Organochlorine Pesticides, Polychlorinated Biphenyls, and Polybrominated Diphenyl Ethers in Irrawaddy Dolphins from India
The Irrawaddy dolphin (Orcaella brevirostris) is at risk of extinction throughout its range as a result of incidental catches, habitat degradation, and pollution. Populations of Irrawaddy dolphins are constrained by the species' narrow habitat requirement-lagoons, estuaries, rivers, and lakes-and are therefore particularly vulnerable to the effects of human activities. In this study, for the first time, concentrations of organochlorine (OC) pesticides, polychlorinated biphenyls (PCBs), and polybrominated diphenyl ethers (PBDEs) were determined in tissues of Irrawaddy dolphins collected from Chilika Lake, India, to understand the status of contamination. Dichlorodiphenyltrichloroethane and its metabolites (DDTs) were the predominant contaminants found in Irrawaddy dolphins; the highest concentration found was 10,000 ng/g lipid weight in blubber. Hexachlorocyclohexanes (HCHs) were the second most prevalent contaminants in dolphin tissues. Concentrations of PCBs, chlordanes, hexachlorobenzene, tris(4-chlorophenyl)methane, and tris(4-chlorophenyl)methanol were in the ranges of few ng/g to few hundreds of ng/g on a lipid-weight basis. In general, concentrations of OC pesticides and PCBs in Irrawaddy dolphins were lower than the concentrations reported for coastal and riverine dolphins collected in Asia. PBDEs were detected in the blubber of Irrawaddy dolphins at concentrations ranging from 0.98 to 18 ng/g lipid weight. BDE congener 47 accounted for 60% to 75% of the total PBDE concentrations. Although these results establish the baseline levels of persistent organic pollutants in Irrawaddy dolphins, efforts should be made to decrease the sources of contamination by DDTs and HCHs in Chilika Lake.
- # Concentrations Of Organochlorine Pesticides
- # Irrawaddy Dolphins
- # Concentrations Of Polychlorinated Biphenyls
- # Dichlorodiphenyltrichloroethane And Its Metabolites
- # Organochlorine Pesticides
- # Polybrominated Diphenyl Ethers
- # Chilika Lake
- # Levels Of Persistent Organic Pollutants
- # Lipid Weight
- # Polychlorinated Biphenyls
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67
- 10.1016/j.envint.2008.08.003
- Sep 18, 2008
- Environment International
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32
- 10.1016/j.chemosphere.2012.10.018
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7
- 10.1007/s10646-015-1475-z
- May 9, 2015
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85
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- Mar 20, 2010
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70
- 10.1021/es901177j
- Aug 19, 2009
- Environmental Science & Technology
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54
- 10.1007/s00244-011-9679-6
- May 19, 2011
- Archives of Environmental Contamination and Toxicology
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32
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- Jun 18, 2014
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53
- 10.1016/j.envres.2016.01.021
- Jan 25, 2016
- Environmental Research
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72
- 10.1016/j.envint.2008.08.002
- Sep 19, 2008
- Environment International
Brominated flame retardants and organochlorines in the European environment using great tit eggs as a biomonitoring tool
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18
- 10.1007/s00244-019-00621-0
- Apr 4, 2019
- Archives of Environmental Contamination and Toxicology
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24
- 10.1007/s11356-017-8659-4
- Mar 9, 2017
- Environmental Science and Pollution Research
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55
- 10.1016/j.envpol.2019.113418
- Oct 17, 2019
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Levels of persistent organic pollutants in pine tree components and ambient air
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120
- 10.1007/s00244-002-0131-9
- Oct 1, 2003
- Archives of Environmental Contamination and Toxicology
Concentrations of organochlorines (OCs) representing persistent organic pollutants (POPs), such as polychlorinated biphenyls (PCBs), dichlorodiphenyl trichloroethane and its metabolites (DDTs), chlordane compounds (CHLs), hexachlorocyclohexane isomers (HCHs), and hexachlorobenzene (HCB), were determined in the liver of skipjack tuna (Katsuwonus pelamis) collected from the offshore waters of various regions in the world (offshore waters around Japan, Taiwan, Philippines, Indonesia, Seychelles, and Brazil, and the Japan Sea, the East China Sea, the South China Sea, the Bay of Bengal, and the North Pacific Ocean). OCs were detected in livers of all of the skipjack tuna collected from the locations surveyed, supporting the thesis that there is widespread contamination of persistent OCs in the marine environment. Within a location, no significant relationship between growth-stage (body length and weight) and OC concentrations (lipid weight basis) was observed, and the OC residue levels were rather uniform among the individuals. Interestingly, the distribution of OC concentrations in skipjack tuna was similar to those in surface seawaters from which they were taken. These results suggest that OC concentrations in skipjack tuna could reflect the pollution levels in seawater from which they are collected and that this species is a suitable bioindicator for monitoring the global distribution of OCs in offshore waters and the open ocean. Concentrations of PCBs and CHLs in skipjack tuna were higher in offshore waters around Japan (up to 1100 and 250 ng/g lipid wt, respectively), suggesting the presence of sources of PCBs and CHLs in Japan. High concentrations of DDTs and HCHs were observed in samples from the Japan Sea, the East China Sea, the South China Sea, and the Bay of Bengal (up to 1300 and 22 ng/g lipid wt, respectively). This result suggests recent use of technical DDT and HCH for agricultural and/or public health purposes in Russia, China, India, and some other developing Asian countries. Relatively high concentrations of PCBs, CHLs, HCHs, and HCB were also observed in samples collected from some locations in the middle of the Pacific Ocean, indicating the expansion of OC contamination on a global scale. Considering these facts, continuous studies monitoring these compounds in offshore waters and the open seas, using skipjack tuna as a bioindicator, are needed to further understand the future trend of contamination.
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92
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- Oct 22, 2013
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