Suitability of a magnetic particle immunoassay for the analysis of PBDEs in Hawaiian euryhaline fish and crabs in comparison with gas chromatography/electron capture detection-ion trap mass spectrometry

被引:25
作者
Xu, Ting [1 ,2 ]
Cho, Il Kyu [1 ]
Wang, Dongli [1 ]
Rubio, Fernando M. [3 ]
Shelver, Weilin L. [4 ]
Gasc, Anne M. E. [5 ]
Li, Ji [2 ]
Li, Qing X. [1 ]
机构
[1] Univ Hawaii Manoa, Dept Mol Biosci & Bioengn, Honolulu, HI 96822 USA
[2] China Agr Univ, Coll Resources & Environm Sci, Beijing 100193, Peoples R China
[3] Abraxis LLC, Warminster, PA 18974 USA
[4] USDA ARS, Biosci Res Lab, Fargo, ND 58105 USA
[5] Encore Inc, Waimanalo, HI 96795 USA
关键词
GC-MS; PBDEs; Aquatic pollution; Fish; ELISA; POLYBROMINATED DIPHENYL ETHERS; BROMINATED FLAME RETARDANTS; POLYCHLORINATED-BIPHENYLS; TEMPORAL TRENDS; SAMPLES; TISSUES; BDE-47; WATERS; RIVER; MILK;
D O I
10.1016/j.envpol.2008.09.033
中图分类号
X [环境科学、安全科学];
学科分类号
08 ; 0830 ;
摘要
A gas chromatograph/electron capture detector-ion trap mass spectrometer (GC/ECD-ITMS) was used for the determination of polybrominated diphenyl ethers (PBDEs) in euryhaline fish and crabs. GC/ECD-ITMS results showed that average recoveries from the spiked fish samples are in a range of 58-123% with relative standard deviations (RSDs) of 5-19%. PBDE concentrations obtained from GC/ECD-ITMS ranged from 28 ng/g to 1845 ng/g lipid weight (1w) in all aquatic species collected from Hawaiian brackish waters. The general BIDE congener concentration profile observed in this study is BDE-47 > BDE-100>BDE-154>BDE-99>BDE-153>BDE-28>BDE-183. The ELISA results expressed 2 as BDE-47 equivalents correlated well with those of GC/ECD-ITMS, with a correlation coefficient (R-2=0.68) and regression coefficient (slope=0.82). Comparison of ELISA with GC/ECD-ITMS results demonstrated that ELISA provides a timely and cost-effective method to screen PBDEs in fish and crab samples. (C) 2008 Elsevier Ltd. All rights reserved.
引用
收藏
页码:417 / 422
页数:6
相关论文
共 38 条
[1]   Polybrominated diphenyl ethers in fish and wastewater samples from an area of the Penobscot River in Central Maine [J].
Anderson, TD ;
MacRae, JD .
CHEMOSPHERE, 2006, 62 (07) :1153-1160
[2]  
[Anonymous], ENV HLTH CRIT
[3]  
ASPLUND L, 1999, ORGANOHALOGEN COMPD, V40, P351
[4]   Levels of PBDEs. PCDDs, PCDFs, and coplanar PCBs in edible fish from California coastal waters [J].
Brown, F. Reber ;
Winkler, Jennifer ;
Visita, Patria ;
Dhaliwal, Joginder ;
Petreas, Myrto .
CHEMOSPHERE, 2006, 64 (02) :276-286
[5]   Comparison of analytical strategies for the chromatographic and mass spectrometric measurement of brominated flame retardants: 1. Polybrominated diphenylethers [J].
Cariou, Ronan ;
Antignac, Jean-Philippe ;
Debrauwer, Laurent ;
Maume, Daniel ;
Monteau, Fabrice ;
Zalko, Daniel ;
le Bizec, Bruno ;
Andre, Francois .
JOURNAL OF CHROMATOGRAPHIC SCIENCE, 2006, 44 (08) :489-497
[6]   Polybrominated diphenyl ethers (PBDEs) in marine fish and blue mussels from southern Greenland [J].
Christensen, JH ;
Glasius, M ;
Pécseli, M ;
Platz, J ;
Pritzl, G .
CHEMOSPHERE, 2002, 47 (06) :631-638
[7]   Developmental neurotoxicity of polybrominated diphenyl ether (PBDE) flame retardants [J].
Costa, Lucio G. ;
Giordano, Gennaro .
NEUROTOXICOLOGY, 2007, 28 (06) :1047-1067
[8]  
de Boer J, 2000, HANDB ENVIRON CHEM, V3, P61
[9]   An overview of brominated flame retardants in the environment [J].
de Wit, CA .
CHEMOSPHERE, 2002, 46 (05) :583-624
[10]  
Dodder NG, 2002, ENVIRON SCI TECHNOL, V36, P146, DOI 10.1021/es010947g