Brix Kevin V, Tellis Margaret S, Crémazy Anne, Wood Chris M
EcoTox, Miami, FL, United States; University of Miami, RSMAS, Miami, FL, United States.
Department of Biology, McMaster University, Hamilton, ON, Canada.
Aquat Toxicol. 2017 Dec;193:217-227. doi: 10.1016/j.aquatox.2017.10.015. Epub 2017 Oct 27.
Biotic Ligand Models (BLMs) for individual metals improve our ability to regulate metals in the aquatic environment by considering the effects of water quality parameters (ionic composition, pH, DOC) on metal bioavailability. However, in natural aquatic systems, organisms are often simultaneously exposed to multiple metals and these interactions are not currently considered in BLMs or most environmental regulations. Recently, several different mixture BLMs (mBLMs) have been developed to begin assessing this issue. Some of these models assume competitive interactions between all metals, while others assume only metals with similar modes of action (e.g., Na or Ca antagonists) will competitively interact. In this study, we used standard in vivo 3-h gill metal binding assays to characterize the uptake of Cd, Pb, and Zn individually and in binary mixtures with Ag, Cd, Cu, Pb, Ni, and Zn across a range of concentrations that encompassed the 96-h LC50 for each metal. Inhibition of Cd, Pb, and Zn uptake at the gill by introduction of a second metal was consistent with mode of action in some cases, but not others. Further, contrary to expectations, inhibition was always either non-competitive or could not be defined statistically. We also observed one example of stimulated metal uptake (Ni stimulated Zn uptake). Consistent with our previous experiments on Ag, Cu, and Ni, these studies suggest that current mBLM frameworks will need revision to better reflect the mechanisms underlying metal mixture interactions.
针对单一金属的生物配体模型(BLMs)通过考虑水质参数(离子组成、pH值、溶解性有机碳)对金属生物可利用性的影响,提高了我们在水生环境中对金属进行调控的能力。然而,在天然水生系统中,生物常常同时暴露于多种金属,而目前生物配体模型或大多数环境法规并未考虑这些相互作用。最近,已经开发出几种不同的混合生物配体模型(mBLMs)来开始评估这一问题。其中一些模型假定所有金属之间存在竞争性相互作用,而另一些模型则假定只有作用方式相似的金属(例如,钠或钙拮抗剂)才会发生竞争性相互作用。在本研究中,我们使用标准的体内3小时鳃金属结合试验,分别测定了镉、铅和锌以及它们与银、镉、铜、铅、镍和锌形成的二元混合物在一系列浓度下的摄取情况,这些浓度涵盖了每种金属的96小时半数致死浓度(LC50)。在某些情况下,引入第二种金属对鳃部镉、铅和锌摄取的抑制作用与作用方式一致,但在其他情况下并非如此。此外,与预期相反,抑制作用总是非竞争性的,或者无法从统计学上进行定义。我们还观察到一个金属摄取受刺激的例子(镍刺激锌的摄取)。与我们之前对银、铜和镍的实验一致,这些研究表明,当前的混合生物配体模型框架需要修订,以更好地反映金属混合物相互作用的潜在机制。