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Green Economy Journal Issue 63

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CIRCULARITY<br />

CIRCULARITY<br />

Figure 3. Plastics recycling two potential closed-loop models.<br />

The process of “denormalising”<br />

plastic waste will take time and<br />

coordinated effort, but it has begun.<br />

The small-loop scenario would involve many separate<br />

plastic-specific circular value chains, such as one for polyester,<br />

one or many for polyolefins (polyethylene and polypropylene) and<br />

one for polyvinylchloride. This would require collecting plastic waste<br />

and then separating it into district streams based on the material<br />

type for further processing to enable its reuse in the value chain at<br />

near-similar value to its virgin equivalent and at a similar point, for<br />

example as a polymer product.<br />

The large-loop scenario would also involve collecting waste, but<br />

it would involve non-material-specific circular value chains that can<br />

handle multiple types of plastics. This large-loop scenario would<br />

rely to a much greater degree on chemical instead of mechanical<br />

recycling and would return material into the value chain further<br />

upstream as feedstock or monomer.<br />

Both scenarios have distinct characteristics and requirements<br />

(Figure 3). Material companies will need to consider both scenarios<br />

when assessing the opportunities and risks of circular solutions for<br />

their product value chains.<br />

What forces will shape and drive the change?<br />

Aluminium recycling is a useful example of a circular ecosystem for<br />

materials that are highly engineered and processed. To understand<br />

how this process evolved, consider the four forces that have transformed<br />

the materials sector. In his book More from Less, research scientist<br />

Andrew McAfee chronicles how these forces have influenced the<br />

production and consumption of many material value chains in the<br />

US and the UK and led to widespread dematerialisation. Although<br />

plastics recycling hasn’t directly contributed to dematerialisation,<br />

these same four forces are likely to define the shape and rate of<br />

development of a circular chain:<br />

Economic value. In the case of aluminium, the recycled material<br />

was sufficiently valued (relative to virgin feedstock) to attract<br />

funding for the required infrastructure and technology. Capital<br />

markets and companies will continue to be the most effective,<br />

efficient and reliable sources of funding for driving the change.<br />

However, plastics require a significant investment for both<br />

mechanical and chemical recycling as well as the associated logistics<br />

infrastructure for collection and sorting. In addition, plastics require<br />

a substantial amount of coordination of incentives along the value<br />

chain from consumers to collectors to sorters to enable the recycled<br />

product to continue to flow.<br />

Technological progress. Infrared and magnetic technologies to<br />

remove plastic and steel were important capabilities for aluminium<br />

recycling, and the widespread availability of these technologies<br />

certainly accelerated adoption of the process. For plastics, the<br />

advancement of mechanical technology (such as sorting, separation,<br />

cleaning and impurity extraction) and chemical technology (such<br />

as depolymerisation, including enzymatic, cracking and pyrolysis)<br />

will govern the rate and the extent of change.<br />

Public awareness and behaviours. A vital part of consumers<br />

choosing to recycle aluminium was their awareness of its recyclability<br />

and their willingness to separate cans from the rest of their trash.<br />

As a result, 60% to 90% of aluminium cans, depending on the<br />

country, are recovered and recycled. 4 Inspired by the images of<br />

waste, many consumers are now calling for less plastic waste,<br />

but the public must broadly change their behaviours and overcome<br />

their love of disposability. The process of “denormalising” plastic<br />

waste will take time and coordinated effort, but it has begun.<br />

Responsive government. To encourage aluminium recycling,<br />

many regional governments in the US and Europe created a beverage<br />

can deposit, which consumers pay at the point of purchase and<br />

then redeem when they return the can to a designated facility. For<br />

plastics, governments have pushed recycling labelling standards to<br />

REFERENCES<br />

1 Nexant and Grand View Research<br />

Article courtesy of Kearney Consulting. Authors: Andy Walberer, Kish Khemani, partners. Figures 1, 2 and 3 supplied by Kearney Analysis.<br />

distinguish different types of plastics to facilitate separation and<br />

sorting, and some municipal governments have banned single-use<br />

plastic bags. Although these initial responses are helpful, standards<br />

and additional investments are needed, including for recycled<br />

content levels and recycling infrastructure.<br />

What should chemical and consumer companies do?<br />

Public pressure to limit plastic waste is accelerating, creating significant<br />

brand risk for consumer companies and reputational and revenue risk<br />

for chemical companies from demand destruction in high-volume<br />

applications. Individually, companies have already started to respond<br />

with specific initiatives focused on innovation in the chemical recycling<br />

space and efforts to make plastics more recyclable without increasing<br />

the burden on consumers. Collectively, companies have started to<br />

form collaborative alliances and efforts, both industry-wide and with<br />

other players in the value chain to improve collection, sorting, and<br />

recyclate production rates.<br />

Companies that want to take a fresh look can begin by identifying<br />

the opportunities and risks that are emerging in their product value<br />

chains and then considering the scenarios and forces described above<br />

to develop a strategy for how to respond. We suggest action in the<br />

following three areas:<br />

- Understand the risks, exposure and opportunities in their product<br />

value chains and calculate the potential economic impact, both<br />

the upside and the downside, including the reputational impact.<br />

- Monitor the four forces that drive change in the materials sector<br />

and use scenario planning to prepare for either the small-loop<br />

or the large-loop future.<br />

- Collaborate with industry peers, value-chain partners, regulatorysetting<br />

bodies and nongovernmental organisations to ensure<br />

that solutions are scalable and economical, standards can be<br />

established, and public outreach and education are addressed.<br />

Exactly which models will win is uncertain, but what is certain is that<br />

now is the time to proactively prepare and respond.<br />

2 Working Party on Resource Productivity and Waste, Organisation for Economic Co-operation and Development Environment Policy Committee, 26 November 2018<br />

3 Recycling International; Resource Recycling, Inc.<br />

4 International Aluminium Institute via international-aluminium.org<br />

44 45

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