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首页> 外文期刊>Journal of Geophysical Research. Biogeosciences >The Evolution of Sulfide in Shallow Aquatic Ecosystem Sediments: An Analysis of the Roles of Sulfate, Organic Carbon, and Iron and Feedback Constraints Using Structural Equation Modeling
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The Evolution of Sulfide in Shallow Aquatic Ecosystem Sediments: An Analysis of the Roles of Sulfate, Organic Carbon, and Iron and Feedback Constraints Using Structural Equation Modeling

机译:浅水生生态系统沉积物中硫化物的演变 - 硫酸盐,有机碳和铁的作用,使用结构方程模型分析

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The generation of elevated concentrations of sulfide in sediment pore waters that are toxic to rooted macrophytes is problematic in both marine and freshwaters. In marine waters, biogeochemical conditions that lead to toxic levels of sulfide generally relate to factors that affect oxygen dynamics or the sediment iron concentration. In freshwaters, increases in surface water sulfate have been implicated in decline of Zizania palustris (wild rice), which is important in wetlands across the Great Lakes region of North America. We developed a structural equation (SE) model to elucidate key variables that govern the evolution of sulfide in pore waters in shallow aquatic habitats that are potentially capable of supporting wild rice. The conceptual basis for the model is the hypothesis that dissimilatory sulfate reduction is limited by the availability of both sulfate and total organic carbon (TOC) in the sediment. The conceptual model also assumes that pore water sulfide concentrations are constrained by the availability of pore water iron and that sediment iron supports the supply of dissolved iron to the pore water. A key result from the SE model is that variations in three external variables (sulfate, sediment TOC, and sediment iron) contribute nearly equally to the observed variations in pore water sulfide. As a result, management efforts to mitigate against the toxic effects of pore water sulfide on macrophytes such as wild rice should approach defining a protective sulfate threshold as an exercise tailored to the geochemistry of each site that quantitatively considers the effects of ambient concentrations of sediment Fe and TOC.
机译:在海洋和新鲜水域中产生毒性孔隙水中的沉积物孔隙水中硫化物浓度的产生是有问题的。在海水中,导致硫化物水平的生物地球化学条件通常涉及影响氧动力学或沉积物铁浓度的因素。在淡水中,表面水硫酸盐的增加涉及Zizania Palustris(野生稻)的下降,这在北美大湖区的湿地中很重要。我们开发了一种结构方程(SE)模型,以阐明临时变量,该模型在浅水中栖息地在浅水中栖息地中硫化物中的脉冲的演变。该模型的概念依据是解析硫酸化硫酸盐的假设受沉积物中硫酸盐和总有机碳(TOC)的可用性的限制。概念模型还假定孔水硫化物浓度受到孔隙水的可用性而受到限制,并且该沉积物支持将溶解铁供应到孔隙水。 SE模型的一个关键结果是三个外部变量(硫酸盐,沉积物TOC和沉积物铁)的变化几乎促进了观察到的孔水硫化物的变化。因此,管理努力减轻孔水硫化物对野生稻等宏观物质的毒性作用的努力,这些方法应该定义保护性硫酸盐阈值,作为定量定量的地球化学地球化学的运动,这些植物数量地认为环境浓度的沉积物Fe的影响和toc。

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