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生物标志物和行为反应的河口鱼类后急性暴露于氟西汀。

Biomarker and behavioural responses of an estuarine fish following acute exposure to fluoxetine.

机构信息

MARE - Marine and Environmental Sciences Centre, Faculdade de Ciências da Universidade de Lisboa, Campo Grande, 1749 016, Lisboa, Portugal.

MARE - Marine and Environmental Sciences Centre, Faculdade de Ciências da Universidade de Lisboa, Campo Grande, 1749 016, Lisboa, Portugal.

出版信息

Mar Environ Res. 2019 May;147:24-31. doi: 10.1016/j.marenvres.2019.04.002. Epub 2019 Apr 6.

Abstract

Antidepressants such as fluoxetine are frequently detected in estuaries and can have profound effects on non-target organisms by interfering with the neural system and affecting essential physiological processes and behaviours. In this context, short-term effects of fluoxetine exposure were analysed in the common goby Pomatoschistus microps, an estuarine resident fish species. Two experiments were conducted with fish exposed to: i) fluoxetine concentrations within the μg/L range for 96 h (0.1, 0.5, 10 and 100 μg/L) and ii) fluoxetine concentrations within the mg/L range for 1 h (1, 5 and 10 mg/L). Acute toxicity was assessed via multiple biomarker responses, namely: activity levels of antioxidant (superoxide dismutase and catalase) and detoxification enzymes (ethoxyresorufin O-deethylase and glutathione S-transferase); and biomarkers of effects (lipid peroxidation and DNA damage) and of neurotoxicity (acetylcholinesterase inhibition). Furthermore, behavioural responses concerning activity (active time, movement delay and number of active individuals) and feeding (number of feeding individuals) were also recorded and analysed. Acute fluoxetine exposure for 96 h (in the μg/L range) reduced antioxidant CAT activity with increasing concentrations but had no significant effect on SOD activity. Biotransformation enzymes showed bell-shaped response curves, suggesting efficient fluoxetine metabolism at concentrations up to 10 μg/L. No significant damage (LPO and DNAd) was observed at both concentration ranges (μg/L and mg/L), yet 1 h exposure to higher fluoxetine concentrations (mg/L range) inhibited acetylcholinesterase activity (up to 37%). Fluoxetine (at mg/L) also decreased the number of both feeding and active individuals (by 67%), decreased fish active time (up to 93%) and increased movement delay almost 3-fold (274%). Overall, acutely exposed P. microps were able to cope with fluoxetine toxicity at the μg/L range but higher concentrations (mg/L) affected fish cholinergic system and behavioural responses.

摘要

抗抑郁药如氟西汀经常在河口被检测到,通过干扰神经系统和影响重要的生理过程和行为,对非目标生物有深远的影响。在这种情况下,分析了常见的河口鱼类欧洲无须鱲(Pomatoschistus microps)短期暴露于氟西汀的影响。进行了两项实验,鱼类暴露于:i)μg/L 范围内的氟西汀浓度 96 小时(0.1、0.5、10 和 100μg/L)和 ii)mg/L 范围内的氟西汀浓度 1 小时(1、5 和 10mg/L)。通过多种生物标志物反应评估急性毒性,即:抗氧化剂(超氧化物歧化酶和过氧化氢酶)和解毒酶(乙氧基Resorufin O-脱乙基酶和谷胱甘肽 S-转移酶)的活性水平;以及效应标志物(脂质过氧化和 DNA 损伤)和神经毒性标志物(乙酰胆碱酯酶抑制)。此外,还记录和分析了与活动(活跃时间、运动延迟和活跃个体数量)和摄食(摄食个体数量)有关的行为反应。96 小时(μg/L 范围内)的急性氟西汀暴露会随着浓度的增加而降低抗氧化 CAT 活性,但对 SOD 活性没有显著影响。生物转化酶显示出钟形响应曲线,表明在浓度高达 10μg/L 时,氟西汀的代谢效率很高。在两种浓度范围(μg/L 和 mg/L)下均未观察到显著的损伤(LPO 和 DNAd),然而,在更高的氟西汀浓度(mg/L 范围内)暴露 1 小时会抑制乙酰胆碱酯酶活性(高达 37%)。氟西汀(mg/L)还减少了摄食和活跃个体的数量(减少 67%),减少了鱼类活跃时间(高达 93%),并使运动延迟增加了近 3 倍(274%)。总的来说,急性暴露于 P. microps 的鱼类能够在μg/L 范围内应对氟西汀的毒性,但更高的浓度(mg/L)会影响鱼类的胆碱能系统和行为反应。

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