The ELV-R Regulation’s impact on the plastic industry

The ELV-R will force Europe’s automotive plastics supply chain to move from limited, image-led recycled content to regulated PCR use. Pierre Juan says the challenge is no longer volume alone, but quality, validation, supply security and recycling capacity, as OEMs, recyclers and material suppliers prepare for 2032 compliance.

Pierre Juan of Sustinplas Europe discusses the ELV-R impact on automotive plastics recycling. — Pierre Juan

The proposed ELV Regulation will reshape how plastics are specified, sourced, recycled and validated across Europe’s automotive supply chain. Pierre Juan, consultant at Sustinplas Europe, examines how the mandatory recycled-content targets, although reduced, still leave OEMs, recyclers and material suppliers facing major practical questions around post-consumer recyclate, automotive plastic recovery, supply security and quality compliance.

In April 2002, when the ELV Directive was adopted, the European Commission intended to set an ambitious target for European member states to address their own automotive waste.

From 11 million new vehicles sold in Europe, 7 million ELVs were collected, resulting in about 8 Million Tons of plastic waste. Besides steel, copper and aluminium, not much of any other materials were recycled from ELVs. Over the following 20 years and several amendments later, ELV collection improved, and hazardous substance pollution decreased, but let’s face it: the vast majority of ELV plastic waste is not recycled and continues to be burnt or landfilled in Europe.

In 2023, a new compelling regulation project was proposed by the EU Commission. The scope of this ELV-R project was much broader, encompassing ELV recyclability standards, digital passports, vehicle design for recycling with an eco-modulation fee, ELV waste treatment processes, mandatory recycling content in new vehicles, and more. One of the additional strategic drivers behind this new regulation was to reuse Critical Raw Materials (CRMs) from old electric vehicles to produce new Battery Electric Vehicles (BEVs) in Europe. In the 2023 ELV-R project, the proposal was to impose a minimum of 25% post-consumer plastic content in new vehicles, of which 6,2% would be sourced from automotive ELVs plastics. This exceeded the expectations of the automotive industry, which was betting at that time on 15%.

Two years later, following the automotive and chemical industry lobby, the final ELV-R reduced the mandatory PCR content from 25% to 15% for new vehicles launched as of 2032, including a minimum of 3% PCR derived from automotive plastic post-consumer waste. The text is now final since December 2025 and should be voted on July 16th 2026. Even though the final ELV-R reduced its original ambition, it will still have a significant impact on the automotive plastic industry and its plastic parts supply chain.

There is another ratio imposed by the ELV-R: 30% of “plastics” contained in old vehicles (ELVs) should be recycled (point 65 in the ELV-R introduction), and this will be part of the Producer Responsibility (EPR) to partially finance the collection and the recycling of plastics contained in ELV (point 34 in the ELV-R introduction).

What do we mean by “Automotive Plastic”?

The definition of “Plastic” in the ELV-R regulation (Article 3.9) has been debated since 2023. In June 2025, automotive plastic was defined to include all thermoplastics and polyurethane. More recently, in February 2026, Elastomers were also included in the scope. All other thermosets are excluded from the scope of the regulation (eg, reinforced thermoset composites, epoxy paints, tires, etc.). This does not, of course, prevent thermosets from being recycled or from containing recycled resin, but it will not be subject to the regulation or counted toward the 15% plastic recycling quota.

PCR volume demand development

In the 2020s, plastic suppliers to the automotive industry were expecting a significant rise in demand for plastic containing PCR feedstock, even before the regulation was proposed. The reality is that despite a tremendous number of announcements, case studies, samples, and application validations conducted by the car manufacturers, the average content of PIR and PCR plastics used in new European vehicles today remains very limited. Sustinplas estimate currently a content of 12%, from which most of it is “open source” PIR (fig. 1). Using PCR or PIR plastics in new vehicles was more a matter of image and green marketing so far, limited to a small number of niche vehicles and non-critical applications.

Fig 1: Graphic of %PCR / PIR by vehicle

Even though using PCR can save up to 80% of Plastic PCF*, all plastic parts today account for “only” 8% of a full Vehicle CO2 footprint, it is quite limited compared to switching from a combustion engine to an electric motor, for example. Therefore, the PCF* reduction is not the main motivation in the ELV-R. The ELV-R objective is to “value” the ELV waste and prevent environmental pollution. But this will cost the industry because using PCR in new vehicles presents multiple challenges for automotive manufacturers, such as the risk of quality failures, supply chain disruptions over a vehicle’s lifetime, and incremental increases in part costs.

On the economic side, the cost of collecting, sorting, and upgrading PCR through mechanical recycling to make it fit for automotive use, regardless of its source, has so far exceeded that of virgin plastics. The reduction in the market price of virgin polymers since 2019 made PCR plastic even less economically attractive. Nevertheless, the recent shortage of virgin plastic resulting from the war in Iran has reversed this situation, making Recycled plastic more attractive than virgin plastic in the short term.

Recycled plastic demand development

Ahead of this ELV-R regulation, OEMs have developed their own approaches to using recycled plastics, mixing PCR* and PIR* in niche vehicles or for targeted applications (see the Renault example in fig. 2). These efforts were mostly driven by cost reductions and, to some extent, by “Green Marketing”. This development accelerated in 2023 with the first ELV-R proposal, targeting, at the time, a 25% PCR content-by-vehicle ratio.

Fig 2: Renault example of PCR & PIR ratio by vehicles

Many automotive tiers and OEMs, mostly German OEMs, then claimed that the quantity of recycled plastic materials would not be available in the required quality to fulfill the ELV-R. With the final ELV-R version, this concern is off the table. Sourcing 12% of “open-loop” PCR should not be an issue if you consider PCR plastics already available from rigid packaging (rPP) or from WEEE (rABS, rPC/ABS). Moreover, recycling 3% of ELV plastic waste does not seem very demanding either, according to the JRC study from 2022* (see fig. 3). With the final text of the ELV-R Sustinplas estimate that the demand for PCR will reach 90 kt/y from Automotive ELV PCR* (closed loop), and 350 kt/y from other PCR sources (Packaging, WEEE,…) to supply the European automotive production of new vehicle as of 2032.

Fig 3: Supply demand from PCR for ELV-R (JRC study 2022)

Therefore, the challenge for OEMs will not be quantitative but rather qualitative, the question is : What is the optimal PCR product in what PCR application to comply with the regulation for a new vehicle at the lowest incremental cost and quality risk?

Following this pragmatic logic, only the lowest-hanging fruit will be harvested to comply. This will exclude many exotic plastics and non-economically viable options that have been tested and studied extensively over the last 10 years. Sustinplas Europe proposes a prioritization rating system to select the most attractive applications to use PCR for an automotive OEM’s in Table 4.

Table 4: Prioritization of PCR usage by automotive application

The volume of plastic “blends” (PCR blended with virgin plastics) will nevertheless be significantly higher than 15% because, with very few exceptions, pure PCR plastics do not meet automotive application requirements and must be blended with virgin plastics or modifiers to meet those requirements. Considering the average PCR ratio in automotive blends reported in recent publications such as PIAE* (Table 5), Sustinplas Europe estimated the volume of recycled plastic “blends” required to comply with the ELV.R (Table 6).

Table 5: Ratio of PCR & PIR by blends/applications

Table 6: Volume demand estimate of PCR blends by polymer families

In any case, the automotive industry will not move unless it is constrained by regulations, shortages or financial penalties. As a matter of fact, we expect a gradual growth in PCR blend demand from most OEMs, not earlier than 2028/ 2029 (fig.7)

Fig. 7: Volume demand projection of PCR

The Capacity bottleneck

Meeting the demand for recycled plastic blends will depend not only on the availability of pure PCR but also on the recycling and compounding production capacity to upgrade them. Nowadays, this appears to be the weakest link. Speculations about a fast-growing demand for recycled plastic in 2020 led to a large increase in mechanical recycling capacity, which grew by 30% from 2018 to 2022, with support from EU funding, according to Plastic Europe. Meanwhile, many investments were made in innovative chemical recycling technology. Unfortunately, this market demand turned out to be a mirage, receding as the SOP deadline approached. The mirage vanished in 2023. Plastic associations in Europe: Plastic Europe (PE), Plastic Recycling Europe (PRE), and Recycling Europe (RE) have all urged the EU about the financial degradation and bankruptcies of recyclers (https://www.linkedin.com/posts/plastics-recyclers-europe). The EU commission is preparing, in the frame of the CEA (Circular Economy Act), measures to save the remaining recyclers in Europe, considering short-term financial incentives. Above and beyond surviving, the recycling industry in Europe will need to further innovate and invest in new technologies to improve its own productivity and competitiveness to meet the demand expected in 2029 (fig.7). When asking the recycling machine manufacturer at the K 2025 where they are selling their latest sorting or filtering technology, the answer was Asia unanimously!

Is ELV-R a threat or an opportunity for European industry?

As with any disruptive change, the ELV-R will present both a threat and an opportunity. On the negative side, the higher costs of purchasing and using PCR blends may confer a cost disadvantage on vehicles produced and sold in Europe. However, on the positive side, cyclical variations or shortages in virgin plastic prices may reverse this in the future, as they did in 2021 and again now, as the global supply chain for virgin thermoplastics is being disrupted. It might give European automotive producers a strategic advantage over OEMs importing vehicles into Europe. Finally, the “mirror” clause, now formally adopted in the ELV-R final text, should also require that imported PCR plastic blends be certified in countries with environmental standards equivalent to those used by European suppliers, thereby protecting the European Automotive plastic industry. Tracking and managing these certifications will likely remain a headache for customs when it comes to imported vehicles or plastic components.

Other implications of the ELV-R on the industry

Beyond cost and supply security, using recycled plastic blends in new vehicles will pose other challenges for the automotive industry, and possibly stimulating innovation.

Among others:

Material specifications for PCR-containing plastics should be extended to include additional measurements and require more statistical data to reduce uncertainty and batch-to-batch variation in PCR plastic sources.
Substance of Concern: the ELV-R specifies in Article 5 the substances of concern, including heavy metals (lead, mercury, cadmium or hexavalent chromium). For the closed-loop PCR (3%), it will nevertheless be extremely difficult to prevent the pollution inherited from vehicles built more than 15 years ago. Some of the SVHC (Substances of Very High Concern) have accumulated. This point remains to be clarified in a delegated act, 72 months after EiF*.
Manufacturing Process monitoring: variations in the viscosity behaviors of recycled plastics from batch to batch typically exceed those of virgin plastics. This will require “smart” manufacturing processes, enhanced with AI, that automatically adapt to incoming plastic in injection molding process.
Plastic component validation process: parts made of recycled plastic will require larger testing windows and more frequent statistical testing. This was presented by Audi during the last PIAE in 2025. Such an extended validation phase will be required for critical applications such as safety parts or parts with aesthetic functions.
Purchasing process: To secure a stable supply of PCR plastic blends over the lifetime of a new vehicle, procurement departments will require more guarantees from their component and material suppliers and will select strategic, reliable, and solid suppliers capable of coping with uncertainties in the PCR supply-demand balance.
Automotive plastic supply chain: The automotive OEM will be accountable for meeting ELV-R regulations to launch their new vehicles as of 2032, but they will depend on the upstream supply of PCR blends. Dealing with ELV collections, plastic recyclers, or securing PCR supply streams from other industries was historically outside the control of automotive manufacturers: To reduce their dependence, we see a gradual integration of plastic recyclers into the automotive supply chain. One of the most visible business models was established by the Renault Group in 2022 with the creation of TFIN*. Recently, Stellantis has also founded “SUSTAINera”, preparing its own automotive circular ecosystem to better reuse its parts and secure material sourcing.
Innovation: The demand for PCR plastic is now partially “guaranteed” by future regulations; the risk of investing in recycling innovation should logically be reduced. For the plastic industry, the PPWR* (Regulation of the packaging industry) is far more decisive than the Automotive ELV-R, simply because the projected annual demand for PCR in packaging is close to 5 million tons, compared with 450 kt for automotives. Large chemical groups, traditional suppliers to the automotive markets (Dow Chemical, BASF, Trinseo, Borealis, LYB), have begun investing in R&D for mechanical recycling (MR) technologies, typically by acquiring recyclers, with very limited success so far. Massive R&D investment went in chemical recycling (CR). Either these chemical groups developed their own CR technology, such as LYB with MoReTec™, BASF with Chemcycling™, or as joint investments, such as INEOS Styrolution with Trinseo, Borealis, TotalEnergies, and Neste to invest in Indaver™ (P2C: PS depolymerization) or building new capacity with licensed technology, such as LG Chem with Mura Technology. These investments in CR have been mostly driven by the projected demand for food-contact polyolefin films or PET in packaging. This may also indirectly benefit the automotive industry. The concept of CR sounds great: plastic-to-plastic with no property loss. Unfortunately, rising energy prices, the relatively low yields of CR, and the high CO2 footprint of these technologies have killed many investment projects at an early stage. Moreover, given the reduced mandatory PCR content in ELV-R of 15%, mechanical recycling alone is very likely sufficient to meet this level at lower cost.

The impact of ELV-R on the thermoset-based composite used in the automotive industry

Is this good news or bad news for thermoset composite materials being excluded from the ELV-R Plastic definition?

On the one hand, the thermoset composite industry is exempt from any mandatory recycled-content ratio and can continue to operate independently of regulations in the Automotive industry. On the other hand, thermoset-based composites will be perceived as a non-recyclable plastic solution that does not contribute to achieving the ELV-R targets or reduce vehicles’ environmental footprint. All Research and development invested in chemically recycled thermoset resins through pyrolysis, or in the recycling of carbon or glass fibre, might benefit other composite industries (aeronautics and wind turbines) but will not be contributing to the ELV-R targets.

Thermoplastic composite on the other hand, should be advantaged at the expense of Thermoset composites in automotives, wherever technically possible.

Let’s put this ELV-R factor in perspective: thermoset composites (SMC, BMC, Carbon fibre-reinforced Epoxy, etc.) have been used in automotive applications so far not because of their recyclability, but for their weight/performance ratio. As far as their environmental footprint is concerned, these materials replace metal and reduce the vehicle’s CO2 footprint over its life through weight reductions. This will not change with the ELV-R regulations. Moreover, the final ELV-R requirement being less demanding than expected, it will play a minor role in the selection process for plastics. As you can see in Fig.3, reaching the ELV plastic ratio targets will be relatively easy with a limited number of thermoplastics and applications in average vehicles; the other “high performance” plastics, whether thermoplastics or thermosets, will remain in place, providing that they remain technically and economically justified in their application.

Definition

E.i.F: Enters into Force is the legally binding date of the vote from the EU parliament, as of which any regulation starts being implemented step by step until its final application.

PIR: Post Industrial Recycled plastics (also referred to as pre-consumer) sourced from any production waste along the Automotive production supply chain, but not directly recyclable on the origin manufacturing site.

PCR: Plastic waste generated after plastic goods have been placed on the market.

PCF: Product Carbon Footprint

TFIN: “The Future Is Neutral” is a JV between Renault and Suez

PIAE: Plastic in Automotive Europe, annual seminar

PPWR: Packaging and Packaging Waste Regulation