Fashion's Circular Economy Promise Collects the Money but Skips the System

Producer Responsibility Organisations bring obligated producers into membership, receive placed-on-the-market data, charge proportionate fees, and distribute the resulting funding across collection, sorting, pre-processing and recycling. The operational logic assumes downstream capacity already exists or can be built in parallel. In packaging and electronics, where recycling infrastructure predated EPR legislation, that assumption held. In textiles, where closed-loop recycling remains below 1% and sorting capacity trails collection rates across every major market, it does not.

The report's own guidance on fund allocation reveals the contradiction. PROs are instructed to calculate fees per unit or by weight, charge membership costs, and disburse funding across the full waste management chain. Where collection rates are already high, the majority of funding should be redirected toward sorting, reuse and recycling infrastructure rather than further collection. The reasoning is explicit: collection without downstream capacity produces stockpiling rather than 'circularity.' The guidance says so itself. Yet the regulatory timetable in the EU has ensured that collection arrived first and processing capacity did not follow.

If the funding model's design creates a structural bias toward collection, the choice of fee metric compounds it further. Weight-based fees risk incentivising producers to reduce fabric weight rather than improve recyclability or durability. Weight does not measure recyclability. Per-unit fees, by contrast, allow PROs to track excessive production volumes and differentiate between product types with different processing costs. Complexity drives cost. A simplistic t-shirt is cheaper to recycle than complex clothing with integrated dyes, zips and buttons. Yet the revised EU Waste Framework Directive requires fees to be charged by weight at a minimum, embedding a metric that aligns more closely with collection tonnage than with the recycling complexity that actually determines downstream cost.

Separate collection of used textiles has been mandatory across the EU since January 2025. National Textiles EPR schemes are not mandatory until April 2028. That three-year gap means member states have been legally compelled to gather volumes for which no EPR-funded sorting or recycling infrastructure yet exists. The country-level variation is sharp. The direction is uniform. Collection has outrun processing in every case.

The report explicitly flags closed-loop recycling technologies for textiles as needing dedicated research and development investment. The EU's PESCO-UP project, funded through HORIZON at over €10 million, is cited as an example of the kind of targeted allocation required. That such investment must be named as an example rather than a norm is itself diagnostic. R&D for recycling infrastructure remains exceptional, not embedded within the funding model's standard disbursement logic. It remains a special case within a system that treats it as optional.

A funding architecture built primarily to reward collection, without matching investment in the processing capacity to absorb what is collected, does not produce a functioning circular loop. It produces a widening, unmanaged backlog. The collection-versus-sorting mismatch documented across EU member states is not a projection of what might go wrong. The damage is already done.

The backlog that this architecture produces is not abstract. France's Textiles EPR PRO, Refashion, operates under competing pressures that no fixed allocation formula can reconcile. Collectors demand free-of-charge collection as a condition of the national scheme. Regulators enforce collection targets with monetary penalties. Export markets absorb surplus volume at prices that undercut domestic processing investment. Each pressure pulls funding toward a different stage of the hierarchy, and none rewards investment in the stage most acutely short of capacity.

The enforcement action that followed exposes how these pressures resolve in practice. Refashion was fined during 2026 for failing to collect textile waste free of charge from collectors operating as part of the national scheme. The fine totalled €170,000 for waste management breaches attributed to deficiencies during both 2024 and 2025. A PRO fined for inadequate collection spending in a system that simultaneously exports 80% of what it collects is not suffering from a single operational failure. It is exhibiting two.

The cost structure confirms it.

Refashion's own cost structure makes the dual breakdown legible. It allocates 38% of funds to collecting, sorting and recycling, with 17% directed to a repair fund, 9% to communications, and 8% to reuse. The largest allocation covers the broadest operational category, making it difficult to determine how much of that 38% reaches sorting and recycling versus collection alone. If the fine indicates inadequate collection spending, and reports indicate that four-fifths of collected textiles were being exported in the years preceding 2024, the more pointed question is whether funds would have been better spent expanding domestic processing capacity.

The pattern has a precedent. When Germany's Packaging EPR scheme was reformed in the early 2000s, multiple PRO-type organisations emerged on a commercial, for-profit basis, competing for producer contracts on price. The competitive logic produced a predictable distortion: some organisations were accused of cherry-picking producer members whose packaging streams were cheaper to manage, avoiding costlier streams that yielded lower-quality recyclates. The incentive structure rewarded organisational efficiency over waste hierarchy outcomes, a race to the bottom dressed as competition. Textiles EPR schemes operating under similar pressure face an analogous risk, of defaulting to the stages of the hierarchy where spending is most visible and least complex.

Systematic 'Needs Assessments,' not fixed formulas, are the report's proposed remedy. The logic is sound but the implication is uncomfortable. A scheme can simultaneously fail its collection obligations and be exporting the majority of what it does collect. Neither side of the loop is functioning. Fixed allocation ratios cannot diagnose a breakdown operating on both sides simultaneously. Only a mechanism capable of identifying where the binding constraint sits, and redirecting revenue toward it, can prevent the pattern from reproducing itself. Fixed formulas cannot do this.

Without flexible reallocation, EPR-generated revenue risks being spent on the stage of the hierarchy easiest to measure rather than the stage most urgently short of capacity. Regulators can verify whether a PRO met its collection obligations. They cannot as easily verify whether collected volumes were domestically sorted, recycled, or shipped elsewhere. The metrics that trigger penalties and the metrics that measure circularity are not the same metrics.

The imbalance between what is collected and what can actually be reused or recycled domestically does not merely expose a funding sequencing problem. It sets the ceiling on what any scheme structured this way can achieve, and it is that ceiling which the next stage of the hierarchy must confront.

Reuse programmes, repair subsidies and improved sorting infrastructure can each extend a garment's time in circulation. Each intervention buys time. None eliminates the underlying maths. Each garment averages barely half a transfer before disposal, and every item that cannot be reused again must either be recycled or discarded. This volume will arrive at the recycling stage. Whether anything will be there to receive it remains unanswered.

The Netherlands has confronted this directly by setting escalating mandatory targets. Twenty-five per cent of collected textiles must be recycled into new textile products by 2025, rising to 33% by 2030. Ten per cent of collected textiles must be reused domestically, increasing to 15% over the same period. These targets acknowledge what voluntary schemes have been reluctant to state explicitly: reuse has a ceiling, and any credible circularity strategy must build recycling capacity beneath it. Whether current infrastructure can deliver those targets remains genuinely uncertain, but the policy design at least sequences the problem correctly. That alone distinguishes it.

The 2025 revision to the EU Waste Framework Directive goes further by embedding hierarchy prioritisation into the legislative architecture itself. Article 22a mandates support for research and development to improve product design and waste management operations in line with the hierarchy. Article 22c requires that producer fees are modulated on the basis of ecodesign requirements most relevant to waste prevention and hierarchical treatment. Article 22d requires that separately collected textiles are subject to sorting operations that ensure treatment follows the hierarchy. The recycling gap is therefore not merely a capacity shortfall that markets will eventually correct. It is a compliance obligation that member states must meet with infrastructure that does not yet exist at the scale required. The law has outpaced the system.

France's approach to extending garment life operates through a different mechanism. The Repair Bonus scheme (Bonus Réparation) offers a state-subsidised discount on clothing and footwear repairs. A typical repair costs around €30. The subsidy reduces that by €8. Roughly 700 cobblers have enrolled in the programme since its introduction. Repair extends a garment's usable life, but it does not resolve what happens once that life is genuinely exhausted. Each repaired item eventually re-enters the waste stream. Repair delays the inevitable, and the system that receives these garments once delay runs out remains one in which closed-loop recycling is virtually non-existent.

Recycled fibre uptake is further constrained by product composition. Mono-material garments made from a single fibre at 95% or above are singled out as significantly easier to recycle than mixed-fibre constructions. Australia's Seamless scheme offers a 25% fee reduction for such products, creating a direct financial incentive for recyclability at the design stage. The incentive is rational, but it reshapes future production only. The existing stock of mixed-fibre garments already circulating through collection systems will not become easier to process because fee structures have changed.

Without matching investment in fibre-to-fibre recycling capacity, the textiles that exhaust their reuse potential face only two destinations. They accumulate domestically, as the EU's post-2025 stockpiling confirms, or they are exported. EU used-textile exports more than doubled between 2005 and 2025 to over 1.44 million tonnes, reaching 3.2 kilograms per person. The destination of that exported volume, and whether EPR-generated funding is positioned to follow it, is the unresolved question the scheme design must now confront.

Money Without Infrastructure to Spend

Every scheme examined here collects more than it can process, prioritises what it can measure over what it cannot fund, and defers the recycling question to infrastructure that does not yet exist. The architecture was not designed to fail. It was designed to collect. Whether the schemes now proliferating across dozens of markets can be restructured quickly enough to fund what collection alone cannot solve, or whether they will reproduce the stockpiling and export patterns already visible in the markets that moved first, depends on a question none has yet been forced to answer: what happens when the money arrives and there is still nowhere for the material to go.