Perfluoroalkyl contaminants in an Arctic marine food web: trophic magnification and wildlife exposure.
To better understand the bioaccumulation behavior of perfluoroalkyl contaminants (PFCs), we conducted a comparative analysis of PFCs and lipophilic organohalogens in a Canadian Arctic marine food web. Concentrations of perfluorooctane sulfonic acid (PFOS), perfluorooctansulfoamide (PFOSA), and C7-C14 perfluorocarboxylic acids (PFCAs) ranged between 0.01 and 0.1 ng x g(-1) dry wt in sediments and 0.1 and 40 ng x g(-1) wet wt in biota, which was equivalent to or higher than levels of PCBs, PBDEs, and organochlorine pesticides. In beluga whales, PFOS and PFCA concentrations were higher (P < 0.05) in protein-rich compartments (liver and blood), compared to other tissues/fluids (milk, blubber, muscle, and fetus). In the marine mammalian food web, concentrations of PFOSA and lipophilic organochlorines (ng x g(-1) lipid equivalent) and proteinophilic substances (i.e., PFOS and C8-C14 PFCAs, ng x g(-1) protein) increased significantly (P < 0.05) with trophic level. Trophic magnification factors (TMFs) of organochlorines ranged between 5 and 14 and exhibited significant curvilinear relationships (P < 0.05) with octanol-water and octanol-air partition coefficients (KOW, KOA). TMFs of perfluorinated acids (PFAs) ranged between 2 and 11 and exhibited similar correlation (P < 0.05) with protein-water and protein-air partition coefficients (KPW, KPA). PFAs did not biomagnify in the aquatic piscivorous food web (TMF range: 0.3-2). This food web specific biomagnification behavior was attributed to the high aqueous solubility and low volatility of PFAs. Specifically, the anticipated phase-partitioning of these proteinophilic substances, represented by their protein-water (KPW) and protein-air (KPA) partition coefficients, likely results in efficient respiratory elimination in water-respiring organisms but very slow elimination and biomagnification in air-breathing animals. Lastly, the results indicate that PFOS exposure in nursing Hudson Bay beluga whale calves (CI95 range = 2.7 x 10(-5) to 1.8 x 10(-4) mg x kg bw(-1) x d(-1)), exceedsthe oral reference dose for PFOS (7.5 x 10(-5) mg x kg bw(-1) x d(-1)), which raises concern for potential biological effects in these and other sensitive Arctic marine wildlife species.
Kelly
Barry C
BC
School of Resource and Environmental Management, Simon Fraser University, Burnaby, British Columbia, Canada.
Ikonomou
Michael G
MG
Blair
Joel D
JD
Surridge
Blair
B
Hoover
Dale
D
Grace
Richard
R
Gobas
Frank A P C
FA
D000818:Animals; D000835:Animals, Wild; D001110:Arctic Regions; D050643:Beluga Whale / Q000378:metabolism; D004784:Environmental Monitoring; D004785:Environmental Pollutants / Q000737:chemistry* / Q000378:metabolism*; D005260:Female; D005399:Fishes / Q000378:metabolism; D020387:Food Chain; D019015:Geologic Sediments; D006845:Hydrocarbons, Fluorinated / Q000737:chemistry* / Q000378:metabolism*; D008099:Liver / Q000737:chemistry / Q000378:metabolism; D008297:Male; D009792:Oceans and Seas
D004785:Environmental Pollutants; D006845:Hydrocarbons, Fluorinated