Distribution and Fate of Mercury in Pulverized Bituminous Coal-Fired Power Plants in Coal Energy-Dominant Huainan City, China

被引:18
作者
Chen, Bingyu [1 ,2 ]
Liu, Guijian [1 ,2 ]
Sun, Ruoyu [1 ]
机构
[1] Univ Sci & Technol China, Sch Earth & Space Sci, CAS Key Lab Crust Mantle Mat & Environm, Hefei 230026, Anhui, Peoples R China
[2] Chinese Acad Sci, Inst Earth Environm, State Key Lab Loess & Quaternary Geol, Xian 710075, Peoples R China
关键词
COMBUSTION BY-PRODUCTS; EMISSIONS; SPECIATION; ATMOSPHERE; POLLUTION; CHLORINE; SELENIUM; ELEMENTS; IMPACT; JAPAN;
D O I
10.1007/s00244-016-0267-7
中图分类号
X [环境科学、安全科学];
学科分类号
08 ; 0830 ;
摘要
A better understanding on the partitioning behavior of mercury (Hg) during coal combustion in large-scale coal-fired power plants is fundamental for drafting Hg-emission control regulations. Two large coal-fired utility boilers, equipped with electrostatic precipitators (ESPs) and a wet flue gas desulfurization (WFGD) system, respectively, in coal energy-dominant Huainan City, China, were selected to investigate the distribution and fate of Hg during coal combustion. In three sampling campaigns, we found that Hg in bottom ash was severely depleted with a relative enrichment (RE) index < 7 %, whereas the RE index for fly ash (9-54 %) was comparatively higher and variable. Extremely high Hg was concentrated in gypsum (a parts per thousand currency sign4500 ng/g), which is produced in the WFGD system. Mass balance calculation shows that the shares of Hg in bottom ash, fly ash, WFGD products (gypsum, effluents, sludge), and stack emissions were < 2, 17-32, 7-22, and 54-82 %, respectively. The Hg-removal efficiencies of ESPs, WFGD, and ESPs + WFGD were 17-32, 10-29, and 36-46 %, respectively. The Hg-emission factor of studied boilers was in a high range of 0.24-0.29 g Hg/t coal. We estimated that Hg emissions in all Huainan coal-fired power plants varied from 1.8 Mg in 2003 to 7.3 Mg in 2010.
引用
收藏
页码:724 / 733
页数:10
相关论文
共 54 条
  • [1] Environmental impact of a coal combustion-desulphurisation plant:: Abatement capacity of desulphurisation process and environmental characterisation of combustion by-products
    Alvarez-Ayuso, E.
    Querol, X.
    Tomas, A.
    [J]. CHEMOSPHERE, 2006, 65 (11) : 2009 - 2017
  • [2] [Anonymous], 1997, MERCURY STUDY REPORT, V3
  • [3] Impact of coal chlorine on mercury speciation and emission from a 100-MW utility boiler with cold-side electrostatic precipitators and low-NOx burners
    Cao, Y
    Duan, YF
    Kellie, S
    Li, LC
    Xu, WB
    Riley, JT
    Pan, WP
    [J]. ENERGY & FUELS, 2005, 19 (03) : 842 - 854
  • [4] Impacts of halogen additions on mercury oxidation, in a slipstream selective catalyst reduction (SCR), reactor when burning sub-bituminous coal
    Cao, Yan
    Gao, Zhengyang
    Zhu, Jiashun
    Wang, Quanhai
    Huang, Yaji
    Chiu, Chengchung
    Parker, Bruce
    Chu, Paul
    Pan, Wei-Ping
    [J]. ENVIRONMENTAL SCIENCE & TECHNOLOGY, 2008, 42 (01) : 256 - 261
  • [5] Mercury pollution in Guizhou, Southwestern China - An overview
    Feng, Xinbin
    Qiu, Guangle
    [J]. SCIENCE OF THE TOTAL ENVIRONMENT, 2008, 400 (1-3) : 227 - 237
  • [6] Finkelman RB., 1993, Organic Geochemistry: principles and applications, P593, DOI [DOI 10.1007/978-1-4615-2890-6_28, 10.1007/978-1-4615-2890-6_28]
  • [7] Marine biogeochemical cycling of mercury
    Fitzgerald, William F.
    Lamborg, Carl H.
    Hammerschmidt, Chad R.
    [J]. CHEMICAL REVIEWS, 2007, 107 (02) : 641 - 662
  • [8] Evaluating mercury transformation mechanisms in a laboratory - scale combustion system
    Galbreath, KC
    Zygarlicke, CJ
    Olson, ES
    Pavlish, JH
    Toman, DL
    [J]. SCIENCE OF THE TOTAL ENVIRONMENT, 2000, 261 (1-3) : 149 - 155
  • [9] Characteristics and composition of fly ash from Canadian coal-fired power plants
    Goodarzi, Fariborz
    [J]. FUEL, 2006, 85 (10-11) : 1418 - 1427
  • [10] Emissions of mercury and other trace elements from coal-fired power plants in Japan
    Ito, Shigeo
    Yokoyama, Takahisa
    Asakura, Kazuo
    [J]. SCIENCE OF THE TOTAL ENVIRONMENT, 2006, 368 (01) : 397 - 402