Reactive and particulate mercury in the Asian marine boundary layer

被引:68
作者
Chand, Duli [1 ,2 ]
Jaffe, Daniel [1 ,2 ]
Prestbo, Eric [3 ]
Swartzendruber, Philip C. [1 ,2 ]
Hafner, William [1 ]
Weiss-Penzias, Peter [4 ]
Kato, Shungo [5 ]
Takami, Akinori [6 ]
Hatakeyama, Shiro [6 ]
Kajii, Yoshizumi [5 ]
机构
[1] Univ Washington, Bothell, WA 98011 USA
[2] Univ Washington, Dept Atmospher Sci, Seattle, WA 98195 USA
[3] Frontier Geosci, Seattle, WA 98109 USA
[4] Univ Calif Santa Cruz, Dept Environm Toxicol, Santa Cruz, CA 95060 USA
[5] Tokyo Metropolitan Univ, Fac Engn, Tokyo 158, Japan
[6] Natl Inst Environm Studies, Div Atmospher Environm, Tsukuba, Ibaraki, Japan
关键词
Mercury; Pollution; Transport; Particulate; Reactive-mercury; Speciated-mercury;
D O I
10.1016/j.atmosenv.2008.06.048
中图分类号
X [环境科学、安全科学];
学科分类号
08 ; 0830 ;
摘要
The variability of atmospheric mercury in elemental, reactive, and particulate forms has been studied at a remote site (Cape Hedo Observatory, CHO) at Okinawa Island (Japan) March 23 to May 2, 2004, downwind of the major Asian source regions. Under prevailing meteorological conditions, episodes of higher levels of atmospheric mercury and other atmospheric species are observed at CHO. The mean (+/- 1 sigma) concentrations of gaseous elemental mercury (GEM), reactive gaseous mercury (RGM) and particulate-bound mercury (PHg) are 2.04 +/- 0.38 ng m(-3), 4.5 +/- 5.4 pg m(-3) and 3.0 +/- 2.5 pg m(-3), respectively. In Asian outflow the combined contribution of RGM and PHg constitutes less than 1% of the GEM in the boundary layer, which indicates that most mercury export in the marine boundary layer is due to the GEM form, and direct outflow of RGM and PHg is very low. While the data from Okinawa suggest minimal export of RGM and PHg, this does not preclude greater export of these species at higher elevations. Based on the correlations of PHg and submicron aerosol mass (SAM), we found a Delta PHg/Delta SAM ratio of 0.20 mu g g(-1) (R = 0.58, p < 0.01), which we believe to be characteristic of East Asian industrial aerosols during outflow. A diurnal variation is observed in RGM with a peak near noon. Using a rate constant of 9 x 10(-14) cm(3) molecule(-1) s(-1) for the OH oxidation rate (Sommar, J., Gardfeldt, K., Stromberg, D., Feng, X., 2001. A kinetic study of the gas phase reaction between the hydroxyl radical and atomic mercury. Atmospheric Environment 35, 3049-3054; Pal, B., Ariya, P.A., 2004a. Gas-phase HO center dot-initiated reactions of elemental mercury: kinetics, product studies, and atmospheric implications. Environmental Science and Technology 38 (21), 5555-5566.) and a typical OH concentration of 1-5 x 10(6) cm(-3) would result in RGM production rates of 0.6-3.0 pg m(-3) h(-1). Although OH may not be the sole oxidant, this is consistent with the observed change in concentration during daytime of 1.4 +/- 1.5 pg m(-3) h(-1). A significant correlation is found between GEM and CO; GEM and SAM; and PHg and SAM. Lower Delta SAM/Delta CO and Delta GEM/Delta CO are observed for transport events with rainfall and for air parcels remaining in the mixed layer. Back trajectory analysis along with the correlation study suggests that the air from China has a higher GEM concentration compared to the air coming from southern Japan. (C) 2008 Elsevier Ltd. All rights reserved.
引用
收藏
页码:7988 / 7996
页数:9
相关论文
共 41 条
[1]   Quantitative sampling using an Aerodyne aerosol mass spectrometer - 1. Techniques of data interpretation and error analysis [J].
Allan, JD ;
Jimenez, JL ;
Williams, PI ;
Alfarra, MR ;
Bower, KN ;
Jayne, JT ;
Coe, H ;
Worsnop, DR .
JOURNAL OF GEOPHYSICAL RESEARCH-ATMOSPHERES, 2003, 108 (D3)
[2]   A generalised method for the extraction of chemically resolved mass spectra from aerodyne aerosol mass spectrometer data [J].
Allan, JD ;
Delia, AE ;
Coe, H ;
Bower, KN ;
Alfarra, MR ;
Jimenez, JL ;
Middlebrook, AM ;
Drewnick, F ;
Onasch, TB ;
Canagaratna, MR ;
Jayne, JT ;
Worsnop, DR .
JOURNAL OF AEROSOL SCIENCE, 2004, 35 (07) :909-922
[3]   Oxidation of elemental mercury in the atmosphere; Constraints imposed by global scale modelling [J].
Bergan, T ;
Rodhe, H .
JOURNAL OF ATMOSPHERIC CHEMISTRY, 2001, 40 (02) :191-212
[4]   Mercury in the global troposphere: a three-dimensional model study [J].
Bergan, T ;
Gallardo, L ;
Rodhe, H .
ATMOSPHERIC ENVIRONMENT, 1999, 33 (10) :1575-1585
[5]   Atmospheric reactions of gaseous mercury with ozone and hydroxyl radical: Kinetics and product studies [J].
Biswajit, P ;
Parisa, AA .
JOURNAL DE PHYSIQUE IV, 2003, 107 :189-192
[6]   Mechanisms of mercury removal by O3 and OH in the atmosphere [J].
Calvert, JG ;
Lindberg, SE .
ATMOSPHERIC ENVIRONMENT, 2005, 39 (18) :3355-3367
[7]  
Carpi A, 1997, WATER AIR SOIL POLL, V98, P241, DOI 10.1007/BF02047037
[8]  
Draxler R.R., 2010, HYSPLIT HYBRID SINGL
[9]   Urban environmental mercury in Changchun, a metropolitan city in Northeastern China: source, cycle, and fate [J].
Fang, FM ;
Wang, QC ;
Li, JF .
SCIENCE OF THE TOTAL ENVIRONMENT, 2004, 330 (1-3) :159-170
[10]   Mercury in the atmosphere around Japan, Korea, and China as observed during the 2001 ACE-Asia field campaign: Measurements, distributions, sources, and implications [J].
Friedli, HR ;
Radke, LF ;
Prescott, R ;
Li, P ;
Woo, JH ;
Carmichael, GR .
JOURNAL OF GEOPHYSICAL RESEARCH-ATMOSPHERES, 2004, 109 (D19) :D19S251-13