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燃煤电厂颗粒物中硫酸根与硝酸根离子的转化规律
引用本文:杨柳,何晴,盛重义.燃煤电厂颗粒物中硫酸根与硝酸根离子的转化规律[J].环境科学,2021,42(10):4678-4686.
作者姓名:杨柳  何晴  盛重义
作者单位:南京师范大学环境学院,南京210023;南京师范大学环境学院,南京210023;浙江大学苏州工业技术研究院,苏州215163
基金项目:国家自然科学基金项目(41877469,41771498)
摘    要:燃煤电厂排放的颗粒物可以分为可凝结颗粒物(condensable particle matter,CPM)和可过滤颗粒物(filterable particle matter,FPM).通过分析7个超低排燃煤电厂的湿法脱硫(wet flue gas desulfurization,WFGD)进出口和湿电除尘(wet electrostatic precipitator,WESP)出口烟气中CPM和FPM的SO42-和NO3-浓度,揭示了这2种典型水溶性离子在烟道内的变化规律与转化特征.结果表明在WFGD前后,CPM中的SO42-和NO3-浓度呈降低趋势,其降低率范围分别为43.12%~86.84%和17.99%~91.58%,而FPM中SO42-和NO3-浓度呈增大趋势.在WESP前后,CPM中SO42-和NO3-浓度呈增大趋势,增长率范围分别为21.05%~424.65%和13.51%~298.37%,而FPM中SO42-和NO3-浓度呈减小趋势.在WFGD中,随着烟气温度降低和湿度增加,部分CPM会通过冷凝和团聚作用进一步转化为FPM;在WESP中,由于烟气一直处于低温、高湿的条件,烟气中存在的SO2与NO2会结合水蒸气发生氧化还原反应,进而经过协同作用促进CPM中SO42-和NO3-的生成.

关 键 词:可凝结颗粒物(CPM)  湿法脱硫系统(WFGD)  湿电除尘系统(WESP)  SO42-  NO3-  转化规律
收稿时间:2021/1/12 0:00:00
修稿时间:2021/3/14 0:00:00

Conversion Characterizations of Sulfate Ion and Nitrate Ion in Particulate Matter from Coal-fired Power Plants
YANG Liu,HE Qing,SHENG Zhong-yi.Conversion Characterizations of Sulfate Ion and Nitrate Ion in Particulate Matter from Coal-fired Power Plants[J].Chinese Journal of Environmental Science,2021,42(10):4678-4686.
Authors:YANG Liu  HE Qing  SHENG Zhong-yi
Institution:School of Environment, Nanjing Normal University, Nanjing 210023, China; School of Environment, Nanjing Normal University, Nanjing 210023, China;Suzhou Industrial Technology Research Institute of Zhejiang University, Suzhou 215163, China
Abstract:The particulate matter emitted from coal-fired power plants includes condensable particulate matter(CPM) and filterable particulate matter(FPM). By analyzing the concentration of SO42-and NO3- components of CPM and FPM in the inlet/outlet of wet flue gas desulfurization(WFGD) and the outlet of wet electrostatic precipitator(WESP) from 7 ultra-low emission coal-fired power plants, the variation laws and transformation characteristics were investigated. The results showed that the concentration of SO42- and NO3- of CPM decreased after WFGD, with reduction rates of 43.12%-86.84% and 17.99%-91.58%, respectively, which were different from the conversion trend of FPM. The concentrations of SO42- and NO3- of CPM increased after WESP, with reduction rates of 21.05%-424.65% and 13.51%-298.37%, respectively, which were also different from that of FPM. In the WFGD system, CPM could be transformed into FPM due via condensation and aggregation under the decreasing temperature and increasing of humidity of the flue gas. In the WESP system, SO2 and NO2 in the flue gas combine with water vapor in a redox reaction, which promotes the generation of SO42- and NO3- in CPM through synergistic action.
Keywords:condensable particle matter(CPM)  wet flue gas desulfurization(WFGD)  wet electrostatic precipitator(WESP)  SO42-  NO3-  conversion characterizations
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