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Estimates of emissions of As, Cd, Hg and Pb to the atmosphere from major source categories in the United States Numbers under the columns are emissions in tonnes per yearEstimates of emissions of As, Cd, Hg and Pb to the atmosphere from major source categories in the United States Numbers under the columns are emissions in tonnes per year |
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Estimates of emissions of As, Cd, Cr, Cu, Hg and Pb to the atmosphere from major source categories in Canada in 1982 Numbers under the columns are emissions in tonnes per yearEstimates of emissions of As, Cd, Cr, Cu, Hg and Pb to the atmosphere from major source categories in Canada in 1982 Numbers under the columns are emissions in tonnes per year |
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Emissions of As, Cd, Ni and Zn to the atmosphere from major sources in the former Soviet Union in 1979/80Emissions of As, Cd, Ni and Zn to the atmosphere from major sources in the former Soviet Union in 1979/80 |
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Major point sources (non-ferrous metal smelters) of Pb to the atmosphere in the Urals and the Asian part of the former Soviet UnionMajor point sources (non-ferrous metal smelters) of Pb to the atmosphere in the Urals and the Asian part of the former Soviet Union |
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The relative importance of different branches of industry in discharges of Cu, Ni, Pb and Zn to the aquatic environment from major point sources in the European Community (EC)The relative importance of different branches of industry in discharges of Cu, Ni, Pb and Zn to the aquatic environment from major point sources in the European Community (EC) |
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Averaged upper (3000 m) air concentrations of Pb in winter (December-February) and summer (June-August) as modeled by the updated (1996) hemispheric EMEP transport model in a simulation for the reference year 1988Averaged upper (3000 m) air concentrations of Pb in winter (December-February) and summer (June-August) as modeled by the updated (1996) hemispheric EMEP transport model in a simulation for the [..] |
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Lead deposition as modeled by the updated (1996) hemispheric EMEP transport model in a simulation for the reference year 1988Lead deposition as modeled by the updated (1996) hemispheric EMEP transport model in a simulation for the reference year 1988 |
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Average contributions from various sources to the atmospheric concentrations of elements in winter air samples at Ny-Ålesund, SvalbardAverage contributions from various sources to the atmospheric concentrations of elements in winter air samples at Ny-Ålesund, Svalbard |
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Cadmium levels in kidney of adult marine birds from Greenland Levels associated with potential for kidney damage are above 100 µg/g wwCadmium levels in kidney of adult marine birds from Greenland Levels associated with potential for kidney damage are above 100 µg/g ww |
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Cadmium levels in kidney of adult ringed seals from Greenland and Svalbard Levels associated with potential for kidney damage are above 100-200 µg/g wwCadmium levels in kidney of adult ringed seals from Greenland and Svalbard Levels associated with potential for kidney damage are above 100-200 µg/g ww |
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Available data in the AMAP radioactivity database as a function of timeAvailable data in the AMAP radioactivity database as a function of time |
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Seawater concentrations of 137Cs in the Barents and East Greenland Seas compared to the yearly releases from SellafieldSeawater concentrations of 137Cs in the Barents and East Greenland Seas compared to the yearly releases from Sellafield |
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Changes with time in 131I activity concentration in Finnish air samplesChanges with time in 131I activity concentration in Finnish air samples |
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Changes with time in 137Cs activity concentration in air in Norway, Finland and RussiaChanges with time in 137Cs activity concentration in air in Norway, Finland and Russia |
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Changes with time in wet and dry deposition of 137Cs in Arctic Finland and north west Russia (Nenets Autonomous Okrug)Changes with time in wet and dry deposition of 137Cs in Arctic Finland and north west Russia (Nenets Autonomous Okrug) |
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