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首页> 外文期刊>International association of theoretical and applied limnoloy >Nitrogen uptake and food web nitrogen transfer in a restored urban stream compared to an unrestored urban stream and a pristine stream
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Nitrogen uptake and food web nitrogen transfer in a restored urban stream compared to an unrestored urban stream and a pristine stream

机译:与未恢复的城市溪流和原始河溪相比,恢复的城市溪流中的氮吸收和食物网中的氮转移

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Urbanization of low-order streams can cause an increase in nitrogen (N) concentration and a decrease in biotic diversity (Lenat 1993). These impacted streams are less efficient at N cycling, and have slower N uptake rates (Meyer et al. 2005). Because over $ 1 billion is spent in the United States annually to restore urbanized streams, the hydrological and biological results of stream restoration are often monitored and studied (Muotka et al. 2002). In contrast, only recently have there been studies examining changes in N retention and transport in restored streams (Bukaveckas 2007). The short-term addition of N heavy stable isotope (~(15)N) into streams can be used to measure N uptake rates (Mul-holland et al. 2002); long-term additions can trace N storage in biotic compartments and trophic interactions (Tank et al. 2000). The ~(15)N tracer additions have been shown to label stream epilithon more rapidly and at a higher level compared to detrital components and can therefore be used to estimate N uptake parameters at whole-reach scales (Mulholland et al. 2000, Wollheim et al. 2001). Based on the distribution of ~(15)N stored in the benthic epilithon, estimated N travel length and uptake rate can be compared between streams. Our aim was to determine if restoration of an urban stream increases the uptake of N into the biotic components when compared to an unrestored urban stream and a pristine Piedmont stream by conducting tracer additions of NH_4~+-~(15)N.
机译:低序河流的城市化会导致氮(N)浓度的增加和生物多样性的减少(Lenat 1993)。这些受影响的溪流在氮循环时效率较低,氮吸收速率较慢(Meyer等人,2005)。由于在美国每年花费超过10亿美元来恢复城市化的河流,因此经常对河流恢复的水文和生物学结果进行监测和研究(Muotka等,2002)。相反,直到最近,才有研究研究还原流中氮的保留和迁移的变化(Bukaveckas 2007)。短期向流中添加N重稳定同位素(〜(15)N)可用于测量N吸收率(Mul-holland等,2002)。长期添加可以追踪氮在生物区隔和营养相互作用中的含量(Tank等,2000)。与碎屑组分相比,〜(15)N示踪剂的添加已显示出更快地标记河表石,且含量更高,因此可用于估算全范围尺度的氮吸收参数(Mulholland等,2000; Wollheim等。 (2001)。根据底栖上层沉积物中〜(15)N的分布,可以比较溪流之间的估计N传播长度和吸收速率。我们的目标是通过进行示踪剂添加NH_4〜+-〜(15)N来确定与未还原的城市溪流和原始的皮埃蒙特溪流相比,城市溪流的恢复是否增加了N对生物成分的吸收。

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