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暴露于亚致死浓度的氧化钴和氧化锰纳米颗粒会导致大型溞体内的金属负荷增加。

Exposure to sublethal concentrations of CoO and MnO nanoparticles induced elevated metal body burden in Daphnia magna.

作者信息

Heinlaan Margit, Muna Marge, Juganson Katre, Oriekhova Olena, Stoll Serge, Kahru Anne, Slaveykova Vera I

机构信息

Environmental Biogeochemistry and Ecotoxicology, Department F.-A. Forel for Environmental and Aquatic Sciences, Faculty of Science, University of Geneva, Uni Carl Vogt, 66, Boulevard Carl-Vogt, CH-1211 Geneva 4, Switzerland; Laboratory of Environmental Toxicology, National Institute of Chemical Physics and Biophysics, Akadeemia tee 23, 12618 Tallinn, Estonia.

Laboratory of Environmental Toxicology, National Institute of Chemical Physics and Biophysics, Akadeemia tee 23, 12618 Tallinn, Estonia; Department of Materials and Environmental Technology, Tallinn University of Technology, Ehitajate tee 5, 19086 Tallinn, Estonia.

出版信息

Aquat Toxicol. 2017 Aug;189:123-133. doi: 10.1016/j.aquatox.2017.06.002. Epub 2017 Jun 6.

Abstract

Despite the significant progress made in ecotoxicological research on nanoparticles (NPs), there is still very limited information available regarding the biological effects of certain types of NPs such as CoO and MnO. Only a couple of studies provide data on their impact on aquatic organisms whereas, alarmingly, these NPs have been proposed to have high toxicity potential. In addition, more data are needed to determine whether the adverse effects the metal NPs induce on aquatic organisms are rather due to their chemical or particulate nature. To address these open questions, the (sub)lethal effects of Co and Mn NPs in parallel with the respective soluble metal salts on Daphnia magna were studied. The aims of the current study were to i) assess the acute toxicity of CoO and MnO NPs (primary size 10-30nm) to D. magna, ii) evaluate whether the acute NP exposure at sublethal concentrations influences D. magna post-exposure feeding behaviour and iii) quantify D. magna metal body burden after exposure and after the post-exposure feeding to estimate the potential of trophic transfer of metals. Flow cytometry and total reflection X-ray fluorescence spectroscopy were applied for feeding and metal body burden evaluations, respectively. CuO NPs (primary size 22-25nm) that are very toxic to D. magna were included in the study as a positive control. Since the release of metal ions is an important possibility for toxicity of metal NPs, soluble Co-, Mn- and Cu-salts were analysed in parallel. The solubilisation of CoO NPs in the OECD202 assay conditions was 0.1% and MnO NPs 35%. MnO NPs also produced reactive oxygen species in abiotic conditions. However CoO and MnO NPs were not acutely toxic to D. magna (48h EC>100mg metal/L) at OECD202 assay conditions. The 48h EC values of soluble Co- and Mn-salts were 3.2mgCo/L and 41mgMn/L, respectively. Post-exposure feeding behaviour after 48h exposure to sublethal concentrations (≤10mg/L) of CoO and MnO NPs differed from that of the unexposed (control) D. magna only at the highest exposure concentrations but was comparable to the feeding behaviour of the respective metal salt-exposed organisms. Upon 48h exposure, dose-dependent increase of D. magna total metal body burden in case of both the NPs and the soluble salts was observed. After 48h post-exposure feeding with algae C. reinhardtii (depuration): D. magna body burden remained elevated (up to 760-fold compared to the control organism) only in case of the NPs. This may indicate potential for trophic transfer of NPs/heavy metals and thus hazard for freshwater ecosystem.

摘要

尽管纳米颗粒(NPs)的生态毒理学研究取得了显著进展,但关于某些类型的纳米颗粒(如氧化钴和氧化锰)的生物学效应的信息仍然非常有限。只有少数研究提供了它们对水生生物影响的数据,而令人担忧的是,这些纳米颗粒被认为具有很高的潜在毒性。此外,还需要更多数据来确定金属纳米颗粒对水生生物产生的不利影响是由于其化学性质还是颗粒性质。为了解决这些悬而未决的问题,研究了钴和锰纳米颗粒以及各自的可溶性金属盐对大型溞的(亚)致死效应。本研究的目的是:i)评估氧化钴和氧化锰纳米颗粒(原始粒径10 - 30nm)对大型溞的急性毒性;ii)评估在亚致死浓度下急性暴露于纳米颗粒是否会影响大型溞暴露后的摄食行为;iii)量化大型溞暴露后以及暴露后摄食后的金属体内负荷,以估计金属的营养转移潜力。分别应用流式细胞术和全反射X射线荧光光谱法进行摄食和金属体内负荷评估。对大型溞毒性很强的氧化铜纳米颗粒(原始粒径22 - 25nm)作为阳性对照纳入研究。由于金属离子的释放是金属纳米颗粒毒性的一个重要可能性,因此同时分析了可溶性钴、锰和铜盐。在经合组织202试验条件下,氧化钴纳米颗粒的溶解率为0.1%,氧化锰纳米颗粒为35%。氧化锰纳米颗粒在非生物条件下也会产生活性氧。然而,在经合组织202试验条件下,氧化钴和氧化锰纳米颗粒对大型溞没有急性毒性(48小时半数有效浓度>100mg金属/L)。可溶性钴盐和锰盐的48小时半数有效浓度分别为3.2mgCo/L和41mgMn/L。在暴露于亚致死浓度(≤10mg/L)的氧化钴和氧化锰纳米颗粒48小时后,暴露后的摄食行为仅在最高暴露浓度下与未暴露(对照)的大型溞不同,但与暴露于相应金属盐的生物的摄食行为相当。暴露48小时后,观察到纳米颗粒和可溶性盐情况下大型溞总金属体内负荷均呈剂量依赖性增加。在以莱茵衣藻进行48小时暴露后摄食(净化)后:仅在纳米颗粒情况下,大型溞的体内负荷仍然升高(与对照生物相比高达760倍)。这可能表明纳米颗粒/重金属具有营养转移潜力,从而对淡水生态系统构成危害。

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