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Capturing interactions between nitrogen and hydrological cycles under historical climate and land use: Susquehanna watershed analysis with the GFDL land model LM3-TAN

机译:在历史气候和土地利用下捕获氮与水文循环之间的相互作用:使用GFDL土地模型LM3-TAN的Susquehanna流域分析

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We developed a process model LM3-TAN to assess the combined effects of directhuman influences and climate change on terrestrial and aquatic nitrogen (TAN)cycling. The model was developed by expanding NOAA's Geophysical FluidDynamics Laboratory land model LM3V-N of coupled terrestrial carbon andnitrogen (C-N) cycling and including new N cycling processes and inputs suchas a soil denitrification, point N sources to streams (i.e., sewage), andstream transport and microbial processes. Because the model integratesecological, hydrological, and biogeochemical processes, it captures keycontrols of the transport and fate of N in the vegetation–soil–river system in acomprehensive and consistent framework which is responsive to climaticvariations and land-use changes. We applied the model at 1/8°resolution for a study of the Susquehanna River Basin. We simulated withLM3-TAN stream dissolved organic-N, ammonium-N, and nitrate-N loadsthroughout the river network, and we evaluated the modeled loads for1986–2005 using data from 16 monitoring stations as well as a reported budgetfor the entire basin. By accounting for interannual hydrologic variability,the model was able to capture interannual variations of stream N loadings.While the model was calibrated with the stream N loads only at the lastdownstream Susquehanna River Basin Commission station Marietta (40°02' N,76°32' W), it captured the N loads well atmultiple locations within the basin with different climate regimes, land-usetypes, and associated N sources and transformations in the sub-basins.Furthermore, the calculated and previously reported N budgets agreed well atthe level of the whole Susquehanna watershed. Here we illustrate how pointand non-point N sources contributing to the various ecosystems are stored,lost, and exported via the river. Local analysis of six sub-basins showedcombined effects of land use and climate on soil denitrification rates, withthe highest rates in the Lower Susquehanna Sub-Basin (extensive agriculture;Atlantic coastal climate) and the lowest rates in the West Branch SusquehannaSub-Basin (mostly forest; Great Lakes and Midwest climate). In the re-growingsecondary forests, most of the N from non-point sources was stored in thevegetation and soil, but in the agricultural lands most N inputs were removedby soil denitrification, indicating that anthropogenic N applications coulddrive substantial increase of N2O emission,an intermediate of the denitrification process.
机译:我们开发了一个过程模型LM3-TAN来评估人类直接影响和气候变化对陆地和水生氮(TAN)循环的综合影响。该模型是通过扩展NOAA的地球物理碳氮循环(CN)循环的LM3V-N陆地模型LM3V-N而开发的,该模型包括新的N循环过程和输入,例如土壤反硝化,将N点污染到河流(即污水)和河流运输和微生物过程。因为该模型整合了生物学,水文和生物地球化学过程,所以它在一个全面,一致的框架中捕获了植被-土壤-河流系统中氮的运输和命运的关键控制,该框架响应气候变化和土地利用变化。我们将模型以1/8°的分辨率应用于Susquehanna流域的研究。我们使用LM3-TAN流模拟了整个河网中溶解的有机氮,铵态氮和硝态氮的负荷,并使用来自16个监测站的数据以及整个流域的报告预算评估了1986-2005年的模拟负荷。通过考虑年际水文变异性,该模型能够捕获N流的年际变化。尽管仅在Susquehanna流域委员会下游玛丽埃塔(40°02'N,76°32 W),它捕获了流域内多个位置的N负荷,这些位置具有不同的气候制度,土地利用类型以及子流域中的相关N来源和转换。此外,计算得出的和先前报告的N预算在整个萨斯奎哈那集水区。在这里,我们说明了对各种生态系统有贡献的点和非点氮源如何通过河流进行存储,丢失和出口。对六个子流域的本地分析表明,土地利用和气候对土壤反硝化率的综合影响是,下萨斯奎汉纳次流域的比率最高(广泛的农业;大西洋沿海气候),而西分支萨斯奎汉纳次流域的比率最低(大部分为森林;大湖区和中西部气候)。在重生的次生林中,来自非点源的大部分N都存储在植被和土壤中,但是在农业土地中,大多数N的输入都通过土壤反硝化作用去除,这表明人为的N施用可以推动N 2的大量增加。 O排放,反硝化过程的中间产物。

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