastics entering natural ecosystems like oceans and rivers, where they can cause pollution and harm wildlife through ingestion and entanglement (Hahladakis, 2020).
Lca of bioplastics
The Life Cycle Assessment (LCA) is a detailed process used to evaluate the environmental impact of bioplastic products throughout their entire life cycle, from raw material extraction to manufacturing, use, and end-of-life (EOL) management (Gadaleta et al., 2023). This comprehensive analysis covers crucial stages, including raw material sourcing, production, use, and disposal (Ali et al., 2023). The LCA process begins with clearly defining the assessment’s objectives and scope. This includes specifying the goals, boundaries, functional units (such as per kilogram of bioplastic), and system limits (Salwa et al., 2021; Alhazmi, Almansour & Aldhafeeri, 2021). Once these parameters are established, the Life Cycle Impact Assessment (LCIA) is conducted, where the collected Life Cycle Inventory (LCI) data is analyzed to assess the potential environmental impacts at various life cycle stages. This analysis uses different methodological frameworks outlined in scholarly research (Beckstrom et al., 2020; Chalermthai et al., 2021). Identifying environmental hotspots and areas of significant impact through this rigorous analysis enables informed decision-making and strategic actions to reduce environmental footprints (Talwar & Holden, 2022). The insights gained from LCA can lead to various interventions, such as optimizing processes, integrating renewable energy sources, minimizing waste, and enhancing recycling infrastructure (Ali et al., 2023; Kakadellis & Harris, 2020). Moreover, sharing LCA results through thorough reporting and verification, in line with standards like ISO 14040 and ISO 14044, strengthens the credibility and reliability of the findings. There is also an option for additional third-party validation to ensure compliance with recognized academic standards (Di Bartolo, Infurna & Dintcheva, 2021).
Comparative studies of the carbon, environmental, and water footprints between conventional polypropylene (PP) plastic and bioplastic fibres have shown significant benefits for bioplastics (Broeren et al., 2017). Specifically, bioplastic fibres have a lower carbon footprint and overall reduced environmental impact compared to PP. Additionally, incorporating starch in the production of biodegradable bioplastics has led to notable reductions in greenhouse gas (GHG) emissions and non-renewable energy use, highlighting the potential for environmental benefits in bioplastic production (Ali et al., 2023). However, using starch in bioplastics can increase eutrophication potential and land use compared to petrochemical plastics, indicating the trade-offs in formulation (Ali et al., 2023). Incorporating residual starch residues in bioplastic blends shows promise in mitigating these negative impacts, leading to reductions in land use, eutrophication potential, GHG emissions, and non-renewable energy consumption (Ali et al., 2023). Additionally, strategies to reduce the water footprint, such as using residual vegetative biomass from various crop sources, offer further opportunities for sustainable production (Ali et al., 2023). Despite these environmental benefits, challenges remain in the commercial viability of bioplastics, particularly polyhydroxyalkanoates (PHA), due to their higher production costs compared to fossil fuel-derived plastics (Khatami et al., 2021). Efforts to lower these costs have been hindered by factors such as slow microbial growth, inefficient raw material conversion, high energy demands, and expensive downstream processing (Mannina et al., 2020). The study combined the carbon, environmental, and water footprints of regular PP plastic with those of bioplastic fibres. The results showed that bioplastic fibres have a smaller carbon footprint and a lower overall environmental impact compared to PP (Ali et al., 2023). Using starch in the production of biodegradable bioplastics reduced greenhouse gas (GHG) emissions by up to 80% and non-renewable energy use by up to 60% (Broeren et al., 2017). However, compared to petrochemical plastics, starch can increase eutrophication potential by up to 400% and land use by 0.3 to 1.3 square meters per kilogram of bioplastic (Broeren et al., 2017). Blending starch with residual starch residues can help reduce these impacts, lowering land use by up to 60%, eutrophication potential by up to 40%, GHG emissions by up to 10%, and non-renewable energy use by up to 60%. Additionally, using residual vegetative biomass from various crops can help reduce the water footprint (Broeren et al., 2017). Despite these environmental benefits, the commercial production of PHA bioplastics remains challenging due to higher costs compared to fossil fuel-based plastics. In 1998, PHA was up to 1,700% more expensive than fossil-based plastic, and while the price has since dropped to around €5 per kilogram, it is still higher than synthetic plastic, which costs between €0.80 and €1.50 per kilogram (Khatami et al., 2021). The high cost of PHA production is due to slow microbial growth, inefficient raw material conversion, high energy requirements for sterilization and aeration, and expensive downstream processing (Mannina et al., 2020).
The environmental performance of bioplastics can vary depending on factors like feedstock type, farming methods, energy sources, and EOL management options (Benavides, Lee & Zarè-Mehrjerdi, 2020). Additionally, LCA studies should consider not just environmental impacts but also social and economic factors to provide a more comprehensive assessment of sustainability (Bishop, Styles & Lens, 2021). When comparing the LCA of bioplastics to traditional plastics, it is crucial to consider that bioplastics often rely on renewable resources like plant-based feedstock (e.g., corn, sugarcane, or cellulose), while traditional plastics typically use fossil fuel-based feedstock such as petroleum or natural gas (Muthusamy & Pramasivam, 2019). Bioplastics generally have a lower environmental impact during the extraction phase due to their renewable nature. Their manufacturing processes often require less energy compared to conventional plastics, especially when efficient technologies and renewable energy sources are used. In contrast, traditional plastics involve energy-intensive processes like polymerization and refining crude oil, leading to higher carbon emissions and other environmental impacts (Rosenboom, Langer & Traverso, 2022). Bioplastics also have the potential to offer more sustainable EOL solutions than standard plastics (Paul-Pont et al., 2023). Some are designed to be compostable, breaking down into organic matter under specific conditions (Gioia et al., 2021). However, it is important to note that not all bioplastics are biodegradable, and proper composting infrastructure is required for those that are. Traditional plastics, unless recycled, often end up in landfills or incineration, causing long-term environmental issues (Zhu & Wang, 2020).
Traditional plastics like polyethylene (PE) and PP have well-established recycling systems and can be recycled multiple times (Fredi & Dorigato, 2021). For example, reprocessed PP from meat trays showed reduced Melt Flow Index (MFI) values, indicating it was initially produced through extrusion and thermoforming processes. However, slight increases in MFI during reprocessing suggest some degradation, making it unsuitable for closed-loop recycling into new trays. Additionally, plastic strings from these samples had rough surfaces, differing from other samples (Eriksen et al., 2019). A study found that reprocessed PE from soap bottles maintained consistent MFI values, indicating limited degradation and suitability for closed-loop recycling into new bottles (Barletta et al., 2019). The European Union (EU) has implemented several policies under the European Green Deal and its Circular Economy Action Plan. These include a recycling target of 50% for plastic packaging by 2030 and a ban on various single-use plastic items, such as polystyrene straws, cutlery, food containers, and oxo-degradable plastics, effective from January 2021 (Hoang et al., 2022; Rosenboom, Langer & Traverso, 2022). In contrast, the recycling infrastructure for bioplastics is less developed and varies depending on the type of bioplastic. Improperly sorted bioplastics can contaminate the recycling stream, and their degradability in natural environments depends on their composition and conditions, with some requiring industrial composting facilities to degrade fully (Folino et al., 2020). LCAs comparing bioplastics and traditional plastics have shown varied results depending on the materials and systems studied. In some cases, bioplastics have demonstrated lower carbon emissions (7.60–73.75% lower) and reduced environmental impacts, especially when renewable energy sources are used during production (Chen et al., 2024).
In 2020, Benavides, Lee & Zarè-Mehrjerdi (2020) conducted a comprehensive LCA to examine the environmental impact of biodegradable polylactic acid (PLA) and bio-based polyethylene (bio-PE) plastics, from raw material sourcing to the EOL phase. The study compared these bioplastics to traditional fossil-based plastics like high-density polyethylene (HDPE) and low-density polyethylene (LDPE). The results showed that bio-PE and PLA had lower greenhouse gas (GHG) emissions, with minimal levels recorded at 1.0 and 1.7 kg CO2 equivalent per kg, respectively, when biodegradation did not occur. Fossil energy consumption (FEC) was also lower for these bio-derived plastics, with bio-PE using 29 and PLA 46 MJ per kg. However, the study highlighted a significant issue with PLA’s environmental performance when it biodegrades in landfills and composting environments. In these cases, PLA’s life cycle emissions increased significantly, by 16% to 163%, compared to scenarios where it did not degrade in landfills. This study provides valuable insights into how biodegradability can influence GHG emissions in landfill settings. However, other environmental factors like land and water use, resource depletion, and potential impacts on biodiversity should also be considered, as they may vary depending on the specific context (Atiwesh et al., 2021). The comparison of LCA related parameters of bioplastics and conventional plastics are tabulated in Table 1. When considering key environmental factors, energy consumption is a major concern. Bioplastics typically require less energy to produce compared to traditional plastics, though this can vary depending on the type of bioplastic and manufacturing process (Bishop, Styles & Lens, 2021). Some bioplastics are produced using renewable energy, which further reduces their carbon footprint (Rosenboom, Langer & Traverso, 2022). However, it is important to account for the energy used in growing raw materials, transportation, and end-of-life management when evaluating overall energy consumption. Bioplastics, like corn-based PLA, can reduce greenhouse gas (GHG) emissions by up to 25% compared to standard plastics (Atiwesh et al., 2021). The Biopolymer Feedstock System (BPFS) offers significant environmental benefits, potentially replacing plastics like PP and nylon, which have higher environmental impacts. For example, PP and nylon have carbon footprints of 1.98 and 8.03 kg CO2eq/kg, respectively (Wernet et al., 2016). In a conservative scenario, BPFS can reduce emissions by 67% compared to traditional plastics, with emissions as low as 0.656 kg CO2eq/kg BPFS. In the best-case scenario, emissions reductions can reach up to 116% (Crocker et al., 2020). These findings highlight the environmental advantages of adopting BPFS to reduce plastic-related emissions. During production, bioplastics often generate fewer emissions due to the use of renewable feedstock and more energy-efficient processes. However, total GHG emissions depend on factors such as feedstock type, cultivation practices, manufacturing methods, and end-of-life options (Coppola et al., 2021). It is crucial to consider emissions from all life cycle stages, including the effects of land use changes on carbon sequestration. Water usage in bioplastic production varies depending on the feedstock and manufacturing process (Ita-Nagy et al., 2020). For example, bioplastics made from water-intensive crops like sugarcane may require more water during cultivation. However, compared to traditional plastics, bioplastics generally use less water during the manufacturing stage (Samberger, 2022). When assessing the environmental impact of bioplastics, it is important to consider both direct water use and potential effects on local water resources, such as pollution or water scarcity. Land and resource requirements for bioplastics depend on the feedstock and cultivation methods used (Chaplin-Kramer et al., 2017). Bioplastics made from agricultural crops require land, which can lead to land-use changes and competition with food production. However, some bioplastics are made from non-food sources, agricultural waste, or algae, reducing land use conflicts (Karan et al., 2019). Sustainable land management practices, such as regenerative agriculture, can help mitigate environmental impacts. Resource utilization should also consider feedstock availability, extraction methods, and potential effects on biodiversity and ecosystem services (Schulte et al., 2022).
Table 1. Comparative account of life cycle assessment related parameters of bioplastics and conventional plastics.
| Sr. no. | Parameter | Bioplastic | Conventional plastics |
|---|---|---|---|
| 1 | Raw material extraction | Made from renewable biomass sources like corn starch, sugarcane, or cellulose. The extraction process generally has a lower carbon footprint compared to fossil fuel extraction. | Derived from petroleum, requiring energy-intensive extraction and refining processes with significant greenhouse gas emissions. |
| 2 | Energy consumption | Production generally consumes less energy due to the use of renewable sources. However, the total energy required can vary based on the type of bioplastic and agricultural practices. | Typically, higher energy consumption due to the extraction, refining, and polymerization of fossil fuels. |
| 3 | Greenhouse gas emissions | Generally, emit fewer greenhouse gases during production. However, emissions can vary significantly based on the feedstock and production methods. | Higher greenhouse gas emissions due to fossil fuel use and energy-intensive production processes. |
| 4 | Land use | Require agricultural land for growing feedstock, which can lead to land-use changes, deforestation, and competition with food production. | Do not require agricultural land, but their extraction and refining processes can cause environmental degradation. |
| 5 | Water use | Production can be water-intensive, especially for irrigation of crops used as feedstock. This varies based on agricultural practices and regional water availability. | Water use is generally lower than bioplastics but still significant in extraction and refining processes. |
| 6 | Resource depletion | Utilize renewable resources, potentially reducing the depletion of finite fossil fuel reserves. However, the sustainability of biomass feedstocks can be an issue if not managed properly. | Depend on non-renewable fossil fuels, contributing to resource depletion. |
| 7 | Biodegradability and end-of-life | Many bioplastics are designed to be biodegradable or compostable, reducing their impact on landfills and marine environments. The actual biodegradability depends on specific conditions (e.g., industrial composting vs. home composting). | Generally, not biodegradable, leading to long-term environmental pollution, especially in marine ecosystems. |
| 8 | Toxicity and pollution | Lower risk of releasing toxic substances during degradation, although the use of fertilizers and pesticides in agriculture can cause pollution. | Can release harmful chemicals during production, use, and disposal. Microplastic pollution is a major environmental concern. |
| 9 | Economic factors | Typically, more expensive due to current production scales and technology. However, costs are decreasing as technology improves and production scales up. | Generally cheaper due to established production processes and economies of scale. |
| 10 | Social impact | Potential to create new agricultural and manufacturing jobs, but may also lead to food vs. fuel debates and land-use conflicts. | Established industry with significant economic impact, but associated with negative health impacts in communities near extraction and refining sites. |
Note:
References: (Hobbs et al., 2021; Bishop, Styles & Lens, 2021; Samanta et al., 2022; Ali et al., 2023).
Overview of bioplastic production methods
Bioplastic production involves various methods that use renewable resources to create plastic-like materials. Two prominent methods are fermentation and microorganism-based processes. For instance, PLA is made through the fermentation of renewable feedstocks. Microorganisms like bacteria or yeast convert sugars from plant sources, such as corn or sugarcane, into lactic acid, which is then used to produce PLA (Reshmy et al., 2021). Another method involves using starch from crops like corn, wheat, or potatoes. This process, known as starch blending, mixes starch with plasticizers and additives to improve its properties. The resulting blend can be processed using traditional plastic manufacturing techniques, such as extrusion, injection molding, or blow molding (Carneiro da Silva, Rios & Campomanes Santana, 2023; Dewi et al., 2023). Some bioplastics are created through chemical processes with renewable raw materials. For example, PHAs are biodegradable bioplastics produced by fermenting plant-based sugars or lipids. These polymers can be used to make various plastic products (Francis & Parayil, 2023). Bio-PE is another type of bioplastic made by partially replacing fossil fuel-derived ethylene with ethylene from renewable sources like sugarcane or ethanol. Although it follows the same polymerization process as traditional PE, Bio-PE has a lower carbon footprint because of its renewable feedstock (Zhao et al., 2023). The comparative analysis of bioplastic production methods is shown in Table 2.
Table 2. Comparative analysis of Bioplastic production methods.
| Sr. No. | Method | Source | Yield | Challenge | Reference |
|---|---|---|---|---|---|
| 1 | Fermentation | Sugars, starches, oils | Moderate | High production costs, scale-up challenges, environmental impact of feedstock cultivation | Bhatia et al. (2021) |
| 2 | Chemical synthesis | Biomass, fossil fuels | Moderate | Dependency on fossil fuels, energy-intensive processes, generation of by-products, limited biodegradability | Coppola et al. (2021) |
| 3 | Bio-based polymer blends | Various biobased sources | High | Compatibility issues between different polymers, performance variability, recycling complexities, environmental impact of additives | Censi et al. (2022) |
| 4 | Enzymatic polymerization | Monomers, polymers | High | Limited substrate specificity, control over polymerization parameters, enzyme stability and recyclability | Fernandes et al. (2022) |
Algae are promising feedstocks for bioplastics due to their fast growth and ability to absorb carbon dioxide. Key biopolymer precursors from algae, such as alginate and carrageenan, are used to make algae-based bioplastics. Research is focused on improving production processes and material properties (Cheah et al., 2023). Another approach is blending bio-based polymers with petroleum-derived plastics, like PLA with PET, to enhance performance and reduce the overall carbon footprint (Gironi & Piemonte, 2011; Mori, 2023). The environmental impact of bioplastic production depends largely on how feedstocks are cultivated, including land use, water consumption, and biodiversity preservation (Thomas et al., 2023). Unsustainable practices, like excessive pesticide use or deforestation, can lead to soil erosion, water contamination, habitat loss, and greenhouse gas emissions (Ortas, 2023). Therefore, choosing the right feedstock and practicing sustainable cultivation are crucial for sustainability. The methods used to extract raw materials, whether through fermentation or chemical synthesis, also affect energy consumption, water use, emissions, and waste (Ortega et al., 2022). To reduce these impacts, it is important to use renewable energy, efficient extraction technologies, and optimize resource use (Luderer et al., 2022). The manufacturing of bioplastics involves energy-intensive processes, such as polymerization, compounding, and shaping, which contribute to greenhouse gas emissions and environmental pollution (Atiwesh et al., 2021). To minimize these impacts, adopting energy-efficient equipment, improving production techniques, and using cleaner technologies are essential steps. The disposal of standard plastics and bioplastics differs significantly in terms of environmental impact and sustainability. Traditional plastics are usually disposed of through landfilling or incineration, which can cause long-term pollution and environmental harm (Bishop, Styles & Lens, 2021). In contrast, bioplastics, especially those designed to be biodegradable or compostable, offer more environmentally friendly disposal options. Biodegradable bioplastics break down into natural substances, reducing plastic waste and its negative effects. Compostable bioplastics can be added to organic waste streams and turned into nutrient-rich compost (Mhaddolkar et al., 2024). Overall, bioplastic disposal can be a more sustainable choice compared to traditional plastics, potentially lowering plastic waste and environmental impact. However, effective waste management practices are crucial to fully benefit from these environmental advantages.
Bioplastic waste management
Degradation and disposal techniques of bioplastics
When considering the EOL stage for bioplastics, the focus is on how they degrade and are disposed of. Composting is a common method for bioplastics made from materials like starch or PLA, which are specifically designed to be compostable (Cucina et al., 2021). During composting, organic matter is broken down into nutrient-rich compost in a controlled environment. Certified compostable bioplastics can decompose in industrial composting facilities, where conditions like temperature, humidity, and microbial activity help them break down into water, carbon dioxide, and biomass within a set period (Nazaruddin & Jamari, 2021). Composting is a sustainable disposal method as it creates valuable compost that enriches the soil (Al-Alawi et al., 2019). Another method is anaerobic digestion, where microorganisms break down organic materials without oxygen. Some bioplastics, such as certain biopolyesters, can be processed this way to produce biogas (Benyahya et al., 2021).
The disposal of bioplastics involves several methods, each with its own environmental implications. Anaerobic digestion uses microorganisms to break down bioplastics without oxygen, producing biogas (mainly methane and carbon dioxide) for energy (Coltelli et al., 2021). Mechanical recycling involves sorting, cleaning, shredding, and reprocessing bioplastic waste into granules or pellets, which helps reduce the need for new raw materials. Its effectiveness depends on the type of bioplastic, contamination levels, and recycling infrastructure (Al-Qadri et al., 2022). Chemical recycling breaks bioplastics down into molecular components, which can be turned into new products. Although it can handle mixed plastics, it requires specialized facilities and ongoing development to be economically viable (Agüero et al., 2023). Incineration involves burning bioplastics in waste-to-energy facilities, generating heat. Bioplastics produce about 17 to 25 MJ/kg of heat energy on average. However, this method also releases carbon dioxide and other pollutants, such as volatile organic compounds (VOCs), nitrogen oxides (NOx), and particulate matter, which can harm health and the environment (Kalair et al., 2021). Composting is another method, particularly for bioplastics designed to be compostable. It turns bioplastics into organic matter in composting facilities, reducing carbon emissions compared to traditional composting processes (Vinci et al., 2021). The choice of disposal method for bioplastics depends on factors like the specific type of bioplastic, local waste management infrastructure, and environmental considerations (Khodaei, Álvarez & Mullen, 2021). Effective management also requires proper collection systems, clear labelling, and consumer education.
Comparison of biodegradable, compostable, and non-biodegradable bioplastics
Bioplastics can be categorized into three main types based on their ability to break down and return to the environment: biodegradable, compostable, and non-biodegradable. Biodegradable bioplastics are designed to decompose naturally into simpler substances such as water, carbon dioxide, and biomass through biological processes. This decomposition is aided by microorganisms like bacteria or fungi and can occur in various environments, including soil, water, or industrial composting facilities. However, biodegradability does not guarantee a specific timeframe for decomposition or complete breakdown. If managed properly, biodegradable bioplastics can help reduce waste and minimize environmental impacts (Mendieta et al., 2022; Kochanska et al., 2022; Dzeikala et al., 2023). Compostable bioplastics are a subset of biodegradable plastics that meet specific criteria for breaking down in industrial composting facilities (Mhaddolkar, Koinig & Vollprecht, 2022). Standards such as ASTM D6400 or EN 13432 define these criteria, which include specific temperature, humidity, and microbial conditions. Compostable bioplastics must be disposed of in industrial composting facilities rather than backyard composting to ensure proper degradation. The resulting compost can then be used to enrich soil (Santi, Elegir & Del Curto, 2020; Dzeikala et al., 2023). Non-biodegradable bioplastics do not easily decompose under normal environmental conditions and often have similar properties to traditional plastics, such as durability and longevity. These bioplastics resist natural breakdown and may need to be managed through recycling or energy recovery methods to mitigate their environmental impact (Reichert et al., 2020; Siddiqui et al., 2023). Choosing between biodegradable, compostable, or non-biodegradable bioplastics depends on application needs, waste management capabilities, and environmental considerations (Vaverková et al., 2012; Falzarano et al., 2023).
Enhancing sustainability: disposal impact and recycling ventures
Environmental consequences of improper disposal and lack of infrastructure
Inadequate disposal practices and insufficient infrastructure for bioplastics can lead to significant environmental issues. Improperly discarded bioplastics in oceans, rivers, or forests can persist for long periods, harming wildlife through entanglement or ingestion. This pollution disrupts ecosystems, threatens biodiversity, and damages habitats (Clause, Celestian & Pauly, 2021). In landfills, bioplastics not designed for biodegradation can release harmful chemicals as they break down, potentially contaminating soil and groundwater, which affects local ecosystems and human health (Okoffo et al., 2022). When bioplastics are disposed of in landfills or incinerated instead of being composted or recycled, they can contribute to greenhouse gas (GHG) emissions, reducing their intended environmental benefits (Maione, Lapko & Trucco, 2022). A lack of infrastructure and appropriate waste management systems often results in bioplastics ending up in mixed waste streams or conventional recycling systems where they may not be properly sorted or recycled. This results in missed opportunities for recycling or composting, increases waste generation, and depletes resources (Kovačević, Flinčec Grgac & Bischof, 2021). Bioplastics, which are largely made from renewable resources like plant-based feedstocks, lose their potential for recovery and reuse when not managed correctly. This worsens reliance on fossil fuel-based plastics and contributes to resource depletion. To address these challenges, it is crucial to develop and implement robust waste management infrastructure, including composting and recycling facilities, along with clear labelling and disposal guidelines for bioplastics (Islam & Cullen, 2023). Education and awareness campaigns are also essential to encourage responsible consumer behaviour and promote sustainable disposal practices. Effective management of bioplastics requires collaboration among governments, industry stakeholders, and consumers to minimize environmental impacts and leverage bioplastics as a sustainable alternative to traditional plastics (Moshood et al., 2022).
Exploration of recycling and composting options for bioplastics
Recycling and composting are important options for managing bioplastics at the end of their life cycle.
Recycling
Mechanical recycling involves several steps to manage bioplastic waste. The process starts with collecting and sorting the waste, followed by cleaning and shredding it. The shredded material is then melted and formed into pellets or flakes, which can be used as raw materials for making new bioplastic products. This closed-loop recycling method helps reduce the need for virgin materials and minimizes waste, as shown in Fig. 1 (Cabrera et al., 2022). However, the effectiveness of mechanical recycling depends on factors such as the type of bioplastic, contamination levels, and the availability of recycling facilities. Chemical recycling, also known as feedstock or depolymerization recycling, breaks down bioplastics into their basic molecular components using chemical processes. This method converts bioplastics into monomers or other valuable chemicals, which can be used to produce new plastics or other products (Agüero et al., 2023). Chemical recycling is particularly useful for handling mixed or complex bioplastic materials that are not suitable for mechanical recycling. However, this technology is still developing and requires specialized facilities and further improvements to become more scalable and economically viable (Agüero et al., 2023).
Figure 1. Circular life cycle and recycling pathways of plastic products.
The circular life cycle of plastic products, highlights the stage of manufacture, consumption, and recycling. It shows two primary recycling pathways: mechanical recycling, organic recycling, where biodegradable plastics are composted and returned to the ecosystem. (Modified from Ali et al. (2023)).
Composting
Composting is a controlled process that breaks down organic waste, including some bioplastics, into nutrient-rich compost (Sayara et al., 2020). Industrial composting facilities create the ideal conditions—such as temperature, humidity, and microbial activity—for bioplastics to decompose effectively (Narancic et al., 2020). Bioplastics that meet compostability standards, like ASTM D6400 or EN 13432, can be processed in these facilities. The resulting compost is then used to enrich soil in agriculture or landscaping, closing the organic waste loop (Pesaranhajiabbas et al., 2022). Compostable bioplastics should not be placed in backyard composting systems unless the manufacturer specifies, they are suitable for home composting. These bioplastics need specific conditions for proper breakdown (Folino et al., 2020). Some bioplastics, especially those made from starch or certain compostable polymers, are compatible with home composting systems. They break down naturally in backyard composting environments where food scraps and yard trimmings decompose. To ensure effective degradation, follow guidelines provided by the manufacturer or local composting authorities (Santi, Elegir & Del Curto, 2020). Home composting is a practical and eco-friendly option for managing bioplastics on a smaller scale. However, effective recycling and composting require robust waste management infrastructure, including separate collection systems, clear labelling, and consumer awareness. Collaboration among governments, waste management authorities, industry stakeholders, and consumers is crucial for developing comprehensive recycling and composting systems (Eriksen et al., 2018). Continued research and innovation in these areas will enhance the effectiveness and efficiency of bioplastic disposal options (Hamid et al., 2022).
Impact on biodiversity and ecosystems
Investigation of the ecological implications of bioplastic production and waste
The production and waste management of bioplastics have ecological implications that need to be carefully considered. The investigation of some key ecological implications associated with bioplastic production and waste.
Land use and deforestation
Bioplastics often rely on plant-based materials like corn, sugarcane, or soy, which require agricultural land. Expanding this land for feedstock cultivation can lead to deforestation, loss of natural habitats, and the creation of monocultures, disrupting biodiversity and reducing carbon sequestration (Piemonte & Gironi, 2011). The water-intensive methods used for growing and processing these feedstocks can contribute to water scarcity and pollution from runoff and waste water, negatively impacting aquatic ecosystems (Helmes et al., 2018; López-Pacheco et al., 2022). When bioplastic production depends on fossil fuels, it contributes to greenhouse gas (GHG) emissions and climate change. To mitigate these effects, using renewable energy sources like solar or wind is essential (Melchor-Martínez et al., 2022). Additionally, the manufacturing and refinement of bioplastics can generate air pollution if not managed properly, and intensive feedstock farming can cause soil erosion, threatening soil fertility and ecosystem health (Qin et al., 2021). Improper disposal of bioplastics, especially when they are not recycled or composted, can result in pollution. Non-degrading bioplastics in landfills or natural environments contribute to plastic pollution, which endangers wildlife through ingestion or entanglement (Baldera-Moreno et al., 2022; Faleti, 2022). Incineration of bioplastics, if not properly controlled, can release harmful pollutants into the air. To address these challenges, it is important to use water-efficient irrigation and wastewater treatment, prioritize renewable energy and energy-efficient technologies, and implement soil conservation practices. Developing comprehensive waste management systems that emphasize recycling and composting, along with consumer education on responsible waste management, are crucial steps (Carballo-Sánchez et al., 2022; Notaro, Elisabetta & Alessandro, 2022). By considering these ecological implications and adopting sustainable practices throughout the life cycle of bioplastics, we can minimize their environmental impact and support a transition to a more sustainable, circular economy (de Souza Vandenberghe et al., 2021). Although bioplastics offer benefits by reducing reliance on fossil fuels, their production and disposal still pose significant environmental challenges, such as deforestation, habitat loss, and potential soil and water contamination (López-Pacheco et al., 2022; Kaur et al., 2023; Koottatep et al., 2023).
To address these issues, adopting sustainable sourcing practices and responsible land use is crucial. Best management practices in agriculture, like precision techniques and organic farming, can help reduce soil and water contamination (Kharb & Saharan, 2022). Inadequate waste management of bioplastics can lead to marine pollution, where they break down into harmful microplastics that threaten aquatic life and enter the food chain (Herzke et al., 2021). To prevent this, it is important to promote recycling and proper disposal methods to keep bioplastics out of water systems. Addressing these ecological concerns involves sustainable feedstock sourcing, responsible manufacturing, effective waste management, and strong regulations for bioplastics. Encouraging sustainable agricultural practices and integrated pest management can further reduce environmental impacts (Winkler, Viers & Nicholas, 2017). Developing and enforcing regulations and infrastructure for waste management, including recycling facilities and public education campaigns, supports the responsible disposal of bioplastics. Promoting the use of biodegradable and compostable bioplastics that meet established standards for degradation can also help minimize ecological impacts (Watt et al., 2021). These combined efforts will enhance the potential of bioplastics as sustainable alternatives to traditional plastics.
Mitigation strategies and sustainable practices
Overview of strategies to minimize environmental impacts
To reduce the environmental impact of bioplastics, a comprehensive approach is needed throughout their life cycle. Sustainable sourcing involves using responsibly obtained feedstocks to avoid deforestation, protect biodiversity, and manage land properly (López-Pacheco et al., 2022). This includes using non-food sources like agricultural residues or algae to avoid competing with food supplies. Improving resource efficiency in bioplastic production means optimizing processes, reducing energy use, and minimizing waste (Gbadeyan, Linganiso & Deenadayalu, 2023). This can be achieved by adopting energy-efficient technologies, recycling production by-products, and creating closed-loop systems to reduce resource extraction (Sidek et al., 2019). A Circular Economy approach involves designing bioplastics to be reusable, recyclable, or compostable (Beltran et al., 2021). Ensuring compatibility with existing recycling systems and setting up dedicated collection systems can help keep bioplastics out of landfills, thus reducing waste and conserving resources (Reichert et al., 2020). Developing strong recycling and composting infrastructure includes expanding facilities that can handle various types of bioplastics and promoting consumer education (Ferreira, Alves & Coelhoso, 2016). Providing composting environments suited for bioplastics allows them to break down into valuable compost. Raising consumer awareness about the benefits of bioplastics and proper disposal practices is also crucial (Ambrosio et al., 2021). Clear labelling and educational campaigns help consumers recycle and compost effectively. Policy initiatives support sustainable bioplastic production and disposal by setting standards for biodegradability and compostability, encouraging eco-friendly innovations with financial incentives, and enforcing effective waste management practices (Abe, Branciforti & Brienzo, 2021). Collaboration among governments, industries, researchers, and NGOs can drive improvements in bioplastics, reducing their environmental footprint and enhancing their sustainability (Boneberg et al., 2016). By adopting these strategies, we can minimize the environmental impact of bioplastics and advance a more sustainable, circular approach to plastic production and waste management (Maione, Lapko & Trucco, 2022).
Promising innovations in bioplastics technology
In recent years, innovations in bioplastics technology have focused on improving their environmental performance and expanding their uses. Researchers are developing biopolymer blends that mix different bioplastics or combine them with other materials to enhance their properties (Ziani et al., 2023). These blends include materials like PLA, PHA, starch-based polymers, and cellulose-based polymers, which come from renewable resources and are biodegradable (Acquavia et al., 2021). They are used in areas such as packaging, medical devices, and textiles. While the production of bioplastics is increasing, ongoing research aims to optimize their properties and processing methods to make them more suitable for industrial use and sustainable (Sid et al., 2021). Bioplastic blends can offer better durability, heat resistance, and flexibility while remaining environmentally friendly. For example, blending PLA with other polymers can improve mechanical properties and broaden its applications (Filho et al., 2022). Adding bio-based and biodegradable materials, such as natural fibers, starch, or nanocellulose, further enhances bioplastics (Jeremić et al., 2020). These additives can strengthen the bioplastics, improve their barrier properties, and boost their biodegradability (Youssef et al., 2019). Additionally, biodegradable polymer composites reinforced with natural fibres like hemp or bamboo provide increased strength and lighter weight, making them useful in automotive, construction, and packaging industries as eco-friendly alternatives (Shaikh, Yaqoob & Aggarwal, 2021; Thanu & Deepak, 2022; Dixon & Wilken, 2018).
Role of government regulations and industry initiatives
Government regulations and industry initiatives play a crucial role in shaping the future of bioplastics. These regulations set clear standards for bioplastic production, including environmental performance, biodegradability, compostability, and safety (Melchor-Martínez et al., 2022; Vinci et al., 2021). By enforcing these standards, regulations ensure consistency, build consumer trust, and provide manufacturers with clear guidelines. Governments can boost bioplastics innovation by offering grants, tax incentives, and funding for research and development (Single-Use Plastic Recycling Funding Opportunity Announcement Topic; Tan, Tiwari & Ramakrishna, 2021). This financial support helps advance technology, ease market entry, and speed up the commercialization of sustainable bioplastics. Extended Producer Responsibility (EPR) policies require manufacturers to manage the EOL of their products, encouraging designs that support recycling or composting and fostering better infrastructure (Ambrosio et al., 2021). Restrictions or bans on non-biodegradable or single-use plastics encourage the use of bioplastics as greener alternatives, reducing plastic pollution and promoting a circular economy (Preka et al., 2022; Nielsen et al., 2023). These measures drive innovation in sustainable packaging and increase the use of renewable resources. Industry associations complement these regulations with voluntary sustainability programs, offering best practices, environmental performance metrics, and resource efficiency guidelines (Xu, Cheng & Liao, 2018). Collaborative initiatives within the bioplastics sector bring together companies, universities, and research institutions to explore new feedstocks, improve manufacturing processes, and overcome technical challenges (Batog et al., 2021). These partnerships will accelerate the development of sustainable solutions.
Future outlook
To evaluate the potential of bioplastics in reducing plastic pollution, it is essential to consider various aspects. This includes examining technological advancements, infrastructure needs, market demand, consumer awareness, and the environmental impacts of bioplastics. Ongoing research and technological improvements are expected to enhance the properties, biodegradability, and recyclability of bioplastics, making them more effective substitutes for conventional plastics (López-Pacheco et al., 2022). Developing strong recycling and composting systems is crucial to fully utilize bioplastics. This requires investments from governments, industry leaders, and waste management sectors (Miksch et al., 2022). Increasing consumer awareness about the environmental impact of plastic pollution and the benefits of bioplastics is also important for boosting market demand and encouraging businesses to adopt sustainable practices (Kakadellis, Lee & Harris, 2022). Assessing the overall sustainability of bioplastics involves understanding their complex environmental effects. Future improvements in feedstock sourcing, manufacturing processes, and waste management strategies are expected to reduce the environmental footprint of bioplastics (Siracusa & Blanco, 2020). Adopting a circular economy approach is key to sustainable bioplastic use, focusing on recycling, composting, and using renewable feedstocks (Guzman-Puyol, Benítez & Heredia-Guerrero, 2021). Standardizing and improving LCAs will provide clear insights into the environmental impacts of bioplastics, aiding stakeholders in making informed decisions (Di Bartolo, Infurna & Dintcheva, 2021). A comprehensive approach to sustainability and waste management is vital for addressing environmental challenges related to plastic pollution. Moving towards a circular economy emphasizes resource efficiency, waste reduction, and sustainable production and consumption (Fytianos et al., 2021). Technological innovations are crucial for improving waste management systems, developing sustainable materials and packaging, and enhancing resource efficiency (Raheem et al., 2022). Collaboration among stakeholders is essential for sharing knowledge, mobilizing resources, and achieving effective and sustainable waste management solutions (Barakat et al., 2022). Additionally, industry efforts focus on consumer education and market development (Marquez et al., 2022). Public awareness campaigns and certification programs help consumers understand the benefits of bioplastics, promote responsible consumption, and provide guidance on proper waste management (Filho et al., 2022). Collaborative efforts also support recycling and waste management infrastructure development (Costa et al., 2023). By aligning regulatory frameworks with industry initiatives, governments and stakeholders create a supportive environment for the sustainable growth and widespread adoption of bioplastics (Cowan et al., 2021). This integrated approach is essential for transitioning to a more environmentally friendly and circular economy, addressing global plastic pollution challenges (Dou, Li & Lu, 2022).
Conclusion
Bioplastics show promise in fighting plastic pollution and promoting sustainability because they are made from renewable resources, can biodegrade or compost, and have a smaller carbon footprint compared to traditional plastics. However, to fully realize their benefits, it is important to assess their entire life cycle, from the sourcing of raw materials and production processes to waste management and environmental impact. To minimize negative ecological effects and avoid depleting resources, sustainable production and management practices are essential. Although bioplastics offer advantages like renewable sourcing and biodegradability, their environmental impact can vary based on factors such as the choice of feedstock, land use, energy consumption, and waste management practices. Maximizing the benefits of bioplastics requires a comprehensive approach that includes responsible sourcing, energy-efficient production, development of infrastructure, and consumer education. Successful integration into the economy involves a balanced approach that includes innovation, regulation, behaviour change, and collaboration across different sectors. Addressing plastic pollution and other environmental challenges requires a broad framework for sustainability and waste management. This means considering the entire life cycle of products to find ways to reduce waste, use resources efficiently, and minimize environmental impacts. Collaboration among stakeholders is key to driving systemic change and implementing practices that promote sustainability. Investing in waste prevention, using sustainable materials, building infrastructure, and adopting circular economy principles are crucial for achieving long-term sustainability and ensuring a healthier environment for future generations.
Supplemental Information
The life cycle of bioplastics, from the biorefining of non-edible feedstock and oil to monomer production, polymerization, and formulation into bioplastic products. It also depicts various degradation pathways, including physical (incineration), chemical (thermolysis and solvolysis), and biological (aerobic, anaerobic, and genetic modification) methods, as well as recycling options (Ali et al., 2023).
Funding Statement
The authors received no funding for this work.
Additional Information and Declarations
Competing Interests
Ganesh Chandrakant Nikalje is an Academic Editor for PeerJ.
Author Contributions
Kushi Yadav conceived and designed the review outline, performed the literature survey, analyzed the data, prepared figures and/or tables, authored or reviewed drafts of the article, and approved the final draft.
Ganesh Chandrakant Nikalje conceived and designed the outline of the review, performed the literature survey, analyzed the data, prepared figures and/or tables, authored or reviewed drafts of the article, and approved the final draft.
Data Availability
The following information was supplied regarding data availability:
This is a literature review.
References
- Abe, Branciforti & Brienzo (2021).Abe MM, Branciforti MC, Brienzo M. Biodegradation of hemicellulose-cellulose-starch-based bioplastics and microbial polyesters. Recycling. 2021;6(1):22. doi: 10.3390/recycling6010022. [DOI] [Google Scholar]
- Acquavia et al. (2021).Acquavia MA, Pascale R, Martelli G, Bondoni M, Bianco G. Natural polymeric materials: a solution to plastic pollution from the agro-food sector. Polymers. 2021;13(1):158. doi: 10.3390/polym13010158. [DOI] [PMC free article] [PubMed] [Google Scholar]
- Adam et al. (2020).Adam I, Walker TR, Bezerra JC, Clayton A. Policies to reduce single-use plastic marine pollution in West Africa. Marine Policy. 2020;116(4):103928. doi: 10.1016/j.marpol.2020.103928. [DOI] [Google Scholar]
- Agüero et al. (2023).Agüero Á, Corral Perianes E, Abarca de las Muelas SS, Lascano D, de la Fuente García-Soto MD, Peltzer MA, Balart R, Arrieta MP. Plasticized mechanical recycled PLA films reinforced with microbial cellulose particles obtained from kombucha fermented in yerba mate waste. Polymers. 2023;15(2):285. doi: 10.3390/polym15020285. [DOI] [PMC free article] [PubMed] [Google Scholar]
- Akash et al. (2023).Akash S, Sivaprakash B, Rajamohan N, Vo DVN. Biotechnology to convert carbon dioxide into biogas, bioethanol, bioplastic and succinic acid using algae, bacteria and yeast: a review. Environmental Chemistry Letters. 2023;21(3):1477–1497. doi: 10.1007/s10311-023-01569-3. [DOI] [Google Scholar]
- Al-Alawi et al. (2019).Al-Alawi M, Szegi T, El Fels L, Hafidi M, Simon B, Gulyas M. Green waste composting under GORE(R) cover membrane at industrial scale: physico-chemical properties and spectroscopic assessment. International Journal of Recycling of Organic Waste in Agriculture. 2019;8(S1):385–397. doi: 10.1007/s40093-019-00311-w. [DOI] [Google Scholar]
- Al-Qadri et al. (2022).Al-Qadri AA, Ahmed U, Abdul Jameel AG, Zahid U, Usman M, Ahmad N. Simulation and modelling of hydrogen production from waste plastics: technoeconomic analysis. Polymers. 2022;14(10):2056. doi: 10.3390/polym14102056. [DOI] [PMC free article] [PubMed] [Google Scholar]
- Alhazmi, Almansour & Aldhafeeri (2021).Alhazmi H, Almansour FH, Aldhafeeri Z. Plastic waste management: a review of existing life cycle assessment studies. Sustainability. 2021;13(10):5340. doi: 10.3390/su13105340. [DOI] [Google Scholar]
- Ali et al. (2023).Ali SS, Abdelkarim EA, Elsamahy T, Al-Tohamy R, Li F, Kornaros M, Zuorro A, Zhu D, Sun J. Bioplastic production in terms of life cycle assessment: a state-of-the-art review. Environmental Science and Ecotechnology. 2023;15:100254. doi: 10.1016/j.ese.2023.100254. [DOI] [PMC free article] [PubMed] [Google Scholar]
- Altalhi (2022).Altalhi T. Handbook of bioplastics and biocomposites engineering applications. Philippines, United States: John Wiley & Sons; 2022. [Google Scholar]
- Ambrosio et al. (2021).Ambrosio G, Faglia G, Tagliabue S, Baratto C. Study of the degradation of biobased plastic after stress tests in water. Coatings. 2021;11(11):1330. doi: 10.3390/coatings11111330. [DOI] [Google Scholar]
- Andreeßen & Steinbüchel (2019).Andreeßen C, Steinbüchel A. Recent developments in non-biodegradable biopolymers: precursors, production processes, and future perspectives. Applied Microbiology and Biotechnology. 2019;103(1):143–157. doi: 10.1007/s00253-018-9483-6. [DOI] [PubMed] [Google Scholar]
- Ashrafi et al. (2019).Ashrafi M, Acciaro M, Walker TR, Magnan GM, Adams M. Corporate sustainability in Canadian and US maritime ports. Journal of Cleaner Production. 2019;220(10):386–397. doi: 10.1016/j.jclepro.2019.02.098. [DOI] [Google Scholar]
- Atiwesh et al. (2021).Atiwesh G, Mikhael A, Parrish CC, Banoub J, Le TA. Environmental impact of bioplastic use: a review. Heliyon. 2021;7(9):e07918. doi: 10.1016/j.heliyon.2021.e07918. [DOI] [PMC free article] [PubMed] [Google Scholar]
- Baldera-Moreno et al. (2022).Baldera-Moreno Y, Pino V, Farres A, Banerjee A, Gordillo F, Andler R. Biotechnological aspects and mathematical modeling of the biodegradation of plastics under controlled conditions. Polymers. 2022;14(3):375. doi: 10.3390/polym14030375. [DOI] [PMC free article] [PubMed] [Google Scholar]
- Barakat et al. (2022).Barakat B, Abou Jaoude A, Mantalovas K, Dunn IP, Acuto F, Yazoghli-Marzouk O, Di Mino G, Srour I. Examining the critical factors that influence the success of construction and demolition waste reverse logistics operations. International Journal of Environmental Impacts. 2022;5(3):236–248. doi: 10.2495/EI-V5-N3-236-248. [DOI] [Google Scholar]
- Barletta et al. (2019).Barletta M, Aversa C, Puopolo M, Vesco S. Extrusion blow molding of environmentally friendly bottles in biodegradable polyesters blends. Polymer Testing. 2019;77:105885. doi: 10.1016/j.polymertesting.2019.05.001. [DOI] [Google Scholar]
- Batog et al. (2021).Batog J, Bujnowicz K, Gieparda W, Wawro A, Rojewski S. Effective utilisation of halophyte biomass from saline soils for biorefining processes. Molecules. 2021;26(17):5393. doi: 10.3390/molecules26175393. [DOI] [PMC free article] [PubMed] [Google Scholar]
- Beckstrom et al. (2020).Beckstrom BD, Wilson MH, Crocker M, Quinn JC. Bioplastic feedstock production from microalgae with fuel co-products: a techno-economic and life cycle impact assessment. Algal Research. 2020;46:101769. doi: 10.1016/j.algal.2019.101769. [DOI] [Google Scholar]
- Beltran et al. (2021).Beltran M, Tjahjono B, Bogush A, Julião J, Teixeira EL. Food plastic packaging transition towards circular bioeconomy: a systematic review of literature. Sustainability. 2021;13(7):3896. doi: 10.3390/su13073896. [DOI] [Google Scholar]
- Benavides, Lee & Zarè-Mehrjerdi (2020).Benavides PT, Lee U, Zarè-Mehrjerdi O. Life cycle greenhouse gas emissions and energy use of polylactic acid, bio-derived polyethylene, and fossil-derived polyethylene. Journal of Cleaner Production. 2020;277:124010. doi: 10.1016/j.jclepro.2020.124010. [DOI] [Google Scholar]
- Benyahya et al. (2021).Benyahya Y, Fail A, Alali A, Sadik M. Recovery of household waste by generation of biogas as energy and compost as bio-fertilizer—a review. Processes. 2021;10(1):81. doi: 10.3390/pr10010081. [DOI] [Google Scholar]
- Bhatia et al. (2021).Bhatia SK, Otari SV, Jeon JM, Gurav R, Choi YK, Bhatia RK, Pugazhendhi A, Bhatia RK, Pugazhendhi A, Kumar V, Banu JR, Yoon J-J, Choi K-Y, Yang Y-H. Biowaste-to-bioplastic (polyhydroxyalkanoates): conversion technologies, strategies, challenges, and perspective. Bioresource Technology. 2021;326:124733. doi: 10.1016/j.biortech.2021.124733. [DOI] [PubMed] [Google Scholar]
- Bishop, Styles & Lens (2021).Bishop G, Styles D, Lens PN. Environmental performance comparison of bioplastics and petrochemical plastics: a review of life cycle assessment (LCA) methodological decisions. Resources, Conservation and Recycling. 2021;168(18):105451. doi: 10.1016/j.resconrec.2021.105451. [DOI] [Google Scholar]
- Bishop, Styles & Lens (2022).Bishop G, Styles D, Lens PN. Land-use change and valorization of feedstock side-streams determine the climate mitigation potential of bioplastics. Resources, Conservation and Recycling. 2022;180(1):106185. doi: 10.1016/j.resconrec.2022.106185. [DOI] [Google Scholar]
- Boneberg et al. (2016).Boneberg BS, Machado GD, Santos DF, Gomes F, Faria DJ, Gomes LA, Santos FA. Biorefinery of lignocellulosic biopolymers. Revista Eletrônica Científica da UERGS. 2016;2(1):79–100. doi: 10.21674/2448-0479.21.79-100. [DOI] [Google Scholar]
- Broeren et al. (2017).Broeren ML, Kuling L, Worrell E, Shen L. Environmental impact assessment of six starch plastics focusing on wastewater-derived starch and additives. Resources, Conservation and Recycling. 2017;127:246–255. doi: 10.1016/j.resconrec.2017.09.001. [DOI] [Google Scholar]
- Cabrera et al. (2022).Cabrera G, Li J, Maazouz A, Lamnawar K. A journey from processing to recycling of multilayer waste films: a review of main challenges and prospects. Polymers. 2022;14(12):2319. doi: 10.3390/polym14122319. [DOI] [PMC free article] [PubMed] [Google Scholar]
- Carballo-Sánchez et al. (2022).Carballo-Sánchez MP, Alarcón A, Pérez-Moreno J, Ferrera-Cerrato R. Agricultural and forestry importance of microorganism-plant symbioses: a microbial source for biotechnological innovations. Reviews in Agricultural Science. 2022;10:344–355. doi: 10.7831/ras.10.0_344. [DOI] [Google Scholar]
- Carneiro da Silva, Rios & Campomanes Santana (2023).Carneiro da Silva LR, Rios AD, Campomanes Santana RM. Polymer blends of poly (lactic acid) and starch for the production of films applied in food packaging: a brief review. Polymers from Renewable Resources. 2023;14(2):108–153. doi: 10.1177/20412479231154924. [DOI] [Google Scholar]
- Censi et al. (2022).Censi V, Saiano F, Bongiorno D, Indelicato S, Napoli A, Piazzese D. Bioplastics: a new analytical challenge. Frontiers in Chemistry. 2022;10:971792. doi: 10.3389/fchem.2022.971792. [DOI] [PMC free article] [PubMed] [Google Scholar]
- Chalermthai et al. (2021).Chalermthai B, Giwa A, Schmidt JE, Taher H. Life cycle assessment of bioplastic production from whey protein obtained from dairy residues. Bioresource Technology Reports. 2021;15(1):100695. doi: 10.1016/j.biteb.2021.100695. [DOI] [Google Scholar]
- Chaplin-Kramer et al. (2017).Chaplin-Kramer R, Sim S, Hamel P, Bryant B, Noe R, Mueller C, Rigarlsford G, Kulak M, Kowal V, Sharp R, Clavreul J. Life cycle assessment needs predictive spatial modelling for biodiversity and ecosystem services. Nature Communications. 2017;8(1):15065. doi: 10.1038/ncomms15065. [DOI] [PMC free article] [PubMed] [Google Scholar]
- Cheah et al. (2023).Cheah WY, Er AC, Aiyub K, Yasin NH, Ngan SL, Chew KW, Khoo KS, Ling TC, Juan JC, Ma Z, Show PL. Current status and perspectives of algae-based bioplastics: a reviewed potential for sustainability. Algal Research. 2023;71:103078. doi: 10.1016/j.algal.2023.103078. [DOI] [Google Scholar]
- Chen et al. (2024).Chen G, Li J, Sun Y, Wang Z, Leeke GA, Moretti C, Cheng Z, Wang Y, Li N, Mu L, Li J, Tao J, Yan B, Hou L. Replacing traditional plastics with biodegradable plastics: impact on carbon emissions. Engineering. 2024;32:152–162. doi: 10.1016/j.eng.2023.10.002. [DOI] [Google Scholar]
- Chong et al. (2022).Chong JW, Tan X, Khoo KS, Ng HS, Jonglertjunya W, Yew GY, Show PL. Microalgae-based bioplastics: future solution towards mitigation of plastic wastes. Environmental Research. 2022;206:112620. doi: 10.1016/j.envres.2021.112620. [DOI] [PubMed] [Google Scholar]
- Clause, Celestian & Pauly (2021).Clause AG, Celestian AJ, Pauly GB. Plastic ingestion by freshwater turtles: a review and call to action. Scientific Reports. 2021;11(1):5672. doi: 10.1038/s41598-021-84846-x. [DOI] [PMC free article] [PubMed] [Google Scholar]
- Coltelli et al. (2021).Coltelli MB, Bertolini A, Aliotta L, Gigante V, Vannozzi A, Lazzeri A. Chain extension of poly (Lactic acid)(pla)–based blends and composites containing bran with biobased compounds for controlling their processability and recyclability. Polymers. 2021;13(18):3050. doi: 10.3390/polym13183050. [DOI] [PMC free article] [PubMed] [Google Scholar]
- Coppola et al. (2021).Coppola G, Gaudio MT, Lopresto CG, Calabro V, Curcio S, Chakraborty S. Bioplastic from renewable biomass: a facile solution for a greener environment. Earth Systems and Environment. 2021;5(2):231–251. doi: 10.1007/s41748-021-00208-7. [DOI] [Google Scholar]
- Costa et al. (2023).Costa A, Encarnação T, Tavares R, Todo Bom T, Mateus A. Bioplastics: innovation for green transition. Polymers. 2023;15(3):517. doi: 10.3390/polym15030517. [DOI] [PMC free article] [PubMed] [Google Scholar]
- Cowan et al. (2021).Cowan E, Booth AM, Misund A, Klun K, Rotter A, Tiller R. Single-use plastic bans: exploring stakeholder perspectives on best practices for reducing plastic pollution. Environments. 2021;8(8):81. doi: 10.3390/environments8080081. [DOI] [Google Scholar]
- Crocker et al. (2020).Crocker M, Zeller A, Quinn JC, Quiroz Nuila D, Beckstrom B, Kesner S, Mohler D, Pace R, Wilson M. CO2 to bioplastics: beneficial re-use of carbon emissions from coal-fired power plants using microalgae. Lexington, KY (United States): University of Kentucky; 2020. [Google Scholar]
- Cucina et al. (2021).Cucina M, de Nisi P, Tambone F, Adani F. The role of waste management in reducing bioplastics’ leakage into the environment: a review. Bioresource Technology. 2021;337(5):125459. doi: 10.1016/j.biortech.2021.125459. [DOI] [PubMed] [Google Scholar]
- Cywar et al. (2022).Cywar RM, Rorrer NA, Hoyt CB, Beckham GT, Chen EY. Bio-based polymers with performance-advantaged properties. Nature Reviews Materials. 2022;7(2):83–103. doi: 10.1038/s41578-021-00363-3. [DOI] [Google Scholar]
- de Souza Vandenberghe et al. (2021).de Souza Vandenberghe LP, de Oliveira PZ, Bittencourt GA, de Mello AF, Vásquez ZS, Karp SG, Soccol CR. The 2G and 3G bioplastics: an overview. Biotechnology Research and Innovation Journal. 2021;5(1):e2021004. doi: 10.4322/biori.202104. [DOI] [Google Scholar]
- Degli Esposti et al. (2021).Degli Esposti M, Morselli D, Fava F, Bertin L, Cavani F, Viaggi D, Fabbri P. The role of biotechnology in the transition from plastics to bioplastics: an opportunity to reconnect global growth with sustainability. FEBS Open Bio. 2021;11(4):967–983. doi: 10.1002/2211-5463.13119. [DOI] [PMC free article] [PubMed] [Google Scholar]
- Dewi et al. (2023).Dewi R, Sylvia N, Zulnazri, Riza M. Melt flow index (MFI) analysis of sago based thermoplastic starch blend with polypropylene and polyethylene. Materials Today: Proceedings. 2023;87(2):396–400. doi: 10.1016/j.matpr.2023.04.173. [DOI] [Google Scholar]
- Di Bartolo, Infurna & Dintcheva (2021).Di Bartolo A, Infurna G, Dintcheva NT. A review of bioplastics and their adoption in the circular economy. Polymers. 2021;13(8):1229. doi: 10.3390/polym13081229. [DOI] [PMC free article] [PubMed] [Google Scholar]
- Dixon & Wilken (2018).Dixon C, Wilken LR. Green microalgae biomolecule separations and recovery. Bioresources and Bioprocessing. 2018;5(1):1–24. doi: 10.1186/s40643-018-0199-3. [DOI] [Google Scholar]
- Dou, Li & Lu (2022).Dou Z, Li LS, Lu L. A public health-oriented new energy industry competitiveness evaluation. Journal of Environmental and Public Health. 2022;2022(1):17. doi: 10.1155/2022/4573629. [DOI] [PMC free article] [PubMed] [Google Scholar] [Retracted]
- Dzeikala et al. (2023).Dzeikala O, Prochon M, Marzec A, Szczepanik S. Preparation and characterization of gelatin-agarose and gelatin-starch blends using alkaline solvent. International Journal of Molecular Sciences. 2023;24(2):1473. doi: 10.3390/ijms24021473. [DOI] [PMC free article] [PubMed] [Google Scholar]
- Eriksen et al. (2019).Eriksen MK, Christiansen JD, Daugaard AE, Astrup TF. Closing the loop for PET, PE and PP waste from households: influence of material properties and product design for plastic recycling. Waste Management. 2019;96(5):75–85. doi: 10.1016/j.wasman.2019.07.005. [DOI] [PubMed] [Google Scholar]
- Eriksen et al. (2018).Eriksen M, Thiel M, Prindiville M, Kiessling T. Microplastic: what are the solutions. In: Wagner M, Lambert S, editors. Freshwater Microplastics. The Handbook of Environmental Chemistry. Cham: Springer; 2018. pp. 273–298. [DOI] [Google Scholar]
- Faleti (2022).Faleti AI. Microplastics in the Nigerian environment-a review. 2022. ChemRxiv.
- Falzarano et al. (2023).Falzarano M, Polettini A, Pomi R, Rossi A, Zonfa T. Anaerobic biodegradability of commercial bioplastic products: systematic bibliographic analysis and critical assessment of the latest advances. Materials. 2023;16(6):2216. doi: 10.3390/ma16062216. [DOI] [PMC free article] [PubMed] [Google Scholar]
- Fernandes et al. (2022).Fernandes CD, Oechsler BF, Sayer C, de Oliveira D, de Araújo PHH. Recent advances and challenges on enzymatic synthesis of biobased polyesters via polycondensation. European Polymer Journal. 2022;169:111132. doi: 10.1016/j.eurpolymj.2022.111132. [DOI] [Google Scholar]
- Ferreira, Alves & Coelhoso (2016).Ferreira AR, Alves VD, Coelhoso IM. Polysaccharide-based membranes in food packaging applications. Membranes. 2016;6(2):22. doi: 10.3390/membranes6020022. [DOI] [PMC free article] [PubMed] [Google Scholar]
- Filho et al. (2022).Filho WL, Barbir J, Abubakar IR, Paço A, Stasiskiene Z, Hornbogen M, Christin, Fendt MT, Voronova V, Klõga M. Consumer attitudes and concerns with bioplastics use: an international study. PLOS ONE. 2022;17(4):e0266918. doi: 10.1371/journal.pone.0266918. [DOI] [PMC free article] [PubMed] [Google Scholar]
- Folino et al. (2020).Folino A, Karageorgiou A, Calabrò PS, Komilis D. Biodegradation of wasted bioplastics in natural and industrial environments: a review. Sustainability. 2020;12(15):6030. doi: 10.3390/su12156030. [DOI] [Google Scholar]
- Francis & Parayil (2023).Francis D, Parayil DJ. Handbook of Bioplastics and Biocomposites Engineering Applications. 2023. Microbial technology in bioplastic production and engineering; pp. 121–148. [Google Scholar]
- Fredi & Dorigato (2021).Fredi G, Dorigato A. Recycling of bioplastic waste: a review. Advanced Industrial and Engineering Polymer Research. 2021;4(3):159–177. doi: 10.1016/j.aiepr.2021.06.006. [DOI] [Google Scholar]
- Fytianos et al. (2021).Fytianos G, Ioannidou E, Thysiadou A, Mitropoulos AC, Kyzas GZ. Microplastics in Mediterranean coastal countries: a recent overview. Journal of Marine Science and Engineering. 2021;9(1):98. doi: 10.3390/jmse9010098. [DOI] [Google Scholar]
- Gadaleta et al. (2023).Gadaleta G, Ferrara C, De Gisi S, Notarnicola M, De Feo G. Life cycle assessment of end-of-life options for cellulose-based bioplastics when introduced into a municipal solid waste management system. Science of the Total Environment. 2023;871:161958. doi: 10.1016/j.scitotenv.2023.161958. [DOI] [PubMed] [Google Scholar]
- Galati et al. (2022).Galati A, Alaimo LS, Ciaccio T, Vrontis D, Fiore M. Plastic or not plastic? That’s the problem: analysing the Italian students purchasing behavior of mineral water bottles made with eco-friendly packaging. Resources, Conservation and Recycling. 2022;179(3):106060. doi: 10.1016/j.resconrec.2021.106060. [DOI] [Google Scholar]
- Gbadeyan, Linganiso & Deenadayalu (2023).Gbadeyan OJ, Linganiso LZ, Deenadayalu N. Assessment and optimization of thermal stability and water absorption of loading snail shell nanoparticles and sugarcane bagasse cellulose fibers on polylactic acid bioplastic films. Polymers. 2023;15(6):1557. doi: 10.3390/polym15061557. [DOI] [PMC free article] [PubMed] [Google Scholar]
- Gioia et al. (2021).Gioia C, Giacobazzi G, Vannini M, Totaro G, Sisti L, Colonna M, Marchese P, Celli A. End of life of biodegradable plastics: composting versus Re/upcycling. ChemSusChem. 2021;14(19):4167–4175. doi: 10.1002/cssc.202101226. [DOI] [PMC free article] [PubMed] [Google Scholar]
- Gironi & Piemonte (2011).Gironi F, Piemonte V. Bioplastics and petroleum-based plastics: strengths and weaknesses. Energy Sources, Part A: Recovery, Utilization, and Environmental Effects. 2011;33(21):1949–1959. doi: 10.1080/15567030903436830. [DOI] [Google Scholar]
- Gong et al. (2023).Gong L, Passari AK, Yin C, Kumar Thakur V, Newbold J, Clark W, Jiang Y, Kumar S, Gupta VK. Sustainable utilization of fruit and vegetable waste bioresources for bioplastics production. Critical Reviews in Biotechnology. 2023;44(2):236–254. doi: 10.1080/07388551.2022.2157241. [DOI] [PubMed] [Google Scholar]
- Guzman-Puyol, Benítez & Heredia-Guerrero (2021).Guzman-Puyol S, Benítez JJ, Heredia-Guerrero JA. Sustainable bio-based polymers: towards a circular bioeconomy. Polymers. 2021;14(1):22. doi: 10.3390/polym14010022. [DOI] [PMC free article] [PubMed] [Google Scholar]
- Hahladakis (2020).Hahladakis JN. Delineating the global plastic marine litter challenge: clarifying the misconceptions. Environmental Monitoring and Assessment. 2020;192(5):1. doi: 10.1007/s10661-020-8202-9. [DOI] [PMC free article] [PubMed] [Google Scholar]
- Hamid et al. (2022).Hamid L, Elhady S, Abdelkareem A, Fahim I. Fabricating starch-based bioplastic reinforced with bagasse for food packaging. Circular Economy and Sustainability. 2022;2(3):1065–1076. doi: 10.1007/s43615-021-00139-5. [DOI] [Google Scholar]
- Helmes et al. (2018).Helmes RJ, López-Contreras AM, Benoit M, Abreu H, Maguire J, Moejes F, Burg SW. Environmental impacts of experimental production of lactic acid for bioplastics from Ulva spp. Sustainability. 2018;10(7):2462. doi: 10.3390/su10072462. [DOI] [Google Scholar]
- Herzke et al. (2021).Herzke D, Ghaffari P, Sundet JH, Tranang CA, Halsband C. Microplastic fiber emissions from wastewater effluents: abundance, transport behavior and exposure risk for biota in an arctic fjord. Frontiers in Environmental Science. 2021;9:662168. doi: 10.3389/fenvs.2021.662168. [DOI] [Google Scholar]
- Hoang et al. (2022).Hoang AT, Varbanov PS, Nižetić S, Sirohi R, Pandey A, Luque R, Ng KH. Perspective review on municipal solid waste-to-energy route: characteristics, management strategy, and role in circular economy. Journal of Cleaner Production. 2022;359(9):131897. doi: 10.1016/j.jclepro.2022.131897. [DOI] [Google Scholar]
- Hobbs et al. (2021).Hobbs SR, Harris TM, Barr WJ, Landis AE. Life cycle assessment of bioplastics and food waste disposal methods. Sustainability. 2021;13(12):6894. doi: 10.3390/su13126894. [DOI] [Google Scholar]
- Islam & Cullen (2023).Islam S, Cullen JM. Criteria for assessing sustainability of lignocellulosic wastes: applied to the cellulose nanofibril packaging production in the UK. Polymers. 2023;15(6):1336. doi: 10.3390/polym15061336. [DOI] [PMC free article] [PubMed] [Google Scholar]
- Ita-Nagy et al. (2020).Ita-Nagy D, Vázquez-Rowe I, Kahhat R, Chinga-Carrasco G, Quispe I. Reviewing environmental life cycle impacts of biobased polymers: current trends and methodological challenges. The International Journal of Life Cycle Assessment. 2020;25(11):2169–2189. doi: 10.1007/s11367-020-01829-2. [DOI] [Google Scholar]
- Jeremić et al. (2020).Jeremić S, Milovanović J, Mojicević M, Škaro Bogojević S, Nikodinović-Runić J. Understanding bioplastic materials-current state and trends. Journal of the Serbian Chemical Society. 2020;85(12):1507–1538. doi: 10.2298/JSC200720051J. [DOI] [Google Scholar]
- Jin et al. (2023).Jin Y, Lenzen M, Montoya A, Laycock B, Yuan Z, Lant P, Li M, Wood R, Malik A. Greenhouse gas emissions, land use and employment in a future global bioplastics economy. Resources, Conservation and Recycling. 2023;193(8):106950. doi: 10.1016/j.resconrec.2023.106950. [DOI] [Google Scholar]
- Kakadellis & Harris (2020).Kakadellis S, Harris ZM. Don’t scrap the waste: the need for broader system boundaries in bioplastic food packaging life-cycle assessment-a critical review. Journal of Cleaner Production. 2020;274(1526):122831. doi: 10.1016/j.jclepro.2020.122831. [DOI] [Google Scholar]
- Kakadellis, Lee & Harris (2022).Kakadellis S, Lee PH, Harris ZM. Two birds with one stone: bioplastics and food waste anaerobic co-digestion. Environments. 2022;9(1):9. doi: 10.3390/environments9010009. [DOI] [Google Scholar]
- Kalair et al. (2021).Kalair AR, Seyedmahmoudian M, Stojcevski A, Abas N, Khan N. Waste to energy conversion for a sustainable future. Heliyon. 2021;7(10):e08155. doi: 10.1016/j.heliyon.2021.e08155. [DOI] [PMC free article] [PubMed] [Google Scholar]
- Karan et al. (2019).Karan H, Funk C, Grabert M, Oey M, Hankamer B. Green bioplastics as part of a circular bioeconomy. Trends in Plant Science. 2019;24(3):237–249. doi: 10.1016/j.tplants.2018.11.010. [DOI] [PubMed] [Google Scholar]
- Kaur et al. (2023).Kaur P, Bhola S, Kumar P, Kumar V, Kulshreshtha S, Sharma A, Park S, Choi KY. Recent development in urban polyhydroxyalkanoates biorefineries. ChemBioEng Reviews. 2023;10(4):441–461. doi: 10.1002/cben.202200045. [DOI] [Google Scholar]
- Kharb & Saharan (2022).Kharb J, Saharan R. Sustainable biodegradable plastics and their applications: a mini review. IOP Conference Series: Materials Science and Engineering. 2022;1248(1):012008. doi: 10.1088/1757-899X/1248/1/012008. [DOI] [Google Scholar]
- Khatami et al. (2021).Khatami K, Perez-Zabaleta M, Owusu-Agyeman I, Cetecioglu Z. Waste to bioplastics: how close are we to sustainable polyhydroxyalkanoates production? Waste Management. 2021;119:374–388. doi: 10.1016/j.wasman.2020.10.008. [DOI] [PubMed] [Google Scholar]
- Khodaei, Álvarez & Mullen (2021).Khodaei D, Álvarez C, Mullen AM. Biodegradable packaging materials from animal processing co-products and wastes: an overview. Polymers. 2021;13(15):2561. doi: 10.3390/polym13152561. [DOI] [PMC free article] [PubMed] [Google Scholar]
- Kiessling et al. (2023).Kiessling T, Hinzmann M, Mederake L, Dittmann S, Brennecke D, Böhm-Beck M, Knickmeier K, Thiel M. What potential does the EU single-use plastics directive have for reducing plastic pollution at coastlines and riversides? An evaluation based on citizen science data. Waste Management. 2023;164(1–2):106–118. doi: 10.1016/j.wasman.2023.03.042. [DOI] [PubMed] [Google Scholar]
- Kochanska et al. (2022).Kochanska E, Wozniak K, Nowaczyk A, Piedade PJ, de Almeida Lavorato ML, Almeida AM, Morais ARC, Lukasik RM. Global ban on plastic and what next? Are consumers ready to replace plastic with the second-generation bioplastic? Results of the snowball sample consumer research in China, Western and Eastern Europe, North America and Brazil. International Journal of Environmental Research and Public Health. 2022;19(21):13970. doi: 10.3390/ijerph192113970. [DOI] [PMC free article] [PubMed] [Google Scholar]
- Koottatep et al. (2023).Koottatep T, Winijkul E, Xue W, Panuvatvanich A, Visvanathan C, Pussayanavin T, Limphitakphong N, Polprasert C. Marine plastics abatement: technology, management, business and future trends (Volume 2) IWA Publishing; 2023. [Google Scholar]
- Kovačević, Flinčec Grgac & Bischof (2021).Kovačević Z, Flinčec Grgac S, Bischof S. Progress in biodegradable flame retardant nano-biocomposites. Polymers. 2021;13(5):741. doi: 10.3390/polym13050741. [DOI] [PMC free article] [PubMed] [Google Scholar]
- Kumar et al. (2021).Kumar R, Verma A, Shome A, Sinha R, Sinha S, Jha PK, Vara Prasad PV. Impacts of plastic pollution on ecosystem services, sustainable development goals, and need to focus on circular economy and policy interventions. Sustainability. 2021;13(17):9963. doi: 10.3390/su13179963. [DOI] [Google Scholar]
- López-Pacheco et al. (2022).López-Pacheco IY, Rodas-Zuluaga LI, Cuellar-Bermudez SP, Hidalgo-Vázquez E, Molina-Vazquez A, Araújo RG, Martínez-Ruiz M, Varjani S, Barceló D, Iqbal HM, Parra-Saldívar R. Revalorization of microalgae biomass for synergistic interaction and sustainable applications: bioplastic generation. Marine Drugs. 2022;20(10):601. doi: 10.3390/md20100601. [DOI] [PMC free article] [PubMed] [Google Scholar]
- Luderer et al. (2022).Luderer G, Madeddu S, Merfort L, Ueckerdt F, Pehl M, Pietzcker R, Rottoli M, Schreyer F, Bauer N, Baumstark L, Bertram C. Impact of declining renewable energy costs on electrification in low-emission scenarios. Nature Energy. 2022;7(1):32–42. doi: 10.1038/s41560-021-00937-z. [DOI] [Google Scholar]
- Maione, Lapko & Trucco (2022).Maione C, Lapko Y, Trucco P. Towards a circular economy for the plastic packaging sector: insights from the Italian case. Sustainable Production and Consumption. 2022;34(1526):78–89. doi: 10.1016/j.spc.2022.09.002. [DOI] [Google Scholar]
- Mannina et al. (2020).Mannina G, Presti D, Montiel-Jarillo G, Carrera J, Suárez-Ojeda ME. Recovery of polyhydroxyalkanoates (PHAs) from wastewater: a review. Bioresource Technology. 2020;297(6):122478. doi: 10.1016/j.biortech.2019.122478. [DOI] [PubMed] [Google Scholar]
- Marquez et al. (2022).Marquez R, Zwilling J, Zambrano F, Tolosa L, Marquez ME, Venditti R, Jameel H, Gonzalez R. Nanoparticles and essential oils with antiviral activity on packaging and surfaces: an overview of their selection and application. Journal of Surfactants and Detergents. 2022;25(6):667–701. doi: 10.1002/jsde.12609. [DOI] [Google Scholar]
- Melchor-Martínez et al. (2022).Melchor-Martínez EM, Macías-Garbett R, Alvarado-Ramírez L, Araújo RG, Sosa-Hernández JE, Ramírez-Gamboa D, Parra-Arroyo L, Alvarez AG, Monteverde RP, Cazares KA, Reyes-Mayer A. Towards a circular economy of plastics: an evaluation of the systematic transition to a new generation of bioplastics. Polymers. 2022;14(6):1203. doi: 10.3390/polym14061203. [DOI] [PMC free article] [PubMed] [Google Scholar]
- Mendieta et al. (2022).Mendieta CM, González G, Vallejos ME, Area MC. Bio-polyethylene furanoate (Bio-PEF) from lignocellulosic biomass adapted to the circular bioeconomy. BioResources. 2022;17(4):7313–7337. doi: 10.15376/biores.17.4.Mendieta. [DOI] [Google Scholar]
- Mhaddolkar, Koinig & Vollprecht (2022).Mhaddolkar N, Koinig G, Vollprecht D. Near-infrared identification and sorting of polylactic acid. Detritus. 2022;20(20):29–40. doi: 10.31025/2611-4135/2022.15216. [DOI] [Google Scholar]
- Mhaddolkar et al. (2024).Mhaddolkar N, Tischberger-Aldrian A, Astrup TF, Vollprecht D. Consumers confused ‘where to dispose biodegradable plastics?’: a study of three waste streams. Waste Management & Research. 2024;42(9):776–787. doi: 10.1177/0734242X241231408. [DOI] [PMC free article] [PubMed] [Google Scholar]
- Miksch et al. (2022).Miksch L, Köck M, Gutow L, Saborowski R. Bioplastics in the sea: rapid in-vitro evaluation of degradability and persistence at natural temperatures. Frontiers in Marine Science. 2022;9:920293. doi: 10.3389/fmars.2022.920293. [DOI] [Google Scholar]
- Mongkoldhumrongkul & Sukkanta (2022).Mongkoldhumrongkul K, Sukkanta P. Carbon emission assessment of bioplastics from durian peel. IOP Conference Series: Earth and Environmental Science. 2022;1111(1):012003. doi: 10.1088/1755-1315/1111/1/012003. [DOI] [Google Scholar]
- Morão & De Bie (2019).Morão A, De Bie F. Life cycle impact assessment of polylactic acid (PLA) produced from sugarcane in Thailand. Journal of Polymers and the Environment. 2019;27(11):2523–2539. doi: 10.1007/s10924-019-01525-9. [DOI] [Google Scholar]
- Mori (2023).Mori R. Replacing all petroleum-based chemical products with natural biomass-based chemical products: a tutorial review. RSC Sustainability. 2023;1(2):179–212. doi: 10.1039/D2SU00014H. [DOI] [Google Scholar]
- Moshood et al. (2021).Moshood TD, Nawanir G, Mahmud F, Mohamad F, Ahmad MH, Abdul Ghani A. Expanding policy for biodegradable plastic products and market dynamics of bio-based plastics: challenges and opportunities. Sustainability. 2021;13(11):6170. doi: 10.3390/su13116170. [DOI] [Google Scholar]
- Moshood et al. (2022).Moshood TD, Nawanir G, Mahmud F, Mohamad F, Ahmad MH, AbdulGhani A. Sustainability of biodegradable plastics: new problem or solution to solve the global plastic pollution? Current Research in Green and Sustainable Chemistry. 2022;5:100273. doi: 10.1016/j.crgsc.2022.100273. [DOI] [Google Scholar]
- Muthusamy & Pramasivam (2019).Muthusamy MS, Pramasivam S. Bioplastics-an eco-friendly alternative to petrochemical plastics. Current World Environment. 2019;14(1):49–59. doi: 10.12944/CWE.14.1.07. [DOI] [Google Scholar]
- Narancic et al. (2020).Narancic T, Cerrone F, Beagan N, O’Connor KE. Recent advances in bioplastics: application and biodegradation. Polymers. 2020;12(4):920. doi: 10.3390/polym12040920. [DOI] [PMC free article] [PubMed] [Google Scholar]
- Nazaruddin & Jamari (2021).Nazaruddin NS, Jamari SS. Effect on thermal properties of nanocellulose fibre (NCF) reinforced biodegradable polyhydroxylalkanoates (PHA) composite. Journal of Chemical Engineering and Industrial Biotechnology. 2021;7(1):10–13. doi: 10.15282/jceib.v7i1.6111. [DOI] [Google Scholar]
- Nielsen et al. (2023).Nielsen MB, Clausen LP, Cronin R, Hansen SF, Oturai NG, Syberg K. Unfolding the science behind policy initiatives targeting plastic pollution. Microplastics and Nanoplastics. 2023;3(1):3. doi: 10.1186/s43591-022-00046-y. [DOI] [PMC free article] [PubMed] [Google Scholar]
- Notaro, Elisabetta & Alessandro (2022).Notaro S, Elisabetta L, Alessandro P. Behaviours and attitudes of consumers towards bioplastics: an exploratory study in Italy. Journal of Forest Science. 2022;2022(68):121–135. doi: 10.17221/26/2022-JFS. [DOI] [Google Scholar]
- Okoffo et al. (2022).Okoffo ED, Chan CM, Rauert C, Kaserzon S, Thomas KV. Identification and quantification of micro-bioplastics in environmental samples by pyrolysis-gas chromatography-mass spectrometry. Environmental Science & Technology. 2022;56(19):13774–13785. doi: 10.1021/acs.est.2c04091. [DOI] [PubMed] [Google Scholar]
- Ortas (2023).Ortas I. A solution to soil, water and environmental crises. A Solution to the Crises of Soil, Water, and Climate in Plant Production. 2023;18 [Google Scholar]
- Ortega et al. (2022).Ortega F, Versino F, López OV, García MA. Biobased composites from agro-industrial wastes and by-products. Emergent Materials. 2022;5(3):873–921. doi: 10.1007/s42247-021-00319-x. [DOI] [PMC free article] [PubMed] [Google Scholar]
- Palsra & Chauhan (2020).Palsra S, Chauhan C. Bioplastics-environment friendly and innovative plastic: a review. Journal of Green Engineering. 2020;10(10):7541–7553. [Google Scholar]
- Paul-Pont et al. (2023).Paul-Pont I, Ghiglione JF, Gastaldi E, Ter Halle A, Huvet A, Bruzaud S, Lagarde F, Galgani F, Duflos G, George M, Fabre P. Discussion about suitable applications for biodegradable plastics regarding their sources, uses and end of life. Waste Management. 2023;157(5):242–248. doi: 10.1016/j.wasman.2022.12.022. [DOI] [PubMed] [Google Scholar]
- Pesaranhajiabbas et al. (2022).Pesaranhajiabbas E, Pal AK, Rodriguez-Uribe A, Mohanty AK, Misra M. Biodegradable polymer blends: studies on performance control through droplet to co-continuous morphology. ACS Applied Polymer Materials. 2022;4(8):5546–5556. doi: 10.1021/acsapm.2c00603. [DOI] [Google Scholar]
- Piemonte & Gironi (2011).Piemonte V, Gironi F. Land-use change emissions: how green are the bioplastics? Environmental Progress & Sustainable Energy. 2011;30(4):685–691. doi: 10.1002/ep.10518. [DOI] [Google Scholar]
- Preka et al. (2022).Preka R, Fiorentino G, De Carolis R, Barberio G. The challenge of plastics in a circular perspective. Frontiers in Sustainable Cities. 2022;4:920242. doi: 10.3389/frsc.2022.920242. [DOI] [Google Scholar]
- Putri (2018).Putri RE. The water and land footprint of bioplastics. 2018. (Master’s thesis, University of Twente)
- Qin et al. (2021).Qin M, Chen C, Song B, Shen M, Cao W, Yang H, Gong J. A review of biodegradable plastics to biodegradable microplastics: another ecological threat to soil environments? Journal of Cleaner Production. 2021;312:127816. doi: 10.1016/j.jclepro.2021.127816. [DOI] [Google Scholar]
- Raheem et al. (2022).Raheem D, Soltermann AT, Tamiozzo LV, Cogo A, Favén L, Punam NJ, Sarmiento CR, Rainosalo E, Picco F, Morla F, Nilson A. Partnership for international development: Finland-Argentina conference on circular economy and bioeconomy with emphasis on food sovereignty and sustainability. International Journal of Environmental Research and Public Health. 2022;19(3):1773. doi: 10.3390/ijerph19031773. [DOI] [PMC free article] [PubMed] [Google Scholar]
- Reichert et al. (2020).Reichert CL, Bugnicourt E, Coltelli MB, Cinelli P, Lazzeri A, Canesi I, Braca F, Martínez BM, Alonso R, Agostinis L, Verstichel S. Bio-based packaging: materials, modifications, industrial applications and sustainability. Polymers. 2020;12(7):1558. doi: 10.3390/polym12071558. [DOI] [PMC free article] [PubMed] [Google Scholar]
- Reshmy et al. (2021).Reshmy R, Thomas D, Philip E, Paul SA, Madhavan A, Sindhu R, Sirohi R, Varjani S, Pugazhendhi A, Pandey A, Binod P. Bioplastic production from renewable lignocellulosic feedstocks: a review. Reviews in Environmental Science and Bio/Technology. 2021;20(1):167–187. doi: 10.1007/s11157-021-09565-1. [DOI] [Google Scholar]
- Rosenboom, Langer & Traverso (2022).Rosenboom JG, Langer R, Traverso G. Bioplastics for a circular economy. Nature Reviews Materials. 2022;7(2):117–137. doi: 10.1038/s41578-021-00407-8. [DOI] [PMC free article] [PubMed] [Google Scholar]
- Salwa et al. (2021).Salwa HN, Sapuan SM, Mastura MT, Zuhri MY, Ilyas RA. Bio-Based Packaging: Material, Environmental and Economic Aspects. 2021. Life cycle assessment of bio-based packaging products; pp. 381–411. [Google Scholar]
- Samanta et al. (2022).Samanta P, Dey S, Ghosh AR, Senapati T. Encyclopedia of Green Materials. Singapore: Springer Nature Singapore; 2022. Life cycle assessment of bioplastics; pp. 1–6. [Google Scholar]
- Samberger (2022).Samberger C. The role of water circularity in the food-water-energy nexus and climate change mitigation. Energy Nexus. 2022;6(6):100061. doi: 10.1016/j.nexus.2022.100061. [DOI] [Google Scholar]
- Santi, Elegir & Del Curto (2020).Santi R, Elegir G, Del Curto B. Designing for sustainable behaviour practices in consumers: a case study on compostable materials for packaging. Proceedings of the Design Society: DESIGN Conference 2020, May, 1; Cambridge University Press; 2020. pp. 1647–1656. [Google Scholar]
- Sayara et al. (2020).Sayara T, Basheer-Salimia R, Hawamde F, Sánchez A. Recycling of organic wastes through composting: process performance and compost application in agriculture. Agronomy. 2020;10(11):1838. doi: 10.3390/agronomy10111838. [DOI] [Google Scholar]
- Schulte et al. (2022).Schulte LA, Dale BE, Bozzetto S, Liebman M, Souza GM, Haddad N, Richard TL, Basso B, Brown RC, Hilbert JA, Arbuckle JG. Meeting global challenges with regenerative agriculture producing food and energy. Nature Sustainability. 2022;5(5):384–388. doi: 10.1038/s41893-021-00827-y. [DOI] [Google Scholar]
- Shaheen & Sabir (2017).Shaheen A, Sabir N. Effect of tillage, residue and fertilizer on yields within a wheat-maize cropping system. Sarhad Journal of Agriculture. 2017;33(1):127–138. doi: 10.17582/journal.sja/2017.33.1.127.138. [DOI] [Google Scholar]
- Shaikh, Yaqoob & Aggarwal (2021).Shaikh S, Yaqoob M, Aggarwal P. An overview of biodegradable packaging in the food industry. Current Research in Food Science. 2021;4(12):503–520. doi: 10.1016/j.crfs.2021.07.005. [DOI] [PMC free article] [PubMed] [Google Scholar]
- Sid et al. (2021).Sid S, Mor RS, Kishore A, Sharanagat VS. Bio-sourced polymers as alternatives to conventional food packaging materials: a review. Trends in Food Science & Technology. 2021;115(1):87–104. doi: 10.1016/j.tifs.2021.06.026. [DOI] [Google Scholar]
- Siddiqui et al. (2023).Siddiqui SA, Sundarsingh A, Bahmid NA, Nirmal N, Denayer JF, Karimi K. A critical review on biodegradable food packaging for meat: materials, sustainability, regulations, and perspectives in the EU. Comprehensive Reviews in Food Science and Food Safety. 2023;22(5):4147–4185. doi: 10.1111/1541-4337.13202. [DOI] [PubMed] [Google Scholar]
- Sidek et al. (2019).Sidek IS, Draman SF, Abdullah SR, Anuar N. Current development on bioplastics and its future prospects: an introductory review. INWASCON Technology Magazine. 2019;1:3–8. doi: 10.26480/itechmag.01.2019.03.08. [DOI] [Google Scholar]
- Siracusa & Blanco (2020).Siracusa V, Blanco I. Bio-polyethylene (Bio-PE), Bio-polypropylene (Bio-PP) and bio-poly (ethylene terephthalate) (Bio-PET): recent developments in bio-based polymers analogous to petroleum-derived ones for packaging and engineering applications. Polymers. 2020;12(8):1641. doi: 10.3390/polym12081641. [DOI] [PMC free article] [PubMed] [Google Scholar]
- Talwar & Holden (2022).Talwar N, Holden NM. The limitations of bioeconomy LCA studies for understanding the transition to sustainable bioeconomy. The International Journal of Life Cycle Assessment. 2022;27(5):680–703. doi: 10.1007/s11367-022-02053-w. [DOI] [PMC free article] [PubMed] [Google Scholar]
- Tan, Tiwari & Ramakrishna (2021).Tan J, Tiwari SK, Ramakrishna S. Single-use plastics in the food services industry: can it be sustainable? Materials Circular Economy. 2021;3(1):7. doi: 10.1007/s42824-021-00019-1. [DOI] [Google Scholar]
- Thanu & Deepak (2022).Thanu HP, Deepak MD. Developing a building performance score model for assessing the sustainability of buildings. Smart and Sustainable Built Environment. 2022;11(1):143–161. doi: 10.1108/SASBE-03-2020-0031. [DOI] [Google Scholar]
- Thomas et al. (2023).Thomas AP, Kasa VP, Dubey BK, Sen R, Sarmah AK. Synthesis and commercialization of bioplastics: organic waste as a sustainable feedstock. Science of the Total Environment. 2023;904:167243. doi: 10.1016/j.scitotenv.2023.167243. [DOI] [PubMed] [Google Scholar]
- Van Roijen & Miller (2022).Van Roijen EC, Miller SA. A review of bioplastics at end-of-life: linking experimental biodegradation studies and life cycle impact assessments. Resources, Conservation and Recycling. 2022;181:106236. doi: 10.1016/j.resconrec.2022.106236. [DOI] [Google Scholar]
- Vaverková et al. (2012).Vaverková M, Toman F, Adamcová D, Kotovicová J. Study of the biodegrability of degradable/biodegradable plastic material in a controlled composting environment. Ecological Chemistry and Engineering S. 2012;19(3):347–358. doi: 10.2478/v10216-011-0025-8. [DOI] [Google Scholar]
- Vinci et al. (2021).Vinci G, Ruggieri R, Billi A, Pagnozzi C, Di Loreto MV, Ruggeri M. Sustainable management of organic waste and recycling for bioplastics: a LCA approach for the Italian case study. Sustainability. 2021;13(11):6385. doi: 10.3390/su13116385. [DOI] [Google Scholar]
- Watt et al. (2021).Watt E, Picard M, Maldonado B, Abdelwahab MA, Mielewski DF, Drzal LT, Misra M, Mohanty AK. Ocean plastics: environmental implications and potential routes for mitigation–a perspective. RSC Advances. 2021;11(35):21447–21462. doi: 10.1039/D1RA00353D. [DOI] [PMC free article] [PubMed] [Google Scholar]
- Wernet et al. (2016).Wernet G, Bauer C, Steubing B, Reinhard J, Moreno-Ruiz E, Weidema B. The ecoinvent database Version 3 (Part 1): overview and methodology. The International Journal of Life Cycle Assessment. 2016;21(9):1218–1230. doi: 10.1007/s11367-016-1087-8. [DOI] [Google Scholar]
- Westlake et al. (2023).Westlake JR, Tran MW, Jiang Y, Zhang X, Burrows AD, Xie M. Biodegradable biopolymers for active packaging: demand, development and directions. Sustainable Food Technology. 2023;1(1):50–72. doi: 10.1039/D2FB00004K. [DOI] [Google Scholar]
- Winkler, Viers & Nicholas (2017).Winkler KJ, Viers JH, Nicholas KA. Assessing ecosystem services and multifunctionality for vineyard systems. Frontiers in Environmental Science. 2017;5:15. doi: 10.3389/fenvs.2017.00015. [DOI] [Google Scholar]
- Wydra et al. (2021).Wydra S, Hüsing B, Köhler J, Schwarz A, Schirrmeister E, Voglhuber-Slavinsky A. Transition to the bioeconomy-analysis and scenarios for selected niches. Journal of Cleaner Production. 2021;294(1):126092. doi: 10.1016/j.jclepro.2021.126092. [DOI] [Google Scholar]
- Xu, Cheng & Liao (2018).Xu CK, Cheng H, Liao ZJ. Towards sustainable growth in the textile industry: a case study of environmental policy in China. Polish Journal of Environmental Studies. 2018;27(5):2325–2336. doi: 10.15244/pjoes/79720. [DOI] [Google Scholar]
- Youssef et al. (2019).Youssef AM, Hasanin MS, Abd El-Aziz ME, Darwesh OM. Green, economic, and partially biodegradable wood plastic composites via enzymatic surface modification of lignocellulosic fibers. Heliyon. 2019;5(3):e01332. doi: 10.1016/j.heliyon.2019.e01332. [DOI] [PMC free article] [PubMed] [Google Scholar]
- Zhao et al. (2023).Zhao X, Wang Y, Chen X, Yu X, Li W, Zhang S, Dong T. Sustainable bioplastics derived from renewable natural resources for food packaging. Matter International Journal of Science and Technology. 2023;6(1):97–127. doi: 10.1016/j.matt.2022.11.006. [DOI] [Google Scholar]
- Zhu & Wang (2020).Zhu J, Wang C. Biodegradable plastics: green hope or greenwashing? Marine Pollution Bulletin. 2020;161:111774. doi: 10.1016/j.marpolbul.2020.111774. [DOI] [PubMed] [Google Scholar]
- Ziani et al. (2023).Ziani K, Ioniță-Mîndrican CB, Mititelu M, Neacșu SM, Negrei C, Moroșan E, Drăgănescu D, Preda OT. Microplastics: a real global threat for environment and food safety: a state-of-the-art review. Nutrients. 2023;15(3):617. doi: 10.3390/nu15030617. [DOI] [PMC free article] [PubMed] [Google Scholar]
Associated Data
This section collects any data citations, data availability statements, or supplementary materials included in this article.
Supplementary Materials
The life cycle of bioplastics, from the biorefining of non-edible feedstock and oil to monomer production, polymerization, and formulation into bioplastic products. It also depicts various degradation pathways, including physical (incineration), chemical (thermolysis and solvolysis), and biological (aerobic, anaerobic, and genetic modification) methods, as well as recycling options (Ali et al., 2023).
Data Availability Statement
The following information was supplied regarding data availability:
This is a literature review.

