Evaluation of PCDD/Fs, PCBs and PBDEs in two penguin species from Antarctica

被引:20
|
作者
Morales, Patricia [1 ,2 ]
Roscales, Jose L. [1 ]
Munoz-Arnanz, Juan [1 ]
Barbosa, Andres [3 ]
Jimenez, Begona [1 ]
机构
[1] CSIC, Inst Organ Chem, Dept Instrumental Anal & Environm Chem, Juan Cierva 3, Madrid 28006, Spain
[2] Univ Complutense Madrid, Dept Biodivers Ecol & Evolut, Jose Antonio Novais 12, Madrid 28040, Spain
[3] CSIC, Natl Museum Nat Sci Madrid, Dept Evolutionary Ecol, Jose Gutierrez Abascal 2, Madrid 28006, Spain
关键词
Persistent organic pollutants (POPs); Polar birds; LRAT; Pygoscelis antarticus; Pygoscelis papua; TEQ; PERSISTENT ORGANIC POLLUTANTS; POLYBROMINATED DIPHENYL ETHERS; DIBENZO-P-DIOXINS; SOUTH SHETLAND ISLANDS; LONG-RANGE TRANSPORT; POLYCHLORINATED-BIPHENYLS; ORGANOCHLORINE CONTAMINANTS; PYGOSCELIS PENGUINS; MARINE-ENVIRONMENT; SEABIRDS;
D O I
10.1016/j.chemosphere.2021.131871
中图分类号
X [环境科学、安全科学];
学科分类号
08 ; 0830 ;
摘要
Persistent Organic Pollutants (POPs) are a global threat, but impacts of these chemicals upon remote areas such as Antarctica remain unclear. Penguins can be useful species to assess the occurrence of POPs in Antarctic food webs. This work's aim was the evaluation of polychlorodibenzo-p-dioxins and furans (PCDD/Fs), polychlorinated biphenyls (PCBs) and polybrominated diphenyl ethers (PBDEs) in eggs of two penguin species, chinstrap (Pygoscelis antarticus) and gentoo penguins (Pygoscelis papua), breeding in the South Shetland Islands. Results showed a common pattern in POP levels regardless of the species, characterized by a major abundance of PCBs (98 %), followed by PBDEs (1-2%) and PCDD/Fs (<1 %). Concentrations of POPs in chinstrap and gentoo penguin eggs were 482 and 3250 pg/g l.w., respectively. PCBs, PBDEs and PCDD/Fs were found at higher concentrations in chinstrap penguin eggs, being these differences significant for PBDEs. Interspecies differences in POP levels agree well with potential trophic position differences among species due to changes in prey composition and foraging areas. POP profiles were dominated by congeners with a low degree of halogenation. Our results therefore suggest similar sources of POPs in the food webs exploited by both species and in both cases attributable to the long-range transportation rather than to the presence of local sources of POPs. TEQs were found between 1.38 and 7.33 pg/g l.w. and followed the pattern non-ortho dl-PCBs > PCDFs > PCDDs > mono-ortho dl-PCBs. TEQ values were lower than the threshold level for harmful effects in birds of 210 pg/g WHO-TEQ/g l.w.
引用
收藏
页数:9
相关论文
共 50 条
  • [21] Determination of levels of persistent organic pollutants (PCDD/Fs, PBDD/Fs, PBDEs, PCBs, and PBBs) in atmosphere near a municipal solid waste incinerator
    Wang, Mao-Sung
    Chen, Shui-Jen
    Huang, Kuo-Lin
    Lai, Yi-Chieh
    Chang-Chien, Guo-Ping
    Tsai, Jen-Hsiung
    Lin, Wen-Yinn
    Chang, Kuo-Ching
    Lee, Jia-Twu
    CHEMOSPHERE, 2010, 80 (10) : 1220 - 1226
  • [22] Bioaccumulation of PCBs, OCPs and PBDEs in Marine Mammals From West Antarctica
    Khairy, Mohammed
    Brault, Emily
    Dickhut, Rebecca
    Harding, Karin C.
    Harkonen, Tero
    Karlsson, Olle
    Lehnert, Kristine
    Teilmann, Jonas
    Lohmann, Rainer
    FRONTIERS IN MARINE SCIENCE, 2021, 8
  • [23] Temporal trends of PCBs, PCDD/Fs and PBDEs in soils from an E-waste dismantling area in East China
    Wang, Pu
    Zhang, Haidong
    Fu, Jianjie
    Li, Yingming
    Thanh Wang
    Wang, Yawei
    Ren, Daiwei
    Ssebugere, Patrick
    Zhang, Qinghua
    Jiang, Guibin
    ENVIRONMENTAL SCIENCE-PROCESSES & IMPACTS, 2013, 15 (10) : 1897 - 1903
  • [24] Persistent organic pollutants (PCDD/Fs, dioxin-like PCBs, marker PCBs, and PBDEs) in health supplements on the Spanish market
    Marti, M.
    Ortiz, X.
    Gasser, M.
    Marti, R.
    Montana, M. J.
    Diaz-Ferrero, J.
    CHEMOSPHERE, 2010, 78 (10) : 1256 - 1262
  • [25] Levels of PCDD/Fs, PCBs and PBDEs in butter from Turkey and estimated dietary intake from dairy products
    Ucar, Yunus
    Traag, Wim
    Immerzeel, Jaap
    Kraats, Cornelis
    van der Lee, Martijn
    Hoogenboom, Ron
    van der Weg, Guido
    Cakirogullari, Gul Celik
    Oymael, Berrin
    Kilic, Devrim
    FOOD ADDITIVES & CONTAMINANTS PART B-SURVEILLANCE, 2011, 4 (02): : 141 - 151
  • [26] PBDEs, PCBs and PCDD/Fs in the sediments from seven major river basins in China: Occurrence, congener profile and spatial tendency
    Wang, Pu
    Shang, Hongtao
    Li, Honghua
    Wang, Yawei
    Li, Yingming
    Zhang, Haidong
    Zhang, Qinghua
    Liang, Yong
    Jiang, Guibin
    CHEMOSPHERE, 2016, 144 : 13 - 20
  • [27] PCDD/Fs and PCBs in seafood species from Moreton Bay, Queensland, Australia
    Matthews, V.
    Paepke, O.
    Gaus, C.
    MARINE POLLUTION BULLETIN, 2008, 57 (6-12) : 392 - 402
  • [28] Brominated and chlorinated contaminants in food (PCDD/Fs, PCBs, PBDD/Fs PBDEs): Simultaneous determination and occurrence in Italian produce
    Ceci, Roberta
    Diletti, Gianfranco
    Bellocci, Mirella
    Chiumiento, Francesco
    D'Antonio, Silvia
    De Benedictis, Alfonso
    Leva, Manuela
    Pirito, Luigi
    Scortichini, Giampiero
    Fernandes, Alwyn R.
    CHEMOSPHERE, 2022, 288
  • [29] PCDD/Fs and dioxin-like PCBs in fish species from Lake Victoria, East Africa
    Ssebugere, Patrick
    Kiremire, Bernard T.
    Henkelmann, Bernhard
    Bernhoeft, Silke
    Kasozi, Gabriel N.
    Wasswa, John
    Schramm, Karl-Werner
    CHEMOSPHERE, 2013, 92 (03) : 317 - 321
  • [30] Temporal trends (2005-2009) of PCDD/Fs, PCBs, PBDEs in rice hulls from an e-waste dismantling area after stricter environmental regulations
    Fu, Jianjie
    Wang, Thanh
    Wang, Pu
    Qu, Guangbo
    Wang, Yawei
    Zhang, Qinghua
    Zhang, Aiqian
    Jiang, Guibin
    CHEMOSPHERE, 2012, 88 (03) : 330 - 335