University of Paris-Saclay, INRAE, UR HYCAR - Artemhys, 92761, Antony, France; Federation Ile-de-France for Research on the Environment, FIRE, FR-3020, 75005, Paris, France.
Freshwater and Oceanic Sciences Unit of ReSearch (FOCUS), Laboratory of Animal Ecology and Ecotoxicology (LEAE), University of Liège B6c, 11 allée du 6 Août, 4000, Liège, Belgium.
Chemosphere. 2020 Oct;257:127253. doi: 10.1016/j.chemosphere.2020.127253. Epub 2020 Jun 4.
In freshwater species, metal toxicity is usually assessed through short-term exposures, hence limiting the practical usefulness of biomarkers for monitoring long-term impacts on wildlife populations. This study investigates the biological alterations elicited by chronic metallic exposures in Gammarus fossarum using multi-level biomarkers. In aquaria, gammarids were exposed for 10 weeks to field-realistic concentrations of Cd, Cu or Pb (0.25, 1.5 or 5.0 μg/L). At the individual level, behavioural traits (respiration, locomotion and feeding) were compared between naive and chronically-exposed gammarids. At the cellular level, enzymatic activities involved in digestion, moult and cell stress were monitored after 2, 6 and 10 weeks of exposure in males and females to consider the temporal feature of their responses. Results showed that the inhibitory effects of Cd and Pb on respiration and locomotion disappeared in chronically-exposed gammarids, reflecting acclimation to maintain these processes, unlike Cu. Chronic Cu- and Pb-elicited feeding inhibition was associated with the inhibitions of digestion enzymes. Chitobiase was inhibited by Cu in males and, by Cd and Pb in females, suggesting gender-dependent disturbances in moulting. In both genders, Cd generated cellular stress by stimulating acidic phosphatase and peroxidase activities. To conclude, such cellular impairments and alterations in individual performances are likely to disturb individual growth, population dynamics and litter decomposition in the long-term. Besides, obtaining biological responses, common to metals or specific to a metal or a gender, supports the development of biomarkers highlighting long-term impacts of metals on the health of organisms and their associated ecological functions in natural environments.
在淡水物种中,金属毒性通常通过短期暴露来评估,因此限制了生物标志物在监测野生动物种群长期影响方面的实际应用。本研究使用多水平生物标志物研究了慢性金属暴露对食蚊鱼(Gammarus fossarum)引起的生物学变化。在水族箱中,食蚊鱼暴露于相当于野外实际浓度的 Cd、Cu 或 Pb(0.25、1.5 或 5.0μg/L)中 10 周。在个体水平上,比较了未暴露和慢性暴露的食蚊鱼的行为特征(呼吸、运动和摄食)。在细胞水平上,在雄性和雌性暴露 2、6 和 10 周后,监测了参与消化、蜕皮和细胞应激的酶活性,以考虑其反应的时间特征。结果表明,Cd 和 Pb 对呼吸和运动的抑制作用在慢性暴露的食蚊鱼中消失,这反映了它们为维持这些过程而适应的能力,而 Cu 则不然。慢性 Cu 和 Pb 引起的摄食抑制与消化酶的抑制有关。在雄性中,甲壳质酶被 Cu 抑制,在雌性中被 Cd 和 Pb 抑制,这表明蜕皮过程中存在性别依赖性的干扰。在两性中,Cd 通过刺激酸性磷酸酶和过氧化物酶的活性产生细胞应激。总之,这些细胞损伤和个体性能的改变可能会干扰个体的生长、种群动态和 litter 的分解。此外,获得对金属共同的或对特定金属或特定性别特异的生物学反应,支持开发生物标志物,以突出金属对生物体健康及其在自然环境中相关生态功能的长期影响。