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THE FASTEST PATHWAY

Atmosphere

Microplastics fall with rain, snow and dust on cities, protected parks, mountain summits and polar ice. How much the world emits into the air is disputed: in 2026 a comparison with 2,782 measurements found that three emission inventories overestimated measured airborne concentrations and deposition by a factor of 100 to 10,000.

9 min readUpdated ReviewedBWell supportedCLimitedDDisputedEUnknownPProvenance

Oblique satellite view of a tan dust plume crossing the dark blue Atlantic from the West African coast at the bottom
Saharan dust streaming west across the tropical Atlantic toward South America, in a NASA composite of Suomi NPP VIIRS data from 25 June 2014, seen obliquely with West Africa at the bottom. The plume is dust, not plastic: it shows long-range transport of fine particles.NASA Earth Observatory; NASA images by Norman Kuring, NASA's Ocean Color webNASASource ↗

Plastic falls out of the sky. Collectors at 11 western US national parks and wilderness areas averaged 132 microplastic particles per square meter per day (level C)1. The authors extrapolated this to more than 1,000 metric tons a year on protected land in that region1. How much the planet sends into the air is disputed. In January 2026 a Vienna team found that three emission inventories overestimated the medians of 2,782 measurements by a factor of 100 to 10,000 (level C)2.

≈0.08 particles/m³

median microplastic concentration in outdoor air over land

concentration in air; from the 925 concentration measurements among 2,782 compiled (the rest are deposition), 76 studies, 283 locations, 2014–2024; coastal sites excluded; sizes from several µm up; mostly µ-Raman and µ-FTIR2

one compilation of heterogeneous methods; across all sites the mean (31 particles/m³) is about a thousand times the overall median (0.03)

CLimited

100–10,000×

how far three emission inventories, run through one transport model, overestimated measured airborne plastic

global median concentrations and deposition; model output aligned to each study's size range, 5–100 µm; Evangelou et al. 20262

single analysis; outside experts question how comparable the compiled measurements are

CLimited

≈4,500 t vs ≈1 Mt

two 2026 estimates of global microplastic emissions into the air per year

estimates, not measurements: 0.0045 Tg/yr for 5–100 µm (Nature, peer reviewed) vs 1,001 ± 781 Gg/yr for 5–250 µm (preprint, not yet peer reviewed)2,3

a disagreement of more than two orders of magnitude, partly from different size ranges; the preprint was under review for Atmospheric Chemistry and Physics on 3 November 2026

DDisputed

>1,000 t/yr

microplastic deposited on protected lands in the western US

deposition onto the ground; 11 network sites sampled over 14 months (as described in the companion 2021 paper); mass extrapolated from particle counts of about 4 µm and larger1,4

CLimited

2,238 particles/m³

median microplastic concentration in car cabin air

concentration in air; particles 1–10 µm; two cars, five samples, southern France; Raman spectroscopy; Yakovenko et al. 20255

small sample; homes in the same study had a median of 528 particles/m³

CLimited

Two kinds of numbers: in the air and on the ground

Airborne plastic is reported in two ways that are easy to mix up. A concentration counts particles suspended in a cubic meter of air, sampled by pumping air through a filter. A deposition rate counts particles that settle onto a square meter of surface per day, caught in a funnel or a bucket that collects rain, snow and dry fallout. Wet deposition comes down with precipitation; dry deposition settles on its own.

The largest compilation so far, by Ioanna Evangelou, Silvia Bucci and Andreas Stohl at the University of Vienna, gathered 925 concentration and 1,857 deposition measurements made between 2014 and 2024 (level P)2. The median concentration was 0.03 particles/m³ across all sites, 0.08 over land and 0.003 over the open sea, 27 times lower (level C)2. The median bulk deposition over land was 0.0006 particles/m² per second, or about 50 particles/m² per day (our conversion from2).

Single sites vary more. Along the southeast coast of China, reported concentrations range from 0.004 to 190 particles/m³ (level C)2. Reported deposition runs from 50 particles/m²/day in a Chinese suburb to 3,100 at a British urban site2. The global mean concentration, 31 particles/m³, is a thousand times the overall median of 0.03, because a few studies report very high values2.

Size limits drive much of this spread. Most compiled studies identified polymers by µ-Raman or µ-FTIR spectroscopy and reported particles from several micrometers to several millimeters2. Particles smaller than a few micrometers are usually not counted, although particle numbers rise steeply as size falls5,6.

Land leads by particle number; the mass split is disputed

Several independent studies find road traffic a major source of airborne plastic over land, at least near roads, in cities and in western US deposition (level B)4,7,8. A 2026 global inversion by Ondřej Tichý and colleagues, still a preprint, ranks road dust, at 51 ± 31 Gg a year, below agriculture at 170 ± 125 Gg (preprint estimate, level C)3.

Janice Brahney and colleagues fitted a transport model to western US deposition data. It attributed 84% of deposited microplastic to roads, 11% to the ocean and 5% to agricultural dust (model estimate, level C)4. Tire and road wear particles were rare in their samples: in their reading, roads mainly resuspend plastic from many products after traffic grinds it down4.

Studies that target tire rubber chemically, by pyrolysis gas chromatography with mass spectrometry (py-GC/MS), give a different picture. At a roadside in Leipzig in September 2022, tire wear made up about 65% of the plastic mass in particles below 10 µm (level C)7. In Oslo, tire wear particles accounted for more than 90% of airborne microplastic mass (level C)8. These studies count tire wear as plastic; the spectroscopy-based western US samples rarely identified it4.

Textiles shed fibers into air. In Paris fallout, Rachid Dris and colleagues found about 29% of fibers synthetic or mixed (level C)9. They estimated that 3 to 10 metric tons of fibers settle on the Paris area each year9.

The ocean's role is disputed (level D). Two earlier models fitted to western US deposition data made sea spray the largest source by mass. Brahney's put the ocean at about 8.6 million metric tons (8.6 Tg) a year, 95% range 0 to 224. An inversion by Nikolaos Evangeliou and colleagues put it at 8.9 ± 3.5 Tg of a 9.6 ± 3.6 Tg total (estimates, level C)10.

Newer models disagree in both directions. A 2025 global model made the ocean about 0.008% of emissions but about 15% of deposition, mainly a sink (estimate, level C)11. The Tichý preprint counters that oceanic emissions are "likely non-negligible": 763 ± 611 of its 1,001 Gg a year3.

Method

Is tire wear counted as plastic? It depends on what a study looks for. The studies cited here that targeted tire polymers counted it: py-GC/MS in Leipzig and Oslo air and over the Norwegian Sea, TD-PTR-MS in Greenland firn7,8,12,13. Detection depends on the target compounds, calibration and sample treatment, not on the instrument family alone. FTIR imaging of snow listed rubber among the main polymers6. Most surveys compiled in 2026 used µ-Raman or µ-FTIR, while the bottom-up inventory tested there combines traffic wear (tire, brake, road markings, road surface) with ocean and bare-soil emissions2. Measurements and models may therefore not count the same particles.

Hours to days aloft, as far as the poles

In the Brahney model, particles of about 4 µm and larger stayed up from one hour to 6.5 days (model estimate, level C)4. The authors suggest smaller particles could stay up for weeks4. In the Vienna model, removal from the air was dominated by settling under gravity rather than by rain2.

That is enough to reach remote places: several independent studies find microplastics deposited at remote mountain, Arctic and polar sites far from local sources (level B)14,6,15,13,16. At Bernadouze in the French Pyrenees, Steve Allen and colleagues measured deposition of about 365 particles/m²/day (5 µm and larger) from November 2017 to March 2018 (level C)14. Air-mass trajectories indicated transport over up to 95 km; the authors note that their data cannot prove long-range transport14.

At the Pic du Midi Observatory (2,877 m), also in the Pyrenees, pumped air from the free troposphere held 0.09–0.66 particles/m³ from June to October 2017 (concentration, µ-Raman, level C)16. Back-trajectories crossed the Atlantic and the Mediterranean, which the authors read as intercontinental and transoceanic transport16.

Snow from the Alps to the Fram Strait held microplastics, with Arctic samples reaching 14,400 particles per liter at 11 µm and above (FTIR imaging, level C)6. Cloud water on Japanese summits from 1,300 to 3,776 m held 6.7 to 13.9 particles per liter, sized 7.1–94.6 µm (level C)17.

Over the Norwegian Sea up to Bear Island, py-GC/MS found up to 37.5 ng/m³ of microplastic in air, with tire wear reaching 35 ng/m³ (level C)12. On Ross Island, Antarctica, snow at all 19 sites sampled in late 2019 held microplastics, about 29 particles per liter of meltwater at 50 µm and above (µFTIR, level C)18. Back-trajectories allow transport of up to 6,000 km, but nearby research stations are a possible local source18.

How much reaches the ocean from the air is a model question. A 2020 simulation estimated that about 100,000 metric tons of tire wear particles a year are deposited in the world ocean (estimate, level C)19. From the few marine deposition measurements, all near coasts, Evangelou and colleagues infer that most suspended microplastic settles close to its land sources2.

Models versus measurements: the 2026 correction

Evangelou, Bucci and Stohl ran three published emission inventories through the FLEXPART transport model, matching each simulated value to the size range of its measurement2. All three overestimated the global median concentrations and deposition by two to four orders of magnitude (level C)2. Over land, simulated median concentrations were 105 to 1,506 particles/m³, against a measured 0.08 (level C)2. Before scaling, even the best correlation with measured concentrations was weak (r = 0.33)2.

With data too sparse for an inversion, two global factors cut land emissions to 0.13% of the bottom-up inventory and raised ocean emissions 3.6 times2. The scaled total is 0.0045 Tg (range 0.0006–0.0089), about 4,500 metric tons a year for 5–100 µm (estimate, level C)2. Land emits over 20 times more particles than the ocean, but the ocean emits more mass, about 4,000 against 500 t a year (estimate, level C)2. That split rests on assumed emission size distributions2.

The emission magnitude is disputed (level D). Soroush Abolfathi (University of Warwick) called the study careful but warned that size cut-offs and mass-to-number conversions can shift results by orders of magnitude20. Richard Lampitt (National Oceanography Centre) argued that the compiled techniques differ too much to compare and that model inputs often come from chains of other models20. Isidro Pérez (University of Valladolid) cited measurements spread over years of changing emissions, sparse sites and an outlier-sensitive correlation coefficient21.

The Tichý preprint is a testable alternative, not a midpoint: fitted to remote deposition data, it estimates about 1 Mt a year for 5–250 µm3. On 3 November 2026 it was under review for Atmospheric Chemistry and Physics, with public discussion open until 11 November (level P)3.

By our comparison, Brahney's extrapolation puts more than 1,000 t a year onto western US protected lands1, twice the scaled model's 500 t a year for all land emissions worldwide2. It is not like for like. Land deposition also receives plastic from the sea and particles lifted again after settling, and the size windows differ (counts from about 4 µm converted to mass, against 5–100 µm). This is a diagnostic to explain, not a refutation of either study.

Estimate

Every global emission figure on this page is a model estimate, not a measurement. The published values span more than three orders of magnitude, from about 9.6 Tg a year10 to 0.0045 Tg a year2, and each covers a different size range. The named air presets behind this site's home counters are explained on Flows & Model.

Indoor air and what we breathe

People in industrialized countries spend about 90% of their time indoors5. Small studies report more plastic indoors than outdoors. In the Paris area, Dris and colleagues counted 1.0–60.0 fibers/m³ in two apartments and an office, against 0.3–1.5 fibers/m³ outdoors; about a third of the indoor fibers were petrochemical (level C)22.

Smaller particles change the scale. Nadiia Yakovenko and colleagues sampled three apartments and two cars in southern France, identifying particles of 1–10 µm by Raman spectroscopy (level C)5. Median concentrations were 528 particles/m³ in homes and 2,238 in car cabins; 94% of particles were smaller than 10 µm5. Combining these with published data, they estimate that an adult inhales about 68,000 particles of 1–10 µm a day indoors, 100 times earlier estimates extrapolated from larger sizes (estimate, level C)5.

By mass, the Leipzig study estimated an inhaled dose of about 2.1 µg of airborne plastic a day for someone breathing that roadside air (estimate, level C)7. The WHO concluded in 2022 that inhalation exposure data were too limited for a human risk assessment23. What inhaled particles do in the body is covered on Human Body; filtration indoors is covered on Solutions by System.

What is uncertain about nanoplastics in air

For nanoplastics below 1 µm, the airborne record is close to empty. We found no peer-reviewed, size-resolved number concentrations of nanoplastics below 1 µm in outdoor air (level E). Search scope: this site's registry, Crossref and web search, papers from 2019–2026 on "airborne nanoplastics", "atmospheric nanoplastics" and "TD-PTR-MS air", November 2026. The models in the 2026 comparison stop at 5 µm, and the compiled measurements start at several micrometers2.

The nanoplastic evidence comes from snow and ice. Dušan Materić and colleagues used thermal desorption proton transfer reaction mass spectrometry (TD-PTR-MS) to find PET nanoplastics in Alpine snow (level C)24.

At the Sonnblick Observatory, 3,106 m up in the Austrian Alps, surface snow in 2017 held on average 46.5 ng/mL, implying deposition of about 42 kg per km² a year (level C)15. Greenland firn averaged 13.2 ng/mL and Antarctic sea ice 52.3 ng/mL, with tire wear nanoparticles identified in Greenland (level C)13. The sea-ice value does not show whether the particles arrived by air or from seawater.

These are masses, not counts or sizes. The Leipzig study reports a fine fraction by mass, not resolved below 1 µm7. Sub-micrometer estimates in the indoor study are extrapolations from a size distribution, not measurements5.

Illustration of a thin translucent fiber crossing a bright blue sky, with a pale spiky pollen grain and a tiny clear fragmentIllustration
Illustration: a synthetic fiber drifting in bright daylight air, with a pollen grain (the pale spiky sphere) touching it and a small clear plastic fragment nearby. Enlarged and brightened for visibility; sizes are illustrative. Not a microscope image.Illustration · AI generatedMade with FLUX.1-schnell (fp8, Comfy-Org/Flux-1-Schnell) · ComfyUI (local), tools/content/generate_l3.pySite illustration (AI-generated, Flux)Site original
Rain sampler with two white buckets and a hinged lid on a metal stand inside a fenced grassy plot
A National Atmospheric Deposition Program sampler in Shenandoah National Park, Virginia, 18 July 2017; its lid opens when it senses rain or snow. Collectors of this network supplied the western US parks study (Brahney et al. 2020); this unit was not in it.NPS / Mary O'NeillPublic domain (US Gov)Source ↗
Road and tire wear, textiles, farmland and bare soil, and sea spray feed the air; particles stay aloft hours to days, then settle near sources or reach remote regions. Land leads by particle number; the ocean's mass share is disputed. Dashed links: model estimates or inference.Nanoplastics ObservatorySite original

Measured vs modeled microplastic concentrations in air, global medians

Log-scale dot and range chart: measured medians of 0.08 particles per cubic meter over land and 0.003 over ocean lie far below model ranges of 105 to 1,506 over land (about 1,300 to 19,000 times higher) and 0.2 to 13.9 over ocean (about 70 to 4,600 times higher, our calculation). Source:2Nanoplastics ObservatorySite original
Data table
labelvalueunitkindscope
Over land, measured median0.08particles/m³measurement2014–2024, coastal sites excluded
Over land, model (TD-B inventory)105particles/m³model estimatelowest of three inventories over land; TD-B is the Brahney et al. 2021 top-down estimate
Over land, model (TD-E inventory)1506particles/m³model estimatehighest of three inventories over land; TD-E is the Evangeliou et al. 2022 top-down estimate
Over ocean, measured median0.003particles/m³measurement2014–2024, open ocean
Over ocean, model (lowest inventory)0.2particles/m³model estimaterange across three inventories
Over ocean, model (highest inventory)13.9particles/m³model estimaterange across three inventories

Global microplastic emissions into the air: published estimates

Log-scale dot chart of five published model estimates of airborne microplastic emissions: 9.6 Tg per year (2022 total), 8.6 (2021 ocean term), a 2026 preprint near 1, 0.32 (2023) and 0.0045 (2026, range 0.0006 to 0.0089). Source:2,4,3,10Nanoplastics ObservatorySite original
Data table
labelvalueunitsize_rangebasissource
Evangeliou et al. 2022, top-down inversion9.6Tg/yrmicroplastics up to 250 µmtotal of all sources; western US deposition data, global extrapolation; ocean 8.9 ± 3.5 of the 9.6 ± 3.6; microfibers (6.5 ± 2.9 Tg/yr) estimated separately and not includedS-199
Brahney et al. 2021, ocean source only8.6Tg/yrmodel bins 0.3–70 µm; observations 4–250 µmocean term only, 95% range 0–22, not a total; western US deposition data, global extrapolation; roads (0.096) and agricultural dust (0.069) add about 2%S-050
Tichý et al. 2026, preprint1Tg/yr5–250 µmremote deposition data, Bayesian inversion; not peer reviewed; under review for Atmospheric Chemistry and Physics on 3 November 2026S-198
Fu et al. 2023, GEOS-Chem0.32Tg/yr0.3–70 µmsecond-hand: as reported in Evangelou et al. 2026; the primary paper was not checked by this siteS-052
Evangelou et al. 2026, scaled0.0045Tg/yr5–100 µm2,782 measurements, two global scaling factors; 90% confidence interval 0.0006–0.0089S-052

Airborne plastic indoors and outdoors: what each study counted

Log-scale dot and range chart: a 0.08 particles per cubic meter outdoor median, Paris fiber ranges of 0.3 to 1.5 outdoors and 1.0 to 60 indoors, and medians of 528 in homes and 2,238 in cars for particles of 1 to 10 µm. Source:2,5,22Nanoplastics ObservatorySite original
Data table
labelvalueunitstatisticsize_rangeplacesourcelow
Outdoor air over land, global median0.08particles/m³medianseveral µm and larger283 locations worldwide, 2014–2024S-052
Outdoor air, Paris area (all fibers)1.5fibers/m³range; value is the high endfibers, natural and syntheticone outdoor site, published 2017S-2030.3
Indoor air, Paris area (all fibers)60fibers/m³range; value is the high endfibers; about one-third petrochemicaltwo apartments and one officeS-2031
Homes, median528particles/m³median1–10 µm, Ramanthree apartments, Toulouse, seven samplesS-063
Car cabins, median2238particles/m³median1–10 µm, Ramantwo cars, southern France, five samplesS-063
Electron micrograph of a single thin, curved airborne plastic fiber with small specks stuck to it, and a 5 µm scale bar in the data strip below
Plastic fiber from airborne particulate matter, Lodhi Road, Delhi, India, 2024; scanning electron micrograph, scale bar 5 µm. Confirmed as plastic by FTIR before imaging; the paper gives no polymer for this fiber. From Rao et al. 2025, figure 7, CC BY 4.025.Figure 7 (bottom-right panel) from Rao et al. (2025), Scientific Reports 15: 25662, https://doi.org/10.1038/s41598-025-04306-8 · CC BY 4.0 · croppedCC BY 4.0Source ↗

Questions

Is there more plastic in indoor or outdoor air?

The small studies available report higher counts indoors: 1.0–60.0 fibers/m³ in Paris-area homes and an office against 0.3–1.5 outdoors, and medians of 528 particles/m³ in homes and 2,238 in cars for particles of 1–10 µm. Samples are few and methods differ (level C,22,5).

Does the ocean put plastic into the air?

How much plastic sea spray lifts is disputed. Evangelou et al. 2026 estimate about 4,000 t a year for 5–100 µm; models from 2021 and 2022 put the ocean near 9 Tg a year; a 2025 model made the ocean mainly a sink; a 2026 preprint makes it the largest source by mass (level D,2,4,10,11,3).

Are tire particles counted as microplastics?

It depends on the study. Studies that target tire polymers chemically (py-GC/MS) count tire wear and find it dominates plastic mass in city air in Leipzig and Oslo; spectroscopy of western US deposition rarely identified it (level C,7,8,4).

Why did the 2026 study lower the emission estimates so much?

Three published inventories, run through a transport model, gave airborne concentrations 100 to 10,000 times higher than the medians of 2,782 measurements. Scaling land emissions down to about one-thousandth made modeled and measured mean concentrations over land match; ocean emissions were then scaled up 3.6 times (level C,2).

Does airborne plastic reach Antarctica?

One study found microplastics in snow at all 19 sites sampled on Ross Island in late 2019, about 29 particles per liter of meltwater at 50 µm and above. Back-trajectories allow transport of up to 6,000 km, but nearby research stations are a possible local source (level C,18). Nanoplastics in Antarctic sea ice (13) do not show whether they arrived by air or from seawater.

Where to go next

What happens to plastic once it lands at sea is on Oceans. The instruments and their size limits are explained on How We Measure It, and open questions on Knowledge Gaps.

Sources

  1. Brahney J, Hallerud M, Heim E, Hahnenberger M, Sukumaran S (2020). Plastic rain in protected areas of the United States. Science. doi:10.1126/science.aaz5819 journal article
  2. Evangelou I, Bucci S, Stohl A (2026). Atmospheric microplastic emissions from land and ocean. Nature. doi:10.1038/s41586-025-09998-6 journal article
  3. Tichý O, Košík V, Eckhardt S, Evangeliou N, Šmídl V (2026). Global continental and oceanic emissions of atmospheric microplastics inferred from pattern-restricted Bayesian inversion. EGUsphere (preprint, open for discussion, not peer reviewed). doi:10.5194/egusphere-2026-5158 Preprint · not peer reviewed open access
  4. Brahney J, Mahowald N, Prank M, Cornwell G, Klimont Z, Matsui H et al. (2021). Constraining the atmospheric limb of the plastic cycle. Proceedings of the National Academy of Sciences. doi:10.1073/pnas.2020719118 journal article
  5. Yakovenko N, Pérez-Serrano L, Segur T, Hagelskjaer O, Margenat H, Le Roux G et al. (2025). Human exposure to PM10 microplastics in indoor air. PLOS One. doi:10.1371/journal.pone.0328011 journal article open access
  6. Bergmann M, Mützel S, Primpke S, Tekman MB, Trachsel J, Gerdts G (2019). White and wonderful? Microplastics prevail in snow from the Alps to the Arctic. Science Advances. doi:10.1126/sciadv.aax1157 journal article open access
  7. Kaushik A, Peter AE, van Pinxteren M, Scholz-Böttcher BM, Herrmann H (2025). Composition, interactions and resulting inhalation risk of micro- and nano-plastics in urban air. Communications Earth & Environment. doi:10.1038/s43247-025-02980-0 journal article open access
  8. Herzke D, Schmidt N, Lervik AE, Schulze D, Celentano S, Eckhardt S et al. (2026). Airborne microplastics on the move: Urban Europe as a source to remote regions. Environmental Pollution. doi:10.1016/j.envpol.2025.127380 journal article
  9. Dris R, Gasperi J, Saad M, Mirande C, Tassin B (2016). Synthetic fibers in atmospheric fallout: A source of microplastics in the environment?. Marine Pollution Bulletin 104:290–293. doi:10.1016/j.marpolbul.2016.01.006 journal article
  10. Evangeliou N, Tichý O, Eckhardt S, Zwaaftink CG, Brahney J (2022). Sources and fate of atmospheric microplastics revealed from inverse and dispersion modelling: From global emissions to deposition. Journal of Hazardous Materials 432:128585. doi:10.1016/j.jhazmat.2022.128585 journal article open access
  11. Yang S, Brasseur G, Walters S, Lichtig P, Li CWY (2025). Global atmospheric distribution of microplastics with evidence of low oceanic emissions. npj Climate and Atmospheric Science 8:81. doi:10.1038/s41612-025-00914-3 journal article open access
  12. Goßmann I, Herzke D, Held A, Schulz J, Nikiforov V, Georgi C et al. (2023). Occurrence and backtracking of microplastic mass loads including tire wear particles in northern Atlantic air. Nature Communications 14:3707. doi:10.1038/s41467-023-39340-5 journal article open access
  13. Materić D, Kjær HA, Vallelonga P, Tison JL, Röckmann T, Holzinger R (2022). Nanoplastics measurements in Northern and Southern polar ice. Environmental Research. doi:10.1016/j.envres.2022.112741 journal article
  14. Allen S, Allen D, Phoenix VR, Le Roux G, Durántez Jiménez P, Simonneau A et al. (2019). Atmospheric transport and deposition of microplastics in a remote mountain catchment. Nature Geoscience. doi:10.1038/s41561-019-0335-5 journal article
  15. Materić D, Ludewig E, Brunner D, Röckmann T, Holzinger R (2021). Nanoplastics transport to the remote, high-altitude Alps. Environmental Pollution. doi:10.1016/j.envpol.2021.117697 journal article
  16. Allen S, Allen D, Baladima F, Phoenix VR, Thomas JL, Le Roux G et al. (2021). Evidence of free tropospheric and long-range transport of microplastic at Pic du Midi Observatory. Nature Communications 12:7242. doi:10.1038/s41467-021-27454-7 journal article open access
  17. Wang Y, Okochi H, Tani Y, Hayami H, Minami Y, Katsumi N et al. (2023). Airborne hydrophilic microplastics in cloud water at high altitudes and their role in cloud formation. Environmental Chemistry Letters 21:3055–3062. doi:10.1007/s10311-023-01626-x journal article open access
  18. Aves AR, Revell LE, Gaw S, Ruffell H, Schuddeboom A, Wotherspoon NE et al. (2022). First evidence of microplastics in Antarctic snow. The Cryosphere 16:2127–2145. doi:10.5194/tc-16-2127-2022 journal article open access
  19. Evangeliou N, Grythe H, Klimont Z, Heyes C, Eckhardt S, Lopez-Aparicio S et al. (2020). Atmospheric transport is a major pathway of microplastics to remote regions. Nature Communications. doi:10.1038/s41467-020-17201-9 journal article open access
  20. Science Media Centre (UK) (2026). Expert reaction to a study investigating global atmospheric microplastic emissions. Science Media Centre, London. www.sciencemediacentre.org/expert-reaction-to-a-study-investigating-global-atmospheric-microplastic-emissions/ web open access
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Evidence levels and provenance

AConsensus
Multiple independent studies or a systematic review plus a statement by a scientific body.
BWell supportedUsed on this page
Several independent studies with concordant findings.
CLimitedUsed on this page
Few studies, narrow conditions, or methodological caveats.
DDisputedUsed on this page
Conflicting results; both sides are shown.
EUnknownUsed on this page
No reliable evidence found; the search scope is stated.
PProvenanceUsed on this page
Provenance: checked against the primary record. A separate category, not an evidence grade: used for bibliographic facts, legal texts, official metadata, definitions quoted from a standard, the site's own arithmetic and statements about the site's process.

Editorial categories of this site. A–E grade scientific findings, per claim, with a one-line rationale; D and E are not lower rungs of the A–C scale. P is not a grade: it marks facts checked against their primary record.