Abundance of microplastics and nanoplastics in urban atmosphere.

Chapter 2 - Sources and occurrence of microplastics and nanoplastics in the environment

The evidence of in-vivo and in-vitro studies on microplastic and nano plastic toxicity in mammals: A possible threat for an upcoming generation?

Plastics are an integral but largely inconspicuous part of daily human routines. The present review paper uses cross-disciplinary scientific literature to examine and assess the possible effects of nanoplastics (NPs) concerning microplastics (MPs) on human health and summarizes crucial areas for future research. Although research on the nature and consequences of MPs has seen a substantial rise, only limited studies have concentrated on the atmospheric nanosized polymeric particles. However, due to the intrinsic technological complications in separating and computing them, their existence has been difficult to determine correctly. There is a consensus that these are not only existing in the environment but can get directly released or as the outcome of weathering of larger fragments, and it is believed to be that combustion can be the tertiary source of polymeric particles. NPs can have harmful consequences on human health, and their exposure may happen via ingestion, inhalation, or absorption by the skin. The atmospheric fallout of micro (nano) plastics may be responsible for contaminating the environment. Apart from this, different drivers affect the concentration of micro (nano) plastics in every environment compartment like wind, water currents, vectors, soil erosion, run-off, etc. Their high specific surface for the sorption of organic pollutions and toxic heavy metals and possible transfer between organisms at different nutrient levels make the study of NPs an urgent priority. These NPs could potentially cause physical damage by the particles themselves and biological stress by NPs alone or by leaching additives. However, there is minimal understanding of the occurrence, distribution, abundance, and fate of NPs in the environment, partially due to the lack of suitable techniques for separating and identifying NPs from complex environmental matrices.HighlightsMicro (nano) plastics generated may reach the soil, water, and atmospheric compartments.Atmospheric currents serve as a way to transport, leading to micro (nano) plastics pollution.Exposure to micro (nano) plastics may happen via ingestion, inhalation, or absorption by the skin.Nanoplastics may be environmentally more harmful than other plastic particles; the focus should be on defining the exact size range.Visual classification of micro (nano) plastics is poor in reliability and may also contribute to microplastics being misidentified.Graphical abstract

Micro(nano)plastics pollution and human health: How plastics can induce carcinogenesis to humans?

Emission of microplastics (MP) to the atmosphere, airborne transport, and subsequent deposition are now recognized. However, the temporal and spatial resolution of data on MP pollution and knowledge of their atmospheric behaviour and fate is still very limited. Hence, we investigated MP wet and dry deposition in Central Germany and examined the role of weather conditions on MP contamination levels. Monthly samples of dry and wet deposition were taken over an eight-month period (05/2019-12/2019) and analysed by micro-Fourier-Transform Infrared spectroscopy (µFTIR) down to 11 μm particle size and one dry deposition sample was subjected to Raman analysis to determine plastic particles down to a size of 0.5 μm. MP in a size range from 11 μm to 130 μm were detected in all wet deposition samples and in 4 out of 8 dry deposition samples by µFTIR. Polypropylene particles were found most frequently and accounted for 62% and 54% of all particles in wet and dry deposition samples, respectively. Over the eight-month period, wet deposition of MP slightly dominated at the study site and comprised 59% of the total MP deposition. The MP mean total (wet + dry) deposition flux (DF) was 17 ± 14 MP m− 2 day− 1. Extensive Raman analyses of an exemplary dry deposition sample revealed additional plastic particles in the extended size range from 1 to 10 μm resulting in a deposition flux of 207 MP m− 2 day− 1. Our results suggest that MP analysis by µFTIR down to 11 μm may underestimate DF at least by an order of magnitude. More comprehensive studies on submicron plastics and nanoplastics are needed to fully assess air pollution by plastic particles.

Toxicity assessment of environmental MPs and NPs and polystyrene NPs on the bivalve Corbicula fluminea using a multi-marker approach

Metagenomic analysis reveals the responses of microbial communities and nitrogen metabolic pathways to polystyrene micro(nano)plastics in activated sludge systems.

Micro- and nanoplastics are plastic particles which are widely distributed in the environment. The pollution status and toxicity of micro- and nanoplastics in various environment matrices have attracted increcesing attention in recent years. In this review, we systematically assess the current literature on the sources and occurrences of micro- and nanoplastics in the environment and their potential impacts on marine organisms. We also discussed the potential human health effect of micro- and nanoplastics by uptake kinetics and toxicity assessment, and the toxic effects of the typical pollutants caused by micro- and nanoplastics. The results show that the sources of micro (nano) plastics in the terrestrial environment are mainly sewage sludge application, residues of plastic products used in agriculture, irrigation water contaminated by microplastics and/or aerial deposition. The micro (nano) plastics enter marine environment mainly by land input, seaside tourism, navigation shipping, marine farming and/or aerial deposition. In the marine environment, micro- and nanoplastics can be transported and accumulated through an aquatic food chain from lower trophic level to higher ones, and disturb the metabolism and propagation of the organisms. The toxicity of micro- and nanoplastics is dependent on the size and functional groups on the surface of plastic particles. In general, nanoplastics with smaller size might more easily penetrate and aggregate in cells and tissues and positively charged nanoplastics pose distinct effects on the physiological activity of the cells. Besides, the release of organic pollutants adsorbed on the plastic particles pose more serious toxic effects than the plastics themselves. We hope this review can provide effective support for systematic risk assessment and toxicology of micro- and nanoplastics in future research.

Plastics released into the environment can be degraded by physical erosion, biodegradation, photocatalytic activity, and oxidation, resulting in smaller plastics particles. Microplastics (MPs) are plastic particles relatively smaller than 5 mm in size. Furthermore, microplastics with particle sizes less than 1000 or 100 nm are known as nano-plastics (NPs). The presence and effect of MPs and NPs in human body has not been adequately studies, thus we aim to explain the origins of MPs and NPs adept, carefully explore the pathways by which MPs and NPs enter the body system and highlight the impact of MPs and NPs on human health. Major examples include Polyethylene (PE), polypropylene (PP), polyvinyl chloride (PVC), polyamide (PA), polystyrene (PS), polyethylene terephthalate (PET), Acrylonitrile-Butadiene-Styrene (ABS), and polymethyl methacrylate (PMMA). MPs and NPs were found to have two sources (primary and secondary). The primary sources are materials purposely produced to suit household and industrial uses, such as exfoliants for skin care products, construction, and packaging materials. Secondary sources originated from the decomposition/degradation of large plastic products over time. Plastics were found in plants (fruits and vegetables), animals (fish, crab, shrimp, oysters, and mussels), water (taps, sachet, and bottled water), salt, sugar, and honey. Plastics' impact on the human ecosystem is getting increasingly severe, and it is imperative that proper attention be paid to this issue. The vast number of MPs and NPs available can influence the lives of the populace in each geographic area. In this review article, we identified three routes through which MPs and NPs gain entrance into the human body: oral ingestion, cutaneous (skin contact), and inhalation. Furthermore, we investigated and summarized the impacts of MPs and NPs on human health. The most impacted organs in the body included the lungs, blood, kidney, brain, ovary, testes, and intestines. In this review, we offered a viable solution that includes the use of biodegradable polymers, increased usage of eco-friendly biotechnology and engineering solutions, and the implementation of regulatory measures. In future, we intend to investigate the bioaccumulation and effect of MPs/NPs on human health.

Resolving the effects of environmental micro- and nanoplastics exposure in biota: A knowledge gap analysis.

To date, previous studies have reported the adverse effects of microplastics (MPs) and nanoplastics (NPs) on both freshwater and marine organisms. However, the information on MPs' and NPs' effects on shrimp species is scarce. In addition, the factors influencing the distribution of these particles in aquatic systems have been explained, yet the mechanisms behind MPs and NPs distribution and consumption, specifically to crustaceans and shrimp, have not been elucidated in detail. The effects of MPs and NPs as well as plastic-carried contaminants and pathogens on shrimp are critical to shrimp production and subsequent human consumption. Recent findings are required to review and discuss to open up new avenues for emerging Shrimp and crustacean research for sustainability. This review summarizes the distribution and fate of MPs and NPs along with contaminants and pathogens and identifies potential risks to shrimp health. The transport of MPs and NPs is influenced by their plastic properties, hydrodynamics, and water properties. Additionally, the fate of these particles on a plastic surface (plastisphere) is regulated by contaminant properties. Pathogens thriving on plastic surfaces and contaminants adsorbed can reach aquatic organisms directly with plastic particles or indirectly after release to an aquatic environment. MPs and NPs can be absorbed by shrimp through their gills and mouth and accumulate in their internal organs. Innate immunity influenced the degree of survival rate, tissue damage, alteration of gut microbiota, and increased oxidative stress caused by MPs and NPs accumulation. The studies on the effects of MPs and NPs are still not sufficient to understand how these particles are absorbed from various parts of the shrimp body and the fate of these plastics inside the body.

Urban street dust is regarded as a significant pollutant in the urban environment and an ideal indicator of urban environmental quality. Even so, studies regarding this matrix for microplastics (MPs) and nanoplastics (NPs) pollution are often overlooked and only a few studies have been conducted to date. MPs and NPs are ubiquitous in nature and of current concern to scientists, governmental and non-governmental organisation. A key issue in understanding the fate and potential effects of MPs and NPs is their dynamic nature, as the size, shape, and charge of the particles change overtime. Reviewed studies suggested that they are present in significant quantities in deposited street dust comprised mainly of PES (Polyester), PP (Polypropylene), PE (Polyethylene), TRWP (Tire and road wear particles) and the concentrations are influenced by anthropogenic activities. These studies therefore suggest dusts as a significant exposure route of human and ecosystem to MPs and NPs. The present review provided a comprehensive overview of current knowledge or information including analytical procedure regarding MPs and NPs in road deposited street dust, identifying gaps in knowledge, and giving suggestions for future research. The significance of this review is that, dusts particles can be easily ingested by humans through inhalation or contact and humans may simultaneously ingest MPs and NPs. Therefore, understanding the dynamics of their sources, pathways, and reservoirs is very important particularly for scientist studying the occurrence and fate of MPs and NPs in ecosystems as well as the general public.

Microplastics (MPs) and nanoplastics (NPs) have gained considerable attention as emerging contaminants that can pose potential risks to subsurface environments due to their widespread presence and persistence in the environment. They can act as carriers for other contaminants, such as heavy metals, by adsorbing onto their surfaces, potentially increasing their mobility and consequently causing toxicity to organisms and human health. MPs and NPs can enter groundwater through landfill leachate, agricultural mulches, and wastewater effluent. However, MPs’ and NPs’ behavior in porous media with complicated components has not been thoroughly examined. Therefore, further research is essential to identify the key factors such as aggregation (particles attaching to each other) and deposition (particles attaching to a transport medium), that may influence MPs' and NPs' behavior, fate, and transport mechanisms in soils and groundwater. The purpose of our research is to investigate how plastic particle properties, pore water chemistry, as well as characteristics of the medium would influence the aggregation and deposition of MPs and NPs. This study focuses on the attachment of low-density polyethylene micro- and nano-plastics (LDPE) released from macro-plastic pellets and synthesized polystyrene micro-spheres to quartz sand under controlled laboratory conditions. Batch experiments were performed to study the aggregation and deposition of LDPE and synthesized polystyrene micro-spheres onto quartz sand that allow for precise control over environmental variables, facilitating the observation of microplastic-sand interactions in varying background solutions. The influence of two common salts, sodium chloride (NaCl) and calcium chloride (CaCl2), on the attachment process is systematically investigated. The results from our experiments indicated that similar to polystyrene micro-spheres, the LDPE particles did not adsorb to quartz sand at pH 5 in 3 mM NaCl solution, while a substantial amount of LDPE adsorbed to quartz sand in 1 mM CaCl2 at pH 5. This could be attributed to the less negative zeta potential of LDPE (~-25 mV) and polystyrene micro-spheres (~-17 mV) in 1mM CaCl2 background solution as a result of lower electrostatic repulsion between particles. Results from these experiments provide insights into the complex mechanisms governing MPs' and NPs' behavior in aquatic environments, aiding in the development of strategies to mitigate their impact on ecosystems.

Microbiome: A forgotten target of environmental micro(nano)plastics?

Microplastics (MPs) and nanoplastics (NPs) are regarded as emerging particulate contaminants. Here, we first summarize the distribution of plastic particles in fish. Field investigations verify the presence of various kinds of fibrous, spherical, and fragmentary MPs in fish gastrointestinal tract and gills, and specifically in muscle and liver. Laboratory works demonstrate that NPs even penetrate into blood vessels of fish and pass onto next generations. Second, we systematically discuss the translocation ability of MPs and NPs in fish. MPs can enter early-developing fish through adherence, and enter adult fish internal organs by intestine absorption or epidermis infiltration. NPs can not only penetrate into fish embryo blastopores, but also reach adult fish internal organs through blood circulation. Third, the cellular basis for translocation of plastic particles, NPs in particular, into cells are critically reviewed. Endocytosis and paracellular penetration are two main pathways for them to enter cells and intercellular space, respectively. Finally, we compare the chemical and physical properties among various particular pollutants (MPs, NPs, settleable particulate matters, and manufactured nanomaterials) and their translocation processes at different biological levels. In future studies, it is urgent to break through the bottleneck techniques for NPs quantification in field environmental matrix and organisms, re-confirm the existence of MPs and NPs in field organisms, and develop more detailed translocating mechanisms of MPs and NPs by applying cutting-edge tracking techniques.