Body measurements and blood plasma lipid, PCB and OH-PCB content of polar bear (U. maritimus) mothers and cubs, Svalbard
Cobertura |
MEDIAN LATITUDE: 77.700000 * MEDIAN LONGITUDE: 20.950000 * SOUTH-BOUND LATITUDE: 77.400000 * WEST-BOUND LONGITUDE: 18.000000 * NORTH-BOUND LATITUDE: 78.000000 * EAST-BOUND LONGITUDE: 23.900000 * DATE/TIME START: 1998-04-14T00:00:00 * DATE/TIME END: 2008-04-21T00:00:00 |
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Data(s) |
27/02/2012
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Resumo |
The aim of this study was to examine the plasma concentrations and prevalence of polychlorinated biphenyls (PCBs) and hydroxylated PCB-metabolites (OH-PCBs) in polar bear (Ursus maritimus) mothers (n = 26) and their 4 months old cubs-of-the-year (n = 38) from Svalbard to gain insight into the mother-cub transfer, biotransformation and to evaluate the health risk associated with the exposure to these contaminants. As samplings were performed in 1997/1998 and 2008, we further investigated the differences in levels and pattern of PCBs between the two sampling years. The plasma concentrations of Sum(21)PCBs (1997/1998: 5710 ± 3090 ng/g lipid weight [lw], 2008: 2560±1500 ng/g lw) and Sum(6)OH-PCBs (1997/1998: 228 ± 60 ng/g wet weight [ww], 2008: 80 ± 38 ng/g ww) in mothers were significantly lower in 2008 compared to in 1997/1998. In cubs, the plasma concentrations of Sum(21)PCBs (1997/1998: 14680 ± 5350 ng/g lw, 2008: 6070 ± 2590 ng/g lw) and Sum(6)OH-PCBs (1997/1998: 98 ± 23 ng/g ww, 2008: 49 ± 21 ng/g ww) were also significantly lower in 2008 than in 1997/1998. Sum(21)PCBs in cubs was 2.7 ± 0.7 times higher than in their mothers. This is due to a significant maternal transfer of these contaminants. In contrast, Sum(6)OH-PCBs in cubs were approximately 0.53 ± 0.16 times the concentration in their mothers. This indicates a lower maternal transfer of OH-PCBs compared to PCBs. The majority of the metabolite/precursor-ratios were lower in cubs compared to mothers. This may indicate that cubs have a lower endogenous capacity to biotransform PCBs to OH-PCBs than polar bear mothers. Exposure to PCBs and OH-PCBs is a potential health risk for polar bears, and the levels of PCBs and OH-PCBs in cubs from 2008 were still above levels associated with health effects in humans and wildlife. |
Formato |
application/zip, 2 datasets |
Identificador |
https://doi.pangaea.de/10.1594/PANGAEA.808112 doi:10.1594/PANGAEA.808112 |
Idioma(s) |
en |
Publicador |
PANGAEA |
Direitos |
CC-BY: Creative Commons Attribution 3.0 Unported Access constraints: unrestricted |
Fonte |
Supplement to: Bytingsvik, Jenny; Lie, Elisabeth; Aars, Jon; Derocher, Andrew E; Wiig, Øystein; Jenssen, Bjørn Munro (2012): PCBs and OH-PCBs in polar bear mother-cub pairs: A comparative plasma levels in 1998 and 2008. Science of the Total Environment, 417, 117-128, doi:10.1016/j.scitotenv.2011.12.033 |
Palavras-Chave | ##0.33 = ~4 months; µg/g lipid weight; 3'-OH-CB138; 3'-OH-CB138; ng/g wet weight; 3'-OH-CB180; 3'-OH-CB180; ng/g wet weight; 4'-OH-CB159; 4'-OH-CB159; ng/g wet weight; 4'-OH-CB172/Cl7-OH-PCB; 4'-OH-CB172/Cl7-OH-PCB; ng/g wet weight; 4-OH-CB107; 4-OH-CB107; ng/g wet weight; 4-OH-CB146; 4-OH-CB146; ng/g wet weight; 4-OH-CB187; 4-OH-CB187; ng/g wet weight; Age; Age, relative, number of years; Age, standard deviation; Age std dev; body condition index; capture day; Date/Time; DATE/TIME; day of capture; Day of the year; dorsal straight-line length; DOY; Event; Gas chromatography - Mass spectrometry (GC-MS); g ax; Girth, axillary; head length; Hydroxy-polychlorinated biphenyl; Hydroxy-polychlorinated biphenyl, standard deviation; Hydroxy-polychlorinated biphenyl 107; Hydroxy-polychlorinated biphenyl 138; Hydroxy-polychlorinated biphenyl 146; Hydroxy-polychlorinated biphenyl 159; Hydroxy-polychlorinated biphenyl 180; Hydroxy-polychlorinated biphenyl 187; Index; index BCI; International Polar Year (2007-2008); IPY; l; Lat e; Latitude, error; Length; Length, standard deviation; Lipids; Lipids, standard deviation; Lipids std dev; Lon e; Longitude, error; l std dev; OH-PCB; OH-PCB_107; OH-PCB_138; OH-PCB_146; OH-PCB_159; OH-PCB_180; OH-PCB_187; OH-PCB std dev; PCB_101; PCB_105; PCB_114; PCB_118; PCB_128; PCB_137; PCB_138; PCB_153; PCB_156; PCB_157; PCB_167; PCB_170; PCB_180; PCB_183; PCB_187; PCB_189; PCB_194; PCB_206; PCB_47; PCB_74; PCB_99; PCB-101; PCB-105; PCB-114; PCB-118; PCB-128; PCB-137; PCB-138; PCB-153; PCB-156; PCB-157; PCB-167; PCB-170; PCB-180; PCB-183; PCB-187; PCB-189; PCB-194; PCB-206; PCB-47; PCB-74; PCB-99; PCB std dev; Polychlorinated biphenyl, standard deviation; Polychlorinated biphenyl 101; Polychlorinated biphenyl 105; Polychlorinated biphenyl 114; Polychlorinated biphenyl 118; Polychlorinated biphenyl 128; Polychlorinated biphenyl 137; Polychlorinated biphenyl 138; Polychlorinated biphenyl 153; Polychlorinated biphenyl 156; Polychlorinated biphenyl 157; Polychlorinated biphenyl 167; Polychlorinated biphenyl 170; Polychlorinated biphenyl 180; Polychlorinated biphenyl 183; Polychlorinated biphenyl 187; Polychlorinated biphenyl 189; Polychlorinated biphenyl 194; Polychlorinated biphenyl 206; Polychlorinated biphenyl 47; Polychlorinated biphenyl 74; Polychlorinated biphenyl 99; sample amount; Sample type; Samp type; Standard deviation; Std dev; straight length; U. maritimus; U. maritimus m; U. maritimus mass; Ursus maritimus; Ursus maritimus, mass; w; Width; Width, standard deviation; w std dev; zygomatic width |
Tipo |
Dataset |