Fingerprint of persistent organic pollutants in tissues of Antarctic notothenioid fish
In the present work, persistent organic pollutants (POPs), such as polychlorinated biphenyls (PCBs), dichlorodiphenyltrichloroethane (DDT) and metabolites, polybrominated diphenyl ethers (PBDEs), and hexachlorocyclohexane (HCH) were analyzed in three Antarctic notothenioids fish species: Trematomus...
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| Formato: | Capítulo de libro |
| Lenguaje: | Inglés |
| Publicado: |
Elsevier
2014
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| Acceso en línea: | Registro en Scopus DOI Handle Registro en la Biblioteca Digital |
| Aporte de: | Registro referencial: Solicitar el recurso aquí |
| LEADER | 20513caa a22021017a 4500 | ||
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| 001 | PAPER-14055 | ||
| 003 | AR-BaUEN | ||
| 005 | 20230518204431.0 | ||
| 008 | 170725s2014 xx ||||fo|||| 00| 0 eng|d | ||
| 024 | 7 | |2 scopus |a 2-s2.0-84906705056 | |
| 024 | 7 | |2 cas |a 1,1 dichloro 2,2 bis(4 chlorophenyl)ethane, 72-54-8; 1,1 dichloro 2,2 bis(4 chlorophenyl)ethylene, 72-55-9; alpha hexachlorocyclohexane, 319-84-6; beta hexachlorocyclohexane, 319-85-7; chlorphenotane, 50-29-3; lindane, 58-89-9; 2,2',4,4',5-brominated diphenyl ether; 2,2',4,4'-tetrabromodiphenyl ether; alpha-hexachlorocyclohexane; beta-hexachlorocyclohexane; DDT; Dichlorodiphenyl Dichloroethylene; Halogenated Diphenyl Ethers; hexabrominated diphenyl ether 153; hexabromodiphenyl ether 154; Hydrocarbons, Chlorinated; Lindane; pentabrominated diphenyl ether 100; Polybrominated Biphenyls; Polychlorinated Biphenyls; tribromodiphenyl ether 28; Water Pollutants, Chemical | |
| 040 | |a Scopus |b spa |c AR-BaUEN |d AR-BaUEN | ||
| 030 | |a STEVA | ||
| 100 | 1 | |a Lana, N.B. | |
| 245 | 1 | 0 | |a Fingerprint of persistent organic pollutants in tissues of Antarctic notothenioid fish |
| 260 | |b Elsevier |c 2014 | ||
| 270 | 1 | 0 | |m Altamirano, J.C.; Laboratorio de Qui´mica Ambiental, Instituto Argentino de Nivologi´a, Glaciologi´a y Ciencias Ambientales (IANIGLA)-CONICET, Mendoza, P.O. Box 131 ZC5500, Argentina |
| 506 | |2 openaire |e Política editorial | ||
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| 520 | 3 | |a In the present work, persistent organic pollutants (POPs), such as polychlorinated biphenyls (PCBs), dichlorodiphenyltrichloroethane (DDT) and metabolites, polybrominated diphenyl ethers (PBDEs), and hexachlorocyclohexane (HCH) were analyzed in three Antarctic notothenioids fish species: Trematomus newnesi (TRN), Notothenia coriiceps (NOC) and Notothenia rossii (NOR). The contribution of each POP-family to the total load was as follows: σPCB (40%) > σDDT (27%) > σPBDEs (23%) > σHCH (10%). Among the 23 PCB congeners analyzed, penta-CBs homologues were the prevalent group, followed by hexa-CBs and hepta-CBs. DDT and its metabolites presented the following trend: p, p'-DDT > p, p'-DDE ~ p, p'-DDD. PBDE profile was dominated by BDE-47 and BDE-99 congeners, followed by BDE-100 > BDE-28 > BDE-154, BDE-153. Among HCHs, the γ-HCH isomer was detected in all samples, constituting 69% total HCH load, while α-HCH and β-HCH contributions were 15% and 16%, respectively. The levels of POPs reported here suggest that NOR and NOC are more susceptible to accumulate the analyzed contaminants than TRN, a species not previously analyzed for POPs. Distribution of POPs among different tissues of the three species (muscle, liver, gonads, and gills) was also investigated. Considering lipid weight, the general pattern of POPs distribution in tissues indicated that while gonads showed higher levels of PCBs, DDTs and HCH, the most significant PBDE concentrations were recorded in gills. Also, a comparative analysis of POPs concentration in fish samples from Antarctic area was included. © 2014 Elsevier B.V. |l eng | |
| 593 | |a Laboratorio de Qui´mica Ambiental, Instituto Argentino de Nivologi´a, Glaciologi´a y Ciencias Ambientales (IANIGLA)-CONICET, Mendoza, P.O. Box 131 ZC5500, Mendoza, Argentina | ||
| 593 | |a Facultad de Ciencias Exactas y Naturales, Universidad Nacional de Cuyo, Mendoza, Argentina | ||
| 593 | |a Toxicological Center, Department of Pharmaceutical Sciences, University of Antwerp, Universiteitsplein 1, Wilrijk, Belgium | ||
| 593 | |a Instituto Argentino de Investigacio´n de Zonas A´ridas (IADIZA)-CONICET, Mendoza, Argentina | ||
| 593 | |a Instituto Anta´rtico Argentino (IAA), Buenos Aires, Argentina | ||
| 593 | |a Museo Argentino de Ciencias Naturales Bernardino Rivadavia-CONICET, Buenos Aires, Argentina | ||
| 593 | |a Laboratorio de Estratigrafi´a Glaciar y Geoqui´mica del AguaylaNieve (LEGAN)-IAA-CONICET, Mendoza, Argentina | ||
| 690 | 1 | 0 | |a ANTARCTICA |
| 690 | 1 | 0 | |a NOTOTHENIOIDS |
| 690 | 1 | 0 | |a POPS |
| 690 | 1 | 0 | |a SOUTH SHETLAND ISLANDS |
| 690 | 1 | 0 | |a TISSUE DISTRIBUTION |
| 690 | 1 | 0 | |a ANTARCTICA |
| 690 | 1 | 0 | |a NOTOTHENIOIDS |
| 690 | 1 | 0 | |a POPS |
| 690 | 1 | 0 | |a SOUTH SHETLAND ISLANDS |
| 690 | 1 | 0 | |a TISSUE DISTRIBUTIONS |
| 690 | 1 | 0 | |a 1,1 DICHLORO 2,2 BIS(4 CHLOROPHENYL)ETHANE |
| 690 | 1 | 0 | |a 1,1 DICHLORO 2,2 BIS(4 CHLOROPHENYL)ETHYLENE |
| 690 | 1 | 0 | |a ALPHA HEXACHLOROCYCLOHEXANE |
| 690 | 1 | 0 | |a BETA HEXACHLOROCYCLOHEXANE |
| 690 | 1 | 0 | |a CHLORPHENOTANE |
| 690 | 1 | 0 | |a LINDANE |
| 690 | 1 | 0 | |a POLYBROMINATED DIPHENYL ETHER |
| 690 | 1 | 0 | |a POLYCHLORINATED BIPHENYL |
| 690 | 1 | 0 | |a 2,2',4,4',5-BROMINATED DIPHENYL ETHER |
| 690 | 1 | 0 | |a 2,2',4,4'-TETRABROMODIPHENYL ETHER |
| 690 | 1 | 0 | |a ALPHA-HEXACHLOROCYCLOHEXANE |
| 690 | 1 | 0 | |a BETA-HEXACHLOROCYCLOHEXANE |
| 690 | 1 | 0 | |a CHLORINATED HYDROCARBON |
| 690 | 1 | 0 | |a DIPHENYL ETHER DERIVATIVE |
| 690 | 1 | 0 | |a HEXABROMINATED DIPHENYL ETHER 153 |
| 690 | 1 | 0 | |a HEXABROMODIPHENYL ETHER 154 |
| 690 | 1 | 0 | |a PENTABROMINATED DIPHENYL ETHER 100 |
| 690 | 1 | 0 | |a POLYBROMINATED BIPHENYL |
| 690 | 1 | 0 | |a TRIBROMODIPHENYL ETHER 28 |
| 690 | 1 | 0 | |a WATER POLLUTANT |
| 690 | 1 | 0 | |a BIOACCUMULATION |
| 690 | 1 | 0 | |a CONCENTRATION (COMPOSITION) |
| 690 | 1 | 0 | |a DDD |
| 690 | 1 | 0 | |a DDE |
| 690 | 1 | 0 | |a DDT |
| 690 | 1 | 0 | |a HCH |
| 690 | 1 | 0 | |a LIPID |
| 690 | 1 | 0 | |a METABOLITE |
| 690 | 1 | 0 | |a ORGANIC POLLUTANT |
| 690 | 1 | 0 | |a PBDE |
| 690 | 1 | 0 | |a PCB |
| 690 | 1 | 0 | |a PERCIFORM |
| 690 | 1 | 0 | |a ANIMAL TISSUE |
| 690 | 1 | 0 | |a ANTARCTICA |
| 690 | 1 | 0 | |a ARTICLE |
| 690 | 1 | 0 | |a BIOACCUMULATION |
| 690 | 1 | 0 | |a CONTROLLED STUDY |
| 690 | 1 | 0 | |a FISH |
| 690 | 1 | 0 | |a GILL |
| 690 | 1 | 0 | |a GONAD |
| 690 | 1 | 0 | |a LIVER |
| 690 | 1 | 0 | |a MUSCLE |
| 690 | 1 | 0 | |a NONHUMAN |
| 690 | 1 | 0 | |a NOTOTHENIA CORIICEPS |
| 690 | 1 | 0 | |a NOTOTHENIA ROSSII |
| 690 | 1 | 0 | |a PERSISTENT ORGANIC POLLUTANT |
| 690 | 1 | 0 | |a TISSUE DISTRIBUTION |
| 690 | 1 | 0 | |a TREMATOMUS NEWNESI |
| 690 | 1 | 0 | |a ANIMAL |
| 690 | 1 | 0 | |a ENVIRONMENTAL MONITORING |
| 690 | 1 | 0 | |a FISH |
| 690 | 1 | 0 | |a METABOLISM |
| 690 | 1 | 0 | |a WATER POLLUTANT |
| 690 | 1 | 0 | |a ANTARCTICA |
| 690 | 1 | 0 | |a SOUTH SHETLAND ISLANDS |
| 690 | 1 | 0 | |a ANIMALS |
| 690 | 1 | 0 | |a ANTARCTIC REGIONS |
| 690 | 1 | 0 | |a DDT |
| 690 | 1 | 0 | |a DICHLORODIPHENYL DICHLOROETHYLENE |
| 690 | 1 | 0 | |a ENVIRONMENTAL MONITORING |
| 690 | 1 | 0 | |a FISHES |
| 690 | 1 | 0 | |a HALOGENATED DIPHENYL ETHERS |
| 690 | 1 | 0 | |a HYDROCARBONS, CHLORINATED |
| 690 | 1 | 0 | |a LINDANE |
| 690 | 1 | 0 | |a POLYBROMINATED BIPHENYLS |
| 690 | 1 | 0 | |a POLYCHLORINATED BIPHENYLS |
| 690 | 1 | 0 | |a WATER POLLUTANTS, CHEMICAL |
| 700 | 1 | |a Berton, P. | |
| 700 | 1 | |a Covaci, A. | |
| 700 | 1 | |a Ciocco, N.F. | |
| 700 | 1 | |a Barrera-Oro, E. | |
| 700 | 1 | |a Atencio, A. | |
| 700 | 1 | |a Altamirano, J.C. | |
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