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无机汞向水生生态系统的负荷率与溶解态气态汞的产生及逸出之间的关系。

Relationship between the loading rate of inorganic mercury to aquatic ecosystems and dissolved gaseous mercury production and evasion.

作者信息

Poulain Alexandre J, Orihel Diane M, Amyot Marc, Paterson Michael J, Hintelmann Holger, Southworth George R

机构信息

Département de Sciences Biologiques, Université de Montréal, C.P. 6128, Succursale Centre-Ville, Pavillon Marie-Victorin, Montréal, QC, Canada H3C 3J7.

出版信息

Chemosphere. 2006 Dec;65(11):2199-207. doi: 10.1016/j.chemosphere.2006.05.066. Epub 2006 Jul 24.

Abstract

The purpose of our study was to test the hypothesis that dissolved gaseous mercury (DGM) production and evasion is directly proportional to the loading rate of inorganic mercury [Hg(II)] to aquatic ecosystems. We simulated different rates of atmospheric mercury deposition in 10-m diameter mesocosms in a boreal lake by adding multiple additions of Hg(II) enriched with a stable mercury isotope ((202)Hg). We measured DGM concentrations in surface waters and estimated evasion rates using the thin-film gas exchange model and mass transfer coefficients derived from sulfur hexafluoride (SF(6)) additions. The additions of Hg(II) stimulated DGM production, indicating that newly added Hg(II) was highly reactive. Concentrations of DGM derived from the experimental Hg(II) additions ("spike DGM") were directly proportional to the rate of Hg(II) loading to the mesocosms. Spike DGM concentrations averaged 0.15, 0.48 and 0.94 ng l(-1) in mesocosms loaded at 7.1, 14.2, and 35.5 microg Hg m(-2) yr(-1), respectively. The evasion rates of spike DGM from these mesocosms averaged 4.2, 17.2, and 22.3 ng m(-2)h(-1), respectively. The percentage of Hg(II) added to the mesocosms that was lost to the atmosphere was substantial (33-59% over 8 weeks) and was unrelated to the rate of Hg(II) loading. We conclude that changes in atmospheric mercury deposition to aquatic ecosystems will not change the relative proportion of mercury recycled to the atmosphere.

摘要

我们研究的目的是检验以下假设

溶解态气态汞(DGM)的产生和逸出与无机汞[Hg(II)]向水生生态系统的负荷率成正比。我们通过多次添加富含稳定汞同位素((202)Hg)的Hg(II),在一个北方湖泊中直径为10米的中型生态系统中模拟了不同速率的大气汞沉降。我们测量了表层水中的DGM浓度,并使用薄膜气体交换模型和由六氟化硫(SF(6))添加得出的传质系数估算了逸出率。Hg(II)的添加刺激了DGM的产生,表明新添加的Hg(II)具有高反应性。实验添加Hg(II)产生的DGM浓度(“尖峰DGM”)与Hg(II)向中型生态系统的负荷率成正比。在以7.1、14.2和35.5微克Hg m(-2) yr(-1)的速率加载的中型生态系统中,尖峰DGM浓度平均分别为0.15、0.48和0.94纳克/升。这些中型生态系统中尖峰DGM的逸出率平均分别为4.2、17.2和22.3纳克 m(-2) h(-1)。添加到中型生态系统中的Hg(II)损失到大气中的比例相当大(8周内为33 - 59%),且与Hg(II)的负荷率无关。我们得出结论,大气汞沉降到水生生态系统的变化不会改变汞再循环到大气中的相对比例。

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