Department of Applied Chemistry, College of Sciences, China Agricultural University, Beijing 100193, China; Department of Physiological Sciences, Center for Environmental and Human Toxicology, University of Florida Genetics Institute, Interdisciplinary Program in Biomedical Sciences Neuroscience, College of Veterinary Medicine, University of Florida, Gainesville, FL 32611, USA.
Department of Physiological Sciences, Center for Environmental and Human Toxicology, University of Florida Genetics Institute, Interdisciplinary Program in Biomedical Sciences Neuroscience, College of Veterinary Medicine, University of Florida, Gainesville, FL 32611, USA.
Neurotoxicol Teratol. 2018 Nov-Dec;70:18-27. doi: 10.1016/j.ntt.2018.10.001. Epub 2018 Oct 2.
The objectives of this study were to compare the biological responses in developing zebrafish to two organophosphate insecticides, chlorpyrifos (CPF) and diazinon (DZN). Zebrafish embryos were exposed to either solvent control (0.1% DMSO, v/v), or one dose of 0.1, 1.0, 10.0 and 25.0 μM CPF, as well as one dose of 0.1, 1.0, 10.0 and 100.0 μM DZN for 96 h. CPF at 10.0 and 25.0 μM caused 70-80% and 100% mortality in embryos after 96 h exposure, whereas embryos treated with 10.0 and 100.0 μM DZN showed 30-40% and 70-80% lethality. CPF at 10.0 μM significantly decreased cumulative hatching rate, whereas hatching rate was significantly reduced in embryos treated with 100.0 μM DZN. Spinal lordosis was primarily observed in larvae exposed to 1.0 and 10.0 μM CPF, whereas pericardial edema was mainly detected with 10.0 and 100.0 μM DZN exposure. Embryo exposed to 1.0, 10.0 and 25.0 μM CPF exhibited no mitochondrial dysfunction; exposure to 100.0 μM DZN significantly inhibited mitochondrial bioenergetics. To determine if CPF and DZN affected larval activity, dark photokinesis response was assessed in larvae following 7 days exposure to 0.1 and 1.0 μM CPF, as well as to 0.1 1.0, and 10.0 μM DZN. Larvae exposed to 1.0 μM CPF showed hypoactivity, whereas the activity in the dark was not overtly changed in larvae exposed to DZN. In summary, CPF showed higher developmental toxicity compared to DZN. Moreover, based on the types of morphological deformities noted, as well as differences in locomotor activity, we conclude that OPs have unique chemical-specific modes of action that can result in varied biological responses during early development.
本研究的目的是比较两种有机磷杀虫剂,毒死蜱(CPF)和二嗪农(DZN)对发育中的斑马鱼的生物反应。将斑马鱼胚胎暴露于溶剂对照(0.1%DMSO,v/v)或 0.1、1.0、10.0 和 25.0μM CPF 的一个剂量以及 0.1、1.0、10.0 和 100.0μM DZN 的一个剂量中 96 小时。96 小时暴露后,10.0 和 25.0μM CPF 导致 70-80%和 100%的胚胎死亡,而用 10.0 和 100.0μM DZN 处理的胚胎的死亡率为 30-40%和 70-80%。10.0μM CPF 显著降低了累积孵化率,而 100.0μM DZN 处理的胚胎孵化率显著降低。在暴露于 1.0 和 10.0μM CPF 的幼虫中主要观察到脊柱侧凸,而在用 10.0 和 100.0μM DZN 暴露时主要检测到心包水肿。暴露于 1.0、10.0 和 25.0μM CPF 的胚胎没有表现出线粒体功能障碍;暴露于 100.0μM DZN 显著抑制了线粒体生物能。为了确定 CPF 和 DZN 是否影响幼虫的活动能力,在幼虫暴露于 0.1 和 1.0μM CPF 以及 0.1、1.0 和 10.0μM DZN 7 天后,评估了黑暗光动反应。暴露于 1.0μM CPF 的幼虫表现出活动能力降低,而暴露于 DZN 的幼虫的黑暗活动没有明显变化。总之,CPF 表现出比 DZN 更高的发育毒性。此外,根据观察到的形态畸形类型以及运动活性的差异,我们得出结论,有机磷具有独特的化学特异性作用模式,这可能导致早期发育过程中产生不同的生物反应。