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Selective non-catalytic reduction of nitrogen oxides by ammonia: Experiments and model calculations.

机译:氨选择性地非催化还原氮氧化物:实验和模型计算。

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The DeNOx process (SNCR of NOx by NH3) was investigated experimentally and numerically. The experiments were conducted by using simulated exhaust gases in a well-defined laminar reactor facility over the temperature range from 850 K to 1350 K (Chapter 5). Established chemical kinetic programs were utilized for the model calculations, including sensitivity analysis to identify the reaction pathways (Chapter 6).; When the beta-ratio (the molar ratio of NH3 to NOx ) was greater than about 1.5, more than 80% of NOx could be removed (Chapter 7). The existing model for the experimental system was improved in two major ways. First, the radial velocity profile was included as opposed to the use of a constant velocity (plug flow). Second, the gas temperatures before and after the center region of the reactor were included. These two improvements resulted in closer agreements with the experiments than the calculations limited to only the major reacting zone (Chapter 8).; For the base conditions of 670-ppm NH3, 325-ppm NO, and 10-ppm of NO2, the NOx removals were determined as functions of the residence time (up to 1527.8/T sec) and the initial levels of O2 (up to 15.0%), CO (up to 1260 ppm), and H2O. The maximum NOx removals occurred at lower temperatures with the increase of the residence time, and the levels O2 and CO, while the effects of H2O (up to about 8%) were insignificant on the NO x removals. In general, the maximum NOx removals were above about 80% at around 1200 +/- 150 K for the current conditions (Chapter 9). The decrease of TDeNOx (the temperature for the maximum NOx removals) due to the increase of the residence time and the O2 levels could be related to simple exponential (logarithmic) functions, while the increase of CO resulted in the linear deductions of TDeNOx (Chapter 10).; Compared to the experiments, the predictions from the currently utilized DeNOx mechanisms showed significant discrepancies for TDeNOx and the formed concentrations of N2O at certain conditions (especially, for the given O2 levels). Possible weaknesses of the current mechanisms were suggested with the identified NO x removal pathways through sensitivity analysis (Chapter 11).
机译:通过实验和数值研究了脱硝工艺(NH3对SNCR的SNCR)。通过在定义明确的层流反应器设施中使用模拟废气在850 K至1350 K的温度范围内进行实验(第5章)。建立的化学动力学程序用于模型计算,包括敏感性分析以识别反应途径(第6章)。当β比(NH3与NOx的摩尔​​比)大于约1.5时,可以去除80%以上的NOx(第7章)。实验系统的现有模型在两个方面进行了改进。首先,与使用恒定速度(活塞流)相反,包括了径向速度分布。第二,包括反应器中心区域之前和之后的气体温度。这两个改进使得与实验的协议更加接近,而不是只限于主要反应区的计算(第8章)。对于670-ppm NH3、325-ppm NO和10-ppm NO2的基本条件,确定的NOx去除量是停留时间(最高1527.8 / T sec)和初始O2水平(最高152.80 / T sec)的函数。 15.0%),CO(最高1260 ppm)和H2O。随着停留时间的增加,最大的NOx去除量在较低的温度下发生,并且O2和CO的含量增加,而H2O的影响(最高约8%)对NOx去除量的影响不明显。通常,在当前条件下,最大的NOx去除率约为1200 +/- 150 K,高于80%(第9章)。由于停留时间和O2含量的增加而导致的TDeNOx的减少(最大NOx去除的温度)可能与简单的指数(对数)函数有关,而CO的增加导致TDeNOx的线性推导(本章) 10)。与实验相比,从当前使用的DeNOx机制进行的预测表明,在特定条件下(特别是对于给定的O2水平),TDeNOx和形成的N2O浓度存在显着差异。通过敏感性分析,确定的NOx去除途径提示了当前机制的可能弱点(第11章)。

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