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Nitrogen biogeochemistry in the Adirondack Mountains of New York: hardwood ecosystems and associated surface waters

机译:纽约阿迪朗达克山脉的氮生物地球化学:硬木生态系统和相关的地表水

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Studies on the nitrogen (N) biogeochemistry in Adirondack northern hardwood ecosystems were summarized. Specific focus was placed on results at the Huntington Forest (HFS), Pancake-Hall Creek (PHC), Woods Lake (WL), Ampersand (AMO), Catlin Lake (CLO) and Hennessy Mountain (HM). Nitrogen deposition generally decreased from west to east in the Adirondacks, and there have been no marked temporal changes in N deposition from 1978 through 1998. Second-growth western sites (WL, PHC) had higher soil solution NO3- concentrations and fluxes than the HFS site in the central Adirondacks. Of the two old-growth sites (AMO and CLO), AMO had substantially higher NO3- concentrations due to the relative dominance of sugar maple that produced litter with high N mineralization and nitrification rates. The importance of vegetation in affecting N losses was also shown for N-fixing alders in wetlands. The Adirondack Manipulation and Modeling Project (AMMP) included separate experimental N additions of (NH4)(2)SO4 at WL, PHC and HFS and HNO3 at WL and HFS. Patterns of N loss varied with site and form of N addition and most of the N input was retained. For 16 lake/watersheds no consistent changes in NO3- concentrations were found from 1982 to 1997. Simulations suggested that marked NO3- loss will only be manifested over extended periods. Studies at the Arbutus Watershed provided information on the role of biogeochemical and hydrological factors in affecting the spatial and temporal patterns of NO3- concentrations. The heterogeneous topography in the Adirondacks has generated diverse landscape features and patterns of connectivity that are especially important in regulating the temporal and spatial patterns of NO3- concentrations in surface waters. (C) 2003 Elsevier Science Ltd. All rights reserved. [References: 45]
机译:总结了阿迪朗达克北部硬木生态系统中氮(N)生物地球化学的研究。重点放在亨廷顿森林(HFS),薄煎饼霍尔溪(PHC),伍兹湖(WL),安培山(AMO),卡特林湖(CLO)和轩尼诗山(HM)的结果上。 1978年至1998年,阿迪朗达克山脉的氮沉降总体上从西向东减少,并且从1978年到1998年氮沉降没有明显的变化。西部生长的西部站点(WL,PHC)的土壤溶液NO3-浓度和通量高于HFS在阿迪朗达克山脉中部。在两个老生长地点(AMO和CLO)中,AMO的NO3-浓度要高得多,这是由于糖枫的相对优势所致,该枫糖产生了具有较高N矿化和硝化率的凋落物。对于湿地固氮al木,植被对影响氮素损失的重要性也得到了证明。阿迪朗达克操作和建模项目(AMMP)包括分别在WL,PHC和HFS处分别添加(NH4)(2)SO4和NNO3在WL和HFS处的实验N。氮素流失的方式随氮素添加部位和形式的变化而变化,大部分氮素输入被保留。从1982年到1997年,对于16个湖泊/流域,没有发现NO3-浓度的一致变化。模拟表明,明显的NO3-损失只会在较长时期内表现出来。 Arbutus流域的研究提供了有关生物地球化学和水文因素在影响NO3-浓度的时空格局中的作用的信息。阿迪朗达克山脉的异质地形产生了多种多样的景观特征和连通性格局,这对于调节地表水中NO3-浓度的时空格局尤其重要。 (C)2003 Elsevier ScienceLtd。保留所有权利。 [参考:45]

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