Univ Lyon, Université Lyon 1, CNRS, Laboratoire de Biométrie et Biologie Evolutive UMR 5558, 69622, Villeurbanne, France; Littoral Environnement et Sociétés (LIENSs), UMR 7266 CNRS - Université de la Rochelle, 2 Rue Olympe de Gouges, 17000, La Rochelle, France; INRAE, RiverLy, Ecotoxicology Laboratory, 5 Avenue de la Doua, CS20244, 69625, Villeurbanne, Cedex, France.
Univ Lyon, Université Lyon 1, CNRS, Laboratoire de Biométrie et Biologie Evolutive UMR 5558, 69622, Villeurbanne, France.
Environ Pollut. 2022 Sep 1;308:119625. doi: 10.1016/j.envpol.2022.119625. Epub 2022 Jun 14.
One of the best approaches for improving the assessment of metal toxicity in aquatic organisms is to study their organotropism (i.e., the distribution of metals among organs) through a dynamical approach (i.e., via kinetic experiments of metal bioaccumulation), to identify the tissues/organs that play a key role in metal regulation (e.g., storage or excretion). This study aims at comparing the organ-specific metal accumulation of a non-essential (Cd) and an essential metal (Zn), at their environmentally relevant exposure concentrations, in the gammarid Gammarus fossarum. Gammarids were exposed for 7 days to Cd- or Zn-radiolabeled water at a concentration of 52.1 and 416 ng.L (stable equivalent), respectively, and then placed in clean water for 21 days. At different time intervals, the target organs (i.e., caeca, cephalons, intestines, gills, and remaining tissues) were collected and Cd or Zn contents were quantified by gamma-spectrometry. A one-compartment toxicokinetic (TK) model was fitted by Bayesian inference to each organ/metal dataset in order to establish TK parameters. Our results indicate: i) a contrasting distribution pattern of concentrations at the end of the accumulation phase (7 day): gills > caeca ≈ intestines > cephalons > remaining tissues for Cd and intestines > caeca > gills > cephalons > remaining tissues for Zn; ii) a slower elimination of Cd than of Zn by all organs, especially in the gills in which the Cd concentration remained constant during the 21-day depuration phase, whereas Zn concentrations decreased sharply in all organs after 24 h in the depuration phase; iii) a major role of intestines in the uptake of waterborne Cd and Zn at environmentally relevant concentrations.
提高水生生物金属毒性评估的最佳方法之一是通过动态方法(即通过金属生物累积的动力学实验)研究其器官亲嗜性(即金属在器官中的分布),以确定在金属调节中发挥关键作用的组织/器官(例如,储存或排泄)。本研究旨在比较非必需金属(Cd)和必需金属(Zn)在环境相关暴露浓度下在蚤状溞 Gammarus fossarum 中的器官特异性金属积累。蚤状溞在分别为 52.1 和 416ng·L(稳定等价物)的 Cd 或 Zn 放射性标记水中暴露 7 天,然后在清洁水中放置 21 天。在不同的时间间隔内,收集靶器官(即盲囊、头节、肠道、鳃和剩余组织),并用伽马谱仪定量测定 Cd 或 Zn 含量。通过贝叶斯推断对每个器官/金属数据集进行单室毒代动力学(TK)模型拟合,以建立 TK 参数。我们的结果表明:i)在积累阶段结束时(7 天)浓度的分布模式截然不同:鳃>盲囊≈肠道>头节>剩余组织 Cd,肠道>盲囊>鳃>头节>剩余组织 Zn;ii)所有器官对 Cd 的消除速度均慢于 Zn,尤其是在鳃中,在 21 天的净化阶段,Cd 浓度保持不变,而在净化阶段 24 小时后,所有器官中的 Zn 浓度急剧下降;iii)肠道在环境相关浓度下对水相 Cd 和 Zn 的摄取具有重要作用。