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      Effects of Co-Contamination of Microplastics and Cd on Plant Growth and Cd Accumulation

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          Abstract

          Microplastics (MPs) occur widely in terrestrial ecosystems. However, information on the interaction of MPs with metals in terrestrial ecosystems is lacking in the literature. The present study investigated the effects of two types of MPs (high-density polyethylene (HDPE) and polystyrene (PS)) with different dosages (i.e., 0, 0.1%, 1%, and 10%) on the uptake and effects of Cd in maize plants grown in an agricultural soil. Results showed that addition of Cd at a 5 mg/kg caused inhibited plant growth and resulted in high Cd accumulation in plant tissues. Polyethylene alone showed no significant phytotoxic effects, but a high-dose of HDPE (10%) amplified Cd phytotoxicity. Polystyrene negatively affected maize growth and phytoxicity further increased in the presence of Cd. Both HDPE and PS caused soil diethylenetriaminepentaacetic acid (DTPA)-extractable Cd concentrations to increase but did not significantly affect Cd uptake into plant tissues. In the soil without Cd addition, HDPE decreased soil pH, while PS did not significantly alter soil pH. However, in the soil spiked with Cd, both HDPE and PS increased pH. Overall, impacts on plant growth and Cd accumulation varied with MP type and dose, and PS induced substantial phytotoxicity. In conclusion, co-occurring MPs can change Cd bioavailability, plant performance, and soil traits. Our findings highlight the ecological impacts that could occur from the release of MPs into soil.

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          Most cited references46

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          Development of a DTPA Soil Test for Zinc, Iron, Manganese, and Copper1

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            Microplastics as an emerging threat to terrestrial ecosystems

            Microplastics (plastics < 5 mm, including nanoplastics which are < 0.1 μm) originate from the fragmentation of large plastic litter or from direct environmental emission. Their potential impacts in terrestrial ecosystems remain largely unexplored despite numerous reported effects on marine organisms. Most plastics arriving in the oceans were produced, used, and often disposed on land. Hence, it is within terrestrial systems that microplastics might first interact with biota eliciting ecologically relevant impacts. This article introduces the pervasive microplastic contamination as a potential agent of global change in terrestrial systems, highlights the physical and chemical nature of the respective observed effects, and discusses the broad toxicity of nanoplastics derived from plastic breakdown. Making relevant links to the fate of microplastics in aquatic continental systems, we here present new insights into the mechanisms of impacts on terrestrial geochemistry, the biophysical environment, and ecotoxicology. Broad changes in continental environments are possible even in particle-rich habitats such as soils. Furthermore, there is a growing body of evidence indicating that microplastics interact with terrestrial organisms that mediate essential ecosystem services and functions, such as soil dwelling invertebrates, terrestrial fungi, and plant-pollinators. Therefore, research is needed to clarify the terrestrial fate and effects of microplastics. We suggest that due to the widespread presence, environmental persistence, and various interactions with continental biota, microplastic pollution might represent an emerging global change threat to terrestrial ecosystems.
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              Microplastics can change soil properties and affect plant performance

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                Author and article information

                Journal
                Toxics
                Toxics
                toxics
                Toxics
                MDPI
                2305-6304
                20 May 2020
                June 2020
                : 8
                : 2
                : 36
                Affiliations
                [1 ]College of Environment and Safety Engineering, Qingdao University of Science and Technology, Qingdao 266042, China; wangfayuan@ 123456qust.edu.cn (F.W.); zhxqing2020@ 123456163.com (X.Z.); zsq9629@ 123456163.com (S.Z.); zhangshuwu@ 123456126.com (S.Z.)
                [2 ]Shandong Key Laboratory of Water Pollution Control and Resource Reuse, School of Environmental Science and Engineering, Shandong University, Qingdao 266237, China
                [3 ]Department of Plant and Microbial Biology, University of California Berkeley, Berkeley, CA 94704, USA; catadams@ 123456berkeley.edu
                Author notes
                [* ]Correspondence: yhsun@ 123456qust.edu.cn ; Tel.: +86-532-8402-2617
                Author information
                https://orcid.org/0000-0003-1345-256X
                Article
                toxics-08-00036
                10.3390/toxics8020036
                7356726
                32443862
                43ce11d6-267b-476e-ba0a-db5b9d9f4ad4
                © 2020 by the authors.

                Licensee MDPI, Basel, Switzerland. This article is an open access article distributed under the terms and conditions of the Creative Commons Attribution (CC BY) license ( http://creativecommons.org/licenses/by/4.0/).

                History
                : 12 March 2020
                : 20 May 2020
                Categories
                Article

                heavy metals,soil contamination,environmental risk,cadmium,phytoavailability

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