Li Bo, Zhao Jinyang, Lu Junfu
Electric Power Planning & Engineering Institute, Ande Rode No. 65, Xicheng District, Beijing 100120, China.
Key Laboratory for Thermal Science and Power Engineering of Ministry of Education, Department of Thermal Engineering, Tsinghua University, Beijing 100083, China.
Int J Environ Res Public Health. 2015 Jan 29;12(2):1595-611. doi: 10.3390/ijerph120201595.
This study used two kinetic mechanisms to evaluate the oxidation processes of NO and SO2 by ozone. The performance of the two models was assessed by comparisons with experimental results from previous studies. The first kinetic mechanism was a combined model developed by the author that consisted of 50 species and 172 reactions. The second mechanism consisted of 23 species and 63 reactions. Simulation results of both of the two models show under predictions compared with experimental data. The results showed that the optimized reaction temperature for NO with O3 ranged from 100~200 °C. At higher temperatures, O3 decomposed to O2 and O, which resulted in a decrease of the NO conversion rate. When the mole ratio of O3/NO was greater than 1, products with a higher oxidation state (such as NO3, N2O5) were formed. The reactions between O3 and SO2 were weak; as such, it was difficult for O3 to oxidize SO2.
本研究采用两种动力学机制来评估臭氧对一氧化氮(NO)和二氧化硫(SO2)的氧化过程。通过与先前研究的实验结果进行比较,评估了这两种模型的性能。第一种动力学机制是作者开发的一个组合模型,它包含50种物质和172个反应。第二种机制由23种物质和63个反应组成。与实验数据相比,这两种模型的模拟结果均显示预测值偏低。结果表明,NO与O3反应的最佳温度范围为100~200°C。在较高温度下,O3分解为O2和O,导致NO转化率降低。当O3/NO的摩尔比大于1时,会形成氧化态更高的产物(如NO3、N2O5)。O3与SO2之间的反应较弱;因此,O3很难氧化SO2。