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Stream-aquifer and in-stream processes affecting nitrogen along a major river and contributing tributary

机译:沿主要河流的氮影响着支流的含水层和河流过程

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This study assesses the spatio-temporal patterns of water and nutrient mass exchange in a stream-riparian system of a major river and a contributing tributary in an irrigated semi-arid region. Field monitoring is performed along reaches of the Arkansas River (4.7 km) and Timpas Creek (2.0 km) in southeastern Colorado during the 2014 growing season, with water quantity and water quality data collected using a network of in-stream sampling sites and groundwater monitoring wells. Mass balance approaches were used to identify temporal and spatial trends in flow, nitrogen (N), and salinity in stream-aquifer exchange. In the Arkansas River, percent decrease of N concentration along the study reach averaged 36% over the period, with results from a stochastic mass balance simulation indicating a 90% probability that 44% to 50% of NO3-N mass in the study reach (109-124 kg/day/km) was removed by in-stream processes between 1 September and 8 November. Results suggest that contact with organic-rich river bed sediments has a strong impact on N removal. A greater decrease in concentrations of NO3-N along the reach during the low flow period suggests the effect of both in-stream processes and dilution by inflowing groundwater that undergoes denitrification as it flows through the riparian and hyporheic zones into the river. In contrast, N concentration decreases in the smaller Timpas Creek were negligible. Results for the Arkansas River also are in contrast with other large agriculturally-influenced rivers, which have not exhibited capacity to remove N at significant rates. Results provide important insights across spatial and temporal scales and point to the need for investigating nutrient dynamics in large streams draining agriculturally-dominated watersheds. (C) 2017 Elsevier B.V. All rights reserved.
机译:这项研究评估了主要河流和半干旱灌溉支流的河岸系统中水和营养物质交换的时空格局。在2014年生长季节期间,对科罗拉多州东南部的阿肯色河(4.7 km)和蒂帕斯河(2.0 km)的河段进行了野外监测,并利用河内采样点和地下水监测网络收集了水量和水质数据井。质量平衡方法用于确定流-含水层交换中流量,氮(N)和盐度的时间和空间趋势。在阿肯色河中,研究期间氮浓度的平均下降百分比在此期间平均达到36%,随机质量平衡模拟结果表明,研究中NO3-N的质量达到44%至50%的可能性为90%(在9月1日至11月8日之间通过插播流程删除了109-124 kg / day / km)。结果表明,接触富含有机物的河床沉积物对脱氮有很大影响。在低流量时期,沿河段NO3-N浓度的较大降低表明,流入河水的过程和稀释作用都受到流入地下水的影响,当地下水流过河岸和水流带进入河中时,该地下水经过反硝化作用。相反,较小的Timpas Creek中的N浓度降低可忽略不计。阿肯色河的结果也与其他大型农业影响河流形成鲜明对比,后者没有表现出以显着速率去除氮的能力。结果提供了跨时空尺度的重要见解,并指出有必要调查排泄以农业为主的流域的大溪流中的营养动态。 (C)2017 Elsevier B.V.保留所有权利。

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