被动式空气采样器网络观测到的瑞士气态元素汞浓度的空间和季节动态†。

IF 2.8 Q3 ENVIRONMENTAL SCIENCES Environmental science: atmospheres Pub Date : 2024-07-03 DOI:10.1039/D4EA00052H
Stefan Osterwalder, Ron Schibler, Christoph Hüglin, Beat Schwarzenbach, Geoff Stupple, Katrina MacSween, Kevin Bishop, Christine Alewell and Nina Buchmann
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引用次数: 0

摘要

汞(Hg)对环境和人类健康构成威胁。因此,2013 年通过了《关于汞的水俣公约》,旨在通过遏制人为排放来减少汞污染。分析大气中气态元素汞(Hg0)的浓度趋势被认为是评估汞污染减排进展的一种具有成本效益的方法。因此,应扩大大气中 Hg0 浓度测量的空间覆盖范围。我们利用汞被动空气采样器(MerPAS®)建立了一个大气中 Hg0 浓度监测网络,在瑞士境内有 22 个站点。瑞士大气中的 Hg0 浓度年平均值为 1.34 ± 0.20 ng m-3(2022 年 8 月 22 日至 2023 年 9 月 21 日),与欧洲空气监测站目前的观测结果相似。农村监测站的平均大气 Hg0 浓度(1.25 ± 0.11 纳克/立方米)明显低于城市监测站(1.37 ± 0.14 纳克/立方米)(曼-惠特尼 U 检验,p < 0.01)。造成这种浓度差异的原因是,城市站点的汞排放量(如燃料燃烧)全年都在增加,而农村站点的气孔汞吸收量在春季和夏季更为明显。我们建议继续使用瑞士大气汞网络,以支持《水俣公约》的呼吁,即监测大气中的 Hg0,以控制国际社会在减少环境中汞含量方面的努力是否成功。此类监测网络的长期记录也将有助于提高对区域和全球汞循环的认识。
本文章由计算机程序翻译,如有差异,请以英文原文为准。

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Spatial and seasonal dynamics of gaseous elemental mercury concentrations over Switzerland observed by a passive air sampler network†

Mercury (Hg) is a threat to the environment and human health. As a consequence, the Minamata Convention on Mercury was adopted in 2013 to reduce Hg pollution by curbing anthropogenic emissions. Analysis of gaseous elemental Hg (Hg0) concentration trends in the atmosphere has been identified as a cost-effective means to evaluate progress on reducing Hg pollution. Therefore, spatial coverage of atmospheric Hg0 concentration measurements should be expanded. We established an atmospheric Hg0 concentration monitoring network with 22 sites across Switzerland, using the Mercury Passive Air Sampler (MerPAS®). The mean annual atmospheric Hg0 concentration in Switzerland was 1.34 ± 0.20 ng m−3 (August 22, 2022 – September 21, 2023), similar to current observations at European air monitoring stations. Mean atmospheric Hg0 concentrations were significantly lower at rural stations (1.25 ± 0.11 ng m−3) than at urban (1.37 ± 0.14 ng m−3) stations (Mann-Whitney U-test, p < 0.01). This concentration difference can be explained by more local Hg emissions at urban sites (e.g., by fuel combustion) throughout the year as well as by more pronounced stomatal Hg0 uptake at rural sites during spring and summer. We recommend continuing the Swiss Atmospheric Mercury Network to support the call from the Minamata Convention to monitor atmospheric Hg0 as a control on whether international efforts are successful in reducing Hg in the environment. Longer term records from such monitoring networks will also help improve the understanding of both regional and global Hg cycles.

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