Trophic Transfer and Accumulation of Microplastics in Freshwater Ecosystem: Risk to Food Security and Human Health

sources and reducing exposure to these sources is of utmost importance.


Introduction
Te term "plastic" indicates a range of polymer materials that can be moulded into diferent sizes and shapes based on the requirements of the end product under diferent temperature and pressure conditions. Fossil resources such as coal, natural gas, and crude oil and organic products such as cellulose and so on are used for the production of these synthetic and semisynthetic polymers. Some of the major polymers include polypropylene (PP), polyethylene (PE), polystyrene (PS), polyvinyl chloride (PVC), polyethylene terephthalate (PET), polyamides (PA), and so on.
Microplastics (MPs) are those plastic particles with a size of not more than 5 mm and not less than 0.1 mm. Some researchers have suggested a few other terms and classifcations according to size range, such as macroplastics as particles larger than 5 mm, mesoplastics as particles in size between 5 and 1 mm, MPs as a size between 1 mm and 0.1 μm, and NPs as particles in size less than 0.1 μm [1]. Many such size ranges have been suggested by diferent researchers. However, generally, the size 5 mm is more accepted as the upper limit [2], as this size includes several small particles that can be readily consumed by organisms. Te plastic particles in these size ranges are again classifed according to their shape for research purposes and better understanding. Primarily, fve main groups or categories are used for the classifcation of MPs based on their shape (Table 1); sometimes the nomenclature may difer among research groups.
Once plastics break down into smaller particles, also known as MPs, and disperse into the environment, their elimination from any part of the ecosystem is a strenuous task. MPs are mostly introduced into aquatic habitats as a result of human activities, and their distribution is quite diverse. Te rise in human population density and the abundance of MPs have been shown to have a positive association, which might contribute to an increase in plastic debris accumulating in aquatic habitats [4]. Among the plastic wastes accumulating in the marine environment, 70-80% of MPs are imported through rivers [5]. In a recent study done at the Saigon River Estuary system, Vietnam, it is estimated that anthropogenic fber release from the river to sea was 115-164 × 10 12 items yr −1 [6].
Tere is evidence showing the presence of plastic in diferent environments/ecosystems for many years [7] and even within pristine and remote locations [8] even in the Artic [9]. Tese minute plastic particles are likely to be derived from diferent sources such as disposable articles, packaging items, particles from tyre and roads, wall paint, roadside litter, fbers from synthetic textiles, and so on [10]. Te composition and physicochemical characteristics of MPs are quite diverse, and attention to their environmental occurrence and impacts has switched to our inland waterways in recent years. For addressing the raising environmental questions regarding MPs, a thorough characterisation including their size, shape, and other major characteristics are important and necessary. In the last two eras, the research regarding MPs pollution has increased exponentially but authenticated and standardized methods for sampling, quantifcation, and characterisation of MPs are still lacking. As a result, interlaboratory comparability has been hampered, resulting in worse quality assurance and under or overestimation of MPs [11].
Secondary MPs and NPs are formed by the degradation of macroplastics through diferent kinds of stresses that impact the structure and reactivity of the polymer, thereby inducing degradation. Tese stresses include hydrolysis, photodegradation due to UV exposure, mechanical abrasion by sand or wave action, and biodegradation [5]. Most of the MP and NP emissions to the environment are accidental and occur without the knowledge of the user because these releases occur during diferent processes which are part of our daily lives.
Diferent kinds of plastics are used in manufacturing a diversity of products. Individual monomers are polymerized, forming the backbone of the polymer for these products. During these processes, several solvents and other chemicals are used as initiators and catalysts. In addition, several additives such as fame retardants, stabilizers, pigments, and fllers are included in the production process to give plastic certain characteristics such as fexibility, strength, and colour as per product requirements. Tese chemicals may get released into the environment at any stage of its life cycle, during production, use, or disposal of the product [12]. Based on the polymers used, additives, and byproducts, the United Nations and European Union frameworks estimate that more than half of all plastics produced are dangerous to the environment [13]. Tese chemical additives may get leached into the surrounding environment. And these chemicals can act as vectors for the contaminants in the environment and organisms.
Several studies have been conducted regarding the threats posed by MPs to aquatic life and ecological processes. Tese studies suggest that MPs may afect food security mainly in lower trophic level organisms [14], human health and well-being [15], and the diferent ecological processes associated with the ecosystem. In this review, we assess the capacity of MPs and NPs as vectors of chemical contaminants and also their efect on food security and human health through trophic transfer.

Cosmetics and Personal Care
Products. Te use of MP beads in personal care and cosmetic items is one of the most common sources and routes for persistent and potentially dangerous primary MP components to enter the aquatic environment [16]. Plastic particles are released directly into wastewater during and after daily use of personal care and cosmetic goods, as the majority of these products are washed of or fushed down the drain. A single scrape can release 4,500 to 94,500 PE microbeads, but a single 1.6 g of toothpaste can hold up to 4000 PE pieces [17]. A recent study in the UAE showed the presence of MPs in facial and body scrubs. Surprisingly, out of 37 products analysed, only 11 products had MPs particles in them [18].

Textiles and Commercial Cleaning of Synthetic Fibers.
Recent feld research identifed fbers as a prominent type of MP in diverse habitats, including remote locales, even in polar glaciers [19]. Textile microfbers are one of the major MP fber sources. Tese fbers get detached from the textile article during every step of its lifecycle, particularly during laundry [20]. Nonfltered efuents from commercial laundries release into the drains, which become a point source of microfbers just like home laundries, in which a single garment can release approximately > 1900 fbers in just one wash [21]. Also, the diferent washing parameters such as the International Journal of Ecology usage of detergents, the period of washing, and the type of fabrics afect the amount of fber released during laundry [22]. Synthetic fbers such as ester and nylon are often used in synthetic textiles [23]. Not only during washing but also during the normal usage of cloths, shredding of fbers will occur. A group of researchers studied this aspect in which they have done sampling lake sediment, snow, and ice purposefully wearing red overalls composed of cotton. And for all the detected fbers in the above-mentioned samples, 25 ± 1%, 20 ± 7%, and 8 ± 6% for snow, ice, and sediment, respectively, originated from sampling attire [11]. Tese fndings show that the normal usage of cloths also leads to the shredding of fbers and also self-contamination plays a signifcant role when quantifying MP pollution. A recent addition to the release of microplastic fbers to the environment is the single-use surgical masks and gloves, whose usage has enormously increased among the public due to the surge in COVID-19 [24].

From Household/Indoor.
Tere are many polymer-based products in our daily lives, both synthetic and natural, that we utilise both indoors and outdoors. Te release of particles during their abrasion is of least concern because of their negligible size, and not a huge amount of material per day is produced. However, all of these plastic substances abrasion and weathering are expected to add home source materials of macro and MPs. Te common things that we use in our households, such as plastic carpets, furniture, curtains, and so on, are shredding thousands of fbers daily. Even fakes and chips from ancient interior paint on the walls, polyurethane particles from mattresses, and plastic dust from electronics become microplastic sources [25]. Recent studies show that disposable plastic containers and disposable cups have traces of plastic particles, which may be unintentionally produced during manufacturing, becoming a primary source of MPs in the household [26]. Also, food packaging in plastic trays has shown traces of MPs in packed foods [27]. Toners in laser printers consist of a large amount of microscopic thermoplastic powder with a diameter of about 2-10 micrometers. Usually, this is a styrene-acrylate copolymer that is melted onto the paper when printing [28]. Te spill out of these toner products adds to the number of MPs particles in the indoor environment.

From Industrial or Commercial
Usage. Abrasive blasting media for cleaning metal surfaces, abrasive hand cleanser soaps, and various uses in the petroleum sector are just a few examples of commercial or industrial applications for primary MPs. In the process of abrasive blasting, sand or water is commonly used as the blasting media. Plastic beads, on the other hand, are favoured for blasting tougher surfaces when the blasting medium must not harm the surface. Tis will release a vast number of plastic particles into the surroundings during the process, which will be fnally washed of into a drain. In geotechnical engineering, while drilling oil and natural gas wells, a drilling fuid is used. Drilling fuids based on plastic microbeads have been used for decades, and Tefon-enhanced particles have even been trademarked and sold globally for drilling purposes [29]. Termal cutting of polystyrene foam produces nanometersized polymer particles with a diameter of 22-220 nm [30].
During their life cycle, many polymers undergo similar thermal treatments. In a study, it is observed that nanometer-sized polymers are emitted during 3D printing in the range of ∼11-116 nm [31], at a considerable rate. Furthermore, several polymer nanoparticles are simple to make and are employed in research and other uses, so they will end up in the environment.

From Fisheries and Aquaculture.
In both fsheries and aquaculture, plastics are signifcant components. Many tools, such as nets, fshing gears, trawls, dredges, hooks and lines, fsh hold insulation, fsh crates, and packing materials, are used in both of these industries. With the advancement of industries, most of these tools are made from synthetic or semisynthetic plastic materials [3]. Synthetic fbers are considered to be more benefcial than natural fber ropes as they ofer more strength and durability and also reduce the overall weight of the tools to a great extent when compared with the old conventional tools. However, in addition to the benefts that synthetic types of equipment give, the fip side of the issue is that when these equipment age and get destroyed, the plastic components immediately enter the water [32], where they decompose to generate MPs and NPs.

From Wastewater Treatment Plants.
Wastewater treatment plants could potentially be a major source of MPs in the aquatic environment [2,33]. In all the above sources that we have discussed, the ultimate destination of those MPs will be wastewater, thereby entering a wastewater treatment plant [17]. Granulated PE, PP, and PS particles found in personal care products (PCPs), cleaning agents, and airblasting media are small enough to bypass the treatment process in wastewater treatment plants [34]. Synthetic clothing, such as polyester and nylon, is also an issue since these materials may shed thousands of synthetic threads into drains during textile manufacturing and laundering. Wastewater treatment systems are not specifcally designed to deal with plastic materials [35].
With the higher usage of pesticides in agriculture, approximately 80,000 tonnes annually [36], the soil ecosystems were damaged both physically and biologically. So, to improve the physical qualities of these soils, processed heatdried sludge is marketed and used as a soil amendment/ conditioner in some places. However, this may pose an additional threat to the soil ecosystem. A study conducted at a wastewater treatment plant in Spain found that the sludge from the plant used for soil improvement could spread up to 10 13 MP particles in agricultural soils per year [37].

Spills during Production and Transport.
For the production of diferent plastic products, granulated forms of plastic are used as raw materials. Also, the used plastics in their recycling stage are converted into plastic granules. During the preproduction and recycling stages, there are International Journal of Ecology high chances for accidental discharge of these granules to the surrounding environment. Hence, the plastic manufacturing and conversion process is often considered a point source for MP discharge into the environment [38]. Tese pelleted or granulated plastics are transported through various means, such as rail, road, air, and water. During all these means particularly by rail, road, and water, these pellets can be spilled into the immediate surroundings.

MPs and NPs as Vectors for Chemical Contaminants and
Heavy Metals. Compared to other usual pathways, the possible role of MPs and NPs as vectors for hydrophobic organic chemicals (HOCs) and heavy metals (HMs) is an issue of much concern. Te sorption of HOCs and HMs to MPs is considered a signifcant environmental process because this will afect the mobility and bioavailability of these pollutants [39]. MPs interact with organic pollutants before, during, and after they are released into natural environments [40]. And adsorption kinetics are infuenced by a variety of parameters, including polymer type, density, and crystallinity, as well as the surrounding environment and contaminants present [41].
Also, the photoaging of certain polymers is found to increase their absorption capacity for hydrophobic organic pollutants [42]. Te buoyancy and transport mechanism of MPs primarily depends on their density, size, and shape [43]. In the freshwater environment, MPs are likely to co-occur with other emerging contaminants such as pharmaceuticals, personal care products, fame retardants, fuorinated and sulfonated organic compounds, household cleaning products, and other industrial chemicals, which enter the environment as a part of complex solid and liquid waste streams [44].
Te general sorption mechanisms found in MPs are hydrophobic interactions, electrostatic interactions, pore flling, Van der Wall forces, hydrogen bonding, and π-π interactions and the type of mechanism depends on the characteristics of the sorbent and sorbate [45]. Since common polymers such as PS, PP, PE, or PET are hydrophobic, among these sorption mechanisms, hydrophobic interaction is the most dominant one [46]. During hydrophobic interaction, an aggregate or cluster is formed by the attraction between two nonpolar substances. Te electrostatic interactions occur due to the attraction between oppositely charged molecules or the repulsion of molecules of similar charge [46]. Te pore-flling process depends on the polymer structure, particularly its pore diameter, and also on the molecular size of the pollutant/chemical. During the poreflling process, the contaminants enter the polymer matrix and get trapped in the small pores of microplastics, and pollutants with lower molecular weight are found to move easily through the polymer matrix with larger pores [47,48]. Laboratory and feld studies show that MPs can adsorb chemicals ranging from 1 to 10,000 ng/g [49].
Due to the high surface area of NPs, they show higher sorption afnities for toxic compounds than MPs [50]. Tis sorption process may difer for diferent polymers and diferent chemicals based on the polymer structure and hydrophobicity of the chemicals. Te diferent additives used in the polymers can also change their structure and thereby afect the sorption process [51]. Polypropylene microfbers are shown to adsorb toxic chemicals such as PCBs (polychlorinated biphenyls), DDE (dichlorodiphenyldichloroethylene), and nonylphenols, whereas polyethylene adsorbs four times more PCBs than polypropylene [52]. After the adsorption of the chemicals to the polymer surface, their transport through the polymer matrix depends on diferent factors of the polymer, such as the free volume within the polymer, the distance between the polymer chains, and the ability of a polymer to transform into diferent physical conformations, which is the segmental mobility of the polymer. With the increase in the distance between polymer chains, the sorptive capacity also increases. Te immediate environment (water, sediment) of the polymer and the chemical also afects the sorption capacity [53].
Tese chemical contaminants and HMs can be transferred from MPs to organisms in an aquatic environment either through the liquid media or by direct interaction exposure of MPs to the organism's skin or exoskeleton. If an organism ingests MPs containing these sorbed contaminants, these contaminants can be moved to the organism's tissue via extracellular/interstitial fuids or direct contact between the MPs and the organism's interior walls. While uptake occurs through water or intraorganismal fuids, desorption of HOCs from the sorbent is required to form freely dissolved molecules. Tis desorption of adsorbed molecules depends on many factors, and it mainly decreases with an increase in partition ratios and increasing binding strength [39]. Mayer [54] in one of his studies found out that HOCs sorbed to MPs are likely to be transferred more rapidly through intraorganismal fuids than water to biota. Te uptake through direct contact with the external or internal parts of the organism might be an important but still overlooked route of exposure.
Also, the increased surface area of MPs provides a favourable environment for the establishment of microbial communities on the MPs' surface and thereby alters the natural composition and structure of microbial communities in the natural environment [55]. Such bacterial bioflms formed on MPs have been shown to include bacteria with antibiotic-resistant genes [56], which might originate from human and animal populations treated with antibiotics and transfer downstream through wastewater into aquatic ecosystems [57]. Tese antibiotics have shown higher adsorption to MPs in freshwater ecosystems than in marine ecosystems. Te spread of these antibiotic-resistant bacteria (ARB) and/or antibiotic-resistant genes (ARG) makes water bodies natural sinks of antibiotic resistance and paves the way for another major societal and economic concern.
2.9. Accumulation of Micro and Nano Plastics through Trophic Transfer. Concerns about the incorporation of MPs and NPs into food webs have grown as the number of MPs and NPs in the aquatic system has increased. Te efect of polymers or plastics starts from the lowest level of the food web itself in the aquatic environment. MPs are the same size as plankton and grains of other organic food materials, allowing them to be consumed by a variety of organisms with various feeding strategies [58]. Also, the diference in densities and shapes of these polymers afects their behavior [59] and distribution into diferent compartments (surface, water column, and sediment) of the aquatic environment and infuences their availability to organisms at diferent trophic levels [60]. Te ingestion of MPs causes several physical and biological impacts on the organisms. It disrupts feeding in algae and flter-feeding organisms [61], thereby reducing the weight of the organisms and thus leading to mortality and a decrease in fertility [62]. As discussed in the earlier section, apart from the physical impacts of ingested MPs alone on organisms, adverse health efects also occur from additives, sorbed contaminants, and so on, which are carcinogenic and even capable of endocrine disruption in organisms [63]. Te efects of diferent types of polymers on some freshwater organisms are listed in Table 2.
Te ingestion could be due to a failure to distinguish MPs from the prey, or it could be due to the intake of lifeforms from lower trophic levels that contain these particles [76]. MPs may also adhere directly to organisms [77]. In terms of food safety, MPs and NPs are also an emerging threat, as these particles can eventually end up in the human food chain through fsh and other kinds of aquatic foods and also through other aquatic-based products [78].
Biofouling may play a key role in the faulty identifcation of plastic as a food source by organisms [79]. Studies suggest that the formation of bioflms increases the likelihood of MP ingestion by altering the vertical distribution of the particle, and they attract organisms by a diethyl sulphide odour which is associated with organic matter that is produced during the breakdown of bioflms on the plastic surface [80]. Sea turtles were also found to ingest plastics for the same reason, with visual cues also playing an important role [81]. Te ingestion of fouled plastic particles is not limited to higher trophic organisms. Copepods exposed to both clean and fouled PS particles ingested a higher frequency of aged particles with a bioflm [82].
Te nutrient cycling or nutrient availability in an aquatic ecosystem is highly dependent on Zooplanktons. Te primary producers and higher trophic organisms are linked by them. Tey consume the primary producers and convert the organic matter into fecal pellets of high density and sinking velocity [83] so that it becomes available to sedimentary organisms and also adds to the carbon sink in the aquatic ecosystem [84]. Along with the food intake, MPs also get ingested and also get egested with fecal pellets. Tese plastic particles present in the fecal pellet could be trophically transferred to other coprophagous animals [85]. All the plastic particles which are ingested by the zooplankton may not get egested through feces. Tus, the residual plastics in the gut of zooplanktons directly get transferred to the higher tropic levels by preying on them.
NPs, either primary or degraded from MPs, enter the food chain through algae, bacteria, and/or flter-feeding organisms [58]. Algae and phytoplankton, which are the major primary producers and credited for half of the total photosynthesis on Earth and the conversion of solar energy into biomass, are facing a threat from these tiny plastic particles. Bhattacharya published the frst evidence of the physical infuence of NP beads on two algae species, Chlorella sp. and Scenedesmus sp [86]. In that study, the adsorption of NPs occurred due to the electrostatic attraction between the positively charged algal cellulose and negatively charged NP beads. Tis tendency of adsorption depends on the cell morphology and motility of the algae and it leads to the generation of an induced reactive oxygen species in the algae. In another study, a signifcant reduction of photosynthesis was seen in algae Dunaliella tertiolecta, Talassiosira pseudonana, and Chlorella vulgaris upon 72 h exposure to micropolystyrene particles, but no changes in algal growth rate were found [87].
Te efects of food chain transfer have been experimented within a study in which an algal species exposed to nanopolystyrene particles and afected by a reduction in chlorophyll were further exposed to the zooplankton Daphnia sp., which resulted in several alterations in reproduction and reduced body size [88]. It was the frst study to show the efects of NPs exposure in algae and Daphnia populations through food chain transfer. A study on the next level of the food chain was conducted in which Daphnia magna exposed to PS nanoparticles was further given to fsh (Crucian carp), and the results were more than expected, that is, not only did the direct uptake of PS NPs from Daphnia magna to fsh (Crucian carp) occurred but also the PS NPs entered the brain of the fsh, which resulted in behavioral disorders and decreased survival rate of the fsh [89].
Benthic and pelagic food webs also get afected by MP and NP accumulation and transfer. Tere is evidence of the trophic transfer of MPs from blue mussels to crabs. Te blue mussel (Mytilus edulis) previously exposed to PS-MPs was further fed to crabs (Carcinus maenas). After 24 hours of exposure, 0.027% of the concentration of MPs fed to the mussels was reported in the crab hemolymph [90]. It is suggested that the feeding type or feeding habits may also afect the percentage of uptake of MPs in organisms. A study reveals that omnivorous fsh species have registered higher MP content than carnivores and herbivores organisms. Tey concluded that the broader diet source of omnivorous organisms is the reason for higher MP content in them [91]. All these results indicate the possible accumulation of micro and nanoplastic particles through the food chain either via direct or indirect uptake. Direct uptake occurs when the organisms could not distinguish between natural prey and synthetic items, while indirect uptake occurs through feeding on previously exposed prey [92]. If the basic level of a food web gets harmed, its efects will be forwarded through the food chain to the entire food web, maybe not very rapidly but in an unpredictable or less recognized manner.
In the case of human consumption of fsh or other aquatic organisms, mostly only the edible feshy parts are consumed, and the visceral organs are excluded, where the ingested MPs are more likely to accumulate but in the case of some small pelagic fsh species that are consumed as such, it poses a risk to human food security. As discussed earlier, rather than the efects of plastics, the additives and chemical contaminants in them pose a greater threat to ecosystem health. PS Danio rerio Infammation and lipid accumulation in fsh liver-oxidative stress was induced. Alterations of metabolic profles in fsh liver [73] PE, PP

Hyalella azteca
Decreased growth and reproduction [74] 6 International Journal of Ecology

Microplastic to Humans through the Aquatic Food Chain.
Several studies have been reported on the exposure and transfer of diferent types of MPs to humans [93] and to diferent parts of the human body. Recently, scientists confrmed the presence of microplastics even in human blood [94] and in human lung tissue [95], which indicates the level of microplastic pollution and its impact on humans. Te available literature regarding the trophic transfer of MPs from aquatic food chains, particularly freshwater ecosystems, to humans is found to be scarce. Te two signifcant exposure pathways of MPs to humans are inhalation and ingestion, and the latter mostly happens through aquatic food consumption. In the freshwater ecosystem, the transfer of MPs to humans happens through the consumption of aquatic organisms. Tere is evidence of MPs in many freshwater organisms consumed by humans, such as fsh [1], bivalves [96], shrimps, and crabs [97]. Te greater risk is when, in the case of some species of fsh, consumption as a whole or incomplete removal of the viscera can increase the MPs load entering the human body [98]. Also, studies show the presence of microplastics in the edible fesh part of fsh, which increases the risk of exposure to MPs [99].
In a study conducted by Senathirajah et al. [100], they made a preliminary estimate of the potential amount of microplastics that may be ingested by humans from aquatic, atmospheric, and other consumables. Te results indicate that globally, on average, humans could potentially be ingesting 0.1-5 g of microplastics per week. So far, there is no accurate data on the mass of MPs ingested by humans through the aquatic food chain alone. However, in a recent study, it is estimated that the per capita microplastic intake through the consumption of shellfsh can be approximately 13 ± 58 microplastic particles per year, in which they studied two species of shrimp, one crab species and one species of squid. An average of 3.2 ± 10 microplastic particles kg −1 have been reported in the edible tissue of one species of crab, Portunus pelagicus [98].
Te impact of MPs on aquatic organisms is a welldiscussed area, but the impacts on humans are yet to be studied or are still in their infancy. Tere is stronger evidence for the ingestion of microplastics by humans since studies show the presence of MPs even in human feces [101]. Deng [102] in his study on mice found that the MPs may accumulate in the liver, kidney, and gut and have adverse efects on the liver, such as troubles in lipid and energy metabolism, oxidative stress, and neurotoxic responses. Tis raises concerns about the same toxicity in human liver cells too [103]. A study conducted on the toxicity of PS-MPs in the human lung epithelial BEAS-2B cells revealed that it can cause cytotoxic and infammatory efects in BEAS-2B cells by inducing reactive oxygen species formation, thereby posing a risk to human respiratory health [104].

Conclusion
Biomagnifcation is not often reported in the case of MPs in organisms and the higher risk is posed or more reported to lower trophic level organisms. However, many studies have revealedthe presence of MPs in species of marine organisms particularly fshes consumed by humans which may occur by the direct exposure of the species to MPs. Currently, there is no clear evidence whether MPs and NPs have a serious efect on humans as it does on aquatic organisms, as the level of these plastics ingested is not at sufcient concentrations to cause the same issues as they do in aquatic animals. When we consider that many aquatic organisms are relevant to the fsh industry and that they can ingest these tiny plastics, it is logical to hypothesize potential risks to human health and food security. Chemically speaking, the plastics themselves are generally inert and do not have much efect on human health. However, the substances with greater concern are the chemical additives used in plastics during manufacturing, toxic chemicals absorbed, and harmful pathogens attached to plastics from the contaminated ecosystem that have potentially negative efects on organisms and ecosystem health. Since these plastic particles have an impact on all environmental matrices, thorough studies on their impact on the terrestrial ecosystem, plant growth performance and yield, atmospheric interactions, and so on also should be conducted.
From the above-mentioned sources of MP and NP emissions to the environment, it is well understood that the major pathways of MP emissions are by the common people through laundry, cosmetics and personal care products, abrasion of household plastics, and so on. However, the public is not much aware of their contribution to this type of pollution. Hence, awareness should be given to the general public about these harmful emissions and they should be encouraged to use plastic-free personal care products, fewer plastics in households, and so on, thereby trimming down the emissions. More eforts should be given to better plastic waste management and monitoring so that it will not enter the environment in a harmful way.
For a better understanding of the current stage of plastic pollution in the aquatic ecosystem, the feld databases about plastics in all size fractions should be increased particularly in freshwater environments. Since plastics fnd their way to oceans mainly through rivers, the estimation of river plastic emissions to the oceans is important. Also, more research studies are needed to identify the role of plastics as vectors for biological and chemical contaminants in the biota. Tere is a lack of studies on the efect of MPs and NPs on humans through the food chain which is a very serious threat to human food security. Terefore, in-depth studies should be carried out and immediate remedial measures should be taken before the MPs and NPs invade our daily diet.

Conflicts of Interest
Te authors declare that they have no conficts of interest.