Textile collection is expanding. Sorting must catch up

Separate collection starts a route; it does not complete one

EU residents consumed an estimated 19 kilograms of clothing, footwear and household textiles per person in 2022. In the same year, Member States generated about 6.94 million tonnes of textile waste, or 16 kilograms per person, according to the European Environment Agency.

The EEA estimated that just under 15% of household textile waste was captured through separate collection in 2022. Approximately 85% entered mixed household waste, where opportunities for reuse and fibre recovery were effectively lost. The figures predate the full effect of the EU requirement for separate textile collection from 2025, so managed volumes are expected to rise.

A collection container does not determine the final route. A garment placed inside may be suitable for direct reuse, repair, fibre recycling, industrial wiping material or no viable recovery process. Its condition, composition and target market still have to be established through professional handling and sorting.

Condition and composition decide what remains possible

Quality protection begins at the collection point. Rain, dirt, oil or cross-contamination can turn a reusable item into waste and make a recyclable fibre fraction harder to process. Covered containers, dry storage and controlled loading are therefore not secondary housekeeping details; they preserve the higher-value routes that remain available.

Sorting first distinguishes products suitable for reuse or preparation for reuse. Non-reusable textiles can then be classified by fibre composition, colour, construction and the process available. This is difficult because a textile product is rarely fibre alone. Buttons, zips, coatings, elastane, prints, laminated layers and blended yarns may need removal or can affect the selected recycling technology.

Fibre-to-fibre recycling also requires an output specification and a buyer. Producing an unidentified mixed fraction is not equivalent to returning material to textile manufacture. Where reliable fibre identification is unavailable, the claimed destination should remain qualified rather than assumed.

• Separate reusable goods from waste fractions before compaction.
• Record moisture, visible contamination and non-textile components at receipt.
• Classify fibre and product groups to the level required by the confirmed recycler.
• Track rejected material and its treatment route alongside recovered output.

Producer responsibility now connects design with end-of-use costs

Directive (EU) 2025/1892 entered into force on 16 October 2025. It establishes common rules for extended producer responsibility schemes covering textile, textile-related and footwear products. Producers will contribute to collection, sorting, preparation for reuse, recycling and other treatment costs, while fee modulation is intended to reflect sustainability criteria such as durability and recyclability.

The directive requires separately collected textile waste to undergo sorting and prioritises reuse and preparation for reuse. It also recognises fibre-to-fibre recycling where technological progress allows. According to the European Commission, Member States have 20 months from entry into force to transpose the revision and 30 months to establish the producer-responsibility schemes.

Those deadlines provide a common direction, not identical operational capacity in every country. Collection networks, social-economy reuse systems, sorting plants and fibre-recycling markets will continue to develop at different rates. Operators should verify the applicable national implementation rather than treating the EU framework as one uniform collection service.

Higher capture makes downstream constraints more visible

The EEA Circularity Metrics Lab reports that 26% of separately collected textile waste is sent to incineration or landfill. It also records 1.4 million tonnes of used-textile exports from the EU in 2025. These indicators cover different parts of the system and reference periods, so they should not be combined into one recycling rate. They do show why collection weight alone is an incomplete performance measure.

Exports can lead to reuse, sorting or recycling, but available evidence also identifies landfill, open burning and uncontrolled disposal in some destinations. A destination record and treatment evidence are therefore more informative than a broad statement that material was exported for recovery.

Sites preparing for higher volumes can define source, collection method, seasonal variation, estimated reusable share, fibre categories, contamination limits and confirmed destinations before specifying storage or handling. Suitable sorted fractions may then be compacted for efficient logistics without damaging reusable products or obscuring fibre categories. Separate collection gives textiles another opportunity to remain in use; circularity depends on protecting and assigning that opportunity after the container is emptied.