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Biological and Photochemical Degradation of Dissolved Organic Carbon in Peatland Ecosystems

机译:泥炭地生态系统中溶解有机碳的生物和光化学降解

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摘要

Approximately one half of terrestrial carbon runoff is processed by inland waters and released into the atmosphere as carbon dioxide (CO2) prior to reaching the oceans, and bacterial consumption of dissolved organic carbon (DOC) comprises a dominant proportion of this carbon loss. Though peatlands export more DOC per area than most other ecosystems, the sources and biodegradability of peatland DOC and their effects on downstream DOC loads and fluxes are poorly understood. Moreover, photochemical degradation plays an important role in the loss of carbon from aquatic ecosystems, especially in peatlands with high DOC concentrations rich in photochemically reactive humic and phenolic compounds, but its contribution to global CO2 evasion from inland waters has not been quantified. This dissertation focuses on predictors of biodegradable DOC (BDOC) in aquatic ecosystems, the sources and biodegradability of DOC in peatland watersheds, and the contribution of photochemical degradation of DOC to global CO2 evasion from peatlands and fluvial ecosystems. Key findings from these studies were that SUVA, a measurement broadly used in ecology and environmental engineering and fairly simple to obtain, is an excellent predictor of the amount of long-term BDOC concentrations in Minnesota lake ecosystems. The peatland bog may be the most important source of BDOC exported from peatlands annually, rather than the upland. And, photochemical enhancement of bacterial respiration in peatland and fluvial ecosystems contributes approximately 0.11--0.22 Pg C yr-1 to the total global CO2 evasion from inland waters (∼1.4 Pg C yr-1), or 9--18% of all inland water CO2 evasion. The results from this dissertation will lend insight into how future changes in hydrology and surface water DOC concentrations will alter the sources, biodegradability, and photochemical enhancement of DOC in aquatic ecosystems in the northern hemisphere, especially peatlands.
机译:陆地碳径流的大约一半由内陆水处理,并在到达海洋之前以二氧化碳(CO2)的形式释放到大气中,细菌消耗的溶解性有机碳(DOC)构成了碳损失的主要部分。虽然泥炭地每面积的DOC出口量比大多数其他生态系统要多,但人们对泥炭地DOC的来源和生物降解性及其对下游DOC负荷和通量的影响知之甚少。此外,光化学降解在水生生态系统的碳损失中起着重要作用,特别是在DOC浓度高,富含光化学反应性腐殖质和酚类化合物的泥炭地中,但其对内陆水域全球CO2逃逸的贡献尚未量化。本文着重研究水生生态系统中可降解DOC(BDOC)的预测因子,泥炭地流域中DOC的来源和可生物降解性以及DOC的光化学降解对泥炭地和河流生态系统全球CO2逃逸的贡献。这些研究的主要发现是,SUVA是在生态和环境工程中广泛使用的一种测量方法,相当容易获得,可以很好地预测明尼苏达州湖泊生态系统中长期BDOC浓度。泥炭地沼泽可能是每年从泥炭地而不是高地出口的BDOC的最重要来源。而且,通过光化学方法增强泥炭地和河流生态系统中细菌的呼吸作用,对内陆水域的全球总CO2排放量(约1.4 Pg C yr-1)贡献了约0.11-0.22 Pg Cyr-1,占总数的9--18%内陆二氧化碳逃逸。这篇论文的结果将有助于深入了解北半球特别是泥炭地水生生态系统未来水文学和地表水DOC浓度的变化将如何改变DOC的来源,生物降解性和光化学强度。

著录项

  • 作者单位

    University of Minnesota.;

  • 授予单位 University of Minnesota.;
  • 学科 Ecology.
  • 学位 Ph.D.
  • 年度 2012
  • 页码 99 p.
  • 总页数 99
  • 原文格式 PDF
  • 正文语种 eng
  • 中图分类
  • 关键词

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