| Peer-Reviewed

Analysis and Occurrences of Methoxylated Polybrominated Diphenyl Ethers and Polybrominated Diphenyl Ethers in Channel Catfish, Crayfish, Fish Feeds and Fishmeal from China

Received: 5 August 2014    Accepted: 19 August 2014    Published: 30 August 2014
Views:       Downloads:
Abstract

PBDEs are widely used brominated flame retardant, which are increasingly reported in the environment. MeO-PBDEs are structural analogs to PBDEs, and reported as natural products and novel pollutants present in the environment. Concentrations of thirteen PBDEs and eight MeO-PBDEs in a large number of channel catfish, crayfish, fish feeds and fishmeal collected from Hubei province of China were investigated in this study. A fast isotopic dilution GC-MS method was firstly developed to simultaneously determine thirteen PBDEs and eight MeO-PBDEs in channel catfish, crayfish, fish feeds and fishmeal in this study, and especially for the first time MeO-PBDEs and PBDEs in crayfish, fish feeds and fishmeal. Pressurized liquid extraction and multi-layer silica gel column chromatography cleanup were used, and some important steps and crucial parameters were modified and intensified compared with other literatures. Besides, the conditions of GC and MS were also optimized. The limits of quantitation values of 0.25-5, 1-5 μg kg-1 wet weight in channel catfish and crayfish were calculated for PBDEs and MeO-PBDEs, respectively; so did 1-20, 4-20 μg kg-1 wet weight in fish feeds and fishmeal. In addition, good repeatability and accuracy of the whole method were achieved. The established methods were therefore suitable for the simultaneous determinations of thirteen PBDEs and eight MeO-PBDEs in these samples at trace contamination levels. Using the established methods, PBDEs or MeO-PBDEs emerged in 2 of 80 channel catfish, 1 of 80 crayfish, 6 of 60 fish feeds and 4 of 40 fishmeal, and in low-μg kg-1 wet weight for these samples.

Published in Science Journal of Analytical Chemistry (Volume 2, Issue 3)
DOI 10.11648/j.sjac.20140203.12
Page(s) 17-28
Creative Commons

This is an Open Access article, distributed under the terms of the Creative Commons Attribution 4.0 International License (http://creativecommons.org/licenses/by/4.0/), which permits unrestricted use, distribution and reproduction in any medium or format, provided the original work is properly cited.

Copyright

Copyright © The Author(s), 2024. Published by Science Publishing Group

Keywords

Methoxylated Polybrominated Diphenyl Ethers (MeO-PBDEs), Channel Catfish, Crayfish, Fish Feeds, Fishmeal

References
[1] C.A. De Wit, “An overview of brominated flame retardants in the environment,” Chemosphere 46, pp. 583–624, 2002
[2] I. Watanabe and S.I. Sakai, “Environmental release and behavior of brominated flame retardants,” Environ. Int. 29, pp. 665–682, 2003
[3] M. Alaee, P. Arias, A. Sjodin, and A. Bergman, “An overview of commercially used brominated flame retardants, their applications, their use patterns in different countries/regions and possible modes of release,” Environ. Int. 29, pp. 683–689, 2003
[4] R. Alcock, A.J. Sweetman, K. Prevedouros, and K.C. Jones, “Understanding levels and trends of BDE-47 in the UK and North America: an assessment of principal reservoirs and source inputs,” Environ. Int. 29, pp. 691–698, 2003
[5] B.H. Wilford, T. Harner, J. Zhu, M. Shoeib, and K.C. Jones, “Passive sampling survey of polybrominated diphenyl ether flame retardants in indoor and outdoor air in Ottawa, Canada: implications for sources and exposure,” Environ. Sci. Technol. 38 (20), pp. 5312– 5318, 2004
[6] H.M. Stapleton, N.G. Dodder, J.H. Offenberg, M.M. Schantz, and S.A. Wise, “Polybrominated diphenyl ethers in house dust and clothes dryer lint,” Environ. Sci. Technol. 39 (4), pp. 925–931, 2005
[7] A. Kirkegaard, A. Bignert, U. Sellstrom, M. Olsson, B. Jansson, and C.A. de Wit, “Polybrominated diphenyl ethers (PBDEs) and their methoxylated derivates in pike from Swedish waters with emphasis on temporal trends, 1967–2000,” Environ. Pollut. 130, pp. 187–198, 2004
[8] D. Meironyte, K. Noren, and A. Bergman, “Analysis of polybrominated diphenyl ethers in Swedish human milk. A time-related trend study, 1992–1997,” J. Toxicol. Env. Heal. A 58, pp. 101–113, 1999
[9] P. Haglund, D.R. Zook, H.R. Buser, and J. Hu, “Identification and quantification of polybrominated diphenyl ethers and methoxy-polybrominated diphenyl ethers in Baltic biota,” Environ. Sci. Technol. 31, pp. 3281–3287, 1997
[10] U. Nordlof, B. Helander, A. Bignert, and L. Asplund, “Levels of brominated flame retardants and methoxylated polybrominated diphenyl ethers in eggs of white-tailed sea eagles breeding in different regions of Sweden,” Sci. Total Environ. 409, pp. 238–246, 2010
[11] S. Losada, F.J. Santos, A. Covaci, and M.T. Galceran, “Gas chromatography–ion trap tandem mass spectrometry method for the analysis of methoxylated polybrominated diphenyl ethers in fish,” J. Chromatogr. A 1217, pp. 5253–5260, 2010
[12] W.B. Ameur, S.B. Hassine, E. Eljarrat, Y.E. Megdiche, S. Trabelsi, B. Hammami, D. Barcelo, and M.R. Driss, “Polybrominated diphenyl ethers and their methoxylated analogs in mullet (Mugil cephalus) and sea bass (Dicentrarchus labrax) from Bizerte Lagoon, Tunisia,” Mar. Environ. Res. 72, pp. 258–264, 2011
[13] J.T. Sun, J.Y. Liu, Q. Liu, G.B. Qu, T. Ruan, and G.B. Jiang, “Sample preparation method for the speciation of polybrominated diphenyl ethers and their methoxylated and hydroxylated analogues in diverse environmental matrices,” Talanta 88, pp. 669– 676, 2012
[14] K. Lofstrand, X.T. Liu, D. Lindqvist, S. Jensen, and L. Asplund, “Seasonal variations of hydroxylated and methoxylated brominated diphenyl ethers in blue mussels from the Baltic Sea,” Chemosphere 84, pp. 527–532, 2011
[15] S. Lacorte, M.G. Ikonomou, and M. Fischer, “A comprehensive gas chromatography coupled to high resolution mass spectrometry based method for the determination of polybrominated diphenyl ethers and their hydroxylated and methoxylated metabolites in environmental samples,” J. Chromatogr. A 1217, pp. 337–347, 2010
[16] G.B. Kim and H.M. Stapleton, “PBDEs, methoxylated PBDEs and HBCDs in Japanese common squid (Todarodes pacificus) from Korean offshore waters,” Mar. Pollut. Bull. 60, pp. 935–940, 2010
[17] A. Rotander, B. van Bavel, F. Riget, G.A. Auðunsson, A. Polder, G.W. Gabrielsen, G. Víkingsson, B. Mikkelsen, and M. Dam, “Methoxylated polybrominated diphenyl ethers (MeO-PBDEs) are major contributors to the persistent organobromine load in sub-Arctic and Arctic marine mammals, 1986–2009,” Sci. Total Environ. 416, pp. 482–489, 2012
[18] P.O. Darnerud, G.S. Eriksen, T. Johannesson, P.B. Larsen, and M. Viluksela, “Polybrominated diphenyl ethers: occurrence, dietary exposure and toxicology,” Environ. Health Persp. 109 (Supplement 1), pp. 49–68, 2001
[19] S.N. Kuriyama, C.E. Talsness, K. Grote, and I. Chahoud, “Developmental exposure to low-dose PBDE-99: Effects on male fertility and neurobehavior in rat offspring,” Environ. Health Persp. 113, pp. 149–154, 2005
[20] P. Eriksson, E. Jakobsson, and A. Fredriksson, “Brominated flame retardants: a novel class of developmental neurotoxicants in our environment?” Environ. Health Persp. 109, pp. 903–908, 2001
[21] H. Viberg, A. Fredriksson, and P. Eriksson, “Neonatal exposure to the brominated flame retardant 2,2’,4,4’,5-pentabromodiphenyl ether causes altered susceptibility in the cholinergic transmitter system in the adult mouse,” Toxicol. Sci. 67, pp. 104–107, 2002
[22] H. Viberg, A. Fredriksson, and P. Eriksson, “Neonatal exposure to polybrominated diphenyl ether (PBDE 153) disrupts spontaneous behaviour, impairs learning and memeory, and decreases hippocampal cholinergic receptors in adult mice,” Toxicol. Appl. Pharm. 192, pp. 95–106, 2003
[23] T. Zhou, M.M. Taylor, M.J. DeVito, and K.M. Crofton, “Developmental exposure to brominated diphenyl ethers results in thyroid hormone disruption,” Toxicol. Sci. 66, pp. 105–116, 2002
[24] I. Branchi, E. Alleva, and L.G. Costa, “Effects of perinatal exposure to a polybrominated diphenyl ether (PBDE-99) on mouse neurobehavioural development,” Neurotoxicology 23, pp. 375–384, 2002
[25] I. Branchi, F. Capone, E. Alleva, and L.G. Costa, “Polybrominated diphenyl ethers: neurobehavioral effects following developmental exposure,” Neurotoxicology 24, pp. 449–462, 2003
[26] T. Reistad, F. Fonnum, and E. Mariussen, “Neurotoxicity of the pentabrominated diphenyl ether mixture, DE-71, and hexabromocyclododecane (HBCD) in rat cerebellar granule cells in vitro,” Arch. Toxicol. 80, pp. 785–796, 2006
[27] F. Madia, G. Giordano, V. Fattori, A. Vitalone, I. Branchi, F. Capone, and L. G. Costa, “Differential in vitro neurotoxicity of the flame retardant PBDE-99 and of the PCB Aroclor 1254 in human astrocytoma cells,” Toxicol. Lett. 154, pp. 11–21, 2004
[28] X.Z. Hu, Y. Xu, D.C. Hu, Y. Hui, and F.X. Yang, “Apoptosis induction on human hepatoma cells Hep G2 of decabrominated diphenyl ether (PBDE-209),” Toxicol. Lett. 171, pp. 19–28, 2007
[29] X.Z. Hu, D.C. Hu, and Y. Xu, “Effects of tetrabrominated diphenyl ether and hexabromocyclododecanes in single and complex exposure to hepatoma HepG2 cells,” Environ. Toxicol. Phar. 27, pp. 327–337, 2009
[30] Y.H. He, M.B. Murphy, R.M.K. Yu, M.H.W. Lam, M. Hecker, J.P. Giesy, R.S.S. Wu, and P.K.S. Lam, “Effects of 20 PBDE metabolites on steroidogenesis in the H295R cell line,” Toxicol. Lett. 176, pp. 230–238, 2008
[31] R.F. Song, Y.H. He, M.B. Murphy, L.W.Y. Yeung, R.M.K. Yu, M.H.W. Lam, P.K.S. Lam, M. Hecker, J.P. Giesy, S.S. WuRudolf, W.B. Zhang, G.Y. Sheng, and J.M. Fu, “Effects of fifteen PBDE metabolites, DE71, DE79 and TBBPA on steroidogenesis in the H295R cell line,” Chemosphere 71, pp. 1888–1894, 2008
[32] X.Z. Hu, D.C. Hu, Q. Song, J. Li, P. Wang, and S.F. Guo, “Analysis and occurrences of perfluorinated compounds in agricultural and aquatic products and water from China,” J. Liq. Chromatogr. R. T. 34, pp. 2196–2210, 2011
[33] X.Z. Hu, D.C. Hu, Q. Song, J. Li, and P. Wang, “Determinations of hexabromocyclododecane (HBCD) isomers in channel catfish, crayfish, hen eggs and fish feeds from China by isotopic dilution LC–MS/MS,” Chemosphere 82, pp. 698–707, 2011
[34] X.Z. Hu, Y. Xu, and A. YEDILER, “Determinations of Residual Furazolidone and Its Metabolite, 3-Amino-2-oxazolidinone (AOZ), in Fish Feeds by HPLC-UV and LC-MS/MS, Respectively,” J. Agric. Food Chem. 55, pp. 1144–1149, 2007
[35] ISO 22032–2006 Water quality–Determination of selected polybrominated diphenyl ethers in sediment and sewage sludge–Method using extraction and gas chromatography/mass spectrometry.
[36] EPA Method 1614 Brominated Diphenyl Ethers in Water Soil, Sediment and Tissue by HRGC/HRMS.
Cite This Article
  • APA Style

    Xiaozhong Hu, Decong Hu, Hui Wang, Wei Chen, Bin Wu, et al. (2014). Analysis and Occurrences of Methoxylated Polybrominated Diphenyl Ethers and Polybrominated Diphenyl Ethers in Channel Catfish, Crayfish, Fish Feeds and Fishmeal from China. Science Journal of Analytical Chemistry, 2(3), 17-28. https://doi.org/10.11648/j.sjac.20140203.12

    Copy | Download

    ACS Style

    Xiaozhong Hu; Decong Hu; Hui Wang; Wei Chen; Bin Wu, et al. Analysis and Occurrences of Methoxylated Polybrominated Diphenyl Ethers and Polybrominated Diphenyl Ethers in Channel Catfish, Crayfish, Fish Feeds and Fishmeal from China. Sci. J. Anal. Chem. 2014, 2(3), 17-28. doi: 10.11648/j.sjac.20140203.12

    Copy | Download

    AMA Style

    Xiaozhong Hu, Decong Hu, Hui Wang, Wei Chen, Bin Wu, et al. Analysis and Occurrences of Methoxylated Polybrominated Diphenyl Ethers and Polybrominated Diphenyl Ethers in Channel Catfish, Crayfish, Fish Feeds and Fishmeal from China. Sci J Anal Chem. 2014;2(3):17-28. doi: 10.11648/j.sjac.20140203.12

    Copy | Download

  • @article{10.11648/j.sjac.20140203.12,
      author = {Xiaozhong Hu and Decong Hu and Hui Wang and Wei Chen and Bin Wu and Changjun Lin},
      title = {Analysis and Occurrences of Methoxylated Polybrominated Diphenyl Ethers and Polybrominated Diphenyl Ethers in Channel Catfish, Crayfish, Fish Feeds and Fishmeal from China},
      journal = {Science Journal of Analytical Chemistry},
      volume = {2},
      number = {3},
      pages = {17-28},
      doi = {10.11648/j.sjac.20140203.12},
      url = {https://doi.org/10.11648/j.sjac.20140203.12},
      eprint = {https://article.sciencepublishinggroup.com/pdf/10.11648.j.sjac.20140203.12},
      abstract = {PBDEs are widely used brominated flame retardant, which are increasingly reported in the environment. MeO-PBDEs are structural analogs to PBDEs, and reported as natural products and novel pollutants present in the environment. Concentrations of thirteen PBDEs and eight MeO-PBDEs in a large number of channel catfish, crayfish, fish feeds and fishmeal collected from Hubei province of China were investigated in this study. A fast isotopic dilution GC-MS method was firstly developed to simultaneously determine thirteen PBDEs and eight MeO-PBDEs in channel catfish, crayfish, fish feeds and fishmeal in this study, and especially for the first time MeO-PBDEs and PBDEs in crayfish, fish feeds and fishmeal. Pressurized liquid extraction and multi-layer silica gel column chromatography cleanup were used, and some important steps and crucial parameters were modified and intensified compared with other literatures. Besides, the conditions of GC and MS were also optimized. The limits of quantitation values of 0.25-5, 1-5 μg kg-1 wet weight in channel catfish and crayfish were calculated for PBDEs and MeO-PBDEs, respectively; so did 1-20, 4-20 μg kg-1 wet weight in fish feeds and fishmeal. In addition, good repeatability and accuracy of the whole method were achieved. The established methods were therefore suitable for the simultaneous determinations of thirteen PBDEs and eight MeO-PBDEs in these samples at trace contamination levels. Using the established methods, PBDEs or MeO-PBDEs emerged in 2 of 80 channel catfish, 1 of 80 crayfish, 6 of 60 fish feeds and 4 of 40 fishmeal, and in low-μg kg-1 wet weight for these samples.},
     year = {2014}
    }
    

    Copy | Download

  • TY  - JOUR
    T1  - Analysis and Occurrences of Methoxylated Polybrominated Diphenyl Ethers and Polybrominated Diphenyl Ethers in Channel Catfish, Crayfish, Fish Feeds and Fishmeal from China
    AU  - Xiaozhong Hu
    AU  - Decong Hu
    AU  - Hui Wang
    AU  - Wei Chen
    AU  - Bin Wu
    AU  - Changjun Lin
    Y1  - 2014/08/30
    PY  - 2014
    N1  - https://doi.org/10.11648/j.sjac.20140203.12
    DO  - 10.11648/j.sjac.20140203.12
    T2  - Science Journal of Analytical Chemistry
    JF  - Science Journal of Analytical Chemistry
    JO  - Science Journal of Analytical Chemistry
    SP  - 17
    EP  - 28
    PB  - Science Publishing Group
    SN  - 2376-8053
    UR  - https://doi.org/10.11648/j.sjac.20140203.12
    AB  - PBDEs are widely used brominated flame retardant, which are increasingly reported in the environment. MeO-PBDEs are structural analogs to PBDEs, and reported as natural products and novel pollutants present in the environment. Concentrations of thirteen PBDEs and eight MeO-PBDEs in a large number of channel catfish, crayfish, fish feeds and fishmeal collected from Hubei province of China were investigated in this study. A fast isotopic dilution GC-MS method was firstly developed to simultaneously determine thirteen PBDEs and eight MeO-PBDEs in channel catfish, crayfish, fish feeds and fishmeal in this study, and especially for the first time MeO-PBDEs and PBDEs in crayfish, fish feeds and fishmeal. Pressurized liquid extraction and multi-layer silica gel column chromatography cleanup were used, and some important steps and crucial parameters were modified and intensified compared with other literatures. Besides, the conditions of GC and MS were also optimized. The limits of quantitation values of 0.25-5, 1-5 μg kg-1 wet weight in channel catfish and crayfish were calculated for PBDEs and MeO-PBDEs, respectively; so did 1-20, 4-20 μg kg-1 wet weight in fish feeds and fishmeal. In addition, good repeatability and accuracy of the whole method were achieved. The established methods were therefore suitable for the simultaneous determinations of thirteen PBDEs and eight MeO-PBDEs in these samples at trace contamination levels. Using the established methods, PBDEs or MeO-PBDEs emerged in 2 of 80 channel catfish, 1 of 80 crayfish, 6 of 60 fish feeds and 4 of 40 fishmeal, and in low-μg kg-1 wet weight for these samples.
    VL  - 2
    IS  - 3
    ER  - 

    Copy | Download

Author Information
  • Technology Center of Hubei Entry-Exit Inspection and Quarantine Bureau of PRC, Qintai Road 588, Wuhan 430050, China

  • Technology Center of Hubei Entry-Exit Inspection and Quarantine Bureau of PRC, Qintai Road 588, Wuhan 430050, China

  • Technology Center of Hubei Entry-Exit Inspection and Quarantine Bureau of PRC, Qintai Road 588, Wuhan 430050, China

  • Technology Center of Hubei Entry-Exit Inspection and Quarantine Bureau of PRC, Qintai Road 588, Wuhan 430050, China

  • Technology Center of Liaoning Entry-Exit Inspection and Quarantine Bureau of PRC, Changjiang East Road 60, Dalian 116001, China

  • Technology Center of Liaoning Entry-Exit Inspection and Quarantine Bureau of PRC, Changjiang East Road 60, Dalian 116001, China

  • Sections