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The central role of critical minerals in the energy transition is well understood. Critical minerals such as copper, manganese, graphite and lithium are vital components of many technologies which drive the energy transition, such as wind turbines, solar panels and batteries for energy storage and electric vehicles. The transition cannot happen without them.
In addition to supply constraints and geopolitical considerations, it is also clear that unlike in previous periods of industrial and technological transition, today's energy transition is moving away from a linear economy to a circular economy in which, rather than harvesting, using and disposing of key critical minerals, the products and processes are or will need to be designed taking into account sustainable production, sustainable and prolonged use, and end of life recycling.
To meet the goals of the energy transition, together with the increasing focus on geopolitical factors, supply chain security and provenance, recycling will increasingly become an important source of the raw materials needed to support the technologies of the transition. While the technologies for recycling are still developing, the end goals for recycled content and carbon footprint are becoming clearer through regulatory developments in the EU and elsewhere.
In this briefing we look at some of the key considerations and elements of critical mineral recycling projects.
The International Energy Agency (IEA) has estimated that there will be an overall quadrupling of the minerals required for clean technologies from 2022 to 2040 to meet the goal of climate stabilisation at well below 2 degrees globally; net zero by 2050 would require six times the 2022 requirement for minerals. It anticipates that even in the less ambitious former scenario, demand for lithium grows by 40 times, and graphite, cobalt and nickel by 20-25 times.
Batteries and other clean energy technologies have a finite lifecycle. As the first generation of lithium-ion batteries are coming to the end of their life, there is the obvious question of what to do with them and a recognition of the valuable metals inside them which could be re-used and developed into new products.
While early batteries were designed and produced under a traditional linear economy, which follows a ‘take-make-dispose’ model, focus is increasingly turning to a circular economy which aims to keep products, materials, and resources in perpetual use by recycling, repairing, refurbishing and reusing existing minerals and products for as long as possible.
The primary focus areas for recycling critical materials include:
Recycling efforts from mine tailings are also gaining traction as a way to recover critical minerals and reduce environmental impact in addition to providing the economic benefits by selling the recovered materials. Phoenix Tailings, based in Boston, Nibeenabe, based in Peru and Metso, headquartered in Finland are actively working on tailings recycling to recover valuable metals.
Several jurisdictions have recognised the importance of a circular economy for critical minerals. Many efforts have focused initially on EV batteries: if the sales of petrol and diesel cars in the UK and EU are phased out from 2030 and 2035 respectively as planned, then there will be both an increased need for critical minerals for manufacture of new batteries, and a significant number of batteries reaching the end of their (approximately 8-10 year) working life from 2030 onwards.
The EU Batteries Regulation came into force in August 2023 and sets out a regulatory framework which is intended to make batteries sustainable throughout their life, from sourcing of materials to battery collection, recycling and repurposing, with the overarching purpose of promoting the development of a competitive sustainable battery industry to support the energy transition.
It imposes comprehensive requirements in relation to all batteries, and affects all stages of the battery lifecycle from the design to redevelopment of waste batteries for a "second life", which includes reuse, repurposing and remanufacturing.
The framework set out in the EU Batteries Regulation broadly covers the following areas:
For more detail on the EU Batteries Regulation, please see our briefing here.
The UK Government published a UK Battery Strategy in November 2023, which recognises the importance of the development of a circular economy for batteries. While EV batteries have been used in stationary energy storage, a growing sector in the UK (see our briefing here), the Battery Strategy acknowledges the importance of recycling given the growing demand for EVs, the objectives of the UK Critical Mineral Strategy and the minimum requirements for the use of recycled mineral content for batteries sold in the EU from 2031, which are set out in the EU Batteries Regulation and described above. It will be interesting to see how the new UK Government progresses these aims.
It is helpful that a significant focus of the regulatory framework is on the outcome of the recycling process, without specifying exactly what recycling processes or technologies are used, which leaves scope for recycling technologies to develop. However, the focus on the carbon footprint of batteries, together with the growing number of other regulatory and disclosure requirements, is likely to influence the direction of travel of the recycling technology which is being developed and influence innovation.
Whilst some recycling techniques are well-established, such as those for lead-acid batteries, many critical mineral recycling methods are still in development. Batteries are designed and manufactured in a variety of ways to suit their different requirements. For example:
Recycling processes for batteries is advancing but not yet fully optimised as it is not a straightforward process: batteries are not manufactured in a standardised way, so variations in their design and composition, and in the quality of the product which is left at the end of their useable life, makes recycling processes more complex. The intellectual property (IP) rights connected with battery designs also cause difficulties in understanding and standardising the recycling processes for batteries generally.
Figure 1.
The recycling process has created a new tradable commodity: black mass is the black-coloured (black due to the high graphite content in the anodes) powder produced from the mechanical shredding and separation (the pre-treatment) of lithium-ion batteries and can be sold (often through a marketing agent or intermediary) to independent processors to further refine and process.
The price of black mass is typically based on the prevailing battery-grade mineral spot prices - in August 2023, Platts, part of S&P Global Commodity Insights, launched four daily spot black mass price assessments based on minimum content parameters of lithium, cobalt and nickel and a combined price for all three with stipulated minimum content. Black mass therefore closely follows the battery-grade mineral prices. Pricing varies significantly, especially in the Western markets, depending on the processes used at the pre-treatment stage. For example, if heat treatments have been used, lithium will be very hard to be extracted at the extraction phase (or may already have been melted out to the slag waste), so lithium content is often less likely to be fully priced in.
Several key players dominate the black mass recycling market. Notable companies include Umicore, BASF SE, and Tenova S.p.A. These companies are heavily involved in the processing and recovery of essential metals from discharged lithium-ion batteries. Additionally, the market is expected to see new competitors entering, which will drive further growth and innovation.
Given the cutting-edge technologies involved, intellectual property (IP) is likely to play a key role through the lifecycle of a company in the critical mineral recycling sector:
The bottom line is that IP is of fundamental importance in securing a company's access to, and ability to commercialise, key technology thereby maintaining a competitive advantage. It should therefore be considered proactively, particularly in a rapidly developing field like critical mineral recycling.
Critical mineral recycling project and technology companies are comparatively new players in the financing markets, therefore there are relatively few examples of funding structures to identify as commonplace. The use of nascent technologies will be a key consideration for lenders and investors more widely as there is an unknown and unproven risk to grapple with.
In seeking the most appropriate funding structures for recycling projects reference can be made to other relatively new technology projects where we have seen funding at the corporate level or structures based more closely on project financing or prepayment principles. Some form of blended finance could be used initially, to increase lenders' confidence in funding these projects. Funding sources are likely to include:
The regulatory landscape will be of great interest to investors, in terms of subsidies and other incentives as well as potential for certain design standardisations to facilitate efficient recycling. This area is developing rapidly, as can be seen above, across a number of jurisdictions, and inter-operability of those regulatory regimes will be key.
The recycling of critical minerals has already been recognised as an important part of the energy transition in the drive to net zero and to energy security. Recycling projects will require financing support to establish themselves, and while many of these projects may need to rely on developing technologies, Government and supra-national policies and a relentless focus on the energy transition should assist. If you would like to discuss any issues raised in this briefing in more detail, please do get in touch.
The contents of this publication are for reference purposes only and may not be current as at the date of accessing this publication. They do not constitute legal advice and should not be relied upon as such. Specific legal advice about your specific circumstances should always be sought separately before taking any action based on this publication.
© Herbert Smith Freehills 2024
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