Lefebvre S, Clément J C, Pinay G, Thenail C, Durand P, Marmonier P
ECOBIO-Unité Mixte de Recherche, 6553 CNRS, Institut Fédératif de Recherche CAREN, Université de Rennes I, Campus de Beaulieu, 35042 Rennes, France.
Ecol Appl. 2007 Dec;17(8):2333-46. doi: 10.1890/06-1496.1.
Many studies have shown that intensive agricultural practices significantly increase the nitrogen concentration of stream surface waters, but it remains difficult to identify, quantify, and differentiate between terrestrial and in-stream sources or sinks of nitrogen, and rates of transformation. In this study we used the delta15N-NO3 signature in a watershed dominated by agriculture as an integrating marker to trace (1) the effects of the land cover and agricultural practices on stream-water N concentration in the upstream area of the hydrographic network, (2) influence of the in-stream processes on the NO3-N loads at the reach scale (100 m and 1000 m long), and (3) changes in delta15N-NO3 signature with increasing stream order (from first to third order). This study suggests that land cover and fertilization practices were the major determinants of delta15N-NO3 signature in first-order streams. NO3-N loads and delta15N-NO3 signature increased with fertilization intensity. Small changes in delta15N-NO3 signature and minor inputs of groundwater were observed along both types of reaches, suggesting the NO3-N load was slightly influenced by in-stream processes. The variability of NO3-N concentrations and delta15N signature decreased with increasing stream order, and the delta15N signature was positively correlated with watershed areas devoted to crops, supporting a dominant effect of agriculture compared to the effect of in-stream N processing. Consequently, land cover and fertilization practices are integrated in the natural isotopic signal at the third-order stream scale. The GIS analysis of the land cover coupled with natural-abundance isotope signature (delta15N) represents a potential tool to evaluate the effects of agricultural practices in rural catchments and the consequences of future changes in management policies at the regional scale.
许多研究表明,集约化农业活动显著提高了河流表层水体的氮浓度,但要确定、量化并区分陆地和河流中的氮源或氮汇以及氮的转化速率仍很困难。在本研究中,我们将农业主导流域中的δ15N-NO3特征作为一个综合标记,以追踪:(1)土地覆盖和农业活动对水系网络上游区域河流水体氮浓度的影响;(2)河流过程对河段尺度(100米和1000米长)的硝酸氮负荷的影响;以及(3)随着河流等级增加(从一级到三级)δ15N-NO3特征的变化。本研究表明,土地覆盖和施肥活动是一级溪流中δ15N-NO3特征的主要决定因素。硝酸氮负荷和δ15N-NO3特征随施肥强度的增加而增加。在两种类型的河段上都观察到δ15N-NO3特征的微小变化和地下水的少量输入,这表明硝酸氮负荷受河流过程的影响较小。硝酸氮浓度和δ15N特征的变异性随河流等级的增加而降低,并且δ15N特征与种植作物的流域面积呈正相关,这表明与河流中氮处理的影响相比,农业的影响占主导地位。因此,土地覆盖和施肥活动在三级溪流尺度上被整合到自然同位素信号中。将土地覆盖的GIS分析与自然丰度同位素特征(δ15N)相结合,是评估农村集水区农业活动影响以及区域尺度上未来管理政策变化后果的潜在工具。