Plastics (Macro-, Micro- and Nano-) as Vectors for Other Environmental Contaminants

A special issue of Toxics (ISSN 2305-6304). This special issue belongs to the section "Ecotoxicology".

Deadline for manuscript submissions: closed (31 August 2021) | Viewed by 3336

Special Issue Editors


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Guest Editor
Department of Biology & CESAM, University of Aveiro, 3810-193 Aveiro, Portugal
Interests: toxicity of anthropogenic contaminants; contaminant interactions; environmental risk assessment; molecular-to-ecological endpoints; remediation solutions; science societal impact
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Special Issue Information

Dear Colleagues,

The industrial production of plastics has exponentially increased since the 1940s due to their exceptional properties, such as their low density and high durability. However, these properties result in the elevated persistency of plastics in the environment. Micro- and nanoplastics are environmental contaminants that have received significant attention from the scientific community in the last few years. They originate from both intentional production and the breakdown of larger plastic items. Several studies demonstrated the persistent environmental contamination by microplastics, including major compartments, e.g., soil, sea, and freshwater. On the other hand, studies are increasingly reporting on the potential of both micro- and nanoplastics to interact with other contaminants and their negative impact on different organisms. However, until now, there is little and controversial information about this research topic.

Therefore, this Special Issue invites the submission of and intends to incorporate original research, case studies, or up-to-date review papers containing information about the role of plastics as vectors for other contaminants. In particular, it will welcome studies focused on specific issues:

- Evaluation of the ecotoxicity of different mixtures of plastics with other contaminants at the individual (e.g. survival, reproduction, and behavior), biochemical (e.g., DNA damage, oxidative stress and neurotransmission) and molecular (e.g., gene and protein expressions) levels;

- Ecotoxicity of these mixtures resultant from long-term exposures with special attention to multigenerational and/or transgenerational effects;

- Advances in the characterization and understanding of the biological interactions of these complexes mixtures and, therefore, biological effects;

- Abiotic characterization of these mixtures in the media of exposure (e.g., spiked soil/water) or in distinct environmental compartments;

 - Analytical methods to assess the potential binding/adsorption between plastics and the other contaminants in complex environmental contexts.

Dr. Vera Lúcia Maria
Dr. Ângela Barreto
Guest Editors

Manuscript Submission Information

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Keywords

  • plastic types
  • carriers
  • pollutants
  • aquatic and terrestrial ecosystems
  • biological effects
  • mode-of-action
  • ecological impact
  • chemical interactions
  • analytical methods

Published Papers (1 paper)

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Research

15 pages, 2377 KiB  
Article
Polystyrene Nanoplastics Can Alter the Toxicological Effects of Simvastatin on Danio rerio
by Angela Barreto, Joana Santos, Mónica J.B. Amorim and Vera L. Maria
Toxics 2021, 9(3), 44; https://0-doi-org.brum.beds.ac.uk/10.3390/toxics9030044 - 26 Feb 2021
Cited by 9 | Viewed by 2472
Abstract
Once in the environment, nanoplastics (NPls) may interact with other contaminants, such as pharmaceuticals, potentially acting as carriers and modulating their toxicity. Thus, the main aim of the current study is to investigate how polystyrene (PS) NPls (mean diameter: 60 nm) interact with [...] Read more.
Once in the environment, nanoplastics (NPls) may interact with other contaminants, such as pharmaceuticals, potentially acting as carriers and modulating their toxicity. Thus, the main aim of the current study is to investigate how polystyrene (PS) NPls (mean diameter: 60 nm) interact with simvastatin (SIM), an anticholesterolemic drug, and modulate its toxicity to zebrafish (Danio rerio) embryos. PS NPls were carboxyl group functionalized, to promote the interaction/binding of NPls with SIM (worst-case scenarios) and it was fluorescently dyed, allowing to detect the intake. Exposure was 96 h to 0–150 mg/L NPls or 0–150 µg/L SIM, as well as to dual combinations (NPls 0.015 or 1.5 mg/L and SIM 12.5 or 15 µg/L). PS NPls alone did not exert effects whereas SIM (≥ 12.5 µg/L) significantly delayed the hatching, decreased the heartbeat, induced edemas and mortality. The combination of NPls (1.5 mg/L) and SIM (12.5 or 15 µg/L) had significant effects on the survival of the organisms while the correspondent NPls and SIM single exposures did not have significant effects on this endpoint. Concerning the malformations appearance, SIM alone had similar effects than when in co-exposures (0.015 mg/L NPls plus 12.5 or 15 µg/L SIM). Hatching and heartbeat increased after the co-exposures SIM and NPls comparing with SIM single exposures, showing that 0.015 mg/L NPls plus 12.5 or 15 µg/L SIM did not cause significant effects on these endpoints. This study shows that NPls effects on bioavailability and toxicity of other contaminants cannot be ignored when assessing the environmental behavior and risks of NPls. Full article
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