Textile Exchange projects that 3–5 million tonnes of textile-to-textile recycled fibre could be available for apparel and home textiles by 2030. Its findings expose the distance between announced capacity and material that manufacturers can use.
Fashion’s recycling ambitions are often expressed through the capacity of proposed factories. Announcements establish how much textile waste a facility expects to process, offering a measure of planned industrial investment. But input capacity is several steps removed from the fibre available to a manufacturer. Understanding that distinction is essential to judging whether the industry’s circularity commitments are becoming commercially useful material.
Textile Exchange’s October 2026 report, Textile-to-Textile Recycled Fiber: Availability Data for Apparel and Home Textiles, examines that journey. Developed with Reverse Resources, Fashion for Good and TEXroad, with funding from lululemon, it connects estimates of textile-waste availability with recycling infrastructure and processing performance to model potential recycled spinnable fibre supply.
The study estimates that approximately 15 million tonnes of recyclable textile feedstock could be available globally in 2030, compared with approximately 10 million tonnes in 2025. When matched with recycling capacity and adjusted for operating conditions and processing efficiencies, the model projects 3–5 million tonnes of recycled spinnable fibre in 2030, up from an estimated 1–1.5 million tonnes in 2025.
These figures describe different stages of a system. Available recyclable material does not establish that suitable infrastructure exists to process it, that facilities will operate at capacity or that their output will meet a manufacturer’s requirements. The report’s contribution is to make those distinctions visible—and they should become central to how fashion measures recycling progress.
The Distance Between Capacity and Production
The study begins with facilities’ estimated recycling input capacity, then adjusts for the risk that planned operations may not become operational or may produce less than expected. It matches feedstocks to compatible technologies, applies utilisation assumptions and accounts for losses during recycling and downstream conversion.
That final stage is particularly important. Pulp, chips and chemical building blocks are intermediate outputs, requiring further processing before they become spinnable fibre. A facility producing those materials has completed one part of the manufacturing chain, rather than delivered an input ready for fabric production.
For 2030, the report models approximately 11–15 million tonnes of recycling input capacity before adjustments for project failure or under-delivery. After accounting for operational risk, feedstock compatibility, utilisation and processing efficiencies, the estimate reaches 3–5 million tonnes of spinnable fibre.
The difference is not a simple measure of material lost inside recycling plants. It also reflects capacity that may not operate, equipment running below its potential and mismatches between available waste and processing technologies. Presenting these figures as a straightforward recycling yield would misrepresent the model.
Polyester makes the execution risk especially clear. Estimated recycling input capacity rises from approximately 0.92 million tonnes in 2025 to 7.48 million tonnes in 2030. Figure 3 attributes 69% of projected 2030 polyester input capacity to “innovators”, defined as companies at research or demonstration stage that are refining technologies and exploring initial scalability. This is a capacity projection before the model’s subsequent adjustments, rather than a forecast of delivered polyester fibre.
The report also identifies large expansion plans from a relatively small number of polyester recyclers as the main driver of projected fibre growth. Bringing those projects into sustained operation will therefore have an outsized influence on the outcome.
Capacity announcements deserve to be assessed alongside commissioning progress, operating rates, feedstock specifications and downstream conversion arrangements. Purchasing commitments matter, too: productive infrastructure requires a commercial route through which recycled material can reach manufacturers and brands.
More Waste Does Not Automatically Mean More Supply
The study’s feedstock breakdown challenges another assumption: textile-to-textile recycling does not necessarily mean discarded clothes returning to clothing. Post-industrial material accounts for 68% of estimated recyclable feedstock in 2025 and 61% in 2030, while the post-consumer share increases from 32% to 39%.
By 2030, the model estimates approximately 9 million tonnes of post-industrial textiles and 5–6 million tonnes of post-consumer textiles available for recycling. Manufacturing remnants remain the larger resource, even as discarded clothing and household textiles contribute more. These estimates already account for factors including collection, reuse and recyclable composition; they do not represent all textile waste generated.
A recycler still needs material compatible with its process, supplied consistently enough to support production. Collection, sorting, preparation and traceability are consequently part of the industrial investment proposition. Access to a large waste stream alone cannot establish a dependable raw-material supply.
The evidence behind the projections also requires scrutiny. The capacity assessment incorporates direct survey responses from 83 facilities, alongside public information and modelled estimates. Approximately 60% of the facility data relies on proxies. The capacity graph draws on data collected between January and July 2025, making the October 2026 publication a model informed by an earlier evidence base, rather than a live inventory of operational plants.
Post-consumer modelling introduces further assumptions, including an average product service life of four years. Gaps in regional information required general consumption data and mainly European fibre-composition data to inform estimates elsewhere. The authors explicitly describe the findings as preliminary and directional.
Asia is expected to record the greatest growth, although the regional maps do not capture the full model. They show mapped facilities and exclude unknown-facility proxies, including substantial anticipated Asian capacity incorporated into the global totals. The maps should therefore be read with their stated boundaries in mind.
The study itself covers apparel and home textiles, including mechanical and chemical recycling pathways, while excluding plastic bottles and technical textiles. It cannot establish a robust apparel-only share because the capacity data does not determine how facilities will allocate production between clothing and home textiles.
These limitations make better reporting an immediate industry priority. More consistent disclosure of actual throughput, utilisation, material composition and downstream output would help replace assumptions with observed performance. The authors also stress that stronger investment and demand could support higher fibre availability than their conservative pathway suggests; the forecast is neither a guaranteed outcome nor a fixed ceiling.
Reaching 3–5 million tonnes would represent meaningful growth, although Textile Exchange expects textile-to-textile recycled fibres to remain a modest share of apparel and home-textile fibre demand in 2030. Fashion’s commercial test is whether recovered textiles become dependable inputs for new products. Measuring that journey consistently would provide a firmer basis for circularity claims than proposed factory capacity alone.
Read the full report: Textile Exchange — Textile-to-Textile Recycled Fiber: Availability Data for Apparel and Home Textiles
