Table 1.
Sources of microplastics and nanoplastics into the environment.
MNPs’ source | Properties | Entry point into the environment | Application | References |
---|---|---|---|---|
Plastic pellets | Granular plastics, commonly with a diameter of 2–5 mm and a regular shape | Drifting/surface runoff/loss | Raw materials and building blocks for nearly every plastic product. | Karkanorachaki et al. (2018); Mendoza et al. (2018) |
Microbead personal care products | Microbeads varying in color and ~ 100–1,000 μm | Wastewater/sewage sludge | Exfoliating, film-forming, hydrophilic, scrubbing agents and functionalized polymers in personal care products as well as in biomedical applications. | Napper et al. (2015); Nel et al. (2019) |
Paint | Between 0.3 and 5 mm from synthetic polymers mainly alkyds, epoxy resins, poly(acrylate/styrene) and polyurethane | Surface runoff | Architectural coatings, marine coatings, automotive coatings, and road-marking paint. | An et al. (2020); Gaylarde et al. (2021) |
Textile fabric | 100–1,000 μm MNPs mainly from acrylic, polyethylene terephthalate, and nylon fabrics | Wastewater/sewage sludge | Enhanced appeal and functionality in synthetic fabrics. | Carney Almroth et al. (2018); Cai et al. (2020b) |
Sewage treatment effluents | Different kinds of MNPs from automobile tire wear, industrial production of plastic, personal care products, chemical laundry products, urban debris, etc. Ranging from 0.1 μm to 5 mm | N/A | N/A | Domogalla-Urbansky et al. (2019); Mak et al. (2020) |
Sports ground (artificial turfs and running tracks) | MNPs from propylene, polyamide 6 (PA6), PE, or polyurethane, styrene-butadiene rubber, thermoplastic elastomer, and green rubber and ethylene propylene diene monomer which is made of EPDM. Usually between 0.5–2.5 mm | Drifting/surface runoff | N/A | Wang et al. (2019); van Kleunen et al. (2020) |
Vehicle tire wear | Roundish, kidney-shaped or elongated particles from styrene butadiene rubber and natural rubber particles 0.01–350 μm | Surface runoff | N/A | Sommer et al. (2018); Järlskog et al. (2020) |
Municipal debris | Fragments of plastic bags, plastic bottles and other packaging materials. Of varying particle sizes from 0.1 μm to 5 mm | Drifting/surface runoff | N/A | Welle and Franz (2018); Sobhani et al. (2020) |
Fishing gears | Polyethylene, polyamide (nylon), and polypropylene monofilaments of between 0.1 and 5 mm | Drifting/loss | N/A | Dowarah and Devipriya (2019); Xue et al. (2020) |
Farming films | Microfilms more commonly from polyethylene between 0.03 and 10 mm | Drifting/surface runoff | N/A | Liu et al. (2018); Zhang and Liu (2018) |
Construction industry | Fragments of typically polyamide, polyethylene, polyvinylchloride and polyurethane polymers | Drifting/surface runoff | N/A | Dehghani et al. (2017); Xu et al. (2020) |
N/A—Not applicable.