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Mercury in tundra vegetation of Alaska: Spatial and temporal dynamics and stable isotope patterns

机译:阿拉斯加苔原植被中的汞:时空动态和稳定的同位素模式

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摘要

Vegetation uptake of atmospheric mercury (Hg) is an important mechanism enhancing atmospheric Hg deposition via litterfall and senescence. We here report Hg concentrations and pool sizes of different plant functional groups and plant species across nine tundra sites in northern Alaska. Significant spatial differences were observed in bulk vegetation Hg concentrations at Toolik Field station (52 +/- 9 mu g kg(-1)), Eight Mile Lake Observatory (40 +/- 0.2 mu g kg(-1)), and seven sites along a transect from Toolik Field station to the Arctic coast (36 +/- 9 mu g kg(-1)). Hg concentrations in non-vascular vegetation including feather and peat moss (58 +/- 6 mu g kg(-1) and 34 +/- 2 mu g kg(-1), respectively) and brown and white lichen (41 +/- 2 mu g kg(-1) and 34 +/- 2 mu g kg(-1), respectively), were three to six times those of vascular plant tissues (8 +/- 1 mu g kg(-1) in dwarf birch leaves and 9 +/- 1 mu g kg(-1) in tussock grass). A high representation of non-vascular vegetation in above ground biomass resulted in substantial Hg mass contained in tundra above ground vegetation (29 mu g m(-2)), which fell within the range of foliar Hg mass estimated for forests in the United States (15 to 45 mu g m(-2)) in spite of much shorter growing seasons.Hg stable isotope signatures of different plant species showed that atmospheric Hg(0) was the dominant source of Hg to tundra vegetation. Mass-dependent isotope signatures (delta Hg-202) in vegetation relative to atmospheric Hg (0) showed pronounced shifts towards lower values, consistent with previously reported isotopic fractionation during foliar uptake of Hg(0). Mass-independent isotope signatures (Delta Hg-199) of lichen were more positive relative to atmospheric Hg(0), indicating either photochemical reduction of Hg(II) or contributions of inorganic Hg (II) from atmospheric deposition and/or dust Delta Hg-199 and Delta Hg-200 values in vascular plant species were similar to atmospheric Hg(0) suggesting that overall photochemical reduction and subsequent re-emission was relatively insignificant in these tundra ecosystems, in agreement with previous Hg(0) ecosystem flux measurements. (C) 2019 Elsevier B.V. All rights reserved.
机译:大气汞(Hg)的植被吸收是通过凋落物和衰老增加大气中Hg沉积的重要机制。我们在这里报告了阿拉斯加北部9个苔原站点上不同植物功能组和植物物种的汞浓度和库大小。在Toolik野外站(52 +/- 9μg kg(-1)),八英里湖天文台(40 +/- 0.2μg kg(-1))和七个大块植被中的汞浓度中观察到了显着的空间差异从Toolik Field站到北极海岸的样带沿线站点(36 +/- 9μg kg(-1))。非血管植被中的汞含量,包括羽毛和泥炭藓(分别为58 +/- 6μg kg(-1)和34 +/- 2 mu g kg(-1))以及棕色和白色地衣(41 + / -2微克kg(-1)和34 +/- 2微克kg(-1)分别是维管植物组织的三到六倍(8 +/- 1微克kg(-1))矮白桦叶和9 +/- 1μg kg(-1)在草丛中)。地上生物量中非脉管植被的高度代表性导致地面植被上的苔原中含有大量的汞(29μgm(-2)),这在美国森林估计的叶面汞质量范围内(尽管生长季节短得多,但仍为15至45μgm(-2))。不同植物物种的汞稳定同位素特征表明,大气Hg(0)是苔原植被中汞的主要来源。植被中相对于大气Hg(0)的质量依赖性同位素特征(δHg-202)显示出明显的向较低值的偏移,这与先前报道的叶面吸收Hg(0)时的同位素分级一致。地衣的与质量无关的同位素特征(Delta Hg-199)相对于大气Hg(0)更为阳性,表明大气中沉积和/或尘埃三角洲Hg(II)的光化学还原或无机Hg(II)的贡献维管植物物种中的-199和Delta Hg-200值与大气中的Hg(0)相似,表明在这些苔原生态系统中总体光化学还原和随后的再排放相对不重要,这与以前的Hg(0)生态系统通量测量结果一致。 (C)2019 Elsevier B.V.保留所有权利。

著录项

  • 来源
    《The Science of the Total Environment》 |2019年第10期|1502-1512|共11页
  • 作者单位

    Desert Res Inst, Div Atmospher Sci, 2215 Raggio Pkwy, Reno, NV 89512 USA;

    Univ Toulouse, CNRS, OMP, Geosci Environm Toulouse, 14 Ave Edouard Belin, F-31400 Toulouse, France|Univ Basel, Environm Geosci, Bernoullistr 30, CH-4056 Basel, Switzerland;

    Univ Toulouse, CNRS, OMP, Geosci Environm Toulouse, 14 Ave Edouard Belin, F-31400 Toulouse, France;

    Desert Res Inst, Div Atmospher Sci, 2215 Raggio Pkwy, Reno, NV 89512 USA|Univ Massachusetts, Dept Environm Earth & Atmospher Sci, Lowell, MA 01854 USA;

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  • 原文格式 PDF
  • 正文语种 eng
  • 中图分类
  • 关键词

    Tundra; Vegetation; Mercury; Stable Hg isotopes; Arctic; Alaska;

    机译:苔原;植被;汞;稳定的Hg同位素;北极;阿拉斯加;

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