Literature DB >> 11996380

Body burdens and tissue concentrations of organochlorines in polar bears (Ursus maritimus) vary during seasonal fasts.

S C Polischu1, R J Norstrom, M A Ramsay.   

Abstract

Lipophilic organochlorines (OCs) are ingested by mammals through their foods and are generally stored in adipose tissue depots. For some species, such as polar bears, the size of these depots can fluctuate seasonally by several-fold. However, the effect of these fluctuations on the fate of stored OCs in an animal with such labile lipid depots is unknown. We determined the whole body burden and tissue concentrations of OCs in free-ranging polar bears categorized by age (cubs-of-the-year, yearlings and adults) and sex before and after a fast averaging 56 days. Adipose tissue, plasma, and milk samples were analysed for sum of chlorobenzenes (sigma-ClBzs), hexachlorocyclohexanes (sigma-HCHs), chlordanes (sigma-CHLORs), dichlorodiphenyltrichloroethane compounds (sigma-DDTs) and polychlorinated biphenyls (sigma-PCBs). Decline in body mass during fasting ranged from 0.2 kg/day for cubs-of-the-year to 0.9 kg/day for sub-adult and adult males. Although all bears showed a decline in both lipid and lean mass during fasting, patterns of OC whole body burden changes were not consistent among compounds and bear classes. The burdens of sigma-DDTs declined by 11-50% for most bears during fasting, those of sigma-CHLORs declined by 67% during fasting in sub-adult and adult males but remained constant for all females, indicating male-specific metabolism of sigma-CHLORs. As fat depots became depleted, OC concentrations in the remaining adipose tissue varied; sigma-DDTs and sigma-HCHs declined while those of sigma-CHLORs and sigma-PCBs generally increased. Thus. within a 3-4 month fast, most polar bears were able to significantly rid their adipose tissue of sigma-DDTs and sigma-HCHs. Burdens of sigma-CHLORs (except males), sigma-ClBzs and sigma-PCBs remained constant for all classes of bears, therefore there was no significant excretion or metabolism during the fast of the specific congeners in these compound classes typically found in polar bears. The ratio of plasma/adipose tissue and milk/adipose tissue OC concentrations was the same for before and after the fast indicating that OC concentrations in polar bears are probably at a steady state among various body compartments. Concentrations of sigma-CHLORs and sigma-PCBs in milk almost doubled during the fast. As a consequence of this rise in milk OC concentrations, the whole body concentrations of these compounds increased in nursing cubs. Since developing young may be susceptible to the effects of environmental contaminants, the increased exposure of nursing cubs to OCs during a fast by their mothers is noteworthy.

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Year:  2002        PMID: 11996380     DOI: 10.1016/s0269-7491(01)00278-0

Source DB:  PubMed          Journal:  Environ Pollut        ISSN: 0269-7491            Impact factor:   8.071


  12 in total

1.  Foraging and fasting can influence contaminant concentrations in animals: an example with mercury contamination in a free-ranging marine mammal.

Authors:  Sarah H Peterson; Joshua T Ackerman; Daniel E Crocker; Daniel P Costa
Journal:  Proc Biol Sci       Date:  2018-02-14       Impact factor: 5.349

2.  Blood-based biomarkers of selenium and thyroid status indicate possible adverse biological effects of mercury and polychlorinated biphenyls in Southern Beaufort Sea polar bears.

Authors:  Katrina K Knott; Patricia Schenk; Susan Beyerlein; Daryle Boyd; Gina M Ylitalo; Todd M O'Hara
Journal:  Environ Res       Date:  2011-09-08       Impact factor: 6.498

3.  Probing the Thermodynamics of Biomagnification in Zoo-Housed Polar Bears by Equilibrium Sampling of Dietary and Fecal Samples.

Authors:  Yuhao Chen; Ying Duan Lei; Jaap Wensvoort; Sarra Gourlie; Frank Wania
Journal:  Environ Sci Technol       Date:  2022-05-20       Impact factor: 11.357

4.  Measuring environmental stress in East Greenland polar bears, 1892-1927 and 1988-2009: what does hair cortisol tell us?

Authors:  T Ø Bechshøft; F F Rigét; C Sonne; R J Letcher; D C G Muir; M A Novak; E Henchey; J S Meyer; I Eulaers; V L B Jaspers; M Eens; A Covaci; R Dietz
Journal:  Environ Int       Date:  2012-05-07       Impact factor: 9.621

5.  Simulating polar bear energetics during a seasonal fast using a mechanistic model.

Authors:  Paul D Mathewson; Warren P Porter
Journal:  PLoS One       Date:  2013-09-03       Impact factor: 3.240

6.  Effects of age, adipose percent, and reproduction on PCB concentrations and profiles in an extreme fasting North Pacific marine mammal.

Authors:  Sarah H Peterson; Jason L Hassrick; Anne Lafontaine; Jean-Pierre Thomé; Daniel E Crocker; Cathy Debier; Daniel P Costa
Journal:  PLoS One       Date:  2014-04-22       Impact factor: 3.240

7.  Dietary composition and spatial patterns of polar bear foraging on land in western Hudson Bay.

Authors:  Linda J Gormezano; Robert F Rockwell
Journal:  BMC Ecol       Date:  2013-12-21       Impact factor: 2.964

8.  Projected polar bear sea ice habitat in the Canadian Arctic Archipelago.

Authors:  Stephen G Hamilton; Laura Castro de la Guardia; Andrew E Derocher; Vicki Sahanatien; Bruno Tremblay; David Huard
Journal:  PLoS One       Date:  2014-11-26       Impact factor: 3.240

9.  Interactions between chemical and climate stressors: a role for mechanistic toxicology in assessing climate change risks.

Authors:  Michael J Hooper; Gerald T Ankley; Daniel A Cristol; Lindley A Maryoung; Pamela D Noyes; Kent E Pinkerton
Journal:  Environ Toxicol Chem       Date:  2013-01       Impact factor: 3.742

10.  Is bone mineral composition disrupted by organochlorines in east Greenland polar bears (Ursus maritimus)?

Authors:  Christian Sonne; Rune Dietz; Erik W Born; Frank F Riget; Maja Kirkegaard; Lars Hyldstrup; Robert J Letcher; Derek C G Muir
Journal:  Environ Health Perspect       Date:  2004-12       Impact factor: 9.031

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