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钇在三种淡水生物( 、 和 )中的毒性及亚细胞分级分离

Toxicity and Subcellular Fractionation of Yttrium in Three Freshwater Organisms: , and .

作者信息

Cardon Pierre-Yves, Triffault-Bouchet Gaëlle, Caron Antoine, Rosabal Maikel, Fortin Claude, Amyot Marc

机构信息

Département de Sciences Biologiques, GRIL, Université de Montréal (UdeM), Pavillon Marie-Victorin, 90 Avenue Vincent-d'Indy, Montréal, Québec H3C 3J7, Canada.

Division de l'écotoxicologie et de l'évaluation du risque, Centre d'expertise en Analyse Environnementale du Québec (CEAEQ), 2700 rue Einstein, Québec, Québec G1P 3W8, Canada.

出版信息

ACS Omega. 2019 Aug 15;4(9):13747-13755. doi: 10.1021/acsomega.9b01238. eCollection 2019 Aug 27.

Abstract

The demand for rare earth elements (REEs) has increased since the 1990s leading to the development of many mining projects worldwide. However, less is known about how organisms can handle these metals in natural aquatic systems. Through laboratory experiments, we assessed the chronic toxicity and subcellular fractionation of yttrium (Y), one of the four most abundant REEs, in three freshwater organisms commonly used in aquatic toxicology: , and . In bioassays using growth as an end point, was the only organism showing toxicity at Y exposure concentrations close to environmental ones. The lowest observable effect concentrations (LOECs) of Y assessed for and were at least 100 times higher than the Y concentration in natural freshwater. A negative correlation between Y toxicity and water hardness was observed for . When exposed to their respective estimated LOECs, bioaccumulated 15-45 times more Y than the other two organisms exposed to their own LOECs. This former species sequestered up to 75% of Y in the NaOH-resistant fraction, a putative metal-detoxified subcellular fraction. To a lesser extent, bioaccumulated 20-30% of Y in this detoxified fraction. In contrast, the Y subcellular distribution in liver did not highlight any notable detoxification strategy; Y was accumulated primarily in mitochondria (ca. 32%), a putative metal-sensitive fraction. This fraction was also the main sensitive fraction where Y accumulated in and . Hence, the interaction of Y with mitochondria could explain its toxicity. In conclusion, there is a wide range of subcellular handling strategies for Y, with accumulating high quantities but sequestering most of it in detoxified fractions, whereas tending to accumulate less Y but in highly sensitive fractions.

摘要

自20世纪90年代以来,对稀土元素(REEs)的需求不断增加,导致全球许多采矿项目的开发。然而,对于自然水生系统中的生物如何处理这些金属,人们了解较少。通过实验室实验,我们评估了稀土元素中含量最丰富的四种元素之一钇(Y)在水生毒理学中常用的三种淡水生物(大型溞、斜生栅藻和斑马鱼)中的慢性毒性和亚细胞分级分离情况。在以生长为终点的生物测定中,大型溞是唯一一种在接近环境浓度的钇暴露下表现出毒性的生物。评估得出的大型溞和斜生栅藻的最低可见效应浓度(LOECs)比天然淡水中的钇浓度至少高100倍。在大型溞中观察到钇毒性与水硬度之间呈负相关。当暴露于各自估计的LOECs时,大型溞生物累积的钇比暴露于自身LOECs的其他两种生物多15至45倍。前一种生物在耐氢氧化钠组分(一种假定的金属解毒亚细胞组分)中螯合了高达75%的钇。在较小程度上,斜生栅藻在该解毒组分中生物累积了20%至30%的钇。相比之下,钇在斑马鱼肝中的亚细胞分布未突出任何显著的解毒策略;钇主要累积在线粒体中(约32%),这是一个假定的金属敏感组分。该组分也是钇在大型溞和斜生栅藻中累积的主要敏感组分。因此,钇与线粒体的相互作用可以解释其毒性。总之,对于钇存在广泛的亚细胞处理策略,大型溞累积大量钇但将其大部分螯合在解毒组分中,而斜生栅藻倾向于累积较少的钇但累积在高度敏感的组分中。

https://cdn.ncbi.nlm.nih.gov/pmc/blobs/eb09/6714508/8d5461dba8b5/ao9b01238_0001.jpg

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