Ruan Qin-Li, Ju Jing-Juan, Li Yun-Hui, Liu Ran, Pu Yue-Pu, Yin Li-Hong, Wang Da-Yong
Department of Occupation and Environmental Health, School of Public Health, Southeast University, Nanjing, China.
J Toxicol Environ Health A. 2009;72(11-12):746-51. doi: 10.1080/15287390902841532.
The aim of this study was to (1) determine whether model organism Caenorhabditis elegans was sensitive to pesticides at the maximum concentration limits regulated by national agency standards, and (2) examine the multi-biological toxicities occurring as a result of exposure to pesticides. Five pesticides, namely, chlorpyrifos, imibacloprid, buprofezin, cyhalothrin, and glyphosate, with four different mechanisms of action were selected for the investigation. In accordance with national agency requirements, 4 exposed groups were used for each tested pesticide with the concentration scales ranging from 1.0 x 10(-3) to 1 mg/L. L4 larvae were exposed for 24 and 72 h, respectively. Endpoints of locomotion, propagation, and development were selected for the assay as parameters of toxicity. After exposure for 24 h, both the body bend frequency and head thrash frequency of nematodes exposed to chlorpyrifos, imibacloprid, and cyhalothrin decreased in a concentration-dependent manner, and there were significant differences between exposed groups at maximum concentration level (MCL) compared to control. The generation time of nematodes exposed to buprofezin 24 h significantly increased in a concentration-dependent manner in the highest exposed group. When exposed for 72 h, the body bend frequency and head thrash frequency of nematodes exposed to cyhalothrin markedly decreased at MCL. The generation time and brood size of nematodes exposed to buprofezin were reduced in a concentration-dependent manner. The behavior of nematodes was sensitive to pesticides with neurotoxic properties, while pesticides affecting insect growth modified the reproductive system. The effects of pesticides on nematodes exposed for 24 h appeared more sensitive than with exposure for 72 h. Caenorhabditis elegans may thus be used for assessing the adverse effects of pesticide residues in aquatic environment.
(1)确定模式生物秀丽隐杆线虫在国家机构标准规定的最大浓度限值下是否对农药敏感;(2)研究接触农药后产生的多种生物毒性。选择了具有四种不同作用机制的五种农药,即毒死蜱、吡虫啉、噻嗪酮、氯氟氰菊酯和草甘膦进行调查。按照国家机构要求,每种受试农药设置4个暴露组,浓度范围为1.0×10⁻³至1mg/L。L4幼虫分别暴露24小时和72小时。选择运动、繁殖和发育终点作为毒性测定参数。暴露24小时后,接触毒死蜱、吡虫啉和氯氟氰菊酯的线虫的身体弯曲频率和头部摆动频率均呈浓度依赖性下降,与对照组相比,最大浓度水平(MCL)暴露组之间存在显著差异。暴露于噻嗪酮24小时的线虫的世代时间在最高暴露组中呈浓度依赖性显著增加。暴露72小时时,接触氯氟氰菊酯的线虫在MCL时身体弯曲频率和头部摆动频率明显下降。暴露于噻嗪酮的线虫的世代时间和产卵量呈浓度依赖性降低。线虫的行为对具有神经毒性的农药敏感,而影响昆虫生长的农药则改变了生殖系统。农药对暴露24小时的线虫的影响似乎比暴露72小时更敏感。因此,秀丽隐杆线虫可用于评估水环境中农药残留的不利影响。