Department of Biology and Center for Environmental and Marine Studies, University of Aveiro, Aveiro, Portugal.
Department of Biology, Terrestrial Ecology Unit, Ghent University, Ghent, Belgium.
Environ Toxicol Chem. 2019 Feb;38(2):412-422. doi: 10.1002/etc.4307. Epub 2019 Jan 8.
Anthropogenic activities such as the use of pesticides may affect aquatic biota populations, due to potential agricultural runoffs or disposals. Carbendazim is one example of a widely used fungicide with a high potential to end up in aquatic ecosystems through runoff. Deleterious effects observed at the individual level are possibly explained by changes in homeostasis at the cellular level, and both factors can then be used to predict effects at the population level. In the present study, an isoclonal population of Daphnia magna (clone K6) was exposed to a concentration that mimics relevant levels of carbendazim in the environment over 12 generations. The effects of carbendazim were assessed in some generations using the following endpoints: biochemical biomarkers (cholinesterase, catalase, and glutathione-S-transferase), lipid peroxidation and energy-related parameters (carbohydrates, lipids, and proteins along with available energy and energy consumption), parental longevity, and population growth (r). Long-term exposure to carbendazim had no effect on the intrinsic rate of natural increase (r) of adult D. magna, but longevity was decreased at the F12 generation compared to that of control. Differences between the exposed and nonexposed populations were found for cholinesterase, glutathione-S-transferase, and lipid peroxidation. However, for catalase and energy-related parameters, no differences were observed between these 2 populations. Natural variability was seen throughout the test period, under control conditions, within the 12 generations. Overall, carbendazim induced some effects at the subcellular level that translated into changes in longevity but these later vanished in terms of population effects. Environ Toxicol Chem 2019;38:412-422. © 2018 SETAC.
人为活动,如使用农药,可能会影响水生生物种群,因为可能会有农业径流或处置。多菌灵是一种广泛使用的杀菌剂,其很有可能通过径流进入水生生态系统。在个体水平上观察到的有害影响可能是由于细胞水平上的内稳态变化引起的,这两个因素都可以用来预测种群水平上的影响。在本研究中,一种克隆的大型溞(K6 克隆)种群在 12 代中暴露于模拟环境中多菌灵相关浓度的浓度下。在一些世代中,使用以下终点评估多菌灵的影响:生化生物标志物(胆碱酯酶、过氧化氢酶和谷胱甘肽-S-转移酶)、脂质过氧化和与能量相关的参数(碳水化合物、脂质和蛋白质以及可用能量和能量消耗)、亲代寿命和种群增长率(r)。长期暴露于多菌灵对成年大型溞的内禀增长率(r)没有影响,但与对照组相比,F12 代的寿命降低。在暴露和未暴露的种群之间发现了胆碱酯酶、谷胱甘肽-S-转移酶和脂质过氧化的差异。然而,对于过氧化氢酶和与能量相关的参数,这两个种群之间没有观察到差异。在对照条件下,整个测试期间,12 代内自然变异性可见。总的来说,多菌灵在亚细胞水平上引起了一些影响,导致寿命发生变化,但在种群效应方面,这些影响后来消失了。环境毒理化学 2019;38:412-422。 © 2018 SETAC。