Gomes Alex Rodrigues, Freitas Ítalo Nascimento, Luz Thiarlen Marinho da, Guimarães Abraão Tiago Batista, Araújo Amanda Pereira da Costa, Kamaraj Chinnaperumal, Rahman Md Mostafizur, Islam Abu Reza Md Towfiqul, Arias Andrés Hugo, Silva Fábia Barbosa da, Karthi Sengodan, Cruz-Santiago Omar, Silva Fabiano Guimarães, Malafaia Guilherme
Laboratory of Toxicology Applied to the Environment, Goiano Federal Institute, Urutaí, GO, Brazil; Post-Graduation Program in Agronomy, Goiano Federal Institute, Rio Verde, GO, Brazil.
Laboratory of Toxicology Applied to the Environment, Goiano Federal Institute, Urutaí, GO, Brazil; Post-Graduation Program in Ecology, Conservation, and Biodiversity, Federal University of Uberlândia, Uberlândia, MG, Brazil.
J Hazard Mater. 2023 May 15;450:131069. doi: 10.1016/j.jhazmat.2023.131069. Epub 2023 Feb 24.
More recently, the number of studies on the impacts of microplastics (MPs) on plants has drawn attention considerably. However, many of these studies focused on terrestrial plants, with vascular plants from freshwater ecosystems being little studied. Thus, we aimed to evaluate the possible effects of exposure of Salvinia auriculata, for 28 days, to different concentrations of polyethylene MPs (PE MPs - diameter: 35.46 ± 18.17 µm) (2.7 ×10 and 8.1 ×10 particles/m), using different biomarkers. Our data indicated that exposure to PE MPs caused alterations in plant growth/development (inferred by the lower floating frond number, "root" length, and the number of "roots"), as well as lower dispersion of individuals in the experimental units. Plants exposed to PE MPs also showed lower epidermal thickness (abaxial leaf face) and a longer length of the central leaf vein and vascular bundle area. Ultrastructural analyses of S. auriculata exposed to MPs revealed rupture of some epidermal cells and trichomes on the adaxial and abaxial, leaf necrosis, and chlorosis. In the "roots", we observed dehydrated filamentous structures with evident deformations in plants exposed to the pollutants. Both on the abaxial leaf face and on the "roots", the adherence of PE MPs was observed. Furthermore, exposure to PE MPs induced lower chlorophyll content, cell membrane damage, and redox imbalance, marked by reduced catalase and superoxide dismutase activity and increased production of reactive oxygen and nitrogen species as well as malondialdehyde. However, in general, we did not observe the dose-response effect for the evaluated biomarkers. The values of the integrated biomarker response index, the principal component analysis (PCA) results and the hierarchical clustering analysis confirmed the similarity between the responses of plants exposed to different PE MPs concentrations. Therefore, our study sheds light on how PE MPs can affect S. auriculata and reinforces that putting these pollutants in freshwater environments might be hazardous from an ecotoxicological point of view.
最近,关于微塑料(MPs)对植物影响的研究数量大幅增加,引起了广泛关注。然而,这些研究大多集中在陆生植物上,对淡水生态系统中的维管植物研究较少。因此,我们旨在评估耳叶满江红暴露于不同浓度的聚乙烯微塑料(PE MPs - 直径:35.46 ± 18.17 µm)(2.7×10⁴和8.1×10⁴颗粒/m³)28天的可能影响,使用不同的生物标志物。我们的数据表明,暴露于PE MPs会导致植物生长/发育的改变(通过较低的漂浮叶状体数量、“根”长度和“根”数量推断),以及实验单元中个体的分散程度降低。暴露于PE MPs的植物还表现出较低的表皮厚度(叶背面)、较长的中央叶脉长度和维管束面积。对暴露于MPs的耳叶满江红进行超微结构分析,发现一些表皮细胞破裂,叶片正面和背面的毛状体、叶坏死和黄化。在“根”中,我们观察到暴露于污染物的植物中丝状结构脱水并明显变形。在叶背面和“根”上,均观察到PE MPs的附着。此外,暴露于PE MPs会导致叶绿素含量降低、细胞膜损伤和氧化还原失衡,表现为过氧化氢酶和超氧化物歧化酶活性降低,活性氧和氮物种以及丙二醛的产生增加。然而,总体而言,我们未观察到所评估生物标志物的剂量反应效应。综合生物标志物反应指数的值、主成分分析(PCA)结果和层次聚类分析证实了暴露于不同PE MPs浓度的植物反应之间的相似性。因此,我们的研究揭示了PE MPs如何影响耳叶满江红,并强调从生态毒理学角度来看,将这些污染物置于淡水环境中可能具有危险性。