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Marine plastic pollution
Marine plastic pollution
from Wikipedia
The pathway by which plastics enters the world's oceans

Marine plastic pollution is a type of marine pollution by plastics, ranging in size from large original material such as bottles and bags, down to microplastics formed from the fragmentation of plastic material. Marine debris is mainly discarded human rubbish which floats on, or is suspended in the ocean. Eighty percent of marine debris is plastic.[1][2] Microplastics and nanoplastics result from the breakdown or photodegradation of plastic waste in surface waters, rivers or oceans. Recently, scientists have uncovered nanoplastics in heavy snow, more specifically about 3,000 tons that cover Switzerland yearly.[3]

It is approximated that there is a stock of 86 million tons of plastic marine debris in the worldwide ocean as of the end of 2013, assuming that 1.4% of global plastics produced from 1950 to 2013 has entered the ocean and has accumulated there.[4] Global consumption of plastics is estimated to be 300 million tonnes per year as of 2022, with around 8 million tonnes ending up in the oceans as macroplastics.[5][6] Approximately 1.5 million tonnes of primary microplastics end up in the seas. Around 98% of this volume is created by land-based activities, with the remaining 2% being generated by sea-based activities.[6][7][8] It is estimated that 19–23 million tonnes of plastic leaks into aquatic ecosystems annually.[9] The 2017 United Nations Ocean Conference estimated that the oceans might contain more weight in plastics than fish by the year 2050.[10]

Oceans are polluted by plastic particles ranging in size from large original material such as bottles and bags, down to microplastics formed from the fragmentation of plastic material. This material is only very slowly degraded or removed from the ocean so plastic particles are now widespread throughout the surface ocean and are known to be having deleterious effects on marine life.[11] Discarded plastic bags, six-pack rings, cigarette butts and other forms of plastic waste which finish up in the ocean present dangers to wildlife and fisheries.[12] Aquatic life can be threatened through entanglement, suffocation, and ingestion.[13][14][15] Fishing nets, usually made of plastic, can be left or lost in the ocean by fishermen. Known as ghost nets, these entangle fish, dolphins, sea turtles, sharks, dugongs, crocodiles, seabirds, crabs, and other creatures, restricting movement, causing starvation, laceration, infection, and, in those that need to return to the surface to breathe, suffocation.[16] There are various types of ocean plastics causing problems to marine life. Bottle caps have been found in the stomachs of turtles and seabirds, which have died because of the obstruction of their respiratory and digestive tracts.[17] Ghost nets are also a problematic type of ocean plastic as they can continuously trap marine life in a process known as "ghost fishing".[18]

The 10 largest emitters of oceanic plastic pollution worldwide are, from the most to the least, China, Indonesia, Philippines, Vietnam, Sri Lanka, Thailand, Egypt, Malaysia, Nigeria, and Bangladesh,[19] largely through the Yangtze, Indus, Yellow River, Hai, Nile, Ganges, Pearl River, Amur, Niger, and Mekong, and accounting for "90 percent of all the plastic that reaches the world's oceans".[20][21] Asia was the leading source of mismanaged plastic waste, with China alone accounting for 2.4 million metric tons.[22] The Ocean Conservancy has reported that China, Indonesia, Philippines, Thailand, and Vietnam dump more plastic in the sea than all other countries combined.[23]

Plastics accumulate because they do not biodegrade in the way many other substances do. They will photodegrade on exposure to the sun, but they do so properly only under dry conditions, and water inhibits this process.[24] In marine environments, photo-degraded plastic disintegrates into ever-smaller pieces while remaining polymers, even down to the molecular level. When floating plastic particles photodegrade down to zooplankton sizes, jellyfish attempt to consume them, and in this way the plastic enters the ocean food chain.[25][26]

Solutions to marine plastic pollution, along with plastic pollution within the whole environment will be intertwined with changes in manufacturing and packaging practices, and a reduction in the usage, in particular, of single or short-lived plastic products. Many ideas exist for cleaning up plastic in the oceans including trapping plastic particles at river mouths before entering the ocean, and cleaning up the ocean gyres.[2]

Scope of the problem

[edit]
A woman and a boy collecting plastic waste at a beach during a cleanup exercise in Ghana.
An exhibit at the Mote Marine Laboratory that displays plastic bags in the ocean that look similar to jellyfish
Atlantic Ocean marine plastic on a beach in Tenerife

Marine pollution caused by plastic substances is recognized as an issue of the highest magnitude, from a pollution perspective.[27] A majority of plastics used in people's day to day lives are never recycled. Single use plastics of this kind contribute significantly to the 8 million tons of plastic waste found in the ocean each year.[2] If this trend continues, by the year 2050 there will be more plastic than fish in the ocean by weight.[28] In just the first decade of the century, more plastic has been created than all the plastic in history up until the year of 2000 and a majority of that plastic is not recycled. One estimate of the historic production of plastic gives a figure of 8,300 million metric tonnes (Mt) for global plastic production up to 2015, of which 79% have been accumulated in landfills or the natural environment.[29] According to the IUCN, this number has grown to 14 million tons of plastic.[2] There is an estimated 15 to 51 trillion pieces of plastic amongst all of the world's oceans stretching from the top of ocean to the seafloor.[30] Oceans are Earth's deepest and most extensive basins with average depths of the abyssal plains being about 4 km beneath sea level. Gravity will naturally move and transfer materials from land to the ocean, with the ocean becoming the end-repository.[31] Oceanic plastic pollution is remarkable for the sheer ubiquity of its presence, from ocean trenches, within deep sea sediment, on the ocean floor and ocean ridges to the ocean surface and coastal margins of oceans. Even remote island atolls can have beaches loaded with plastic from a faraway source. At the ocean surface, plastic debris is concentrated within circular structures of large areal extent, called ocean gyres. Ocean gyres form within all oceans, due to alternating patterns of zonal winds that drive equatorward interior transport in the subtropics, and poleward interior transport in subpolar oceans. Ocean currents concentrate plastic waste within the gyres.

Plastics have been increasingly manufactured because of their flexible, molding and durable qualities, which provides plastic with a myriad of useful applications. Plastics are remarkably resistant to natural weathering processes that break down many other materials at the Earth's surface. Ocean processes, including storms, wave action, ocean currents, hydration, and surface exposure to the atmospheric weathering processes (e.g. oxidation) and ultraviolet radiation, tend to break plastic particles into ever-decreasing sizes (resulting in microplastics), rather than organically digest or chemically alter plastic substances. Estimates of the total number and weight of plastic across five ocean gyre plastic concentration zones are of the order of 5.25 trillion particles weighing almost 300,000 tons.[32] The reduction in size of plastic particles to the millimeter and micro-scales allow plastic to settle within deep sea sediments, with perhaps four times as much plastic ending up within sediments compared to surface ocean waters.[33] Plastics are now a part of complex biogeochemical cycles with living organisms, such as cetaceans, seabirds, mammals, and bacteria, ingesting plastic.[34]

Over 300 million tons of plastic are produced every year, half of which is used in single-use products like cups, bags, and packaging. It is estimated that 19–23 million tonnes of plastic leaks into aquatic ecosystems annually.[9] It is impossible to know for sure, but it is estimated that about 150 million metric tons of plastic exists in our oceans. Plastic pollution makes up 80% of all marine debris from surface waters to deep-sea sediments. Because plastics are light, much of this pollution is seen in and around the ocean surface, but plastic trash and particles are now found in most marine and terrestrial habitats, including the deep sea, Great Lakes, coral reefs, beaches, rivers, and estuaries. Submarine canyons are important accumulation sites as well, contributing to the transfer of such debris to the deep sea.[35] The most eye-catching evidence of the ocean plastic problem are the garbage patches that accumulate in gyre regions. A gyre is a circular ocean current formed by the Earth's wind patterns and the forces created by the rotation of the planet.[36] There are five main ocean gyres: the North and South Pacific Subtropical Gyres, the North and South Atlantic Subtropical Gyres, and the Indian Ocean Subtropical Gyre. There are significant garbage patches in each of these.[37]

Larger plastic waste (macroplastics) can be ingested by marine species, filling their stomachs and leading them to believe they are full when in fact they have taken in nothing of nutritional value. This can bring seabirds, whales, fish, and turtles to die of starvation with plastic-filled stomachs. Marine species can also be suffocated or entangled in plastic garbage.[2]

Macroplastic waste can break can weather into smaller fragments of plastic debris, known as microplastics when they are smaller than 5mm in size. Sunlight exposure, temperature, humidity, waves, and wind begin to break the plastic down into pieces smaller than five millimeters long. Plastics can also be broken down by smaller organisms who will eat plastic debris, breaking it down into small pieces, and either excrete these microplastics or spit them out. In lab tests, it was found that amphipods of the species Orchestia gammarellus could quickly devour pieces of plastic bags, shredding a single bag into 1.75 million microscopic fragments.[38] Although the plastic is broken down, it is still a man-made material that does not biodegrade. It is estimated that approximately 90% of the plastics in the pelagic marine environment are microplastics.[36] There are also primary sources of microplastics, such as microbeads and nurdles. These microplastics are frequently consumed by marine organisms at the base of the food chain, like plankton and fish larvae, which leads to a concentration of ingested plastic up the food chain. Plastics are produced with toxic chemicals, so these toxic substances enter the marine food chain, including the fish that some humans eat.[39]

Types of sources and amounts

[edit]
Average estimated decomposition times of typical marine debris items. Plastic items are shown in blue.

Plastic waste entering the seas is increasing each year with much of the plastic entering the seas is in particles smaller than 5 millimetres.[41] As of 2016 it was estimated that there was approximately 150 million tonnes of plastic pollution in the world's oceans, estimated to grow to 250 million tonnes in 2025.[42] Another study estimated that in 2012, it was approximately 165 million tonnes.[43] In 2020 a study found that the Atlantic Ocean contains approximately ten times more plastic than was previously thought.[44] The largest single type of plastic pollution (~10%) and majority of large plastic in the oceans is discarded and lost nets from the fishing industry.[45]

The Ocean Conservancy reported that China, Indonesia, Philippines, Thailand, and Vietnam dump more plastic in the sea than all other countries combined.[46]

One study estimated that there are more than 5 trillion plastic pieces (defined into the four classes of small microplastics, large microplastics, meso- and macroplastics) afloat at sea.[47] In 2020, new measurements found more than 10 times as much plastic in the Atlantic Ocean than previously estimated to be there.[48][49]

In October 2019, when research indicated a substantial proportion of ocean plastic pollution comes from Chinese cargo ships,[50] an Ocean Cleanup spokesperson said: "Everyone talks about saving the oceans by stopping using plastic bags, straws and single use packaging. That's important, but when we head out on the ocean, that's not necessarily what we find."[51]

Almost 20% of plastic debris that pollutes ocean water, which translates to 5.6 million tonnes, comes from ocean-based sources. MARPOL, an international treaty, "imposes a complete ban on the at-sea disposal of plastics".[52][53] Merchant ships expel cargo, sewage, used medical equipment, and other types of waste that contain plastic into the ocean. In the United States, the Marine Plastic Pollution Research and Control Act of 1987 prohibits discharge of plastics in the sea, including from naval vessels.[54][55] Naval and research vessels eject waste and military equipment that are deemed unnecessary. Pleasure craft release fishing gear and other types of waste, either accidentally or through negligent handling. The largest ocean-based source of plastic pollution is discarded fishing gear (including traps and nets), estimated to be up to 90% of plastic debris in some areas.[56][57]

Continental plastic litter enters the ocean largely through storm-water runoff, flowing into watercourses or directly discharged into coastal waters.[58] Plastic in the ocean has been shown to follow ocean currents which eventually form into what is known as Great Garbage Patches.[59]

The impact of microplastic and macroplastic into the ocean is not subjected to infiltration directly by dumping of plastic into marine ecosystems, but through polluted rivers that lead or create passageways to oceans across the globe. Rivers can either act as a source or sink depending on the context. Rivers are thought to be a major source of plastic pollution for the ocean,[20][60] although possibly not as much as direct input from coastal populations.[61][62]

The amount of plastic that is recorded to be in the ocean is considerably less than the amount of plastic that is entering the ocean at any given time. According to a study done in the UK, there are "ten top" macroplastic dominant typologies that are solely consumer related (located in the table below).[63] Within this study, 192,213 litter items were counted with an average of 71% being plastic and 59% were consumer related macroplastic items.[63] Even though freshwater pollution is the major contributor to marine plastic pollution there is little studies done and data collection for the amount of pollution going from freshwater to marine. Majority of papers conclude that there is minimal data collection of plastic debris in freshwater environments and natural terrestrial environments, even though these are the major contributor. The need for policy change in production, usage, disposal, and waste management is necessary to decrease the amount and potential of plastic to enter freshwater environments.[64]

A 1994 study of the seabed using trawl nets in the north-western Mediterranean around the coasts of Spain, France, and Italy reported mean concentrations of debris of 1,935 items per square kilometre. Plastic debris accounted for 77%, of which 93% was plastic bags.[13]

Buoyancy

[edit]

Approximately half of the plastic material introduced to the marine environment is buoyant, but fouling by organisms can cause plastic debris to sink to the sea floor, where it may interfere with sediment-dwelling species and sedimental gas exchange processes. Several factors contribute to microplastic's buoyancy, including the density of the plastic it is composed of as well as the size and shape of the microplastic fragments themselves.[65] Microplastics can also form a buoyant biofilm layer on the ocean's surface.[66] Buoyancy changes in relation to ingestion of microplastics have been clearly observed in autotrophs because the absorption can interfere with photosynthesis and subsequent gas levels.[67] However, this issue is of more importance for larger plastic debris.

Plastic densities[68]
Plastic Type Abbreviation Density (g/cm3)
Polystyrene PS 1.04–1.08
Expanded Polystyrene EPS 0.01–0.04
Low-density Polyethylene LDPE 0.89–0.93
High-density Polyethylene HDPE 0.94–0.98
Polyamide PA 1.13–1.16
Polypropylene PP 0.85–0.92
Acrylonitrile-butadiene-styrene ABS 1.04–1.06
Polytetrafluoroethylene PTFE 2.10–2.30
Cellulose Acetate CA 1.30
Polycarbonate PC 1.20–1.22
Polymethyl methacrylate PMMA 1.16–1.20
Polyvinyl chloride PVC 1.38–1.41
Polyethylene terephthalate PET 1.38–1.41

Land-based sources

[edit]
Mismanaged plastic waste generation by country.

Estimates for the contribution of land-based plastic vary widely. While one study estimated that a little over 80% of plastic debris in ocean water comes from land-based sources, responsible for 800,000 tonnes (880,000 short tons) every year.[56] In 2015, it was calculated that 275 million tonnes (303 million short tons) of plastic waste was generated in 192 coastal countries in 2010, with 4.8 to 12.7 million tonnes (5.3 to 14 million short tons) entering the ocean – a percentage of only up to 5%.[19]

Most land-based plastic pollution enters the ocean from South, Southeast, and East Asia, with the largest emitters including China, Indonesia, Philippines, and India.[19][61]

A source that has caused concern is landfills. Most waste in the form of plastic in landfills are single-use items such as packaging. Discarding plastics this way leads to accumulation.[69] Although disposing of plastic waste in landfills has less of a gas emission risk than disposal through incineration, the former has space limitations. Another concern is that the liners acting as protective layers between the landfill and environment can break, thus leaking toxins and contaminating the nearby soil and water.[70] Landfills located near oceans often contribute to ocean debris because content is easily swept up and transported to the sea by wind or small waterways like rivers and streams. Marine debris can also result from sewage water that has not been efficiently treated, which is eventually transported to the ocean through rivers. Plastic items that have been improperly discarded can also be carried to oceans through storm waters.[56]

Microplastics

[edit]
Microplastics in the surface ocean 1950–2000 and projections beyond, in million metric tonnes
Polystyrene foam beads on an Irish beach
Great Pacific Garbage Patch – Pacific Ocean currents have created three "islands" of debris.[71]
Sample of microplastic collected by Oregon State University

A growing concern regarding plastic pollution in the marine ecosystem is the use of microplastics. Microplastics are beads of plastic less than 5 millimeters wide,[72] and they are commonly found in hand soaps, face cleansers, and other exfoliators. When these products are used, the microplastics go through the water filtration system and into the ocean, but because of their small size they are likely to escape capture by the preliminary treatment screens on wastewater plants.[73] These beads are harmful to the organisms in the ocean, especially filter feeders, because they can easily ingest the plastic and become sick. The microplastics are such a concern because it is difficult to clean them up due to their size, so humans can try to avoid using these harmful plastics by purchasing products that use environmentally safe exfoliates.

Because plastic is so widely used across the planet, microplastics have become widespread in the marine environment. For example, microplastics can be found on sandy beaches[74] and surface waters[75] as well as in the water column and deep sea sediment. Microplastics are also found within the many other types of marine particles such as dead biological material (tissue and shells) and some soil particles (blown in by wind and carried to the ocean by rivers). Population density and proximity to urban centers have been considered the main factors that influence the abundance of microplastics in the environment.

A greater concentration of microplastics have been associated with rainfall events. The runoff after rainfall on land, where plastic production and degradation rate of plastic debris is higher, could deliver these microplastics into the aquatic environment. The greater the rainfall, the stronger the erosion effect of surface runoff on land will be, and the more plastic debris will be transported.[76]

Microplastics enter waterways through many avenues including deterioration of road paint, tire wear and city dust entering the waterways, plastic pellets spilled from shipping containers, ghost nets and other synthetic textiles dumped into the ocean, cosmetics discharged and laundry products entering sewage water and marine coatings on ships degrading.[41]

Coatings used on ships are significant sources of plastic pollution - nearly 80% of plastic fragments collected in the German Bight were determined to have originated from marine coatings rather than land-based sources, based on their polymeric content.[77] Plastic pollution leached from coatings are usually based on polyvinyl chloride or poly(methyl methacrylate) polymers, whereas terrestrial plastics are usually made from polypropylene, polyethylene, and polyethylene terephthalate.[77] Coating surfaces degrade over time due to weathering and the action of waves on the coating surface. Compared with land-based plastics, pollution from marine coatings contains much higher quantities of chemical additives, such as adhesion promoters, biocides, crosslinkers, pigments, plasticizers, and UV absorbers. As such, marine coatings act as a source of toxic chemical substances into the ocean, in addition to microplastics.[78] Biocides are toxic chemical additives, typically heavy metals (though there is a push towards fouling-release technologies), which are added to prevent fouling attaching to the hull.[78] However, as the plastic polymer networks degrade, biocide previously within the polymeric "mesh" leaches into the ocean. The leaching of tributyltin (TBT) biocides from marine coatings was first identified in 1980 as the cause of imposex observed in dog whelks in coastal regions.[79] TBT compounds are endocrine disruptors, which have the ability to mimic sex hormones, which can result in imposex, rendering the non-target organism infertile. Manufacturers are trending towards fouling-release coating technologies, though these coatings have even higher quantities of chemical additives to address their inherent mechanical weakness. These coatings undergo degradation easily, and can act as a vehicle for the release of microplastics into the ocean. To date, the International Convention for the Prevention of Pollution from Ships (MARPOL) does not outline any regulations addressing the leaching of chemical-laced plastics from marine coatings,[80] though the International Maritime Organization (IMO) has set out international restrictions for a very limited number of biocidal compounds, such as TBT compounds in 2008, and Cybutryne (Irgarol 1051) in 2023.[81]

Upon reaching marine environments, due to their small size and low density, microplastics are transported over long distances via wind and surface ocean currents. The transportation is affected by their inherent characteristics (texture and shape) but also environmental factors such as flow velocity, matrix type and seasonal variability.[76] Numerical models are able to trace small plastic debris (micro- and meso-plastics) drifting in the ocean,[82] thus predicting their fate.

Some microplastics leave the sea and enter the air, as researchers from the University of Strathclyde discovered in 2020.[83] Some remain on the ocean's surface; microplastics account for 92% of plastic debris on the ocean's surface, according to a 2018 study.[84] And some sink to the ocean floor. Australia's national science agency CSIRO estimated that 14 million metric tons of microplastics are already on the ocean floor in 2020.[85] This represents an increase from a 2015 estimate that the world's oceans contain 93–236 thousand metric tons of microplastics[86][87] and a 2018 estimate of 270 thousand tons.[88]

A study of the distribution of eastern Pacific Ocean surface plastic debris (not specifically microplastic, although, as previously mentioned, most is likely microplastic) helps to illustrate the rising concentration of plastics in the ocean. By using data on surface plastic concentration (pieces of plastic per km2) from 1972 to 1985 (n=60) and 2002–2012 (n=457) within the same plastic accumulation zone, the study found the mean plastic concentration increase between the two sets of data, including a 10-fold increase of 18,160 to 189,800 pieces of plastic per km2.[89]

Arctic Ocean microplastics come mainly from Atlantic sources, especially Europe and North America.[90] Recent studies have revealed that the concentration of microplastics on glaciers or snow is surprisingly higher than even urban water bodies, even though microplastics are not directly used or produced near glaciers.[91] As of 2021, Europe and Central Asia account for around 16% of global microplastics discharge into the seas.[6][92]

A higher concentration of microplastics in glaciers indicates that transport via wind is a significant pathway to distribute microplastics in the environment.

Microplastics can accumulate in the whitecaps of ocean waves or sea foam and increase the stability of breaking waves, potentially affecting sea albedo or atmosphere-ocean gas exchange.[93] A study found that microplastics from oceans have been found in sea breeze and may re-enter the atmosphere.[94]

Microplastics can concentrate in the gills and intestines of marine life and can interfere with their feedings habits, typically resulting in death.[95] Microplastics have been shown to induce a lethargic swimming and feeding behavior in fish, mussels and nematodes, under severe overload situations. Microplastic size is an important feature for the production of toxic effects on the different organisms, however, the tissue structure and anatomy of each organism play an important role in the severity of the damage that these particles can produce.[76]

Microplastics impact on marine food web

Bioaccumulation of microplastics can have a huge effect on the food web, thus altering ecosystems and contributing to loss of biodiversity.[95] Once ingested, microplastics will either be egested or retained by an organism. If a predator consumes an organism that has retained microplastic, the predator will be indirectly consuming this plastic as part of its diet, in a process referred to as "trophic transfer'. Retention of plastics can be influenced by food availability and shape but will be governed by the size of the plastic. Ingested microplastics will typically be passed along the intestinal tract, then will either be adsorbed across the gut lining, become entrapped in the gut (i.e., intestinal blockage causing retention of plastic), or become incorporated into the animal's feces and egested.[96]

The ingestion of plastic by marine organisms has now been established at full ocean depth. Microplastic was found in the stomachs of hadal amphipods sampled from the Japan, Izu-Bonin, Mariana, Kermadec, New Hebrides and the Peru-Chile trenches. The amphipods from the Mariana Trench were sampled at 10,890 m and all contained microfibres.[97]

According to one recent research estimate, a person who consumes seafood will ingest 11 000 bits of microplastics per year. Even very minute microplastics have been discovered in human blood.[6][98][99]

Research studies

[edit]

The extent of microplastic pollution in the deep sea has yet to be fully determined, and as a result scientists are currently examining organisms and studying sediments to better understand this issue.[100][101][102] A 2013 study surveyed four separate locations to represent a wider range of marine habitats at depths varying from 1100–5000m. Three of the four locations had identifiable amounts of microplastics present in the top 1 cm layer of sediment. Core samples were taken from each spot and had their microplastics filtered out of the normal sediment. The plastic components were identified using micro-Raman spectroscopy; the results showed man-made pigments commonly used in the plastic industry.[103] In 2016, researchers used an ROV to collect nine deep-sea organisms and core-top sediments.[104] The nine deep-sea organisms were dissected and various organs were examined by the researchers on shore to identify microplastics with a microscope.[104] The scientists found that six out of the nine organisms examined contain microplastics which were all microfibers, specifically located in the GI tract.[104] Research performed by MBARI in 2013 off the west coast of North America and around Hawaii found that out of all the debris observed from 22 years of VARS database video footage, one-third of the items was plastic bags.[105] This debris was most common below 2000 m depth.[105] A recent study that collected organisms and sediments in the Abyssopelagic Zone of the Western Pacific Ocean extracted materials from samples and discovered that poly(propylene-ethylene) copolymer (40.0%) and polyethylene terephthalate (27.5%) were the most commonly detected polymers.[100]

Another study was conducted by collecting deep-sea sediment and coral specimens between 2011 and 2012 in the Mediterranean Sea, Southwest Indian Ocean, and Northeast Atlantic Ocean. Of the 12 coral and sediment samples taken, all were found with an abundance of microplastics.[33] Rayon is not a plastic but was included in the study due to being a common synthetic material. It was found in all samples and comprised 56.9% of materials found, followed by polyester (53.4%), plastics (34.1%) and acrylic (12.4%).[33] This study found that the amount of microplastics, in the form of microfibres, was comparable to that found in intertidal or subtidal sediments.[33] A 2017 study had a similar finding – by surveying the Rockall Trough in the Northeast Atlantic Ocean at a depth of more than 2200 meters, microplastic fibers were identified at a concentration of 70.8 particles per cubic meter.[101] This is comparable to amounts reported in surface waters. This study also looked at micropollution ingested by benthic invertebrates Ophiomusium lymani, Hymenaster pellucidus and Colus jeffreysianus and found that of the 66 organisms studied, 48% had ingested microplastics in quantities also comparable to coastal species.[101] A recent review of 112 studies found the highest plastic ingestion in organisms collected in the Mediterranean and Northeast Indian Ocean with significant differences among plastic types ingested by different groups of animals, including differences in colour and the type of prevalent polymers. Overall, clear fibre microplastics are likely the most predominant types ingested by marine megafauna around the globe.[102]

In 2020 scientists created what may be the first scientific estimate of how much microplastic currently resides in Earth's seafloor, after investigating six areas of ~3 km depth ~300 km off the Australian coast. They found the highly variable microplastic counts to be proportionate to plastic on the surface and the angle of the seafloor slope. By averaging the microplastic mass per cm3, they estimated that Earth's seafloor contains about 14 million tons of microplastic – about double the amount they estimated based on data from earlier studies – despite calling both estimates "conservative" as coastal areas are known to contain much more microplastic. These estimates are about one to two times the amount of plastic thought to currently enter the oceans annually.[106][107][108]

Two billion people worldwide lack adequate garbage collection facilities to capture harmful plastics. Improved wastewater treatment and stormwater management in many poor nations would prevent part of the 1.5 million tonnes of microplastics from entering the marine ecosystems each year.[109][110][111][112]

Toxic chemicals

[edit]

Toxic additives used in the manufacture of plastic materials can leach out into their surroundings when exposed to water.[113] Approximately 8000–19000 tonnes of additives are transported with buoyant plastic matrices globally with a significant portion also transported to the Arctic.[114] Waterborne hydrophobic pollutants collect and magnify on the surface of plastic debris,[115] thus making plastic far more deadly in the ocean than it would be on land.[1] Hydrophobic contaminants are also known to bioaccumulate in fatty tissues, biomagnifying up the food chain and putting pressure on apex predators and humans.[116] Some plastic additives are known to disrupt the endocrine system when consumed, others can suppress the immune system or decrease reproductive rates.[117]

Floating debris can also absorb persistent organic pollutants from seawater, including PCBs, DDT, and PAHs.[118] Plastic debris can absorb toxic chemicals from ocean pollution, potentially poisoning any creature that eats it.[119] Aside from toxic effects[120] when ingested some of these affect animal brain cells similarly to estradiol, causing hormone disruption in the affected wildlife.[121] A study discovered, when plastics eventually decompose, they produce potentially toxic bisphenol A (BPA) and PS oligomer into the water.[122] These toxins are believed to bring harm to the marine life living in the area. Bisphenol A (BPA) is a famous example of a plasticizer produced in high volumes for food packing from where it can leach into food, leading to human exposure. As an estrogen and glucocorticoid receptor agonist, BPA is interfering with the endocrine system and is associated with increased fat in rodents.[123]

Researchers collected seawater samples worldwide, and found that all samples contained polystyrene derivatives. Polystyrene is a plastic found in styrofoam and many household and consumer goods. The scientists then simulated the decomposition of polystyrene in the open ocean. The results of this simulation showed that polystyrene, which begins breaking down at temperatures of 86° and higher, breaks down into harmful chemicals, such as Bisphenol A (BPA, which can cause reproductive harm in animals), styrene monomer (a suspected carcinogen), and styrene trimer (a by-product of polystyrene).[124]

Plasticizers in microplastics have been linked to abnormal growth and reproductive problems in multiple animal models due to endocrine disruption. Microplastics have also been postulated to cause GI irritation, alteration of the microbiome, disturbance of energy and lipid metabolism, and oxidative stress.[95]

Organic pollutants, such as pesticides, can leach into organisms that ingest microplastics, along with dangerous metals such as lead and cadmium.[95]

Accumulation sites

[edit]
Pacific garbage on a black sand beach in Maui, Hawaii
North Pacific Subtropical Convergence Zone

Plastic debris tends to accumulate at the center of ocean gyres. The North Pacific Gyre, for example, has collected the Great Pacific Garbage Patch, which is now estimated to be one to twenty times the size of Texas (approximately from 700,000 to 15,000,000 square kilometers). There could be as much plastic as fish in the sea.[125] It has a very high level of plastic particulate suspended in the upper water column. In samples taken from the North Pacific Gyre in 1999, the mass of plastic exceeded that of zooplankton (the dominant animal life in the area) by a factor of six.[1][117]

Midway Atoll, in common with all the Hawaiian Islands, receives substantial amounts of debris from the garbage patch. Ninety percent plastic, this debris accumulates on the beaches of Midway where it becomes a hazard to the bird population of the island.[126][127]

Garbage patches

[edit]
Trash washed ashore in Hawaii from the Great Pacific Garbage Patch

A garbage patch is a gyre of marine debris particles caused by the effects of ocean currents and increasing plastic pollution by human populations. These human-caused collections of plastic and other debris are responsible for ecosystem and environmental problems that affect marine life, contaminate oceans with toxic chemicals, and contribute to greenhouse gas emissions. Once waterborne, marine debris becomes mobile. Flotsam can be blown by the wind, or follow the flow of ocean currents, often ending up in the middle of oceanic gyres where currents are weakest.

Environmental impacts

[edit]
Model results for the count density of planktonic plastic particles (red is more dense, green is less dense)[47]

The litter that is being delivered into the oceans is toxic to marine life, and humans. The toxins that are components of plastic include diethylhexyl phthalate, which is a toxic carcinogen, as well as lead, cadmium, and mercury.

Plankton, fish, and ultimately the human race, through the food chain, ingest these highly toxic carcinogens and chemicals. Consuming the fish that contain these toxins can cause an increase in cancer, immune disorders, and birth defects.[128] However, these toxins are not only found in fish but also in staple foods, drinking water, table salts, toothpaste, and other kinds of seafood. These issues can be found in Indonesia, which is the second largest contributor of plastic waste, where human stools were collected from fishermen finding that 50% had concentrations of microplastics. Each human stool that had microplastics had a concentration between 3.33 and 13.99 μg of microplastic per gram of feces.[129]

The majority of the litter near and in the ocean is made up of plastics and is a persistent pervasive source of marine pollution.[130] In many countries improper management of solid waste means there is little control of plastic entering the water system.[41] As of 2016, there are 5.25 trillion particles of plastic pollution that weigh as much as 270,000 tonnes. Since then, studies have found that the amount of plastic particles has increased to somewhere from 15 to 51 trillion particles in 2021.[131] This plastic is taken by the ocean currents and accumulates in large vortexes known as ocean gyres. The majority of the gyres become pollution dumps filled with plastic.

Research on floating plastic debris in the ocean was the fastest-growing topic among 56 sustainability topics examined in a study of scientific publishing by 193 countries over 2011 to 2019. Over nine years, global research documenting this phenomenon ballooned from 46 (2011) to 853 (2019) publications.[132]

Marine ecosystems

[edit]

Concern among experts has grown since the 2000s that some organisms have adapted to live on[133] floating plastic debris, allowing them to disperse with ocean currents and thus potentially become invasive species in distant ecosystems.[134] Marine animals can experience internal injuries, lacerations, infections, starvation, and diminished swimming ability from injesting plastic or getting entangled in plastic garbage.[135] Additionally, floating plastics aid in the spread of invasive marine organisms, endangering marine biodiversity and the food chain.[135] Research in 2014 in the waters around Australia[136] confirmed a wealth of such colonists, even on tiny flakes, and also found thriving ocean bacteria eating into the plastic to form pits and grooves. These researchers showed that "plastic biodegradation is occurring at the sea surface" through the action of bacteria, and noted that this is congruent with a new body of research on such bacteria. Their finding is also congruent with the other major research undertaken[137] in 2014, which sought to answer the riddle of the overall lack of build up of floating plastic in the oceans, despite ongoing high levels of dumping. Plastics were found as microfibres in core samples drilled from sediments at the bottom of the deep ocean. The cause of such widespread deep sea deposition has yet to be determined.

The hydrophobic nature of plastic surfaces stimulates rapid formation of biofilms,[136] which support a wide range of metabolic activities, and drive succession of other micro- and macro-organisms.[138]

Photodegradation of plastics

[edit]
Photodegraded plastic straw – a light touch breaks a straw into microplastics
Washed-up plastic waste on a beach in Singapore

The garbage patches are one of several oceanic regions where researchers have studied the effects and impact of plastic photodegradation in the neustonic layer of water.[139] Unlike organic debris, which biodegrades, plastic disintegrates into ever smaller pieces while remaining a polymer (without changing chemically). This process continues down to the molecular level.[140] Some plastics decompose within a year of entering the water, releasing potentially toxic chemicals such as bisphenol A, PCBs and derivatives of polystyrene.[141]

As the plastic flotsam photodegrades into smaller and smaller pieces, it concentrates in the upper water column. As it disintegrates, the pieces become small enough to be ingested by aquatic organisms that reside near the ocean's surface. Plastic may become concentrated in neuston, thereby entering the food chain. Disintegration means that much of the plastic is too small to be seen. Moreover, plastic exposed to sunlight and in watering environments produce greenhouse gases, leading to further environmental impact.[142]

As the plastic particles are primarily found in the pelagic layer of the ocean they experience high levels of photodegradation, which causes the plastics to break down into ever smaller pieces. These pieces eventually become so small that even microorganisms can ingest and metabolize them, converting the plastics into carbon dioxide. In some instances, these microplastics are absorbed directly into a microorganism's biomolecules.[143] However, before reaching this state, any number of organisms could potentially interact with these plastics.

Climate change and air pollution aspects

[edit]

Plastic pollution and climate change are linked together and the effects of both are complements.[144] The toxins released by plastic pollutants breaking down and releasing into the air are causing climate change rates to move up and worsen as a fast pace. The way that plastic contributes to climate change issues is because of the way plastic is made. Through fossil fuels being used to run machinery creating more plastic, it is released into the air resulting in greenhouse gas emissions.[145] The ocean contains millions of pounds of plastic residue and large pieces, but also contains most of the greenhouse gases produced.[145] The plastics in the oceans emit greenhouse gases while breaking down in the water.[146]

The greenhouse gases produced by the making of plastics makes it difficult for the ocean to trap in carbon and help slow the processes of climate change.[147] Another way that plastic consumption and pollution results in increasing climate change rates, is from incineration of plastic waste. This releases way more toxins into the air and then it all gets consumed by ocean water. The oceans end up taking up chemicals, but also the small pieces of plastic that were not fully broken down. This causes dirty marine water and affects the ecosystems living in the oceans.[148] The incineration of plastic products pushes black carbon into the air.[149] Black carbon comes from emissions and is a lead contributor to climate change.[150]

Effects on animals

[edit]
The feeding habit of sea turtles influences their reaction to artificial marine debris. (Video)

Plastic waste has reached all the world's oceans. This plastic pollution harms an estimated 100,000 sea turtles and marine mammals and 1,000,000 sea creatures each year.[151] Larger plastics (called "macroplastics") such as plastic shopping bags can clog the digestive tracts of larger animals when consumed by them[13] and can cause starvation through restricting the movement of food, or by filling the stomach and tricking the animal into thinking it is full. Microplastics on the other hand harm smaller marine life. For example, pelagic plastic pieces in the center of our ocean's gyres outnumber live marine plankton, and are passed up the food chain to reach all marine life.[152]

Fishing gear such as nets, ropes, lines, and cages often get lost in the ocean and can travel large distances which has negatively impacted many marine animals such as coral. The fishing gear is made up of non-biodegradable plastic in many different species of coral get tangled in which causes them to lose tissue and possibly die.[153]

Plastic pollution has the potential to poison animals, which can then adversely affect human food supplies.[154][155] Plastic pollution has been described as being highly detrimental to large marine mammals, described in the book Introduction to Marine Biology as posing the "single greatest threat" to them.[156] Some marine species, such as sea turtles, have been found to contain large proportions of plastics in their stomach.[155] When this occurs, the animal typically starves, because the plastic blocks the animal's digestive tract.[155] Sometimes marine mammals are entangled in plastic products such as nets, which can harm or kill them.[155]

Entanglement

[edit]
Sea turtle entangled in a ghost net

Entanglement in plastic debris has been responsible for the deaths of many marine organisms, such as fish, seals, turtles, and birds. These animals get caught in the debris and end up suffocating or drowning. Because they are unable to untangle themselves, they also die from starvation or from their inability to escape predators.[56] Being entangled also often results in severe lacerations and ulcers. It was estimated that at least 267 different animal species have suffered from entanglement and ingestion of plastic debris.[157][158] It has been estimated that over 400,000 marine mammals perish annually due to plastic pollution in oceans.[155] Marine organisms get caught in discarded fishing equipment, such as ghost nets. Ropes and nets used to fish are often made of synthetic materials such as nylon, making fishing equipment more durable and buoyant. These organisms can also get caught in circular plastic packaging materials, and if the animal continues to grow in size, the plastic can cut into their flesh. Equipment such as nets can also drag along the seabed, causing damage to coral reefs.[159]

Some marine animals find themselves tangled in larger pieces of garbage that cause just as much harm as the barely visible microplastics.[160] Trash that has the possibility of wrapping itself around a living organism may cause strangulation or drowning.[160] If the trash gets stuck around a ligament that is not vital for airflow, the ligament may grow with a malformation.[160] Plastic's existence in the ocean becomes cyclical because marine life that is killed by it ultimately decompose in the ocean, re-releasing the plastics into the ecosystem.[161][162]

Animals can also become trapped in plastic nets and rings, which can cause death. Plastic pollution affects at least 700 marine species, including sea turtles, seals, seabirds, fish, whales, and dolphins.[163] Cetaceans have been sighted within the patch, which poses entanglement and ingestion risks to animals using the Great Pacific Garbage Patch as a migration corridor or core habitat.[18]

Ingestion

[edit]
The remains of an albatross containing ingested flotsam

Many animals that live on or in the sea consume flotsam by mistake, as it often looks similar to their natural prey.[164] Plastic debris, when bulky or tangled, is difficult to pass, and may become permanently lodged in the digestive tracts of these animals. Especially when evolutionary adaptions make it impossible for the likes of turtles to reject plastic bags, which resemble jellyfish when immersed in water, as they have a system in their throat to stop slippery foods from otherwise escaping.[165] Thereby blocking the passage of food and causing death through starvation or infection.[166][167]

Many of these long-lasting pieces end up in the stomachs of marine birds and animals,[166] including sea turtles, and black-footed albatross.[121] This results in obstruction of digestive pathways, which leads to reduced appetite or even starvation.[168] In a 2008 Pacific Gyre voyage, Algalita Marine Research Foundation researchers began finding that fish are ingesting plastic fragments and debris. Of the 672 fish caught during that voyage, 35% had ingested plastic pieces.[169]

With the increased amount of plastic in the ocean, living organisms are now at a greater risk of harm from plastic consumption and entanglement. Approximately 23% of aquatic mammals, and 36% of seabirds have experienced the detriments of plastic presence in the ocean.[160] Since as much as 70% of the trash is estimated to be on the ocean floor, and microplastics are only millimeters wide, sealife at nearly every level of the food chain is affected.[170][171][172] Animals who feed off of the bottom of the ocean risk sweeping microplastics into their systems while gathering food.[173] Smaller marine life such as mussels and worms sometimes mistake plastic for their prey.[160][174]

Larger animals are also affected by plastic consumption because they feed on fish, and are indirectly consuming microplastics already trapped inside their prey.[173] Likewise, humans are also susceptible to microplastic consumption. People who eat seafood also eat some of the microplastics that were ingested by marine life. Oysters and clams are popular vehicles for human microplastic consumption.[173] Animals who are within the general vicinity of the water are also affected by the plastic in the ocean. Studies have shown 36% species of seabirds are consuming plastic because they mistake larger pieces of plastic for food.[160] Plastic can cause blockage of intestines as well as tearing of interior stomach and intestinal lining of marine life, ultimately leading to starvation and death.[160]

Some long-lasting plastics end up in the stomachs of marine animals.[166][175][176] Plastic attracts seabirds and fish. When marine life consumes plastic allowing it to enter the food chain, this can lead to greater problems when species that have consumed plastic are then eaten by other predators.

Multiple studies have found plastics and microplastics in the stomach contents of marine animals.[95][177][178]

The ingestion of large amounts of plastic debris, such as fish nets and ropes, can lead to marine animal's deaths via gastric impaction.[177]

Mammals and fish

[edit]

A 2021 literature review published in Science identified 1,288 marine species that are known to ingest plastic. Most of these species are fish.[179]

Sea turtles are affected by plastic pollution. Some species are consumers of jelly fish, but often mistake plastic bags for their natural prey. This plastic debris can kill the sea turtle by obstructing the oesophagus.[159] Baby sea turtles are particularly vulnerable according to a 2018 study by Australian scientists.[180]

Plastics are ingested by various species of whales, such as beaked whales, baleen whales, and sperm whales. They can mistake plastics for food and consume them accidentally when feeding on prey organisms that are gathered near plastics. Plastics can also enter their system if their prey already had synthetic plastic particles in their digestive tract via bioaccumulation.[18] Large amounts of plastics have been found in the stomachs of beached whales.[159] Plastic debris started appearing in the stomach of the sperm whale since the 1970s, and has been noted to be the cause of death of several whales.[181][182] In June 2018, more than 80 plastic bags were found inside a dying pilot whale that washed up on the shores of Thailand.[183] In March 2019, a dead Cuvier's beaked whale washed up in the Philippines with 88 lbs of plastic in its stomach.[184] In April 2019, following the discovery of a dead sperm whale off of Sardinia with 48 pounds of plastic in its stomach, the World Wildlife Foundation warned that plastic pollution is one of the most dangerous threats to sea life, noting that five whales have been killed by plastic over a two-year period.[185]

Some of the tiniest bits of plastic are being consumed by small fish, in a part of the pelagic zone in the ocean called the Mesopelagic zone, which is 200 to 1000 metres below the ocean surface, and completely dark. Not much is known about these fish, other than that there are many of them. They hide in the darkness of the ocean, avoiding predators and then swimming to the ocean's surface at night to feed.[186] Plastics found in the stomachs of these fish were collected during Malaspina's circumnavigation, a research project that studies the impact of global change on the oceans.[187]

A study conducted by Scripps Institution of Oceanography showed that the average plastic content in the stomachs of 141 mesopelagic fish over 27 different species was 9.2%. Their estimate for the ingestion rate of plastic debris by these fish in the North Pacific was between 12,000 and 24,000 tonnes per year.[188] The most popular mesopelagic fish is the lantern fish. It resides in the central ocean gyres, a large system of rotating ocean currents. Since lantern fish serve as a primary food source for the fish that consumers purchase, including tuna and swordfish, the plastics they ingest become part of the food chain. The lantern fish is one of the main bait fish in the ocean, and it eats large amounts of plastic fragments, which in turn will not make them nutritious enough for other fish to consume.[189]

Another study found bits of plastic outnumber baby fish by seven to one in nursery waters off Hawaii. After dissecting hundreds of larval fish, the researchers discovered that many fish species ingested plastic particles. Plastics were also found in flying fish, which are eaten by top predators such as tunas and most Hawaiian seabirds.[190]

Deep sea animals have been found with plastics in their stomachs.[191] In 2020, deep sea species Eurythenes plasticus was discovered, with one of the samples already having plastics in its gut; it was named to highlight the impacts of plastic pollution.[192]

It was found in 2016–2017 that more than 35% of south Pacific Lanternfish had consumed plastic particles. When ingested by the fish, the chemical compounds found in these plastics cannot be digested. This can affect humans, as the Lanternfish is a food source for both salmon and tuna.[193] Fish and whales may also mistake the plastic as a food source.[194][195][196][197][198]

Birds
[edit]
Northern gannet on Helgoland, Germany, trapped in their nests that are built only of old nets and other plastic waste

Plastic pollution does not only affect animals that live solely in oceans. Seabirds are also greatly affected. In 2004, it was estimated that gulls in the North Sea had an average of thirty pieces of plastic in their stomachs.[199] Seabirds often mistake trash floating on the ocean's surface as prey. Their food sources often has already ingested plastic debris, thus transferring the plastic from prey to predator. Ingested trash can obstruct and physically damage a bird's digestive system, reducing its digestive ability and can lead to malnutrition, starvation, and death. Toxic chemicals called polychlorinated biphenyls (PCBs) also become concentrated on the surface of plastics at sea and are released after seabirds eat them. These chemicals can accumulate in body tissues and have serious lethal effects on a bird's reproductive ability, immune system, and hormone balance. Floating plastic debris can produce ulcers, infections and lead to death. Marine plastic pollution can even reach birds that have never been at the sea. Parents may accidentally feed their nestlings plastic, mistaking it for food.[200] Seabird chicks are the most vulnerable to plastic ingestion since they cannot vomit up their food like the adult seabirds.[201]

Plasticosis is a type of fibrotic disease initially found in one species of bird in 2023.[202][203]

A great blue heron capturing a fish already caught in a plastic bag – birds and other wildlife regularly consume plastic when it gets entangled with or confused with food.

After the initial observation that many of the beaches in New Zealand had high concentrations of plastic pellets, further studies found that different species of prion ingest the plastic debris. Hungry prions mistook these pellets for food, and these particles were found intact within the birds' gizzards and proventriculi. Pecking marks similar to those made by northern fulmars in cuttlebones have been found in plastic debris, such as styrofoam, on the beaches on the Dutch coast, showing that this species of bird also mistake plastic debris for food.[159]

Of the 1.5 million Laysan albatrosses that inhabit Midway Atoll, nearly all are likely to have plastic in their gastrointestinal tract.[204] Approximately one-third of their chicks die, and many of those deaths are from plastic unwittingly fed to them by their parents.[205][206] Twenty tons of plastic debris washes up on Midway every year with five tons ending up in the bellies of albatross chicks.[207] These seabirds choose red, pink, brown, and blue plastic pieces because of similarities to their natural food sources. As a result of plastic ingestion, the digestive tract can be blocked resulting in starvation. The windpipe can also be blocked, which results in suffocation.[157] The debris can also accumulate in the animal's gut, and give them a false sense of fullness which would also result in starvation. On the shore, thousands of birds corpses can be seen with plastic remaining where the stomach once was. The durability of the plastics is visible among the remains. In some instances, the plastic piles are still present while the bird's corpse has decayed.[157]

Similar to humans, animals exposed to plasticizers can experience developmental defects. Specifically, sheep have been found to have lower birth weights when prenatally exposed to bisphenol A. Exposure to BPA can shorten the distance between the eyes of a tadpole. It can also stall development in frogs and can result in a decrease in body length. In different species of fish, exposure can stall egg hatching and result in a decrease in body weight, tail length, and body length.[208]

The unaltered stomach contents of a dead albatross chick include a variety of plastic marine debris.

A study found that in 1960 less than 5% of seabirds were found to have consumed waste material, while as of August 2015 that figure climbed to about 90%. It is predicted that by 2050, 99% of seabirds will have consumed such materials.[209] Scientists studying the stomach contents of Laysan albatross chicks report a 40% mortality rate before fledging. When the stomach contents were analyzed following necropsies, they were found to contain plastic waste. Not only do plastic pellets used in manufacturing worldwide absorb toxic chemicals such as DDT and PCBs from the water, but they can even leach chemicals such as biphenyl.[210] It is estimated that up to 267 marine species are affected by plastic pollution.[124]

Coral

Lost fish nets or ghost nets make up around 46% of what is known as the Great Pacific Garbage Patch and have had a negative impact on many different species of coral as they often accidentally trap themselves in these nets. These fishing nets have caused tissue loss, algae growth, and fragmentation of coral. In addition, as coral gets trapped in different types of fishing gear, this causes coral to develop stress as they are not in a favorable condition, which causes coral to break and die off. According to multiple research studies, Tubastraea micranthus is a type of coral species that appears to be the most impacted by fishing gear in the ocean because of its branches and its ability to grow on top of fishing gear such as nets, ropes, and lines.[153]

Phytoplankton

In 2019 and 2020 there were week-long studies done in Australia along the Georges River to measure the number of microplastics. The purpose of these studies was to determine if phytoplankton living in the river were being affected by the microplastics in the water. The studies included the completion of microcosm experiments where water samples were collected in bottles from the river and then filtered. In addition, microplastic solutions were made along with the collection of phytoplankton from the same river. After the studies were complete, scientists found out that there were very high concentrations of microplastics in the river which have negatively impacted phytoplankton such as cyanobacteria.[211]

As many different species of phytoplankton are being exposed to microplastics in the Georges River, not only does this impact the lives of the phytoplankton themselves, but also affects other animals in their food chain. Phytoplankton are primary producers; therefore, when microplastics are ingested, other living organisms in the environment that feed on phytoplankton also ingest microplastics.[211]

Fin Whales

In the Mediterranean Sea, studies have been performed to determine how the number of microplastics on the surface level of the ocean has affected fin whale populations. In the study, researchers collected samples of microplastics during the day when there was little to no wave action. The plastic pieces collected from the samples were then observed under a microscope to determine their size and whether they were microplastics or mesoplastics. The fin whale population's habitat was then observed where the zooplankton population was measured along with sea surface chlorophyll levels within their habitat. The Tyrreno-ROMS model was used to measure the ocean current or gyres along with the sea surface temperatures in the fin whales' habitat within the Mediterranean Sea.[212]

The results of the studies indicated that there were high levels of microplastics within the surface level of the Mediterranean Sea which is the fin whales' habitat and serves as the location of their food source mainly during the summer months. The results indicate that when fin whales search for food to eat on the surface level of the ocean, they often accidentally consume microplastics. These microplastics have many toxins and chemicals that could harm the fin whale if they consume them as these toxins are then stored in the tissues of the fin whale for long periods of time.[212]

Other

[edit]

A study from 2019 indicates that the large amounts of plastic in the Great Pacific Garbage Patch could affect the behavior and distribution of some marine animals, as they can act as fish aggregating devices (FAD). FADs can attract feeding cetaceans, thus increasing the risk of being entangled or ingesting additional plastic.[18]

Effects on humans

[edit]

Nanoplastics can penetrate the intestine tissue in aquatic creatures[213] and can end up in the human food chain by inhalation (breathing) or ingestion (eating), particularly through shellfish and crustaceans.[214] Ingestion of plastics has been associated with a variety of reproductive, carcinogenic, and mutagenic effects.[215] The most well-known organic synthetic compound used in many plastics is bisphenol A (BPA).[216] It has been linked with autoimmune disease and endocrine disrupting agents, leading to reduced male fertility and breast cancer. Phthalate esters are also linked to causing reproductive effects due to being found in packing products for food. The toxins from phthalate esters affect the developing male reproductive system.[217] Diethylhexyl phthalate is also suspected to disrupt the functions of the thyroid; however, studies are currently inconclusive.[218]

Plastics in the human body can stop or slow down detoxification mechanisms, causing acute toxicity and lethality.[17] They have the potential to affect the central nervous system and reproductive system, although this would be unlikely unless exposure levels were very high and absorption levels were increased. In vitro studies from human cells showed evidence that polystyrene nanoparticles are taken up and can induce oxidative stress and pro-inflammatory responses.[213]

Reduction efforts

[edit]

Solutions to marine plastic pollution, along with plastic pollution within the whole environment will be intertwined with changes in manufacturing and packaging practices, and a reduction in the usage, in particular, of single or short-lived plastic products. Many ideas exist for cleaning up plastic in the oceans including trapping plastic particles at river mouths before entering the ocean, and cleaning up the ocean gyres.[2]

Collection in the ocean

[edit]
NOAA's marine debris removal in 2014

Plastics pollution in the oceans might be irreversible.[113][219] Once microplastics enter the marine environment, they are extremely difficult and expensive to remove.[9]

The organization "The Ocean Cleanup" is trying to collect plastic waste from the oceans by nets. There are concerns from harm to some forms of sea organisms, especially neuston.[220]

At TEDxDelft2012,[221][222] Boyan Slat unveiled a concept for removing large amounts of marine debris from oceanic gyres. Calling his project The Ocean Cleanup, he proposed to use surface currents to let debris drift to collection platforms. Operating costs would be relatively modest and the operation would be so efficient that it might even be profitable. The concept makes use of floating booms that divert rather than catch the debris. This avoids bycatch, while collecting even the smallest particles. According to Slat's calculations, a gyre could be cleaned up in five years' time, amounting to at least 7.25 million tons of plastic across all gyres.[223] He also advocated "radical plastic pollution prevention methods" to prevent gyres from reforming.[223][224] In 2015, The Ocean Cleanup project was a category winner in the Design Museum's 2015 Designs of the Year awards.[225] A fleet of 30 vessels, including a 32-metre (105-foot) mothership, took part in a month-long voyage to determine how much plastic is present using trawls and aerial surveys.[225]

The organization "everwave" uses special rubbish collection boats in rivers and estuaries to prevent rubbish from entering the world's oceans.[226]

There is also Ocean Plastic Utilisation Ships System R&D project (OPUSS). The main objective of this project is to make the ocean cleaning process commercially realistic in time, environmentally efficient and viable in general. The central idea of the OPUSS project lies in developing new circular logistic scheme of the ocean cleanup, as existing reverse logistics supply chains are not able to capture the specifics of the plastic waste collection out on the ocean. The main target of a project is cleaning the ocean with optimal results in terms of logistics and construction costs, as well as with minimal operating costs.[227]

Plastic-to-fuel conversion strategy

[edit]

The Clean Oceans Project (TCOP) promotes conversion of the plastic waste into valuable liquid fuels, including gasoline, diesel and kerosene, using plastic-to-fuel conversion technology developed by Blest Co. Ltd., a Japanese environmental engineering company.[228][229][230][231] TCOP plans to educate local communities and create a financial incentive for them to recycle plastic, keep their shorelines clean, and minimize plastic waste.[229][232]

In 2019, a research group led scientists of Washington State University found a way to turn plastic waste products into jet fuel.[233]

Also, the company "Recycling Technologies", has come up with a simple process that can convert plastic waste to an oil called Plaxx. The company is led by a team of engineers from the university of Warwick.[234][235]

Other companies working on a system for converting plastic waste to fuel include GRT Group and OMV.[236][237][238]

Policies and legislation

[edit]

Shortcomings in the existing international policy framework include: "the focus on sea-based sources of marine plastic pollution; the prevalence of soft law instruments; and the fragmentation of the existing international regulatory framework".[239] Four aspects are important for an integrated approach to solve the problem of marine plastic pollution: harmonization of international laws (action example: develop a new global plastics treaty); coherence across national policies; coordination of international organizations (action example: identify a leading coordinating organization (e.g., UN Environment Programme (UNEP)); and science-policy interaction.[239] These shortcomings are often listed as drivers for the advancement of a global plastics treaty. The development of such a treaty is underway as of March 2022 and is expected to conclude by the end of 2024.[240]

In the EU it is estimated that banning the intentional addition of microplastics to cosmetics, detergents, paints, polish and coatings, among others, would reduce emissions of microplastics by about 400,000 tonnes over 20 years.[9]

The trade in plastic waste from industrialized countries to developing countries has been identified as the main cause of marine litter because countries importing the waste plastics often lack the capacity to process all the material.[241] Therefore, the United Nations has imposed a ban on waste plastic trade unless it meets certain criteria. The global plastic waste trade when it comes into effect in January 2021.[241]

History

[edit]

Background

[edit]

Plastic pollution was first found in central gyres, or rotating ocean currents in which these observations from the Sargasso Sea were included in the 1972 Journal Science. In 1986, a group of undergraduate students conducted research by recording how much plastic they came across on their ship while traveling across the Atlantic Ocean. Their research led to them being able to collect useful and long term data about plastic in the Atlantic Ocean along with Charles Moore being able to discover the Great Pacific Garbage Patch. In addition, the undergraduate students' research helped lead to the invention of the term "microplastics".[242]

Terminology

[edit]

Microplastics

The term "microplastics" was first used by Richard Thompson in 2004 as he described microplastics to be small pieces of plastic, specifically less than 5 mm, that are found in the ocean and other bodies of water. After Thompson's invention of the term "microplastics", many scientists have conducted research to try to determine the effects that microplastics have in the ocean.[242]

Plastic soup

[edit]

The term "plastic soup" was coined by Charles J. Moore in 1997, after he found patches of plastic pollution in the North Pacific Gyre between Hawaii and California.[243] This Great Pacific Garbage Patch had previously been described in 1988 by scientists who used the term neuston plastic to describe "The size fraction of plastic debris caught in nets designed to catch surface plankton (hereafter referred to as neuston plastic)", and acknowledged that earlier studies in the 1970s had shown that "neuston plastic is widespread, is most abundant in the central and western North Pacific, and is distributed by currents and winds".[244]

In 2006, Ken Weiss published an article in the Los Angeles Times which was the first to make the public aware about the effects of the Garbage Patch in the Pacific Ocean. In 2009, a group of researchers decided to go out into the Pacific Ocean to prove if the Great Pacific Garbage Patch was real or a myth. After days out on the sea, the research group came across hundreds of plastic pieces in the ocean that were seen as a soup of microplastics rather than large pieces of plastics as expected.[242]

The term is sometimes used to refer only to pollution by microplastics, pieces of plastic less than 5mm in size such as fibres shed from synthetic textiles in laundry: the British National Federation of Women's Institutes passed a resolution in 2017 headlined "End Plastic Soup" but concentrating on this aspect of pollution.[245]

The Amsterdam-based Plastic Soup Foundation is an advocacy group which aims to raise awareness of the problem, educate people, and support the development of solutions.[246]

As of January 2019, the Oxford English Dictionary did not include the terms plastic soup, neuston plastic or neustonic plastic, but it defined the term microplastic (or micro-plastic) as "Extremely small pieces of plastic, manufactured as such (in the form of nurdles or microbeads) or resulting from the disposal and breakdown of plastic products and waste" and its illustrative quotations all relate to marine pollution, the earliest being a 1990 reference in the South African Journal of Science: "The mean frequency of micro-plastic particles increased from 491 m1 of beach in 1984 to 678 m1 in 1989".[247]

See also

[edit]

Sources

[edit]

 This article incorporates text from a free content work. Licensed under Cc BY-SA 3.0 IGO (license statement/permission). Text taken from Drowning in Plastics – Marine Litter and Plastic Waste Vital Graphics​, United Nations Environment Programme.

References

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Further reading

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from Grokipedia
Marine pollution refers to the entry and persistence of debris in and coastal environments, where it fragments into and accumulates in gyres, primarily derived from land-based mismanaged transported via rivers. Estimates indicate that between 1.15 and 2.41 million metric tons of enter the oceans annually through rivers, representing roughly 0.5% of global production, with the top 1,000 rivers—mostly in —accounting for about 80% of this flux. Approximately 70% to 80% of plastics originate from land sources, while 20% stem from marine activities such as discarded gear. The most prominent accumulation is the Great Pacific Garbage Patch, a vast area of dispersed in the containing an estimated 1.8 trillion pieces, where comprise 94% of the particle count but only 8% of the mass, with fishing-related items forming a significant portion of larger . affects marine through physical mechanisms like entanglement in nets and lines, which can cause injury, restricted movement, and drowning, and ingestion of mistaken for food, leading to internal blockages, starvation, and reduced reproductive success in species including seabirds, , and mammals—documented across hundreds of taxa. While acute harms are evident in individual cases, population-level ecological consequences remain subject to ongoing research, with confounding factors like chemical leaching and requiring further empirical validation beyond correlative studies. Efforts to address marine plastic pollution emphasize prevention at sources through improved in high-emission regions, rather than , which captures only a fraction of dispersed ; initiatives include river interception technologies and international agreements targeting single-use plastics, though effectiveness is limited by enforcement challenges in developing economies. Controversies arise from discrepancies between visible macro-debris impacts and the diffuse nature of microplastic threats, with some analyses questioning the prioritization of plastics over other marine stressors like or habitat loss, and critiques of alarmist narratives that may inflate perceived risks relative to verifiable data.

Definition and Scope


Recent modeling studies informed by improved data and river transport simulations estimate that 1 to 2 million metric tons of enter the annually, with over 1,000 rivers accounting for 80% of riverine emissions, primarily from densely populated coastal regions with inadequate . This figure represents a downward revision from earlier assessments, such as the Jambeck et al. estimate of 4.8 to 12.7 million tons based on global mismanaged waste proxies, which did not fully account for barriers to ocean entry like retention in rivers or beaches. Higher estimates, such as 19 to 23 million tons reported by the for broader aquatic ecosystems including inland waters, reflect inclusion of non-marine leakage and advocacy-oriented projections rather than ocean-specific fluxes.
The standing stock of plastic in the marine environment is difficult to quantify precisely due to fragmentation into , sinking to the seafloor, stranding on shores, and degradation, but surface waters alone held an estimated 170 trillion particles totaling 2.3 million metric tons as of 2019, predominantly smaller than 1 mm. On the ocean floor, 3 to 11 million metric tons accumulated by 2020, based on extrapolations from deep-sea surveys accounting for historical inputs and settling rates. Overall historical accumulation is approximated at 75 to 199 million tons across all marine compartments, with estimates around 150 million metric tons corresponding to roughly 150 million cubic meters in volume assuming an average density of about 1 g/cm³, though these ranges underscore methodological uncertainties from sparse global sampling and variable effects. Trends indicate stagnation or fluctuation in plastic concentrations until the early , followed by rapid escalation paralleling global plastic production growth from 2 million tons in to 460 million tons in 2019, driven by rising consumption in low-management regions. A 60-year of marine entanglements documents a marked rise since the , confirming increasing prevalence of floating . These patterns persist despite some national reductions in mismanaged waste, as persistent legacy pollution and ongoing inputs outweigh removal efforts, with gyre-concentrated surveys revealing biases toward high-density zones that may inflate perceived uniformity.

Measurement and Quantification Challenges

Quantifying marine plastic pollution presents significant methodological hurdles due to the ocean's immense volume, the heterogeneous distribution of debris, and the dynamic processes of fragmentation, sinking, and that alter plastic detectability. Traditional in-situ sampling techniques, such as tows, predominantly capture macroplastics (>5 mm) and larger but systematically underestimate smaller (<1 mm) and nanoplastics, as these pass through meshes or evade collection in low-density surface waters. For instance, studies indicate that net-based methods may overlook up to 99% of microplastic particles in certain size fractions, leading to concentrations reported as low as 0.01–1 particle per cubic meter, while laboratory filtration of unfiltered seawater reveals orders of magnitude higher abundances. The absence of globally standardized protocols exacerbates comparability issues, with variations in sampling depth, mesh size, extraction techniques, and particle identification (e.g., visual vs. spectroscopic) yielding inconsistent results across studies. Observer bias further complicates beach and surface surveys, particularly in citizen-science programs, where detection rates for low-contrast or weathered debris differ by up to 50% among participants due to experience levels and environmental conditions. Remote sensing approaches, including satellite imagery and drones, offer broad-scale monitoring but struggle with spectral confusion—plastics often mimic sea foam, algae, or wood in optical signatures—and fail to detect submerged or small particles, potentially underestimating total loads by factors of 10–100 in convergence zones. Subsurface and deep-sea quantification remains particularly elusive, as most data derive from sparse trawls or sediment cores that capture only localized snapshots, ignoring vertical transport via currents or density changes from biofouling. Recent analyses suggest subsurface microplastic concentrations may exceed surface levels by 10–20 times in some regions, yet observational data remain limited by deployment costs and technological constraints, such as sensor durability in high-pressure environments. Modeling efforts to extrapolate from these samples face uncertainties in degradation rates, advection, and removal processes, often resulting in global estimates ranging widely from 0.1 to 2.5 million metric tons annually entering oceans, with error margins exceeding 50%. These discrepancies underscore the need for integrated, multi-method validation to refine inventories beyond current approximations.

Sources and Entry Pathways

Land-Based Contributions

Land-based sources dominate estimates of plastic inputs to the marine environment, primarily through mismanaged waste that enters waterways via rivers, stormwater runoff, and inadequate wastewater treatment. Mismanaged plastic waste, including littering from urban areas and overflowing landfills, constitutes a key pathway, with global plastic waste generation exceeding 350 million metric tons annually, of which approximately 0.5%—or about 1.75 million metric tons—reaches the oceans each year. This figure aligns with refined models indicating that rivers alone transport 0.8 to 2.7 million metric tons of plastic annually into coastal waters, accounting for the bulk of land-based flux. Rivers serve as primary conduits, with over 1,000 rivers—predominantly in and —responsible for nearly 80% of global riverine emissions, driven by population density, poor waste infrastructure, and high precipitation in coastal basins. For instance, the and rivers rank among the top emitters, channeling macroplastics like bottles and bags alongside microplastics from urban and agricultural runoff. Earlier projections, such as Jambeck et al. (2015), estimated land-based inputs at 4.8 to 12.7 million metric tons per year based on 2010 waste data, but subsequent studies incorporating improved modeling of retention in river systems have revised these downward, emphasizing that only a fraction of mismanaged waste (estimated at 31.9 million metric tons globally in 2010) actually escapes to sea. Additional land-based vectors include direct coastal littering, atmospheric deposition of microplastics, and diffuse sources like tire abrasion particles and synthetic textile fibers released during laundry, which enter via stormwater drains and sewage overflows. Wastewater treatment plants capture much macroplastic but release microplastics, with tire wear alone contributing an estimated 0.2 to 1 million metric tons of particulates to waterways annually worldwide. While the oft-cited 80% land-based versus 20% maritime sourcing ratio persists in many assessments, recent analyses question its universality, noting higher maritime contributions in remote regions and variability by plastic type and size; nonetheless, empirical river sampling and modeling consistently affirm land as the principal origin for plastics reaching accumulation zones. Geographic disparities underscore causal factors: high-income nations generate less per capita mismanagement due to robust collection systems, whereas low- and middle-income countries in tropical regions, facing rapid urbanization and limited infrastructure, export disproportionate shares—up to 90% of riverine flux from just 10 rivers in such areas. Mitigation thus hinges on enhancing waste management at source, as evidenced by interventions reducing river outflows by up to 50% in modeled scenarios for Southeast Asian basins.

Maritime and Ocean-Based Sources

Maritime and ocean-based sources account for approximately 20% of marine plastic pollution, with the remainder primarily originating from land-based inputs. These sources include discarded fishing gear, illegal discharges from vessels, and lost cargo, which persist in the marine environment due to the durable nature of plastics used in maritime operations. Abandoned, lost, or otherwise discarded fishing gear (ALDFG) represents the predominant ocean-based contributor, estimated at 640,000 tonnes entering oceans annually. This gear, including nets, lines, and traps, constitutes about 10% of total marine plastic waste globally, though proportions reach 75-86% in accumulation zones like the Great Pacific Garbage Patch. Loss occurs through snags on obstacles, weather damage, or deliberate abandonment, leading to "ghost fishing" where derelict gear continues to trap marine life indefinitely. Industrial fishing fleets from industrialized nations, particularly in the North Pacific, are primary sources of floating debris in gyres. Commercial shipping contributes through potential illegal garbage discharges, despite prohibitions under the International Convention for the Prevention of Pollution from Ships (MARPOL) Annex V, which bans all plastic disposal at sea from vessels. Compliance varies, with enforcement challenges in international waters allowing sporadic violations, though quantified contributions remain lower than fishing gear due to regulatory frameworks and port reception facilities. Cargo losses from container spills, such as during storms, add episodic inputs of plastic items like packaging and consumer goods. Other minor maritime sources include offshore oil and gas platforms, aquaculture operations, and naval activities, which generate plastics through equipment wear and waste mismanagement but lack comprehensive global estimates. The durability of maritime plastics, engineered for harsh conditions, exacerbates accumulation, with gillnets and trawl nets comprising vast lost areas—equivalent to thousands of square kilometers annually.

Transport Mechanisms and Buoyancy Effects

Marine plastics are primarily transported from coastal and riverine entry points by ocean surface currents, which converge in subtropical gyres to form accumulation zones such as the North Pacific Subtropical Gyre. Wind-driven drift and wave action further influence horizontal movement, with particles following Stokes drift patterns that can carry debris thousands of kilometers over months to years. Vertical transport occurs through turbulence and mixing in the upper ocean layers, enabling subduction of lighter particles into the mixed layer or deeper waters, particularly in regions of downwelling. Buoyancy of marine plastics is determined by material density relative to seawater (approximately 1.025 g/cm³), with low-density polymers like polyethylene (0.91–0.96 g/cm³) and polypropylene (0.85–0.92 g/cm³) initially floating, while denser types such as polyvinyl chloride (1.3–1.45 g/cm³) sink rapidly. Approximately 90% of observed floating marine debris consists of plastics, but nearly half of all entered plastic sinks directly due to inherent low buoyancy or fragmentation, with the remainder subject to dynamic changes. Biofouling by microbial biofilms and algae significantly alters buoyancy by increasing particle density through biomass accumulation, causing up to 50% of initially buoyant plastics to sink within weeks to months, with sinking probability reaching 50% in 17–66 days depending on particle volume, temperature, and nutrient levels. Larger, thicker-walled low-density plastics resist sinking longer and are preferentially transported long distances by currents, whereas smaller or denser fragments subside faster, contributing to subsurface distributions. Degradation-induced fragmentation and air entrapment loss further promote vertical flux, with models indicating that barotropic tidal currents have minimal global impact on floating microplastic transport but enhance local mixing. In polar regions, sea ice facilitates both accumulation and seasonal transport of buoyant microplastics, releasing them upon melt.

Types and Characteristics of Debris

Macroplastics

Macroplastics refer to plastic debris items larger than 5 millimeters in size, distinguishing them from smaller microplastics. This category encompasses a wide range of consumer and industrial products that enter marine environments primarily through land-based runoff, river transport, and maritime activities. Macroplastics are prevalent across surface waters, beaches, and even deep-sea habitats, with documented occurrences in every marine ecosystem examined. Common types of macroplastics include beverage bottles, plastic bags, fishing nets and lines, styrofoam fragments, bottle caps, and food wrappers. Polymers such as polyethylene (PE) and polypropylene (PP) dominate, comprising up to 55% of coastal plastic waste due to their widespread use in packaging and durable goods. These items often originate as intact objects that fragment over time, contributing to secondary debris formation. Macroplastics exhibit high buoyancy, particularly low-density variants like and , allowing them to accumulate in ocean surface convergence zones before vertical mixing or sinking occurs. Their persistence stems from resistance to biodegradation, with degradation primarily driven by photodegradation from ultraviolet radiation and mechanical abrasion from waves, leading to fragmentation rather than complete breakdown. This slow degradation process positions macroplastics as a primary source of secondary in the marine environment.

Microplastics and Nanoplastics

Microplastics are defined as synthetic plastic particles ranging in size from 1 micrometer (μm) to 5 millimeters (mm) in diameter. This size classification distinguishes them from larger macroplastics and smaller nanoplastics, with the upper limit of 5 mm adopted by organizations such as NOAA and GESAMP to facilitate consistent environmental monitoring. Nanoplastics, a subset of microplastics, consist of particles smaller than 1 μm, typically ranging from 1 nanometer (nm) to 1 μm, though definitions vary slightly with some extending to 1000 nm. Their nanoscale dimensions render them invisible to the naked eye and challenging to detect using standard filtration methods, complicating quantification in marine samples. Microplastics originate from two primary pathways: primary microplastics, which are intentionally manufactured at small sizes for uses such as microbeads in personal care products or industrial abrasives, and secondary microplastics, formed through the mechanical, photolytic, and biological degradation of larger plastic debris by ocean waves, UV radiation, and microbial action. In marine environments, secondary microplastics predominate, comprising the majority of particles observed in surface waters and sediments due to the ubiquity of macroplastic breakdown. Common shapes of marine microplastics include fibers (often from synthetic textiles), fragments (irregular shards from degraded items), films (thin sheets from packaging), and pellets (pre-production nurdles). Fibers constitute a significant proportion, reported at up to 44% in some global surveys, while fragments follow at around 29%. Polymer composition varies but is dominated by polyethylene (PE), polypropylene (PP), and polystyrene (PS), with densities influencing vertical distribution: low-density polymers like PE (0.91–0.96 g/cm³) and PP (0.85–0.92 g/cm³) tend to remain buoyant or suspend in surface layers, whereas higher-density types such as polyvinyl chloride (PVC, 1.3–1.45 g/cm³) sink to deeper waters or sediments. Estimates of microplastic abundance in ocean surface waters indicate approximately 35,540 metric tonnes floating globally, though particle counts exceed 170 trillion due to the prevalence of sub-millimeter sizes. Nanoplastics remain under-quantified but are projected to constitute substantial masses, with one 2025 study estimating 27 million metric tons in the North Atlantic alone, highlighting their potential dominance in total plastic burden despite detection challenges. Surface concentrations vary regionally, often reported in particles per cubic meter, with higher values near coastal inputs and convergence zones.

Accumulation and Distribution

Surface Convergence Zones

Surface convergence zones arise in the ocean where wind-driven Ekman transport and geostrophic currents direct floating materials toward central gyre regions, creating areas of enhanced retention for buoyant debris like plastics. These dynamics result in downwelling-resistant accumulation, as surface waters converge without significant vertical mixing, trapping particles that follow current pathways from distant sources. The five subtropical gyres—North Pacific, South Pacific, North Atlantic, South Atlantic, and Indian Ocean—host the principal convergence zones globally, where plastic debris concentrations exceed those in surrounding open waters by orders of magnitude. A 2014 survey across 1.3 million square kilometers using neuston nets documented plastic in 88% of 3,070 samples, with the highest densities confined to these gyre interiors, estimating a total surface plastic load of 7,000–35,000 metric tons. The North Pacific gyre alone contributes 33–35% of this global inventory, highlighting its disproportionate role. In the North Pacific Subtropical Convergence Zone, observations from aerial surveys in 2005 identified over 1,800 debris items, including 122 derelict fishing nets and numerous plastic floats, with peak accumulations north of the Transition Zone Chlorophyll Front between 23°N and 37°N. Microplastics, often exceeding 92% of floating debris mass in gyres, show abundances up to 334 particles per cubic meter throughout the water column in this region, predominantly smaller than 100 micrometers. These zones trap debris from land-based runoff, maritime activities, and atmospheric deposition, but their diffuse nature—characterized by scattered micro- and macroplastics rather than cohesive rafts—complicates quantification and remediation. Recent global estimates indicate surface plastic particles now number 82–358 trillion, weighing 1.1–4.9 million tonnes, with gyre convergence zones sustaining elevated hotspots amid ongoing inputs.

Deep-Sea and Seabed Deposits

Plastics initially entering the marine environment as buoyant macrodebris often transition to the deep sea through biofouling, where microbial and faunal colonization increases density, leading to vertical sinking over time scales of months to years. Microplastics, denser than seawater or fragmented from larger items, contribute directly via gravitational settling or ingestion-mediated transport by vertically migrating organisms such as amphipods. This process results in the ocean floor acting as a persistent sink, with limited degradation due to low temperatures, high pressure, and darkness inhibiting microbial breakdown. Global estimates indicate 3 to 11 million metric tonnes of plastic reside on the seabed as of 2020, derived from remotely operated vehicle (ROV) surveys and modeling of sinking fluxes, representing a substantial fraction of total marine plastic inventory—potentially up to 100 times more than surface accumulations. For microplastics specifically, approximately 3.05 million tonnes are projected in deep ocean sediments, based on mass balance assessments incorporating fragmentation rates and burial efficiencies. These figures underscore under-sampling biases in shallower waters, as deep-sea coverage remains sparse despite expeditions revealing hotspots. Hadal zones, such as ocean trenches, exhibit elevated concentrations: in the , microplastic abundances in sediments reach 200 to 2,200 particles per liter, exceeding surface ocean levels by orders of magnitude and correlating with proximity to land-based pollution sources via currents. Macrodebris, including bags and fishing gear, has been documented at depths exceeding 10,000 meters, with a plastic bag observed at the in 2019, highlighting incomplete fragmentation before burial. Distribution patterns favor abyssal plains and submarine canyons as depositional environments, where downslope currents concentrate debris, though quantification challenges persist due to patchy sampling and methodological variances in extraction from sediments. Ongoing research emphasizes the need for standardized protocols to refine these estimates amid rising plastic inputs.

Chemical and Physical Processes

Degradation Pathways

Marine plastics primarily degrade through abiotic processes rather than biodegradation, fragmenting into smaller particles over extended periods without full mineralization. Photodegradation, driven by ultraviolet (UV) radiation, initiates chain scission and oxidation in surface-exposed polymers, embrittling materials like polyethylene (PE) and polypropylene (PP) to facilitate further breakdown. Mechanical forces from wave action and abrasion then physically fragment these weakened plastics, accelerating the production of microplastics. Thermo-oxidative degradation occurs at lower rates in the cooler ocean environment, while hydrolysis affects hydrolyzable polymers such as polyethylene terephthalate (PET) but proceeds slowly due to limited water reactivity with most carbon-backbone plastics. Biodegradation by marine microorganisms remains negligible for dominant plastics like PE, PP, PET, and polyvinyl chloride (PVC), with microbial attachment forming biofilms but rarely achieving significant mass loss or depolymerization. Studies indicate weight loss rates below 1% over months to years for these polymers under marine conditions, contrasting with faster degradation of biodegradable alternatives not widely used in marine debris. Enzymes such as cutinases and laccases from marine bacteria and fungi can initiate surface erosion, yet environmental factors like low temperatures and nutrient scarcity limit efficacy, resulting in fragmentation persisting as micro- and nanoplastics rather than biological assimilation. Degradation timelines vary by polymer and additives; for instance, PE exhibits surface erosion at approximately 0.45% weight loss per month in controlled exposures, slowed by stabilizers, while PP degrades at 0.39% per month, often taking centuries for macroplastics to reduce to microplastic sizes in natural settings. resists photodegradation due to chlorine content but undergoes dehydrochlorination under UV, releasing hydrochloric acid and forming brittle residues. Overall, these pathways transform intact debris into pervasive microplastics, amplifying environmental distribution without resolving pollution through complete breakdown.

Additive Leaching and Toxicity

Plastics incorporate various additives, including phthalates for flexibility, brominated flame retardants for fire resistance, bisphenol A for polymerization, and UV stabilizers, to achieve desired material properties; these substances, comprising up to 60% by weight in some formulations, are typically not covalently bonded to the polymer matrix, enabling their gradual migration and release. In marine settings, leaching accelerates through diffusion driven by concentration gradients between the plastic and surrounding seawater, exacerbated by factors such as UV-induced polymer degradation, wave abrasion, biofilm formation, and temperature fluctuations, resulting in additive concentrations in ocean waters ranging from nanograms to micrograms per liter depending on plastic type and exposure duration. Empirical studies confirm significant leaching from weathered microplastics and macrodebris; for instance, polyvinyl chloride (PVC) microplastics release di(2-ethylhexyl) phthalate (DEHP) at rates yielding environmentally relevant levels over months of immersion, with modeling indicating sustained emission as a long-term source in aquatic systems. Similarly, polyethylene and polypropylene debris leach antioxidants like Irganox 1010, while polystyrene releases styrene oligomers, with release rates reduced by up to twofold in deep-sea conditions due to lower temperatures and pressures compared to surface waters. Biofilm coatings on plastics can modulate leaching by altering surface hydrophobicity and providing microbial enzymes that degrade polymer-additive interfaces, potentially increasing additive bioavailability in coastal zones. These leached additives exhibit toxicity to marine biota at concentrations observed in polluted areas, primarily through bioaccumulation and biomagnification across trophic levels; phthalates like DEHP disrupt endocrine function in fish, causing reproductive impairment and altered sex ratios at exposure levels of 0.1–10 μg/L, as demonstrated in laboratory assays with species such as Japanese medaka (Oryzias latipes). Brominated flame retardants, including polybrominated diphenyl ethers (PBDEs), induce neurodevelopmental defects and thyroid hormone interference in invertebrates and crustaceans, with lethal concentrations (LC50) for copepods around 1–50 μg/L and sublethal effects like reduced reproduction persisting at lower doses. Antioxidants and UV stabilizers, such as benzotriazoles, exhibit oxidative stress and genotoxicity in algae and bivalves, inhibiting photosynthesis and causing DNA damage at environmentally realistic levels below 1 μg/L.
Common AdditivePlastic TypeKey Toxicity MechanismExample Marine Organism EffectThreshold Concentration
DEHP (phthalate)PVCEndocrine disruptionReproductive failure in fish0.1–10 μg/L
PBDEs (flame retardant)VariousNeurotoxicity, thyroid interferenceDevelopmental delay in crustaceansLC50 1–50 μg/L
Irganox 1010 (antioxidant)PE, PPOxidative stressGrowth inhibition in algae<1 μg/L
While acute toxicity is evident in controlled exposures, field-based risks remain uncertain due to additive interactions with sorbed pollutants like PCBs, which may synergize effects, and dilution in open oceans; however, hotspots near urban outflows show elevated bioaccumulation in sentinel species like mussels, underscoring additive leachates as a persistent chemical hazard beyond physical plastic ingestion. Peer-reviewed assessments emphasize that, unlike inert polymers, these leachates function as classical toxicants, with ecotoxicological models predicting population-level declines in sensitive taxa under chronic exposure scenarios.

Ecological Impacts

Interactions with Marine Ecosystems

Marine plastics interact with ecosystems primarily through physical entanglement, ingestion across trophic levels, and the formation of novel habitats via biofouling. Floating debris serves as substrates for microbial colonization, creating the "plastisphere," a biofilm community dominated by bacteria such as Proteobacteria and Bacteroidetes, which differs from surrounding seawater assemblages. This colonization can facilitate the dispersal of invasive or pathogenic species, potentially altering local biodiversity by providing artificial rafts for attachment and transport. Microplastics, in particular, enter food webs at basal levels through ingestion by phytoplankton and zooplankton, leading to trophic transfer to higher predators. For instance, studies detect microplastic particles in primary consumers like mussels (Mytilus edulis) at concentrations of 0.36 ± 0.07 particles per gram wet weight and oysters (Crassostrea gigas) at 0.47 ± 0.16 particles per gram. This transfer biomagnifies associated pollutants, such as PCBs and PAHs adsorbed onto particles, exacerbating toxicity through mechanisms like oxidative stress and reduced reproductive output in affected organisms. Physical effects include gut blockages and energy diversion in invertebrates, disrupting feeding efficiency and growth. At the ecosystem scale, these interactions impair biodiversity and service provision, including primary productivity and nutrient cycling. Microplastics induce morphological changes in phytoplankton, such as deformed thylakoids, and developmental delays in zooplankton, potentially cascading to reduced marine productivity. Biofouling on plastics increases density, promoting vertical transport to sediments and altering benthic communities, though the full extent of long-term biodiversity shifts remains uncertain due to variability in exposure and particle types. Overall, plastics contribute to diffuse stress on marine systems, with evidence of inflammation and energy reserve depletion in key species like lugworms (Arenicola marina).

Contributions to Broader Environmental Stressors

Marine plastic pollution interacts with by contributing to greenhouse gas emissions across its lifecycle, including production from fossil fuels, transport, and environmental degradation. The breakdown of plastics in marine environments releases methane and carbon dioxide, with studies estimating that degrading plastics could emit up to 2.5 billion tonnes of CO2-equivalent by 2060 under business-as-usual scenarios. Plastic manufacturing alone consumes 3.4-4.2% of global oil production, amplifying fossil fuel dependency and associated emissions. These emissions create feedback loops, as warmer oceans accelerate plastic fragmentation and further GHG release, intensifying climate-driven stressors like sea level rise and ecosystem disruption. Plastics also exacerbate ocean acidification through abiotic leaching of polymer additives and degradation byproducts, which release acidic compounds into seawater. Laboratory experiments have demonstrated that exposure to microplastics increases local pH decreases, with polyethylene and polypropylene leachates contributing protons that compound CO2-driven acidification. This interaction disrupts carbonate chemistry, hindering calcification in organisms like corals and shellfish, and amplifying the vulnerability of marine habitats already stressed by rising atmospheric CO2 levels, which have lowered surface ocean pH by 0.1 units since pre-industrial times. Furthermore, microplastics serve as vectors for other pollutants, adsorbing persistent organic pollutants (POPs) like PCBs and heavy metals, thereby enhancing their transport, bioavailability, and synergistic toxicity in marine systems. This adsorption, driven by hydrophobic surfaces and high surface area, can increase bioaccumulation factors by orders of magnitude, intensifying oxidative stress and endocrine disruption in organisms exposed to multiple contaminants. In combination with stressors like nutrient pollution or hypoxia, plastics alter microbial communities and carbon cycling, potentially reducing oceanic CO2 sequestration efficiency by fouling phytoplankton and sediments. Such synergies push ecosystems closer to tipping points, as evidenced by models showing amplified biodiversity loss and altered biogeochemical fluxes.

Effects on Wildlife

Physical Harm Mechanisms

Entanglement in marine plastic debris, particularly derelict fishing gear such as ghost nets and monofilament lines, represents the predominant physical harm mechanism to wildlife, leading to injuries, impaired mobility, and mortality across multiple taxa. This occurs when flexible plastics like ropes, nets, and packaging bands constrict appendages or torsos, causing lacerations, tissue necrosis, and secondary infections; in severe cases, constriction results in amputation or drowning due to inability to surface for air in marine mammals and sea turtles. NOAA reports that entanglement contributes to the annual death of hundreds of thousands of marine mammals and sea turtles globally, with fishing gear accounting for over 40% of documented cases in large whales. Seabirds and pinnipeds experience similar physical trauma, including wing fractures and reduced flight efficiency from entanglement in debris like six-pack rings and balloon strings, which can also exacerbate starvation by hindering foraging. Empirical observations indicate that 81 of 123 marine mammal species have encountered plastic entanglement, often resulting in behavioral changes such as increased energy expenditure and vulnerability to predators. Fish species suffer gill abrasion and fin damage from discarded nets, impairing respiration and locomotion, with studies documenting elevated mortality rates in affected populations. Abrasion from larger macroplastics during interactions further compounds physical harm, eroding skin and mucous membranes in species like turtles and dolphins, potentially facilitating pathogen entry. While ingestion-related blockages fall under internal effects, external physical contact with sharp-edged debris causes immediate wounds, as evidenced by necropsy data showing scarring in over 50% of entangled cetaceans examined between 2015 and 2020. These mechanisms underscore the direct causal link between persistent plastic durability and wildlife injury, independent of chemical leaching.

Ingestion and Internal Effects

Marine wildlife ingests plastics through mistaken consumption as prey, leading to internal physical and chemical effects. Seabirds, such as , frequently exhibit stomach blockages from accumulated debris, resulting in starvation despite apparent feeding activity. Autopsies of affected chicks reveal masses of plastics displacing nutritious food, causing malnutrition and reduced chick survival rates at sites like . In fish, ingestion incidence reaches 26% across 386 species, with rates doubling over the past decade at 2.4% annually, primarily from microplastics smaller than 5 mm. Internal retention leads to false satiety, suppressing appetite and causing energy deficits, while sharp fragments induce tissue abrasions and inflammation in the gastrointestinal tract. Sea turtles face similar blockages, with ingested bags mimicking jellyfish, obstructing intestines and impairing nutrient absorption, often culminating in lethargy and death. Chemical effects arise from leaching of plastic additives like phthalates and bisphenol A, alongside adsorbed pollutants such as PCBs, into tissues. These induce oxidative stress, metabolic disruptions, and immune suppression in exposed organisms, with studies on invertebrates showing declined fertility and slowed larval development. In mammals like whales, beached specimens contain tons of plastic, correlating with ulcerations and toxin bioaccumulation that exacerbate physiological strain. Deep-sea fish and crustaceans show ingestion rates of 26-29%, with plastics potentially altering enzymatic functions and increasing vulnerability to pathogens. Overall, these internal impacts manifest as reduced growth, reproductive impairment, and heightened mortality, though long-term population effects remain understudied due to challenges in isolating plastics from other stressors. Experimental evidence confirms dose-dependent toxicity, including genotoxicity and histopathology, underscoring causal links beyond mere physical obstruction.

Population-Level Consequences

Population-level consequences of marine plastic pollution on wildlife arise mainly from cumulative individual mortality via entanglement and ingestion, alongside sublethal impairments to reproduction and growth, though attributing declines solely to plastics is complicated by confounding factors like overfishing, habitat loss, and climate variability. Entanglement in derelict fishing gear accounts for significant direct mortality, with estimates indicating up to 300,000 cetacean deaths annually worldwide, exacerbating risks for small, slow-reproducing populations such as the critically endangered (Eubalaena glacialis), where gear interactions contribute substantially to ongoing declines. For pinnipeds and sea turtles, entanglement prevalence can exceed 10-20% in surveyed populations, leading to chronic injuries that reduce survival rates and reproductive output, potentially hindering recovery in species like the Hawaiian monk seal (Neomonachus schauinslandi) and loggerhead turtle (Caretta caretta). Ingestion of plastics similarly imposes population pressures through starvation and toxin bioaccumulation; in seabirds, over 90 species exhibit ingestion rates above 50% in some regions, correlating with nestling mortality and inferred declines in species like the flesh-footed shearwater (Ardenna carneipes), though isolating plastic-specific effects remains challenging. Despite these individual harms, empirical assessments reveal limited evidence for broad population declines directly caused by plastic pollution across marine megafauna. A synthesis of long-term monitoring data for whales, dolphins, seals, seabirds, and turtles found no overall correlation between plastic abundance and species population trajectories, suggesting that while plastics contribute additively to mortality, they do not drive systemic collapses amid dominant threats like bycatch. In smaller taxa such as fish and benthic invertebrates, microplastics induce sublethal effects including reduced fecundity and larval viability, as demonstrated in copepod models where exposure lowered population growth rates by altering demographic parameters. Field studies on fish populations in polluted estuaries report correlations between microplastic loads and decreased recruitment, implying potential long-term declines, but causality requires further validation beyond laboratory proxies.

Human Health Considerations

Exposure Routes

Humans are primarily exposed to microplastics originating from marine environments through dietary ingestion, with seafood consumption representing a key pathway. Microplastics have been detected in various marine species, including fish and shellfish, which bioaccumulate these particles through the food web. For instance, studies on commercial fish from regions like the South China Sea and Straits of Malacca have identified microplastic fibers in edible tissues, with concentrations varying by species and habitat. Global seafood intake, providing approximately 6.7% of human protein as of 2015, facilitates transfer of these contaminants, though exact annual ingestion estimates depend on regional consumption patterns and filtration by gastrointestinal tracts. Shellfish, such as mussels and oysters, exhibit higher retention rates due to their filter-feeding behavior, potentially exposing consumers to hundreds of particles per serving. Sea salt derived from evaporated seawater serves as another ingestion route, as marine microplastics concentrate during production. Analyses of commercial sea salts from multiple countries reveal particle counts ranging from 1 to 10 microplastics per kilogram, predominantly fragments and fibers. In Europe, annual exposure via sea salt consumption is estimated at around 14 micrograms (less than 12 particles) per person, with sea salt contributing up to a quarter of total microplastic intake from salts. Similar findings in Lebanese salts suggest up to 2,372 particles per adult annually, underscoring variability based on sourcing and processing methods. Inhalation represents a secondary route, particularly for coastal populations, via aerosolized microplastics generated by sea spray and wave action. Airborne particles, including polystyrene and polyethylene, have been sampled in remote marine atmospheres, with ocean-derived aerosols transporting them inland or globally through atmospheric circulation. These microplastics can enter the respiratory tract, though quantitative human exposure data remain limited compared to ingestion pathways. Dermal contact during activities like swimming in contaminated coastal waters offers minimal exposure, as microplastic penetration through intact skin is negligible without associated chemicals or abrasion. Drinking water from desalinated marine sources may introduce trace amounts, but reverse osmosis processes in modern facilities filter particles effectively, reducing this vector's significance for most populations. Overall, ingestion dominates estimated exposures, with seafood and salts linking marine pollution directly to human intake.

Evidence of Risks and Uncertainties

Microplastics from marine sources enter the human body primarily through ingestion of contaminated seafood, such as shellfish and fish that accumulate particles via the food web, with estimated annual intake ranging from 39,000 to 52,000 particles per person via diet alone. Inhalation of airborne microplastics, including those transported from ocean surfaces, represents another route, with particles detected in human lung tissue and sputum samples from urban and coastal populations. Dermal contact with polluted water or sediments provides a minor pathway, though bioavailability via skin remains understudied and likely limited to nanoplastics. Detection of microplastics in human blood, placenta, and breast milk confirms systemic translocation, but concentrations are typically low, on the order of parts per billion. In vitro studies using human cell lines demonstrate that microplastics can induce oxidative stress, DNA damage, and inflammatory responses, particularly when carrying adsorbed pollutants like heavy metals or persistent organic compounds from marine environments. Animal models exposed to environmentally relevant doses of marine-derived microplastics exhibit metabolic disruptions, liver inflammation, and altered gut microbiota, suggesting plausible mechanisms for human effects such as endocrine disruption or cardiovascular strain. For instance, polystyrene microplastics, common in ocean debris, have been linked to increased lipid accumulation and immune dysregulation in rodent livers, mirroring potential risks from chronic low-dose exposure via seafood. Epidemiological correlations, such as higher microplastic levels in populations with elevated cardiovascular events, hint at associations, though causation remains unestablished. Despite these findings, substantial uncertainties persist regarding the magnitude and causality of risks. Human epidemiological data are scarce, with no robust longitudinal studies demonstrating direct links between marine microplastic exposure and disease outcomes like cancer or reproductive impairment; most derives from high-dose lab extrapolations that exceed real-world concentrations by orders of magnitude. Bioavailability is constrained by particle size—larger fragments (>150 μm) are often excreted via , while nanoplastics may translocate but at doses insufficient for in current models. The World Health Organization's 2019 assessment concluded that microplastics in pose low health concern due to limited of harm, a view echoed in subsequent reviews emphasizing variability in type, additive leaching, and individual susceptibility. factors, including co-exposure to legacy pollutants on plastics, complicate attribution, and standardized testing remains inconsistent, hindering risk quantification. Overall, while potential exists, current data indicate minimal proven risk, underscoring the need for prioritized research on dose-response thresholds and additive interactions over alarmist projections.

Mitigation Approaches

Technological Interventions

Technological interventions for marine plastic pollution primarily focus on preventing plastic entry into oceans via river interception systems and direct removal from marine environments, though scalability and ecological impacts remain challenges. River interceptors, such as The Ocean Cleanup's Interceptor, deploy solar-powered barriers and conveyor systems to capture floating debris before it reaches the sea; deployments in rivers like those in and have prevented thousands of kilograms of plastic from entering oceans annually. These systems target the estimated 80% of ocean plastic originating from land-based sources, particularly rivers in high-waste regions, with individual units capable of processing up to 50 cubic meters of water per second. Ocean-based cleanup technologies, exemplified by The Ocean Cleanup's System 03, use long floating booms to concentrate and extract plastics from gyres like the Great Pacific Garbage Patch; by 2024, the organization reported extracting over 1 million kilograms of plastic, aiming for 90% reduction by 2040 through iterative improvements in capture efficiency. However, assessments indicate variable effectiveness, with capture rates influenced by plastic fragmentation and drift dynamics, and full-scale operations potentially emitting 0.4 to 2.9 million metric tons of CO2 over a decade due to fuel and material use. Biotechnological approaches seek to degrade existing plastics using microbial enzymes, such as from , which breaks into monomers under ambient conditions; lab demonstrations show up to 90% degradation of certain plastics over weeks, but marine field applications remain limited by slow rates and incomplete mineralization. Engineered bacteria and fungi, including those modified for , offer promise for microplastic remediation, yet scalability in open oceans is hindered by dilution, , and potential ecosystem disruptions. Emerging monitoring technologies, including drone swarms and satellite-based , enhance intervention targeting by mapping plastic distributions with resolutions down to microplastic scales, informing deployment in hotspots. Overall, prevention technologies demonstrate higher cost-efficiency per removed compared to ocean extraction, underscoring the causal priority of source control over remediation.

Regulatory and Policy Measures

In 2022, the Environment Assembly (UNEA) adopted a resolution establishing an Intergovernmental Negotiating Committee (INC) to develop a legally binding international instrument addressing , including in the marine environment, with negotiations aiming for completion by the end of 2024. As of August 2025, the fifth session (INC-5.2) concluded without consensus on a text, primarily due to divisions over production caps, chemical regulations, and financial mechanisms, though member states expressed intent to resume talks. Existing frameworks like the Convention on the (UNCLOS) and the International Convention for the Prevention of Pollution from Ships (MARPOL) indirectly address through general pollution prevention obligations, but lack specific enforceable targets for plastics. At the national level, numerous countries have implemented bans or restrictions on single-use plastics to curb marine inputs. In the United States, the Save Our Seas 2.0 Act of 2020 directed the Agency (EPA) to develop a National Strategy to Prevent Plastic Pollution, finalized in 2024, which promotes reuse systems, taxes, and bans on certain single-use items while emphasizing accountability. As of March 2025, 19 U.S. states and territories have enacted jurisdiction-wide bans on one or more single-use plastics, such as bags and foam, with studies showing these measures reduce litter by up to 70-90% in affected areas. leads with a 2014 ban on single-use s and prohibitions on in rinse-off products, contributing to lower coastal levels. Regionally, the European Union has advanced directives like the 2019 Single-Use Plastics Directive, banning items such as straws, cutlery, and plates, with member states required to transpose these by 2021 and report on implementation efficacy. Other nations, including Kenya (2017 nationwide plastic bag ban) and Rwanda (2008 ban), have enforced strict prohibitions, often coupled with fines, resulting in measurable declines in riverine plastic leakage to oceans. Despite these efforts, analyses indicate that while bans effectively target visible litter, broader marine pollution—estimated at 80% from land-based mismanaged waste—requires integrated waste management and enforcement, with fewer than 10% of global policies rigorously evaluated for long-term ocean impacts.

Market-Driven and Innovative Solutions

Private sector initiatives have developed scalable technologies to intercept plastic waste in rivers and coastal areas, preventing entry into marine environments. , founded as a private engineering effort, deploys Interceptor systems in rivers, which passively capture debris using river flow. These systems target the estimated 80% of ocean plastic originating from land-based sources via waterways. By December 2024, the organization had extracted 11.5 million kilograms of plastic from oceans and rivers combined, surpassing prior annual totals. In the first half of 2025, deployments captured more trash than in all of 2024, contributing to a cumulative removal exceeding 30 million kilograms by mid-year. Startups like RanMarine offer autonomous electric vessels, such as the WasteShark drone, designed for harbors and inland waters to collect floating plastics, oils, and organics without emissions. Deployed in over 40 locations worldwide by , these devices process up to 500 kilograms of waste per day per unit, supported by private investments including EU BlueInvest funding. Similarly, Seabin Technology produces floating catchment devices that skim surface litter from marinas, with over 1,000 units installed globally by 2023, capturing millions of kilograms annually through sales to yacht clubs and ports. On the materials front, chemical firms enable circular economies by breaking down plastics into reusable s, reducing reliance on virgin production that risks mismanagement into oceans. Agilyx employs and to recycle and mixed plastics, operating commercial plants that process thousands of tons yearly into styrene for new products. ExxonMobil's advanced facilities, operational since 2022, convert into molecular building blocks, with partnerships scaling output to mitigate and pathways. These technologies address the 5.8 billion tons of plastic produced historically, of which only 9% has been recycled mechanically, by offering higher-quality loops. Corporate collaborations, such as 4ocean's model tying product sales to equivalent extractions, have removed over 19 million pounds of debris by through consumer-funded pulls, incentivizing market participation via branded sustainable goods. In , enzyme-based innovations, including those from firms advancing microbial degradation, promise on-site breakdown of plastics, though commercial scalability remains nascent. These efforts, driven by profit motives and investor capital, complement but do not yet match the volume of annual plastic inputs estimated at 11 million metric tons to oceans.

Individual Actions

Individuals can reduce contributions to marine plastic pollution by minimizing single-use plastics through the use of reusable bags, water bottles, metal straws, and durable containers in place of disposables. Selecting products with reduced packaging and avoiding cosmetics containing microbeads further limits plastic inputs from consumer waste streams, complementing broader technological, regulatory, and market-driven mitigation efforts.

Controversies and Scientific Debates

Scale and Severity Assessments

Estimates of plastic entering the oceans annually range from 1 to 23 million metric tonnes, with recent assessments converging toward the lower end of 1-2.4 million tonnes primarily from land-based sources via rivers, though higher figures from organizations like UNEP include broader aquatic ecosystems. This variability stems from differences in modeling inputs, such as mismanaged waste projections and riverine transport efficiencies, with peer-reviewed studies emphasizing empirical data over extrapolations that may overestimate fluxes due to unaccounted sinks like coastal deposition. The standing stock of plastic in the marine environment is estimated at 75-199 million tonnes cumulatively, but surface-floating debris constitutes a small fraction—approximately 0.3 million tonnes for macroplastics and microplastics combined—indicating substantial removal via beaching, sinking, and biofouling. This total mass, approximating 150 million tonnes, corresponds to roughly 150 million cubic meters in volume (assuming an average density of about 1 g/cm³), contributing an extremely small amount to sea level rise—approximately 0.0004 mm in total—because the displaced volume is spread over the vast ocean surface area of about 361 million km²; this is negligible compared to the observed sea level rise of ~3.7 mm per year, primarily driven by thermal expansion of seawater and melting land ice. Microplastic concentrations in surface waters average around 2.76 particles per cubic meter across ocean basins, with subsurface abundances varying from 10^{-4} to 10^4 particles per cubic meter, highlighting heterogeneous distribution influenced by ocean currents and particle properties. Global microplastic particle counts are assessed at 82-358 trillion, equivalent to 1.1-4.9 million tonnes, predominantly small fragments rather than primary particles. Severity assessments quantify ecological exposure rather than definitive harm, with plastic debris documented in over 267 species, including by 44% of species and entanglement risks for marine mammals. However, discrepancies—where observed oceanic stocks are orders of magnitude below cumulative inputs—suggest overestimation of persistence or under-sampling of submerged fractions, complicating severity claims; fragmentation into may dilute visibility but increase . Quantitative impact models indicate potential annual economic losses from habitat degradation around 8 billion USD, though these integrate unverified assumptions on decline causality. Debates persist on whether alarmist scales amplify responses disproportionate to verified trophic disruptions, as empirical long-term show stable or declining macroplastic abundances in some regions despite rising inputs.

Attribution of Causality and Comparative Priorities

Empirical assessments attribute the majority of marine plastic pollution to land-based sources, with estimates ranging from 70% to 80% of ocean plastics entering via rivers, coastal runoff, and direct littering from mismanaged waste. Riverine transport dominates, as approximately 1,000 rivers—primarily in Asia and Africa—account for nearly 80% of global annual plastic emissions to the ocean. These inputs stem largely from inadequate waste management infrastructure in densely populated coastal regions, where uncollected or improperly disposed waste enters waterways during storms or through open dumping. Regional disparities underscore the concentration of emissions: Asian countries contribute around 86% of plastic waste flowing into the ocean, driven by high volumes of total waste generation combined with elevated rates of mismanagement in nations like , , the , and . In contrast, while high-income countries generate substantial consumption per capita, their advanced waste systems result in negligible ocean inputs, often below 1% of global totals despite exporting some recyclables that may be mismanaged abroad. Sea-based sources, such as abandoned fishing gear and shipping debris, comprise 20% to 30% of inputs globally but dominate in accumulation zones like the Great Pacific Garbage Patch, where they represent up to 80% of collected macroplastics due to their durability and persistence at sea. Microplastics add complexity, with secondary sources like tire abrasion and synthetic fiber shedding from laundry contributing diffusely from land, though primary macroplastic litter remains the principal vector for initial ocean entry. Comparative priorities emphasize source prevention over remediation, as interventions targeting high-emission rivers could avert 80% of riverine flows at lower cost than , which recovers only a fraction of dispersed debris. Enhancing and in top-emitting developing regions yields higher marginal returns than broad production reductions in low-mismanagement areas, given that only 1-2% of mismanaged typically reaches the even without intervention. Debates persist over undercounting durable sea-based items like ghost nets, which may constitute 50-100% of macrodebris in remote areas, challenging narratives that overprioritize land sources uniformly. However, causal realism favors data-driven allocation: total emission volumes, not consumption, dictate accumulation, prioritizing aid and to mismanagement hotspots over global bans that overlook local enforcement gaps.

Efficacy and Unintended Consequences of Responses

Efforts to mitigate marine through regulatory bans on single-use items, such as s, have demonstrated localized reductions in specific types but limited broader impacts on ocean-wide levels. A peer-reviewed analysis of cleanup data from multiple U.S. sites found that bans correlated with 25-47% fewer bags encountered on shorelines in affected areas, attributing this to decreased usage and disposal. However, global assessments indicate these measures fail to significantly marine inputs, as the of —estimated at over 80%—originates from mismanaged waste in rivers of developing nations like and , where such bans are often unenforced or absent. Consequently, policies in high-income countries address only a minor fraction of the influx, with legacy plastics from prior decades persisting and fragmenting into that evade surface-level interventions. Beach cleanup initiatives effectively remove macroplastic debris and curb secondary microplastic release from shoreline erosion, with studies showing rapid declines in microplastic leakage following repeated efforts. These actions also enhance public awareness and may indirectly support policy adherence, outperforming passive education in fostering behavioral changes. Yet, their scalability is constrained: cleanups target accessible coastal zones, recovering less than 1% of total oceanic plastic, which predominantly accumulates in remote gyres or sinks as microplastics beyond reach. Emerging technologies, such as river interception barriers and ocean booms, show promise in preventing entry—capturing up to 86% of riverine plastics in trials—but face challenges in high-flow environments and require sustained maintenance to avoid structural failures that could exacerbate fragmentation. Unintended consequences of these responses often undermine net environmental gains. Plastic bag bans frequently prompt substitution with thicker "reusable" bags, which consumers discard after fewer uses, or alternatives that demand higher inputs and emit more gases during production—up to 50 times more than thin plastics per unit. Empirical data from banned regions reveal "spillover" effects, including rises in unregulated like foil packets or increased purchases of s once fees are imposed, persisting even post-repeal in some jurisdictions. Cleanup operations, while beneficial, can disturb sediments and release embedded or harm benthic organisms if mechanized methods are employed without targeted protocols. Broader pushes for reduced production overlook causal realities, such as the barriers posed to vulnerable populations—e.g., homeless individuals relying on single-use for —potentially elevating transmission risks without viable substitutes. These outcomes highlight the need for interventions prioritizing infrastructure in source hotspots over symbolic restrictions in low-contribution regions.

Historical Context

Pre-Modern Observations

Marine plastic pollution, as a distinct environmental issue, did not exist in pre-modern eras due to the absence of synthetic polymers. The first fully synthetic plastic, , was invented in 1907 by , with widespread production and disposal occurring only after . Prior to this, consisted primarily of biodegradable materials such as wooden wreckage from ships, natural fibers like ropes, and organic refuse from coastal settlements or fishing activities. These substances decomposed through microbial action and physical breakdown within months to a few years in , precluding the long-term persistence and accumulation seen with plastics today. Historical accounts from antiquity and the medieval period document episodic marine debris, typically linked to storms, naval conflicts, or exploration mishaps, but without evidence of chronic or widespread littering. For example, ancient mariners encountered floating flotsam in regions like the , which described in 1492 as impeded by tangled seaweed and possible wreckage, yet such observations emphasized transient, natural, or wooden elements rather than enduring pollutants. Similarly, 19th-century literature, such as Jules Verne's 1870 depiction in Twenty Thousand Leagues Under the Sea of debris converging in ocean gyres, reflected pre-plastic accumulations of organic and wooden matter, not synthetic waste. These pre-modern instances highlight that marine systems self-cleared debris efficiently compared to the recalcitrant nature of plastics, which resist and fragment into . The lack of persistent anthropogenic in pre-modern records underscores a key causal distinction: without industrial-scale production of non-degradable synthetics, oceans avoided the gyre-concentrated patches and hazards that define modern . from sediment cores and historical logs confirms minimal legacy debris from pre-1900 sources, as opposed to the traceable plastic signals emerging in the . This baseline of relative cleanliness informs assessments of plastic's unique , driven by its and volume exceeding natural debris cycles.

Modern Recognition and Key Developments

Scientific observations of plastic debris in the marine environment began in the early 1970s, with the first peer-reviewed report documenting small plastic particles in surface waters of the western North Atlantic, particularly in the , collected via plankton nets. These findings highlighted the persistence of plastics, which resisted degradation unlike natural materials, marking an initial shift from anecdotal beach litter reports to systematic evidence of ocean-wide distribution. By the mid-1970s, studies expanded to quantify waste dumping, with a 1975 U.S. assessment revealing that approximately 14 million tons of waste, including significant plastic fractions, had been legally discharged into oceans under international conventions up to that point. Concurrent in the 1970s documented plastic ingestion by seabirds and entanglement in , such as in studies from the 1960s onward on albatrosses and other species, underscoring risks though initial focus remained on macro-debris rather than fragmentation. A pivotal development occurred in 1997 when Captain Charles Moore, returning from the Transpacific Yacht Race, navigated through the North Pacific Subtropical Gyre and encountered extensive floating plastic debris, later termed the Great Pacific Garbage Patch; this observation, publicized through his Algalita Marine Research Foundation expeditions starting in 1999, drew global attention to gyre accumulations where plastics outnumbered by ratios up to 6:1 in some samples. Subsequent surveys in the 2000s revealed —fragments under 5 mm—from degraded larger items pervading surface waters, with early estimates in 2004 confirming their presence in open ocean communities. International recognition intensified in the , propelled by reports like the 2015 study estimating annual land-based plastic inputs to oceans at 1.15–2.51 million metric tons, primarily from mismanaged waste in coastal regions, shifting discourse toward source control over mere cleanup. The (UNEP) advanced this through initiatives like the 2016 Clean Seas campaign and 2021 assessments emphasizing 19–23 million tonnes of annual leakage into aquatic systems, though critiques note overreliance on modeled projections amid data gaps in historical baselines. These milestones catalyzed policy debates, revealing discrepancies in early underestimations of persistence and scale due to limited sampling technologies.

References

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