The European Parliament voted on 15 June 2026 to adopt the new EU regulation on circularity requirements for vehicle design and end-of-life vehicle management. Council approval is still pending before entry into force, but the text is politically agreed and the direction is set. For anyone in the automotive chemicals supply chain, now is the right time to map what changes.
The regulation replaces Directive 2000/53/EC on end-of-life vehicles (ELV Directive) and Directive 2005/64/EC on reusability, recyclability and recoverability (RRR Directive). Unlike a directive, it will apply directly across all EU Member States without national transposition, which removes a significant layer of legal variation that has complicated compliance for cross-border suppliers for two decades.
A lifecycle regulation, not just a waste rule
The old ELV Directive was fundamentally a waste management instrument. It set recycling and recovery targets, restricted four hazardous substances in vehicle manufacturing (lead, mercury, cadmium, and hexavalent chromium), and required producers to fund end-of-life collection. Those obligations are carried forward. But the new regulation reaches upstream into vehicle design and material selection in ways the directive never did.
New vehicles must be designed for disassembly. Manufacturers will need to ensure parts and components can be removed efficiently for reuse or recycling, and to provide documented instructions for doing so at end-of-life. A Circularity Vehicle Passport will record restricted substances, recycled content shares, and circularity strategies for each vehicle type, creating a data trail that runs through the entire value chain.
For chemical and material suppliers at the top of that chain, this is the part that matters most.
Recycled plastic content: a new supply chain pressure point
The regulation introduces mandatory minimum recycled plastic content in new vehicles: 15% within six years of entry into force, rising to 25% within ten years. At least 20% of that recycled plastic must come from end-of-life vehicles themselves — a closed-loop requirement designed to stimulate demand for automotive-grade recyclates.
These targets create a direct problem for formulation and compounding suppliers. Post-consumer recycled plastics carry higher contamination variability than virgin grades. Achieving consistent mechanical and chemical performance in safety-critical automotive applications, while also meeting the substance restrictions under Reg. (EC) No 1907/2006 (REACH), adds a layer of complexity that virgin-material supply chains simply did not have.
If a recycled polymer feedstock contains a Candidate List substance above 0.1% w/w, the obligations under REACH Article 33 apply regardless of its recycled origin. The material's history does not exempt it from substance communication requirements or SCIP notification under the Waste Framework Directive. Suppliers feeding recycled content into the automotive supply chain will need to characterise their feedstocks against the current REACH Candidate List — which now stands at 253 substances following the February 2026 additions of n-hexane and Bisphenol AF — and update their documentation accordingly.
Substance restrictions and the REACH interface
The regulation maintains the four existing substance bans (lead, mercury, cadmium, hexavalent chromium) with a mechanism to revise exemptions in line with scientific developments. Critically, it explicitly leaves additional substance restrictions to REACH, rather than creating a parallel vehicle-specific hazardous substances regime.
This is a meaningful design choice. It means that as ECHA expands the SVHC Candidate List and progresses substances toward Annex XIV authorisation or Annex XVII restriction, those developments will directly affect automotive supply chains without needing a separate amendment to the ELV regulation. The two instruments are linked by reference, not by repetition.
For suppliers of specialty chemicals used in coatings, adhesives, sealants, and polymer systems for automotive applications — categories where Bisphenol AF (now SVHC due to reproductive toxicity) and n-hexane (SVHC due to neurotoxicity, a first for the equivalent level of concern pathway) are both relevant — this regulatory cross-reference has immediate practical consequences. An SVHC addition at ECHA can now trigger Article 33 communication requirements and SCIP obligations that affect automotive customers well before any specific vehicle regulation amendment.
The Circularity Vehicle Passport and substance data upstream
The digital Circularity Vehicle Passport requires manufacturers to record restricted substance information as part of the vehicle's lifecycle documentation. Producing that information requires it to flow up through the supply chain in the first place. OEMs will be asking tier-1 and tier-2 suppliers to provide substance transparency data in formats consistent with the passport's information requirements, and that pressure will reach chemical and materials suppliers faster than the regulation's own transition timelines suggest.
The SCIP database, established under the revised Waste Framework Directive, already captures substance-of-concern information in articles at the 0.1% w/w threshold. The vehicle passport adds another layer of structured substance reporting that is conceptually aligned with SCIP but operates at vehicle-type level and with a broader scope of substances of concern extending beyond the current REACH Candidate List. Navigating the relationship between these two instruments — what SCIP covers, what the passport requires, and where gaps or duplications exist — will be one of the more practical compliance questions automotive chemical suppliers face over the next two to three years.
Extended producer responsibility for vehicle manufacturers
Three years after entry into force, extended producer responsibility (EPR) will require vehicle manufacturers to cover the cost of collecting and treating end-of-life vehicles across the EU. This has downstream pricing implications for suppliers: as OEM cost structures absorb EPR obligations, pressure on upstream supply chains to reduce overall lifecycle cost — including through material substitution — will increase. Substances that are costly to manage at end-of-life, whether because of SVHC classification, restricted status, or complex waste treatment requirements, become less attractive to specify.
That pressure is separate from the formal regulatory obligation, but it is real, and it compounds over time as EPR costs become visible in OEM accounts.
Export restrictions on non-roadworthy vehicles
Five years after entry into force, the regulation bans the export of vehicles declared non-roadworthy. This is relevant to the chemical supply chain primarily because it changes the geography of end-of-life vehicle streams. Currently, a significant share of "missing" ELVs — vehicles that disappear from national registration systems without verified end-of-life treatment — exit the EU and are dismantled outside the regulatory framework. Closing that route should increase the volume of ELVs processed through authorised EU treatment facilities, which in turn increases the scale of depollution and material recovery operations subject to REACH and other EU environmental requirements.
Treatment facilities stripping fluids, removing hazardous components, and processing plastics and metals will face growing throughput and, with it, growing scrutiny of how they handle substances of concern. For suppliers of depollution chemicals and industrial process inputs to the treatment sector, that is an expanding market with corresponding regulatory compliance demands.
The new ELV Regulation text is available via the European Parliament press release of 11 June 2026 (reference 20260611IPR45210). Council formal approval is the next procedural step before publication in the Official Journal.