Atmospheric mercury emissions and speciation at the sulphur bank mercury mine superfund site, Northern California.
One pathway for release of mercury (Hg) from naturally enriched sites is emission to the atmosphere. Elemental Hg, when emitted, will enter the global atmospheric pool. In contrast, if reactive gaseous Hg or Hg2+ (as HgCl2, HgBr2, or HgOH2) is formed, it will most likely be deposited locally. This study focused on the measurement of elemental Hg flux and reactive gaseous Hg concentrations at the Sulphur Bank Superfund Site, an area of natural Hg enrichment with anthropogenic disturbance and ongoing geothermal activity. Mean Hg emissions ranged from 14 to 11000 ng m(-2) h(-1), with the highest emissions from anthropogenically disturbed materials. Reactive gaseous Hg concentrations were the highest ever reported for a natural setting (0.3-76 ng m(-3)). Measured Hg fluxes were used within a Geographic Information System to estimate mercury releases to the atmosphere from the site. Results indicated approximately 17 kg of Hg y(-1) of is emitted to the atmosphere from the 3.8 km2 area, with half from mine waste, ore, and tailing piles and half from relatively undisturbed naturally enriched substrate.
Nacht
David M
DM
Department of Environmental and Resource Sciences, MS 370, University of Nevada, Reno, Nevada 89557, USA.
Gustin
Mae Sexauer
MS
Engle
Mark A
MA
Zehner
Richard E
RE
Giglini
Anthony D
AD
D000393:Air Pollutants / Q000032:analysis*; D002140:California; D004784:Environmental Monitoring; D040362:Geographic Information Systems; D006256:Hazardous Waste; D008628:Mercury / Q000032:analysis* / Q000737:chemistry; D008906:Mining; D012037:Refuse Disposal; D013455:Sulfur / Q000032:analysis* / Q000737:chemistry
D000393:Air Pollutants; D006256:Hazardous Waste; D013455:Sulfur; D008628:Mercury