Atmospheric mercury (Hg) in the Adirondacks: Concentrations and sources

被引:69
作者
Choi, Hyun-Deok [1 ]
Holsen, Thomas M. [1 ]
Hopke, Philip K. [2 ]
机构
[1] Clarkson Univ, Dept Civil & Environm Engn, Potsdam, NY 13699 USA
[2] Clarkson Univ, Ctr Air Resource Engn & Sci, Potsdam, NY 13699 USA
关键词
D O I
10.1021/es7028137
中图分类号
X [环境科学、安全科学];
学科分类号
08 ; 0830 ;
摘要
Hourly averaged gaseous elemental Hg (GEM) concentrations and hourly integrated reactive gaseous Hg (RGM), and particulate Hg (Hg-P) concentrations in the ambient air were measured at Huntington Forest in the Adirondacks, New York from June 2006 to May 2007. The average concentrations of GEM, RGM, and Hg-P were 1.4 +/- 0.4 ng m(-3), 1.8 +/- 2.2 pg m(-3), and 3.2 +/- 3.7 pg m(-3), respectively. RGM represents <3.5% of total atmospheric Hg or total gaseous Hg (TGM: GEM + RGM) and Hg-P represents <3.0% of the total atmospheric Hg. The highest mean concentrations of GEM, RGM, and Hg-P were measured during winter and summer whereas the lowest mean concentrations were measured during spring and fall. Significant diurnal patterns were apparent in warm seasons for all species whereas diurnal patterns were weak in cold seasons. RGM was better correlated with ozone concentration and temperature in both warm (rho(RGM - ozone) = 0.57, p < 0.001; rho (RGM - temperature) = 0.62, p < 0.001) and cold seasons (rho (RGM - ozone)= 0.48, p = 0.002; rho (RGM - temperature) = 0.54, p = 0.011) than the other species. Potential source contribution function (PSCF) analysis was applied to identify possible Hg sources. This method identified areas in Pennsylvania, West Virginia, Ohio, Kentucky, Texas, Indiana, and Missouri, which coincided well with sources reported in a 2002 U.S. mercury emissions inventory.
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页码:5644 / 5653
页数:10
相关论文
共 51 条
[1]  
[Anonymous], APPL PRINCIPAL COMPO
[2]   Four years of continuous total gaseous mercury (TGM) measurements at sites in Ontario, Canada [J].
Blanchard, P ;
Froude, FA ;
Martin, JB ;
Dryfhout-Clark, H ;
Woods, JT .
ATMOSPHERIC ENVIRONMENT, 2002, 36 (23) :3735-3743
[3]   A REFINEMENT OF THE POTASSIUM TRACER METHOD FOR RESIDENTIAL WOOD SMOKE [J].
CALLOWAY, CP ;
LI, S ;
BUCHANAN, JW .
ATMOSPHERIC ENVIRONMENT, 1989, 23 (01) :67-69
[4]   Trend and variability of total gaseous mercury (TGM) in the state of Connecticut, USA during 1997-1999 [J].
Chen, H ;
Yang, XS ;
Perkins, C .
WATER AIR AND SOIL POLLUTION, 2004, 151 (1-4) :103-116
[5]  
CHOI HD, 2008, ENVIRON POLLUT UNPUB
[6]   Modeling the atmospheric transport and deposition of mercury to the Great Lakes [J].
Cohen, M ;
Artz, R ;
Draxler, R ;
Miller, P ;
Poissant, L ;
Niemi, D ;
Ratté, D ;
Deslauriers, M ;
Duval, R ;
Laurin, R ;
Slotnick, J ;
Nettesheim, T ;
McDonald, J .
ENVIRONMENTAL RESEARCH, 2004, 95 (03) :247-265
[7]   Photoreduction of mercury in sea water and its possible implications for Hg0 air-sea fluxes [J].
Costa, M ;
Liss, PS .
MARINE CHEMISTRY, 1999, 68 (1-2) :87-95
[8]  
Draxler R.R., 2005, ARL230 NOAA ERL
[9]   Seasonal variation of gaseous mercury exchange rate between air and water surface over Baihua reservoir, Guizhou, China [J].
Feng, XB ;
Yan, HY ;
Wang, SF ;
Qiu, GL ;
Tang, SL ;
Shang, LH ;
Dai, QJ ;
Hou, YM .
ATMOSPHERIC ENVIRONMENT, 2004, 38 (28) :4721-4732
[10]   Mercury emissions from burning of biomass from temperate North American forests: laboratory and airborne measurements [J].
Friedli, HR ;
Radke, LF ;
Lu, JY ;
Banic, CM ;
Leaitch, WR ;
MacPherson, JI .
ATMOSPHERIC ENVIRONMENT, 2003, 37 (02) :253-267