Environnement et Sociétés (LIENSs), UMR 7266 CNRS - La Rochelle Université, 2 Rue Olympe de Gouges, 17000 La Rochelle, France.
International Atomic Energy Agency (IAEA), Marine Environment Laboratories, 4 Quai Antoine Ier, 98000, Principality of Monaco, France.
Environ Res. 2022 Dec;215(Pt 1):114201. doi: 10.1016/j.envres.2022.114201. Epub 2022 Aug 31.
The bioaccumulation of mercury (Hg) in marine organisms through various pathways has not yet been fully explored, particularly in cephalopods. This study utilises radiotracer techniques using the isotope Hg to investigate the toxicokinetics and the organotropism of waterborne inorganic Hg (iHg) and dietary inorganic and organic Hg (methylHg, MeHg) in juvenile common cuttlefish Sepia officinalis. The effect of two contrasting CO partial pressures in seawater (400 and 1600 μatm, equivalent to pH 8.08 and 7.54, respectively) and two types of prey (fish and shrimp) were tested as potential driving factors of Hg bioaccumulation. After 14 days of waterborne exposure, juvenile cuttlefish showed a stable concentration factor of 709 ± 54 and 893 ± 117 at pH 8.08 and 7.54, respectively. The accumulated dissolved iHg was depurated relatively rapidly with a radiotracer biological half-life (Tb) of 44 ± 12 and 55 ± 16 days at pH 8.08 and 7.54, respectively. During the whole exposure period, approximately half of the iHg was found in the gills, but iHg also increased in the digestive gland. When fed with Hg-radiolabelled prey, cuttlefish assimilated almost all the Hg provided (>95%) independently of the prey type. Nevertheless, the prey type played a major role on the depuration kinetics with Hg Tb approaching infinity in fish fed cuttlefish vs. 25 days in shrimp fed cuttlefish. Such a difference is explained by the different proportion of Hg species in the prey, with fish prey containing more than 80% of MeHg vs. only 30% in shrimp. Four days after ingestion of radiolabelled food, iHg was primarily found in the digestive organs while MeHg was transferred towards the muscular tissues. No significant effect of pH/pCO variation was observed during both the waterborne and dietary exposures on the bioaccumulation kinetics and tissue distribution of iHg and MeHg. Dietary exposure is the predominant pathway of Hg bioaccumulation in juvenile cuttlefish.
汞(Hg)在海洋生物体内通过各种途径的生物累积尚未得到充分研究,特别是在头足类动物中。本研究利用放射性示踪技术,使用同位素 Hg 研究了水生无机汞(iHg)和膳食无机及有机汞(甲基汞,MeHg)在幼年普通乌贼 Sepia officinalis 中的毒代动力学和器官亲嗜性。测试了两种不同的海水 CO 分压(400 和 1600 μatm,分别相当于 pH 值 8.08 和 7.54)和两种类型的食物(鱼类和虾类)作为 Hg 生物累积的潜在驱动因素。经过 14 天的水暴露后,幼年乌贼在 pH 值为 8.08 和 7.54 时,稳定的浓度系数分别为 709±54 和 893±117。累积的溶解 iHg 被快速排泄,放射性示踪生物半衰期(Tb)分别为 44±12 和 55±16 天。在整个暴露期间,约有一半的 iHg 存在于鳃中,但 iHg 在消化腺中也增加了。当喂食含 Hg 放射性示踪剂的食物时,乌贼几乎吸收了所提供的所有 Hg(>95%),而与食物类型无关。然而,食物类型对清除动力学起着重要作用,用含 Hg 放射性示踪剂的鱼喂食乌贼时,Hg Tb 接近无穷大,而用含 Hg 放射性示踪剂的虾喂食乌贼时,Hg Tb 为 25 天。这种差异可以用食物中 Hg 物种的不同比例来解释,鱼类食物中含有超过 80%的 MeHg,而虾类食物中只有 30%。在摄入放射性示踪食物后的 4 天内,iHg 主要存在于消化器官中,而 MeHg 则转移到肌肉组织中。在水暴露和膳食暴露期间,pH 值/pCO 变化对 iHg 和 MeHg 的生物累积动力学和组织分布均无显著影响。膳食暴露是幼年乌贼体内 Hg 生物累积的主要途径。