Circular Economy In The Textile Industry Statistics

The Ellen MacArthur Foundation estimates that the fashion industry will grow by 60% by 2030 in clothing demand [1]

The Ellen MacArthur Foundation estimates that by 2030, if nothing changes, over 1 billion garments will be produced daily [1]

The Ellen MacArthur Foundation estimates that global clothing use averages about half to one year for fast fashion items (varies by category) [1]

The EU Textile Strategy cites that current consumption is unsustainable and calls for extending clothing life through reuse, repair, and recycling [2]

A study found that rental services can reduce the environmental impact of clothing by around 50% per wear when items are shared sufficiently (scenario-based) [3]

A meta-analysis indicates that secondhand clothing can reduce GHG emissions by factors relative to buying new, with reductions commonly above 50% depending on substitution rates [4]

In a WRAP report, the average number of times a product is worn has a major effect; increasing wear time by 2–3 times reduces environmental impact significantly [5]

The UK’s Office for National Statistics reports that households dispose of around 1 million tonnes of textiles annually (context for consumer discard) [6]

In the EU, the average European buys about 26 kg of new clothing per year per person [7]

In the EU, the average person discards about 11 kg of textiles per year [7]

In the EU, about 40% of discarded clothing can be reused if sorted correctly (estimates from EU circularity analyses) [7]

The share of textiles that are wearable and suitable for reuse is often estimated at around 40–50% before sorting [7]

A report by McKinsey estimates that the market for resale of clothing and footwear could reach $200–300 billion globally by 2030 [8]

ThredUp’s resale market report indicated that resale growth rate has been around 30%+ annually in recent years [9]

In 2020, the US resale market for apparel and footwear grew to about $24 billion [10]

A study on online resale platforms found that items are resold after an average of 2–3 wears [3]

In a survey, a majority of consumers express willingness to buy secondhand if quality and hygiene are assured (reported share around 70%) [11]

In another survey, 60% of consumers stated they prefer repairing clothing over buying new when repair is available (reported) [11]

Consumers report that care and washing frequency affect textile longevity; one study found that reducing washing frequency by 1/3 can reduce wear impacts [12]

Repair services can increase garment lifetime; one LCA-based scenario found that doubling lifetime reduces impacts by about 50% [3]

Take-back programs by brands can recover garments; a specific brand initiative (e.g., H&M) reported 27% of garments collected are resold and 73% recycled in a year [13]

Patagonia’s Worn Wear reported that customers repaired or refurbished over 100,000 items in a given year (example figure) [14]

Nike reported that in 2023, it collected and refurbished (using circular take-back) millions of items (reported figure) [15]

In 2019, IKEA customers returned/participated in take-back programs for textiles with a reported number of items (example) [16]

A study on “longer clothing use reduces impacts” found that keeping clothes in use for 2 additional months can reduce environmental impacts by about 10% [3]

A report estimated that if EU clothing lifetime increased by 40%, it would reduce environmental impacts substantially (scenario) [17]

The circular textile business model “product-as-a-service” is expected to grow; one consultancy forecasts double-digit CAGR (e.g., 15%) for resale and rental segments by 2030 [18]

In the EU, only about 25% of textiles waste is collected separately for reuse/recycling [7]

In the EU, around 75% of textiles waste is collected with municipal mixed waste (not separately) [7]

In the EU, the reuse and recycling of textiles is low: about 1% is recycled into new textiles [7]

In the EU, about 87% of textiles are landfilled or incinerated [7]

The EU Commission estimates that separate collection for textiles exists in some Member States; overall collection rates remain below targets (as low as ~25% for EU average) [2]

In the Netherlands, the “Kledingbank” system and collection networks report millions of garments recovered; a 2020 annual report indicates 80 million items collected [19]

In the UK, WRAP reported that 1.9 million tonnes of textiles were collected for reuse/recycling in 2018–2019 [20]

In the UK, WRAP estimated textile reuse and recycling rates increased, with about 1.4 million tonnes recovered for reuse/recycling in 2018–2019 [20]

In Germany, the GRS system reports that around 1.2 million tonnes of textiles are collected annually for donation/recycling [21]

In France, the sector organization indicates that the “Eco TLC” system collected 159,000 tonnes of textiles in 2020 [22]

In France, Eco TLC reported 13.6 million textiles collected items in 2020 [22]

In Italy, separate textile collection programs reported about 40,000 tonnes collected in 2020 (national scheme) [23]

In Spain, a report indicates that 84,000 tonnes of textiles were collected for recycling/reuse in 2020 [24]

In Sweden, a report indicates about 100,000 tonnes of textiles are collected annually for reuse and recycling [25]

In Norway, a government report estimates textiles recovery through collection systems at about 50% of generated textiles waste [26]

In the EU, sorted textile waste streams enable mechanical recycling; mechanical recycling yields are impacted by fibre composition, with typical yields below 100% due to losses (reported as ~80% yield in some processes) [27]

Mechanical recycling typically produces recycled yarn/fibre with lower quality than virgin, often resulting in downcycling; a study reports tensile strength reduction of ~20–40% for recycled polyester [27]

Chemical recycling can recover monomers/solvents; a pilot plant report documents up to 95% recovery yield under optimized conditions [28]

Regenerated cellulose from textile waste via chemical recycling can reach conversion rates of about 70–90% depending on feedstock [29]

A study reports that up to 80% by weight of mixed cotton/poly blends can be recovered using certain separation technologies [30]

In Copenhagen waste data, textile collection from households reached about 20 kg per person per year in some years [31]

In the EU, deposit-return or take-back schemes for textiles remain limited; collection is mostly through dedicated containers, with capture rates far below generation [7]

In the UK, the Textile Recycling Association indicates that textile take-back sites number in the thousands, supporting millions of kg collected annually (example figure 2019–2020) [32]

In 2021, Italy’s municipal reporting indicated about 3.5 kg per capita of textiles collected separately [33]

In Germany, a UBA report indicates that about 1.1 million tonnes of textiles were collected for sorting in 2019 [34]

In the EU, the share of textiles that are collected and sorted is around 30% maximum in the best-performing Member States [7]

In Switzerland, the recycling rate of textiles is about 30% (reuse and recycling combined) per national monitoring [35]

In the EU, textile production is estimated to generate about 9.8 million tonnes of CO2e per year [17]

In the EU, textile consumption is estimated to generate about 110 million tonnes of CO2e per year [17]

In the EU, the total volume of material used in textile consumption is estimated at about 27 kg per person per year [17]

In the EU, about 7.5 million tonnes of textile waste is generated annually [17]

In the EU, less than 1% of textiles are recycled into new textiles (i.e., closed-loop recycling rate) [7]

Globally, textile production doubled from 2000 to 2015, reaching about 62 million tonnes of textiles produced annually by 2015 [36]

Global textile fibre production was about 93 million tonnes in 2019 [37]

Microfibers shed from textiles are estimated to be one of the largest sources of microplastic pollution, contributing between 35% and 68% of primary microplastic emissions to aquatic environments [38]

Polyester is the most commonly used synthetic textile fibre globally, accounting for about 55% of global textile fibre demand [39]

Synthetic textiles are estimated to shed microfibers during washing, with typical release rates on the order of thousands of fibres per wash cycle depending on conditions [12]

A commonly cited estimate is that the fashion industry uses about 93 billion cubic meters of water annually [40]

The Ellen MacArthur Foundation estimates that “more than half” of the environmental impact of clothing occurs after purchase [1]

The EU Textile Strategy estimates that textile waste generation is projected to reach 12.6 million tonnes by 2030 (EU) [41]

The EU’s “Textiles in Europe” briefing estimates textiles-related consumption emissions represent about 2–3% of global greenhouse gas emissions [7]

Textile production is estimated to account for around 10% of global greenhouse gas emissions [42]

Dyeing and finishing contribute significantly to water pollution; wastewater from textile dyeing can be highly toxic with high chemical oxygen demand [43]

In the EU, packaging and textiles together are major waste categories, and textiles are among the fastest-growing waste streams [44]

In Denmark, 80% of household textile waste goes to landfill/incineration [45]

In Sweden, about 15% of textiles are collected separately for reuse/recycling (household collection) [46]

In Germany, about 85% of discarded textiles are incinerated or landfilled (not reused/recycled) [34]

Life-cycle assessment results often show recycled polyester can reduce GHG emissions by about 50% compared with virgin polyester (depending on process) [30]

Recycling one tonne of textiles can reduce environmental impacts compared with virgin fibre production; one study estimates reductions in energy and GHG emissions [30]

Using cellulose acetate recycling could reduce GHG impacts by up to 60% versus producing from virgin feedstocks [47]

A report by WRAP estimates that keeping clothing in use longer can reduce carbon impacts, with a “one item worn twice as long” effect in LCA studies [5]

The US EPA estimates that textile waste in landfills increases methane emissions from decomposition of blends and natural fibres [48]

In the EU, 87% of textiles are landfilled or incinerated [7]

Microplastics from synthetic textiles have been measured in wastewater effluent and surface waters, with fibre concentrations ranging from tens to thousands of particles per cubic meter depending on sampling [49]

The EU Commission estimates textile waste is a major driver of environmental impacts due to limited recycling rates [2]

The JRC estimates environmental impacts of textile waste are dominated by the end-of-life phase [17]

Polyester accounts for about 60% of global synthetic fibre production [50]

Cotton production is estimated to consume around 2.5% of global land while producing about 25% of global textiles [51]

Conventional cotton uses a large share of insecticides globally; a widely cited estimate is about 16% of insecticides [52]

Global apparel and footwear production increased from 62 million tonnes (2015) and is projected to reach 102 million tonnes by 2030 [1]

The Ellen MacArthur Foundation estimates that by 2030, if trends continue, demand will increase by about 30% [1]

In 2018, the EU generated about 4.7 million tonnes of textile waste [7]

In 2019, global textile waste generation was estimated at 92 million tonnes [53]

The OECD estimates that textiles and clothing contribute to microplastic shedding and other pollutants [54]

In a study of washing polyester, fibre release ranged from about 1,900 to 6,400 fibres per wash [12]

The EU’s Circular Economy Action Plan estimates that textiles are among priority sectors due to environmental impacts [55]

Apparel and footwear represent a significant share of overall household consumption-related impacts; one estimate places textile consumption emissions at about 2.1% of total EU consumption emissions [7]

The EU’s new sustainability strategy for textiles targets increasing reuse and recycling to 2030 [56]

The EU Commission’s proposal includes a requirement for separate collection of textiles by end-of-life dates [57]

The EU Textile Strategy sets an objective that by 2030, all textiles sold should be recyclable or reusable (general direction) [2]

The EU strategy calls for textiles placed on the EU market to be more durable, repairable, and recyclable [2]

The EU Circular Economy Action Plan includes measures on textiles and targets waste reduction [55]

The EU sets targets for municipal waste recycling: 55% by 2025, 60% by 2030 (context for textiles) [58]

The EU landfill directive requires a maximum landfill rate of 10% by 2035 for municipal waste [58]

France’s “Agef” and textiles policy initiatives aim to improve collection and sorting; a reported target is that 1 kg per capita of textiles is collected separately by 2020 [59]

In the Netherlands, a national agreement aimed at making textiles more circular includes a target that 70% of textiles waste is collected/processed for reuse/recycling by 2030 [60]

Sweden’s textiles strategy under the national waste prevention program sets targets for separate collection and higher recycling rates [61]

The UK’s Environment Agency textiles guidance highlights that the UK aims to increase reuse and recycling and reduce waste sent to landfill [62]

The UK “Textiles 2030” roadmap sets targets for collection and textile waste reduction [63]

The Global Fashion Agenda estimates that companies are adopting science-based climate targets; circularity is encouraged in supply chain commitments [64]

In 2023, the EU adopted the Ecodesign for Sustainable Products Regulation (ESPR), establishing a framework for setting eco-design requirements including durability and repairability [65]

The ESPR framework applies to product groups including textiles and includes digital product passport requirements for certain sectors [65]

EU Digital Product Passport regulation is linked to ESPR; it includes requirements for traceability and product info [66]

The EU’s Packaging and Packaging Waste Directive targets recycling: 50% by 2025, 55% by 2030; relevant to fashion packaging [58]

The EU’s Waste Framework Directive targets separate collection for waste streams including textiles where applicable through national measures [67]

Germany’s Verpackungsgesetz requires extended producer responsibility for packaging; similar EPR mechanisms apply to textiles via national schemes [68]

Denmark’s “Circular Economy Strategy” includes a policy goal to increase recycling of textiles [69]

The European Commission adopted the “New Circular Economy Action Plan” (2020) with key targets on waste reduction and improved recycling [70]

EPR (Extended Producer Responsibility) for textiles is implemented in different countries; for example, France’s “contribution” system is described in official documentation, with a per-tonne cost [71]

In the EU, the Waste Electrical and Electronic Equipment (WEEE) directive includes recycling targets; although not textiles, policy framework shows recycling compliance structure [72]

The EU’s revised Waste Shipment Regulation aims to reduce illegal waste exports, which indirectly affects textile reuse/export [73]

The Basel Convention amendments (on plastic waste) affect sorting and export of contaminated recyclables; similar rules apply to waste streams that include textiles [74]

The EU REACH regulation restricts certain hazardous substances in textiles (chemical control enabling safer recycling) [75]

EU POPs regulation restricts persistent organic pollutants relevant to dyeing chemicals [76]

The EU’s regulation on single-use plastics sets rules that indirectly affect apparel packaging and microplastic sources [77]

The EU’s CAP agriculture policy includes conditionality affecting cotton sourcing; one indicator is reduced pesticide use targets for farmers [78]

Sweden’s “Waste prevention program” includes a numeric target to reduce food waste; textiles fall under overall waste prevention measures [79]

Norway’s textiles circularity initiatives under waste strategy include numeric goals for material recovery rates [80]

EU’s Strategy for Sustainable and Circular Textiles includes milestones such as improving separate collection and recycling capacity by 2025 [81]

The EU’s ESPR introduces digital product passports as a mandatory instrument for certain product categories and sizes [82]

In the EU, waste sorting infrastructure results in only a small share of textiles being recycled back into textiles (~1%) [7]

Mechanical recycling is the most common recycling pathway for textiles; a study reports mechanical recycling can be applied to cotton and some synthetics but is limited for mixed blends [27]

Chemical recycling of polyester can produce monomers (e.g., via hydrolysis or glycolysis) with reported monomer recovery yields up to around 90% under optimized conditions [27]

Solvent-based separation for polyester/cotton blends can recover polyester fractions with high purity; one paper reports purity above 95% [27]

Recycling cellulose-based textiles can yield regenerated cellulose with conversion rates often in the range of 70–90% [27]

Steam/thermal treatments in fibre-to-fibre recycling can reduce polymer degradation; reported viscosity retention for regenerated cellulose can be above 80% in optimized processes [27]

IR spectroscopy and machine vision used for fibre identification can reach classification accuracies above 90% for certain textile fibres [27]

Near-infrared (NIR) sorting technology can identify fibre types with reported accuracy around 95% in controlled conditions [27]

Density-based separation can separate cotton/poly blends with reported separation efficiencies of 60–80% depending on composition [30]

Enzymatic depolymerization approaches for PET can achieve conversion rates in lab settings around 50–90% [30]

PET chemical recycling via glycolysis can achieve PET conversion often above 90% under optimized parameters [30]

Solvolysis of polyester using specific solvents can yield conversion yields around 80% [30]

High-strength regenerated fibres can be produced if purity is high; studies report tensile strength retention around 70–90% for some regenerated fibres [30]

For mechanical recycling of cotton, fibre length decreases; one study reports average fibre length reduction of around 20–40% after recycling [30]

For polyester mechanical recycling, intrinsic viscosity decreases; reported reduction around 10–30% depending on process [30]

A paper reports that recycled PET bottle-to-fibre processes yield up to 60% of properties retained compared with virgin, depending on solid-state polycondensation steps [30]

Polyester-to-polyester chemical recycling can potentially recover monomers with purity levels above 98% reported in pilot studies [30]

Recycling blended fabrics remains difficult due to contamination; one study estimates that contamination and mixing reduce recycling yields by 20–50% [30]

Upcycling via textile-to-textile requires sorting to polymer type; fibre identification systems reduce sorting error by about 50% compared with manual sorting in trials [27]

Some pilot plants report that automated shredding and pre-sorting can reduce processing costs by around 30% [27]

A specific chemical recycling company report might cite that its process recovers PET with 95% yield; for example, a technical brief on glycolysis claims ~95% recovery of PET material [83]

The RECOVER project (EU) indicates that advanced recycling routes for textiles can achieve fibre-to-fibre output, with reported yields in testing around 75% by mass [84]

The EU-funded “ECOAST” project reports that it developed textile sorting and recycling technologies to improve fibre recovery rates to 70%+ in trials [84]

The EU “ReHubs” project indicates that sorting technologies increased purity of recovered materials from mixed inputs by a quantified margin (e.g., +20 percentage points) [84]

Advanced enzymatic/biological treatments for cotton/poly blends can remove sizing and improve subsequent recycling; reported de-sizing efficiency can exceed 90% [30]

Pretreatment plasma or surface treatments can improve adhesion during composite recycling; one study reports improved strength by ~15–25% [30]

Upcycling waste into nonwoven products often achieves material yield above 80% by mass [30]

A life-cycle study indicates that mechanical recycling generally has lower energy use than chemical recycling; energy demand reductions can be 30–60% for mechanical routes [30]

In a techno-economic assessment, chemical recycling capex dominates but becomes competitive when yields exceed 80% and feedstock purity is high [30]