The textile industry faces a growing gap between the volume of discarded materials that could be recycled and the supply of recycled fibers available for new products. Global recyclable textile feedstock could reach 15 million metric tons by 2030, while the supply of recycled spinnable fibers from apparel and home textiles is projected to reach only 3–5 million metric tons, according to Textile Exchange. The difference highlights a key constraint in textile circularity: collecting waste is only the first step. Fiber identification, sorting, processing yields, recycling technology and commercial demand all determine how much discarded material can return to textile production. For manufacturers and brands, the challenge is not simply to increase recycled content, but to build a reliable supply chain capable of converting textile waste into fibers that meet quality and cost requirements.
Rising fiber production increases the waste challenge
According to Textile Exchange’s October 2026 report, Textile-to-Textile Recycled Fiber Availability Data for Apparel and Home Textiles, global recyclable textile feedstock was estimated at 10 million metric tons in 2025. This could rise to around 15 million metric tons by 2030. However, recycled spinnable fiber supply from apparel and home textiles was estimated at only 1 to 1.5 million metric tons in 2025. The report was developed with Fashion for Good, Reverse Resources, and TEXroad. These figures measure different stages of the recycling process. Feedstock is waste that may be suitable for recycling. Recycling capacity refers to the amount that facilities can process. Recycled fiber output measures the material produced after processing. The final output depends on the quality and availability of feedstock, processing losses, and the technology used.
Global fiber production adds to this challenge. Textile Exchange’s Materials Market Report 2025 reported that production reached 132 million metric tons in 2024, up from 125 million metric tons in 2023. Its business-as-usual projection indicated that production could reach 169 million metric tons by 2030.
However, not all discarded textiles can become new fibers. Garments may contain cotton, polyester, nylon, elastane, dyes, chemical finishes, and accessories. These materials can complicate separation and recycling. The latest Textile Exchange assessment covers post-industrial and post-consumer waste containing cotton, polyester, nylon, man-made cellulosic fibers, wool, and their blends. It excludes non-textile feedstocks, such as plastic bottles, and technical textiles.
Textile Exchange also warns that its estimates are directional because reliable data remain limited in some areas. Better data from recyclers and suppliers will be necessary to improve future estimates.
Europe exposes the collection and sorting gap
Europe shows how much waste can remain outside recycling systems. According to the March 2026 report Advancing Textile Circularity by Boston Consulting Group (BCG) and ReHubs, Europe generated around 15.2 million metric tons of textile waste in 2025. This included 13.3 million metric tons of post-consumer waste, but only around 1.5 million metric tons were collected and sorted.
This gap limits the supply of suitable materials for textile-to-textile recycling. Collection systems must capture discarded garments before sorting facilities can separate them by fiber type, condition, and recycling suitability.
Separate collection alone is not enough. Sorting facilities must identify material composition and remove unsuitable items. The waste may then require cleaning, cutting, or other preprocessing before entering a recycling plant.
BCG and ReHubs estimate that less than 1% of Europe’s textile waste is recycled into new textiles. Their 2035 target is to recycle around 2.7 million metric tons of textiles annually. Reaching this level would require annual collection of 8 million metric tons and an increase in sorting rates from 36% to 63%.
Recycling capacity does not guarantee fiber output
Textile Exchange projects that recycled spinnable fiber supply could rise to 3 to 5 million metric tons by 2030, compared with 1 to 1.5 million metric tons in 2025. However, recyclable feedstock could reach 15 million metric tons over the same period. The difference highlights the losses and limitations across the recycling chain.
Sorting errors, unknown fiber compositions, chemical contamination, heavy dyes, specialized finishes, and elastane blends can make materials difficult to recycle. Different technologies also produce different yields and require specific feedstock quality.
Mechanical recycling is generally suitable for clean, well-sorted materials, but repeated processing can shorten fibers and reduce their quality. Chemical recycling can separate or recover components from some complex blends, although it requires suitable technology, process control, and investment.
A July 2026 analysis by Cleantech Group, Mechanical Recycling Is the Near-Term Answer, but Chemical Pathways Will Define the Ceiling for Textiles Recycling, identifies mechanical recycling as an important near-term option and chemical recycling as a potential route for handling more complex materials.
Recycling projects are advancing at different stages
Several companies are developing technologies to process textile waste. However, announced capacity, pilot operations, and commercial output must be assessed separately.
- Circulose, Sweden: The company has stated an annual capacity of 60,000 metric tons and was scheduled to reopen in 2026, supported by long-term brand commitments. Its actual operating status and output should be verified before treating this capacity as available supply.
- Circ, France: The company is developing a chemical recycling facility designed to process 70,000 metric tons of polycotton feedstock annually by 2029. The process aims to recover cellulose pulp, purified terephthalic acid (PTA), and monoethylene glycol (MEG).
- Worn Again Technologies, Switzerland: The company started its Accelerator plant in March 2026 to recover spinnable polyester from end-of-life polycotton blends.
These projects demonstrate different approaches to textile recycling. Their commercial contribution will depend on reliable feedstock, operating performance, fiber quality, and demand from buyers.
Investment must extend beyond recycling plants
Scaling textile recycling requires investment across the entire supply chain. BCG and ReHubs estimate that Europe needs €8 billion to €11 billion in capital investment and €5 billion to €6.5 billion in annual operating costs by 2035. These estimates cover the wider system, not recycling plants alone.
Funding must support collection networks, optical sorting, fiber identification, transportation, preprocessing, and quality control. Without these systems, recycling facilities may struggle to secure enough suitable material or operate efficiently.
Extended Producer Responsibility (EPR) can help fund textile waste management, while Digital Product Passports (DPP) can improve access to product and material information. However, traceability requirements alone cannot guarantee that waste will be recyclable or economically viable.
Brand commitments are also essential. Recyclers need predictable orders and reliable revenue to attract investment. Brands must therefore help create demand for recycled fibers rather than wait for large volumes to become available at competitive prices.
For Bangladesh, manufacturing waste offers a practical starting point. Factories can separate cotton, polyester, and blended waste, record material composition, and prepare feedstock according to recyclers’ specifications. Better traceability and consistent waste quality could help connect local suppliers with recycling facilities and buyers.
However, progress will depend on whether suitable waste can be collected, processed economically, and converted into fibers that meet buyers’ requirements.
By 2030, recyclable textile feedstock could reach 15 million metric tons globally. Yet the industry’s success will depend on how much of this material becomes usable fiber and reaches fashion brands. Closing the gap requires coordinated investment in collection, sorting, recycling technology, and long-term demand.
