烟气脱硫
烟气
泥浆
化学
氨
反硝化
挥发
溶解
微粒
环境化学
废物管理
环境工程
氮气
环境科学
有机化学
工程类
作者
Wei Liu,Bobo Wu,Xiaoxuan Bai,Shuhan Liu,Xiangyang Liu,Yan Hao,Weizhao Liang,Shu‐Min Lin,Huanjia Liu,Lining Luo,Shuang Zhao,Chuanyong Zhu,Jiming Hao,Hezhong Tian
标识
DOI:10.1021/acs.est.9b04995
摘要
To investigate the up-to-date migration and emission characteristics of NH3/NH4+ in coal-fired power plants (CFPPs) after implementing ultralow emission retrofitting, typical air pollution control devices (APCDs) in CFPPs, including flue gas denitrification, dust collectors, combined wet flue gas desulfurization (WFGD), and wet precipitators are involved in field measurements. The results show that most of the excessive injected and/or unreacted ammonia from the flue gas denitrification system, whether selective catalytic reduction (SCR) or selective noncatalytic reduction (SNCR), is converted into particle-bound NH4+ (>91%), and the rest (less than 9%) is carried by flue gas in the form of gaseous NH3, with a concentration value of 0.15-0.54 mg/(N m3) at the denitrification outlet. When passing through dust collectors, particle-bound NH4+ concentration decreases substantially along with the removal of particle matter. In WFGD, the dissolution and volatilization effects affect the gaseous ammonia concentration, which decreases when using limestone slurry and a 20% solution of ammonia as a desulfurization agent, while liquid ammonia solution with a high concentration (99.8%) may cause the flue gas NH3 concentration to increase considerably by 13 times. Particle-bound NH4+ concentration is mainly influenced by the relative strength of desulfurization slurry scouring and flue gas carrying effects and increases 2.84-116 times through ammonia-based WFGD. Furthermore, emission factors of NH3 for combinations of APCDs are discussed.
科研通智能强力驱动
Strongly Powered by AbleSci AI