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dc.contributor.authorRezaei, M
dc.contributor.authorAbbasi, S
dc.contributor.authorPourmahmood, H
dc.contributor.authorOleszczuk, P
dc.contributor.authorRitsema, C
dc.contributor.authorTurner, A
dc.date.accessioned2022-05-04T16:00:28Z
dc.date.issued2022-09
dc.identifier.issn0013-9351
dc.identifier.issn1096-0953
dc.identifier.other113213
dc.identifier.urihttp://hdl.handle.net/10026.1/19187
dc.description.abstract

Despite the importance of agricultural soils, little is known about the fate of microplastics (MPs) in this environment. In the present study, MPs have been determined in soils and wind-eroded sediments from two vegetable-growing fields in the Fars province of Iran, one using plastic mulch for water retention (Field 1) and the other using wastewater for irrigation (Field 2). MPs were heterogeneously distributed in the surface (0-5 cm) and subsurface (5-15 cm) soils of both fields, with a maximum concentration overall of about 1.1 MP g-1 and no significant differences in concentrations between either fields or depths. Fibres represented the principal shape of MPs, but spherules, presumably from wastewater, also made a significant (∼25%) contribution to MPs in Field 2. Analysis of selected samples by Raman spectroscopy and scanning electron microscopy revealed that polyethylene terephthalate (PET) and nylon were the most abundant polymers and that MPs exhibited varying degrees of weathering. Concentrations of MPs in this study are within the range reported previously for agricultural soils, although the absence of PET observed in earlier studies is attributed to the use of insufficiently dense solutions to isolate plastics. Deployment of a portable wind tunnel revealed threshold wind velocities for soil erosion of up to 7 and 12 m s-1 and MP erosion rates up to about 0.4 and 1.1 MP m-2 s-1 for Fields 1 and 2, respectively. Erosion rates are considerably greater than published depositional rates for MPs and suggest that agricultural soils act as both a temporary sink and dynamic secondary source of MPs that should be considered in risk assessments and global transport budgets.

dc.format.extent113213-113213
dc.format.mediumPrint-Electronic
dc.languageen
dc.language.isoeng
dc.publisherElsevier
dc.subjectMicroplastics
dc.subjectAgriculture
dc.subjectSoils
dc.subjectWind
dc.subjectErosion
dc.subjectTransport
dc.subjectFlux
dc.titleMicroplastics in agricultural soils from a semi-arid region and their transport by wind erosion
dc.typejournal-article
dc.typeArticle
plymouth.author-urlhttps://www.ncbi.nlm.nih.gov/pubmed/35398314
plymouth.issueB
plymouth.volume212
plymouth.publisher-urlhttp://dx.doi.org/10.1016/j.envres.2022.113213
plymouth.publication-statusPublished
plymouth.journalEnvironmental Research
dc.identifier.doi10.1016/j.envres.2022.113213
plymouth.organisational-group/Plymouth
plymouth.organisational-group/Plymouth/Faculty of Science and Engineering
plymouth.organisational-group/Plymouth/Faculty of Science and Engineering/School of Geography, Earth and Environmental Sciences
plymouth.organisational-group/Plymouth/REF 2021 Researchers by UoA
plymouth.organisational-group/Plymouth/REF 2021 Researchers by UoA/UoA07 Earth Systems and Environmental Sciences
plymouth.organisational-group/Plymouth/Research Groups
plymouth.organisational-group/Plymouth/Research Groups/BEACh
plymouth.organisational-group/Plymouth/Research Groups/Marine Institute
plymouth.organisational-group/Plymouth/Users by role
plymouth.organisational-group/Plymouth/Users by role/Academics
dc.publisher.placeNetherlands
dcterms.dateAccepted2022-03-25
dc.rights.embargodate2023-4-18
dc.identifier.eissn1096-0953
rioxxterms.versionofrecord10.1016/j.envres.2022.113213
rioxxterms.licenseref.urihttp://www.rioxx.net/licenses/all-rights-reserved
rioxxterms.licenseref.startdate2022-04-07
rioxxterms.typeJournal Article/Review


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