Abstract:
Nitrogen oxides (NO
x) is one of the main pollutants produced by coal-fired power plants. Selective non-catalytic reduction (SNCR) denitration technology has been widely used due to its advantages of simple structure, low cost and no need for catalyst. A large number of OH radicals are produced in the process of SNCR denitration. It is necessary to explore the role of OH radical to improve the efficiency of SNCR denitration. Based on density functional theory (DFT), the role of OH radical in the selective non-catalytic reduction of NO by NH
3 was explored. The results showed that there are three reaction pathways for the reaction of NH
3 and NO, and the optimal reaction pathway is that NH
3 and NO first react to form the intermediate NH
2NO and an isolated H atom, which attacks the O atom of NH
2NO to form OH and NH
2N, followed by the formation of NNH and H
2O. The process of removing the first hydrogen atom from NH
3 requires the highest energy barrier (265.0 kJ/mol), which is the rate-limiting step. The energy barrier of rate-limiting step of NH
2+NO reaction (140.2 kJ/mol) is 124.8 kJ/mol lower than that of NH
3+NO reaction (265.0 kJ/mol), indicating that the denitration reaction rate of NH
2+NO is faster. The energy barrier of rate-limiting step of NH
3+NO+OH reaction (198.7 kJ/mol) is 66.3 kJ/mol lower than that of NH
3+NO reaction (265.0 kJ/mol). The OH radical improves the denitration efficiency of NH
3+NO mainly by promoting the removal of the first hydrogen atom from NH
3 to produce NH
2. The reaction mechanism of NH
3+NO+OH is similar to that of NH
2+NO. The OH radical participating in NH
2+NO denitration reaction can form a six-element complex structure and promote denitration reaction. The OH radical can not only significantly improve the denitration reaction rate of NH
3+NO, but also promote the denitration reaction rate of NH
2+NO at a lower temperature (673−1 273 K). The OH radical can reduce the activation energy of NH
3+NO and NH
2+NO reactions, promoting the denitration reaction. For the selective non-catalytic reduction of NO with NH
3, the removal of the first hydrogen atom from NH
3 to NH
2 is the rate-limiting step, and accelerating this process is the key to improve the denitration efficiency of SNCR.