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淡水沉积物中硝化和反硝化耦合的模拟模型。

Simulation Model of the Coupling between Nitrification and Denitrification in a Freshwater Sediment.

机构信息

Department of Microbial Ecology, Institute of Biological Sciences, University of Aarhus, Ny Munkegade, DK-8000 Aarhus C, Denmark.

出版信息

Appl Environ Microbiol. 1994 Sep;60(9):3089-95. doi: 10.1128/aem.60.9.3089-3095.1994.

Abstract

A model was constructed to simulate the results of experiments which investigated nitrification and denitrification in the freshwater sediment of Lake Vilhelmsborg, Denmark (K. Jensen, N. P. Sloth, N. Risgaard-Petersen, S. Rysgaard, and N. P. Revsbech, Appl. Environ. Microbiol. 60:2094-2100, 1994). The model output faithfully represented the profiles of O(2) and NO(3) and rates of nitrification, denitrification, and O(2) consumption as the O(2) concentration in the overlying water was increased from 10 to 600 muM. The model also accurately predicted the response, to increasing O(2) concentrations, of the integrated (micromoles per square meter per hour) rates of nitrification and denitrification. The simulated rates of denitrification of NO(3) diffusing from the overlying water (D(w)) and of NO(3) generated by nitrification within the sediment (D(n)) corresponded to the experimental rates as the O(2) concentration in the overlying water was altered. The predicted D(w) and D(n) rates, as NO(3) concentration in the overlying water was changed, closely resembled those determined experimentally. The model was composed of 41 layers 0.1 mm thick, of which 3 represented the diffusive boundary layer in the water. Large first-order rate constants for nitrification and denitrification were required to completely oxidize all NH(4) diffusing from the lower sediment layers and to remove much of the NO(3) produced. In addition to the flux of NH(4) from below, the model required a flux of an electron donor, possibly methane. Close coupling between nitrification and denitrification, achieved by allowing denitrification to tolerate some O(2) ( approximately 10 muM), was necessary to reproduce the real data. Spatial separation of the two processes (no toleration by denitrification of O(2)) resulted in too high NO(3) concentrations and too low rates of denitrification.

摘要

构建了一个模型来模拟丹麦 Vilhelmsborg 湖淡水沉积物中硝化和反硝化作用的实验结果(K. Jensen、N. P. Sloth、N. Risgaard-Petersen、S. Rysgaard 和 N. P. Revsbech,应用环境微生物学 60:2094-2100,1994)。当表层水中的 O(2)浓度从 10 增加到 600 μM 时,模型输出忠实地再现了 O(2)和 NO(3)的分布以及硝化、反硝化和 O(2)消耗的速率。该模型还准确地预测了整合(每平方米每小时微摩尔)硝化和反硝化速率对 O(2)浓度增加的响应。从表层水中扩散的 NO(3)的模拟反硝化速率(D(w))和沉积物中硝化生成的 NO(3)的模拟反硝化速率(D(n))与实验速率相对应,因为表层水中的 O(2)浓度发生了变化。随着表层水中 NO(3)浓度的变化,预测的 D(w)和 D(n)速率与实验确定的速率非常相似。该模型由 41 层 0.1 毫米厚的层组成,其中 3 层代表水中的扩散边界层。需要较大的硝化和反硝化一级速率常数才能完全氧化从下部沉积物层扩散的所有 NH(4)并去除大部分生成的 NO(3)。除了来自下方的 NH(4)通量外,模型还需要电子供体的通量,可能是甲烷。通过允许反硝化耐受一些 O(2)(约 10 μM),实现硝化和反硝化的紧密耦合,是复制实际数据所必需的。两种过程的空间分离(反硝化不能耐受 O(2))导致 NO(3)浓度过高和反硝化速率过低。

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引用本文的文献

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1
Estimation of nitrification and denitrification from microprofiles of oxygen and nitrate in model sediment systems.
Appl Environ Microbiol. 1994 Jun;60(6):2094-100. doi: 10.1128/aem.60.6.2094-2100.1994.

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