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首页> 外文期刊>Water resources research >Denitrification in the banks of fluctuating rivers: The effects of river stage amplitude, sediment hydraulic conductivity and dispersivity, and ambient groundwater flow
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Denitrification in the banks of fluctuating rivers: The effects of river stage amplitude, sediment hydraulic conductivity and dispersivity, and ambient groundwater flow

机译:脉动河岸的反硝化作用:河段幅度,沉积物水力传导率和分散性以及周围地下水流量的影响

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Hyporheic exchange induced by periodic river fluctuations leads to important biogeochemical processes, particularly nitrogen cycling, in riparian zones (RZs) where chemically distinct surface water and groundwater mix. We developed a two-dimensional coupled flow, reactive transport model to study the role of bank storage induced by river fluctuations on removing river-borne nitrate. Sensitivity analyses were conducted to quantify the effects of river amplitude, sediment hydraulic conductivity and dispersivity, and ambient groundwater flow on nitrate removal rate. The simulations showed that nitrification occurred in the shallower zone adjacent to the bank where oxic river water and groundwater interacted while denitrification occurred deeper into the aquifer and in the riverbed sediments where oxygen was depleted. River fluctuations greatly increased the amount of nitrate being removed; the nitrate removal rate increased as river amplitude increased. Similarly, increasing hydraulic conductivity increased overall nitrate removal since it expanded the denitrifying zone but decreased efficiency. In contrast, increasing sediment dispersivity increased the removal efficiency of nitrate because it promoted mixing between electron acceptors and donors. The presence and direction of ambient groundwater flow had a significant impact on nitrate removal rate when compared to neutral conditions. A losing river showed a larger nitrate removal rate, whereas a gaining river showed a smaller nitrate removal rate. Our results demonstrated that daily river fluctuations created denitrification hot spots within the RZ that would not otherwise exist under naturally neutral or gaining conditions.
机译:周期性河水波动引起的羟交换导致重要的生物地球化学过程,特别是在沿河带(RZs)中氮的循环,在沿岸带化学上不同的地表水和地下水混合。我们开发了一个二维耦合流动反应运输模型,以研究由河水波动引起的河岸存储在去除河中硝酸盐中的作用。进行了敏感性分析,以量化河流幅度,沉积物水力传导率和分散性以及周围地下水流量对硝酸盐去除率的影响。模拟结果表明,硝化作用发生在与河床相邻的较浅区域,在这里河水和地下水之间发生相互作用,反硝化作用发生在含水层的较深处以及氧被耗尽的河床沉积物中。河流的波动大大增加了硝酸盐的去除量;硝酸盐去除率随河道幅度的增加而增加。同样,增加水力传导率会增加总硝酸盐的去除量,因为它扩大了反硝化区,但降低了效率。相反,增加沉积物的分散性会提高硝酸盐的去除效率,因为它促进了电子受体与施主之间的混合。与中性条件相比,周围地下水流的存在和方向对硝酸盐去除率有重要影响。流失的河水的硝酸盐去除率较高,而流经的河水的硝酸盐去除率较小。我们的结果表明,每天的河水波动在RZ内造成了反硝化热点,而在自然中性或收益条件下原本不会存在。

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