
What is micropollution and why is it a concern for the environment and human health?
Plastics are some of the most versatile man-made products. Being durable and lightweight, they've integrated into nearly every facet of everyday life - from food packaging to toiletries to vehicles to textiles. However, the resulting proliferation of plastic use has come with the significant downside – microscopic fragments of plastic accumulating in the environment (this development can be referred to as micropollution). The growing presence brings risks for ecosystems and human health, which are briefly outlined in this article.
Sources of micropollution
Microplastics can be defined as plastics smaller than 5mm (approximately the length of an average red ant)1. Microplastics can either enter the environment at the micro-sized scale (primary microplastics) or fragment from larger, ‘macro’-sized plastics already in the environment (secondary microplastics). Primary microplastics manufactured at the micro-scale are typically used in industrial and domestic products including cosmetics, cleansers/exfoliators, and air-blasting media, as well as preproduction pellets for plastic production. Secondary microplastics are plastic fragments resulting from the mechanical, chemical, or biodegradation of larger plastic debris, such as the particles resulting from the breakdown of plastic bags2.
Microfibres are generally defined as any natural or synthetic microscopic fibres shed from textiles or related fibre-based products, with a size only about 1/5 the diameter of a human hair3. All textiles shed microfibres, including natural (derived from plants and animals), synthetic (derived from plastics) and semi-synthetic (artificially produced plant-based) textiles. Clothes and textiles are the main sources of microfiber pollution4; however microfibers also come from a range of industrial textile applications5:
- Industrial textiles (e.g. carpets)
- Home textiles (e.g. bedding furniture, towels)
- Automotive textiles (e.g. seating fabric)
- Geotextiles (e.g. those used in construction)
- Cigarettes
- Fishing lines and nets
- Personal care products.
Sources of micropollution
Micropollution as environmental and human health hazard
The key characteristics of micropollutants which pose danger to humans and the environment
- Small size that facilitates widespread distribution in the environment
- Lack of biodegradability
- Negative impacts on the environment and human health.
Distribution in the environment
Microplastics and microfibres have been found in virtually every type of habitat on the planet, including the deep ocean6, on coastlines7, in Artic seawater8, in freshwater lakes and rivers9, in soil10, on mountaintops11, and in the air12. The abundance of micropollutants in the marine environment has been particularly well-documented:
- The Indian Ocean has approximately 4 billion microfibres per square km of sediment13
- Synthetic microfibres account for over 90% of the microplastic pollution identified in Arctic seawater14
- The most commonly found type of synthetic microfibre in the ocean is polyester15.
Local geographical conditions can impact micropollution levels. For example, the Mediterranean Sea has been found to contain relatively high concentration of microfibres, despite the fact that it is remote from the largest pollution entry points, such as Asia and the US. This could be due to the Mediterranean Sea having the lower exchange and flow of water (it being a more closed water system compared to the other basins), resulting in higher pollution accumulation.
Lack of biodegradability
Biodegradation ultimately depends on how accessible the micronutrients of an item are to the microorganisms in the environment. Due to their unique molecular properties, plastics are fairly resistant to biodegradation16. Plastics are largely broken down in the environment by chemical and physical factors including UV radiation, temperature, and abrasion, and as a result may take hundreds of years to decompose. Microfibres also biodegrade slowly under natural conditions, if at all. Although natural and semi-synthetic fibres degrade faster than synthetic fibres, the speed of degradation between different polymers is currently under-researched17.
Existing evidence indicates that:
- A polyester fabric remained largely intact after 100 days both in laboratory conditions and in a composting environment18
- Natural microfibres and some semi-synthetics can biodegrade under the right conditions, and may degrade within weeks to months (e.g. natural fibres may be more likely to degrade in warm, moist environments in the presence of microorganisms and chemical, photochemical and mechanical abrasive forces)19
- Almost 80% of the microfibres identified in various oceanic basins are cellulosic (i.e. cotton, linen and regenerated cellulose like rayon and viscose) - this suggests that natural and semi-synthetic fibres may persist in the environment longer than we would expect them to20. One reason that cellulosic fibres may persist in the environment is because textiles often contain residues of chemicals used in fibre production and textiles processing that can interfere with the nutritional value of the fibre to microorganisms21. However, the extent to which these chemicals can interfere with the deterioration of different materials remains an open question.
Lack of biodegradability in micropollutants presents a problem because they:
- Continue to accumulate in the environment
- Can serve as breeding grounds for pathogens22
- Can act as concentrators for contaminants such as metals and other chemicals23
- Can be easily ingested by organisms.
Negative impact on the environment
Once in the environment, microplastics and microfibres can be easily ingested by marine and terrestrial fauna. In marine environments, crustaceans (such as krill, shrimps, crabs) , shellfish, zooplankton, and fish often mistake micropollutants for food24. Over one third of UK-caught fish were found to contain microplastics in their gastrointestinal tracts. Due to their size and shape, microfibres are significantly more likely to be ingested - nearly half of the microplastics found in the guts of common tropical fish were microfibres25.
Micropollutants also move up the food chain and eventually contaminate human food: microplastics and microfibres have been found in bottled water, tap water, beer, salt, shellfish, fish, birds, vegetables, and fruit26. Humans are estimated to consume between 39-52 thousand microfibre particles per year, and to inhale between 35-69 thousand particles (mostly fibres), although these figures are likely to be underestimated27. These estimates roughly equate to consuming, either through ingestion or through inhalation, a paper clip’s worth of microfibres annually28.
While the effects of micropollution are still not fully understood, there is some evidence of negative impact:
- In the aquatic species, microfibre exposure has been linked to endocrine disruption, toxicity, gut blockages, reduced reproduction and death; the uptake of microplastics allows for the transfer of innate and adsorbed toxins into the organism, which can affect reproduction, impair development, and induce genetic aberrations in invertebrates, fish and amphibians29
- the ingestion of prey containing microplastics by organisms on the higher levels of the food chain (i.e. ‘indirect ingestion’ or ‘secondary poisoning’) can lead to the bioaccumulation of toxic chemicals30
- For humans, microplastics can be consumed through the ingestion of contaminated shellfish and fish, but also from some canned foods, honey, sugar, table salt, root crops, leaf crops, meat, and beverages including milk, drinking water, and beer31; humans are also exposed to inhalation of airborne particles and dermal exposure. Atmospheric microfibre exposure has been linked to respiratory complications, as well as reproductive, carcinogenic, and mutagenic effects32.
There has been limited research on the effects of microplastics on terrestrial organisms, although similar exposure pathways are likely to exist on land, as soil organisms, including earthworms and collembola, have been shown to carry microplastics in their gastrointestinal tracts33.
Micropollution can also cause negative economic impacts on the tourism and fishing industries: tourists may avoid engaging in water-based recreational activities or consuming local seafood in regions where microplastic pollution is a problem.
Effects on organisms | Effects on humans | |
---|---|---|
Reduced growth‚ reproduction and survival of water fleas and amphipods34 | Respiratory complications‚ including obstructive lung disease43 | |
Gut blockages and nutritional deficiency in fish35 | Endocrine disruption and cancer (from bisphenol A (BPA))44 | |
Reduced feeding in mussels‚ worms‚ and crabs36 | Inflammation and fibrosis45 | |
Reduced growth in crabs37 | Reproductive dysfunction‚ cancer and mutations caused by plasticisers46 | |
Toxicity and mortality in zooplankton38 | Microplastics could permeate biological membranes and enter organs47 | |
Translocation to organs after consumption in crabs39 | Presence in lung tissue49 | |
Toxicity and endocrine disruptions40 | Found in placenta50 | |
Impaired development and reproduction in invertebrates‚ fish and amphibians caused by plasticisers41 | ||
Bioaccumulation of toxins in larger organisms through indirect digestion42 | ||
Crossing the brain barrier in mice48 |
Observed effects on microfibre exposure on organisms and humans
Reduced growth‚ reproduction and survival of water fleas and amphipods34
- Effects on humans
- Respiratory complications‚ including obstructive lung disease43
Gut blockages and nutritional deficiency in fish35
- Effects on humans
- Endocrine disruption and cancer (from bisphenol A (BPA))44
Reduced feeding in mussels‚ worms‚ and crabs36
- Effects on humans
- Inflammation and fibrosis45
Reduced growth in crabs37
- Effects on humans
- Reproductive dysfunction‚ cancer and mutations caused by plasticisers46
Toxicity and mortality in zooplankton38
- Effects on humans
- Microplastics could permeate biological membranes and enter organs47
Translocation to organs after consumption in crabs39
- Effects on humans
- Presence in lung tissue49
Toxicity and endocrine disruptions40
- Effects on humans
- Found in placenta50
Impaired development and reproduction in invertebrates‚ fish and amphibians caused by plasticisers41
- Effects on humans
Bioaccumulation of toxins in larger organisms through indirect digestion42
- Effects on humans
Crossing the brain barrier in mice48
- Effects on humans
How significant is the problem? The current scale and the projected pace of micropollution
Micropollution projections vary; based on available data, we estimate that around 1-5.6 million metric tonnes (MMT) could enter the environment every year. Given their microscopic size, this is a material volume of pollution – the higher estimates reach over 10% of global annual mismanaged plastic waste50. The global release of microplastics into the ocean is estimated to be between 0.8 and 2.5 million tonnes per year,.
Despite these concerns, microplastic and microfibre pollution is still largely unregulated51. If left unaddressed, growth in textile consumption is likely to exacerbate it even more. By 2030, with the continuing increase of global apparel consumption and fibre production, annual microfibre release into the environment could increase by 54% by 2030 (or to approximately 0.5 – 6.0 MMT per annum)52. Another estimate suggests that further 22 MMT of synthetic microfibres could enter the environment by 205053. Microplastic pollution can also be expected to grow, as the production of many microplastics sources, especially vehicle tyres and pre-production plastics, is projected to increase over the next 15 years54.
For a detailed overview of the challenges and potential solutions to micropollution, please see the SII reports on microfibers https://www.firstsentier-mufg-sustainability.com/research/Microfibres.html and microplastics pollution https://www.firstsentier-mufg-sustainability.com/research/microplastics-05-2020.html.
References
1 Browne, M. A. et al. (2008) ‘Ingested Microscopic Plastic Translocates to the Circulatory System of the Mussel, Mytilus edulis (L.)’, Environmental Science & Technology, 42, pp. 5026–5031.
2 Carney Almroth, B. and Eggert, H. (2019) ‘Marine plastic pollution: Sources, impacts, and policy issues’, Review of Environmental Economics and Policy, 13(2), pp. 317–326. doi: 10.1093/reep/rez012.
3 Cornish Plastic Pollution Coalition (2018) ‘Bio-Bead pollution on our beaches’, (July), pp. 1–74.
4 UL (2019) Addressing the environmental impact of microfibers in textiles.
5 European Commission (2013) MSDF Guidance on Monitoring Marine Litter. doi: 10.2788/99475; Watts, A. J. R. et al. (2014) ‘Uptake and retention of microplastics by the shore crab carcinus maenas’, Environmental Science and Technology, 48(15), pp. 8823–8830. doi: 10.1021/es501090e.
6 German Federal Institute for Risk Assessment (BfR) (2018) BfR Consumer Monitor 08 | 2018.
7 GESAMP (2015) Sources, fate and effects of microplastics in the marine environment: a global assessment. London, UK.
8 Geyer, R., Jambeck, J. R. and Law, K. L. (2017) ‘Production, use, and fate of all plastics ever made’, Science Advances, 3(e1700782).
9 European Bioplastics (2018) ‘What are bioplastics? Material types, terminology, and labels – an introduction’, pp. 1–4; Greenpeace (2016) Global Cosmetics and Personal Care companies’ Microbead commitment ranking; Hernandez, E., Nowack, B. and Mitrano, D. M. (2017) ‘Polyester Textiles as a Source of Microplastics from Households: A Mechanistic Study to Understand Microfiber Release during Washing’, Environmental Science and Technology, 51(12), pp. 7036–7046. doi: 10.1021/acs.est.7b01750.
10 Eunomia and ICF (2018) ‘Investigating options for reducing releases in the aquatic environment of microplastics emitted by (but not intentionally added in) products - Final Report’, Report for DG Env EC, Vol. 62, N(February), p. 335.
11 Hidalgo-Ruz, V. et al. (2012) ‘Microplastics in the marine environment: A review of the methods used for identification and quantification’, Environmental Science and Technology, 46(6), pp. 3060–3075. doi: 10.1021/es2031505.
12 Horton, A. A. et al. (2017) ‘Microplastics in freshwater and terrestrial environments: Evaluating the current understanding to identify the knowledge gaps and future research priorities’, Science of the Total Environment. Elsevier B.V., 586, pp. 127–141. doi: 10.1016/j.scitotenv.2017.01.190;
13 Kane, I. A. et al. (2020) ‘Seafloor microplastic hotspots controlle by deep-sea circulation’, Science, 368(6495), pp. 1140–1145. doi: 10.1126/science.aba5899.
14 Karbalaei, S. et al. (2018) ‘Occurrence, sources, human health impacts and mitigation of microplastic pollution’, Environmental Science and Pollution Research. Environmental Science and Pollution Research, 25(36), pp. 36046–36063. doi: 10.1007/s11356-018-3508-7.
15 Kazimirova, A. et al. (2016) ‘Automotive airborne brake wear debris nanoparticles and cytokinesis-block micronucleus assay in peripheral blood lymphocytes: A pilot study’, Environmental Research. Elsevier, 148, pp. 443–449. doi: 10.1016/j.envres.2016.04.022.
16 Booth, A. M. et al. (2020) ‘Handbook of Microplastics in the Environment’, Handbook of Microplastics in the Environment, (October). doi: 10.1007/978-3-030-10618-8.
17 Lassen, C. et al. (2015) Microplastics: Occurrence, effects and sources of releases to the environment in Denmark, Danish Environmental Protection Agency.
18 Latini, G., De Felice, C. and Verrotti, A. (2004) ‘Plasticizers, infant nutrition and reproductive health’, Reproductive Toxicology, 19(1), pp. 27–33. doi: 10.1016/j.reprotox.2004.05.011.
19 Australian Government: Department of Agriculture Water and the Environment (2021) National Plastics Plan 2021. Canberra; Barnes, D. K. A. et al. (2009) ‘Accumulation and Fragmentation of Plastic Debris in Global Environments’, Philosophical Transactions: Biological Sciences, 364(1526), pp. 1985–1998; Liu, F. et al. (2020) ‘Microplastics removal from treated wastewater by a biofilter’, Water (Switzerland), 12(4), pp. 1–11. doi: 10.3390/W12041085.
20 UL (2019) Addressing the environmental impact of microfibers in textiles.
21 Federal Department of the Environment Transport Energy and Communications (2003) Ban on the use of sludge as a fertiliser. Available at: https://www.admin.ch/gov/en/start/documentation/media-releases.msg-id-1673.html (Accessed: 8 April 2021).
22 Booth, A. M. et al. (2020) ‘Handbook of Microplastics in the Environment’, Handbook of Microplastics in the Environment, (October). doi: 10.1007/978-3-030-10618-8.
23 Botterell, Z. L. R. et al. (2019) ‘Bioavailability and effects of microplastics on marine zooplankton: A review’, Environmental Pollution. Elsevier Ltd, 245(2019), pp. 98–110. doi: 10.1016/j.envpol.2018.10.065; Boucher, J. and Friot, D. (2017) Primary microplastics in the oceans (IUCN).
24 Barnes, D. K. A. et al. (2009) ‘Accumulation and Fragmentation of Plastic Debris in Global Environments’, Philosophical Transactions: Biological Sciences, 364(1526), pp. 1985–1998; Lusher, A. L., McHugh, M. and Thompson, R. C. (2013) ‘Occurrence of microplastics in the gastrointestinal tract of pelagic and demersal fish from the English Channel’, Marine Pollution Bulletin, 67(1–2), pp. 94–99. doi: 10.1016/j.marpolbul.2012.11.028; M. Spuijbroek (2019) Textile Waste in Mainland China.
25 Barnes, D. K. A. et al. (2009) ‘Accumulation and Fragmentation of Plastic Debris in Global Environments’, Philosophical Transactions: Biological Sciences, 364(1526), pp. 1985–1998; Maagoe, V. (2016) ‘Review study on the Regulation (EC) No 1222/2009 on the labelling of tyres’, (1222), p. 152.
26 Magnusson, K. et al. (2016) Swedish sources and pathways for microplastics to the marine environment: A review of existing data; Magnusson, K. and Norén, F. (2014) ‘Screening of microplastic particles in and down-stream a wastewater treatment plant’, IVL Swedish Environmental Research Institute, C 55(C), p. 22; Manshoven, S. et al. (2019) ‘Textiles and the environment in a circular economy’, European Topic Centre on Waste and Materials in a Green Economy, (November), pp. 1–60.
27 Van der Meulen, M. D. et al. (2014) ‘Socio-economic impact of microplastics in the 2 Seas, Channel and France Manche Region: an initial risk assessment’, MICFO Interreg project IVa.
28 Browne, M. A. et al. (2008) ‘Ingested Microscopic Plastic Translocates to the Circulatory System of the Mussel, Mytilus edulis (L.)’, Environmental Science & Technology, 42, pp. 5026–5031.
29 European Chemicals Agency (2020) ‘Opinion of the Committee for Risk Assessment and Opinion of the Committee for Socio-economic Analysis on an Annex XV dossier proposing restrictions of the manufacture, placing on the market or use of a substance within the EU’. Helsinki, Finland.
30 European Chemicals Agency (EHCA) (2019b) Annex XV Restriction Report 2019: Proposal for Restriction (intentionally added microplastics). Helsinki, Finland.
31 European Commission (2013) MSDF Guidance on Monitoring Marine Litter. doi: 10.2788/99475.
32 Excell, C. et al. (2018) Legal Limits on Single-Use Plastics and Microplastics: A Global Review of National Laws and Regulation, United Nations Environment Programme; De Falco, F. et al. (2019) ‘The contribution of washing processes of synthetic clothes to microplastic pollution’, Scientific Reports. Springer US, 9(1), pp. 1–11. doi: 10.1038/s41598-019-43023-x.
33 European Commission (2008) Commission Staff Working Document: Accompanying document to the Proposal for a Directive of the European Parliament and of the Council on Labelling of Tyres with Respect to Fuel Efficiency and Other Essential Parameters – Impact Assessment. Brussels.
34 Ziajahromi, S., Kumar, A., Neale, P. A. & Leusch, F. D. L. Impact of Microplastic Beads and Fibers on Waterflea (Ceriodaphnia dubia) Survival, Growth, and Reproduction: Implications of Single and Mixture Exposures. Environ. Sci. Technol. 51, 13397–13406 (2017).
35 Zhao, Y., Qiao, R., Zhang, S. & Wang, G. Metabolomic profiling reveals the intestinal toxicity of different length of microplastic fibers on zebrafish (Danio rerio). J. Hazard. Mater. 403, 123663 (2021).
36 Zhao, Y., Qiao, R., Zhang, S. & Wang, G. Metabolomic profiling reveals the intestinal toxicity of different length of microplastic fibers on zebrafish (Danio rerio). J. Hazard. Mater. 403, 123663 (2021).
37 Watts, A. J. R., Urbina, M. A., Corr, S., Lewis, C. & Galloway, T. S. Ingestion of Plastic Microfibers by the Crab Carcinus maenas and Its Effect on Food Consumption and Energy Balance. Environ. Sci. Technol. 49, 14597–14604 (2015).
38 Jemec, A., Horvat, P., Kunej, U., Bele, M. & Kržan, A. Uptake and effects of microplastic textile fibers on freshwater crustacean Daphnia magna. Environ. Pollut. 219, 201–209 (2016).
39 Brennecke, D. et al. Ingested microplastics (>100μm) are translocated to organs of the tropical fiddler crab Uca rapax. Mar. Pollut. Bull. 96, 491–495 (2015).
40 Zhao, Y., Qiao, R., Zhang, S. & Wang, G. Metabolomic profiling reveals the intestinal toxicity of different length of microplastic
fibers on zebrafish (Danio rerio). J. Hazard. Mater. 403, 123663 (2021).
41 Oehlmann, J. et al. (2009) ‘A critical analysis of the biological impacts of plasticizers on wildlife’,Philosophical Transactions of the Royal Society B: Biological Sciences, 364, pp. 2047–2062. doi: 10.1098/rstb.2008.0242.
42 Browne, M. A. et al. (2008) ‘Ingested Microscopic Plastic Translocates to the Circulatory System of the Mussel, Mytilus edulis (L.)’, Environmental Science & Technology, 42, pp. 5026–5031.;
Farrell, P. and Nelson, K. (2013) ‘Trophic level transfer of microplastic: Mytilus edulis (L.) to Carcinus maenas (L.)’, Environmental Pollution. Elsevier Ltd, 177, pp. 1–3. doi: 10.1016/j.envpol.2013.01.046.;
Setälä, O., Fleming-Lehtinen, V. and Lehtiniemi, M. (2014) ‘Ingestion and transfer of microplastics in the planktonic food web’, Environmental Pollution. Elsevier Ltd, 185, pp. 77–83. doi: 10.1016/j.envpol.2013.10.013.;
Watts, A. J. R. et al. (2014) ‘Uptake and retention of microplastics by the shore crab Carcinus maenas’, Environmental Science and Technology, 48. doi: 10.1021/es501090e.;
Horton, A. A. et al. (2017) ‘Microplastics in freshwater and terrestrial environments: Evaluating the current understanding to identify the knowledge gaps and future research priorities’, Science of the Total Environment. Elsevier B.V., 586, pp. 127–141. doi: 10.1016/j.scitotenv.2017.01.190.;
Scudo, A. (2017) Intentionally added microplastics in products.
43 Lai, P. S. & Christiani, D. C. Long term respiratory health effects in textile workers. Curr. Opin. Pulm. Med. 19, 152–157 (2013).
44 Acharya, S., Rumi, S. S., Hu, Y. & Abidi, N. Microfibers from synthetic textiles as a major source of microplastics in the environment: A review. Text. Res. J. 91, 2136–2156 (2021).
45 Oliveira, M., Almeida, M. and Miguel, I. (2019) ‘A micro(nano)plastic boomerang tale: A never ending story?’, Trends in Analytical Chemistry. Elsevier Ltd, 112, pp. 196–200. doi: 10.1016/j.trac.2019.01.005.;
Zhang, J., Wang, L. and Kannan, K. (2020) ‘Microplastics in house dust from 12 countries and associated human exposure’, Environment International. Elsevier, 134, p. 105314. doi: 10.1016/j.envint.2019.105314.
46 Wright and Kelly 2017; Oliveira, Almeida and Miguel 2019;
Latini, De Felice and Verrotti 2004; Wright and Kelly 2017
47 Oliveira, M., Almeida, M. and Miguel, I. (2019) ‘A micro(nano)plastic boomerang tale: A never ending story?’, Trends in Analytical Chemistry. Elsevier Ltd, 112, pp. 196–200. doi: 10.1016/j.trac.2019.01.005.
48 Shan, Sh. Et all (2022) Polystyrene nanoplastics penetrate across the blood-brain barrier and induce activation of microglia in the brain of mice (https://pubmed.ncbi.nlm.nih.gov/35302003/)
49 Jenner, L. et al (2022) Detection of microplastics in human lung tissue using μFTIR spectroscopy (https://www.sciencedirect.com/science/article/pii/S0048969722020009)
50 Ragusa, A. et al (2021) Plasticenta: First evidence of microplastics in human placenta https://www.sciencedirect.com/science/article/pii/S0160412020322297)
51 UNEP, From pollution to solution (2021); OECD, Global Plastics Outlook (2022); Our World in Data
52 Andrady, A. L. (2011) ‘Microplastics in the marine environment’, Marine Pollution Bulletin. Elsevier Ltd, 62(8), pp. 1596–1605. doi: 10.1016/j.marpolbul.2011.05.030.
53 Farrell, P. and Nelson, K. (2013) ‘Trophic level transfer of microplastic: Mytilus edulis (L.) to Carcinus maenas (L.)’, Environmental Pollution. Elsevier Ltd, 177, pp. 1–3. doi: 10.1016/j.envpol.2013.01.046.
54 Federal Department of the Environment Transport Energy and Communications (2003) Ban on the use of sludge as a fertiliser. Available at: https://www.admin.ch/gov/en/start/documentation/media-releases.msg-id-1673.html (Accessed: 8 April 2021).
55 U.S. Environmental Protection Agency (EPA) (2004) ‘Report to Congress on Impacts and Control of Combined Sewer Overflows and Sanitary Sewer Overflows’, Water, 51(October), pp. 1–680.