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Mercury dynamics in a small Northern Minnesota lake: water to air exchange and photoreactions of mercury

机译:明尼苏达州北部一个小湖中的汞动力学:水与空气的交换和汞的光反应

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摘要

Mercury speciation at a small seepage lake in Northern Minnesota was shown to be influenced by photoreduction and photooxidation. Fluxes of Hg~0 from water to air were greatest in the warmer, sunnier months in 2001 to 2002; however, correlation with solar radiation was weak. The daytime evasional loss was generally from water to air and was estimated at 5.3 pmol m~(-2) h~(-1) for 2001 and 6.2 pmol m~(-2)h~(-1) for 2002 using a two-layer gas transfer model. Losses of Hg_((aq))~0 in the dark over 10 days were observed in lake water (0.02 h~(-1)), Milli-Q~(TM) water, and HPLC grade water (0.002 h~(-1)) and agreed with reported pseudo-first-order loss rates in the dark in other freshwaters. Using a mercury arc lamp, the pseudo-first-order loss rate of Hg~0 in water from Spring Lake was found to range from 0.39 to 0.76 h~(-1). Other sinks for Hg~0 exist through reaction with ozone, hydroxyl radical, and possibly singlet oxygen. A second-order reaction rate constant for Hg_((aq))~0 and ~·OH of 1.0 x 10~9 M~(-1) s~(-1) was estimated based on data from experiments and the literature. Although less reactive, there is a higher steady state concentration of ozone in lake water compared to hydroxyl radical. Consequently, loss of Hg_((aq))~0 by ozone may predominate. Potential oxidation of Hg_((aq))~0 by singlet oxygen using rose bengal as a sensitizer could not distinguish between oxidation by rose bengal and by singlet oxygen itself. Chloride enhanced the oxidation of Hg_((aq))~0 and should be considered in the mercury cycle in the ocean.
机译:明尼苏达州北部一个小渗漏湖中的汞形态受到光还原和光氧化的影响。从2001年到2002年,在温暖,阳光充足的月份,Hg〜0从水到空气的通量最大。但是,与太阳辐射的相关性很弱。白天的逸散损失通常是从水到空气,估计2001年为5.3 pmol m〜(-2)h〜(-1),2002年为6.2 pmol m〜(-2)h〜(-1),使用两个层气体传输模型。在湖水(0.02 h〜(-1)),Milli-Q〜TM水和HPLC级水(0.002 h〜(-)中,在10天内黑暗中Hg _((aq))〜0的损失被观察到1)),并同意其他淡水在黑暗中报告的伪一级损失率。使用汞弧灯,发现Spring Lake水中Hg〜0的假一阶损失率为0.39至0.76h〜(-1)。通过与臭氧,羟基自由基和可能的单线态氧反应而存在Hg〜0的其他吸收剂。基于实验和文献数据估计Hg _((aq))〜0和〜·OH的二阶反应速率常数为1.0 x 10〜9 M〜(-1)s〜(-1)。尽管反应性较低,但与羟基自由基相比,湖水中的臭氧稳态浓度更高。因此,可能会导致臭氧损失Hg _((aq))〜0。以玫瑰红为敏化剂的单重态氧对Hg _((aq))〜0的潜在氧化作用无法区分玫瑰红对向的氧化和单重态氧本身的氧化。氯化物增强了Hg _((aq))〜0的氧化,应在海洋的汞循环中考虑。

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