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Chemicals · Market Analysis

Battery Recycling and Critical-Material Localization Redefine Industrial Strategy

6 min readUSD Analytics

EU packaging rules are accelerating redesign across polymers, coatings, adhesives, inks and recycled-content systems. PPWR-driven recyclability, PFAS restrictions, EPR modulation and higher PCR requirements are shifting packaging innovation toward integrated, recycling-compatible material architectures and application-engineered specialty chemistry.

Battery recycling is moving beyond waste management and becoming a core instrument of industrial policy. Governments increasingly view end-of-life batteries, production scrap and black mass as strategic sources of lithium, nickel, cobalt, graphite, copper and manganese. Automakers, cell producers, chemical companies and recyclers are consequently building regional systems that connect battery collection, diagnostics, dismantling, material recovery, refining and battery-grade material production.

The commercial opportunity is substantial, but capacity expansion alone will not create a viable recycling industry. Feedstock availability, battery chemistry, collection networks, processing yields, material qualification, electricity and reagent costs, regulatory compliance and customer offtake will determine which projects become durable industrial assets.

 

Executive Takeaway

Battery deployment expanded far faster than end-of-life battery availability during the first half of the 2020s. The International Energy Agency estimates an approximately 15-year structural lag between rapid growth in battery demand and the emergence of comparable recycling feedstock. China currently hosts more than 85% of global battery-recycling capacity, while announced worldwide capacity for 2030 could equal seven times the available feedstock if all planned projects proceed.

This is shifting strategic attention from plant construction toward feedstock security, reverse logistics and downstream material qualification. Production scrap will remain a major near-term input, but end-of-life EV and energy-storage batteries are expected to become the largest feedstock source from 2035 onward. Recycling will therefore develop in two phases: an initial scrap-led market followed by a significantly larger end-of-life battery cycle.

 

Key Metrics Shaping the Battery-Recycling Strategy

Table 1: Key Metrics Shaping the Global Battery-Recycling Strategy

Key metric

Strategic significance

~15 years

Estimated lag between rapid battery deployment and comparable end-of-life battery availability

More than 85%

Share of global recycling capacity currently hosted by China

Potential ratio of announced recycling capacity to available feedstock in 2030

80% lower

Average greenhouse-gas emissions from recycled lithium, nickel and cobalt versus primary mined materials

1.2 million to 14 million

Estimated increase in EV batteries reaching end of life between 2030 and 2040

Up to $500 million

US DOE funding opportunity announced for critical-material processing, battery manufacturing and recycling

 

End-of-Life Batteries Become a Major Industrial Feedstock

The expected end-of-life battery wave is substantial. The IEA estimates that approximately 1.2 million EV batteries could reach retirement in 2030, rising to around 14 million in 2040. This expansion will create a larger regional material reservoir, but its commercial availability will depend on collection rates, second-life deployment, vehicle exports, ownership arrangements and battery condition.

Bar chart showing estimated end-of-life EV batteries rising from about 1.2 million in 2030 to 14 million in 2040, illustrating the rapid expansion of future battery-recycling feedstock.

 

Recycling Moves from Circularity Initiative to Industrial Policy

Recycling reduces dependence on geographically concentrated mining and refining capacity by retaining materials already present in domestic vehicle, electronics and energy-storage fleets. It also provides governments with a mechanism to support local battery manufacturing without relying entirely on new mineral extraction.

The EU Critical Raw Materials Act sets 2030 benchmarks for domestic capacity equivalent to at least 10% of annual consumption from extraction, 40% from processing and 25% from recycling. It also seeks to limit dependence on any one third country to no more than 65% of annual consumption for each strategic material at a relevant processing stage.

The United States is similarly supporting domestic processing and recycling. In March 2026, the Department of Energy announced a funding opportunity of up to $500 million covering critical-material processing, recovery from manufacturing scrap and end-of-life batteries, and domestic battery-material and component manufacturing.

A resilient battery supply chain now depends on collection rights, battery data, black-mass capacity, chemical separation, recycled-material certification and long-term offtake.

The Feedstock Timing Gap Is the Central Commercial Constraint

Lithium-ion battery deployment across EVs, stationary storage and other applications increased more than sixfold between 2020 and 2025. Most of those batteries remain in service and are unlikely to become available for recycling until the mid-2030s or later.

Manufacturing scrap therefore remains critical during the industry’s early development. The IEA estimates that production scrap will still account for approximately two-thirds of available battery-recycling feedstock in 2030. End-of-life EV and storage batteries are expected to become the largest source from 2035 onward and represent more than 90% of available feedstock by 2050.

The imbalance creates several strategic risks:

  • Plants may operate below nameplate capacity before end-of-life volumes accelerate.
  • Recyclers without automaker or cell-manufacturer contracts may struggle to secure feedstock.
  • Competition for gigafactory scrap can increase acquisition costs.
  • Black mass may flow toward regions offering lower processing costs or higher recovery value.
  • Used EV exports can transfer future recycling feedstock from vehicle-selling countries to importing markets.

The IEA estimates that global announced recycling capacity in 2030 could be seven times available feedstock. By 2040, the position could reverse, with available feedstock exceeding currently announced capacity by approximately 60%.

Regulatory Pivots Transforming Battery Supply Chains

EU Batteries Regulation

The EU Batteries Regulation establishes requirements across battery design, due diligence, collection, material recovery, recycled content and digital traceability. The battery passport becomes mandatory from 18 February 2027 for covered EV, light-transport and industrial batteries. The European Commission’s Digital Product Passport Registry became operational in July 2026, giving companies a testing environment ahead of implementation.

Minimum recycled-content requirements begin in August 2031 for covered batteries:

  • 16% cobalt
  • 85% lead
  • 6% lithium
  • 6% nickel

Requirements increase again in 2036 for cobalt, lithium and nickel.

EU minimum recycled-content requirements increase after 2031

Exhibit: Minimum share of recovered material required in active battery materials for covered battery categories- 

Bar chart comparing EU minimum recycled-content requirements for batteries in 2031 and 2036: cobalt increases from 16% to 26%, lithium from 6% to 12%, nickel from 6% to 15%, while lead remains at 85%.

The EU framework also establishes material-recovery targets. By the end of 2027, recyclers must recover 90% of cobalt, copper, lead and nickel and 50% of lithium. By the end of 2031, those requirements increase to 95% for cobalt, copper, lead and nickel and 80% for lithium.

EU battery-material recovery targets tighten by 2031

Exhibit: Required material-recovery rates from waste batteries: 

EU battery-material recovery targets for 2027 and 2031, with cobalt, copper, lead, and nickel rising from 90% to 95%, and lithium increasing from 50% to 80%.

 

US Domestic Battery-Supply Policy

Table 2. US Policy Measures Supporting Domestic Battery Materials and Recycling

US policy lever

Supply-chain relevance

Section 45X advanced-manufacturing production credit

Supports qualifying battery components, electrode active materials and applicable critical minerals produced in the United States

Prohibited Foreign Entity restrictions

Introduce ownership, material-assistance and supply-chain conditions affecting credit eligibility

DOE critical-material funding

Supports processing, recycling and battery-material manufacturing facilities

RCRA and transport regulation

Governs the handling, classification and movement of discarded batteries and certain recycling intermediates

IRS guidance issued in 2026 confirms that Section 45X covers qualifying battery components and applicable critical minerals, while amended rules exclude eligible components containing specified material assistance from a prohibited foreign entity.

Black-Mass Classification and Cross-Border Movement

Black mass composition varies according to the battery chemistries entering the shredding process, the degree of preprocessing and the presence of electrolyte or other materials. The US EPA states that black mass is no longer a battery and is not universal waste; its regulatory status depends on its characteristics and management.

The EU updated battery-related waste codes in 2025, classifying several battery waste streams—including lithium-based black mass—as hazardous and strengthening controls under waste-shipment rules. The policy is intended partly to retain recoverable battery materials within the European recycling economy.

Regulatory Comparison

Table 3. European Union and United States Battery-Supply Regulatory Approaches

Dimension

European Union

United States

Primary mechanism

Binding lifecycle regulation

Tax credits, funding and environmental regulation

Digital traceability

Mandatory battery passport from February 2027

No equivalent nationwide battery-passport mandate

Recycled content

Binding minimum requirements from 2031

Primarily encouraged through manufacturing and sourcing policy

Material recovery

Defined recovery-rate targets

Varies by regulation, programme and jurisdiction

Supply localization

CRMA benchmarks and circularity rules

Section 45X, PFE restrictions and DOE funding

Black mass

Hazardous waste codes and shipment controls

RCRA classification depends on characteristics and management

Critical-Mineral Economics: Primary Supply Versus Urban Mining

Table 4. Primary Critical-Mineral Supply Versus Battery-Recycling Economics

Dimension

Primary mineral extraction and refining

Secondary supply from battery recycling

Resource basis

Geological deposits, ore grades, brines and mining infrastructure

Manufacturing scrap, end-of-life batteries and black mass

Development profile

Long permitting, infrastructure, mine development and commissioning cycles

Potentially modular development, but still dependent on permitting, feedstock and offtake

Environmental exposure

Land disturbance, water requirements, beneficiation and refining emissions

Lower average lifecycle emissions, but requires energy, chemicals and waste management

Geopolitical exposure

Concentrated mineral extraction and refining locations

Can support regional supply, although recycling technology and capacity remain concentrated

Main economic constraint

Resource quality, capital intensity, commodity prices and permitting

Feedstock availability, utilization, chemistry mix, logistics and recovered-product quality

Commercial output

Concentrates, refined metals and battery-grade compounds

Black mass, metal salts, precursors and regenerated active materials

On average, recycled lithium, nickel and cobalt generate approximately 80% fewer greenhouse-gas emissions than equivalent primary materials from mining. The IEA also estimates that stronger recycling could reduce the need for new mining activity by 25% to 40% for selected energy-transition minerals by 2050 under its Announced Pledges Scenario. Recycling nevertheless supplements rather than eliminates primary extraction because battery-material demand continues to expand.

 

Recycling-Technology Comparison

Table 5. Comparison of Pyrometallurgical, Hydrometallurgical and Direct Battery-Recycling Pathways

Technology

Principal advantages

Main limitations

Best-fit conditions

Pyrometallurgy

Tolerates mixed or contaminated feedstock; established high-temperature processing

High energy requirements; lithium and other materials may require additional recovery stages

Mixed batteries, uncertain chemistry and integrated metallurgical operations

Hydrometallurgy

Potential for high recovery and refined metal salts; lower processing temperatures

Reagent consumption, wastewater, impurity control and multistage purification

Controlled black mass and production of battery-grade intermediates

Direct recycling

Preserves more of the active material’s engineered value; may reduce remanufacturing energy

Requires chemistry identification, clean separation and extensive product requalification

Consistent, chemistry-specific feedstock and integrated battery-material ecosystems

 

 

Corporate Ecosystems and Closed-Loop Joint Ventures

Corporate Ecosystems and Closed-Loop Joint Ventures

BASF and TSR: Integrating Collection with Material Processing

BASF began commercial operation of its Schwarzheide black-mass plant in 2025. The facility can process up to 15,000 tonnes of end-of-life lithium-ion batteries and production scrap annually, equivalent to approximately 40,000 EV batteries according to BASF.

In 2026, BASF and TSR Group announced cooperation covering dismantling, discharging, black-mass production, metal-fraction recovery and battery logistics. The partnership adds collection and preprocessing capabilities to BASF’s broader European battery-material and recycling activities.

Redwood and General Motors: Managing the Full Battery Lifecycle

Redwood Materials and General Motors expanded their relationship in 2026 across production-scrap recycling, end-of-life EV battery management and second-life energy storage. Redwood reported receiving more than 28,000 tonnes of material from GM and Ultium Cells and having approximately 10,000 EV packs in its repurposing pipeline.

The companies also announced plans to deploy about 100 repurposed GM packs at a Michigan manufacturing site, providing 1.5 MW and 7.2 MWh of dispatchable energy. The arrangement demonstrates that diagnostic triage can extend battery value before final material recovery.

Glencore: Connecting Metals, Refining and Recycling

Glencore’s proposed Portovesme Critical Raw Materials Hub in Italy was selected as an EU Strategic Project in 2025. The project is intended to establish a European recycling value chain capable of recovering lithium, nickel and cobalt from battery material.

Glencore acquired Li-Cycle in August 2025 and integrated it into Glencore Battery Recycling, expanding its position across battery feedstock, processing and metal recovery.

 

Related Battery and Critical-Materials Research

Explore detailed research on battery recycling technologies, critical-material supply chains, anode materials, electrolytes, and specialized chemicals supporting the global battery value chain.

 

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Principal Government and Intergovernmental Sources

  • European Union Batteries Regulation and official implementation guidance.
  • European Critical Raw Materials Act.
  • US Department of Energy critical-material processing and recycling funding.
  • US Treasury and IRS Section 45X and Prohibited Foreign Entity guidance.
  • US EPA lithium-ion battery recycling and black-mass guidance.
  • International Energy Agency battery circularity and critical-minerals recycling analysis.

 

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