Carbon Footprint In The Luxury Fashion Industry Statistics

The fashion industry’s primary hotspot is upstream production (fiber, yarn, dyeing/finishing) [1]

Increasing garment lifetime is consistently identified as a key lever to reduce carbon footprint [1]

Extending clothing use by 9 months can reduce its carbon footprint by 20–30% in some LCAs [2]

A study found that if customers extend the life of a garment by 50%, the global warming impact can drop substantially [3]

Apparel reuse and recycling depend on collection and sorting; global recycling rates into new textiles remain very low [4]

Under “take-back” schemes, only a portion of returned textiles can be recycled into new fibers due to contamination and mixed materials [1]

The average number of times a garment is worn before disposal has declined; reported averages as low as ~7–8 wears for fast fashion items [5]

“Use phase” can become more important when garments are used less; however, upstream production still dominates typical cradle-to-grave footprints [1]

Consumers overbuy due to low prices; overconsumption increases total production, leading to more emissions [6]

In a UK study, sorting and reuse are limited by infrastructure; only a subset of clothing is suitable for reuse [7]

UK clothing disposal was estimated at ~2.7 million tonnes in recent years, including reuse and recycling [8]

EU consumers disposed of significant quantities of textiles; estimates place textile waste at around 5.8 million tonnes per year (EU-27) in early 2010s [1]

The EEA notes that textiles are increasingly incinerated or landfilled when reuse/recycling is not available, contributing to emissions from waste treatment [1]

Incineration of textiles releases fossil carbon for synthetic fibers; carbon emissions depend on composition [1]

Landfill emissions of textiles include methane if conditions allow anaerobic decomposition [9]

IPCC default methane generation uses a time-dependent decay profile for degradable waste [9]

A common strategy is repair and alteration; durability reduces total required production (a reduction in upstream emissions intensity per wear) [3]

Luxury fashion often emphasizes higher durability/longer use compared with fast fashion; durability supports lower lifetime carbon per wear (qualitative but quantified in some cases) [10]

A report estimated that if the industry adopted circularity practices, it could reduce annual carbon emissions by hundreds of millions of tonnes by 2030 (range) [11]

Increasing sorting and collecting used textiles is necessary to raise recycling rates above current low levels [6]

Textile recycling limitations due to fiber blends reduce achievable recycling outputs [1]

In many corporate LCAs, “cradle-to-gate” excludes use and end-of-life; total carbon can be multiple times higher in cradle-to-grave when garments are discarded quickly [3]

The EU’s waste framework encourages separate collection to improve textile circularity, which reduces carbon by enabling recycling [12]

The EU Circular Economy Action Plan aims to make textiles more recyclable and reduce waste [13]

The EEA reports that EU waste collection and sorting limitations constrain textile recycling outcomes [1]

A key policy lever is extended producer responsibility (EPR) for textiles to increase collection and recycling [14]

The EU strategy for sustainable and circular textiles includes targets and monitoring measures aimed at improving reuse and recycling [14]

The EU strategy aims to reduce textile waste to landfill through higher reuse and recycling [14]

In 2021, global clothing and footwear were shipped worldwide at large volumes; growth drives production emissions [15]

Shipping intensity affects emissions; freight transport emissions scale with ton-kilometers [16]

The IMO indicates shipping emissions have been growing and are a significant share of global emissions [16]

Global apparel sector greenhouse gas emissions were estimated at 2.1 billion tonnes of CO2e in 2018 [6]

Fast fashion (global apparel) was estimated to account for 10% of global carbon emissions [6]

The fashion industry was estimated to produce 2 billion tonnes of CO2e per year [6]

In the EU, clothing and footwear consumption contributed about 5% of the EU’s total household consumption GHG footprint in 2015 [17]

The clothing consumption footprint per capita in the EU was about 4.7 tonnes CO2e per person in 2015 [17]

In the UK, clothing production and use emissions were estimated at 44 million tonnes CO2e per year (2019) [18]

In the UK, emissions from clothing consumption were estimated at 19.0 MtCO2e in 2019 [19]

The global textile sector contributes about 1.2 billion tonnes of CO2e annually (material production + manufacturing) [20]

A report estimated the production stage accounts for about 80% of a garment’s climate impact [1]

Life-cycle assessment literature indicates fiber production can account for ~50–70% of garment GHG emissions depending on fiber type [21]

Fashion’s upstream activities (fiber production, dyeing, spinning, weaving/knitting) were highlighted as major contributors to the industry’s climate footprint [3]

Textile and apparel global emissions were estimated at about 1.7 billion tonnes CO2e per year in a 2015 estimate [22]

Methane is a significant contributor to the climate impact of cotton cultivation due to nitrous oxide emissions from fertilizers [23]

Nitrous oxide emissions from agricultural soils are about 300 times more potent than CO2 over 100 years [24]

Over 100 years, global warming potential of methane is about 28–36 times CO2 depending on assessment [24]

The textile sector accounts for around 20% of industrial water pollution globally, which correlates with energy-intensive wet processing emissions [6]

In a European Environment Agency report, the textile sector is linked to energy use from wet processing, with key hotspots including spinning, dyeing and finishing, and garment manufacturing [25]

In a study, polyester (a fossil-based fiber) has the highest greenhouse gas emissions among common fibers when comparing cradle-to-gate [26]

Switching from virgin polyester to recycled polyester can reduce greenhouse gas emissions by about 30% for fiber production in some LCA studies [3]

Textile-to-textile recycling rates remain low globally (e.g., <1% of textiles are recycled into new textiles) [4]

In 2020, total global CO2 emissions from fossil fuels were ~34.8 GtCO2, used as a baseline in comparisons for fashion’s share [27]

The Global Carbon Project reports global CO2 emissions in 2019 at 36.8 GtCO2 [28]

Global apparel retail sales increased from $1.9 trillion (2010) to about $2.8 trillion (2018), driving more production and emissions [29]

Global apparel consumption increased by 63% between 2000 and 2014 per a cited study [30]

Average number of wears per garment fell from about 30 to 8 per year in some markets [5]

In an LCA, end-of-life treatment (incineration/landfill) contributes a smaller share than fiber production for many garments [31]

In a UK report, emissions from clothing consumption were estimated at 7% of household emissions [19]

In the EU, the carbon footprint of clothing and footwear consumption was estimated at around 100 MtCO2e in total [17]

Textile production is energy-intensive; garment manufacturing (sewing) contributes relatively less than upstream stages in cradle-to-gate LCAs [1]

The UNEP report indicates that each stage of the fashion lifecycle has carbon footprint contributions, reinforcing that fiber and manufacturing dominate [6]

The World Bank report highlights that textile production and consumption generate significant GHG emissions and waste [20]

The Ellen MacArthur Foundation estimates that the fashion industry would need structural changes to be circular, implying large emissions reduction potential [32]

A key figure in circularity discussions is that textile recycling rates are very low relative to the amount of textiles produced [4]

The EEA emphasizes that carbon hotspots occur upstream (materials and manufacturing) [1]

Carbon footprint comparisons often show that replacing virgin fibers with recycled lowers impacts in LCA models [3]

The IPCC states that CO2 remains in the atmosphere for centuries, meaning emissions today have long-term climate effects [33]

The IPCC states that climate impacts depend on cumulative CO2 emissions [33]

The IPCC notes that mitigation paths rely on reducing emissions across sectors, including industry and agriculture [34]

Global methane concentration in 2020 was about 1,866 ppb (context for methane-driven emissions) [35]

Atmospheric N2O concentration around 2020 was about 333 ppb (context for fertilizer-related emissions) [36]

The EEA text notes the importance of reducing textile waste generation to reduce emissions from waste treatment [1]

UNFCCC data indicates global CO2 emissions peaked in 2019 at 36.8 GtCO2, showing baseline for comparisons [28]

The Global Carbon Project reports CO2 emissions in 2021 at 37.0 GtCO2 (approx) [27]

A 2018/2019 report estimated that the fashion industry’s overall greenhouse gas emissions could be reduced by about 30% by switching to more sustainable materials and process changes [10]

McKinsey estimated that the fashion sector can reduce emissions by 44% by 2030 through a mix of changes [10]

A list of luxury brands’ science-based targets includes commitments covering Scope 1, 2, and many Scope 3 categories [37]

Burberry set a target to reduce absolute GHG emissions 46% by 2030 vs 2014 baseline (reported) [38]

Gucci set a target to reduce emissions by 50% by 2030 vs 2019 (absolute) per its climate plan [39]

Kering’s Science Based Targets include reducing absolute Scope 1 and 2 emissions by 50% by 2025 (vs 2015) and Scope 3 by 50% by 2025 (vs 2015) [40]

Louis Vuitton (LVMH) has a target to reduce product carbon footprint by 25% by 2023 vs 2015 (reported) [41]

Chanel set targets for reducing carbon emissions related to its value chain (scope includes emissions reduction milestones) [42]

Prada targets include emissions reductions across its value chain under sustainability reporting [43]

Hermes reports a reduction in carbon footprint per unit produced (absolute reductions reported in annual sustainability) [44]

Dior (LVMH) publishes environmental reporting including GHG emissions and climate actions [45]

Saint Laurent (Kering) reports climate initiatives and progress in its sustainability reporting [46]

Valentino Group sustainability reporting includes GHG emissions accounting and reduction plans [47]

Richemont publishes sustainability targets including emissions reduction [48]

Rolex sustainability reporting includes emissions and climate-related initiatives [49]

Tiffany & Co. (luxury) has climate commitments; disclosed targets in sustainability reports include GHG reduction goals [50]

Burberry’s ESG reporting includes annual Scope 1 and 2 emissions figures [51]

Kering reports Scope 1 and 2 and some Scope 3 emissions totals in annual Universal Registration Document [52]

LVMH publishes group-level Scope 1/2 and progress on climate targets in its sustainability reporting [53]

L’Oréal (beauty luxury adjacent) has a declared science-based target to reduce GHG emissions by 2030 (method referenced for luxury reporting) [54]

Many luxury brands report Scope 1 and 2 reductions due to renewable electricity procurement (market-based reductions) [55]

Kering reports progress on renewable electricity in operations contributing to Scope 2 reductions [40]

LVMH has a climate plan with quantified actions for energy and electricity in operations [56]

Prada reports renewable energy use and efficiency actions in sustainability reporting with quantified progress [43]

Burberry reports renewable electricity and emissions reduction efforts in its annual report [51]

Chanel sustainability reporting provides quantified GHG emissions and reduction initiatives [42]

Recycling a ton of polyester can avoid ~1.5 tonnes CO2e compared to virgin polyester production in some assessments [57]

Producing 1 kg of virgin polyester can emit roughly 3–4 kg CO2e (cradle-to-gate) [5]

Producing cotton has high land and fertilizer impacts; cotton cultivation can drive significant N2O emissions (nitrous oxide) [23]

Cultivating cotton typically requires substantial water; cotton water footprint is commonly reported around 10,000 liters per kg (varies) [58]

Dyestuff and dyeing processes are energy-intensive wet processes; dyeing and finishing are identified as key hotspots [1]

Creating a cotton garment involves spinning, weaving/knitting, dyeing, and finishing stages that drive emissions [25]

Leather production is emission-intensive; cattle raising is a major source of methane and nitrous oxide [59]

Common LCA estimates show leather’s climate footprint can be multiple times that of synthetic textiles per unit area [60]

A study reported that viscose/rayon can have lower GHG than polyester but higher than some cotton conditions depending on electricity and process [10]

Steel and aluminum hardware in luxury bags/jewelry can require high energy for production; aluminum requires ~14–16 MWh electricity per ton (primary) [61]

Primary aluminum production emits roughly 8–12 tonnes CO2 per tonne aluminum depending on electricity mix [62]

Tanning processes (chrome tanning) can contribute to GHG through energy use; chrome tanning is widely used in leather industry [63]

Fur farming contributes emissions mainly from feed production and manure; estimates vary but feed is a major driver [23]

Wool production emissions are linked to methane from sheep; enteric fermentation produces methane [64]

Enteric methane from ruminants is a major component of livestock GHG emissions globally [64]

Polyester fiber is produced from petroleum/natural gas feedstocks, leading to fossil CO2 emissions [65]

Nylon (polyamide) is also fossil-based and has significant cradle-to-gate carbon [66]

In LCAs of garments, fiber production typically dominates climate impacts compared to use phase [1]

The carbon intensity of electricity strongly affects manufacturing footprints in energy-intensive stages [67]

Europe’s grid electricity carbon intensity was around 0.25–0.35 kgCO2e per kWh in mid-2010s (varies) [68]

Polyester recycling “mechanical recycling” often has lower yield and quality constraints, limiting repeated recycling loops [3]

Recycling chemical processes can improve fiber quality but energy use varies by technology [3]

Cotton production yields vary widely by region, affecting per-kg footprints [23]

Polyester accounts for the majority of global fiber demand in recent years (e.g., ~60%), increasing fossil-based emissions [69]

Global cotton share of fiber demand has been lower than synthetics, contributing to differing emission profiles [69]

Viscose/rayon is typically produced from wood pulp using chemical processes (intense chemicals and energy) [1]

In 2017, the fashion industry used about 79 billion cubic meters of water globally (context for wet processes and energy) [6]

Life-cycle assessment is commonly used for carbon footprint calculation across stages (fiber-to-grave) [70]

ISO 14040 defines principles and framework for LCA used to measure environmental impacts like GHGs [71]

ISO 14044 specifies requirements and guidelines for LCA [72]

GHG Protocol Corporate Accounting and Reporting Standard is widely used for corporate emissions accounting [73]

GHG Protocol Scope 3 Standard provides calculation methods for value chain emissions [74]

The IPCC AR6 provides updated global warming potentials for CO2e calculations used in emissions estimates [75]

The EU Product Environmental Footprint (PEF) methodology defines product carbon footprint calculation approaches [76]

The European Commission’s PEFCR guidance for textiles provides category rules for carbon footprinting of textile products [77]

The World Business Council for Sustainable Development (WBCSD) and others publish apparel footprint guidance with GHGP calculations [78]

CDP discloses climate data including Scope 1/2/3 and targets in standardized questionnaires [79]

CDP’s Climate Change questionnaire requires reporting of GHG emissions (Scopes) [80]

The Science Based Targets initiative (SBTi) requires companies to set targets aligned with climate science including emissions reductions [81]

SBTi defines target types including absolute and intensity targets for Scope 1/2 and Scope 3 [82]

SBTi requires disclosure of emissions inventories and methodologies as part of target validation [81]

The Greenhouse Gas Protocol requires categorizing emissions into Scope 1, Scope 2, and Scope 3 [83]

The GHG Protocol Scope 2 Guidance establishes location-based and market-based reporting approaches [55]

The EU ETS covers emissions from certain sectors; methodology distinguishes direct emissions from energy-related, relevant to Scope 1/2 accounting [84]

Mandatory climate reporting in the EU under CSRD includes disclosures of GHG emissions for many companies [85]

The Task Force on Climate-related Financial Disclosures (TCFD) framework became widely used for climate risk disclosures including emissions metrics [86]

ISSB IFRS S2 climate-related disclosures require entity disclosure of Scope 1/2/3 greenhouse gas emissions as relevant [87]

GHG Protocol Scope 3 categories include upstream and downstream activities; textiles span multiple categories (purchased goods, transport, use, end-of-life) [74]

The Scope 3 Standard requires reporting for Category 1 (purchased goods and services) and Category 11 (use of sold products) when relevant [74]

The Scope 3 Standard includes Category 11 as use of sold products, which for garments depends on laundering and wear time [74]

Scope 3 Category 12 covers end-of-life treatment of sold products, relevant to textile waste emissions [74]

The PEFCR for textiles provides how to compute product carbon footprint with category rules [88]

JRC’s eLCA tool supports environmental footprint assessment consistent with PEF methodology [88]

The EU PEF is implemented via specific PEFCRs which include calculation steps and requirements [89]

ISO 14067 specifies requirements and guidelines for quantifying and communicating the carbon footprint of products [90]

ISO 14064 provides quantification and reporting of GHG emissions reductions and removals [91]