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Environmental oestrogens are widespread in the aquatic environment and cause alterations in sexual development and function in vertebrates. The molecular pathways underpinning these effects, however, remain poorly understood. In this study, we aimed at generating a mechanistic understanding of the disruptive effects of exposure to environmentally relevant concentrations of 17 alpha-ethinyloestradiol (EE(2)) on reproduction in zebrafish, by anchoring the transcriptomic alterations induced with the physiological consequences of exposure. Breeding colonies of zebrafish were exposed for a 21-day period to three concentrations of EE(2) (0.05, 0.5 and 5 ng/L) and the gonadal transcriptomic alterations induced (determined using a 17,000 oligonucleotide microarray) were analysed together with physiological effects seen on reproductive output of both males and females. Exposure to 5 ng EE(2)/L resulted in reproductive impairment characterised by a decrease in egg production, alterations in sperm quality and reduced fertilisation success. The effects seen were associated with altered expression of 114 and 131 genes in the gonads of males and females, respectively. The biological processes most affected by the exposure were protein metabolism in males and mitochondria organisation and biogenesis in females. Genes involved in the regulation of cell cycle progression, the ubiquitin system and glutathione peroxidase were affected by the EE(2) exposure and associated with the changes observed in gamete quality in both genders. In summary, we demonstrated that EE(2) exposure compromised the reproductive health of breeding zebrafish at environmentally relevant concentrations. The molecular mechanisms mediating some of these effects were identified and included those impacting processes central to gametogenesis in both males and females.

Sexually mature goldfish (Carassius auratus) of both sexes were exposed to two doses (100 and 1000 microg/l) of the widely used herbicide atrazine (2-chloro-4-ethylamino-6-isopropylamino-s-triazine) for a period of 21 days and effects on the concentrations of gonad and plasma sex steroids (testosterone (T), 17beta-estradiol (E2) and 11-ketotestosterone (11-KT)), plasma vitellogenin (VTG) and gonad histo-morphology assessed. Atrazine did not show any obvious estrogenic effect in males, as determined by a lack of vitellogenin induction. There were, however, effects of atrazine on plasma androgen concentrations (androgen dynamics) and tissue (plasma and gonad) estrogen concentrations in male goldfish; exposure to 1000 microg/l atrazine induced suppression in both testosterone and 11-ketotestosterone, and resulted in elevated 17beta-estradiol, after 21 day of exposure. Further, these suppressive effects on plasma androgens and the induction in estrogen were dose- and time-related. The highest atrazine exposure dose induced structural disruption in the testis and both 100 and 1000 microg/l induced elevated levels of atresia in ovaries.