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一项支持镍水生风险评估的微观世界研究:群落水平效应及与生物有效性归一化物种敏感度分布的比较。

A microcosm study to support aquatic risk assessment of nickel: Community-level effects and comparison with bioavailability-normalized species sensitivity distributions.

作者信息

Hommen Udo, Knopf Burkhard, Rüdel Heinz, Schäfers Christoph, De Schamphelaere Karel, Schlekat Chris, Garman Emily Rogevich

机构信息

Fraunhofer Institute for Molecular Biology and Applied Ecology IME, Schmallenberg, Hochsauerlandkreis, Germany.

Environmental Toxicology Unit (GhEnToxLab), Ghent University, Ghent, East Flanders, Belgium.

出版信息

Environ Toxicol Chem. 2016 May;35(5):1172-82. doi: 10.1002/etc.3255. Epub 2016 Mar 18.

Abstract

The aquatic risk assessment for nickel (Ni) in the European Union is based on chronic species sensitivity distributions and the use of bioavailability models. To test whether a bioavailability-based safe threshold of Ni (the hazardous concentration for 5% of species [HC5]) is protective for aquatic communities, microcosms were exposed to 5 stable Ni treatments (6-96 μg/L) and a control for 4 mo to assess bioaccumulation and effects on phytoplankton, periphyton, zooplankton, and snails. Concentrations of Ni in the periphyton, macrophytes, and snails measured at the end of the exposure period increased in a dose-dependent manner but did not indicate biomagnification. Abundance of phytoplankton and snails decreased in 48 μg Ni/L and 96 μg Ni/L treatments, which may have indirectly affected the abundance of zooplankton and periphyton. Exposure up to 24 μg Ni/L had no adverse effects on algae and zooplankton, whereas the rate of population decline of the snails at 24 μg Ni/L was significantly higher than in the controls. Therefore, the study-specific overall no-observed-adverse-effect concentration (NOAEC) is 12 μg Ni/L. This NOAEC is approximately twice the HC5 derived from a chronic species sensitivity distribution considering the specific water chemistry of the microcosm by means of bioavailability models. Thus, the present study provides support to the protectiveness of the bioavailability-normalized HC5 for freshwater communities.

摘要

欧盟对镍(Ni)的水生风险评估基于慢性物种敏感性分布和生物有效性模型的应用。为了测试基于生物有效性的镍安全阈值(5%物种的有害浓度[HC5])是否对水生群落具有保护作用,将微型生态系统暴露于5种稳定的镍处理浓度(6 - 96μg/L)和一个对照浓度下4个月,以评估生物累积以及对浮游植物、周丛生物、浮游动物和蜗牛的影响。暴露期结束时测量的周丛生物、大型植物和蜗牛中的镍浓度呈剂量依赖性增加,但未显示生物放大作用。在48μg Ni/L和96μg Ni/L处理中,浮游植物和蜗牛的丰度下降,这可能间接影响了浮游动物和周丛生物的丰度。暴露于高达24μg Ni/L对藻类和浮游动物没有不利影响,而在24μg Ni/L时蜗牛的种群下降速率显著高于对照组。因此,该研究特定的总体未观察到不良反应浓度(NOAEC)为12μg Ni/L。考虑到微型生态系统的特定水化学性质,通过生物有效性模型从慢性物种敏感性分布得出的HC5,该NOAEC约为其两倍。因此,本研究为生物有效性归一化的HC5对淡水群落的保护作用提供了支持。

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