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微纳束 X 射线荧光成像中稀土元素镧和钆的分布测定。

Determination of the distribution of rare earth elements La and Gd in micro and nano-SXRF imaging.

机构信息

Life Sciences, Hamburg University of Applied Science, Ulmenliet 20, D-21033 Hamburg, Germany.

University of the CWest of Scotland, Paisley, PA1 2BE, UK.

出版信息

Environ Sci Process Impacts. 2023 Aug 16;25(8):1288-1297. doi: 10.1039/d3em00133d.

Abstract

While our awareness of the toxicity of rare earth elements to aquatic organisms increases, our understanding of their direct interaction and accumulation remains limited. This study describes the acute toxicity of lanthanum (La) and gadolinium (Gd) in neonates and discusses potential modes of action on the basis of the respective patterns of biodistribution. Ecotoxicological bioassays for acute toxicity were conducted and dissolved metal concentrations at the end of the tests were determined. The results showed a significant difference in nominal EC (immobility) between La (>30 mg L) and Gd (13.93 (10.92 to 17.38) mg L). Daphnids that were then exposed to a concentration close to the determined EC of Gd (15 mg L, nominal concentration) for 48 h and 72 h were studied by synchrotron micro and nano-X-ray fluorescence to evaluate the biodistribution of potentially accumulated metals. X-ray fluorescence analyses showed that La was mainly found in the intestinal track and appeared to accumulate in the hindgut. This accumulation might be explained by the ingestion of solid La precipitates formed in the media. In contrast, Gd could only be detected in a small amount, if at all, in the intestinal tract, but was present at a much higher concentration in the tissues and became more pronounced with longer exposure time. The solubility of Gd is higher in the media used, leading to higher dissolved concentrations and uptake into tissue in ionic form common metal transporting proteins. By studying La and Gd biodistribution in after an acute exposure, the present study has demonstrated that different uptake pathways of solid and dissolved metal species may lead to different accumulation patterns and toxicity.

摘要

尽管我们越来越意识到稀土元素对水生生物的毒性,但我们对它们的直接相互作用和积累的理解仍然有限。本研究描述了镧(La)和钆(Gd)在幼体中的急性毒性,并根据各自的生物分布模式讨论了潜在的作用模式。进行了生态毒理学急性毒性生物测定,并测定了测试结束时溶解金属的浓度。结果表明,La(>30mg/L)和 Gd(13.93(10.92 至 17.38)mg/L)之间的名义 EC(不活动)值存在显著差异。然后,将暴露于接近 Gd 确定 EC(15mg/L,名义浓度)的浓度 48 小时和 72 小时的水蚤通过同步加速器微纳米 X 射线荧光进行研究,以评估潜在积累金属的生物分布。X 射线荧光分析表明,La 主要存在于肠道中,并似乎在直肠中积累。这种积累可能是由于摄入了在介质中形成的固体 La 沉淀物。相比之下,Gd 只能在肠道中微量检测到,如果有的话,但在组织中的浓度要高得多,并且随着暴露时间的延长而变得更加明显。在所使用的介质中,Gd 的溶解度更高,导致更高的溶解浓度和以离子形式摄取到组织中,这是常见的金属转运蛋白。通过研究急性暴露后 La 和 Gd 的生物分布,本研究表明,固体和溶解金属物种的不同摄取途径可能导致不同的积累模式和毒性。

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