Abrahamson et al. (2008) used an ex vivo gill EROD assay in Atlantic cod as a biomarker for CYP1A-inducing compounds in NS crude oil and PW. Exposure of cod to fairly high nominal concentrations of dispersed crude oil (1 and 10 mg L−1 THC) for 24 h induced a concentration-dependent EROD activity. The same was found following 14 days of exposure to typical near-zone concentrations of PW (0.5% and 0.1% PW) and dispersed crude oil (0.2 mg L−1).

On the other hand, EROD activity was not induced selleck in cod caged for 6 weeks between 500–10 000 m from two NCS platforms ( Abrahamson et al., 2008). Jonsson and Björkblom (2011) compared hepatic CYP1A enzyme activity in Atlantic halibut (Hippoglossus hippoglossus), turbot (Psetta maxima), long rough dab (Hippoglossoides platessoides), Atlantic salmon (Salmo salar), and Atlantic cod exposed to dispersed crude oil (0.3–9.1 μg L−1 PAHs) for 4 weeks. CYP1A activity was induced in all species except sprat. The activity level varied with species

and concentration level. Changes in the hepatic lipid composition following exposure to crude oil have been reported for Atlantic cod and winter flounder (Pseudopleuronectes americanus) ( Dey et al., 1983). Meier et al. (2007a) studied changes in the fatty acid profile and cholesterol content in membrane lipids from liver and brain tissues in Atlantic cod after 5 weeks of force feeding with AP containing paste. APs altered the fatty acid profile of polar also lipids in the liver towards more saturated fatty acids (SFA) and less n-3 polyunsaturated fatty acids (n-3 PUFA). A similar effect was found in the brain, although Erismodegib datasheet with elevated SFA content in the neutral lipids (mainly cholesterol ester), but not in the polar lipids. The AP exposure also caused a decline in the cholesterol levels in the brain. Changes in hepatic lipid composition were also reported by Grøsvik et al. (2010) in free-living Atlantic cod and haddock caught in the vicinity of the Tampen area, a northern NS region with very high petroleum activity. Haddock from Tampen

had lower hepatic lipid content than haddock from other NCS regions. Also, the fatty acid profiles had relatively high levels of arachidonic acid (20:4; n-6), and the ratio between omega-3 and omega-6 polyunsaturated fatty acids was significantly lower in neutral lipids, free fatty acids, phosphotidylcholine and phosphotidylethanolamine compared with haddock from other regions. The lipid alterations may have been caused by exposure to PW, oil, or contaminated drill cuttings. The biological implication, significance and reversibility of these fatty acid alterations are not yet understood. Widdows et al. (1987) found complete recovery within 55 days in blue mussel that had digestive gland lipid changes and heavy digestive disorder ( Lowe and Pipe, 1987) after 8 months of exposure to 28 and 125 μg l−1 dispersed diesel oil.