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Tracing Nitrate-Nitrogen Sources and Modifications in a Stream Impacted by Various Land Uses, South Portugal

机译:在南葡萄牙,在受到各种土地利用影响的河流中追踪硝酸盐氮源及其变质

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The identification of nitrate-nitrogen (NO 3 –N) origin is important in the control of surface and ground water quality. These are the main sources of available drinking water. Stable isotopes ( 15 N and 18 O) for NO 3 –N and along with a 1-D reactive transport model were used to study the origin and processes that lead to nitrogen transformation and loss in a major stream that flows into a reservoir within an intensively cultivated catchment area (352 km 2 ) in Alentejo-Portugal. Seasonal water samples (October–November 2008, March 2009 and September 2009) of stream surface water, wells and sediment pore water were collected. The results showed consistently increasing isotope values and decreasing NO 3 –N concentrations downstream. During winter (wet period, November 2008 and March 2009) slightly higher NO 3 –N concentrations were found in comparison to early fall (dry period: October 2008) and summer (dry period: September 2009). Isotopic composition of 15 N and 18 O values in surface water samples from the stream and wells indicated that the dominant NO 3 –N sources were derived mainly from the soil and fertilizers. There was also significant nitrification in surface water at the head of the stream. Sediment pore waters showed high NO 3 –N values near the sediment-water interface (reaching 25 mg·N·L ?1 ) and NO 3 –N concentrations sharply decreasing with sediment depth, suggesting significant NO 3 –N consumption. Denitrification was also detected using the 15 N signature in upstream waters, but not downstream where very low NO 3 –N levels were measured. In the stream, the calculated isotopic enrichment factor for NO 3 –N was ?2.9‰ for 15 N and ?1.78 for 18 O, this indicates that denitrification accounts for 7.8% to 48% of nitrate removal.
机译:识别硝酸盐氮(NO 3 -N)的来源对于控制地表水和地下水的质量很重要。这些是可用饮用水的主要来源。用于NO 3 -N的稳定同位素(15 N​​和18 O)以及一维反应性传输模型被用于研究导致氮转化和流失的主要来源的过程和过程。阿连特茹-葡萄牙集约化集水区(352 km 2)。收集了溪流地表水,井和沉积物孔隙水的季节性水样(2008年10月至11月,2009年3月和2009年9月)。结果表明,同位素值不断增加,下游NO 3 -N浓度不断降低。在冬季(2008年11月和2009年3月的潮湿时期),NO 3 -N的浓度与秋季(干旱时期:2008年10月)和夏季(干旱时期:2009年9月)相比略高。河流和水井的地表水样品中15 N和18 O值的同位素组成表明,主要的NO 3 -N来源主要来自土壤和肥料。溪水顶部的地表水中也有明显的硝化作用。沉积物孔隙水在沉积物-水界面附近显示较高的NO 3 -N值(达到25 mg·N·L?1),NO 3 -N浓度随沉积物深度而急剧下降,表明大量消耗NO 3 -N。还使用15 N信号在上游水域中检测到反硝化作用,但在下游水域中测得的NO 3 -N水平非常低的情况下未检测到。在该流中,计算得出的15 N中NO 3 -N的同位素富集系数为?2.9‰,而18 O中为?1.78,这表明反硝化作用占硝酸盐去除量的7.8%至48%。

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