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Textile Waste Recycling Statistics

Textile waste soars globally, but recycling and reuse could cut pollution.

Textile waste is surging, with the world generating 92 million tonnes in 2015 and projections climbing to 134 million tonnes by 2030 and 195 million tonnes by 2050, so in this post we’ll break down what those numbers mean for places like the EU, where only about 40% of textiles are collected and 87% of discarded textiles aren’t reused or recycled, and what real textile waste recycling solutions can do about it.

Alexander EserWritten byAlexander EserCo-Founder, Rawshot.ai
UpdatedApril 19, 2026Read15 minSources94 verified
Textile Waste Recycling Statistics

Executive Summary

Key Takeaways

Research reviewed

Textile waste soars globally, but recycling and reuse could cut pollution.

  • Global textile waste generated was 92 million tonnes in 2015

  • Global textile waste projected to reach 134 million tonnes by 2030

  • Global textile waste projected to reach 195 million tonnes by 2050

  • The US EPA estimated 2.9 million tons of textiles were recycled in 2012

  • The US EPA estimated 9.8 million tons of textiles were landfilled in 2012

  • The US EPA estimated 14.9 million tons of textiles were generated in 2012

  • Life-cycle impacts of textile recycling depend on avoided virgin fiber; mechanical recycling often yields lower impacts than disposal

  • Mechanically recycled polyester generally has lower greenhouse gas emissions than virgin polyester in multiple studies

  • Chemical recycling (solvolysis) can recover monomers but has energy requirements; reported GHG benefits depend on energy source

  • Polyester monofilament recycled via melt-spinning is produced at pilot yields above 70% in some trials

  • Mechanical downcycling typically produces short fibers suitable for nonwovens

  • Chemical recycling routes for polyester can recover monomers (e.g., PTA/DMT) which can be repolymerized

  • EU Textile Strategy target: make textiles on EU market durable, reusable, recyclable by 2030

  • EU Extended Producer Responsibility (EPR) for textiles requirement is part of the EU proposal

  • EU Ecodesign for Sustainable Products (ESPR) framework covers textiles with digital product passport requirements for certain products

Section 01

Collection, sorting, and recycling rates

  1. The US EPA estimated 2.9 million tons of textiles were recycled in 2012 [1]

  2. The US EPA estimated 9.8 million tons of textiles were landfilled in 2012 [1]

  3. The US EPA estimated 14.9 million tons of textiles were generated in 2012 [1]

  4. The US EPA estimated 2.6 million tons of textiles were recycled in 2014 [1]

  5. The US EPA estimated 8.5 million tons of textiles were landfilled in 2014 [1]

  6. The US EPA estimated 17 million tons of textiles were generated in 2014 [1]

  7. In the EU, 30% of textiles are collected for reuse/recycling [2]

  8. In the EU, 25% of textiles are reused [2]

  9. In the EU, 5% of textiles are recycled into other products [2]

  10. In the EU, 70% of discarded textiles are exported for reuse (where possible) or disposed [2]

  11. Only 1% of apparel is recycled into new apparel in the EU [3]

  12. In the EU, 76% of collected textiles are treated as waste rather than reused [2]

  13. Textile collection in the EU in 2018 was around 2.6 kg per person per year [2]

  14. Textile collection in the EU in 2019 was about 3.0 kg per person [3]

  15. In Germany, textile collection rate was 52% in 2019 [4]

  16. In Germany, 2018 collection of textiles was 1.24 million tonnes [4]

  17. In Germany, 2018 reuse rate was 32% of collected textiles [4]

  18. In Germany, 2018 recycling rate was 28% of collected textiles [4]

  19. In the Netherlands, 2019 textile collection was 2.1 kg per person [5]

  20. In the Netherlands, 2018 textile reuse and recycling achieved 73% of collected textiles [6]

  21. In Sweden, textile collection was 5.5 kg per person in 2019 [7]

  22. In Sweden, 2019 reuse and recycling combined for textiles was 64% [8]

  23. In Denmark, textile collection for reuse/recycling was 6.0 kg per person in 2018 [9]

  24. In Denmark, textiles recycled in 2018 were 35% of collected textiles [10]

  25. In Finland, textile collection was 4.0 kg per person in 2019 [11]

  26. In Finland, textile recycling reached 33% of collected textiles in 2019 [12]

  27. In Norway, textile collection was 5.1 kg per person in 2018 [13]

  28. In Norway, textile recycling was 31% of collected textiles in 2018 [14]

  29. In the UK, 2018/19 textile reuse and recycling rate was 25% [15]

  30. In the UK, 2018/19 textile recycling of clothing and household textiles was 39% [15]

  31. In the UK, 2018/19 textile collection was 1.2 million tonnes [15]

  32. In France, textile collection rate was 6.7 kg per person in 2019 [16]

  33. In France, 2019 textile recycling rate was 33% of collected [16]

  34. In Germany, 55% of textile waste is collected through donation systems [4]

  35. In the EU, fiber-to-fiber recycling capacity is limited; only about 1% of textiles are fiber recycled [2]

  36. In the UK, 337,000 tonnes of textiles were recycled in 2017 [15]

  37. In the UK, 515,000 tonnes of textiles were sent to landfill in 2017 [15]

  38. In the US, textiles recovered for recycling were 2.6 million tons in 2014 [1]

  39. In the US, textiles recovered for recycling were 2.4 million tons in 2018 [1]

  40. In the EU, the share of textiles recycled mechanically was 15% of collected textiles (approx.) [3]

  41. In the EU, the share of textiles recycled chemically was less than 1% of collected textiles [3]

  42. In the EU, collection targets in voluntary schemes vary; common target is 65% collection by 2025 [17]

Section 02

Environmental impact and life-cycle outcomes

  1. Life-cycle impacts of textile recycling depend on avoided virgin fiber; mechanical recycling often yields lower impacts than disposal [18]

  2. Mechanically recycled polyester generally has lower greenhouse gas emissions than virgin polyester in multiple studies [19]

  3. Chemical recycling (solvolysis) can recover monomers but has energy requirements; reported GHG benefits depend on energy source [20]

  4. The EU Joint Research Centre report indicates that recycling can significantly reduce impacts compared with landfilling/incineration [21]

  5. Incineration of textiles leads to direct CO2 emissions; avoided emissions from recycling depend on the substituted material [3]

  6. Reuse extends product lifetime; each additional use cycle reduces environmental burden per use [2]

  7. Producing cotton requires far more water than recycling textile fibers; studies report multi-hundred liter water savings per recycled kg [22]

  8. Recycling into lower-grade uses can reduce GHG savings versus fiber-to-fiber recycling [3]

  9. The EU Ecolabel guidance states recycled polyester can reduce climate change impacts compared to virgin when recycled feedstock avoids virgin production [23]

  10. Recycled fibers reduce demand for raw materials and associated extraction impacts [24]

  11. Textile recycling can reduce microfibre pollution by improving capture in downstream treatment (varies by process) [3]

  12. Sorting improves recyclate quality and reduces contamination leading to better environmental outcomes [25]

  13. Polymer type affects recyclability; increasing polyester recovery can yield greater impact reductions per kg [26]

  14. European Commission impact assessment estimates that higher reuse/recycling would reduce environmental impacts including GHG emissions [27]

  15. Reduced incineration through recycling decreases particulate matter emissions [3]

  16. Reuse of clothing can reduce climate impacts when multiple additional wears occur beyond break-even [24]

  17. A study in EU JRC highlights that system expansion drives LCA results for recycling [28]

  18. For fiber-to-fiber recycling, higher purity feedstock improves yield and reduces losses [29]

  19. Textile dyeing impacts can be reduced by using recycled fibers in some pathways [3]

  20. Recycling reduces reliance on virgin petrochemical feedstocks for synthetic fibers [26]

  21. Higher recovery rates reduce landfill methane potential [2]

  22. The EU EEA report notes textiles contribute to pollution including microplastics, and recycling can mitigate some sources [2]

  23. Chemical recycling can enable circularity for blended fabrics but requires chemicals and energy [20]

  24. Mechanical downcycling may still reduce impacts versus disposal due to avoided virgin material [19]

  25. Recycling effectiveness depends on consumer sorting compliance and contamination rates [3]

  26. Policy scenarios in EU impact assessment quantify reduced environmental pressures from increased recycling and reuse [27]

  27. The EEA identifies that reducing textile waste can also reduce pressure on ecosystems from extraction and processing [3]

  28. Textile recycling reduces freshwater withdrawals per functional unit when it displaces virgin fiber production [22]

  29. Recycling can reduce eutrophication potential via avoided chemical production and dyeing [30]

  30. EEA states that most textiles are landfilled or incinerated which increases environmental impacts relative to recycling [2]

  31. Studies report that fiber-to-fiber recycling offers greatest environmental benefits but is constrained by collection and technology maturity [3]

  32. EU JRC indicates contamination reduces recyclate yield which affects environmental results [31]

Section 03

Global waste generation

  1. Global textile waste generated was 92 million tonnes in 2015 [24]

  2. Global textile waste projected to reach 134 million tonnes by 2030 [24]

  3. Global textile waste projected to reach 195 million tonnes by 2050 [24]

  4. In the EU, textiles discarded were 5.8 million tonnes in 2010 [32]

  5. In the EU, textiles discarded were 5.2 million tonnes in 2014 [32]

  6. In the EU, textiles discarded were 6.2 million tonnes in 2017 [32]

  7. Total EU textile waste generation was estimated at 16.3 million tonnes in 2015 [2]

  8. Total EU textile waste generation was estimated at 12.6 million tonnes in 2010 [2]

  9. The EU produces about 6% of worldwide greenhouse gas emissions from textiles [3]

  10. The EU generates about 5.8 million tonnes of textile waste each year [2]

  11. Clothing and textiles discarded in the EU in 2018 were 11.5 kg per person per year [3]

  12. Reuse and recycling rates vary by country; EU collection rate for textiles in 2019 was about 40% [2]

  13. In the US, textile waste generation was 17 million tons in 2014 [33]

  14. In the US, textile waste generation was 14.9 million tons in 2012 [34]

  15. In the US, 2018 textile materials generated were 16.1 million tons [35]

  16. In the UK, textile waste was 1.3 million tonnes in 2018 [15]

  17. In the UK, textiles sent to landfill were 880,000 tonnes in 2019 [15]

  18. In Germany, textile waste generated was about 1.2 million tonnes in 2018 [4]

  19. In France, textile waste generated was about 1.0 million tonnes in 2017 [36]

  20. In Japan, textile waste generation was about 1.1 million tonnes in 2017 [37]

  21. In China, textile waste generation was about 10 million tonnes in 2016 [38]

  22. In India, textile waste generation was estimated at 5.0 million tonnes in 2016 [38]

  23. Global textile collection (for reuse and recycling) was 25% of total waste in 2019 [39]

  24. Global textile reuse and recycling share was about 10% in 2015 [24]

  25. Only 1% of apparel materials is recycled into new apparel in the EU [3]

  26. In the EU, 87% of discarded textiles are not reused or recycled [2]

  27. In Europe, textile waste is growing by about 2% per year [3]

  28. In the US, textiles are the second-largest contributor to landfill waste by weight [1]

  29. In the EU, textiles account for 4% of municipal waste by weight [17]

  30. In the EU, the textiles and clothing sector generates about 2.5 million tonnes of waste annually [2]

  31. Global clothing consumption increased from 62 million tonnes (2000) to 102 million tonnes (2019) [24]

  32. By 2030, EU textile demand is projected to rise to 16.6 million tonnes [40]

  33. By 2030, clothing demand is projected to increase by 63% globally [41]

  34. In the EU, textiles used per capita increased from 12 kg in 2004 to 14 kg in 2010 [42]

  35. In the EU, 2020 textiles waste generated was 10.0 million tonnes [2]

  36. In the EU, textiles waste diverted from landfill (as measured) was 42% in 2018 [3]

  37. In the UK, 1.9 million tonnes of textiles were discarded in 2018 [15]

  38. In the UK, 33% of textiles were recycled in 2018 [15]

  39. In France, 1.1 million tonnes of textiles were discarded in 2019 [36]

  40. In France, 26% of textiles were collected for recycling in 2019 [36]

  41. In Germany, 60% of collected textiles are sent for recycling [4]

  42. In Germany, 1.2 million tonnes of textiles were collected in 2018 [4]

  43. In Spain, 0.5 million tonnes of textiles were collected in 2018 [43]

  44. In Spain, 20% of collected textiles were recycled in 2018 [43]

  45. In Sweden, 0.3 million tonnes of textiles were collected in 2019 [44]

  46. In Sweden, 29% of textiles were recycled in 2019 [44]

  47. In Australia, textile waste generated was 0.9 million tonnes in 2018 [45]

  48. In Canada, textile waste generated was 0.5 million tonnes in 2018 [46]

  49. In Brazil, textile waste generated was about 1.2 million tonnes in 2017 [47]

  50. In South Africa, textile waste generated was about 0.6 million tonnes in 2018 [48]

Section 04

Policy, business practices, and economic indicators

  1. EU Textile Strategy target: make textiles on EU market durable, reusable, recyclable by 2030 [49]

  2. EU Extended Producer Responsibility (EPR) for textiles requirement is part of the EU proposal [49]

  3. EU Ecodesign for Sustainable Products (ESPR) framework covers textiles with digital product passport requirements for certain products [50]

  4. European Parliament adoption of textiles regulation is underway with key recycling and waste targets [51]

  5. Proposed EU target: ensure separate collection of textiles by end of 2025 [49]

  6. Proposed EU target: by 2030, 55% of textiles should be recycled [49]

  7. Proposed EU target: by 2030, 20% of textiles should be collected separately for reuse [49]

  8. UK government ambition: recycle or reuse all textiles by 2040 (end of 2040 target) [52]

  9. UK EPR for packaging and textiles; UK has consultation on textiles EPR covering costs for collection and recycling [53]

  10. France has extended producer responsibility schemes for textiles; CITEO/eco-organizations operate collection systems at scale [54]

  11. Germany’s VerpackG style EPR model exists; textiles have deposit and collection rules under dual system participation [55]

  12. In 2020, EU funding for textile circularity via Horizon 2020 and successor includes multiple projects under calls [56]

  13. European Commission Circular Economy Action Plan includes measures addressing textiles reuse and recycling [57]

  14. EU Commission impact assessment describes economic benefits of circular textiles, including reduced waste management costs [27]

  15. Microfibers washing contributes to pollution; policy includes measures to reduce shedding [49]

  16. Extended producer responsibility is expected to increase collection rates and recycling [49]

  17. US EPA notes textiles recycling challenges and that textiles are hard to recycle due to contamination and blends [1]

  18. US EPA estimates only 15% of textiles are recycled [1]

  19. Textile recycling businesses rely on commodity value of recyclates; reported market volatility affects demand [24]

  20. The Ellen MacArthur Foundation reports that only 1% of used clothing is recycled back into new clothing [58]

  21. EU targets include achieving high separate collection; the strategy calls for separate collection of textiles where feasible [49]

  22. The EU strategy aims for a market where waste is avoided and recycled content increases [49]

  23. The EU’s ESPR provides for digital product passports for relevant products including textiles [59]

  24. The EU’s Waste Framework Directive requires separate collection and improved recycling targets [60]

  25. Under the EU waste hierarchy, prevention and reuse are prioritized over recycling [60]

  26. In the EU, recycling targets for municipal waste are 55% by 2025, providing context for textiles [60]

  27. EIB supports circular economy investments including recycling infrastructure that can include textiles [61]

  28. The Ellen MacArthur Foundation states that the textile industry is linear with only about 12% reused/recycled [58]

  29. The Global Fashion Agenda reports that policy and regulation are drivers for increasing recycling rates in Europe [62]

  30. The OECD report cites that textile recycling faces economic barriers from low fiber prices and cost of sorting [24]

  31. Sorting and processing costs are a key barrier to scaling fiber-to-fiber recycling [24]

  32. Without policy, market incentives for recycling are weak; extended producer responsibility aims to address this [49]

Section 05

Recycling technologies, yields, and outputs

  1. Polyester monofilament recycled via melt-spinning is produced at pilot yields above 70% in some trials [63]

  2. Mechanical downcycling typically produces short fibers suitable for nonwovens [64]

  3. Chemical recycling routes for polyester can recover monomers (e.g., PTA/DMT) which can be repolymerized [65]

  4. Solvolysis of PET textile waste can produce high purity monomers in optimized conditions [66]

  5. Recovered cotton fibers can be reused in blending for new textiles [67]

  6. Thermal treatment can separate fibers and remove finishes to improve recyclability [68]

  7. Textile-to-textile recycling requires removing dyes and finishing chemicals to meet quality specs [69]

  8. Blended fabric recycling remains challenging; yield reductions occur due to incompatible polymers [2]

  9. Chemical recycling can handle blends better than mechanical recycling in some processes [70]

  10. Recycling feedstock preparation (sorting by fiber content) is critical for output quality [71]

  11. NIR sorting can identify polymer type for recycling at high accuracy levels (often >90% in deployments) [72]

  12. Dyestuff removal process efficiency determines regenerated fiber quality [73]

  13. Mechanical recycling process outputs commonly include 2-20 mm fiber lengths depending on shredding parameters [74]

  14. Recycling to nonwovens includes needle-punching and carding steps, yielding materials for insulation and wipes [75]

  15. Wet processing and purification steps are required for cellulosic fiber regeneration [76]

  16. Regenerated cellulose can be spun into viscose/rayon-like fibers depending on process chemistry [77]

  17. Hydrothermal pretreatment can improve fiber accessibility before dissolution in chemical recycling [78]

  18. Some PET glycolysis processes report conversion efficiencies above 90% for PET waste under optimized conditions [79]

  19. Catalysts used in chemical recycling impact both conversion rate and downstream purity; conversion targets often exceed 80% [80]

  20. Recycling plants can recover usable fibers after scouring and shredding; reported mass yields often around 60-80% depending on feedstock [81]

  21. Output from fiber recycling is typically lower grade; blending ratios such as 30-70% recycled fraction are common to meet strength requirements [82]

  22. Recycled polyester used in apparel commonly blends 10-30% recycled content to ensure performance [83]

  23. Mechanical recycling throughput in industrial lines can be several tonnes per day [84]

  24. Chemical recycling capacity in pilot plants is typically in the range of 1,000-10,000 tonnes/year [85]

  25. Sortation systems separate by fiber type to enable fiber-to-fiber recycling pathways [86]

  26. Textile-to-textile recycling depends on contamination removal; even small contamination can reduce spinning performance [87]

  27. For enzymatic recycling of cellulose, process yields can be limited by substrate accessibility; reported yields vary [88]

  28. In thermal depolymerization of synthetic blends, composition determines conversion to monomers [89]

  29. Pilot studies of textile-to-textile recycling show significant yield loss at every preprocessing step (sorting, cleaning, shredding) [90]

  30. Some steel shredders produce particle size distributions that correlate with downcycling level [91]

  31. Nonwoven recycling outputs often require 1-5 denier fibers; blends adjust denier to meet specs [92]

  32. Recycled fibers for insulation boards can be produced at densities around 30-150 kg/m3 depending on binder [93]

  33. Regenerated cellulose can be spun into fibers with similar fineness to virgin depending on process control [94]

References

Footnotes

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