Bohne-Kjersem et al., 2009 and Bohne-Kjersem et al., 2010 studied protein changes in plasma of juvenile Atlantic cod and in fertilized Atlantic cod eggs and fry. The juveniles were exposed to dispersed NS crude oil (0.06–1.0 mg oil L−1) and check details a surrogate PW (the 1.0 mg L−1 crude oil spiked with APs and PAH). Similarly, eggs and subsequent fry were exposed to 0.01, 0.1, and 1% NS PW for about 90 days. In juvenile cod 137 proteins were differentially expressed
due to exposure, and 40 of these at the lowest exposure (Bohne-Kjersem et al., 2009). Twenty-nine proteins were identified, and a total of 14 proteins were considered potential biomarker candidates. These proteins are linked to a wide range of biological systems and processes including fibrinolysis and the complement cascade, the immune system, fertility, bone resorption, fatty acid metabolism, oxidative stress, impaired cell mobility, and apoptosis. Several responses were interlinked, suggesting that an array of biomarkers may give a better indication of the adverse effects in fish than single biomarkers. Also, in exposed cod eggs many of the protein changes occurred at the lowest exposure, including structural, cytoskeletal, and signaling proteins regulating selleck chemical muscle development, rod/retina function, cellular signaling, and tissue integrity of the fry. These are important for swimming and predator escape. The changes indicate that PW
can affect liver functions such as cellular integrity, signal transduction and metabolism. This supports earlier indications (e.g. Meier et al., 2010) that effects of PW at low doses on cod fry are mainly non-estrogenic. Karlsen et al. (2011) compared the proteome changes in cod fry
and juveniles based on studies on protein changes in brain, liver, and plasma of juvenile Atlantic cod following exposure to PW and surrogate PW. Proteome changes in fry seemed more linked to morphological changes and disturbances of cod development, whereas the changes in the proteome of juvenile cod seemed to reflect functions important for vitality. This might reflect difference in responses between different 17-DMAG (Alvespimycin) HCl developmental stages, but it could also be explained by difference in function between tissues. In another study with juvenile Atlantic cod exposed to crude oil, 17β-estradiol (E2) and 4-nonylphenol Nilsen et al. (2011) investigated the suitability of the SELDI-TOF MS (Surface-Enhanced Laser Desorption/Ionization Time-Of-Flight Mass Spectrometry) technique for screening of protein biomarkers in plasma indicating exposure to estrogenic compounds. Protein expression analysis revealed that 13 plasma peaks were significantly altered in response to the E2 treatment, and found reproducible when re-analyzed six months later. Antibody-assisted SELDI-TOF MS identified two possibly E2-responsive peaks. These were identified as fragments of the well-known biomarkers Vtg and/or Zrp.