Lukaszewicz Germán, Iturburu Fernando G, Garanzini Daniela S, Menone Mirta L, Pflugmacher Stephan
Laboratorio de Ecotoxicología, Instituto de Investigaciones Marinas y Costeras (IIMYC), Consejo Nacional de Investigaciones Científicas y Técnicas (CONICET), Universidad Nacional de Mar del Plata, Funes 3350, 7600 Mar del Plata, Buenos Aires, Argentina.
University of Helsinki, Faculty of Biological and Environmental Sciences, Ecosystems and Environment Research Programme, Aquatic Ecotoxicology in an Urban Environment, Niemenkatu 73, 15140 Lahti, Finland.
Heliyon. 2019 Jul 24;5(7):e02118. doi: 10.1016/j.heliyon.2019.e02118. eCollection 2019 Jul.
Imidacloprid (IMI) is a neonicotinoid insecticide widely used in agricultural activities all around the world. This compound is transported from croplands to surrounding freshwater ecosystems, producing adverse effects on non-target organisms. Because of the relevance of aquatic macrophytes in the above-mentioned environments and the lack of studies of potential effects of IMI on them, this work aimed to assess the mitotic process and potential genotoxicity in the aquatic macrophyte L. Although the analysis of the Mitotic Index (MI) showed that IMI was not cytotoxic, the Cell Proliferation Kinetics (CPK) frequencies evidenced modifications in the kinetics of the mitotic process. Indeed, the anaphases ratio decreased at 10 and 100 μg/L IMI, while at 1000 μg/L an increase of prophases ratio and a decrease of metaphases ratio were observed. Regarding genotoxicity, IMI produced an increase of the abnormal metaphases frequency from 10 μg/L to 1000 μg/L as well as an increase in clastogenic anaphases-telophases frequency at 100 and 1000 μg/L. In addition, aneugenic anaphases-telophases and C-mitosis frequencies also increased at 1000 μg/L, confirming the effects on the mitotic spindle. Considering the genotoxic effects on through two different mechanisms (aneugenic and clastogenic) and the wide spread use of IMI in agriculture, these mechanisms of toxicity on macrophytes should be considered among other recognized effects of this insecticide on aquatic biota.
吡虫啉(IMI)是一种新烟碱类杀虫剂,在世界各地的农业活动中广泛使用。这种化合物从农田输送到周围的淡水生态系统,对非目标生物产生不利影响。由于水生大型植物在上述环境中的重要性以及缺乏关于IMI对其潜在影响的研究,这项工作旨在评估水生大型植物L中的有丝分裂过程和潜在的遗传毒性。虽然有丝分裂指数(MI)分析表明IMI没有细胞毒性,但细胞增殖动力学(CPK)频率证明有丝分裂过程的动力学发生了改变。确实,在10和100μg/L的IMI浓度下后期比例下降,而在1000μg/L时观察到前期比例增加和中期比例下降。关于遗传毒性,IMI使异常中期频率从10μg/L增加到1000μg/L,并且在100和1000μg/L时致断裂后期 - 末期频率增加。此外,在1000μg/L时非整倍体后期 - 末期和C - 有丝分裂频率也增加,证实了对有丝分裂纺锤体的影响。考虑到通过两种不同机制(非整倍体和致断裂)对L产生的遗传毒性作用以及IMI在农业中的广泛使用,这种杀虫剂对大型植物的这些毒性机制应与该杀虫剂对水生生物群的其他公认影响一并考虑。