The Home Textile Waste Problem: What U.S. and European Data Reveal

A research report of home textile consumption, waste and prevention in Europe and the United States

Research Report | Analysis of official U.S. and European data | October 7, 2026

A linen tablecloth sewn in Europe and shipped to an American home connects two different parts of the textile economy. Decisions about materials, cutting and finished stock are made in Europe, while the product’s useful life and eventual disposal may take place in the United States. Understanding the wider waste problem requires looking at both ends of that journey.

This research review brings together official data on household linens, textile consumption, unused stock and waste management. It examines what the figures reveal, where their limits lie and which production and purchasing decisions can address avoidable waste. The central finding is that better recycling needs to be accompanied by longer product use and measures that prevent unnecessary waste before it reaches a collection system.

The European and American figures answer different questions. EU data provide context for consumption, resource use and production practices; U.S. data show the scale and disposal routes of textile waste in the consumer market examined here. They do not track the same products across the Atlantic or establish that European-made textiles account for a particular share of American waste.

Household linen waste in the United States has more than doubled

EPA estimates show that waste from towels, sheets and pillowcases increased from 710,000 U.S. short tons in 1990 to 1.52 million in 2018. That is a rise of approximately 114%, with 810,000 additional short tons entering the measured waste stream. The category gives household linens a distinct place in a discussion often dominated by clothing. [1]

Figure 1. Household linen waste generated and landfilled in the United States. Source: EPA; growth calculated from the published values. [1]

Landfilled waste in this category rose from 490,000 to 1.03 million short tons over the same period, an increase of approximately 110%. The landfill share edged down from about 69.0% to 67.8%, but the quantity sent there more than doubled. This distinction matters: a small improvement in the percentage diverted from landfill can coexist with a much larger volume of discarded material. [1]

Table 1. Selected years for U.S. towels, sheets and pillowcases, in thousands of U.S. short tons. ¹Combustion with energy recovery. EPA labels the recovery row “recycled” and describes the 2018 quantity as export or recycling. [1]

Year	Generated	Recycled or exported	Combusted¹	Landfilled
1990	710	120	100	490
2000	820	140	130	550
2010	1,290	220	190	880
2018	1,520	240	250	1,030

The recovered quantity also increased, from 120,000 to 240,000 short tons, but its share fell slightly, from approximately 16.9% to 15.8%. More material was being recovered in absolute terms, yet recovery did not keep pace with the growth in waste. These calculations show why both tonnage and percentage shares are needed to assess progress. [1]

The series does not explain the increase by itself. Population growth, purchasing volumes, product weight, replacement habits and the length of time products stay in use may all affect aggregate waste; these figures do not separate their contributions. They therefore cannot establish that the average American household discards twice as much linen or that individual products last half as long.

Landfill remains the main endpoint in the national data

The household-linen pattern resembles the wider textile waste stream. EPA recorded 17.03 million U.S. short tons of textile material in municipal solid waste in 2018, up approximately 79.6% from 9.48 million in 2000. Of the 2018 total, 11.30 million short tons were landfilled, 3.22 million combusted with energy recovery and 2.51 million recycled. [2]

Figure 2. Waste pathways in 2018. The household-linen category is part of the broader textile stream, so the two totals must not be added together. [1] [2]

For towels, sheets and pillowcases specifically, 250,000 short tons were combusted with energy recovery and 240,000 were exported or recycled. Together with landfill, combustion accounted for approximately 84.2% of this category’s waste. Energy recovery is a different outcome from keeping fabric or fibers available for further material use, and the recovery figure does not establish how much became new household textiles. [1]

These are historical figures: 2018 remains the latest comprehensive EPA national reporting year as of September 2026. A 2024 Government Accountability Office review identified limited textile-waste data, fragmented collection and sorting, and technical and economic barriers to recycling. The EPA series is consequently a useful national baseline, not an estimate of today’s waste volumes. [3] [4]

The household category covers towels, sheets and pillowcases made from different materials, not just flax linen, and does not represent every type of home textile. EPA also excludes reuse that happens before products enter its measured waste stream. Donations and secondhand circulation should therefore not be read as missing percentages that can simply be added to the chart. [1] [2]

Home textiles carry a substantial footprint before disposal

In Europe, household textiles form a significant part of consumption. The EEA’s published summary estimates approximately 19 kg of clothing, household textiles and footwear per EU resident in 2022, including about 7 kg of household textiles. Total apparent consumption was approximately 8.5 million metric tonnes. [5]

Figure 3. Rounded values from the EEA’s 2025 briefing. The indicator excludes carpets and industrial or technical textiles. [5]

“Apparent consumption” is calculated from production plus imports minus exports, rather than by counting individual purchases. It describes an estimated material flow into the market and does not mean every resident personally bought that weight of new products. Even with that qualification, the household-textile category is large enough to merit attention alongside fashion. [5]

The environmental pressures associated with these products arise well before disposal. The EEA estimates that the upstream supply chains for textiles purchased by EU households in 2022 generated around 159 million metric tonnes of greenhouse gas emissions, expressed as CO₂ equivalent, and used approximately 234 million tonnes of primary raw materials. Those totals cover clothing, footwear and household textiles together. [5] [6]

Table 2. Modeled upstream footprints, 2022. Blue water refers to consumed surface water and groundwater, excluding rainwater. Source: EEA. [6]

Supply chain indicator	Estimated amount per EU resident
Greenhouse gas emissions	355 kg CO₂ equivalent
Primary raw materials	523 kg
Blue water consumption	Approximately 12 m³
Land use	323 m²

These figures describe different pressures and cannot be added into a single environmental score. The raw-material estimate, for example, covers resources used across the supply chain rather than the weight of the finished textile alone. The estimates are modeled and are best read as indications of scale, rather than precise measurements of every product’s production history. [6]

Their geographic meaning is equally important. The figures concern products consumed in the EU, with much of their production impact occurring outside Europe; they are not a footprint of European factories alone. A Lithuanian-made tablecloth shipped to the United States cannot be assigned these averages, nor does this dataset compare linen with cotton or synthetic alternatives.

The broader implication is that discarding a finished product also wastes the opportunity to benefit from resources already invested in making it. Longer use can spread that production burden over more occasions of service, but the net environmental effect still depends on care, replacement and what new purchases are actually avoided. A product-specific assessment is needed to quantify those effects.

Separate collection does not guarantee reuse or recycling

The EU generated an estimated 6.94 million metric tonnes of textile waste in 2022, around 16 kg per person. The EEA reports 11.1 kg per person outside separate collection and 4.6 kg separately collected from households and economic activities. The rounded figures do not exactly reproduce the reported total, and their source coverage needs to be kept in view. [7]

For household textile and shoe waste specifically, the average capture rate across EU countries was just under 15%. This is an average of national capture rates, not a calculation obtained by dividing the broader 4.6 kg collection figure by total waste. It indicates that household collection systems were capturing only a limited share, with substantial differences between countries. [8]

The first loss of opportunity happens when textiles enter mixed household waste. They are then managed as residual waste, typically heading toward landfill or incineration, rather than being assessed for reuse or recycling. Keeping suitable textiles separate preserves those options, although it does not guarantee that either will happen. [7] [8]

A second loss occurs after collection. The EEA reports that around a quarter of separately collected textile waste treated within the EU still went to landfill or incineration; including textiles in mixed household waste, it estimates a disposal share of approximately 73% in 2022. These figures describe different populations of material and should not be multiplied together as if they were stages in one measured flow. [9]

The practical lesson is that collection volumes alone are an incomplete measure of circularity. Information about sorting, the condition of collected goods and their subsequent treatment is also needed. A growing collection system can improve access while still struggling to find useful destinations for some of the material it receives.

Used textile exports move the question beyond Europe

The EU exported more than 1.44 million metric tonnes of used textiles in 2025. Asia received 48% and Africa 43%, leaving approximately 9% for other destinations; these figures describe exports of used textile articles, not new European products sold to American households. The two trade flows should not be confused. [10]

Exported textiles may be reused, recycled or re-exported, while some end up dumped or burned. The EEA highlights limited information on quality and final destinations, so the exported tonnage cannot be treated as an equivalent quantity successfully recycled. Export is a movement between markets, not a verified end use. [10]

This helps explain why the location of a collection bin is only part of the story. Once goods enter international sorting and resale markets, their eventual use depends on condition, demand and the receiving system’s capacity. A credible account of textile recovery therefore needs to follow outcomes beyond the point of collection.

Some textiles become waste before their first use

The EEA estimates that 4% to 9% of textile products placed on the European market are destroyed before use. Applying this range to 2020 consumption produces an estimated 264,000 to 594,000 metric tonnes. Unlike worn-out household textiles, these finished goods reach disposal without first delivering their intended service. [11]

Figure 4. The EEA’s estimate uses limited research on returned and unsold textiles. It is not a measured 2026 total or a rate established specifically for household linen. [11]

The range is deliberately wide because open data on returned and unsold products are limited and the underlying studies differ. Choosing its midpoint and presenting that as a measured annual total would imply more certainty than the evidence supports. The estimate is nevertheless useful for showing that waste prevention must include finished stock that never reaches a user. [11]

Production planning is one place to intervene. Manufacturing many sizes or colors in advance can leave businesses holding stock for which demand does not materialize; producing closer to confirmed demand can reduce exposure to that particular problem. It does not eliminate cutting waste, defects or canceled orders, and it is not automatically proof of a lower overall footprint.

Returns are related but require separate interpretation. The EEA’s online return estimates concern clothing, so applying them to tablecloths, towels or bedding would overstate what is known. For cross-border home-textile orders, the defensible priority is to reduce avoidable mismatches through accurate information, without assigning a generic carbon saving to every return avoided. [11]

Policy is expanding responsibility for textile waste

Europe and individual U.S. states are putting more emphasis on collection and producer responsibility. Extended producer responsibility, often shortened to EPR, brings businesses placing products on a market into the financing or organization of their end-of-life management. It addresses the cost of collection and treatment, rather than leaving the entire responsibility with households or public waste services. [13] [14] [15]

Table 3. Selected policy milestones, checked September 30, 2026. Implementation details, company definitions and exemptions vary by scheme.

Market and milestone	What changes
Massachusetts November 1, 2022	Textiles banned from disposal or transport for disposal, subject to exemptions. [12]
European Union January 1, 2025	Separate collection of textile waste required. [13]
European Union October 16, 2025	Revised Waste Framework Directive enters into force, requiring textile producer responsibility schemes. Covered categories include bed, table, toilet and kitchen linen; schemes are due in 2028. [13] [14]
California July 1, 2026	Covered producers required to join the approved producer responsibility organization. Products include tablecloths, napkins, towels and bedding; full program implementation is scheduled for 2031. [15]
European Union July 19, 2026	Large companies prohibited from destroying unsold apparel, clothing accessories and footwear, subject to exceptions. Medium-sized companies follow in 2030; this is not a blanket ban covering all home textiles. [16]

The EU’s inclusion of bed, table, toilet and kitchen linen is relevant to home-textile producers, as is California’s express coverage of tablecloths, napkins, towels and bedding. These products cannot be assumed to sit outside textile policy simply because they are not clothing. At the same time, the scope of the EU’s unsold-goods destruction ban is narrower than its textile EPR framework. [14] [15] [16]

The dates also describe different stages. A producer-registration deadline does not mean a statewide collection and recycling system is already fully operating, and an EU directive’s entry into force is distinct from national implementation. California’s timetable illustrates the gap between joining an organization and full program delivery. [13] [15]

For companies selling internationally, production location alone does not determine which obligations apply. Product definitions, market placement, company size and sales arrangements matter, and specific duties must be checked against the relevant rules. The broader policy direction is clear: textile recovery is becoming an issue businesses need to consider when designing products and managing their route to market.

How Thing Stories applies prevention in production

Thing Stories produces home textiles in Lithuania and sells to U.S. households. Its reported practices provide a small-business example of decisions made before products reach a waste system. They illustrate approaches to prevention, rather than independently measured reductions in waste, water use or carbon emissions.

Matching finished stock to demand

The company reports sewing a substantial share of products in response to customer orders and keeping limited finished stock. This reduces the need to decide every finished size and quantity before a customer has chosen a product. It addresses the risk of surplus finished inventory, although fabric purchasing and production still require planning.

The distinction between fabric stock and finished stock matters. Holding fabric that can be used for different orders may leave more production options open than holding a finished item in a particular size. Demonstrating the actual waste benefit would require records of orders, unused stock and disposal over time, which this research review does not provide.

Using offcuts and explaining fabric treatment

Thing Stories reports using larger linen offcuts for smaller items, including pouches, cloths and packaging bags, and narrow remnants for parcel ties. Giving a usable remnant another purpose can improve material use within the workshop. It should be described as offcut reuse, rather than evidence that production creates no waste.

For selected thicker table linens, the company reports using non-prewashed fabric, omitting that additional processing stage before sale. Other products are treated differently. This removes a particular factory step, but does not establish the product’s lifetime water or energy savings, since customer care and later washing also matter.

Clear sizing and care information is essential to making that choice useful for customers. The company’s guidance indicates that some non-prewashed linen may shrink by up to approximately 5%, mainly in length. Customers need to consider the relevant product’s guidance when choosing the dimensions they will need after washing.

Helping customers choose and keep suitable products

The business also provides guidance on dimensions, colors and suitability to help avoid ordering mistakes. For a product traveling from Lithuania to the United States, a mismatch can create additional handling and transport. The size of any environmental saving from avoiding that movement depends on the shipment and what happens to the item afterward.

Where appropriate, the company may suggest gifting an unwanted but usable item, without replacing applicable return rights. That can keep a product in service if the recipient needs it, but the benefit cannot be assumed merely because another item is purchased. Continued useful service is the relevant outcome.

Thing Stories reports using OEKO-TEX STANDARD 100 certified fabrics and threads, alongside recycled paper and FSC-certified paper products in parts of its packaging. STANDARD 100 concerns testing for harmful substances; it does not measure a textile’s carbon footprint. Certified components and packaging choices should therefore be described precisely, without implying that every finished product is certified or the whole business has no environmental impact. [17]

What the findings mean for households and producers

For households, the first opportunity is to choose textiles that meet a real need and fit the intended use. Checking dimensions, likely shrinkage and care instructions before ordering reduces the chance of acquiring something unsuitable. Durability is valuable when a product is actually kept in regular service, rather than replaced while it remains functional.

Care, repair and reuse influence what happens next. A textile that no longer suits one room may still serve elsewhere or be passed to someone who needs it, while a damaged item may have a practical second use. These choices depend on condition and suitability; the research review does not establish a universal lifespan for every household textile.

When an item can no longer be used, local acceptance rules matter. Textile collection is the entry point to sorting and possible recovery, and different programs accept different items and conditions. Consumers should check the collector’s guidance instead of assuming every textile belongs in ordinary household recycling.

For producers, the evidence points to decisions about stock, fabric use and product information as well as disposal arrangements. Keeping records of finished goods left unsold, cutting remnants reused and avoidable returns would make future progress easier to assess. Such measurements can connect a credible production story with evidence of what changed in the business.

The combined findings show why recycling capacity and waste prevention need to develop together. Better recovery can improve the destination of discarded material, while more careful production and longer use can reduce the volume requiring that destination. Neither a collection claim nor a material label alone answers the full question of how a home textile is made, used and eventually managed.

Methodology and data limits

This secondary-source study was reviewed on September 30, 2026, using EEA, EPA, GAO and official policy sources. European and U.S. totals are not compared as a performance ranking because their years, coverage and units differ: EU data use metric tonnes, while EPA reports U.S. short tons. The research review is a synthesis of public evidence, not a new survey or product lifecycle assessment.

EPA figures cover municipal solid waste rather than all industrial textile waste, and pre-waste reuse is outside the measured generation totals. Growth is calculated as (later value ÷ earlier value − 1) × 100, and pathway shares as pathway tonnage ÷ total generation × 100. For example, (1,520 ÷ 710 − 1) × 100 gives household-linen waste growth of 114.1%, rounded to 114%.

The EU consumption graphic consistently uses the rounded 8/7/4 kg split in the EEA’s 2025 briefing. Footprint estimates are modeled, unused-stock estimates carry substantial uncertainty, and none of the market datasets isolates flax linen or measures Thing Stories. Company practices are reported by the business and were not independently audited for this review.

Sources

[1] U.S. EPA. Nondurable Goods data, towels, sheets and pillowcases. https://www.epa.gov/facts-and-figures-about-materials-waste-and-recycling/nondurable-goods-product-specific-data 

[2] U.S. EPA. Textiles material data. https://www.epa.gov/facts-and-figures-about-materials-waste-and-recycling/textiles-material-specific-data 

[3] U.S. EPA. Facts and Figures, latest reporting year. https://www.epa.gov/facts-and-figures-about-materials-waste-and-recycling 

[4] U.S. GAO. Textile Waste, December 2024. https://www.gao.gov/products/gao-25-107165 

[5] EEA. Circularity of the EU textiles value chain in numbers. https://www.eea.europa.eu/en/analysis/publications/circularity-of-the-eu-textiles-value-chain-in-numbers 

[6] EEA. Circularity Metrics Lab, textile footprint indicators. https://www.eea.europa.eu/en/circularity/sectoral-modules/textiles 

[7] EEA. Textile waste generation. https://www.eea.europa.eu/en/circularity/sectoral-modules/textiles/textile-waste-generation-per-person-in-the-eu-per-year 

[8] EEA. Capture rate for waste textiles and shoes. https://www.eea.europa.eu/en/circularity/sectoral-modules/textiles/capture-rate-for-waste-textiles-and-shoes-in-the-eu 

[9] EEA. Textile waste treatment. https://www.eea.europa.eu/en/circularity/sectoral-modules/textiles/share-of-textile-waste-sent-to-incineration-or-landfill-in-the-eu 

[10] EEA. EU exports of used textiles. https://www.eea.europa.eu/en/circularity/sectoral-modules/textiles/eu-export-of-used-textiles 

[11] EEA. The destruction of returned and unsold textiles, 2024. https://www.eea.europa.eu/en/analysis/publications/the-destruction-of-returned-and-unsold-textiles-in-europes-circular-economy 

[12] MassDEP. Clothing and textile recovery. https://www.mass.gov/guides/clothing-and-textile-recovery 

[13] European Commission. Waste Framework Directive. https://environment.ec.europa.eu/topics/waste-and-recycling/waste-framework-directive_en 

[14] EUR-Lex. Directive EU 2025/1892, including Annex IVc. https://eur-lex.europa.eu/eli/dir/2025/1892/oj/eng 

[15] CalRecycle. Textile stewardship program and timetable. https://calrecycle.ca.gov/epr/textiles/ 

[16] European Commission. Unsold clothes and shoes destruction ban, July 2026. https://environment.ec.europa.eu/news/ban-destruction-unsold-clothes-and-shoes-enters-application-2026-07-17_en 

[17] OEKO-TEX. STANDARD 100 scope. https://www.oeko-tex.com/en/our-standards/oeko-tex-standard-100