(Table 1) Concentrations of persistant organic pollutants in brain and liver of glaucous gulls, Bjørnøya, Svalbard archipelago


Autoria(s): Sagerup, Kjetil; Helgason, Lisa Bjørnsdatter; Polder, Anuschka; Strøm, Hallvard; Josefsen, Terje D; Skaare, Janneche Utne; Gabrielsen, Geir W
Cobertura

LATITUDE: 74.360000 * LONGITUDE: 19.030000

Data(s)

25/07/2009

Resumo

Dead and dying glaucous gulls (Larus hyperboreus) were collected on Bjornoya in the Barents Sea in 2003, 2004 and 2005. Autopsies of the seabirds only explained a clear cause of death for three (14%) of the 21 birds. A total of 71% of the birds were emaciated. Liver and brain samples were analysed for organochlorine pesticides (OCPs), polychlorinated biphenyls (PCBs), polybrominated diphenyl ether (PBDEs), hexabromo-cyclododecanes (HBCDs) and mercury (Hg). High levels of OCPs, PCBs, PBDEs and alpha-HBCD were found in liver and brain. Compared to the dead and dying glaucous gulls found 1989, the congeners' composition tended to change toward more persistent compounds in the 2003-2005 samples. The brain levels of OCPs and PCBs did not differ between 1989 and 2003-2005, while the liver levels were significantly lower. The brain/liver ratio for PCB and PBDE significantly decreased with halogenations of the molecule, indicating a clear discrimination of highly halogenated PCBs and PBDEs entering the brain. There was further a clear negative correlation between contaminant concentrations and body condition. The brain levels were not as high as earlier published lethal levels of p,p'-DDE or PCB. However, more recent studies reported a range of sub-lethal OCP- and PCB-related effects in randomly sampled glaucous gulls. An additional elevation of pollutants due to emaciation may increase the stress of the already affected birds. The high brain levels of OCP, PCB and PBDE of present study might therefore have contributed to the death of weakened individuals of glaucous gull.

Formato

text/tab-separated-values, 363 data points

Identificador

https://doi.pangaea.de/10.1594/PANGAEA.786530

doi:10.1594/PANGAEA.786530

Idioma(s)

en

Publicador

PANGAEA

Direitos

CC-BY: Creative Commons Attribution 3.0 Unported

Access constraints: unrestricted

Fonte

Supplement to: Sagerup, Kjetil; Helgason, Lisa Bjørnsdatter; Polder, Anuschka; Strøm, Hallvard; Josefsen, Terje D; Skaare, Janneche Utne; Gabrielsen, Geir W (2009): Persistent organic pollutants and mercury in dead and dying glaucous gulls (Larus hyperboreus) at Bjornoya (Svalbard). Science of the Total Environment, 407(23), 6009-6016, doi:10.1016/j.scitotenv.2009.08.020

Palavras-Chave #alpha-Hexabromocyclododecane; alpha-Hexachlorocyclohexane; Bear Island; beta-Hexachlorocyclohexane; Bjørnøya; Bjørnøya, Svalbard archipelago, Norway; Chlordane, standard deviation; cis-Chlordane; Dichlorodiphenyldichloroethylene, standard deviation; gamma-Hexachlorocyclohexane (Lindane); Gas chromatography - Mass spectrometry (GC-MS); HAND; Hexabromocyclododecane, standard deviation; Hexachlorobenzene; Hexachlorocyclohexane, standard deviation; International Polar Year (2007-2008); ipy; IPY; Lipids; Lipids, total, standard deviation; Method comment; Mirex; Mirex, standard deviation; Oxychlordane; para,para-Dichlorodiphenyldichloroethylene; Polybrominated diphenyl ethers; Polybrominated diphenyl ethers, congener BDE-100; Polybrominated diphenyl ethers, congener BDE-153; Polybrominated diphenyl ethers, congener BDE-154; Polybrominated diphenyl ethers, congener BDE-183; Polybrominated diphenyl ethers, congener BDE-206; Polybrominated diphenyl ethers, congener BDE-207; Polybrominated diphenyl ethers, congener BDE-208; Polybrominated diphenyl ethers, congener BDE-209; Polybrominated diphenyl ethers, congener BDE-28; Polybrominated diphenyl ethers, congener BDE-47; Polybrominated diphenyl ethers, congener BDE-99; Polybrominated diphenyl ethers, standard deviation; Polychlorinated biphenyl; Polychlorinated biphenyl, standard deviation; Polychlorinated biphenyl 101; Polychlorinated biphenyl 105; Polychlorinated biphenyl 110; Polychlorinated biphenyl 114; Polychlorinated biphenyl 118; Polychlorinated biphenyl 128; Polychlorinated biphenyl 138; Polychlorinated biphenyl 141; Polychlorinated biphenyl 149; Polychlorinated biphenyl 153; Polychlorinated biphenyl 156; Polychlorinated biphenyl 157; Polychlorinated biphenyl 170; Polychlorinated biphenyl 180; Polychlorinated biphenyl 183; Polychlorinated biphenyl 187; Polychlorinated biphenyl 194; Polychlorinated biphenyl 206; Polychlorinated biphenyl 209; Polychlorinated biphenyl 28; Polychlorinated biphenyl 52; Polychlorinated biphenyl 66; Polychlorinated biphenyl 74; Polychlorinated biphenyl 99; Sample type; Sampling by hand; Standard deviation; trans-Nonachlor
Tipo

Dataset