Soil Contamination and Human Health
Micronanoplastics
Microplastics are plastic particles with a diameter of less than 5 mm and more than 1 µm, that are brought to this size by microbial activities, photodegradation or mechanical forces. Nanoparticles are even smaller, with a diameter of less than 1 µm. The term Micronanoplastics considers both groups (Bartkova et al., 2017; Ullah et al., 2021).
Although Micronanoplastics have been extensively studied in aquatic systems, their presence and fate in agricultural systems are still insufficiently understood. They are persistent contaminants that are ubiquitous in the soil environment (Kumar et al., 2020). They are also of particular concern, as the use of plastic materials in agriculture is expected to further increase (Huang et al., 2020).
1.) the use of plastic materials in the production process, such as mulching films (Okeke et al., 2021; Bläsing & Amelung, 2018) greenhouse or tunnel materials, silage films, boxes, packaging materials, harvesting nests, plastic reservoirs, or irrigation tubes (Ng et al., 2018; Kim et al., 2020; Sarker et al., 2020; Isari et al., 2021);
2.) the application of contaminated substances, such as sewage sludge, biosolids, or organic fertilizers, irrigation with treated wastewater or contaminated freshwater (Bläsing & Amelung, 2018; Wang et al., 2021); and
3.) the application of substances intentionally containing plastics, such as polymer-based slow-release fertilizers or pesticides (Kumar et al., 2020).
Plastic mulching, mostly made by low-density polyethylene and polypropylene, has become a globally applied practice for plant protection from harsh climatological conditions. It is considered one of the major causes of micronanoplastic pollution in agricultural soils (Huang et al., 2020; Sarker et al., 2020). About 83,000 tons of mulch films were sold in Europe in 2019 (Campanale et al., 2021), with projections that the global market will grow until 2030 at a rate of 5.6% per year (Huang et al., 2020)
Though soils, particularly agricultural soils, have been recognized as a major sink of micronanoplastics, the impacts of micronanoplastics on soil ecosystems remain uncertain (Boots et al., 2019). Because of their minute size, it is difficult to separate and isolate them from soil samples, hampering identification and observation procedures. Hence, future studies should focus on finding standardized analytical methods to estimate micronanoplastics in soil samples as a basis for identifying and closing knowledge gaps about its effects in the soil environment (Allouzi et al., 2021).
Only limited evidence confirming the effects of micro- and nanoplastics on human health is available. However, the presence of micronanoplastics in agricultural soils leads to increased human uptake with food. This has been suggested to affect human health (oxidative stress, inflammation processes, genotoxicity, neurotoxicity, mitochondrial function) (Allouzi et al., 2021; Fournier et al., 2021).
Recent studies have found that micronanoplastics can be accumulated in the human intestines (Yu et al., 2022). This may cause gastrointestinal issues such as local inflammation and alter the community composition and diversity of intestinal microbes (Yu et al., 2022; Fackelmann & Sommer, 2019; Teles et al., 2020). Additionally, micronanoplastics further have the ability to pass through the intestinal barrier and enter the circulatory system, including the spleen and liver (Yu et al., 2022; Teles et al., 2020).
Most of the studies suggest that the main risk of micronanoplastics for human health arises from the release of additives which are known to be endocrine disruptors or carcinogenic (e.g., bisphenol A, phthalates) (Pathan et al., 2020), or from their ability to sequester co-pollutants from the environment (e.g., heavy metals, antibiotic-resistant bacteria), enhancing their transfer and uptake (Campanale et al., 2021; Campanale et al., 2020). Furthermore, owing to their tendency to adsorb other chemicals or soil constituents, plastic particles could cause bioaccumulation and bioamplification phenomena by adsorbing persistent organic pollutants, agrochemicals, heavy metals, antibiotics resistance genes, or pathogenic microorganisms. This significantly increases their potential environmental and health threat (Ullah et al., 2021; Wang et al., 2021; Da Costa et al., 2016).
Very few studies have investigated the effects of micronanoplastics on the growth of plants. Micronanoplastics can accumulate in the roots of plants and then be transported to their leaves, flowers, and fruits (Tian et al., 2021). Different micronanoplastics may trigger different responses in soils and plants (De Souza Machado et al., 2019) and overall, neither a generally positive or negative effect on plants can be postulated at present (De Souza Machado et al., 2019; Rillig et al., 2019). Observations suggest that micronanoplastics may be able to delay germination, affect both vegetative and reproductive growth of plants, and exert eco- and genotoxicity to plants (Xu et al., 2019). On the other hand, they can promote roots and plant growth and result in higher total biomass. Furthermore, they may enhance the colonization of roots by soil microbes (De Souza Machado et al., 2019).
Likewise, the effect of micronanoplastics on soil fauna under real-life conditions is still poorly understood (Xu et al., 2019). Fungi and bacteria can promote the degradation of plastics (Wang et al., 2019), though the persistent and pervasive nature of micronanoplastics in the soil environment has been confirmed (Kumar et al., 2020). Micronanoplastics can alter soil microbial community diversity, as well as the activity of soil microbiota and enzymes. They may hence disturb microbial ecosystems and affect soil nutrient cycles (Xu et al., 2019). However, these effects display great variability (Sajjad et al., 2022) and may depend on micronanplastic type, shape, size, concentration, and composition, as well as on soil characteristics such as texture (Xu et al., 2019; Sajjad et al., 2022). Negative effects exerted by micronanoplastics may also be related to concomitant pollutants found on them (Xu et al., 2019).
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Sarker, A.; Deepo, D.M.; Nandi, R.; Rana, J.; Islam, S.; Rahman, S.; Hossain, M.N.; Islam, S.; Baroi, A.; Kim, J.-E. A review of microplastics pollution in the soil and terrestrial ecosystems: A global and Bangladesh perspective. Sci. Total Environ. 2020, 733, 139296.
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Ullah, R.; Tsui, M.T.; Chen, H.; Chow, A.; Williams, C.; Ligaba-Osena, A. Microplastics interaction with terrestrial plants and their impacts on agriculture. J. Environ. Qual. 2021, 50, 1024–1041.
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Xu, B.; Liu, F.; Cryder, Z.; Huang, D.; Lu, Z.; He, Y.; Wang, H.; Lu, Z.; Brookes, P.C.; Tang, C.; et al. Microplastics in the soil environment: Occurrence, risks, interactions and fate–A review. Crit. Rev. Environ. Sci. Technol. 2019, 50, 2175–2222.
Yu, H.; Zhang, Y.; Tan, W.; Zhang, Z. Microplastics as an Emerging Environmental Pollutant in Agricultural Soils: Effects on Ecosystems and Human Health. Front. Environ. Sci. 2022, 10, 855292.
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The research project below deals with effects of microplastic in the rhizosphere of crop plants: