Prevalence of Long-Chained Perfluorinated Carboxylates in Seabirds from the Canadian Arctic between 1975 and 2004

Craig M. Butt, Scott A. Mabury, Derek C.G. Muir, and Birgit M. Braune*§
Department of Chemistry, University of Toronto, 80 St. George Street, Toronto, Ontario M5S 3H6, Canada, Water Science and Technology Branch, Environment Canada, 867 Lakeshore Road, Burlington, Ontario L7R 4A6, Canada, and National Wildlife Research Centre, Environment Canada, Carleton University, Raven Road, Ottawa, Ontario K1A 0H3, Canada
Environ. Sci. Technol., 2007, 41 (10), pp 3521–3528
DOI: 10.1021/es062710w
Publication Date (Web): April 18, 2007
Copyright © 2007 American Chemical Society

 University of Toronto.

 Environment Canada.

*

 Corresponding author phone:  (613) 998-6694, fax:  (613) 998-0458; e-mail:  birgit.braune@ec.gc.ca.

§

 National Wildlife Research Centre, Environment Canada.

Abstract

Temporal trends in perfluoroalkyl compounds (PFCs) were investigated in liver samples from two seabird species, thick-billed murres (Uria lomvia) and northern fulmars (Fulmaris glacialis), from Prince Leopold Island in the Canadian Arctic. Thick-billed murre samples were from 1975, 1993, and 2004, whereas northern fulmars were from 1975, 1987, 1993, and 2003. Between 8 and 10 individuals were analyzed per year. Analytes included C7−C15 perfluorinated carboxylates (PFCAs) and their suspected precursors, the 8:2 & 10:2 fluorotelomer saturated and unsaturated carboxylates (FTCAs, FTUCAs), C6, C8 (perfluorooctane sulfonate, PFOS), C10 sulfonates, and perfluorooctane sulfonamide (PFOSA). Liver samples were homogenized, liquid−liquid extracted with methyl tert-butyl ether, cleaned-up using hexafluoropropanol, and analyzed by LC−MS/MS. Overall, concentrations in seabirds were lower than those in other marine animals that occupy similar or higher trophic positions. In contrast to most other wildlife samples, PFC profiles were dominated by the PFCAs which comprised 81% and 93% of total PFC profiles in the 2004 thick-billed murre and 2003 northern fulmar samples, respectively. As well, the PFCA profiles were mainly comprised of the C11−C15 PFCAs, which appears to be unique among other wildlife species. PFC concentrations were found to increase significantly from 1975 to 2003/2004. Doubling times in thick-billed murres ranged from 2.3 yrs for perfluoropentadecanoate (PFPA) to 9.9 yrs for perfluorododecanoate (PFDoA), and from 2.5 yrs for PFPA to 11.7 yrs for perfluorodecanoate (PFDA) in northern fulmars. PFCA concentration increases in thick-billed murres were significant for both time periods (1975→1993, 1993→2004), but in northern fulmars appeared to remain steady after 1993. Differences in the temporal trends observed may be the result of differing migratory patterns of the seabirds. Finally, the detection of the 8:2 and 10:2 FTUCAs in seabirds is suggestive of fluorotelomer alcohols as a source of some PFCAs.

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History

  • Published In Issue May 15, 2007
  • Received for review November 13, 2006
    Revised manuscript received February 26, 2007
    Accepted March 4, 2007

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