(Table 1) Neutral and phenolic organohalogen compounds in blubber samples of ringed seals (Pusa hispida) from East Greenland

Fuente: PANGAEA
Salvato in:
Dettagli Bibliografici
Autori principali: Letcher, Robert J, Gebbink, Wouter A, Sonne, Christian, Born, Erik W, McKinney, Melissa A, Dietz, Rune
Natura: Dataset Open Access
Lingua:en
Pubblicazione: PANGAEA 2009
Soggetti:
Accesso online:
Tags: Aggiungi Tag
Nessun Tag, puoi essere il primo ad aggiungerne!!
_version_ 1867168142610923520
author Letcher, Robert J
Gebbink, Wouter A
Sonne, Christian
Born, Erik W
McKinney, Melissa A
Dietz, Rune
author_facet Letcher, Robert J
Gebbink, Wouter A
Sonne, Christian
Born, Erik W
McKinney, Melissa A
Dietz, Rune
collection Datos científicos de ciencias marinas y ambientales
contents We report on the comparative bioaccumulation, biotransformation and/or biomagnification from East Greenland ringed seal (Pusa hispida) blubber to polar bear (Ursus maritimus) tissues (adipose, liver and brain) of various classes and congeners of persistent chlorinated and brominated contaminants and metabolic by-products: polychlorinated biphenyls (PCBs), chlordanes (CHLs), hydroxyl (OH-) and methylsulfonyl (MeSO2-) PCBs, polybrominated biphenyls (PBBs), OH-PBBs, polybrominated diphenyl ether (PBDE) and hexabromocyclododecane (HBCD) flame retardants and OH- and methoxyl (MeO-) PBDEs, 2,2-dichloro-bis(4-chlorophenyl)ethene (p,p'-DDE), 3-MeSO2-p,p'-DDE, pentachlorophenol (PCP) and 4-OH-heptachlorostyrene (4-OH-HpCS). We detected all of the investigated contaminants in ringed seal blubber with high frequency, the main diet of East Greenland bears, with the exception of OH-PCBs and 4-OH-HpCS, which indicated that these phenolic contaminants were likely of metabolic origin and formed in the bears from accumulated PCBs and octachlorostyrene (OCS), respectively, rather than being bioaccumulated from a seal blubber diet. For all of the detectable sum of classes or individual organohalogens, in general, the ringed seal to polar bear mean BMFs for SumPCBs, p,p'-DDE, SumCHLs, SumMeSO2-PCBs, 3-MeSO2-p,p'-DDE, PCP, SumPBDEs, total-(alpha)-HBCD, SumOH-PBDEs, SumMeO-PBDEs and SumOH-PBBs indicated that these organohalogens bioaccumulate, and in some cases there was tissue-specific biomagnification, e.g., BMFs for bear adipose and liver ranged from 2 to 570. The blood-brain barrier appeared to be effective in minimizing brain accumulation as BMFs were <= 1 in the brain, with the exception of SumOH-PBBs (mean BMF = 93±54). Unlike OH-PCB metabolites, OH-PBDEs in the bear tissues appeared to be mainly accumulated from the seal blubber rather than being metabolic formed from PBDEs in the bears. In vitro PBDE depletion assays using polar bear hepatic microsomes, wherein the rate of oxidative metabolism of PBDE congeners was very slow, supported the probability that accumulation from seals is the main source of OH-PBDEs in the bear tissues. Our findings demonstrated from ringed seal to polar bears that organohalogen biotransformation, bioaccumulation and/or biomagnification varied widely and depended on the contaminant in question. Our results show the increasing complexity of bioaccumulated and in some cases biomagnified, chlorinated and brominated contaminants and/or metabolites from the diet may be a contributing stress factor in the health of East Greenland polar bears.
format Dataset Open Access
id pangaea_https___doi_org_10_1594_PANGAEA_815795
institution PANGAEA
language en
publishDate 2009
publisher PANGAEA
record_format pangaea
spellingShingle (Table 1) Neutral and phenolic organohalogen compounds in blubber samples of ringed seals (Pusa hispida) from East Greenland
Letcher, Robert J
Gebbink, Wouter A
Sonne, Christian
Born, Erik W
McKinney, Melissa A
Dietz, Rune
3-methylsulfonyl p,p-dichlorodiphenyl dichloroethylene; 4-hydroxy-heptachlorostyrene; alpha-Hexabromocyclododecane; Biological sample; BIOS; Brominated biphenyl, standard deviation; Brominated biphenyl 101; Chlordane; Chlordane, standard deviation; DATE/TIME; Date/time end; Dichlorodiphenyldichloroethylene, standard deviation; East Greenland; Hexabromocyclododecane, standard deviation; Hydroxylated polybrominated biphenyl; Hydroxylated polybrominated biphenyl, standard deviation; Hydroxylated polybrominated diphenyl ethers; Hydroxylated polybrominated diphenyl ethers, standard deviation; Hydroxy-polychlorinated biphenyl; International Polar Year (2007-2008); IPY; Ittoqqort_Scoreby; Lipids; Lipids, standard deviation; Methoxylated polybrominated diphenyl ethers; Methoxylated polybrominated diphenyl ethers, standard deviation; Methyl sulfone polychlorinated biphenyl; Methyl sulfone polychlorinated biphenyl, standard deviation; para,para-Dichlorodiphenyldichloroethylene; Pentachlorophenol; Pentachlorophenol, standard deviation; Polybrominated diphenyl ethers; Polybrominated diphenyl ethers, standard deviation; Polychlorinated biphenyl; Polychlorinated biphenyl, standard deviation; Sample type; Species
We report on the comparative bioaccumulation, biotransformation and/or biomagnification from East Greenland ringed seal (Pusa hispida) blubber to polar bear (Ursus maritimus) tissues (adipose, liver and brain) of various classes and congeners of persistent chlorinated and brominated contaminants and metabolic by-products: polychlorinated biphenyls (PCBs), chlordanes (CHLs), hydroxyl (OH-) and methylsulfonyl (MeSO2-) PCBs, polybrominated biphenyls (PBBs), OH-PBBs, polybrominated diphenyl ether (PBDE) and hexabromocyclododecane (HBCD) flame retardants and OH- and methoxyl (MeO-) PBDEs, 2,2-dichloro-bis(4-chlorophenyl)ethene (p,p'-DDE), 3-MeSO2-p,p'-DDE, pentachlorophenol (PCP) and 4-OH-heptachlorostyrene (4-OH-HpCS). We detected all of the investigated contaminants in ringed seal blubber with high frequency, the main diet of East Greenland bears, with the exception of OH-PCBs and 4-OH-HpCS, which indicated that these phenolic contaminants were likely of metabolic origin and formed in the bears from accumulated PCBs and octachlorostyrene (OCS), respectively, rather than being bioaccumulated from a seal blubber diet. For all of the detectable sum of classes or individual organohalogens, in general, the ringed seal to polar bear mean BMFs for SumPCBs, p,p'-DDE, SumCHLs, SumMeSO2-PCBs, 3-MeSO2-p,p'-DDE, PCP, SumPBDEs, total-(alpha)-HBCD, SumOH-PBDEs, SumMeO-PBDEs and SumOH-PBBs indicated that these organohalogens bioaccumulate, and in some cases there was tissue-specific biomagnification, e.g., BMFs for bear adipose and liver ranged from 2 to 570. The blood-brain barrier appeared to be effective in minimizing brain accumulation as BMFs were <= 1 in the brain, with the exception of SumOH-PBBs (mean BMF = 93±54). Unlike OH-PCB metabolites, OH-PBDEs in the bear tissues appeared to be mainly accumulated from the seal blubber rather than being metabolic formed from PBDEs in the bears. In vitro PBDE depletion assays using polar bear hepatic microsomes, wherein the rate of oxidative metabolism of PBDE congeners was very slow, supported the probability that accumulation from seals is the main source of OH-PBDEs in the bear tissues. Our findings demonstrated from ringed seal to polar bears that organohalogen biotransformation, bioaccumulation and/or biomagnification varied widely and depended on the contaminant in question. Our results show the increasing complexity of bioaccumulated and in some cases biomagnified, chlorinated and brominated contaminants and/or metabolites from the diet may be a contributing stress factor in the health of East Greenland polar bears.
title (Table 1) Neutral and phenolic organohalogen compounds in blubber samples of ringed seals (Pusa hispida) from East Greenland
topic 3-methylsulfonyl p,p-dichlorodiphenyl dichloroethylene; 4-hydroxy-heptachlorostyrene; alpha-Hexabromocyclododecane; Biological sample; BIOS; Brominated biphenyl, standard deviation; Brominated biphenyl 101; Chlordane; Chlordane, standard deviation; DATE/TIME; Date/time end; Dichlorodiphenyldichloroethylene, standard deviation; East Greenland; Hexabromocyclododecane, standard deviation; Hydroxylated polybrominated biphenyl; Hydroxylated polybrominated biphenyl, standard deviation; Hydroxylated polybrominated diphenyl ethers; Hydroxylated polybrominated diphenyl ethers, standard deviation; Hydroxy-polychlorinated biphenyl; International Polar Year (2007-2008); IPY; Ittoqqort_Scoreby; Lipids; Lipids, standard deviation; Methoxylated polybrominated diphenyl ethers; Methoxylated polybrominated diphenyl ethers, standard deviation; Methyl sulfone polychlorinated biphenyl; Methyl sulfone polychlorinated biphenyl, standard deviation; para,para-Dichlorodiphenyldichloroethylene; Pentachlorophenol; Pentachlorophenol, standard deviation; Polybrominated diphenyl ethers; Polybrominated diphenyl ethers, standard deviation; Polychlorinated biphenyl; Polychlorinated biphenyl, standard deviation; Sample type; Species
url https://doi.org/10.1594/PANGAEA.815795