Key takeaways
- The EU ban on destroying covered unsold clothing and footwear applies to large enterprises from 19 July 2026 and to medium-sized enterprises from 19 July 2030, subject to the law’s conditions.
- Textile EPR under Directive (EU) 2025/1892 is a separate obligation: national transposition is due June 2027 and relevant schemes are due April 2028, with special microenterprise timing.
- Recycling is generally not an automatic way around the unsold-goods destruction ban; allowable derogations require substantiation and retention of records.
- Italy’s 2024 separate textile collection reached 180,313 tonnes; collection, sorting, inventory management and industrial recovery remain distinct challenges.
European textile regulation is moving the cost of an inefficient product system back toward the businesses that create and place products on the market. The implications reach well beyond environmental reporting. Design complexity, material selection, demand planning, returns, excess stock, sorting and recovery are becoming linked operating questions.
Three developments matter particularly for fashion companies: the obligation to collect textiles separately, the revised Waste Framework Directive's rules on extended producer responsibility (EPR), and the Ecodesign for Sustainable Products Regulation (ESPR) prohibition on destroying specified unsold goods. They do not all begin on the same date or impose the same duties. But together they challenge the assumption that the lifecycle ends at wholesale delivery or retail sale. [1][2][3]
The regulatory map: which obligations apply, and when?
The operational error is to treat these dates as a single “2027 fashion sustainability deadline.” They belong to different legal instruments, economic operators and implementation mechanisms. Individual duties must be checked against the final legal texts, product classification and company size.
Italy demonstrates why collection is only the first step
Italy moved earlier than the European baseline by introducing mandatory separate collection of textile waste in 2022. Yet collection statistics reveal the scale of the industrial task rather than completion of it. According to ISPRA's 2025 reporting on 2024 municipal waste data, approximately 180,000 tonnes of textile waste were separately collected in Italy in 2024, up around 5.1% from 2023. The 2023 figure was approximately 171,500 tonnes (171,539 tonnes in 2023 versus 180,313 tonnes in 2024). These figures describe recorded separate collection within the municipal-waste reporting perimeter; they are not a complete count of all textiles discarded, reused or circulating in Italy. [5]
At EU level, the European Environment Agency estimated 6.94 million tonnes of textile waste in 2022, equivalent to around 16 kilograms per person. Its estimated capture rate for separately collected household textile waste was below 15% that year. Those statistics cannot be combined mechanically with Italy's tonnage because their geographical coverage, data boundaries and methodologies are different. [4]
Separately, the EEA estimates that 4–9% of all textile products placed on the European market are destroyed before use. This percentage is not a share of unsold stock alone and should not be interpreted as a rate for products collected as waste. It is a European estimate based on research with substantial data limitations. [7]
Collection quality is as consequential as collection volume. A bag of wearable clothing, a heavily contaminated textile and a bonded multi-material product enter radically different economic routes. Without sorting capacity, commercial outlets for reusable goods and viable fibre recovery, increased collection can simply move a problem from households to operators and municipalities.
This is the first governing principle: a collection system becomes circular only when its downstream destinations retain or recover value at scale.
Extended producer responsibility changes the economics upstream
Under the revised Waste Framework Directive, Member States must establish harmonised textile EPR frameworks. Producers covered by the scheme will be expected to finance relevant waste-management activities through producer-responsibility arrangements. The rules also connect financial contributions with product characteristics and circularity considerations in ways to be elaborated through implementation. [1][6]
For brand leadership, EPR is not merely a future line in the compliance budget. It raises questions that should be considered at product approval: How complex is this fibre blend? How readily can the product be sorted or disassembled? Are its components durable? How often will material changes occur after development has been frozen? Can usable goods stay in circulation through repair or resale?
A hypothetical garment with a lower purchase cost but high processing complexity can transfer significant cost to later stages of the chain. EPR creates a stronger rationale for incorporating those downstream consequences into sourcing and product-development decisions rather than treating them as externalities.
The directive provides a later start, 17 April 2029, for the relevant requirements applicable to enterprises with fewer than ten employees and turnover and balance-sheet totals within the specified microenterprise threshold; this is not the same regime as the ESPR unsold-goods destruction ban. [1]
The precise fee levels and their modulation must not be stated as fixed EU-wide rates today. National rules, producer-responsibility organisations and implementing measures will determine the applicable obligations and calculations.
The unsold-goods ban: what “destruction” really means
From 19 July 2026, the ESPR prohibits large enterprises from destroying specified unsold clothing, clothing accessories and footwear, subject to defined derogations. Medium-sized enterprises follow from 19 July 2030. This is not a universal prohibition covering every non-sold product or every business size. [2][3]
An important legal detail is easily missed: sending an unsold product for recycling can still constitute “destruction” under the ESPR's definition. The regulation generally treats intentional damage or discarding as destruction, with an exclusion for discarding undertaken solely to prepare products for reuse, including refurbishment or remanufacturing. Recycling is not automatically a compliant substitute for resale or repair. Specific derogations exist under Commission Delegated Regulation (EU) 2026/296, including documented product-safety grounds, certain legal non-compliance or substantiated intellectual-property infringements, as well as other specified circumstances. Mere commercial inconvenience is not a general exemption. [2][3][8]
Documentation is part of the exception, not an optional afterthought. When a product is destroyed under an applicable derogation, the operator must retain supporting documentation for five years after destruction, and make it available electronically to competent authorities within the time required by the delegated regulation. Records and grounds must be specific to the derogation invoked. This is different from the ESPR disclosure obligation concerning discarded unsold goods. [8]
The operating hierarchy is therefore different from simply choosing the least harmful waste pathway:
Prevent unnecessary inventory → sell through appropriate channels → evaluate reuse or donation → repair or refurbish → remanufacture where appropriate → assess legally permitted exceptional outcomes.
This is an operating sequence, not an exhaustive legal decision tree. Each route still requires appropriate controls for product safety, consumer rules, tax, waste status and documentation where applicable.
Returns, outlet channels and inventory become governance issues
Fashion has historically separated collection creation from replenishment, markdown management, returns handling and disposal. The emerging framework makes that separation harder to defend. Consider what happens when a business produces too many variants, manages size curves poorly or lacks a reliable grading process for returned goods: unsold and returned stock accumulates, the cost of inspection rises and the lawful options for value recovery narrow.
Three operational practices deserve particular scrutiny.
Assortment discipline. SKU proliferation generates complexity across design, procurement, stock allocation and after-sales processing. Fewer, better-governed product families may improve forecasting, repeatability and potential repairability — where customer demand and the product offer support that choice.
Reverse logistics. Returned products need consistent assessment: new and sellable, repairable, suitable for refurbishment, unsuitable for further use, or requiring exceptional treatment. Each classification should be supported by evidence and connected to the relevant route.
Data and accountability. Companies need reliable records of unsold quantities, decisions, dispositions and reasons, aligned with the disclosure duties that apply to them. Accounting write-offs and physical product outcomes are not the same data point.
None of these changes requires a claim that sustainability always increases margin. Prevention and retention can protect value, but building sorting, verification and repair capacity also has costs. The appropriate comparison is the total cost of the product system, including markdowns, returns, waste handling, compliance and lost recoverable value.
Materials, blended fibres and chemical safety
Circularity is constrained by the physical characteristics of products. Multi-fibre blends, trims, coatings and finishes can complicate identification and recovery; their actual effect depends on construction, available technology and processing infrastructure. A high-performance blended material cannot simply be labelled “non-circular,” nor can a nominally recyclable mono-material product be called circular without a realistic recovery route.
Chemical compliance adds another dimension. Businesses should preserve sufficient material and supplier evidence to avoid passing restricted substances or contamination into secondary-material flows. For chemical issues, including PFAS where relevant, obligations must be established under the applicable product and chemicals legislation rather than assumed from EPR alone.
The connection with the emerging Digital Product Passport is strategic: better records of composition and product characteristics can support compliance, sorting and eventual recovery. A passport does not, however, create recycling infrastructure that does not exist.
What a board-level circularity dashboard should actually measure
A practical management dashboard should follow decisions and outcomes, not just publication of a sustainability report. A credible starting set includes:
- Inventory exposure: unsold units and value by age, collection, category and channel.
- Return quality: return rate, grading outcomes, resale eligibility and time to disposition.
- Product architecture: number of SKUs, material families, repair-sensitive constructions and change frequency.
- Retention performance: units resold, repaired, refurbished, remanufactured or donated, with documented destinations.
- Material evidence: coverage and quality of fibre-composition and supplier documentation.
- Financial consequence: markdown, handling, recovery and disposal costs, measured against achievable value retention.
These metrics require clear definitions and must not be presented as mandated EU KPI formulas. They are proposed operating indicators for a governed fashion business.
The competitive question is not compliance versus creativity
The circular transition will be decided partly through design and industrial judgement: the number of products created, their technical coherence, the supplier structures that deliver them, the credibility of their information and what happens when they are not sold immediately.
Europe's evolving rules are making those decisions economically and legally more visible. For manufacturers, brands and retailers, the priority is to bring product governance, inventory intelligence and end-of-life accountability into one management conversation. Circularity is not achieved when a product becomes waste. It is shaped at the point where the company decides what should exist and how responsibly it can remain useful.
Frequently asked questions
When did the EU ban the destruction of unsold fashion?
The ESPR prohibition applies to covered unsold apparel, clothing accessories and footwear from 19 July 2026 for large enterprises and from 19 July 2030 for medium-sized enterprises, with specified derogations. [2][3]
Can an unsold garment be recycled instead of being destroyed?
Not as a general automatic workaround. Under the ESPR definition, discarding for recycling is normally treated as destruction; exceptions must be assessed against the applicable law. [2]
When do textile EPR schemes become mandatory in the EU?
Directive (EU) 2025/1892 requires Member States to put the relevant textile EPR schemes in place by 17 April 2028. The national implementation and the exact obligations for a producer require country-specific assessment. [1][6]
Virgili Studio perspective. Circularity begins with product architecture, stock governance, technical development and accountable manufacturing decisions. Explore Sustainability & Responsibility and the wider Atlas.
Related Atlas research
- Digital Product Passport for Fashion: EU Rules, Traceability and Product Data
- Sustainable Fashion in China and Europe: Consumer Behaviour and Market Strategy
References and further reading
[1] Directive (EU) 2025/1892 amending the Waste Framework Directive, including textile EPR and transposition. https://eur-lex.europa.eu/eli/dir/2025/1892/oj
[2] Regulation (EU) 2024/1781, ESPR, especially the provisions on unsold consumer goods. https://eur-lex.europa.eu/eli/reg/2024/1781/oj
[3] European Commission, New EU rules to stop the destruction of unsold clothes and shoes, 9 February 2026; and Ban on destruction of unsold clothes and shoes enters into application, 17 July 2026. https://environment.ec.europa.eu/news/new-eu-rules-stop-destruction-unsold-clothes-and-shoes-2026-02-09_en and https://environment.ec.europa.eu/news/ban-destruction-unsold-clothes-and-shoes-enters-application-2026-07-17_en
[4] European Environment Agency, Circularity of the EU textiles value chain in numbers, with 2022 estimates and methodological context. https://www.eea.europa.eu/en/analysis/publications/circularity-of-the-eu-textiles-value-chain-in-numbers
[5] ISPRA, Rapporto Rifiuti Urbani — Edizione 2025 (2024 data, textiles separate collection chapter). https://www.isprambiente.gov.it/files2025/pubblicazioni/rapporti/rapportorifiutiurbani_ed-2025_n419_versioneintegrale.pdf
[6] European Commission, Revised Waste Framework Directive enters into force, 16 October 2025. https://environment.ec.europa.eu/news/revised-waste-framework-directive-enters-force-2025-10-16_en
[7] European Environment Agency, The destruction of returned and unsold textiles in Europe’s circular economy, 2024 (4–9% estimate and methodological limits). https://www.eea.europa.eu/en/analysis/publications/the-destruction-of-returned-and-unsold-textiles-in-europes-circular-economy
[8] Commission Delegated Regulation (EU) 2026/296 of 9 February 2026, especially Arts 2–4 (derogations and documentary retention). https://eur-lex.europa.eu/eli/reg_del/2026/296/oj