State Environmental Protection Key Laboratory of Wetland Ecology and Vegetation Restoration, School of Environment, Northeast Normal University, Changchun, Jilin, 130117, PR China; Center for Environmental and Human Toxicology, Department of Physiological Sciences, College of Veterinary Medicine, UF Genetics Institute, Interdisciplinary Program in Biomedical Sciences Neuroscience, University of Florida, Gainesville, FL, 32611, USA.
State Environmental Protection Key Laboratory of Wetland Ecology and Vegetation Restoration, School of Environment, Northeast Normal University, Changchun, Jilin, 130117, PR China.
Chemosphere. 2018 Nov;210:633-644. doi: 10.1016/j.chemosphere.2018.07.056. Epub 2018 Jul 12.
Fluazinam is a pyridinamine fungicide that induces oxidative stress and mitochondrial damage in cells, and it has been reported to be neurotoxic. To characterize the biological effects of fluazinam, we assessed mitochondrial bioenergetics, dopamine system expression, and behavior of early life staged zebrafish (0.01 μM-0.5 μM). Fluazinam at environmentally-relevant levels did not induce sub-lethal effects in larvae, but at the LC (0.5 μM), fluazinam decreased basal and ATP-linked respiration significantly in embryos. As mitochondria are directly related to redox homeostasis and apoptosis, the expression of genes related to oxidative stress and apoptosis were measured. Superoxide dismutase 2 (sod2), heat stock protein 70 (hsp70), bcl2-associated X protein (bax), and caspase 9 (casp9) mRNA levels were up-regulated by 0.5 μM fluazinam. Taken together, there was evidence for mitochondrial dysfunction and oxidative damage at the highest concentration of fluazinam (0.5 μM) tested. As there are reports for fluazinam-induced neurotoxicity in dopamine synthesizing cells, transcriptional targets in the dopamine system were assessed in the zebrafish. Tyrosine hydroxylase 1 (th1) and dopamine receptor 2a (drd2a) mRNA levels were decreased by 0.5 μM fluazinam, suggesting that this fungicide may affect the dopaminergic system. To further assess the potential for fluazinam-mediated neuromodulation, the dark photokinesis response was assessed in larvae following exposure. Larvae exposed to 0.1 μM fluazinam showed hyperactivity, while larvae exposed to 0.2 and 0.3 μM showed hypo-activity. This study demonstrates that fluazinam disrupts mitochondrial bioenergetics in zebrafish, inducing an oxidative stress response, and aberrant behaviors in larvae that are dose dependent.
氟唑菌酰胺是一种吡啶胺类杀菌剂,它会导致细胞内氧化应激和线粒体损伤,并且已被报道具有神经毒性。为了研究氟唑菌酰胺的生物学效应,我们评估了早期发育阶段斑马鱼的线粒体生物能量、多巴胺系统表达和行为(0.01μM-0.5μM)。在环境相关浓度下,氟唑菌酰胺对幼虫没有产生亚致死效应,但在 LC(0.5μM)时,氟唑菌酰胺显著降低了胚胎的基础呼吸和 ATP 连接呼吸。由于线粒体与氧化还原稳态和细胞凋亡直接相关,因此测量了与氧化应激和细胞凋亡相关的基因的表达。超氧化物歧化酶 2(sod2)、热休克蛋白 70(hsp70)、Bcl-2 相关 X 蛋白(bax)和半胱天冬酶 9(casp9)mRNA 水平在 0.5μM 氟唑菌酰胺的作用下上调。总的来说,在测试的最高氟唑菌酰胺浓度(0.5μM)下,有证据表明线粒体功能障碍和氧化损伤。由于有氟唑菌酰胺诱导多巴胺合成细胞神经毒性的报道,因此评估了斑马鱼中多巴胺系统的转录靶标。0.5μM 氟唑菌酰胺降低了酪氨酸羟化酶 1(th1)和多巴胺受体 2a(drd2a)的 mRNA 水平,表明这种杀菌剂可能影响多巴胺能系统。为了进一步评估氟唑菌酰胺介导的神经调节的潜力,在暴露后评估了幼虫的暗感光运动反应。暴露于 0.1μM 氟唑菌酰胺的幼虫表现出过度活跃,而暴露于 0.2 和 0.3μM 的幼虫表现出活动减少。本研究表明,氟唑菌酰胺会破坏斑马鱼的线粒体生物能量,诱导氧化应激反应,并导致幼虫出现依赖于剂量的异常行为。