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淡水肉食性无脊椎动物体内汞生物放大的荟萃分析:群落多样性和饮食暴露驱动变异性。

A Meta-Analysis of Mercury Biomagnification in Freshwater Predatory Invertebrates: Community Diversity and Dietary Exposure Drive Variability.

机构信息

Department of Fisheries, Wildlife, and Conservation Sciences, Oregon State University, Corvallis, Oregon 97331, United States.

Forest and Rangeland Ecosystem Science Center, U.S. Geological Survey, Corvallis, Oregon 97330, United States.

出版信息

Environ Sci Technol. 2024 Oct 29;58(43):19429-19439. doi: 10.1021/acs.est.4c05920. Epub 2024 Oct 11.

Abstract

Accurate estimates of methylmercury (MeHg) exposure are valuable to actionably assess risk and protect wildlife and human health. MeHg trophic transfer is a critical driver of risk: MeHg is generally biomagnified by a factor of 8.3 ± 7.5 from one trophic level to the next, averaged across freshwater communities (mean ± standard deviation). This variability can produce disparate risks even where basal MeHg concentrations are similar. Taxonomy may be one driver of this variability: physiologically diverse groups, like vertebrates and invertebrates, may assimilate MeHg differently. To determine whether taxonomy affects trophic transfer efficiency, we conducted a meta-analysis characterizing predatory invertebrate MeHg biomagnification. Our analyses estimated that freshwater predatory invertebrates biomagnify MeHg by factors of 2.1 ± 0.2 to 4.3 ± 0.3, with a 98.9 ± 0.4% posterior probability that factors are below 5 (mean ± standard error). When vertebrates or primary producers were included, a site's trophic magnification factor was 18.6 ± 6.2 to 54.1 ± 7.7% higher than estimates for invertebrates alone. Biomagnification was inversely correlated to prey MeHg concentration and varied among systematic and functional groups. These data suggest that predatory invertebrates biomagnify MeHg less efficiently than vertebrates and that a community's diversity and structure determine its biomagnification efficiency. Incorporating organismal variation in trophic transfer estimates may improve the assessment, communication, and management of MeHg risk.

摘要

准确估计甲基汞 (MeHg) 的暴露水平对于评估风险并保护野生动物和人类健康非常重要。MeHg 的营养级传递是风险的关键驱动因素:在淡水群落中,MeHg 通常从一个营养级到下一个营养级被生物放大 8.3 ± 7.5 倍,平均值(平均值 ± 标准差)。这种变异性即使在基础 MeHg 浓度相似的情况下也可能产生不同的风险。分类学可能是这种变异性的驱动因素之一:生理多样化的群体,如脊椎动物和无脊椎动物,可能会以不同的方式同化 MeHg。为了确定分类学是否会影响营养级传递效率,我们进行了一项元分析,以描述捕食性无脊椎动物 MeHg 的生物放大作用。我们的分析估计,淡水捕食性无脊椎动物将 MeHg 生物放大 2.1 ± 0.2 至 4.3 ± 0.3 倍,98.9 ± 0.4%的后验概率表明放大倍数低于 5(平均值 ± 标准误差)。当包括脊椎动物或初级生产者时,一个地点的营养级放大因子比仅无脊椎动物的估计值高 18.6 ± 6.2 至 54.1 ± 7.7%。生物放大作用与猎物 MeHg 浓度呈反比,并且在系统和功能组之间存在差异。这些数据表明,捕食性无脊椎动物比脊椎动物更有效地将 MeHg 生物放大,而一个群落的多样性和结构决定了其生物放大效率。在营养级传递估计中纳入生物体的变异性可能会改善 MeHg 风险的评估、沟通和管理。

https://cdn.ncbi.nlm.nih.gov/pmc/blobs/bf2f/11526377/fb245f29f1eb/es4c05920_0001.jpg

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