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Sum-DDT (ng/g ww) in Arctic animals as food items compared to no-effect-concentrations (NOAEC) and environmental quality guidelines for protecting fish-eating/aquatic wildlife (1 Baril et al 1990, 2 USEPA 1995,

Sum-DDT (ng/g ww) in Arctic animals as food items compared to no-effect-concentrations (NOAEC) and environmental quality guidelines for protecting fish-eating/aquatic wildlife (1 Baril et al 1990, 2 [..] 		Sum-DDT (ng/g ww) in Arctic animals as food items compared to no-effect-concentrations (NOAEC) and environmental quality guidelines for protecting fish-eating/aquatic wildlife (1 Baril et al 1990, 2 USEPA 1995,

Age accumulation and temporal comparison of mean concentrations of Hg in liver tissue of ringed seal (Phoca hispida) and beluga whale (Delphinapterus leucas) fron the Canadian Arctic

Age accumulation and temporal comparison of mean concentrations of Hg in liver tissue of ringed seal (Phoca hispida) and beluga whale (Delphinapterus leucas) fron the Canadian Arctic 		Age accumulation and temporal comparison of mean concentrations of Hg in liver tissue of ringed seal (Phoca hispida) and beluga whale (Delphinapterus leucas) fron the Canadian Arctic

Summary of ranges of Cd levels (mean values) in Arctic marine organisms Solid parts of the lines indicate ranges for Greenlandic data

Summary of ranges of Cd levels (mean values) in Arctic marine organisms Solid parts of the lines indicate ranges for Greenlandic data 		Summary of ranges of Cd levels (mean values) in Arctic marine organisms Solid parts of the lines indicate ranges for Greenlandic data

Summary of ranges of Pb levels (mean values) in Arctic marine organisms Solid parts of the lines indicate ranges for Greenlandic data

Summary of ranges of Pb levels (mean values) in Arctic marine organisms Solid parts of the lines indicate ranges for Greenlandic data 		Summary of ranges of Pb levels (mean values) in Arctic marine organisms Solid parts of the lines indicate ranges for Greenlandic data

Summary of ranges of Hg levels (mean values) in Arctic marine organisms Solid parts of the lines indicate ranges for Greenlandic data

Summary of ranges of Hg levels (mean values) in Arctic marine organisms Solid parts of the lines indicate ranges for Greenlandic data 		Summary of ranges of Hg levels (mean values) in Arctic marine organisms Solid parts of the lines indicate ranges for Greenlandic data

Summary of ranges of Se levels (mean values) in Arctic marine organisms Solid parts of the lines indicate ranges for Greenlandic data

Summary of ranges of Se levels (mean values) in Arctic marine organisms Solid parts of the lines indicate ranges for Greenlandic data 		Summary of ranges of Se levels (mean values) in Arctic marine organisms Solid parts of the lines indicate ranges for Greenlandic data

Cadmium levels in kidney of adult marine birds from Greenland Levels associated with potential for kidney damage are above 100 µg/g ww

Cadmium levels in kidney of adult marine birds from Greenland Levels associated with potential for kidney damage are above 100 µg/g ww 		Cadmium levels in kidney of adult marine birds from Greenland Levels associated with potential for kidney damage are above 100 µg/g ww

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 ww

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 ww 		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 ww

Changes with time in 137Cs activity concentration in whales from Greenland waters

Changes with time in 137Cs activity concentration in whales from Greenland waters 		Changes with time in 137Cs activity concentration in whales from Greenland waters

Changes with time in 137Cs activity concentration in seals from Greenland waters

Changes with time in 137Cs activity concentration in seals from Greenland waters 		Changes with time in 137Cs activity concentration in seals from Greenland waters

Time trends of mean methylmercury concentrations

Time trends of mean methylmercury concentrations 		Time trends of mean methylmercury concentrations

Distribution (in percentiles) of whole blood lead concentrations in four regions in Greenland and in Greenlanders living in Denmark

Distribution (in percentiles) of whole blood lead concentrations in four regions in Greenland and in Greenlanders living in Denmark 		Distribution (in percentiles) of whole blood lead concentrations in four regions in Greenland and in Greenlanders living in Denmark

Distribution (in percentiles) of whole blood mercury concentrations in four regions in Greenland and in Greenlanders living in Denmark

Distribution (in percentiles) of whole blood mercury concentrations in four regions in Greenland and in Greenlanders living in Denmark 		Distribution (in percentiles) of whole blood mercury concentrations in four regions in Greenland and in Greenlanders living in Denmark

Distribution (in percentiles) of whole blood cadmium concentrations in four regions in Greenland and in Greenlanders living in Denmark

Distribution (in percentiles) of whole blood cadmium concentrations in four regions in Greenland and in Greenlanders living in Denmark 		Distribution (in percentiles) of whole blood cadmium concentrations in four regions in Greenland and in Greenlanders living in Denmark

Sum-PCB (ng/g lw) in Arctic mammals compared to thresholds for mammalian effects (1 Leonards et al 1995, 2 Tryphonas 1994, 3 Kihlström et al 1992, 4 Olsson et al 1996a, 5 Boon et al 1987, 6 Ahlborg et al 1992, 7 Helle et al 1976b)

Sum-PCB (ng/g lw) in Arctic mammals compared to thresholds for mammalian effects (1 Leonards et al 1995, 2 Tryphonas 1994, 3 Kihlström et al 1992, 4 Olsson et al 1996a, 5 Boon et al 1987, 6 Ahlborg et [..] 		Sum-PCB (ng/g lw) in Arctic mammals compared to thresholds for mammalian effects (1 Leonards et al 1995, 2 Tryphonas 1994, 3 Kihlström et al 1992, 4 Olsson et al 1996a, 5 Boon et al 1987, 6 Ahlborg et al 1992, 7 Helle et al 1976b)
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