Are Atlantic cod in Store Lungegårdsvann, a seawater recipient in Bergen, affected by environmental contaminants? A qRT-PCR survey.
The aim of this study was to examine the transcriptional levels of selected genes in liver and head kidney of Atlantic cod Gadus morhua sampled in Store Lungegårdsvann, a seawater recipient situated in the middle of the city of Bergen, Norway, for effects of contaminants released from municipal sewage effluents and former dump sites. Five males and six females were caught with fish traps in Store Lungegårdsvann in 2006. Cod from a location near Jondal in the Hardanger Fjord were used as controls (five males and four females). The following 12 genes were picked as potential markers of contaminant exposure: cytochrome P-450 1A (CYP1A), cytochrome P-450 2C33-like (CYP2C33-like), cytochrome P-450 3C (CYP3C), glutathione S-transcriptase pi (GST) (detoxification and biotransformation), Mn superoxide dismutase (Mn SOD), glutathione reductase (GR), heat-shock protein 70 (HSP70) (oxidative stress), vitellogenin A (VtgA), vitellogenin B (VtgB), zona pellucida 2 (ZP2) (effects of estrogen disruptors), B-cell lymphoma 2 (Bcl-2), and cyclin-dependent kinase inhibitor 1A (CDKN1A) (radiation). The results showed that two males caught in Store Lungegårdsvann possessed high transcriptional levels of VtgA, VtgB, and ZP2 mRNA in the liver. In addition, CYP1A was 4.9-fold higher expressed in males from Store Lungegårdsvann compared to males from the reference population. CYP2C33-like mRNA expression was significantly higher (1.8-fold) in females from Store Lungegårdsvann than in females from the reference population. CYP1A was significantly lower (4.7-fold) expressed in head kidney of females from Store Lungegårdsvann than in females from Hardanger Fjord. In a follow-up examination with sexually mature cod sampled in Store Lungegårdsvann in 2007, the livers were shown to contain high levels of polychlorinated biphenyls (PCB) and dioxin-like PCB. In conclusion, fish inhabiting Store Lungegårdsvann are exposed not only to endocrine disruptors but also to other contaminants that affect the transcription of phase I biotransformation genes.
Olsvik
Pål A
PA
National Institute of Nutrition and Seafood Research, Bergen, Norway. pal.olsvik@nifes.no
Lie
Kai K
KK
Goksøyr
Anders
A
Midtun
Torbjørn
T
Frantzen
Sylvia
S
Maage
Amund
A
D000818:Animals; D003577:Cytochrome P-450 Enzyme System / Q000235:genetics / Q000378:metabolism; D004147:Dioxins / Q000032:analysis; D004784:Environmental Monitoring / Q000379:methods*; D005260:Female; D048388:Gadiformes / Q000502:physiology*; D020869:Gene Expression Profiling; D005786:Gene Expression Regulation / Q000187:drug effects*; D007668:Kidney / Q000187:drug effects / Q000378:metabolism; D008099:Liver / Q000187:drug effects / Q000378:metabolism; D008297:Male; D050216:Metabolic Detoxication, Phase I / Q000235:genetics; D010088:Oxidoreductases / Q000235:genetics / Q000378:metabolism; D011078:Polychlorinated Biphenyls / Q000032:analysis; D012333:RNA, Messenger / Q000378:metabolism; D020133:Reverse Transcriptase Polymerase Chain Reaction / Q000379:methods*; D014819:Vitellogenins / Q000235:genetics / Q000378:metabolism; D014874:Water Pollutants, Chemical / Q000737:chemistry / Q000633:toxicity*
D004147:Dioxins; D012333:RNA, Messenger; D014819:Vitellogenins; D014874:Water Pollutants, Chemical; D003577:Cytochrome P-450 Enzyme System; D011078:Polychlorinated Biphenyls; D010088:Oxidoreductases