首页> 美国卫生研究院文献>ACS Omega >Toxicity and Subcellular Fractionation of Yttriumin Three Freshwater Organisms: Daphnia magna Chironomusriparius and Oncorhynchus mykiss
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Toxicity and Subcellular Fractionation of Yttriumin Three Freshwater Organisms: Daphnia magna Chironomusriparius and Oncorhynchus mykiss

机译:钇的毒性和亚细胞分级三种淡水生物中的一种:大水蚤Chironomusriparius和Oncorhynchus mykiss

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摘要

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: Daphnia magna, Chironomus riparius, and Oncorhynchus mykiss. In bioassays using growth as an end point, C. riparius was the only organism showing toxicity at Y exposure concentrations close to environmental ones. The lowest observable effect concentrations (LOECs) of Y assessed for D. magna and O. mykiss 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 D. magna. When exposed to their respective estimated LOECs, D. magna 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, C. riparius bioaccumulated 20–30% of Y inthis detoxified fraction. In contrast, the Y subcellular distributionin O. mykiss liver did not highlightany notable detoxification strategy; Y was accumulated primarily inmitochondria (ca. 32%), a putative metal-sensitive fraction. Thisfraction was also the main sensitive fraction where Y accumulatedin C. riparius and D.magna. Hence, the interaction of Y with mitochondriacould explain its toxicity. In conclusion, there is a wide range ofsubcellular handling strategies for Y, with D. magna accumulating high quantities but sequestering most of it in detoxifiedfractions, whereas O. mykiss tendingto accumulate less Y but in highly sensitive fractions.
机译:自1990年代以来,对稀土元素(REE)的需求有所增加,导致全世界许多采矿项目的发展。然而,关于生物如何在天然水生系统中处理这些金属的知识知之甚少。通过实验室实验,我们评估了水生毒理学中常用的三种淡水生物:大水蚤(Daphnia magna),河岸线虫(Chironomus riparius)和Oncorhynchus mykiss中四种最丰富的REE之一钇(Y)的慢性毒性和亚细胞分级。在以生长为终点的生物测定中,河曲菌是唯一在Y暴露浓度接近环境浓度时显示毒性的生物。 D. magna和O. mykiss的Y的最低可观察效果浓度(LOEC)比天然淡水中的Y浓度至少高100倍。 D. magna观察到Y毒性和水硬度之间呈负相关。当暴露于各自估计的LOEC时,大果D.生物体的Y累积量是暴露于其自己的LOEC的其他两种生物的15-45倍。前者在耐NaOH的部分中最多吸收了75%的Y,推定的金属解毒的亚细胞部分。在较小的范围内,河滨梭菌生物累积了20%至30%的Y。这个排毒的部分。相反,Y亚细胞分布在O. mykiss肝脏中未突出显示任何明显的排毒策略; Y主要累积在线粒体(约32%),对金属敏感的部分。这个分数也是Y累积的主要敏感分数在C. riparius和D.玛格纳。因此,Y与线粒体的相互作用可以解释其毒性。总结来说,Y的亚细胞处理策略,D。magna积累大量,但大部分被隔离在解毒状态分数,而O. mykiss趋于积累较少的Y,但积累高度敏感的分数。

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