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首页> 外文期刊>Journal of Geophysical Research. Biogeosciences >Factors controlling temporal and spatial distribution of total mercury and methylmercury in hyporheic sediments of the Allequash Creek wetland, northern Wisconsin
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Factors controlling temporal and spatial distribution of total mercury and methylmercury in hyporheic sediments of the Allequash Creek wetland, northern Wisconsin

机译:威斯康星州北部Allequash Creek湿地低水沉积物中总汞和甲基汞的时空分布控制因素

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Hyporheic pore water samples were collected from two sites within the Allequash Creek wetland, in Vilas County, northern Wisconsin, from August 2003 to October 2004. Samples were collected simultaneously at the surface and at 2, 5, 7, 10, and 15 cm below the sediment-water interface. Concentration ranges were 3.7 to 58 pM for inorganic mercury, < 0.5 to 16 pM for methylmercury, 3.02 to 152 mu M and 0.38 to 96.6 mu M for oxidized and reduced iron, respectively, 1.28 to 48.2 mu M and< 0.05 to 9.76 mu M for oxidized and reduced sulfur, respectively, and 109 to 689 mu M for dissolved organic carbon. These concentrations are typical of anoxic environments such as wetlands and lake sediments. These data were used to gain a better understanding of the processes controlling spatial and temporal variability of inorganic mercury and methylmercury. Findings show that conditions conducive to mercury methylation exist in the hyporheic zone, especially in late summer, when accumulation of reduced iron and sulfide are indicative of microbial iron and sulfate reduction. Methylmercury concentrations also peak in late summer, with the highest concentrations appearing 2 to 10 cm below the sediment-water interface. While there is a general covariance of total mercury and methylmercury over the depth profile, poor correlation was observed over time, highlighting the dynamic nature of hyporheic zone conditions and suggesting changes in mercury speciation and partitioning.
机译:从2003年8月至2004年10月,从威斯康星州北部维拉斯县的Allequash Creek湿地的两个地点采集了亲水性孔隙水样品。同时在地表以及下方2、5、7、10和15 cm处采集了样品沉积物-水界面。无机汞的浓度范围为3.7至58 pM,甲基汞的浓度范围为<0.5至16 pM,氧化铁和还原铁的浓度范围为3.02至152μM和0.38至96.6μM,分别为1.28至48.2μM和<0.05至9.76μM分别用于氧化硫和还原硫,溶解有机碳为109至689μM。这些浓度是典型的缺氧环境,例如湿地和​​湖泊沉积物。这些数据被用来更好地理解控制无机汞和甲基汞的时空变化的过程。研究结果表明,在流变带中存在有利于汞甲基化的条件,尤其是在夏末,还原铁和硫化物的积累表明微生物体内铁和硫酸盐的还原。甲基汞浓度也在夏末达到峰值,最高浓度出现在沉积物-水界面以下2至10厘米处。尽管总的汞和甲基汞在深度剖面上存在一般的协方差,但随着时间的推移,相关性很差,这突出说明了流变带条件的动态性质,并暗示了汞形态和分配的变化。

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