Tsui Martin T K, Wang Wen-Xiong
Department of Biology, The Hong Kong University of Science and Technology (HKUST), Clear Water Bay, Kowloon, Hong Kong, People's Republic of China.
Environ Sci Technol. 2004 Feb 1;38(3):808-16. doi: 10.1021/es034638x.
Mercury (Hg) is an important environmental pollutant due to its highly toxic nature and widespread occurrence in aquatic systems. The biokinetics of Hg in zooplankton have been largely ignored in previous studies. This study examines the assimilation, dissolved uptake, and efflux of inorganic mercury [Hg(II)] and methylmercury (MeHg) in a freshwater cladoceran, Daphnia magna, and models the exposure pathways of Hg(II) and MeHg in the daphnids. The assimilation efficiencies (AEs) of both Hg species decreased significantly with increasing algal carbon concentrations. The dissolved uptake of Hg(II) and MeHg was proportional to the ambient concentration (ranging from environmentally realistic to high concentration over a 3-4 orders of magnitude variation), whereas MeHg had a slightly higher uptake rate constant (0.46 L g(-1) h(-1)) than Hg(II) (0.35 L g(-1) h(-1)). Surprisingly, the efflux rate constants of Hg(ll) and MeHg were rather comparable (0.041 -0.063 day(-1)). The release of both Hg(II) and MeHg via different routes (excretion, egestion, molting, and neonate production) was further examined at different food concentrations. It was found that regeneration into the dissolved phase was important for D. magna to eliminate both Hg species, but maternal transfer of Hg(II) (11-15%) and MeHg (32-41%) to neonates represented another important pathway for the elimination of Hg(II) and MeHg from the mothers. Modeling results suggest that food is an important source for MeHg exposure (47-98%), but water exposure represents 31-96% of Hg(II) accumulation in D. magna, depending on the variation of Hg bioconcentration factor in ingested food. Furthermore, MeHg predominates the bioaccumulation of Hg in D. magna even though MeHg constitutes only a small percentage of the total Hg in the water. The results strongly indicate that maternal transfer of Hg(II) and MeHg in freshwater zooplankton should be considered in manytoxicity testings and risk assessment in aquatic food chains.
汞(Hg)因其高毒性以及在水生系统中的广泛存在,成为一种重要的环境污染物。以往研究很大程度上忽略了浮游动物体内汞的生物动力学。本研究考察了淡水枝角类大型溞对无机汞[Hg(II)]和甲基汞(MeHg)的同化、溶解吸收及排出情况,并模拟了大型溞体内Hg(II)和MeHg的暴露途径。两种汞形态的同化效率(AE)均随藻类碳浓度的增加而显著降低。Hg(II)和MeHg的溶解吸收与环境浓度成正比(环境实际浓度到高浓度范围有3 - 4个数量级的变化),而MeHg的吸收速率常数(0.46 L g⁻¹ h⁻¹)略高于Hg(II)(0.35 L g⁻¹ h⁻¹)。令人惊讶的是,Hg(II)和MeHg的排出速率常数相当(0.041 - 0.063 day⁻¹)。在不同食物浓度下,进一步研究了Hg(II)和MeHg通过不同途径(排泄、排粪、蜕皮和产幼体)的释放情况。研究发现,再生进入溶解相对于大型溞消除两种汞形态很重要,但Hg(II)(11 - 15%)和MeHg(32 - 41%)向幼体的母体转移是大型溞母体消除Hg(II)和MeHg的另一个重要途径。模拟结果表明,食物是MeHg暴露的重要来源(47 - 98%),但水体暴露占大型溞体内Hg(II)积累的31 - 96%,这取决于摄入食物中汞生物浓缩系数的变化。此外,尽管MeHg在水中总汞中所占比例很小,但它在大型溞体内汞的生物积累中占主导地位。结果有力地表明,在许多水生食物链的毒性测试和风险评估中,应考虑淡水浮游动物体内Hg(II)和MeHg的母体转移。