Europe is rewriting the rules of sustainable fashion. France is tightening regulation, Finland is developing next-generation fibres, Italy is investing in textile recycling infrastructure and the Netherlands is pursuing circularity at a national level. But following a garment beyond the collection bin reveals a more complicated picture of Europe’s transition to circular fashion.
Europe has become a testing ground for fashion’s environmental transition. Extended producer responsibility (EPR), mandatory separate textile collection, environmental product information, restrictions on destroying unsold clothing and increasingly ambitious circular-economy policies are changing the conditions under which the industry operates. At the same time, textile districts, universities, technology companies and manufacturers are investing in new fibres, sorting systems, recycling technologies and lower-impact production processes.
Look across the continent and there is no shortage of apparent leaders. France has built one of Europe’s most developed regulatory frameworks for textiles. Italy has a manufacturing and recycling ecosystem few European countries can replicate. Finland and Sweden have established themselves in textile research and material innovation, while the Netherlands has pushed circularity deep into national policy. Germany has pursued certification, supply-chain responsibility and sustainable public procurement; Denmark has become an international centre for the sustainable-fashion conversation; and Portugal is developing a less visible but increasingly sophisticated ecosystem of textile manufacturing and material innovation.
Yet these achievements answer only part of the sustainability question. What happens when Europeans no longer want their clothes reveals the limits of the system being built around them.
Yet these achievements answer only part of the sustainability question. What happens when Europeans no longer want their clothes reveals the limits of the system being built around them.
According to the European Environment Agency (EEA), textile consumption in the European Union has reached approximately 19 kilograms of clothing, footwear and household textiles per person annually, while around 16 kilograms of textile waste is generated per person. Historically, only about 15 percent of household textile and footwear waste has been separately captured, meaning the overwhelming majority has entered mixed household waste, where meaningful reuse or textile recycling becomes significantly more difficult.
Following clothing beyond the collection point exposes further complications. Some garments are reused domestically or enter Europe’s expanding second-hand economy; others reach textile recyclers. Some are downcycled into products such as insulation or industrial wiping cloths, while others are incinerated, landfilled or exported to markets outside Europe, where their eventual fate can be difficult to trace.
As Europe attempts to establish itself as the global regulatory leader in circular fashion, the distinction between collecting textiles and keeping their materials in circulation is becoming increasingly important.
Different models of sustainable fashion
France is perhaps the clearest example of sustainability being driven through regulation. Its extended producer responsibility system for clothing, household textiles and footwear has operated since 2009, placing responsibility for end-of-life products on producers years before textile EPR became an EU-wide direction. France has since expanded its anti-waste framework and introduced an environmental-cost methodology for clothing, moving beyond voluntary corporate sustainability commitments towards a system in which government increasingly defines how fashion’s environmental impact is measured and managed.
The Netherlands has pursued a similarly structural approach. Textile EPR has applied since July 2023, while its Circular Textile Policy Programme 2025–2030 is intended to accelerate reuse and recycling. Its wider economy also provides unusually favourable conditions for circular systems. Eurostat recorded a circular material use rate of 32.7 percent in 2024, the highest in the EU, followed by Belgium at 22.7 percent and Italy at 21.6 percent. These are economy-wide rather than textile-specific measurements, but they provide useful context for the infrastructure within which circular-fashion ambitions must operate.
Italy’s significance lies more heavily in manufacturing. Prato, one of Europe’s historic textile districts, offers perhaps the clearest example of how traditional textile expertise could be adapted to a circular economy. The EEA describes a district of roughly 7,000 fashion enterprises processing more than 100,000 tonnes of pre- and post-consumer textile waste annually and producing approximately 28,000 tonnes of regenerated-fibre yarn.
That infrastructure expanded in July 2026 with the opening of Prato’s €31.3 million Textile Hub. Designed to process approximately 33,000 tonnes of material annually — around 20,000 tonnes of post-consumer textiles and 13,000 tonnes of pre-consumer waste — the facility uses technologies including artificial intelligence and near-infrared identification to improve textile sorting. It addresses one of the less visible but critical barriers to textile-to-textile recycling: before a discarded garment can become reliable recycling feedstock, its fibre composition, trims, contaminants and condition must be identified.
Northern Europe offers another model. Finland has emerged as an important centre for next-generation textile fibres and recycling technologies, with research institutes and companies developing cellulose-based materials, recycled yarns and processes capable of transforming textile waste into new fibres. Infinited Fiber Company, whose technology originated at Finland’s VTT Technical Research Centre, has developed a process that converts cellulose-rich waste, including cotton textiles, into regenerated textile fibre. Sweden’s textile ecosystem around Borås has similarly brought universities, designers, researchers and industry together around circular production, longevity, resource efficiency and material innovation.
Taken together, these countries present a persuasive case for European leadership. Once their waste systems are examined, however, the picture becomes considerably less straightforward.
Germany’s strength lies partly in institutionalisation. Its government-backed Green Button certification, introduced in 2019, combines requirements for textile products with corporate responsibility across supply chains, while public procurement has increasingly been used to stimulate demand for more sustainable textiles. Switzerland’s Sustainable Textiles Switzerland 2030 programme establishes sector objectives around emissions, circular product design and supply-chain due diligence, while Austria has incorporated textiles directly into its national circular-economy strategy.
Denmark’s influence is particularly visible through Copenhagen’s role as a meeting point for brands, policymakers, manufacturers, NGOs and sustainability organisations. Portugal represents a different but equally relevant case. Its textile and clothing sector includes almost 12,000 manufacturing companies, employs more than 118,000 people and generated turnover exceeding €8.2 billion in 2024. Research and industrial projects are exploring regenerative cotton, recycled polyester, lyocell, lower-water finishing processes, biological dyeing and other material innovations.
Portugal’s case highlights a weakness in many comparisons of sustainable-fashion markets: focusing primarily on consumer-facing brands can overlook transformation taking place upstream, inside mills, fibre companies, dye houses, research centres and manufacturing clusters.
Europe’s textile collection challenge
Around 6.9 million tonnes of textile waste was generated across the EU in 2022, equivalent to approximately 16 kilograms per person. According to EEA estimates, around 85 percent of household textile waste was not separately collected and instead entered mixed household rubbish. Once textiles enter that stream, opportunities for reuse and high-quality recycling are substantially reduced.
The EU requirement for separate textile collection, which took effect in January 2025, was intended to change this. The principle is straightforward: divert unwanted clothing from general waste, collect it separately and create the possibility of reuse, repair or recycling. Implementation, however, is exposing the next bottleneck. Europe is expanding textile collection faster than it is developing economically viable destinations for everything it collects.
Even among separately collected textiles, around 26 percent was still being sent to landfill or incineration in the EEA’s 2022 data. Landfill figures alone can also create a misleading impression of performance. Countries with exceptionally low landfill rates may rely heavily on waste-to-energy incineration instead. Denmark illustrates the distinction particularly clearly: its municipal landfill rate is extremely low, but incineration remains an important component of the country’s waste system. From the perspective of textile circularity, a garment that is burned rather than buried has still permanently left the material cycle.
The variation in textile collection between countries is nevertheless significant. Comparable EEA data indicate household textile capture rates of around 50 percent in Belgium, 38 percent in the Netherlands and approximately 30 percent in Austria, against an EU average below 15 percent. Belgium therefore presents an interesting case: it rarely dominates international conversations around sustainable fashion, yet its collection performance and wider circular-material use suggest its infrastructure warrants closer attention.
France provides one of the clearest demonstrations of why collection alone cannot solve fashion’s waste problem. Its mature EPR system supported the collection of approximately 289,000 tonnes of used clothing, household textiles and footwear in 2024. By 2025, that figure had fallen to around 272,000 tonnes, or 3.96 kilograms per resident, as the economics underpinning textile collection came under pressure.
International markets for used clothing weakened, sorting operators faced financial difficulties and the value of parts of the second-hand stream deteriorated. Collection disruptions followed, forcing the French system to mobilise tens of millions of euros in additional support for sorting and processing. What initially appears to be a waste-management problem is therefore also an economic one: collection, transport and sorting cost money, and part of that cost has historically been supported by the resale value of wearable clothing.
When that value declines, responsibility for financing the unwanted garments becomes critical. Extended producer responsibility is intended, at least partly, to address this by shifting more of the financial burden towards the companies placing textiles on the market.
France also exposes another contradiction. Approximately 3.6 billion new clothing, footwear and textile items entered the French market in 2025, while second-hand still represented only a relatively small proportion of overall consumption. One of Europe’s most sophisticated fashion-waste regulatory systems therefore continues to operate alongside extraordinarily high volumes of new product.
Better waste management can make fashion less wasteful. It cannot, by itself, make rising consumption circular.
When collection outpaces reuse
Germany illustrates another side of the problem. A 2026 study from the country’s textile recycling sector reported approximately 1.3 million tonnes of used textiles collected in 2023, but the proportion directed towards reuse had fallen from around 54 percent in 2013 to 44 percent a decade later. Over the same period, thermal treatment increased from approximately 8 percent to 21 percent, while collectors reported increasing volumes of contaminated or unsuitable material.
This creates a paradox at the centre of Europe’s circular-fashion strategy. A country can improve collection infrastructure and recover enormous quantities of clothing while simultaneously struggling to maintain the quality and economic value of the material collected. As more low-quality garments enter the system, sorting becomes more expensive and the proportion capable of supporting profitable reuse can decline.
Recent research also challenges the assumption that Europeans discard clothing primarily because garments have physically reached the end of their useful lives. Fashion for Good’s 2026 Sorting for Circularity: Project Rewear examined 8,280 discarded garments across four European countries and found that 37 percent displayed no damage, while another 41 percent had only minor defects.
Physical deterioration, then, cannot fully explain why clothing leaves European wardrobes. Fit, changing tastes, perceived value, low purchase prices and the sheer quantity of clothing available all influence how long garments remain in use. Designing a shirt to last longer has limited effect if its owner chooses to replace it after relatively few wears.
The waste problem is therefore inseparable from the volume of fashion entering the market.
Europe has plenty of textile waste — but not enough recycling-ready material
Recycling presents another complication because the term itself covers very different outcomes. A cotton garment transformed into fibre suitable for another textile product is not equivalent to the same garment being shredded for insulation or industrial wiping cloths. Both can appear within broad recycling statistics, but only the former begins to approach a closed textile-to-textile system.
True fibre-to-fibre recycling remains extremely limited relative to the volume of clothing entering the European market. The obstacle is not simply whether recycling technology exists. The greater challenge is transforming heterogeneous piles of discarded clothing into sufficiently clean and predictable feedstock for industrial recycling.
A single garment can contain cotton, polyester, viscose, polyamide and elastane, alongside zips, buttons, coatings, prints, membranes, linings and chemical finishes. Recyclers, by contrast, require material streams that meet relatively precise specifications. Europe has consequently developed an unusual feedstock paradox: it has an abundance of unwanted textiles, yet recyclers can still struggle to secure the type and quality of material their processes require.
Fashion for Good launched Feedstock Activation Europe in 2026 to address this gap between post-consumer textile collection and the requirements of textile-to-textile recyclers. The EU-funded T-REX project has meanwhile demonstrated recycling pathways for polyester, polyamide 6 and cellulosic fibres recovered from household textile waste.
These projects suggest that technical solutions are emerging. The harder question is whether Europe can develop the sorting, preprocessing, recycling capacity and demand for recycled fibres required to operate them at commercial scale.
Europe’s exported clothes complicate the numbers
The picture becomes still more difficult to assess once clothing leaves Europe.
The EU exported around 1.4 million tonnes of used textiles in 2023, almost three times the volume recorded in 2000. Africa and Asia are the principal destinations. Some of those garments enter functioning second-hand markets and continue to be worn; others are sorted, recycled or re-exported. Some ultimately become waste.
This makes classifications such as “prepared for reuse” or “exported for reuse” problematic when the final destination of a garment cannot be verified.
Fashion for Good’s Project Rewear followed part of this journey to Ghana’s Kantamanto market. Among garments sampled there that had entered the market as rewearable clothing, 86.5 percent displayed some form of damage. The finding does not invalidate the second-hand clothing trade, which supports extensive commercial ecosystems and keeps large quantities of clothing in use. It does, however, underline the difficulty of treating an exported garment as evidence of successful circularity simply because it has left Europe.
If the environmental cost of dealing with low-value clothing is ultimately transferred elsewhere, the waste has not disappeared. Its geography has changed.
Regulation moves from ambition to implementation
European policy is beginning to address some of these structural weaknesses. The revised EU Waste Framework Directive entered into force in October 2025, establishing common requirements for extended producer responsibility schemes for textiles across member states. The principle is significant because it changes who is expected to finance the end of a garment’s life. Municipalities, charities, collectors and resale markets can no longer be expected to carry the full economic burden of increasingly large volumes of discarded fashion.
Another important change took effect in July 2026, when large companies operating in the EU became subject to restrictions on destroying unsold clothing, clothing accessories and footwear under rules stemming from the Ecodesign for Sustainable Products Regulation. The measure targets an often overlooked source of fashion waste: products becoming waste without ever being worn.
The EEA has estimated that between 4 and 9 percent of textile products placed on the European market may previously have been destroyed before use, equivalent to roughly 264,000 to 594,000 tonnes annually. The European Commission estimates that destroying unsold textiles and footwear generates approximately 5.6 million tonnes of CO₂-equivalent emissions each year.
Preventing a product from becoming waste in the first place is fundamentally different from attempting to recycle it afterwards. The policy shift therefore points towards a broader definition of circularity — one concerned not only with what happens at the end of a garment’s life, but with preventing unnecessary production and destruction throughout the system.
The next test for European fashion
France demonstrates how far fashion regulation and producer responsibility can be developed. The Netherlands shows the importance of embedding textiles within a broader circular economy. Italy demonstrates the potential of combining established manufacturing expertise with industrial recycling infrastructure, while Finland and Sweden illustrate the role of research and material innovation. Germany shows both the possibilities of institutional intervention and the difficulties that arise when collection volumes increase while reuse becomes harder. Belgium’s collection performance deserves greater attention, while Portugal demonstrates how much of fashion’s environmental transition is taking place upstream in manufacturing rather than in consumer-facing sustainability campaigns.
There is no convincing single “most sustainable” fashion country in Europe. What emerges instead is a series of specialised models. None yet offers a complete circular-fashion system.
For much of the past decade, sustainable fashion concentrated heavily on materials: organic cotton, recycled polyester, alternative fibres, lower-impact dyes and reductions in water consumption. Attention then broadened towards traceability, working conditions and supply-chain responsibility. Europe’s next challenge is increasingly infrastructural.
A functioning circular-fashion economy requires more than a collection bin. It requires systems capable of determining whether a garment should be reused, repaired or recycled; economically viable sorting operations; reliable markets for second-hand clothing; recycling plants capable of handling complex fibre compositions; manufacturers willing to purchase recycled material; and financing mechanisms capable of supporting garments that have little or no resale value.
Europe is beginning to build parts of that system. Regulation is becoming more demanding, textile collection is expanding, new sorting facilities are opening and recycling technologies are moving towards industrialisation. Extended producer responsibility should provide new financing for end-of-life management, while restrictions on destroying unsold products are beginning to address waste before it occurs.
Yet the evidence also reveals the distance still to travel. Collection is expanding faster than high-value reuse and textile-to-textile recycling. Large quantities of clothing continue to be incinerated or exported, while growing volumes of inexpensive fashion place further pressure on sorting and resale systems.
The next phase of Europe’s sustainable-fashion transition will therefore be judged less by how effectively it collects unwanted clothes than by what happens to them afterwards. The real test is whether Europe can build a system capable of keeping garments and their materials in productive use — rather than simply becoming more efficient at managing their disposal.
