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  • 1
    Publication Date: 2023-05-12
    Keywords: Aerial survey; Beaufort_Sea; Beaufort Sea; DATE/TIME; Date/time end; Delphinapterus leucas; Duration, number of days; Number; OBSE; Observation; Profile/sampling length; Sample amount; Sample comment
    Type: Dataset
    Format: text/tab-separated-values, 41 data points
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  • 2
    Publication Date: 2023-05-12
    Keywords: Aerial survey; Beaufort_Sea; Beaufort Sea; Category; DATE/TIME; Delphinapterus leucas; expected; OBSE; Observation; Parameter; Sample amount; Sample comment
    Type: Dataset
    Format: text/tab-separated-values, 434 data points
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  • 3
    Publication Date: 2023-05-12
    Keywords: all-cis-11,14,17-Eicosatrienoic acid of total fatty acids; all-cis-4,7,10,13,16,19-Docosahexaenoic acid of total fatty acids; all-cis-5,8,11,14,17-Eicosapentaenoic acid of total fatty acids; all-cis-5,8,11,14-Eicosatetraenoic acid of total fatty acids; all-cis-6,9,12-Octadecatrienoic acid of total fatty acids; all-cis-7,10,13,16,19-Docosapentaenoic acid of total fatty acids; all-cis-9,12,15-Octadecatrienoic acid of total fatty acids; all-cis-9,12-Octadecadienoic acid of total fatty acids; Biological sample; BIOS; DATE/TIME; Date/time end; Hudson Bay; Sample type; Standard deviation; Ursus maritimus; W_Hudson_Bay
    Type: Dataset
    Format: text/tab-separated-values, 133 data points
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  • 4
    Publication Date: 2023-05-12
    Keywords: Biological sample; BIOS; DATE/TIME; Date/time end; Female; Hudson Bay; Lipids; Lipids, standard deviation; Male; Sample type; Ursus maritimus; W_Hudson_Bay
    Type: Dataset
    Format: text/tab-separated-values, 56 data points
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  • 5
    Publication Date: 2023-05-12
    Keywords: 3-methylsulfonyl p,p-dichlorodiphenyl dichloroethylene; alpha-Hexachlorocyclohexane; beta-Hexachlorocyclohexane; Biological sample; BIOS; Chlordane; Chlorobenzene; cis-Chlordane; cis-Nonachlor; Confidence interval; DATE/TIME; Date/time end; Dichlorodiphenyltrichloroethane; Dieldrin; Gas chromatography - Mass spectrometry (GC-MS); Heptachlor epoxide; Hexachlorobenzene; Hudson Bay; Mirex; Octachlorostyrene; Oxychlordane; para,para-Dichlorodiphenyldichloroethane; para,para-Dichlorodiphenyldichloroethylene; para,para-Dichlorodiphenyltrichloroethane; Sample type; trans-Chlordane; trans-Nonachlor; Ursus maritimus; W_Hudson_Bay
    Type: Dataset
    Format: text/tab-separated-values, 742 data points
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  • 6
    Publication Date: 2023-05-12
    Keywords: alpha-Hexabromocyclododecane; Biological sample; BIOS; Brominated biphenyl 101; Brominated biphenyl 153; Confidence interval; DATE/TIME; Date/time end; Decabromodiphenyl ethane; Gas chromatography - Mass spectrometry (GC-MS); Hexabromobenzene; Hudson Bay; Pentabromoethylbenzene; Polybrominated diphenyl ethers; Polybrominated diphenyl ethers, congener BDE-100; Polybrominated diphenyl ethers, congener BDE-116; Polybrominated diphenyl ethers, congener BDE-153; Polybrominated diphenyl ethers, congener BDE-154; 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-54; Polybrominated diphenyl ethers, congener BDE-99; Sample type; Ursus maritimus; W_Hudson_Bay
    Type: Dataset
    Format: text/tab-separated-values, 394 data points
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  • 7
    Publication Date: 2023-05-12
    Keywords: Biological sample; BIOS; Confidence interval; DATE/TIME; Date/time end; Gas chromatography - Mass spectrometry (GC-MS); Hudson Bay; Methyl sulfone polychlorinated biphenyl; Methyl sulfone polychlorinated biphenyl 101; Methyl sulfone polychlorinated biphenyl 110; Methyl sulfone polychlorinated biphenyl 132; Methyl sulfone polychlorinated biphenyl 141; Methyl sulfone polychlorinated biphenyl 149; Methyl sulfone polychlorinated biphenyl 49; Methyl sulfone polychlorinated biphenyl 64; Methyl sulfone polychlorinated biphenyl 70; Methyl sulfone polychlorinated biphenyl 87; Methyl sulfone polychlorinated biphenyl 91; Polychlorinated biphenyl; Polychlorinated biphenyl 118; Polychlorinated biphenyl 130; Polychlorinated biphenyl 138; Polychlorinated biphenyl 146; Polychlorinated biphenyl 153; Polychlorinated biphenyl 156; Polychlorinated biphenyl 170; Polychlorinated biphenyl 180; Polychlorinated biphenyl 183; Polychlorinated biphenyl 187; Polychlorinated biphenyl 194; Polychlorinated biphenyl 206; Polychlorinated biphenyl 47; Polychlorinated biphenyl 85; Polychlorinated biphenyl 99; Sample type; Ursus maritimus; W_Hudson_Bay
    Type: Dataset
    Format: text/tab-separated-values, 775 data points
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  • 8
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    Unknown
    PANGAEA
    In:  Supplement to: Asselin, Natalie C; Barber, David G; Stirling, Ian; Ferguson, Steven H; Richard, Pierre R (2011): Beluga (Delphinapterus leucas) habitat selection in the eastern Beaufort Sea in spring, 1975-1979. Polar Biology, 34(12), 1973-1988, https://doi.org/10.1007/s00300-011-0990-5
    Publication Date: 2023-12-13
    Description: An understanding of the adaptability of belugas (Delphinapterus leucas) to changing ice conditions is required to interpret and predict possible changes in habitat selection in response to projected loss of sea ice throughout the circumpolar Arctic. We analyzed beluga observations made during spring aerial surveys for ringed seals conducted from 1975 to 1979 in the eastern Beaufort Sea. Despite interannual variability in the extent and distribution of sea ice, belugas consistently selected areas with water depths of 200-500 m and heavy ice concentrations (8/10 to 10/10) while areas of open water to light ice concentrations (0/10 to 1/10) were not selected. Belugas were also found in proximity to regions with 〉0.5 degrees seafloor slope which include the continental slope and other areas with the potential for oceanographic upwellings. In most years (4 of 5), fast-ice edges and coastal areas were not selected. In the lightest ice year analyzed, belugas showed less specificity in habitat selection as their distribution expanded and shifted shoreward to fast-ice edges. The observed distribution is discussed in terms of predator-prey relationships particularly with reference to beluga feeding on polar cod (Boreogadus saida). More research is required to examine and compare possible changes in distribution since the late 1970s and to investigate the factors driving the patterns described.
    Keywords: Beaufort_Sea; Beaufort Sea; International Polar Year (2007-2008); IPY; OBSE; Observation
    Type: Dataset
    Format: application/zip, 2 datasets
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  • 9
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    Unknown
    PANGAEA
    In:  Supplement to: McKinney, Melissa A; Stirling, Ian; Lunn, Nick J; Peacock, Elizabeth; Letcher, Robert J (2010): The role of diet on long-term concentration and pattern trends of brominated and chlorinated contaminants in western Hudson Bay polar bears, 1991–2007. Science of the Total Environment, 408(24), 6210-6222, https://doi.org/10.1016/j.scitotenv.2010.08.033
    Publication Date: 2023-12-13
    Description: Adipose tissue was sampled from the western Hudson Bay (WHB) subpopulation of polar bears at intervals from 1991 to 2007 to examine temporal trends of PCB and OCP levels both on an individual and sum-contaminant basis. We also determined levels and temporal trends of emerging polybrominated diphenyl ethers (PBDEs), hexabromocyclododecane (HBCD), polybrominated biphenyls (PBBs) and other current-use brominated flame retardants. Over the 17-year period, sum DDT (and p,p'-DDE, p,p'-DDD, p,p'-DDT) decreased (-8.4%/year); alpha-hexachlorocyclohexane (alpha-HCH) decreased (-11%/year); beta-HCH increased ( + 8.3%/year); and sum PCB and sum chlordane (CHL), both contaminants at highest concentrations in all years (〉1 ppm), showed no distinct trends even when compared to previous data for this subpopulation dating back to 1968. Some of the less persistent PCB congeners decreased significantly (-1.6%/year to -6.3%/year), whereas CB153 levels tended to increase (+ 3.3%/year). Parent CHLs (c-nonachlor, t-nonachlor) declined, whereas non-monotonic trends were detected for metabolites (heptachlor epoxide, oxychlordane). sum chlorobenzene, octachlorostyrene, sum mirex, sum MeSO2-PCB and dieldrin did not significantly change. Increasing sum PBDE levels (+13%/year) matched increases in the four consistently detected congeners, BDE47, BDE99, BDE100 and BDE153. Although no trend was observed, total-(alpha)-HBCD was only detected post-2000. Levels of the highest concentration brominated contaminant, BB153, showed no temporal change. As long-term ecosystem changes affecting contaminant levels may also affect contaminant patterns, we examined the influence of year (i.e., aging or "weathering" of the contaminant pattern), dietary tracers (carbon stable isotope ratios, fatty acid patterns) and biological (age/sex) group on congener/metabolite profiles. Patterns of PCBs, CHLs and PBDEs were correlated with dietary tracers and biological group, but only PCB and CHL patterns were correlated with year. DDT patterns were not associated with any explanatory variables, possibly related to local DDT sources. Contaminant pattern trends may be useful in distinguishing the possible role of ecological/diet changes on contaminant burdens from expected dynamics due to atmospheric sources and weathering.
    Keywords: Biological sample; BIOS; Hudson Bay; International Polar Year (2007-2008); IPY; W_Hudson_Bay
    Type: Dataset
    Format: application/zip, 5 datasets
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  • 10
    Electronic Resource
    Electronic Resource
    Oxford, UK : Blackwell Publishing Ltd
    Marine mammal science 6 (1990), S. 0 
    ISSN: 1748-7692
    Source: Blackwell Publishing Journal Backfiles 1879-2005
    Topics: Biology
    Notes: Polar bears were held in captivity and fasted for an average of 38 d prior to being fed for three days. Blood samples were collected prior to feeding and then at one and three days post-feeding in 1984 and at one, four, and seven days post-feeding in 1985. The ratio of serum urea to serum creatinine varied significantly in 1984, rising from a pre-feeding mean of 11.0 (SE = 2.6) to 32.0 (SE = 3.2) on the first day post-feeding and then dropped to 22.8 (SE =3.2) in the last sample. In 1985, the ratio of serum urea to serum creatinine increased from a pre-feeding mean of 15.8 (SE = 2.3) to 61.2 (SE = 10.6) after three days of feeding and dropped to a mean of 29.2 (SE = 5.1) seven days after feeding ended. Serum urea levels varied over the study period in both years. No significant variation in serum creatinine levels was found in 1984, but in 1985, serum creatinine levels demonstrated significant variation, declining from the pre-feeding mean of 1.83 mg/dl (SE = 0.29) to 0.96 mg/dl (SE = 0.12) in the last sample.The findings suggest that polar bears can have a low serum urea to serum creatinine ratio, similar to that found in hibernating black bears, or higher ratios after feeding. Polar bears can rapidly return to a fasting serum urea to creatinine ratio after food is withheld. Polar bears may demonstrate urea conservation, similar to that found in black bears, and may be able to move between a fasting and a feeding metabolism based on food availability throughout the year, an adaptation to life on the labile sea ice.
    Type of Medium: Electronic Resource
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