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Patterns of nitrogen fluxes in watersheds of the H. J. Andrews Experimental Forest, Oregon.

机译:俄勒冈州H.J.安德鲁斯实验森林的流域中氮通量的模式。

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摘要

Seasonal and annual patterns of N fluxes and concentrations in streamwater in six conifer-dominated watersheds at the H. J. Andrews Experimental Forest, OR, were studied to gain insight into the factors that influence N retention in this ecosystem. Processes affecting N flux in streamwater differed between organic (DON) and inorganic (DIN; NO3-N and NH4-N) forms of N. Annual DON flux increased with increasing annual discharge in all watersheds, implying that regional-level climatic fluctuations may influence DON retention. Annual DIN flux, in contrast, was not consistently related to annual stream discharge. DON concentrations in stream water peaked in winter before the peak in the hydrograph, suggesting that DON may be flushed from the soil into the stream. Concentrations of DIN were relatively constant throughout the year.; Annual and seasonal patterns of N retention were calculated using three separate estimates of N inputs to this ecosystem: (1) atmospheric DIN alone, (2) atmospheric DIN + DON, and (3) atmospheric DIN + DON + inputs from biological fixation. Vegetation demand for N had little effect on annual DIN retention, perhaps because inputs of DIN to the Andrews Forest and periods of forest growth are asynchronous. High inputs of biologically-fixed N did not result in increased nitrate leaching, suggesting that biologically-fixed N is efficiently retained in this ecosystem.; Forest harvest at the Andrews resulted in very small losses of N from the soil relative to other sites. The high C:N ratio of soil at the Andrews Forest probably promotes immobilization of N after harvest, and little of the N released by decomposing roots or made available via reduced vegetation demand escapes the soil microbial community.
机译:在俄勒冈州H. J.安德鲁斯实验森林的六个针叶树为主的流域,研究了溪流中氮通量的季节性和年度模式,以了解影响该生态系统中氮保留的因素。影响河流水中氮通量的过程在有机(DON)和无机(DIN; NO3-N和NH4-N)形式的氮之间有所不同。所有流域的年度DON通量都随着年排放量的增加而增加,这表明区域性气候波动可能会影响唐保留。相比之下,年度DIN通量与年度溪流排放量并不一致。溪流水中的DON浓度在冬季在水文图的峰值之前达到峰值,这表明DON可能从土壤冲入溪流。全年中,DIN的浓度相对恒定。使用对该生态系统的N输入的三个单独估计来计算N保留的年度和季节性模式:(1)仅大气DIN,(2)大气DIN + DON,以及(3)大气DIN + DON +来自生物固定的输入。植被对氮的需求对每年的DIN保留几乎没有影响,这可能是因为对Andrews森林的DIN输入和森林生长周期是异步的。高生物固定氮的投入并不会增加硝酸盐的淋失,这表明生物固定氮有效地保留在该生态系统中。与其他地点相比,安德鲁斯的森林砍伐导致土壤中氮的损失非常小。在安德鲁斯森林中,土壤高的C:N比值​​可能促进了氮素在收获后的固定化,而分解根部释放出来的氮素或由于减少的植被需求而提供的氮素很少能逃脱土壤微生物群落。

著录项

  • 作者

    Vanderbilt, Kristin L.;

  • 作者单位

    Oregon State University.;

  • 授予单位 Oregon State University.;
  • 学科 Agriculture Forestry and Wildlife.; Biology Ecology.
  • 学位 Ph.D.
  • 年度 2001
  • 页码 110 p.
  • 总页数 110
  • 原文格式 PDF
  • 正文语种 eng
  • 中图分类 森林生物学;生态学(生物生态学);
  • 关键词

  • 入库时间 2022-08-17 11:46:52

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