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      Assessment of pollution and risks associated with microplastics in the riverine sediments of the Western Ghats: a heritage site in southern India

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          Abstract

          There is very little knowledge on microplastic pollution in the Western Ghats (WG), a heritage site in southwest India. To address this, we have studied the spatiotemporal variations of sedimentary microplastics (MPs) from the River Sharavathi, a pristine river in the Western Ghats (WG), southern India. The rich biodiversity in the region makes it relevant to analyse the distribution of this emerging pollutant that is causing harm to the biota and the ecosystem. We analysed the sedimentological and carbon content (organic and inorganic) of these sediments and explored their relationship with MPs. Finally, risk assessment indices such as the Pollution Load Index (PLI), the Polymer Hazard Index (PHI), and the Potential Ecological Risk Index (PERI) were calculated to detect the levels of plastic pollution. The concentration of MPs ranged from 2.5 to 57.5 pieces/kg and 0 to 15 pieces/kg during the pre-monsoon and post-monsoon seasons, respectively. The dip in the MPs’ abundance during the post-monsoon season was due to the extremely high rainfall in the river basin during July–August 2019, which would have entrained the sedimentary MPs and transported them to the coast/Arabian Sea. Smaller MPs (0.3–1 mm) were more abundant than the larger MPs (1–5 mm), mainly due to the breakdown of sedimentary plastics by physical processes. Fragments, films, foams, and fibres were the main categories of MPs, and the main polymers were polyethylene, polyethylene terephthalate, and polypropylene. No significant relationship was observed between the sedimentological properties and microplastics, which may be due to the different physical properties of sediments and microplastics. The PLI, PHI, and PERI indices suggest different contamination levels in the river basin. Based on the PLI scores, all the samples belong to the hazardous level I suggesting minor risk category, and the risk of microplastic pollution falls under the high to hazardous risk category based on the PHI values. The PERI value ranged from 160 to 440 and 40 to 2240 during the pre-monsoon and post-monsoon seasons, respectively. The risk assessment in a region known for its rich biodiversity is crucial, as the data can be used by the district administration to mitigate plastic pollution.

          Supplementary Information

          The online version contains supplementary material available at 10.1007/s11356-022-24437-z.

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          Microplastics in the marine environment.

          This review discusses the mechanisms of generation and potential impacts of microplastics in the ocean environment. Weathering degradation of plastics on the beaches results in their surface embrittlement and microcracking, yielding microparticles that are carried into water by wind or wave action. Unlike inorganic fines present in sea water, microplastics concentrate persistent organic pollutants (POPs) by partition. The relevant distribution coefficients for common POPs are several orders of magnitude in favour of the plastic medium. Consequently, the microparticles laden with high levels of POPs can be ingested by marine biota. Bioavailability and the efficiency of transfer of the ingested POPs across trophic levels are not known and the potential damage posed by these to the marine ecosystem has yet to be quantified and modelled. Given the increasing levels of plastic pollution of the oceans it is important to better understand the impact of microplastics in the ocean food web. Copyright © 2011 Elsevier Ltd. All rights reserved.
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            Lost at sea: where is all the plastic?

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              Microplastics in the marine environment: a review of the methods used for identification and quantification.

              This review of 68 studies compares the methodologies used for the identification and quantification of microplastics from the marine environment. Three main sampling strategies were identified: selective, volume-reduced, and bulk sampling. Most sediment samples came from sandy beaches at the high tide line, and most seawater samples were taken at the sea surface using neuston nets. Four steps were distinguished during sample processing: density separation, filtration, sieving, and visual sorting of microplastics. Visual sorting was one of the most commonly used methods for the identification of microplastics (using type, shape, degradation stage, and color as criteria). Chemical and physical characteristics (e.g., specific density) were also used. The most reliable method to identify the chemical composition of microplastics is by infrared spectroscopy. Most studies reported that plastic fragments were polyethylene and polypropylene polymers. Units commonly used for abundance estimates are "items per m(2)" for sediment and sea surface studies and "items per m(3)" for water column studies. Mesh size of sieves and filters used during sampling or sample processing influence abundance estimates. Most studies reported two main size ranges of microplastics: (i) 500 μm-5 mm, which are retained by a 500 μm sieve/net, and (ii) 1-500 μm, or fractions thereof that are retained on filters. We recommend that future programs of monitoring continue to distinguish these size fractions, but we suggest standardized sampling procedures which allow the spatiotemporal comparison of microplastic abundance across marine environments.
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                Author and article information

                Contributors
                anish.warrier@manipal.edu , akwarrier@gmail.com
                Journal
                Environ Sci Pollut Res Int
                Environ Sci Pollut Res Int
                Environmental Science and Pollution Research International
                Springer Berlin Heidelberg (Berlin/Heidelberg )
                0944-1344
                1614-7499
                3 December 2022
                3 December 2022
                2023
                : 30
                : 12
                : 32301-32319
                Affiliations
                [1 ]GRID grid.411639.8, ISNI 0000 0001 0571 5193, Department of Civil Engineering, , Manipal Institute of Technology, Manipal Academy of Higher Education, ; Manipal, 576104 Karnataka India
                [2 ]GRID grid.411639.8, ISNI 0000 0001 0571 5193, Centre for Climate Studies, , Manipal Academy of Higher Education, ; Manipal, 576104 Karnataka India
                [3 ]GRID grid.412206.3, ISNI 0000 0001 0032 8661, Nitte (Deemed to Be University), Department of Public Health Dentistry, , AB Shetty Memorial Institute of Dental Sciences (ABSMIDS), ; Mangalore, 574199 Karnataka India
                [4 ]National Centre for Coastal Research, NIOT Campus, Velacherry-Tambaram Main Road, Pallikaranai, Chennai - 600100 India
                [5 ]GRID grid.464957.d, National Centre for Polar and Ocean Research, ; Headland Sada, Vasco-da-Gama, 403804 Goa India
                Author notes

                Responsible Editor: Christian Gagnon

                Author information
                http://orcid.org/0000-0003-0044-6224
                Article
                24437
                10.1007/s11356-022-24437-z
                10017654
                36462078
                10d41dca-63ff-4136-ae79-b1d82aad7df6
                © The Author(s) 2022

                Open AccessThis article is licensed under a Creative Commons Attribution 4.0 International License, which permits use, sharing, adaptation, distribution and reproduction in any medium or format, as long as you give appropriate credit to the original author(s) and the source, provide a link to the Creative Commons licence, and indicate if changes were made. The images or other third party material in this article are included in the article's Creative Commons licence, unless indicated otherwise in a credit line to the material. If material is not included in the article's Creative Commons licence and your intended use is not permitted by statutory regulation or exceeds the permitted use, you will need to obtain permission directly from the copyright holder. To view a copy of this licence, visit http://creativecommons.org/licenses/by/4.0/.

                History
                : 18 February 2022
                : 23 November 2022
                Funding
                Funded by: FundRef http://dx.doi.org/10.13039/100012653, Karnataka State Council for Science and Technology, Indian Institute of Science;
                Award ID: KSTePS/VGST-RGS/F/GRD No. 697/2017-18 dated 27-08-2018
                Award Recipient :
                Funded by: Department of Science and Technology
                Award ID: DST/INSPIRE Fellowship/2018/IF180508 dated 25-09-2019
                Award Recipient :
                Funded by: FundRef http://dx.doi.org/10.13039/501100001410, Human Resource Development Group;
                Award ID: 09/1165(0009)/2019-EMR-l dated 11/11/2019
                Award Recipient :
                Funded by: Manipal Academy of Higher Education, Manipal
                Categories
                Research Article
                Custom metadata
                © Springer-Verlag GmbH Germany, part of Springer Nature 2023

                General environmental science
                microplastic pollution,rainfall,pristine river,heritage sites,western ghats,southern india

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