Britta Denise Hardesty
Kathryn Willis
Joanna Vince- 1CSIRO Oceans and Atmosphere, Hobart, TAS, Australia
- 2Centre for Marine Socioecology, University of Tasmania, Hobart, TAS, Australia
- 3School of Aquatic and Fishery Science, University of Washington, Seattle, WA, United States
- 4School of Social Sciences, University of Tasmania, Launceston, TAS, Australia
There is an increased focus on plastic pollution and the resultant harms in our oceans and on our shores at local, regional, and global scales. New technologies are being developed and trialed, multilateral agreements are coming into play, and the role of a circular economy is increasingly touted as the key to help solve the plastic pollution crisis. Simultaneously, we are witnessing the disruption of global supply chains from the COVID-19 pandemic, increased fuel prices and increased scope and scale of natural disasters. Individual countries are setting national targets and are developing national plans of action to combat plastic pollution. In this paper, we focus on Australia's National Plastics Plan as a case study of a national approach to addressing this transboundary issue. We discuss the Plan in relation to supply chains, the role of standards and best practices, and principles for a successful circular plastic economy. We explicitly consider the role of reverse logistics and regional approaches that could be developed and implemented within island nations. Overall, we argue for culturally appropriate, economically and environmentally place-based solutions as a necessary approach to help reduce plastic losses to the environment, acknowledging that plastics leakage to the environment is a social equity issue.
Introduction
Plastic production is increasing globally at unprecedented rates. Accordingly, plastic pollution is now described as a crisis and a wicked problem (Landon-Lane, 2018; Vince and Stoett, 2018; Stoll et al., 2020), which transcends geopolitical borders and affects individuals and countries preferentially based upon wealth. Further confounding the management of wicked problems is the notion that “decisions are not allowed to be wrong” (Rittel and Webber, 1973; Landon-Lane, 2018). This 21st-century tragedy of the commons (Vince and Hardesty, 2018) affects the most remote marine environments, with plastics that weigh thousands of kilograms (e.g., derelict fishing gear; see Richardson et al., 2019) to those small enough to pass through tissues and cell boundaries (Järvenpää et al., 2022). Plastics of all sizes have been discovered in the most remote marine environments from the artic to the Antarctic (Kelly et al., 2020; Collard et al., 2021), including the deepest depths of the ocean in the Mariana Trench (Chiba et al., 2018). It is estimated that globally, around nearly 80% of all plastics ever produced has accumulated in landfills or the natural environment, while only 9% of all plastics have been recycled and 12% has been incinerated (Geyer et al., 2017). Plastic is estimated have a social and environmental cost of US $2.2 trillion each year (Forrest et al., 2019). An estimated 19 to 23 million metric tons of plastic waste has entered aquatic and marine ecosystems on a global scale, and this is predicted to reach up to 53 million metric tons annually by 2030 if current trends continue (Borrelle et al., 2020).
While plastic has only been in production for around 60 years, its ubiquity in society—and in the environment—is notorious. Up to 80% of the plastic found in the coastal and marine environment is sourced from the land, and we require socially, culturally appropriate, place-based solutions to prevent manufactured plastics reaching the global ocean. The plastic problem is so widespread across the world's terrestrial and marine environments that microplastics have been found in the snow on the Swiss Alps (Bergmann et al., 2019) and on the Antarctic continent (Zhang et al., 2020), as well as in the deepest depths of the ocean (Barrett et al., 2020). The impact of plastics on human health as a result of its presence in the environment is still relatively unknown, however, some evidence suggests that the leaching of endocrine disrupters from plastic can be linked to numerous human health issues (Flaws et al., 2020). The global COVID-19 pandemic has further complicated the problem resulting in an increase of single-use plastic and personal protective equipment use and waste in the environment (Prata et al., 2020; Silva et al., 2020; Schofield et al., 2021). This transboundary problem has grown exponentially. To address this, policy making needs to be responsive to maximise effectiveness.
There are a number of international measures, including treaties and soft law/governance attempts to support and encourage international collaboration to reduce plastic losses to the environment. The Honolulu Strategy is a global framework document which meant to guide countries toward reducing plastic inputs to the marine environment (UNEP, 2011). Following this, we have seen the Manilla Declaration on Furthering the Implementation of the Global Programme of Action for the Protection of the Marine Environment from Land-based Activities (2012), the G7 Action Plan to Combat Marine Litter (2015), and more recently, the Basel Convention. To date, the Basel Convention is the sole global instrument that addresses plastic waste in a legally binding framework, however, compliance is difficult to enforce (Raubenheimer and Mcilgorm, 2018). In March 2022 UNEP passed a Resolution “To end Plastic Pollution” which will begin the negotiations toward a legally binding agreement by 2024. In the meanwhile, nation states such as Australia will need to manage their plastic use through national approaches.
Australia's National Plastic Plan
Historically, waste management has happened at state and local levels. However, in 2021 the federal government announced a National Plastics Plan (DAWE, 2021), which followed the first National Plastics Summit in early 2020.
This Plan outlines that the Australian government will address plastic pollution by
“working with industry to fast-track the phase-out of particularly problematic plastic materials; stopping the export of unprocessed plastic waste and promoting product stewardship through the Recycling and Waste Reduction Act 2020; unprecedented investments to turbo-charge Australia's plastic recycling capacity; research to make Australia a global leader in plastic recycling and reprocessing; community education to help consumers make informed decisions and recycle correctly” (DAWE, 2021).
The aims of the Plastics Plan include, inter alia, to phase out non-compostable plastic packaging, consumer education, actions to reduce plastics leaking into the marine environment and an emphasis on research. This Plan has a number of targets for the immediate future including phasing out expanded polystyrene in consumer packaging by 2022 and having 100% reusable, recyclable or compostable packaging by 2025. The Recycling and Waste Reduction Act (2020) provides a national framework to manage waste and recycling across Australia including waste exports (DAWE, 2021). These regulations and plans provide a national framework; however, it is the state and local governments that are responsible for waste management and recycling efforts. While the responsibility falls on local governments in national and state plans, support and resources by upper levels of government will deliver a nationally coordinated approach and ensure effective implementation. For example, in multilevel political systems, such as Australia, local governments are responsible for waste management. With increased pressure to grow recycling capabilities, more resources will be required. Additionally, successful implementation of the Plan will require developing resilient supply-chains that overcome system shocks such as oil prices affecting recycling sector economics, disruptions in global supply chains from waste bans and COVID-19, and the increasing influence of politics on the plastics sector (Ebner and Iacovidou, 2021).
The effect of COVID-19 on plastic pollution and supply chains
In December 2019, the SARS-CoV-2 virus began to spread around the world, the first pandemic of such severity in centuries. Given the severity of the respiratory syndrome that results from the novel coronavirus and its highly contagious nature, what began as a health crisis has quickly become an economic, social, political and environmental threat (Silva et al., 2020). Initially, the world experienced a global shutdown in international and domestic travel. Consequent to people becoming less mobile were decreased carbon emissions, increased sightings of wildlife in urban areas, and potentially decreased amounts of several types of plastic waste lost to the environment. However, this decrease was counteracted by the tremendous growth in single-use plastic personal protective equipment (PPE) and other medical waste associated with the pandemic (Ammendolia et al., 2021; Schofield et al., 2021). Additionally, there was a proliferation of single-use plastic bags, cups and take away containers associated with the food industry (Parashar and Hait, 2021). This demand on plastics for packaging, medical use and other applications is expected to grow (Prata et al., 2020). We have also seen plastic industry lobbyists utilize the hygiene and cleanliness concerns of customers to pressure jurisdictions to reverse or delay policies to ban or reduce single-use plastics (Prata et al., 2020; Silva et al., 2020; Da Costa, 2021).
Increasing disruptions to supply chains around the world began in early 2020 when the World Health Organization declared COVID-19 a global health emergency (Hedwall, 2020; Magableh, 2021). Supply chain disruptions have occurred for a range of products such as medicines and medical equipment including PPE, fuel, electricity, food, toilet paper and other household goods. Examples of supply chain disruptions have included demand drop (e.g., airline travel), demand surge (e.g., toilet paper, online shopping), reduction in productivity (e.g., retail or restaurant jobs), storage/access restrictions (e.g., storage warehouses, meat production and storage facilities, etc.), a shortage of raw materials (e.g., electronics parts such as memory chips, building materials) (Pujawan and Bah, 2022). These supply chain disruptions are unevenly distributed among countries, industries and communities and highlight the instability within global markets (Bassett et al., 2021; Castañeda-Navarrete et al., 2021). Countries are seeking to reduce their reliability on global markets by building and strengthening resilient regional and domestic markets. One approach that is seeing an increased focus is the shift to an increasingly circular plastics economy. This focus is heightened by the desire to buffer supply chains from system shocks (such as having resulted from the current COVID-19 pandemic, political instability, and other emergent or urgent crises (Vince and Hardesty, in press).
The potential for a plastics circular economy
The magnification of single-use plastic consumption, insufficient disposal and management during the pandemic highlighted the urgent need to close the plastic loop. Recently, there has been a shift in perspective, as countries begin to acknowledge the value of plastic and a circular plastic economy (Yuan et al., 2021). If we treat plastic as a commodity, rather than as waste, we will increase the market for material recovery. A voluntary contribution from industry has been proposed as one approach to support the elimination of plastic pollution and help drive a circular plastic economy (Forrest et al., 2019). Embedding a whole of life cycle approach that includes plastics manufacturers and multi-national corporations will undoubtedly assist in changing the dial on the global community's relationship with plastic. Current circular economy solutions can often be derived from experiences and management of waste in OECD (Organization for Economic Co-operation and Development) countries and may lack applicability to low-income nations or communities (Mihai et al., 2022). This only emphasizes the need for circular economy solutions to be place-based, tailored to a region, so that they adequately address necessary social and ethical dimensions (Murray et al., 2017). For example, some argue that plastic waste in developing countries could be solved by locally managed decentralized circular economy models (Browning et al., 2021). Circular approaches need to consider context, socioeconomics and transport as well as culture, social and economic context. Approaches suitable in higher OECD countries may not be appropriate in small island developing states, for example, where land and resources are much more limited.
Australia has established an Australian Circular Economy Hub and Marketplace to support the transition for Australian companies, communities and individuals to a circular system. In Australia, the adoption of circular economy principles could abate approximately 165 million tons of carbon pollution each year (Thorpe and Carmody, 2021) and establishing a plastics circular economy has been valued at $2 trillion. Lengthening and diversifying supply-chains within a circular system will buffer supply-chains from system shocks such as disruptions caused by catastrophic weather events or pandemics. At present, recirculating many plastic polymers back into the economy are constrained by material quality, product design and current sorting, handling and processing practices (Hahladakis and Iacovidou, 2018). Advancements in reprocessing and sorting technology alongside the redesigning of plastic products will progress the quality standard improvements required to increase secondary material recovery and recycling and enable a circular model transition to succeed (Hahladakis and Iacovidou, 2018). Circular plastics solutions that are adapted to the small island context where landfill space is scarce, and waste infrastructure is often lacking are more likely to succeed. Taking a regional approach may yield more positive, collaborative outcomes, whereby materials recover is more likely to prosper, and circular businesses can develop that are place-based, socially and culturally appropriate, whilst keeping financial benefits local.
Harnessing innovations and technology opportunities
It seems that nearly on a daily basis, we learn of novel approaches to addressing the plastic waste issue. These include everything from social enterprises such as recovering thongs and turning them into artwork or toys (https://oceansoleonline.com/) to chemical recycling (Thiounn and Smith, 2020), alternative packaging materials such as seaweed (Teixeira-Costa and Andrade, 2022), refillable container systems, and the proliferation of “degradable/biodegradable” plastic bags, food containers, and other food associated items (Evans et al., 2020). Product design and recycling systems (including the collection, sorting and reprocessing of materials) is a crucial point where government and industry can work hand-in-hand to provide products to consumers that make recycling easier and advance plastic pollution reductions. Success will require collaboration across the whole lifecycle of plastic packaging production, and to date, the pace to achieving a sustainable circular plastics economy has been slow (Gerassimidou et al., 2022). Advances in plastic-alternative materials will facilitate the phase-out of problematic and hard to recycle single-use plastics, such as expanded polystyrene used for packaging fill and consumer food and beverage containers; and microbeads used in cosmetic, cleaning, and personal care products. Advances in software programs will facilitate more recycling, such as the Recycle Mate or CurbCycle App to aid consumer decision-making regarding the recyclability of a product; or AI-enabled autonomous sorting systems in material recovery facilities. Australia is funding projects advancing their technology capacity to recycling plastics and integrating plastic waste into other materials. For example, recently projects funded by the Cooperative Research Center span chemical recycling of plastics, integrating plastic waste as a concrete or asphalt aggregate, and smart/AI technologies to improve recycling facility efficiency and material quality (CRC-P, 2022).
Advances in technology to capture and clean litter trap devices on urban drainage networks will improve the capture of plastics before they reach the ocean. Advancements in product labeling and polymer composite standards will additionally facilitate increases in recycling rates. For example, simplifying the complexity of current polymers and polymer composites could improve their recirculation into new products (Kummerer et al., 2020). Make international accepted definitions for biodegradable, degradable, oxo-degradable plastic standards to improve trust and transparency in domestic and international supply-chains. Improve product labeling to provide information that makes it easier for consumers to dispose of the item correctly (Burrows et al., 2022). For example, Australia aims to have 80% of supermarket products to display the Australasian Recycling Label, a world-leading label system (United Nations Environment Programme Consumers International, 2020) which provides information on how each component of the product should be disposed (Figure 1). Furthermore, consideration of the important role logistics can play in moving material between locations is critical to reduce carbon costs, increase benefits where they are needed and advance opportunities for increased circularity.
Figure 1. Example of the Australasian recycling label to be featured on 80% of supermarket products by 2023. The label will also be used for business-business packaging.
Australia as a regional leader
A fundamental springboard that launched plastic pollution into the forefront of the minds of decision-makers was a 2015 paper which included a list of the top 20 countries that are losing mismanaged plastic waste to the ocean (see Jambeck et al., 2015). At least half of these countries are within the Asia-Pacific region. Australia, also an island nation within the region, has a unique opportunity to provide guidance and support to neighboring countries.
Australia can become a leader in reducing plastic waste domestically and in the Asia-Pacific region. One major step Australia has taken toward reducing its waste burden on other countries is banning the export of unsorted mixed plastics and unprocessed single polymer or resin plastics. Australia has a larger technological and financial capacity compared to many of its neighbors, putting Australia in a position to develop and trial different management solutions and support neighboring nations to do the same. The country has prioritized supporting community-led projects that address local environmental priorities (i.e., place-based solutions) through the Plan and has funded over 1,330 community-led projects in 2019–20 to the value of $18 AUS million.
A target of Australia's National Plastics Plan is to phase-out problematic and unnecessary single-use plastics such as expanded polystyrene packaging fill and consumer food and beverage containers. With clear targets, the country is looking at domestic business opportunities and being a regional leader. For example, the country has successfully supported industry to voluntary phase-out plastic microbeads from 99.3% of cosmetic, cleaning and personal care products sold in Australia.
Furthermore, Commonwealth procurement rules and sustainable procurement guidelines have been updated to ensure recycled materials are purchased. Consumers can feel confident that the plastic they place in their recycling bin is recycled and placed back on the shelf as a new product for them to purchase.
The mismatch between political cycles and policy implementation—Agenda setting
A risk to any policy, particularly those that arise from surges in public interest, is its discontinued or delayed implementation due to changes in elected governments, political agenda, and public attention (Bailey, 2022). Amid the disruptions of the COVID-19 pandemic, Australia moved forward with policy actions that target reducing plastic waste. With plastic pollution identified as an important global issue, increased focus from government and industry to tackle the problem will be key. Governments often take low-risk approaches, typical of wicked problems, to deal with creeping crises such as plastic pollution (Mcconnell, 2018; Mæland and Staupe-Delgado, 2020). The “crisis overreaction” to COVID-19 was used as a political tool by many nations, such as the US, Australia and Canada to win national elections in 2020 and 2021 (Maor, 2020). The COVID-19 focus overshadowed the plastic issue. The outcome of the most recent Federal election in Australia held in May resulted in a change of government. While plastics were not a major focus of the campaign, environmental issues and climate change were key topics. The Australia National Plastics Plan does provide long-term guidance for actions that extend beyond a single policial cycle, and the change of government will determine how the Plan will continue to be utilized. The Plan's success will require collaboration between and within those implementing the Plan and its end users. Long-term political will could buffer the Plan's momentum against declining interest which often occurs during change of ministers or government (especially if the political party that forms government changes) (Hudson et al., 2019). Currently, few countries have the mechanisms need to support more robust policies (Gold 2014). Australia's commitment to UNEA and the upcoming Plastics Treaty may be the catalyst to keep plastics on the agenda.
A call to action
A fundamental shift in society's relationship with plastics can include a multitude of approaches. By treating plastic as a commodity rather than as waste and with economic incentives, materials recovery will be improved, which in turn can drive new business opportunities. There is also a substantial role for best practice guidelines and standards, whether for food safe packaging, for targets such as those set by the National Plastics Plan of Australia, or by industry, local or state governments, or from grass roots campaigns (Willis et al., 2022). Taking a regional approach to materials recovery will likely also yield benefits, particularly if reverse logistics are included in products through supply chains. It is an exciting time with the recent binding UNEA 5.2 resolution passed earlier in 2022. There is an increased will and focus on plastics from local to global scales. In this decade of the Ocean, there are multiple opportunities to shift the dial on plastics, from inception, to manufacture, through use and materials recovery. Focusing on place-based, equitable solutions will result in improved outcomes locally, regionally, and globally.
Data availability statement
The original contributions presented in the study are included in the article/supplementary material, further inquiries can be directed to the corresponding author.
Author contributions
All authors listed have made a substantial, direct, and intellectual contribution to the work and approved it for publication.
Funding
This work was supported by CSIRO Oceans and Atmosphere (BDH), the University of Tasmania (JV), and the Fulbright Scholars Program (KW).
Conflict of interest
The authors declare that the research was conducted in the absence of any commercial or financial relationships that could be construed as a potential conflict of interest.
Publisher's note
All claims expressed in this article are solely those of the authors and do not necessarily represent those of their affiliated organizations, or those of the publisher, the editors and the reviewers. Any product that may be evaluated in this article, or claim that may be made by its manufacturer, is not guaranteed or endorsed by the publisher.
References
Ammendolia, J., Saturno, J., Brooks, A. L., Jacobs, S., and Jambeck, J. R. (2021). An emerging source of plastic pollution: environmental presence of plastic personal protective equipment (PPE) debris related to COVID-19 in a metropolitan city. Environ. Pollut. 269, 116160. doi: 10.1016/j.envpol.2020.116160
Bailey, I. (2022). Media coverage, attention cycles and the governance of plastics pollution. Environ. Policy Govern. 1–13. doi: 10.1002/eet.1977
Barrett, J., Chase, Z., Zhang, J., Holl, M. M., Willis, K., Williams, A., et al. (2020). Microplastic pollution in deep-sea sediments from the Great Australian Bight. Front. Mar. Sci. 2020:808doi: 10.3389/fmars.2020.576170
Bassett, H. R., Lau, J., Giordano, C., Suri, S. K., Advani, S., and Sharan, S. (2021). Preliminary lessons from COVID-19 disruptions of small-scale fishery supply chains. World Dev. 143, 105473. doi: 10.1016/j.worlddev.2021.105473
Bergmann, M., Mützel, S., Primpke, S., Tekman, M. B., Trachsel, J., and Gerdts, G. (2019). White and wonderful? Microplastics prevail in snow from the Alps to the Arctic. Sci. Adv. 5, eaax1157. doi: 10.1126/sciadv.aax1157
Borrelle, S. B., Ringma, J., Law, K. L., Monnahan, C. C., Lebreton, L., Mcgivern, A., et al. (2020). Predicted growth in plastic waste exceeds efforts to mitigate plastic pollution. Science 369, 1515–1518. doi: 10.1126/science.aba3656
Browning, S., Beymer-Farris, B., and Seay, J. R. (2021). Addressing the challenges associated with plastic waste disposal and management in developing countries. Curr. Opin. Chem. Eng. 32, 100682. doi: 10.1016/j.coche.2021.100682
Burrows, S. D., Ribeiro, F., O'brien, S., Okoffo, E., Toapanta, T., Charlton, N., et al. (2022). The message on the bottle: rethinking plastic labelling to better encourage sustainable use. Environ. Sci. Policy 132, 109–118. doi: 10.1016/j.envsci.2022.02.015
Castañeda-Navarrete, J., Hauge, J., and López-Gómez, C. (2021). COVID-19's impacts on global value chains, as seen in the apparel industry. Dev. Policy Rev. 39, 953–970. doi: 10.1111/dpr.12539
Chiba, S., Saito, H., Fletcher, R., Yogi, T., Kayo, M., Miyagi, S., et al. (2018). Human footprint in the abyss: 30 year records of deep-sea plastic debris. Marine Policy 96, 204–212. doi: 10.1016/j.marpol.2018.03.022
Collard, F., Husum, K., Eppe, G., Malherbe, C., Hallanger, I. G., Divine, D. V., et al. (2021). Anthropogenic particles in sediment from an Arctic fjord. Sci. Total Environ. 772, 145575. doi: 10.1016/j.scitotenv.2021.145575
CRC-P (2022). CRC Projects Selection Round Outcomes. Canberra, Australia: The Australian Government Cooperative Research Centres Projects
Da Costa, J. P. (2021). The 2019 global pandemic and plastic pollution prevention measures: playing catch-up. Sci. Total Environ. 774, 145806. doi: 10.1016/j.scitotenv.2021.145806
DAWE (2021). National Plastics Plan 2021. Department of Agriculture, W.a.t.E. (ed). Canberra: Commonwealth of Australia, 16.
Ebner, N., and Iacovidou, E. (2021). The challenges of Covid-19 pandemic on improving plastic waste recycling rates. Sustain. Prod. Consum. 28, 726–735. doi: 10.1016/j.spc.2021.07.001
Evans, D. M., Parsons, R., Jackson, P., Greenwood, S., and Ryan, A. (2020). Understanding plastic packaging: the co-evolution of materials and society. Glob. Environ. Change 65, 102166. doi: 10.1016/j.gloenvcha.2020.102166
Flaws, J., Damdimopoulou, P., Patisaul, H. B., Gore, A., Raetzman, L., and Vandenberg, L. N. (2020). Plastics, EDCs and Health: A Guide for Public Interest Organizations and Policy-Makers on Endocrine Disrupting Chemicals and Plastic. Endocrine Society and International Pollutants Elimination Network.
Forrest, A., Giacovazzi, L., Dunlop, S., Reisser, J., Tickler, D., Jamieson, A., et al. (2019). Eliminating plastic pollution: how a voluntary contribution from industry will drive the circular plastics economy. Front. Mar. Sci. 6, 627. doi: 10.3389/fmars.2019.00627
Gerassimidou, S., Lovat, E., Ebner, N., You, W., Giakoumis, T., Martin, O. V., et al. (2022). Unpacking the complexity of the UK plastic packaging value chain: a stakeholder perspective. Sustain. Prod. Consum. 30, 657–673. doi: 10.1016/j.spc.2021.11.005
Geyer, R., Jambeck, J. R., and Law, K. L. (2017). Production, use, and fate of all plastics ever made. Sci. Adv. 3, e1700782. doi: 10.1126/sciadv.1700782
Hahladakis, J. N., and Iacovidou, E. (2018). Closing the loop on plastic packaging materials: what is quality and how does it affect their circularity? Sci. Total Environ. 630, 1394–1400. doi: 10.1016/j.scitotenv.2018.02.330
Hedwall, M. (2020). The Ongoing Impact of COVID-19 on Global Supply Chains. International Commerce and Trade, Baker McKenzie: World Economic Forum
Hudson, B., Hunter, D., and Peckham, S. (2019). Policy failure and the policy-implementation gap: can policy support programs help? Policy Design Pract. 2, 1–14. doi: 10.1080/25741292.2018.1540378
Jambeck, J. R., Geyer, R., Wilcox, C., Siegler, T. R., Perryman, M., Andrady, A., et al. (2015). Plastic waste inputs from land into the ocean. Science 347, 768–771. doi: 10.1126/science.1260352
Järvenpää, J., Perkkiö, M., Laitinen, R., and Lahtela-Kakkonen, M. (2022). PE and PET oligomers' interplay with membrane bilayers. Sci. Rep. 12, 2234. doi: 10.1038/s41598-022-06217-4
Kelly, A., Lannuzel, D., Rodemann, T., Meiners, K. M., and Auman, H. J. (2020). Microplastic contamination in east Antarctic sea ice. Mar. Pollut. Bull. 154, 111130. doi: 10.1016/j.marpolbul.2020.111130
Kummerer, K., Clark, J. H., and Zuin, V. G. (2020). Rethinking chemistry for a circular economy. Science 367, 369–370. doi: 10.1126/science.aba4979
Landon-Lane, M. (2018). Corporate social responsibility in marine plastic debris governance. Mar. Pollut. Bull. 127, 310–319. doi: 10.1016/j.marpolbul.2017.11.054
Mæland, C. E., and Staupe-Delgado, R. (2020). Can the global problem of marine litter be considered a crisis? Risk, Hazards and Crisis in Public Policy 11, 87–104. doi: 10.1002/rhc3.12180
Magableh, G. M. (2021). Supply chains and the COVID-19 pandemic: a comprehensive framework. Eur. Manage. Rev. 18, 363–382. doi: 10.1111/emre.12449
Maor, M. (2020). Policy overreaction styles during manufactured crises. Policy Polit. 48, 523–539. doi: 10.1332/030557320X15894563823146
Mcconnell, A. (2018). Rethinking wicked problems as political problems and policy problems. Policy Polit. 46, 165–180. doi: 10.1332/030557317X15072085902640
Mihai, F.-C., Gündogdu, S., Markley, L. A., Olivelli, A., Khan, F. R., Gwinnett, C., et al. (2022). Plastic pollution, waste management issues, and circular economy opportunities in rural communities. Sustainability 14, 20. doi: 10.3390/su14010020
Murray, A., Skene, K., and Haynes, K. (2017). The circular economy: an interdisciplinary exploration of the concept and application in a global context. J. Bus. Ethics 140, 369–380. doi: 10.1007/s10551-015-2693-2
Parashar, N., and Hait, S. (2021). Plastics in the time of COVID-19 pandemic: protector or polluter? Sci. Total Environ. 759, 144274. doi: 10.1016/j.scitotenv.2020.144274
Prata, J. C., Silva, A. L. P., Walker, T. R., Duarte, A. C., and Rocha-Santos, T. (2020). COVID-19 pandemic repercussions on the use and management of plastics. Environ. Sci. Technol. 54, 7760–7765. doi: 10.1021/acs.est.0c02178
Pujawan, I. N., and Bah, A. U. (2022). Supply chains under COVID-19 disruptions: literature review and research agenda. Supply Chain Forum: An Int. J. 23, 81–95. doi: 10.1080/16258312.2021.1932568
Raubenheimer, K., and Mcilgorm, A. (2018). Can the Basel and Stockholm Conventions provide a global framework to reduce the impact of marine plastic litter? Marine Policy 96, 285–290. doi: 10.1016/j.marpol.2018.01.013
Richardson, K., Hardesty, B. D., and Wilcox, C. (2019). Estimates of fishing gear loss rates at a global scale: a literature review and meta-analysis. Fish and Fisheries 20, 1218–1231. doi: 10.1111/faf.12407
Rittel, H., and Webber, M. (1973). Dilemmas in a general theory of planning. Policy Sci. 26, 155–169. doi: 10.1007/BF01405730
Schofield, J., Praet, E., Townsend, K. A., and Vince, J. (2021). COVID waste' and social media as method: an archaeology of personal protective equipment and its contribution to policy. Antiquity 95, 435–449. doi: 10.15184/aqy.2021.18
Silva, A. L. P., Prata, J. C., Walker, T. R., Campos, D., Duarte, A. C., Soares, A. M., et al. (2020). Rethinking and optimising plastic waste management under COVID-19 pandemic: policy solutions based on redesign and reduction of single-use plastics and personal protective equipment. Sci. Total Environ. 742, 140565. doi: 10.1016/j.scitotenv.2020.140565
Stoll, T., Stoett, P., Vince, J., and Hardesty, B. D. (2020). Handbook of Microplastics in the Environment, eds M.C. T Rocha-Santos and C. Mouneyrac (Switzerland: Springer, Cham), 1–23. doi: 10.1007/978-3-030-10618-8_26-1
Teixeira-Costa, B. E., and Andrade, C. T. (2022). Natural polymers used in edible food packagingandmdash;history, function and application trends as a sustainable alternative to synthetic plastic. Polysaccharides 3, 32–58. doi: 10.3390/polysaccharides3010002
Thiounn, T., and Smith, R. C. (2020). Advances and approaches for chemical recycling of plastic waste. J. Polymer Sci. 58, 1347–1364. doi: 10.1002/pol.20190261
Thorpe, J., and Carmody, L. (2021). Building a More Circular Australia: The Opportunity of Transitioning to a Circular Economy. Sydney, Australia: PricewaterhouseCoopers Australia.
UNEP (2011). The Honolulu Strategy: A Global Framework for Prevention and Management of Marine Debris. Available online at: https://marinedebris.noaa.gov/sites/default/files/publications-files/Honolulu_Strategy.pdf
United Nations Environment Programme Consumers International (2020). “Can I Recycle this?” A Global Mapping and Assessment of Standards, Labels and Claims on Plastic Packaging, 75. Available online at: https://www.consumersinternational.org/media/352255/canirecyclethis-finalreport.pdf
Vince, J., and Hardesty, B. D. (2018). Governance solutions to the tragedy of the commons that marine plastics have become. Front. Mar. Sci. 5, 214. doi: 10.3389/fmars.2018.00214
Vince, J., and Hardesty, B. D. (in press). A False Sense of Timeliness to Address a Creeping Crisis When an Urgent Crisis Arises: The Reprioritisation of Plastic Pollution Issues During COVID-19 Policy Politics.
Vince, J., and Stoett, P. (2018). From problem to crisis to interdisciplinary solutions: plastic marine debris. Marine Policy 96, 200–203. doi: 10.1016/j.marpol.2018.05.006
Willis, K., Hardesty, B. D., Vince, J., and Wilcox, C. (2022). Local waste management successfully reduces coastal plastic pollution. One Earth. 5, 1–11. doi: 10.1016/j.oneear.2022.05.008
Yuan, X., Wang, X., Sarkar, B., and Ok, Y. S. (2021). The COVID-19 pandemic necessitates a shift to a plastic circular economy. Nat. Rev. Earth Environ. 2, 659–660. doi: 10.1038/s43017-021-00223-2
Keywords: Australia, circular economy, place-based solutions, plastic, plastic supply chain, reverse logistics
Citation: Hardesty BD, Willis K and Vince J (2022) An imperative to focus the plastic pollution problem on place-based solutions. Front. Sustain. 3:963432. doi: 10.3389/frsus.2022.963432
Received: 07 June 2022; Accepted: 05 September 2022;
Published: 14 October 2022.
Edited by:
Atiq Zaman, Curtin University, AustraliaReviewed by:
Spyridoula Gerassimidou, University of Leeds, United KingdomCopyright © 2022 Hardesty, Willis and Vince. This is an open-access article distributed under the terms of the Creative Commons Attribution License (CC BY). The use, distribution or reproduction in other forums is permitted, provided the original author(s) and the copyright owner(s) are credited and that the original publication in this journal is cited, in accordance with accepted academic practice. No use, distribution or reproduction is permitted which does not comply with these terms.
*Correspondence: Britta Denise Hardesty, denise.hardesty@csiro.au