Introduction about ABS Resins Recycling Market:
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The ABS Resins Recycling Market analysis report offers a wealth of insights to companies, investors, and other stakeholders. It forecasts market trends, opportunities, Applications (Automotive, Electronics and Electrical Appliances, Packaging, Consumer Goods, Construction, Medical Equipment, Others), and Types (Post-Consumer Recycled ABS, Post-Industrial Recycled ABS), as well as the challenges that might shape the industry's direction in the years ahead. Actionable insights and recommendations are furnished to guide market participants in maintaining a competitive advantage. Ask for a Sample Report
ABS Resins Recycling Market Attributes:
ABS Resins Recycling Market Valuation in 2022: The global was valued at USD 1162.6 million in 2022. This indicates the initial market size at the beginning of the specified period.
ABS Resins Recycling Market Projected Market Size in 2028: The market is expected to grow substantially, reaching a value of USD 1892 million by the year 2028. This demonstrates a significant increase in market value over the course of six years.
Compound Annual Growth Rate (CAGR): The estimated Compound Annual Growth Rate (CAGR) for the ABS Resins Recycling market during the period from 2022 to 2028 is 7.2%. CAGR reflects the average annual growth rate over the specified timeframe.
Who are the leading manufacturers in the global ABS Resins Recycling Market?
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Recycled ABS resins are made from recycled ABS plastic waste through a process of sorting, cleaning, melt extrusion, and compounding. The waste ABS plastic can come from various sources such as post-industrial waste, post-consumer waste from electronic products, and end-of-life products.
The report includes an overview of the development of the ABS Resins Recycling industry chain, the market status of Automotive (Post-Consumer Recycled ABS, Post-Industrial Recycled ABS), Electronics and Electrical Appliances (Post-Consumer Recycled ABS, Post-Industrial Recycled ABS), and key enterprises in developed and developing market, and analysed the cutting-edge technology, patent, hot applications and market trends of ABS Resins Recycling.
Regionally, the report analyzes the ABS Resins Recycling markets in key regions. North America and Europe are experiencing steady growth, driven by government initiatives and increasing consumer awareness. Asia-Pacific, particularly China, leads the global ABS Resins Recycling market, with robust domestic demand, supportive policies, and a strong manufacturing base.
The ABS Resins Recycling Market report combines extensive quantitative analysis and exhaustive qualitative analysis, ranges from a macro overview of the total market size, industry chain, and market dynamics to micro details of segment markets by type, application and region, and, as a result, provides a holistic view of, as well as a deep insight into the ABS Resins Recycling market covering all its essential aspects.
For the competitive landscape, the report also introduces players in the industry from the perspective of the market share, concentration ratio, etc., and describes the leading companies in detail, with which the readers can get a better idea of their competitors and acquire an in-depth understanding of the competitive situation. Further, mergers & acquisitions, emerging market trends, the impact of COVID-19, and regional conflicts will all be considered.
The reports will be useful in answering the following questions:
Global ABS Resins Recycling Market: Drivers and Restrains
The research report has incorporated the analysis of different factors that augment the market’s growth. It constitutes trends, restraints, and drivers that transform the market in either a positive or negative manner. This section also provides the scope of different segments and applications that can potentially influence the market in the future. The detailed information is based on current trends and historic milestones. This section also provides an analysis of the volume of production about the global market and about each type from 2018 to 2030. This section mentions the volume of production by region from 2018 to 2030. Pricing analysis is included in the report according to each type from the year 2018 to 2031, manufacturer from 2018 to 2022, region from 2018 to 2022, and global price from 2018 to 2031.
A thorough evaluation of the restrains included in the report portrays the contrast to drivers and gives room for strategic planning. Factors that overshadow the market growth are pivotal as they can be understood to devise different bends for getting hold of the lucrative opportunities that are present in the ever-growing market. Additionally, insights into market expert’s opinions have been taken to understand the market better.
Global ABS Resins Recycling Market: Segment Analysis
The research report includes specific segments by region (country), by manufacturers, by Type and by Application. Each type provides information about the production during the forecast period of 2018 to 2031. by Application segment also provides consumption during the forecast period of 2018 to 2028. Understanding the segments helps in identifying the importance of different factors that aid the market growth.
Based on TYPE, the ABS Resins Recycling market from 2023 to 2030 is primarily split into:
Based on applications, the ABS Resins Recycling market from 2023 to 2030 covers:
Highlights of The ABS Resins Recycling Market Report:
Key offerings from the Global ABS Resins Recycling Market Report:
Market Size Estimates: ABS Resins Recycling market size estimation in terms of value and sales volume from 2018-2031
Market Trends and Dynamics: ABS Resins Recycling market drivers, opportunities, challenges, and risks
Macro-economy and Regional Conflict: Influence of global inflation and Russia & Ukraine War on the ABS Resins Recycling market
Segment Market Analysis: ABS Resins Recycling market value and sales volume by type and by application from 2018-2031
Regional Market Analysis: ABS Resins Recycling market situations and prospects in North America, Asia Pacific, Europe, Latin America, Middle East, Africa
Country-level Studies on the ABS Resins Recycling Market: Revenue and sales volume of major countries in each region
ABS Resins Recycling Market Competitive Landscape and Major Players: Analysis of 10-15 leading market players, sales, price, revenue, gross, gross margin, product profile and application, etc.
Trade Flow: Import and export volume of the ABS Resins Recycling market in major regions.
ABS Resins Recycling Industry Value Chain: ABS Resins Recycling market raw materials & suppliers, manufacturing process, distributors, downstream customers
ABS Resins Recycling Industry News, Policies & Regulations
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Regional Insights:
Geographically, the detailed analysis of consumption, revenue, market share and growth rate, historical data and forecast (2018-2030) of the following regions are covered in this report:
United States
Europe
China
Japan
India
Southeast Asia
Latin America
Middle East and Africa
ABS Resins Recycling Market Report Outline:
Chapter 1 begins with the ABS Resins Recycling market scope and definition, product segment introduction, global overall market size, as well as market dynamics scenarios such as opportunities, challenges, and industry development trends under inflation. It offers a high-level view of the current state of the ABS Resins Recycling market and its likely evolution in the short to mid-term and long term.
Chapter 2 provides ABS Resins Recycling industry chain analysis, covering raw materials analysis, cost structure, price estimate, and forecast, along with price-impacting factors, downstream channels, and major customers. It aims to help readers to grab insights into product upstream, midstream, and downstream fields.
Chapter 3 depicts ABS Resins Recycling industry competitive analysis regarding market concentration rate, saturation rate, feasibility analysis from new entrants, as well as substitute's status and trends. It indicates the developing space and prospects of the current industry.
Chapter 4 analyzes extensive company profiles, comprising company basic info, product or service profiles, and sales, price, value, gross, and gross margin 2018-2023. It incorporates the ABS Resins Recycling market ranking, benchmarks, and company business portfolio.
Chapter 5 presents trade statistics of import and export volume from 2018-2023, demonstrating domestic and international market comparisons in specific countries.
Chapters 6-10 highlight ABS Resins Recycling market status at the regional and country levels, including 5 major regions of North America, Europe, Asia Pacific, the Middle East and Africa, and Latin America. The region and country list in the sample is only for reference, and it can be adjusted as required.
Chapter 11 involves geographical market figures of sales, value, market share, and growth rate. Economic, social, environmental, technological, and political factors have been taken into consideration while assessing the growth of each specific region.
Chapters 12-13 evaluate the ABS Resins Recycling market based on different types and applications. It focuses on sales and value of 2018-2023 from both vertical and horizontal perspectives.
Chapters 14-15 elaborate on the ABS Resins Recycling market forecast data from 2023-2031, segmented by types and applications, regions, and major countries, helping readers to know future aspects and growth trends.
Chapter 16 ends with an elaboration of data sources and research methodology. All possible parameters that affect the markets covered in this research study have been accounted for, viewed in extensive detail, verified through primary research, and analyzed to get the final quantitative and qualitative data.
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Some Major Points from the Table of Contents:
1 ABS Resins Recycling Market Overview
1.1 Product Overview and Scope of ABS Resins Recycling
1.2 ABS Resins Recycling Segment by Type
1.3 ABS Resins Recycling Segment by Application
1.4 Global Market Growth Prospects
1.5 Global Market Size by Region
2 Market Competition by Manufacturers
2.1 Global ABS Resins Recycling Production Capacity Market Share by Manufacturers (2018-2022)
2.2 Global ABS Resins Recycling Revenue Market Share by Manufacturers (2018-2022)
2.3 ABS Resins Recycling Market Share by Company Type (Tier 1, Tier 2 and Tier 3)
2.4 Global ABS Resins Recycling Average Price by Manufacturers (2018-2022)
2.5 Manufacturers ABS Resins Recycling Production Sites, Area Served, Product Types
2.6 ABS Resins Recycling Market Competitive Situation and Trends
3 Production Capacity by Region
3.1 Global Production Capacity of ABS Resins Recycling Market Share by Region (2018-2022)
3.2 Global ABS Resins Recycling Revenue Market Share by Region (2018-2022)
3.3 Global ABS Resins Recycling Production Capacity, Revenue, Price and Gross Margin (2018-2022)
3.4 North America ABS Resins Recycling Production
3.5 Europe ABS Resins Recycling Production
3.6 China ABS Resins Recycling Production
3.7 Japan ABS Resins Recycling Production
4 Global ABS Resins Recycling Consumption by Region
4.1 Global ABS Resins Recycling Consumption by Region
4.2 North America
4.3 Europe
5 Segment by Type
5.1 Global ABS Resins Recycling Production Market Share by Type (2018-2022)
5.2 Global ABS Resins Recycling Revenue Market Share by Type (2018-2022)
5.3 Global ABS Resins Recycling Price by Type (2018-2022)
6 Segment by Application
6.1 Global ABS Resins Recycling Production Market Share by Application (2018-2022)
6.2 Global ABS Resins Recycling Revenue Market Share by Application (2018-2022)
6.3 Global ABS Resins Recycling Price by Application (2018-2022)
7 Key Companies Profiled
8 ABS Resins Recycling Manufacturing Cost Analysis
8.1 ABS Resins Recycling Key Raw Materials Analysis
8.2 Proportion of Manufacturing Cost Structure
8.3 Manufacturing Process Analysis of ABS Resins Recycling
8.4 ABS Resins Recycling Industrial Chain Analysis
9 Marketing Channel, Distributors and Customers
9.1 Marketing Channel
9.2 ABS Resins Recycling Distributors List
9.3 ABS Resins Recycling Customers
10 Market Dynamics
10.1 ABS Resins Recycling Industry Trends
10.2 ABS Resins Recycling Market Drivers
10.3 ABS Resins Recycling Market Challenges
10.4 ABS Resins Recycling Market Restraints
11 Production and Supply Forecast
11.1 Global Forecasted Production of ABS Resins Recycling by Region (2023-2031)
11.2 North America ABS Resins Recycling Production, Revenue Forecast (2023-2031)
11.3 Europe ABS Resins Recycling Production, Revenue Forecast (2023-2031)
11.4 China ABS Resins Recycling Production, Revenue Forecast (2023-2031)
11.5 Japan ABS Resins Recycling Production, Revenue Forecast (2023-2031)
12 Consumption and Demand Forecast
12.1 Global Forecasted Demand Analysis of ABS Resins Recycling
12.2 North America Forecasted Consumption of ABS Resins Recycling by Country
12.3 Europe Market Forecasted Consumption of ABS Resins Recycling by Country
12.4 Asia Pacific Market Forecasted Consumption of ABS Resins Recycling by Region
12.5 Latin America Forecasted Consumption of ABS Resins Recycling by Country
13 Forecast by Type and by Application (2023-2031)
13.1 Global Production, Revenue and Price Forecast by Type (2023-2031)
13.2 Global Forecasted Consumption of ABS Resins Recycling by Application (2023-2031)
14 Research Finding and Conclusion
15 Methodology and Data Source
15.1 Methodology/Research Approach
15.2 Data Source
15.3 Author List
15.4 Disclaimer
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Key Questions Answered 1. How big is the global ABS Resins Recycling market? 2. What is the demand of the global ABS Resins Recycling market? 3. What is the year over year growth of the global ABS Resins Recycling market? 4. What is the total value of the global ABS Resins Recycling market? 5. Who are the major players in the global ABS Resins Recycling market?
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In our full entry on Plastic Pollution we provide an in-depth overview of global plastic production, distribution, management, and impacts through data visualisations and explainers. There you should find most of the data and context needed to understand the problem of global plastics.
Here I answer some common questions on plastic pollution:
In 1950 the world produced only 2 million tonnes per year. By 2019, annual production had increased nearly 230-fold, reaching 460 million tonnes. Over the period from 1950 to 2019, cumulative production reached 9.5 billion tonnes of plastic — more than one tonne of plastic for every person alive today.
In our entry we provide data visualisations and explainers on plastic waste by country, plastic waste per person, and importantly for plastic pollution (especially of the oceans), mismanaged waste by country and by region. Overall, it's generally the case that plastic waste per person is highest in high-income countries. However, richer countries tend to have effective waste management systems meaning mismanaged waste is low. Most mismanaged waste tends to arise from low-to-middle income countries where large coastal populations and rapid industrialization means waste management systems have failed to keep pace.
Estimates vary by source, but tend to converge on a range between 4 to 8 percent of global oil consumption. 6 percent of global oil consumption is taken as the mid-range estimate.1
This chart shows how global plastics emitted into the oceans breaks down by region.
Packaging is the dominant sectoral use of plastics globally accounting for 42 percent (146 million tonnes) in 2016. This was followed by construction with 19 percent (65 million tonnes). You can view plastic use across main sector categories here.
Since packaging tends to have a much lower product lifetime than other products (such as construction or textiles), it is also dominant in terms of annual waste generation. It is responsible for almost half of global plastic waste — the breakdown by sector is shown in the chart here.
We cover this question more fully in our entry on Plastics, found here.
In summary, best estimates suggest that approximately 80% of global ocean plastics come from land-based sources, and the remaining 20% from marine.2 Marine inputs here are dominated by fishing activity, including discarded nets, fishing lines, and abandoned vessels.
Whilst this is the relative contribution as an aggregate of global ocean plastics, the relative contribution of different sources will vary depending on geographical location and context. For example, our most recent estimates of the contribution of marine sources to the 'Great Pacific Garbage Patch' (GPGP) is that abandoned, lost or otherwise discarded fishing gear make up 75% of 86% of floating plastic mass (greater than 5 centimeters).3 This research suggests that most of this fishing activity originates from five countries – Japan, South Korea, China, the United States and Taiwan.
One option of handling plastic waste is sending it to landfill. Here, it's important to distinguish between the quality/effectiveness of landfills.
The modern definition of a landfill is of a disposal site for materials through burial. This is typically the case in high-income countries today where landfills are well-managed and effectively regulated. However, across many countries today landfill resources can be poorly-managed; in many cases dumped in open landfills, pits or dumps. Such uncontrolled disposal facilities can make plastics vulnerable to pollution of the surrounding environment and at risk of entering the ocean.
Well-managed landfill facilities have expectations to gather, compact and safely store waste. In many cases this involves covering or burying with soils or other materials. However, such landfills still have negative environmental impacts:
Greenhouse gases: when organic matter decomposes to produce methane (CH4) and carbon dioxide (CO2) — both are greenhouse gases which contribute to climate change. In some landfill sites, methane gas can be captured and 'flared' (burned) for energy production. Plastic, which is hard to break down, degrades over very long timescales (particularly under low oxygen conditions) does not contribute to this effect.
Leachate: decomposing material can produce nutrient-rich or polluted waters which — if not properly contained — can leach to the surrounding environment and potentially enter waterways and soils. Well-managed landfills are usually surrounded by protective lining to prevent water leaching to the surrounding environment. However, local pollution can occur where this is not implemented effectively, or the lining breaks down and is not replaced.
Where plastics are not handled correctly, some types of plastic — such as polyvinyl chloride; PVC — can leach chemicals such as additives and plasticiser compounds.4 A report by the European Commission aimed to provide a detailed analysis and overview of the available evidence on the behaviour of PVC in landfills.5 The study concluded that whilst leachate of substances as either non-detectable or in very low concentrations, a precautionary approach would deem this material only controllable if landfills are equipped with adequate liner and leachate treatment.
Incineration is the burning of a given material — in the case of plastic, this is done at very high temperatures. Incineration is one form of waste management. What are the environmental impacts of incineration?
Greenhouse gases: the incineration of plastic produces carbon dioxide (CO2) — a primary driver of global climate change. However, the incineration process can be integrated as a 'Waste to Energy' (WtE) solution. WtE is a form of energy recovery; in this case energy from the plastics can be stored and utilised for energy. On a net balance, does incineration therefore have a net positive or negative impact on greenhouse gas emissions?
It depends. The relative gains from energy recovery vary depending on the efficiency of the incineration process in addition to the mix of energy sources it's replacing. In countries where the energy mix is dominated by fossil fuels, incineration energy recovery can reduce emissions. However, across many countries — most across Europe — where incineration efficiency is low and the energy mix is lower-carbon, this does provide a net source of greenhouse gas emissions.6
For more information, please visit recycled ABS plastic China.
Air pollution: a common concern of incineration is that it releases toxic emissions to the surrounding environment. The burning of plastics can produce several toxic gases: incomplete combustion of Polyethylene (PE), Polypropylene (PP) and Polystyrene (PS) can release carbon monoxide (CO) and noxious emissions, while polyvinyl chloride (PVC) can produce dioxins.7,8 Such gases can be toxic and dangerous to both human and ecosystem health. Open or uncontrolled burning of plastics should therefore be strongly avoided.
Is this also the case in incinerator facilities? It largely depends on the efficiency and environmental control of emissions of the particular incinerator site. In high-income countries in particular, waste management and incinerator sites are heavily regulated with monitoring of emissions and potential leaks to the surrounding environment. Modern incinerators have largely dealt with the problem of dioxin or other toxin emissions. Technologies here include efficient combustion, end-of-pipe treatment, selective catalytic reduction, and the addition of suitable inhibitors.9 A study in Belgium, for example, reported no difference in dioxin-serum levels of maintenance workers of municipal waste incinerator facilities — individuals who would experience high exposure rates if such methods were not implemented.10
However, such incinerator technologies and standards are not implemented everywhere — in countries where environmental regulation is less strict, unsafe or open burning of municipal waste remains common. This typically occurs in low-t0-middle income countries. Studies in India, Kenya and Thailand, for example, report notable pollution from the burning of waste (including the generation of dioxins).11,12,13 For incineration to become a universally safe solution, standards and uptake of appropriate technologies and approaches must be adopted globally.
There are three key options for handling plastic waste: recycling, incineration or disposal in landfill.14 What should we choose?
What seems like a simple question can sometimes be complex. Opinions differ depending on what particular environmental, health or economic issues someone cares about. Impact of different methods can be assessed across multiple factors including greenhouse gas emissions, energy use, local pollution, and cost of processing.
In the table we show the summary results of a meta-study on the comparison between recycling (R), incineration (I) and landfill (L) of plastics.15 This summarises the conclusions of a range of location-specific studies assessing the relative global warming potential (GWP) and total energy use (TEU) of the three methods. Each is shown from lowest impact to highest impact (e.g. R-L-I means recycling has the lowest impact, followed by landfill, then incineration has the highest).
Reference
Material/application
Global warming potential (GWP)
Ranked best-mid-worst
Total energy use (TEU)
Ranked best-mid-worst
Arena et al. 2003
PE and PET liquid containers
R-L-I
R-I-L
Beigl and Salhofer 2004
Plastic packaging
R-I
-
Chilton et al. 2010
PET
R-I
-
Craighill and Powell 1996
PET, HDPE and PVC
R-L
-
Dodbiba et al. 2008
Plastics (PE, PS and PVC)
R-I
-
Eriksson and Finnveden 2009
Non-recyclable plastic
I-L
-
Eriksson et al. 2005
PE
PE, PP, PS, and PET
R-I-L
R-I-L
R-I-L
R-I-L
Finnveden et al. 2005
PVC
PE, PP, PS, PET and PVC
R=I-L
I-L-R
R-I-L
I-R-L
Foolmaun and Ramjeeawon 2013
PET
R-L-I
R-I-L
Grant et al. 2001
PET, HDPE AND PVC
R-L
R-L
Moberg et al. 2005
PET
R-I-L
R-I-L
Mølgaard 1995
Plastics
Plastics
-
-
R-I-L
I-L-R
Perigini et al. 2004
PE and PET liquid containers
R-L-I
R-I-L
Perigini et al. 2005
PE and PET liquid containers
R-L-I
R-I-L
Rajendran et al. 2013
Plastics
R-I
-
US EPA 2006
HDPE, LDPE and PET
R-L-I
R-I-L
Wenisch et al. 2004
Plastics
R=L
-
Wollny et al. 2001
Plastic packaging
R-L-I
R-I-L
M. Al-Maaded et al. 2012
Plastics, non-specified
Plastics
R-L
R-L-I
-
R-I-L
Shonfield 2008
Plastics
I-L-R
-
Recycling had the lowest global warming potential and energy use across nearly all of the studies. From an environmental perspective, recycling is usually the best option. This typically holds true, but note that there are a few caveats:
Nonetheless, recycling in general is the best of the three options.
But what about the plastic that is not recyclable — should we send it to landfill or incinerate? Here, the winner is less clear-cut. As we see across the range of studies above: it depends on context, plastic type and conditions as to whether landfill or incineration has lower impact in terms of greenhouse gas emissions or energy use.
As we describe in the sections above on landfill and incineration consequences, both have potential environmental risks if they're not managed or regulated correctly. The best choice may depend on local context. Incineration for example, can have a net positive on greenhouse gas emissions if burned efficiently and is utilised in a fossil fuel dominant energy mix. Across some countries — many across Europe — incineration efficiency is low and the energy mix is lower-carbon6, meaning landfill may be more favourable. Incineration may be favourable where fossil fuels are dominant, landfill space is limited or poorly managed, or subsurface conditions are unfavourable to landfills.
In either case it's critical that proper management and regulation is in place to minimise environmental impacts.
We cover this question more fully in our entry on Plastics, found here. In summary, it's estimated that in 2015, around 55 percent of global plastic waste was discarded, 25 percent was incinerated, and 20 percent was recycled. Of the plastic waste produced between 1950 and 2015, only 9 percent was recycled.
Unfortunately, yes. Some plastics intended for recycling end up in landfill.
There are several reasons why this can occur:
Approaches to recycling differ both between and within countries in terms of handling protocol at recycling centres, as well as guidance for disposal of waste at home. Some localities, for example, have a single mixed recycling disposal bin whilst others have separate bins for plastic, paper, and aluminium/cans. It's therefore difficult to provide universal guidance on the correct approach to separating waste. But there are some key points which apply in most cases.
Many believe that taking care of what they do or don't put into recycling at home is irrelevant — that landfill and recycling are mixed then separated later at waste management facilities. This is false. Landfill and recycling collections are not mixed. If you place recyclables in general waste bins (in localities with designated recycling bins) they will end up landfill.
It's important to be careful about what you place in recycling; non-recyclable plastics can lead to contamination of the supply. Although many facilities have automated and/or manual procedures for removing non-recyclables, they're not always 100 percent effective. If waste loads contain a significant amount of non-recyclables, facilities may deem them non-economic to sort. The same applies to food or liquid waste: unwashed plastics can contaminate the supply. These loads can be sent straight to landfill.
What about the separation of different recyclables (e.g. plastic, paper, and metal cans) — is it necessary to sort these at home? If your locality has only mixed recycling collection (called 'single-stream') then your job is easy. The exception here is glass and batteries — they should be recycled separately. The municipality will collect fully mixed loads and sort them at dedicated facilities using methods such as density separation, magnets and infrared technology. Infrared cameras can be used to determined specific plastic polymer types. You can read an overview of the recycling process by one UK locality here.
Some localities still use 'multi-stream' recycling where you have separate bins for each type of recyclable. But, with evidence that single-stream recycling increases recycling rates, many are turning away from multi-stream.19 If your locality relies on multi-stream recycling then its waste management processes are less likely to separate different types of recycling in waste streams. Ensuring your recycling goes in the correct bin is therefore important.
There are a wide range of polymers used in common plastics. Such materials have different properties and are therefore appropriate for different uses. The structure of the polymers also affect a plastic's recyclability. Some polymers fail and break down under mechanical or thermal stress; this affects their ability to be recycled.
In the table we summarise the key categories of plastics, their common uses, properties and whether they can be recycled or not. Most plastic items have a marked symbol numbered from 1 to 7 on them — this should provide some guidance on recyclability. Note that this information is based on general guidelines for household collection, however, these can vary depending on waste management infrastructure in specific locations. You should check local recycling guidelines for clarification. For example, it used to be the case that most recycling facilities were unable to handle plastic caps/tops from water or soft drink bottles. Some facilities now can, and encourage residents to recycle both together.
In general I try to remember a simple code of: 1 and 2 are recyclable; 3 and 5 sometimes recyclable; 4, 6 and 7 usually not recyclable. One good general source of information of what items are and aren't accepted is available here. You can also search for specific items, where guidance is provided on how to dispose of it properly.
You can view the relative amounts of plastic waste generation by polymer here.
It's a common misconception that most plastics can be recycled many times over. This belief can allow us to justify high rates of single-use plastics on the basis that they are recyclable and therefore do not end up as waste in landfill.
In practice, the majority of recycled plastics are only recycled once or twice before being finally disposed of in landfill or incineration. In their 2017 Science paper on the fate of global plastics, Geyer et al. (2017) write that "Recycling delays, rather than avoids, final disposal. It reduces future plastic waste generation only if it displaces primary plastic production; however, because of its counterfactual nature, this displacement is extremely difficult to establish."20 The study estimates that of the plastic recycled to date, only 10 percent has been recycled more than once. Following this, they end up in the municipal waste stream.
The limits to repeated mechanical recycling occur because of thermal breakdown/destruction in processing (which can degrade the quality of material) and the mixing or contamination of plastic polymer types means secondary plastics can be of low economic or practical value. When plastics become products of lower quality following recycling, this is often termed 'downcycling'. A 2016 report by the World Economic Forum, the Ellen MacArthur Foundation, and McKinsey & Company, estimated that around 14 percent of plastic packaging globally is collected for recycling, however the costs of sorting and reprocessing mean that only 5 percent of material value is retained for use as further materials.1
In recent years there has been promising progress in the development of polymer materials which can be chemically recycled back to their initial raw materials for the production of virgin plastic production.21 In a recent study, Zhu et al. (2018) successfully synthesised a plastic with mechanical properties similar to commercially available plastics, but with infinite recyclability through chemical recycling. Such methods are currently expensive and unfavourable in terms of energy inputs, but could provide a commercially-viable solution in the years to follow.22
Many plastics are defined as non-degradable, meaning they fail to decompose and are instead broken down into smaller and smaller particles. Materials can slowly break down through photodegradation (from UV radiation). Estimated decomposition times for plastics and other common marine debris items are shown in the chart here.
Fishing lines, for example, take an estimated 600 years to break down. Plastic bottles take an estimated 450 years.23
The production of so-called 'bioplastics' or biodegradable plastics is currently very low: estimated at around 4 million tonnes per year (which would be just over one percent of global plastics production).24,25
'Biodegradable' plastic is typically defined as plastics which break down at faster rates than standard plastics. However, this broad definition means the boundary of what constitutes biodegradable plastics is often intensely debated. Biodegradability can in some cases be claimed simply because break down is accelerated (without necessitating fast degradation).
One example of this is ‘oxo-degradable plastics’: plastics (such as polyethylene) with additives which accelerate the oxidation process (causing them to break down faster). In essence, however, all this does is break the plastics down into microplastics.
This has been the case with several so-called biodegradable plastics: they are proven to break down faster under specific environmental conditions (which may not actually reflect the normal environment), but may not be effectively degradable under natural conditions. The labels of 'biodegradable', 'bio-based', 'compostable', are therefore often claimed and used in marketing contexts, with little understanding for consumers on what these definitions mean in practice.
A key current challenge of biodegradable plastics is that they tend to need particular waste management methods which are not always widely available. They usually need to be separated from the traditional recycling stream (which can be difficult and expensive), and have to go to specific compostable facilities. This doesn’t mean such methods are unfeasible, but could be additional economic cost especially if they're in the waste stream at low concentrations, and would take significant work in terms of infrastructure redesign.
In 2015, the United Nations Environment Programme (UNEP) published a report on the misconceptions, concerns and impacts of biodegradable plastics.26 It concluded that: "the adoption of plastic products labelled as ‘biodegradable’ will not bring about a significant decrease either in the quantity of plastic entering the ocean or the risk of physical and chemical impacts on the marine environment, on the balance of current scientific evidence."
Plastics are undeniably a key environmental concern — particular in terms of impacts to ocean health and wildlife. But it's also important to acknowledge the value plastic plays across many aspects of society. It is a unique material: often lightweight, resilient, usually non-reactive, waterproof and cheap. For most of us, it has an almost constant place in our lives. Even those who try to minimise or cut plastic from their lives are likely to come into contact with it every day.
One example where plastic plays an important role is food packaging. Whilst over-packaging can undoubtedly be a significant issue, packaging of food products is essential for the prevention of food losses, wastage and contamination.27 Storage and packaging plays a crucial role from harvest all the way through to final consumption of the foods we eat. Even if some consider the final phase of packaging (from retail to home) to be unnecessary, it is likely it has played an important role in preserving food from the farm to the retail stage. It protects foods from pest and disease, significantly increases shelf life, and maintains food safety.28
Packaging is sometimes taken for granted in higher income countries. Across many low-to-middle income countries, lack of packaging is an important issue for food security. The UN Food and Agriculture Organization (FAO) emphasise that lack of packaging, storage and refrigeration leads to significant post-harvest losses.29 It notes: "large losses from farm to plate are attributed to poor handling, distribution, storage, and purchase/ consumption behavior. Huge resources that could otherwise be spent on more productive activities go into producing and transporting goods that only go to waste. Losses at almost every stage of the food chain may be reduced by using appropriate packaging."
In fact, studies have shown that when we compare environmental impacts such as greenhouse gas emissions, energy, water and resource use, plastic packaging tends to have a net positive impact. The impact of plastic production and handling is lower than the impacts which would result from food waste without packaging.30,31,32 Reducing packaging where it is used in excess is useful, however, abandoning packaging completely would have serious implications for food security, safety, and would ultimately lead to large increases in the environment impact of food.
The question is therefore: is plastic the best material to use for packaging? Which material is 'best' for the environment? As designer and sustainability innovator, Leyla Acaroglu, discusses in her TED Talk 'Paper beats plastic? How to rethink environmental folklore', there is no universal consensus on 'best' or 'worst' materials.33 Materials have different relative impacts across different environmental metrics. This ultimately leads to trade-offs. Some materials may release fewer greenhouse gas emissions but require more water or fertiliser inputs, for example.
There's no simple answer; your choice would be different depending on the environmental impacts you're most concerned about. In general, plastic tends to be cheap and has significantly lower greenhouse gas emissions, energy, water and fertilizer inputs than alternatives such as paper, aluminium, cotton or glass. The obvious environmental detriment is it's pollution of the natural environment when poorly managed. In the charts here we summarise one life-cycle analysis (LCA) study of environmental impacts by grocery bag type. This is based on results from the Danish Environmental Protection Agency.34 These figures present the number of times a grocery bag would have to be reused to have as low an environmental impact as a standard LDPE (Low-density polyethylene) single-use plastic bag. For example, a value of 5 indicates a bag would have to be reused 5 times to equal the environmental impact of a standard single-use plastic bag.
This is shown for greenhouse gas emissions only, and for combined environmental impact (including greenhouse gas emissions, ozone depletion, human toxicity (cancer effects), human toxicity (non-cancer effects), photochemical ozone formation, ionizing radiation, particulate matter, terrestrial acidification, terrestrial eutrophication, marine eutrophication, ecosystem toxicity, resource depletion (fossil), resource depletion (abiotic), and water resource depletion).
Microplastics tend to receive a lot of public and media attention. They are often discussed, or confused, as being a unique and different from conventional plastics.
By definition, microplastic is simply plastic of a very small particle size. When we discuss plastics we sometimes categorise them based on particle size; typical particle size ranges are shown in the table.35 Microplastics are plastic particles with a diameter typically less than 5 millimetres, or in some scales less than 4.75 millimetres. Even smaller particles, measuring less than 0.0001 millimetres (<0.1μm — micrometre) in diameter are often referred to as nanoplastics.
Microplastic can arise through primary or secondary processes. Primary microplastics are already of a small size in production: common sources include fibres, pellets, microbeads, and capsules. Secondary microplastics form from the breakdown of larger plastic products. For example, when meso- or macroplastic particles are exposed to the natural environment (for example in rivers, ocean waters, sunlight), physical or ultraviolet (UV) weathering can occur, which degrades them into smaller particles.
One challenge of microplastics is that their small size makes them easier to (consciously or not) ingest. Ingestion of microplastics could have detrimental impacts on wildlife health. The small size of these particles make them difficult to track and monitor; evidence on the impacts and behaviour of microplastics are therefore currently very limited.
Particle category
Diameter range
(mm = millimetres)
Nanoplastics
< 0.0001 mm (0.1μm)
Small microplastics
0.0001 – 1 mm
Large microplastics
1 – 4.75 mm
Mesoplastics
4.76 – 200 mm
Macroplastics
>200 mm
If we want to reduce or stop the amount of plastic entering the oceans, what can we do?
There are multiple levels at which we can answer this question: there are things we can do as individuals, innovators, corporations, and in policy-making and financing.
Global cooperation to upscale waste management is therefore crucial. Such solutions are not new or innovative: they have already been implemented successfully across many countries. Note that this is not a case of finger-pointing or blame: rich countries too have benefited from the rapid industrialization (a rate at which waste management could not keep up) of others. This is a global system we have collective responsibility for.
Middle- and low-income countries where plastics are poorly managed have an obvious role and responsibility. But if high-income countries are truly serious about addressing the ocean plastic issue, the most impactful way to contribute is to invest in the improvement of waste management infrastructure practices across the world. Without such investment and cooperation we will not be able to reduce the quantity of plastic entering the ocean. We are still currently on a trend of rapidly increasing plastic waste: to stabilise, let alone reduce, will require large-impact solutions.
Effective management of waste we produce is an essential and urgent demand if we are to prevent plastic entering the ocean. As noted above, this is a solution we know how to achieve: many countries have low levels of mismanaged waste. This is important, regardless of how successful we are in reducing plastic usage.
However, reducing demand for new plastic production is also crucially important. Whilst recycled plastic is usually favourable to primary plastics, it is not a long-term solution: most recycled plastics still end up in landfill or incineration after one or two cycles.20 For recycling to be sustainable over the long-term, innovations which would allow for continuous recycling would have to be developed. As noted in another question, there has been promising progress in recent years in the development of polymer materials which can be chemically recycled back to their initial raw materials.21 However, they are currently expensive and unfavourable in terms of energy inputs.22
The economic viability and environmental trade-offs will be critical components to the development of not only recyclable materials but other alternatives. Plastic is so widely used because it is cheap, versatile, and requires relatively little energy, water and land to produce. To achieve wide uptake of alternatives across countries of all income levels, breakthrough alternatives will have to be economically competitive with current methods. Functionality, price and scalability of innovations are key to addressing this challenge.
Plastic removal at large-scale is always going to be a major challenge. This becomes an even greater challenge over time, since plastics in the ocean tend to break down into smaller particles (and the smaller they are, they less easy it is to detect and then remove them at scale). Of course the easiest way to mitigate this problem is to stop plastic entering the ocean in the first place.
But still, we already have a large quantity of plastic in the ocean and this will continue (even if we can begin to reduce the amount that reaches the ocean in the years which follow).
Very small particles (microplastics, for example) are difficult to remove. Technologies being proposed currently for plastic removal therefore tend to focus on larger plastics. The fact that plastic tends to accumulate in gyres at the centre of ocean basins makes this easier: it concentrates plastics for removal.
The removal solution which has received the most attention from investors and researchers is The Ocean Cleanup. They are focusing on one major gyre of plastic: the Great Pacific Garbage Patch. Their technology in simple terms deploys buoyant tubes several kilometres in length. The project claim it can capture plastic ranging in size from tens of metres down to 1 cm.
It's too early to say whether this could be a feasible contribution. You can follow their milestone journey here. They make some bold claims, stating that full deployment of the technology could remove 50% of the plastic within 5 years. The prototype has been proven at various small-scales and in the summer of 2018 launch their first cleanup system in the Great Pacific Garbage Patch. If all goes well, their timeline suggests they aim to expand globally in 2020.
Yes, in 2017 researchers discovered that the wax worm (the larvae of the wax moth) has the ability to break down polyethylene (PE).36 PE accounts for around 40% of global plastics.
PE is largely non-degradable, but there have been a couple of previous instances where particular bacteria or fungi have been able to break it down at very, very slow rates. This latest discovery of the wax worm, however, showed faster rates of breakdown — although still slow. The researchers left 100 wax worms on a PE plastic bag for 12 hours and measured a 92 milligram breakdown of the plastic (about 3% of the plastic bag).
These rates are of course very slow, and at a tiny scale. The plan wouldn't be to scale-up the use of wax worms for plastic degradation — this would be unscalable. However, this discovery could be useful in allowing us to identify a particular enzyme which breaks down plastics. The authors suggest that wax worms break down the carbon-carbon bonds in PE either from the organism itself, or from the generation of a particular enzyme from its flora.
It could be possible to produce this enzyme or the bacteria which secrete this given enzyme at industrial scales.
Yes, there are particular strains of bacteria that are effective in breaking down plastic.
The most prominent discovery of this bacteria was made in Japan where researchers found a bacterium, Ideonella sakaiensis 201-F6, which could digest polyethylene terephthalate (PET) — the material used for single-use plastic bottles.37 This bacterium does so by producing and secreting an enzyme called PETase.
PETase (a protein which accelerates reactions) can split certain chemical bonds in PET; the bacteria can then absorb the smaller molecules it left behind (which contain carbon, and can be used by the bacteria as fuel/food).38
This breakthrough has been shown at very small laboratory scales. However, the authors and researchers in this field are open about the fact that this is not a near-term solution and would take major technological and scientific developments before it can close to the scale that would have an impact.
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Hannah Ritchie (2018) - “FAQs on plastics” Published online at OurWorldInData.org. Retrieved from: 'https://ourworldindata.org/faq-on-plastics' [Online Resource]BibTeX citation
@article{owid-faq-on-plastics,
author = {Hannah Ritchie},
title = {FAQs on plastics},
journal = {Our World in Data},
year = {2018},
note = {https://ourworldindata.org/faq-on-plastics}
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