Butt Craig M, Mabury Scott A, Muir Derek C G, Braune Birgit M
Department of Chemistry, University of Toronto, 80 St. George Street, Toronto, Ontario M5S 3H6, Canada.
Environ Sci Technol. 2007 May 15;41(10):3521-8. doi: 10.1021/es062710w.
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.
在加拿大北极地区的利奥波德王子岛,对厚嘴海鸦(厚嘴海鸦属)和北极海鸥(暴雪鹱属)这两种海鸟肝脏样本中的全氟烷基化合物(PFCs)的时间趋势进行了研究。厚嘴海鸦样本采集于1975年、1993年和2004年,而北极海鸥样本采集于1975年、1987年、1993年和2003年。每年分析8至10只个体。分析物包括C7 - C15全氟羧酸盐(PFCAs)及其疑似前体、8:2和10:2氟调聚物饱和与不饱和羧酸盐(FTCAs、FTUCAs)、C6、C8(全氟辛烷磺酸,PFOS)、C10磺酸盐和全氟辛烷磺酰胺(PFOSA)。肝脏样本进行匀浆处理,用甲基叔丁基醚进行液 - 液萃取,用六氟异丙醇进行净化,然后通过液相色谱 - 串联质谱进行分析。总体而言,海鸟体内的浓度低于占据相似或更高营养级的其他海洋动物。与大多数其他野生动物样本不同,PFC谱以PFCAs为主,在2004年厚嘴海鸦样本和2003年北极海鸥样本中,PFCAs分别占总PFC谱的81%和93%。此外,PFCA谱主要由C11 - C15 PFCAs组成,这在其他野生动物物种中似乎是独特的。发现PFC浓度从1975年到2003/2004年显著增加。厚嘴海鸦中全氟十五烷酸(PFPA)的倍增时间为2.3年,全氟十二烷酸(PFDoA)为9.9年;北极海鸥中PFPA的倍增时间为2.5年,全氟癸酸(PFDA)为11.7年。厚嘴海鸦中PFCA浓度在两个时间段(1975 - 1993年,1993 - 2004年)均显著增加,但北极海鸥中PFCA浓度在1993年后似乎保持稳定。观察到的时间趋势差异可能是由于海鸟不同的迁徙模式导致的。最后,在海鸟中检测到8:2和10:2 FTUCAs表明氟调聚物醇是一些PFCAs的来源。