Quellen und Datenbasis.
Jedes Gewicht, jede Recyclingquote und jeder Abbauzeitraum im Archiv stützt sich auf begutachtete Ökobilanz-Literatur, staatliche Fachberichte oder anerkannte Branchenverbände. Diese Seite listet auf, was wir wo und warum verwendet haben.
Die angegebenen Gewichte sind Kategorie-Durchschnittswerte (±15 %). Für markenspezifische Prüfungen wiegen wir auf kalibrierten Waagen nach und geben das Einzelgewicht direkt auf der Produktseite an.
Echte Produktfotos stammen aus den Gemeinschaftsdatenbanken Open Food Facts, Open Beauty Facts und Open Products Facts, genutzt unter der Lizenz CC BY-SA 3.0 und unter jedem Foto ausgewiesen. Wo kein frei lizenziertes Foto existiert, zeigen wir eine neutrale Studioaufnahme der Verpackungsform.
Jede Referenz zuletzt geprüft im September 2026
Hair & body care packaging
- Reducing the Environmental Impacts of Plastic Cosmetic Packaging: A Multi-Attribute Life Cycle AssessmentVassallo, N. & Refalo, P. · 2024 · Cosmetics (MDPI), 11(2), 34
Peer-reviewed LCA of a rigid powder compact (ABS base and lid, 7.29 grams, Toly Malta), modelling dematerialisation, recycled content and polymer choice. We use it for the rigid compact case weight and for the recycled-content effect, not for bottle, cap or pump weights, which it does not measure.
Rigid compact case weightRecycled-content and dematerialisation effects - Life Cycle Assessment of a Plant-Based, Regionally Marketed Shampoo and Analysis of Refill OptionsKröhnert, H. & Stucki, M. · 2021 · Sustainability (MDPI), 13(15), 8478
Swiss plant-based shampoo, measured per hair wash. Compares a 500 ml glass bottle with in-shop refills from tin and PE canisters and a PET stand-up refill pouch. Refills cut the packaging share sharply, while heating the shower water dominates the total footprint, which is why we treat refills as a packaging win rather than a whole-footprint fix.
Shampoo refill vs bottle comparisonRefill packaging per wash - Life cycle assessment (LCA) of the innovative eco-designed container for shampooOkada, N., Shibata, S., Sakata, K., Nakajima, A. & Itsubo, N. · 2021 · Cleaner and Responsible Consumption, Elsevier, 3, 100027
Component-level breakdown of a shampoo container, bottle wall, cap, label and adhesive. Primary source for our material splits and cap and label masses.
Material breakdown chartCap & label weightsShampoo bottle - One step closer to circularity: recycling post-consumer PE-HD into shampoo bottlesBichler, S., Koch, T., Krempl, N. et al. · 2025 · Journal of Material Cycles and Waste Management, 28, 1060–1076
Industrial study of recycled HDPE bottle production with measured wall thicknesses and unit weights.
HDPE bottle wall mass - Sustainable Design Strategy of Cosmetic Packaging in China Based on Life Cycle AssessmentRen, Z., Zhang, D. & Gao, Z. · 2022 · Sustainability (MDPI), 14(13), 8155
LCA of cosmetic containers with packaging mass and material split per format. Primary source for our bottle and jar weights, read alongside the component-level studies below so no figure rests on one paper.
Shampoo bottleConditioner bottleBody washFace cream jar - Life cycle assessment of multiple dispensing systems used for cosmetic product packagingRathore, S., Schuler, B. & Park, J. · 2023 · Packaging Technology and Science, 36(7), 533–547
Compares pump, spray and flip-top dispensing systems part by part. Source for the closure and pump masses that a container-level study does not resolve.
Pump weightsCap & closure weightsTrigger spray weights
Oral care
- 300 million toothpaste tubes go to landfillBritish Dental Journal editorial · 2021 · British Dental Journal, 230, 390
UK-level disposal volume for toothpaste tubes, used to contextualise per-tube plastic mass.
Toothpaste tube - Revolutionising recycling: the journey of toothpaste tubesWRAP (Waste & Resources Action Programme) · 2025 · WRAP case study
Recyclability and material composition of mono-material HDPE tubes, basis for our recyclability percentages.
Toothpaste recyclability % - Colgate-Palmolive HDPE Toothpaste TubeU.S. Plastics Pact · 2023 · U.S. Plastics Pact case study
Industry case study confirming ~20 billion toothpaste tubes/year and the shift to mono-material HDPE. Written by the brand-led pact itself, so we use it for the material composition and volume, while the recyclability claim is carried by the independent WRAP and peer-reviewed tube studies above.
Quelle eines Branchenverbands: wird nur zusammen mit unabhängigen Belegen gelesen und nie allein für strittige Recyclingangaben verwendet.
Tube material composition
Regulatory & cross-category benchmarks
- Revision of EU Ecolabel Criteria for Soaps, Shampoos and Hair Conditioners, Technical AnalysisEscamilla, M. et al. (LEITAT / JRC IPTS) · 2012 · European Commission, JRC (archived copy)
EU technical reference for typical packaging-to-product ratios across personal-care formats.
Cross-category packaging ratios - Global Commitment 2022, Household & Personal Care insightsEllen MacArthur Foundation & UNEP · 2022 · Ellen MacArthur Foundation
Industry-wide benchmarks: virgin-plastic share, recycled content rates, and recyclability progress for FMCG personal-care signatories.
Industry recyclability baselinesVirgin-content flags
Beverage packaging (PET, cans, cartons)
- Meta-Analysis of Life Cycle Assessment Studies for Polyethylene Terephthalate Water Bottle SystemGo, Y.-J., Kang, D.-H., Park, H.-J., Lee, J.-H. & Shim, J.-K. · 2024 · Sustainability (MDPI), 16(2), 535
Pooled LCA evidence on PET bottle mass, recycled-content rates and end-of-life pathways, primary basis for our PET bottle weights.
Coca-Cola bottleEvian bottleSmartwaterDasaniFiji water - Single-use plastic bottles and their alternatives, Recommendations from LCAUnited Nations Environment Programme / Life Cycle Initiative · 2020 · UNEP
UNEP-backed comparative LCA of PET, glass, aluminium and reusable bottles. Anchors our 'reusable bottle' alternative figures.
Reusable bottle alternativesBeverage category baselines - PET Life Cycle Assessment Report 2023NAPCOR (National Association for PET Container Resources) · 2023 · NAPCOR
North American industry LCA with current PET bottle weights, recycled-content levels and production energy figures. Published by the PET value chain, so we use it for the engineering figures (bottle mass, production energy) and read its recycling and recycled-content numbers next to the peer-reviewed PET meta-analysis and the UNEP bottle report listed on this page.
Quelle eines Branchenverbands: wird nur zusammen mit unabhängigen Belegen gelesen und nie allein für strittige Recyclingangaben verwendet.
Production energy per gram PETPET bottle wall mass - PET Bottle Lightweighting and Design for RecyclingPetcore Europe · 2022 · Petcore Europe AISBL
European PET value-chain body documenting decades of bottle lightweighting; a 0.5 litre bottle now weighs about 7.5 grams, with conventional bottles roughly in the 7.5 to 12 gram range. European counterpart to the NAPCOR bottle masses. Also an industry body, so we use it only for measured packaging weights, not for recyclability claims.
Quelle eines Branchenverbands: wird nur zusammen mit unabhängigen Belegen gelesen und nie allein für strittige Recyclingangaben verwendet.
PET bottle weightsBeverage bottle range
Flexible food packaging & films
- Recyclability and Redesign Challenges in Multilayer Flexible Food Packaging, A ReviewBauer, A.-S. et al. · 2021 · Foods (MDPI), 10(11), 2702
Comprehensive review of why multilayer film (snack bags, pouches, lidding film) is almost never recycled in practice, backs our low recyclability scores.
PringlesDoritosLaysOreo packSauce pouchesBread bag - Quantifying environmental benefits of monomaterial transition in flexible packaging applicationsStefanini, R. & Vignali, G. · 2026 · Environmental Impact Assessment Review, Elsevier, 118, 108321
Quantifies the impact reduction when multilayer film is redesigned as mono-PE or mono-PP for kerbside recycling.
Refill pouch alternativesMono-material film flag - LCA Guidance for Flexible PackagingFlexible Packaging Europe · 2024 · Flexible Packaging Europe (FPE)
Process-level guidance for modelling flexible packaging, whose worked examples run on film of 40 and 46 grams per square metre. We use it as an order-of-magnitude check on our bag, pouch and wrap weights, not as a measured grammage survey, and it is written by the converting industry itself.
Quelle eines Branchenverbands: wird nur zusammen mit unabhängigen Belegen gelesen und nie allein für strittige Recyclingangaben verwendet.
Film and pouch weightsCling filmBread bagSnack bags
Baby, feminine & medical hygiene
- Single-use nappies and their alternatives, Recommendations from LCAUnited Nations Environment Programme / Life Cycle Initiative · 2021 · UNEP
UNEP comparative LCA of disposable vs reusable nappies, material composition and per-unit plastic mass for disposable diapers.
PampersBaby wipesReusable nappy alternative - Life Cycle Assessment of Disposable and Reusable Nappies in the UKUK Environment Agency · 2005 · UK Environment Agency, Science Report SCHO0505BJCW
Foundational government LCA quantifying plastic content (SAP, PE backsheet, PP topsheet) in standard disposable nappies.
Diaper material breakdown - The value of reusable feminine hygiene products evaluated by comparative environmental life cycle assessmentHait, A. & Powers, S. E. · 2019 · Resources, Conservation and Recycling, Elsevier, 150, 104422
Peer-reviewed comparison of pads, tampons (with/without applicators) and menstrual cups, backs our applicator and pad plastic weights.
Sanitary padTampon applicatorMenstrual cup alternative
Household cleaning & laundry
- Comparative Life Cycle Assessment of Multiple Liquid Laundry Detergent Packaging FormatsKim, S. & Park, J. · 2020 · Sustainability (MDPI), 12(11), 4669
Cradle-to-grave LCA of HDPE jugs vs refill pouches vs pods, direct source for our laundry-jug-vs-refill savings figure.
Luxe Laundry JugLaundry podRefill pouch alternative - Comparative Life-Cycle Assessment of Laundry Detergent Formulations in the UK, Part IVan Hoof, G., Schowanek, D. & Feijtel, T. C. J. · 2003 · Tenside Surfactants Detergents, 40(5), 266–275
Cradle-to-grave LCA of five UK detergent formats per wash; finds the use stage dominates (>70%), which is why we treat packaging as the actionable share rather than the largest one.
Detergent sheets alternativePackaging-per-wash baseline - Case Study on Detergent Bottles: An Example of Weighing Sustainability Criteria for Rigid Plastic Non-Food PackagingOECD · 2023 · OECD Series on Risk Management, No. 63
Independent authority-level case study on HDPE detergent bottle design and lightweighting, used as a second opinion alongside the Kim and Park life cycle assessment.
Detergent bottle and jug weights
Single-use foodservice (cups, cutlery, takeaway)
- Single-use plastic tableware and its alternatives, Recommendations from LCAUnited Nations Environment Programme / Life Cycle Initiative · 2021 · UNEP
UNEP LCA of plastic, paper, bagasse and reusable cups/cutlery, backs our foodservice plastic-per-use figures and the 'reusable beats compostable' claim above ~20 reuses.
Plastic cupPlastic cutleryPaper plateTakeaway containerCoffee cup - Compostable Cutlery and Waste Management: An LCA ApproachRazza, F. et al. · 2009 · Waste Management, 29(4), 1424–1433
Per-1000-meals LCA quantifying when compostable cutlery actually beats conventional plastic at end-of-life.
Bamboo/compostable cutlery alternatives
Production footprint (water & energy per gram of resin)
- Cradle-to-Gate Life Cycle Analysis of High-Density Polyethylene (HDPE) ResinFranklin Associates, A Division of ERG · 2020 · American Chemistry Council, Plastics Division
Full cradle-to-gate inventory for HDPE resin: 8.14 litres of water and 73.8 MJ of total energy per kilogram, with electricity only a small share of that total. Primary source for our per-gram water coefficient. Commissioned by the resin industry, so we read it next to the peer-reviewed polymer water-footprint study below.
Quelle eines Branchenverbands: wird nur zusammen mit unabhängigen Belegen gelesen und nie allein für strittige Recyclingangaben verwendet.
Water per gram resinElectricity per gram resin - Cradle-to-Gate Life Cycle Analysis of Polypropylene (PP) ResinFranklin Associates, A Division of ERG · 2021 · American Chemistry Council, Plastics Division
Companion inventory for PP resin: 9.13 litres of water and 75.5 MJ of total energy per kilogram. Same authors and same industry commissioner as the HDPE report, so we treat the pair as one industry dataset rather than two independent ones.
Quelle eines Branchenverbands: wird nur zusammen mit unabhängigen Belegen gelesen und nie allein für strittige Recyclingangaben verwendet.
Water per gram resinElectricity per gram resin - Water Footprint Assessment of Selected Polymers, Polymer Blends, Composites, and Biocomposites for Industrial ApplicationKorol, J., Hejna, A., Burchart-Korol, D., Chmielnicki, B. & Wypiór, K. · 2019 · Polymers (MDPI), 11(11), 1791
Peer-reviewed water-footprint assessment across common polymers, confirming that fossil-based resin production sits in the single-digit to low-tens of litres per kilogram, not the thousands.
Water per gram resin - Eco-profiles Programme and Methodology, Version 3.1PlasticsEurope · 2022 · PlasticsEurope AISBL
The European methodology behind the PET, HDPE and PP resin datasets, used to check that our coefficients match European practice as well as North American data. Industry-published, and cross-checked here against the peer-reviewed Korol water-footprint study and the Zheng & Suh energy compilation.
Quelle eines Branchenverbands: wird nur zusammen mit unabhängigen Belegen gelesen und nie allein für strittige Recyclingangaben verwendet.
Electricity per gram resinEuropean resin datasets - Strategies to reduce the global carbon footprint of plasticsZheng, J. & Suh, S. · 2019 · Nature Climate Change, 9, 374–378
Compiles cradle-to-gate energy across polymers at roughly 60 to 90 MJ per kilogram, the basis for our statement that total energy including feedstock is far higher than the electricity we display.
Total energy context - Global Plastics Outlook: Economic Drivers, Environmental Impacts and Policy OptionsOECD · 2022 · OECD Publishing, Paris
System-level framing of plastic production, resource use and policy. It does not publish a single per-resin litre or kilowatt-hour coefficient, so we use it for context rather than for the numbers themselves.
Production and waste context - Plastics, the Fast Facts 2023PlasticsEurope · 2023 · PlasticsEurope AISBL
Industry-association reference for global resin production volumes and polymer mix, used to weight our averages. Its recycled-content shares are the association's own and have no independent equivalent at this granularity, so we treat them as indicative rather than settled.
Quelle eines Branchenverbands: wird nur zusammen mit unabhängigen Belegen gelesen und nie allein für strittige Recyclingangaben verwendet.
Polymer-mix weighting - Facts and Figures about Materials, Waste and Recycling, Plastics Material-Specific DataU.S. Environmental Protection Agency · 2024 update · EPA
Official U.S. recycling-rate dataset by polymer (PET, HDPE, PP, film) used to ground our recyclability-percent estimates.
Recyclability % by polymer
Marine fate & end-of-life impact
- Plastic Waste Inputs from Land into the OceanJambeck, J. R. et al. · 2015 · Science, 347(6223), 768–771
Landmark estimate of 4.8–12.7 million tonnes of plastic entering the ocean per year, frames the archive's pollution context.
Homepage statisticsDecomposition framing - Production, Use, and Fate of All Plastics Ever MadeGeyer, R., Jambeck, J. R. & Law, K. L. · 2017 · Science Advances, 3(7)
Global mass-balance: of 8.3 Bt of virgin plastic ever produced, only ~9% has been recycled. Source for our recycled-content baselines.
Global recycling rateVirgin-content flags - River Plastic Emissions to the World's OceansLebreton, L. C. M. et al. · 2017 · Nature Communications, 8, 15611
Quantifies riverine plastic flux (1.15–2.41 Mt/yr), used to contextualise per-item pollution numbers in our blurbs.
Ocean-leakage context - Degradation Rates of Plastics in the EnvironmentChamas, A., Moon, H., Zheng, J., Qiu, Y., Tabassum, T., Jang, J. H., Abu-Omar, M., Scott, S. L. & Suh, S. · 2020 · ACS Sustainable Chemistry & Engineering, 8(9), 3494–3511
Open-access review harmonising plastic degradation studies into one metric (specific surface degradation rate), with half-lives from 58 years for an HDPE bottle to 1,200 years for thick HDPE pipe. Peer-reviewed basis for our decomposition windows and for why thin films disappear far sooner than rigid containers.
Decomposition years (all products)Film vs rigid persistence - Environmental Deterioration of Biodegradable, Oxo-biodegradable, Compostable, and Conventional Plastic Carrier Bags in the Sea, Soil, and Open-Air Over a 3-Year PeriodNapper, I. E. & Thompson, R. C. · 2019 · Environmental Science & Technology, 53(9), 4775–4783
Three-year field exposure of carrier bags in seawater, soil and open air; conventional and biodegradable bags alike were still intact enough to hold shopping. Measured basis for the persistence window on films, bags and wrappers.
Decomposition years (films, bags, wrappers) - Pathways for degradation of plastic polymers floating in the marine environmentGewert, B., Plassmann, M. M. & MacLeod, M. · 2015 · Environmental Science: Processes & Impacts, 17(9), 1513–1521
Review of the chemical routes by which PE, PP, PET, PS and PVC break down at sea, showing that carbon-backbone polymers resist hydrolysis and rely on slow photo-oxidation. Explains why our persistence windows differ by polymer as well as by format.
Decomposition years (all products)Polymer-specific persistence - The Mystery of How Long Until It's Gone, Decomposition of Marine DebrisNOAA Marine Debris Program · ongoing · U.S. National Oceanic and Atmospheric Administration
Widely used government reference for marine litter timelines by item type (bag, cup, straw, bottle). We keep it as the plain-language companion to Chamas 2020.
Decomposition years (all products) - We need better data about the environmental persistence of plastic goodsWard, C. P. & Reddy, C. M. · 2020 · Proceedings of the National Academy of Sciences, 117(26), 14618–14621
Shows that popular persistence figures, above all the 450 years often quoted for a plastic bottle, cannot be traced to any measurement. This is why we present persistence as a modelled range and do not use the 450-year claim anywhere on the site.
Persistence framingWhy we dropped the 450-year figure - Ranking environmental degradation trends of plastic marine debris based on physical properties and molecular structureMin, K., Cuiffi, J. D. & Mathers, R. T. · 2020 · Nature Communications, 11, 727
Ranks PE, PP, PET, PS, PVC and nylon by degradation susceptibility and shows that thickness, crystallinity and additives move estimated lifetimes by one to two orders of magnitude.
Format-dependent persistenceFilm vs rigid persistence - Monitoring polymer degradation under different conditions in the marine environmentBeltrán-Sanahuja, A., Casado-Coy, N., Simó-Cabrera, L. & Sanz-Lázaro, C. · 2020 · Environmental Pollution, 259, 113836
Nine-month field exposure of PET, LDPE, HDPE, PP and PS in seawater, sediment and beach sand; conventional polymers lost only a few percent of their mass. Measured evidence behind our long marine persistence windows.
Marine persistenceDecomposition years (all products) - Alteration and progressive degradation of plastic waste in a Polish operational landfill analysed over 60 yearsRedko, V., Wolska, L., Cieślak-Piotrowicz, A. et al. · 2024 · Communications Earth & Environment, 5, 563
Polyethylene bags and film excavated after up to six decades of burial showed only partial surface oxidation, not disappearance. Real-world confirmation that landfilled film persists far longer than commonly quoted.
Landfill persistenceBag and film entries - Plastic Teabags Release Billions of Microparticles and Nanoparticles into TeaHernandez, L. M. et al. · 2019 · Environmental Science & Technology, 53(21), 12300–12310
Peer-reviewed evidence of microplastic shedding from PET/nylon pyramid teabags into the cup itself.
Tea / Lipton teaMicroplastic warnings
Global commitments & policy
- The Global Commitment 2023 Progress ReportEllen MacArthur Foundation & UN Environment Programme · 2023 · Ellen MacArthur Foundation
Latest signatory-level data on recyclable/reusable/compostable packaging and recycled-content targets across 1000+ FMCG brands.
Refill Available badgeRecyclability scores - Single-Use Plastics: A Roadmap for SustainabilityUnited Nations Environment Programme · 2018 · UNEP
Global review of single-use plastic policy and consumption, frames the archive's category list and 'avoidability' badges.
Single-use foodserviceBag and straw entries - The UK Plastics Pact, Progress Report 2024/25WRAP (Waste & Resources Action Programme) · 2025 · WRAP
UK industry progress data on problem-plastic elimination, recycled-content uptake and on-pack recyclability labelling.
UK-market recyclability adjustments
Food & drink packaging
- The role of flexible packaging in the life cycle of coffee and butterBüsser, S. & Jungbluth, N. · 2009 · The International Journal of Life Cycle Assessment, 14, 80–91
Shows how little of a coffee or butter product's footprint sits in the flexible wrapper compared with the contents, the basis for our 'the food usually beats the film' caveat on pouches.
Coffee packagingFlexible pouchesButter & spread wrappers - Comparative Life Cycle Assessment of Packaging Systems for Extended Shelf Life MilkBertolini, M., Bottani, E., Vignali, G. & Volpi, A. · 2016 · Packaging Technology and Science, 29, 525–546
Compares HDPE bottles, cartons and pouches for the same litre of milk, including distribution and losses, used for our milk and drink container weights.
Milk bottleCarton alternativesBeverage category baselines - Life cycle inventory of HDPE bottle-based liquid milk packaging systemsSingh, J., Krasowski, A. & Singh, S. P. · 2010 · Packaging Technology and Science, 24, 49–60
Detailed inventory of bottle, cap and crate masses across common milk sizes, a primary source for our HDPE bottle gram figures.
Milk bottleHDPE bottle weightsClosures - Life cycle assessment and life cycle costing of emerging circular flexible plastic food and non-food packagingHaslinger, A., Nhu, T. T., Cadena, E., Thomassen, G., Dewulf, J. & Huysveld, S. · 2026 · Resources, Conservation and Recycling, 226, 108674
Recent assessment of mono-material and recyclable flexible packaging routes, including what recycling actually recovers, informs our pouch recyclability ratings.
Flexible pouchesRecyclability ratingsSnack & refill packs - Environmental life cycle assessment of single-use and reusable food takeaway containersKadabinakatti, S. & Shinde, A. · 2025 · Acta Periodica Technologica, 251–265
Break-even reuse counts for takeaway containers, the source for how many uses a reusable box needs before it beats the disposable one.
Takeaway containersReusable break-even counts
Cleaning & household
- Comparative life cycle assessment of conventional and Green Seal-compliant industrial and institutional cleaning productsKapur, A., Baldwin, C., Swanson, M., Wilberforce, N., McClenachan, G. & Rentschler, M. · 2012 · The International Journal of Life Cycle Assessment, 17, 377–387
Compares concentrated and ready-to-use cleaning formats including their packaging, supports our concentrate and dilution-at-home alternatives.
Surface cleanerConcentratesCleaning category baselines - Analysis of Life Cycle Environmental Effect by Operation of Detergent Refill StationJin, K. M., Kim, Y. W. & Hwang, Y. W. · 2021 · Korean Journal of Life Cycle Assessment, 22, 23–27
Measures the packaging avoided when detergent is dispensed in-store into a returned container, the evidence behind our refill-station savings.
Laundry detergentRefill stationsBulk dispensing - Life-cycle environmental impact assessment and plastic pollution prevention measures of wet wipesZhang, Y., Wen, Z., Lin, W., Hu, Y., Kosajan, V. & Zhang, T. · 2021 · Resources, Conservation and Recycling, 174, 105803
Quantifies plastic content and end-of-life fate of wet wipes, including fibre release, used for our wipes entries and their alternatives.
Wet wipesBathroom disposablesMicroplastic notes
Kitchen disposables & carrier bags
- Multidimensional evaluation for environment impacts of plastic straws and alternatives based on life cycle assessmentGuo, X., Zhao, Y., Zhao, H., Lv, Y. & Huo, L. · 2023 · Journal of Cleaner Production, 404, 136716
Compares plastic, paper, PLA and steel straws across several impact categories, the basis for our straw weights and the honest caveats about paper.
StrawsSingle-use foodservice - A comparative cradle-to-grave life cycle assessment of single-use plastic shopping bags and various alternatives available in South AfricaStafford, W., Russo, V. & Nahman, A. · 2022 · The International Journal of Life Cycle Assessment, 27, 1213–1227
Non-European carrier-bag study showing how reuse counts and local waste systems change the answer, keeps our bag guidance global rather than EU-only.
Carrier bagsReusable bag break-evenNon-OECD waste systems
Textiles & microfibres
- Release of synthetic microplastic plastic fibres from domestic washing machines: Effects of fabric type and washing conditionsNapper, I. E. & Thompson, R. C. · 2016 · Marine Pollution Bulletin, 112, 39–45
Measures fibre counts shed per wash by fabric type, the reference for our synthetic-textile entries and laundry-bag advice.
Synthetic textilesLaundry microfibres - The contribution of washing processes of synthetic clothes to microplastic pollutionDe Falco, F., Di Pace, E., Cocca, M. & Avella, M. · 2019 · Scientific Reports, 9, 6633
Per-wash microfibre release measured for polyester, polypropylene and polyamide garments, basis for our shedding notes on fast-fashion items.
Polyester t-shirtLeggingsSports braSwimwearTights - Analysis of the polyester clothing value chain to identify key intervention points for sustainabilityPalacios-Mateo, C., van der Meer, Y. & Seide, G. · 2021 · Environmental Sciences Europe, 33(1), 2
Cradle-to-grave analysis of polyester garments: fibre production energy, dyeing and finishing, and end-of-life fate. Primary basis for our polyester weights and energy figures.
Polyester garmentsFast Fashion energy figures - Environmental assessment of Swedish clothing consumption, six garments, sustainable futuresSandin, G., Roos, S., Spak, B., Zamani, B. & Peters, G. · 2019 · Mistra Future Fashion, Report 2019:05
Life cycle study with measured masses for real retail garments: T-shirt 110 g, jeans 477 g, jacket 444 g, socks 43 g per pair. Independent cross-check for every garment weight in the archive.
Garment weightsFast Fashion entries - Open-loop recycling: A LCA case study of PET bottle-to-fibre recyclingShen, L., Worrell, E. & Patel, M. K. · 2010 · Resources, Conservation and Recycling, 55(1), 34–52
Quantifies energy and impact savings of recycled bottle-to-fibre polyester against virgin PET fibre.
Recycled-polyester t-shirt - Environmental impact of textile reuse and recycling – A reviewSandin, G. & Peters, G. M. · 2018 · Journal of Cleaner Production, 184, 353–365
Review of 41 studies: reuse consistently outperforms recycling, and blended fabrics are rarely recycled fibre-to-fibre. Backs our low recycling odds for blends.
Blended garmentsRecycling odds - The water footprint of cotton consumption: An assessment of the impact of worldwide consumption of cotton products on the water resources in the cotton producing countriesChapagain, A. K., Hoekstra, A. Y., Savenije, H. H. G. & Gautam, R. · 2006 · Ecological Economics, 60(1), 186–203
Standard reference for cotton's water footprint (~10,000 L per kg of lint), used for cotton and cotton-blend water figures.
Stretch denim jeansPoly-cotton bedding - A New Textiles Economy: Redesigning fashion's futureEllen MacArthur Foundation · 2017 · Ellen MacArthur Foundation
System-level data on garment lifespans, collection rates and the share of clothing recycled into new clothing (<1%).
Fast Fashion end-of-life percentages - Textiles and the environment: the role of design in Europe's circular economyEuropean Environment Agency · 2022 · EEA Briefing
EU per-person consumption, water and land use of textiles and the design decisions that drive them.
Fast Fashion category baselines - Materials Market Report 2023Textile Exchange · 2023 · Textile Exchange
Global fibre production volumes and the recycled-content share of polyester. Published by a fibre-industry membership organisation, so we use it for production volumes and read its recycled-content share next to the peer-reviewed bottle-to-fibre and textile-recycling studies above.
Quelle eines Branchenverbands: wird nur zusammen mit unabhängigen Belegen gelesen und nie allein für strittige Recyclingangaben verwendet.
Recycled-polyester context
Recycling systems & collection reality
- Increasing the PP-recyclate quality by enhanced mechanical processing of post-consumer packaging wasteKuhn, N., Mager, M., Fischer, J., Koinig, G. & Tischberger-Aldrian, A. · 2025 · Resources, Conservation and Recycling, 223, 108494
Shows what mechanical recycling actually recovers from mixed household packaging, why our recyclability scores discount 'technically recyclable' claims.
Recyclability ratingsPP itemsRecycled-content claims - Are Deposit–Return Schemes an Optimal Solution for Beverage Container Collection in the European Union? An Evidence ReviewSidorczuk-Pietraszko, E., Piontek, W. & Larsson, A. · 2025 · Sustainability, 17, 8791
Collected return rates across deposit and non-deposit systems, used in our local-disposal guidance for bottles and cans.
PET bottlesDeposit return guidance - What a Waste 2.0: A Global Snapshot of Solid Waste Management to 2050Kaza, S., Yao, L., Bhada-Tata, P. & Van Woerden, F. · 2018 · World Bank Group
Country-level waste generation, collection and disposal data worldwide, the source for our non-European end-of-life assumptions.
Global disposal guidanceCollection-rate assumptions - Regulation (EU) 2025/40 on packaging and packaging waste (Packaging and Packaging Waste Regulation)European Parliament & Council of the European Union · 2025 · Official Journal of the European Union
Binding EU rules on recyclability, reuse targets, minimum recycled content and packaging minimisation, the legal backdrop for our EU disposal notes.
EU disposal guidanceDesign-for-recycling rules
Microplastics & human health
- Discovery and quantification of plastic particle pollution in human bloodLeslie, H. A., van Velzen, M. J. M., Brandsma, S. H., Vethaak, A. D., Garcia-Vallejo, J. J. & Lamoree, M. H. · 2022 · Environment International, 163, 107199
Plastic particles quantified in the blood of 17 of 22 healthy donors — the first demonstration that particles circulate in humans.
Human exposure evidenceBlood detection - Plasticenta: First evidence of microplastics in human placentaRagusa, A., Svelato, A., Santacroce, C., Catalano, P., Notarstefano, V., Carnevali, O., Papa, F., Rongioletti, M. C. A., Baiocco, F., Draghi, S., D'Amore, E. & Rinaldo, D. · 2021 · Environment International, 146, 106274
First detection of microplastic fragments on both the maternal and foetal sides of human placenta.
Placenta detectionReproductive exposure - Detection of microplastics in human lung tissue using μFTIR spectroscopyJenner, L. C., Rotchell, J. M., Bennett, R. T., Cowen, M., Tentzeris, V. & Sadofsky, L. R. · 2022 · Science of The Total Environment, 831, 154907
Microplastics identified in 11 of 13 surgical human lung tissue samples, including the lower lobes.
Lung detectionAirborne exposure - Raman Microspectroscopy Detection and Characterisation of Microplastics in Human BreastmilkRagusa, A., Notarstefano, V., Svelato, A., Belloni, A., Gioacchini, G., Blondeel, C., Zucchelli, E., De Luca, C., D'Avino, S., Gulotta, A., Carnevali, O. & Giorgini, E. · 2022 · Polymers, 14(13), 2700
Microplastics detected in 26 of 34 human breast-milk samples.
Breast milk detection - Microplastics detected in cirrhotic liver tissueHorvatits, T., Tamminga, M., Liu, B., Sebode, M., Carambia, A., Fischer, L., Püschel, K., Huber, S. & Fischer, E. K. · 2022 · eBioMedicine, 82, 104147
Six polymer types found in cirrhotic liver tissue; none in healthy controls.
Liver detection - Microplastic presence in dog and human testis and its potential association with sperm count and weights of testis and epididymisHu, C. J., Garcia, M. A., Nihart, A., Liu, R., Yin, L., Adolphi, N., Gallego, D. F., Kang, H., Campen, M. J. & Yu, X. · 2024 · Toxicological Sciences, 200(2), 235–240
Microplastics present in every human and dog testis sampled; higher concentrations correlated with lower sperm count in dogs.
Testis detectionReproductive signals - Bioaccumulation of microplastics in decedent human brainsNihart, A. J., Garcia, M. A., El Hayek, E., Liu, R., Olewine, M., Kingston, J. D., Castillo, E. F., Gullapalli, R. R., Howard, T., Bleske, B., Scott, J. & Gonzalez-Estrella, J. · 2025 · Nature Medicine, 31, 1114–1119
Post-mortem brains carried higher plastic concentrations than liver or kidney, and 2024 samples exceeded 2016 samples.
Brain accumulation - Microplastics and Nanoplastics in Atheromas and Cardiovascular EventsMarfella, R., Prattichizzo, F., Sardu, C., Fulgenzi, G., Graciotti, L., Spadoni, T., D'Onofrio, N., Scisciola, L., La Grotta, R., Frigé, C., Pellegrini, V. & Municinò, M. · 2024 · New England Journal of Medicine, 390(10), 900–910
Cohort of 257 carotid surgery patients: plaque containing polyethylene or PVC was associated with a higher rate of heart attack, stroke or death over about 34 months.
Cardiovascular outcomes - Detection of Various Microplastics in Human StoolSchwabl, P., Köppel, S., Königshofer, P., Bucsics, T., Trauner, M., Reiberger, T. & Liebmann, B. · 2019 · Annals of Internal Medicine, 171(7), 453–457
Up to nine polymer types found in the stool of all eight participants across three continents.
Ingestion evidenceStool detection - Rapid single-particle chemical imaging of nanoplastics by SRS microscopyQian, N., Gao, X., Lang, X., Deng, H., Bratu, T. M., Chen, Q., Stapleton, P., Yan, B. & Min, W. · 2024 · Proceedings of the National Academy of Sciences, 121(3)
New imaging counted roughly 240,000 plastic fragments per litre of bottled water, about 90% of them nanoplastics.
Bottled water nanoplasticsPET bottles - Microplastic release from the degradation of polypropylene feeding bottles during infant formula preparationLi, D., Shi, Y., Yang, L., Xiao, L., Kehoe, D. K., Gun'ko, Y. K., Boland, J. J. & Wang, J. J. · 2020 · Nature Food, 1, 746–754
Polypropylene infant bottles released about 16 million particles per litre when formula was prepared at 70 °C.
Infant feeding bottlesHeat and plastic - Microfiber Masses Recovered from Conventional Machine Washing of New or Aged GarmentsHartline, N. L., Bruce, N. J., Karba, S. N., Ruff, E. N., Sonar, S. U. & Holden, P. A. · 2016 · Environmental Science & Technology, 50(21), 11532–11538
Measured microfibre mass shed per machine wash by garment and machine type — roughly 0.2 to 4 g per load.
Textile microfibresFast Fashion washing - Microplastics and human healthVethaak, A. D. & Legler, J. · 2021 · Science, 371(6530), 672–674
Peer-reviewed overview of exposure routes, plausible mechanisms of harm, and the gaps in the evidence.
Health mechanism overview - Dietary and inhalation exposure to nano- and microplastic particles and potential implications for human healthWorld Health Organization · 2022 · World Health Organization
WHO assessment of dietary and inhalation exposure: exposure is widespread, evidence for health effects remains limited.
Exposure assessmentHonest limits
Blog articles
- Capturing microfibers, marketed technologies reduce microfiber emissions from washing machinesMcIlwraith, H. K., Lin, J., Erdle, L. M., Mallos, N. & Diamond, M. L. · 2019 · Marine Pollution Bulletin, 139, 40–45
Independent test of catch balls and in-line filters: fibre reduction ranged from about a quarter to roughly 87%.
Blog: The microplastic shedding in your laundry - A cradle-to-grave life cycle assessment of multilayer plastic film food packaging materialsMousania, Z. & Atkinson, J. D. · 2025 · Waste Management, 200, 114747
Confirms multilayer films are effectively unrecyclable and end in landfill or incineration.
Blog: A kitchen without cling film - Life cycle-based water assessment of a hand dishwashing product: Opportunities and limitationsVan Hoof, G., Buyle, B., Kounina, A. & Humbert, S. · 2013 · Integrated Environmental Assessment and Management, 9(4), 633–644
Shows the use phase and packaging split for hand dishwashing products.
Blog: A dishwashing routine without plastic bottles - Raman imaging for the identification of Teflon microplastics and nanoplastics released from non-stick cookwareLuo, Y., Gibson, C. T., Chuah, C., Tang, Y. & Naidu, R. · 2022 · Science of The Total Environment, 851, 158293
Measures Teflon particles released from scratched and broken non-stick coatings.
Blog: Cookware that outlives you - PTFE-coated non-stick cookware and toxicity concerns: a perspectiveSajid, M. & Ilyas, M. · 2017 · Environmental Science and Pollution Research, 24, 23436–23440
Peer-reviewed review of PTFE coating breakdown at high temperature and the compounds released.
Blog: Cookware that outlives you - Antimony leaching from polyethylene terephthalate (PET) plastic used for bottled drinking waterWesterhoff, P., Prapaipong, P., Shock, E. & Hillaireau, A. · 2008 · Water Research, 42(3), 551–556
Antimony release from PET rises sharply with temperature and storage time, though it stays below drinking-water limits in fresh product.
Blog: PET bottles, recyclable on paper - Social life cycle assessment of drinking water: Tap water, bottled mineral water and tap water treatment systemsGarfí, M., Requejo-Castro, D. & Villanueva, C. M. · 2025 · Environmental Impact Assessment Review, 112, 107815
Comparison of tap, filtered and bottled water across environmental and social indicators.
Blog: How to grocery shop with less plastic - Life Cycle Sustainability Assessment of Stainless-Steel Cutlery: An Industrial Case Study from ItalyLa Rosa, A. D., De Pizzol, C., Salandini, D. & Ginestra, P. · 2025 · SSRN working paper
Industrial assessment of stainless-steel cutlery production, the basis for treating long-lived steel tools as an amortised footprint.
Blog: Buy one knife, keep it sharp for twenty years
Carbon intensity factors (Swap Tracker)
- Manufacturing energy and greenhouse gas emissions associated with plastics consumptionNicholson, S. R., Rorrer, N. A., Carpenter, A. C. & Beckham, G. T. · 2021 · Joule, 5(3), 673–686
Cradle-to-gate emissions per kilogram for the commodity resins that dominate packaging (PE, PP, PET). Basis for the 2.9 kg CO2e per kilo of plastic used in the Swap Tracker estimate.
Swap Tracker carbon estimate - Emissions Factors 2024, CO2 emissions per kWh of electricity generationInternational Energy Agency · 2024 · IEA, Paris
Average grid carbon intensity of electricity generation. Basis for the 0.35 kg CO2e per kWh applied to avoided production energy in the Swap Tracker.
Swap Tracker carbon estimate
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