Migration and Emission Characteristics of Ammonia/Ammonium through Flue Gas Cleaning Devices in Coal-Fired Power Plants of China

被引:53
|
作者
Liu, Wei [1 ,2 ]
Wu, Bobo [1 ,2 ]
Bai, Xiaoxuan [1 ,2 ]
Liu, Shuhan [1 ,2 ]
Liu, Xiangyang [1 ,2 ]
Hao, Yan [1 ]
Liang, Weizhao [2 ]
Lin, Shumin [1 ,2 ]
Liu, Huanjia [1 ,2 ]
Luo, Lining [1 ,2 ]
Zhao, Shuang [1 ,2 ]
Zhu, Chuanyong [2 ,3 ]
Hao, Jiming [4 ]
Tian, Hezhong [1 ,2 ]
机构
[1] Beijing Normal Univ, Sch Environm, State Key Joint Lab Environm Simulat & Pollut Con, Beijing 100875, Peoples R China
[2] Beijing Normal Univ, Ctr Atmospher Environm Studies, Beijing 100875, Peoples R China
[3] Qilu Univ Technol, Sch Environm Sci & Engn, Jinan 250353, Shandong, Peoples R China
[4] Tsinghua Univ, Sch Environm, Beijing 100084, Peoples R China
基金
中国国家自然科学基金;
关键词
SELECTIVE CATALYTIC-REDUCTION; HIGH-RESOLUTION; PARTICULATE MATTER; ATMOSPHERIC AMMONIA; ELECTROSTATIC PRECIPITATOR; FORMATION MECHANISMS; INVENTORY; COMBUSTION; PM2.5; TEMPERATURE;
D O I
10.1021/acs.est.9b04995
中图分类号
X [环境科学、安全科学];
学科分类号
08 ; 0830 ;
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 m(3)) 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.
引用
收藏
页码:390 / 399
页数:10
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