Polybrominated diphenyl ethers in sediment and caged mussels (Elliptio complanata) deployed in the Niagara River.

Polybrominated diphenyl ethers (PBDEs) were detected in caged mussels (Elliptio complanata), deployed in the Niagara River for 3weeks in 2003, 2004 and 2006 and in sediment collected from the river and tributaries. The highest concentrations (measured as the sum of 17 BDE congeners) were in mussels deployed within tributaries to the American side of the River (Cayuga Creek: 11.5ngg(-1) wet wt.; Two Mile Creek 9.5ngg(-1); and Gill Creek: 5.8ngg(-1)). In addition to contributions from the atmosphere, each urban tributary has multiple potential sources of PBDEs which include storm sewers, sewage treatment plants and industries located upstream of the sampling sites. Total PBDE concentrations in sediment ranged from 0.25 to 188ngg(-1). In general, mean mussel tissue concentrations were positively correlated with sediment BDE concentrations. Total PBDE concentrations were higher in mussels deployed at most sites in the Tonawanda Channel which is highly industrialised, compared with mussels deployed on the Canadian side of the upper Niagara River where the surrounding area is generally rural. The sum of BDE-47, -99, -100, -153, -154 and -209 contributed between 92% and 96% of the total BDE concentrations in all of the mussel samples. BDE-209 represented between 39% and 100% of the total BDE in sediment samples. BSAFs in mussels ranged from 1 to 18 depending on the sampling station. Ratios of BDE-47/99 and BDE-100/99 and congener patterns in mussels and sediment were suggestive of the penta formulation as the historical source.

The analysis of halogenated flame retardants by GC-HRMS in environmental samples.

The analytical conditions required to determine polybrominated diphenylethers (PBDEs) and a variety of other halogenated flame retardants (HFRs) by gas chromatography-high resolution mass spectrometry (HRMS) in environmental samples are reported. HRMS can be used to analyze brominated diphenylethers (BDEs), 2,2',4,4',5,5'-hexabromobiphenyl (BB-153) as well as for a number of other emerging HFRs like allyl 2,4,6-tribromophenyl ether (ATE), 2-bromoallyl 2,4,6-tribromophenyl ether (BATE), 2,3-dibromopropyl 2,4,6-tribromophenyl ether (DPTE), octabromotrimethylphenylindane (OBIND), pentabromoethylbenzene (PBEB), hexabromobenzene (HBB), 1,2-bis (2,4,6-tribromophenoxy) ethane (BTBPE), decabromodiphenylethane (DBDPE), Dechlorane Plus (DP), hexachlorocyclopentadienyl-dibromocyclooctane (HCDBCO), tetrabromoethylcyclohexane (TBECH), 1,2,5,6-tetrabromocylcooctane (TBCO), 2-ethylhexyl-2,3,4,5-tetrabromobenzoate (EHTeBB), and bis(2-ethly-1-hexyl)tetrabromophthalate (BEHTBP). The detection in environmental matrices and use of these non-BDE flame retardants is reviewed. A method for the analysis of PBDEs by isotope dilution HRMS and 16 other halogenated compounds primarily used as flame retardants is reported. A survey of selected environmental samples, which included Lake Ontario surface and tributary sediments, municipal wastewater effluent, sludge, and mussel tissues, detected PBDEs, DP, DBDPE, BTBPE, PBEB, BB-153, and HBB.

Factors influencing trends of polychlorinated naphthalenes and other dioxin-like compounds in lake trout (Salvelinus namaycush) from Lake Ontario, North America (1979-2004).

Concentrations of polychlorinated naphthalenes (PCNs) were determined in archived lake trout (Salvelinus namaycush) from Lake Ontario, North America, collected between 1979 and 2004 to evaluate their temporal trends and the factors influencing their trends. Concentrations of PCNs, as well as polychlorinated dibenzo-p-dioxins and dibenzofurans (PCDD/Fs), and non- and mono-ortho-substituted polychlorinated biphenyls (DL-PCBs), which were measured for comparative purposes, declined by eight-, seven-, and fivefold, respectively, between 1979 and 2004. Apparent elimination rate constants (k2) were calculated as the slopes of the regression lines of concentration versus time for PCN, DL-PCB, and PCDD/F congeners to compare the rate of decrease among congeners within and between compound classes. The k2 values for PCNs that had two pairs or three adjacent carbons unsubstituted with chlorine (congeners that can be biotransformed by vertebrates) were not significantly different from zero, indicating no decline in fish. For PCN congeners having no adjacent carbons unsubstituted with chlorine, the k2 values generally increased with hydrophobicity and degree of chlorination. This pattern differed from that of PCDD/Fs and DL-PCBs and from previous findings for non-DL-PCBs, for which the rate of contaminant decline decreased with hydrophobicity, and the pattern also differed from expectations based on thermodynamics. Differences in the rate of decline of PCN congeners may be caused by changes in source or mixture formulations over time and/or metabolic dechlorination of the less stable, higher-chlorinated PCNs 73, 74, and 75 to lower-chlorinated congeners. Based on suggested dioxin toxic equivalency factors, PCN concentrations in these whole lake trout may be sufficient to trigger consumption restrictions in Ontario, Canada, and our results suggest that PCNs merit incorporation into monitoring and assessment programs.