Foliar exchange of mercury vapor: Evidence for a compensation point

Foliar exchange of mercury vapor: Evidence for a compensation point
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DOI:
10.1007/978-94-011-0153-0_41
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发表时间:
1995-02
期刊:
Water, Air, and Soil Pollution
影响因子:
--
通讯作者:
P. Hanson;S. Lindberg;T. A. Tabberer;J. Owens;K. Kim
P. Hanson;S. Lindberg;T. A. Tabberer;J. Owens;K. Kim
中科院分区:
其他
文献类型:
--
作者:
P. Hanson;S. Lindberg;T. A. Tabberer;J. Owens;K. Kim

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对作物和杂草物种的历史研究记录了元素汞蒸气(Hg°)沉积到树叶上的情况,但他们使用的Hg°浓度比目前已知的背景条件下的水平高出几个数量级,可能在大气和景观表面之间人为地造成高梯度。用白色栎(Quercus阿尔巴尔.)红枫(Acer rubrum L.),挪威云杉(Picea abiesL.),和黄杨(Liriodendron tumeferaL.)在开放的气体交换系统中进行叶面试验,该系统允许在受控的环境条件下同时测量CO2、H2O和Hg°交换。当Hg°浓度保持在0.5至1.5 ng m−3时,红枫(Acer rubrum L.),挪威云杉(Picea abiesL.),黄杨(鹅掌楸),和白色栎(Quercus阿尔巴尔.)树叶的平均Hg°排放量分别为5.5、1.7、2.7和5.3 ng m− 2 h −1。当Hg°浓度在9 - 20 ng m− 3之间时,几乎没有观察到Hg°的净交换。然而,当浓度在50 - 70 ng m− 3之间时,Hg°以22 - 38 ng m− 2 h −1的速率沉积到叶子上。这些数据表明,陆地森林景观中干燥的叶面可能是一个动态交换面,可以作为源或汇,取决于当前Hg°浓度的大小。这些数据提供了证据,表明在10-25 ng m− 3的范围内,Hg°沉积到幼苗叶片上的补偿浓度(或补偿点)因物种而异。
Historical studies for crop and weed species documented elemental Hg vapor (Hg°) deposition to foliage, but they used Hg° concentrations that were orders of magnitude higher than levels now known to occur under background conditions, possibly creating artificially high gradients between the atmosphere and landscape surfaces. Measurements of Hg° exchange with white oak (Quercus albaL.), red maple (Acer rubrumL.), Norway spruce (Picea abiesL.), and yellow-poplar (Liriodendron tulipiferaL.) foliage were conducted in an open gas exchange system that allows for simultaneous measurements of CO2, H2O and Hg° exchange under controlled environmental conditions. When Hg° concentrations were held at 0.5 to 1.5 ng m−3, red maple (Acer rubrumL.), Norway spruce (Picea abiesL.), yellow-poplar (Liriodendron tulipiferaL.), and white oak (Quercus albaL.) foliage exhibited mean Hg° emissions of 5.5, 1.7, 2.7, and 5.3 ng m−2h−1, respectively. At Hg° concentrations between 9 and 20 ng m−3little net exchange of Hg° was observed. However at concentrations between 50 and 70 ng m−3the Hg° was deposited to foliage at rates between 22 and 38 ng m−2h−1. These data suggest that dry foliar surfaces in terrestrial forest landscapes may be a dynamic exchange surface that can function as a source or sink dependent on the magnitude of current Hg° concentrations. These data provide evidence of species-specific compensation concentrations (or compensation points) for Hg° deposition to seedling foliage in the 10–25 ng m−3range.