Female reproductive impacts of dietary methylmercury in yellow perch (Perca flavescens) and zebrafish (Danio rerio).

The purpose of this study was to evaluate the effects of environmentally relevant dietary MeHg exposures on adult female yellow perch (Perca flavescens) and female zebrafish (Danio rerio) ovarian development and reproduction. Yellow perch were used in the study for their socioeconomic and ecological importance within the Great Lakes basin, and the use of zebrafish allowed for a detailed analysis of the molecular effects of MeHg following a whole life-cycle exposure. Chronic whole life dietary exposure of F1 zebrafish to MeHg mimics realistic wildlife exposure scenarios, and the twenty-week adult yellow perch exposure (where whole life-cycle exposures are difficult) captures early seasonal ovarian development. For both species, target dietary accumulation values were achieved prior to analyses. In zebrafish, several genes involved in reproductive processes were shown to be dysregulated by RNA-sequencing and quantitative real-time polymerase chain reaction (QPCR), but no significant phenotypic changes were observed regarding ovarian staging, fecundity, or embryo mortality. Yellow perch were exposed to dietary MeHg for 12, 16, or 20 weeks. In this species, a set of eight genes were assessed by QPCR in the pituitary, liver, and ovary, and no exposure-related changes were observed. The lack of genomic resources in yellow perch hinders the characterization of subtle molecular impacts. The ovarian somatic index, circulating estradiol and testosterone, and ovarian staging were not significantly altered by MeHg exposure in yellow perch. These results suggest that environmentally relevant MeHg exposures do not drastically reduce the reproductively important endpoints in these fish, but to capture realistic exposure scenarios, whole life-cycle yellow perch exposures are needed.

Reproductive effects in fathead minnows (Pimphales promelas) following a 21 d exposure to 17α-ethinylestradiol.

17α-ethinylestradiol (EE2) is a synthetic estrogen that is an active ingredient in oral contraception and hormone replacement therapy. Surveys of wastewater treatment plant effluents and surface waters throughout the world have reported EE2 concentrations in the ng/L range, and these low levels can cause significant reproductive effects in fish. This study tested the effects of three environmentally relevant EE2 concentrations: 0.47, 1.54 and 3.92 ng/L using a 21 d short-term reproductive assay to investigate the effects of EE2 on fathead minnow (Pimephales promelas) reproduction. The two highest EE2 concentrations tested in this study caused significant liver gene expression and induction of vitellogenin plasma protein in male fathead minnows. Exposure to 3.92 ng EE2/L increased the production of plasma vitellogenin in the females. Plasma estradiol concentrations were significantly reduced in females exposed to 1.54 and 3.92 ng EE2/L. All three tested concentrations significantly reduced fathead minnow egg production after a 21 d exposure to EE2. The results of this study indicate that the previously reported no observed adverse effect concentration (NOAEC) for EE2 on fathead minnow egg production (1.0 ng/L) may be too high. Because all three treatments resulted in significantly reduced egg production, the lowest observed adverse effect concentration (LOAEC) for EE2 on fathead minnow egg production is 0.47 ng EE2/L. This research estimates a NOAEC for fathead minnow reproduction at 0.24 ng EE2/L following a 21 d exposure. Additionally, induction of vitellogenin is a sensitive indicator of estrogen exposure but does not appear to be predictive of fathead minnow egg production.

Determining the effects of a mixture of an endocrine disrupting compound, 17α-ethinylestradiol, and ammonia on fathead minnow (Pimephales promelas) reproduction.

Aquatic organisms are exposed to a multitude of contaminants and to fully understand the impact of multiple stressors on fish populations, we must first understand the mechanism of action for each toxicant and how the combined effects manifest at the level of the individual. 17α-ethinylestradiol (EE2) has been known to cause adverse reproductive effects including reduced fecundity and fertility, intersex and skewed sex ratios in fish by mimicking naturally produced estrogen at low concentrations. Ammonia can cause adverse reproductive and mortality effects in individual fish through effects or damage to the central nervous system. Both EE2 and ammonia are found in most municipal effluents in various concentrations. A flow-through diluter system was used to test the individual effects of these two contaminants at their respective no observable adverse effect concentration (NOAEC) as well as their combined effects on fathead minnow, (Pimephales promelas) reproduction in a mixture exposure. While neither contaminant nor their mixture altered reproduction in terms of fecundity, their mixture resulted in significant fathead minnow mortality during a 21 d exposure. This study demonstrated the need to consider mixture effects when assessing risk for toxicity testing with multiple stressors.

Determining the effects of ammonia on fathead minnow (Pimephales promelas) reproduction.

Ammonia can cause adverse reproductive and mortality effects in individual fish by interacting with the central nervous system. The last published study that assessed the effects of ammonia on fathead minnow reproduction was a lifecycle study conducted in 1986. Our study's main goal was to re-evaluate ammonia toxicity on fathead minnow Pimephales promelas reproduction using a 20-day fecundity flow-through diluter method. Flow-through diluter systems have been used by regulatory agencies, such as the U.S. Environmental Protection Agency, in the past as an effective way to estimate acceptable levels of contaminants. There was a significant difference in cumulative egg production among treatments (ANOVA; F=10.167, p≤0.01, df=3). All three concentrations of ammonia tested in this study significantly reduced fecundity after 20days of exposure (Dunnett's, p≤0.05 for each treatment). The lowest un-ionized ammonia concentration (0.06mg/L at a pH of 7.3 and temperature of 25.1°C) tested during this study resulted in a 29% decrease in cumulative fecundity. Because all tested ammonia concentrations caused an effect on P. promelas reproduction, the no effect concentration was estimated to be 0.025mg/L un-ionized ammonia (2.19mg/L total ammonia-nitrogen). This estimate was determined using the U.S. EPA Toxicity Relationship Analysis Program to calculate the 10% effect concentration of ammonia on P. promelas reproduction. This value is much lower than the previous reported no effect concentration on P. promelas reproduction (0.37mg/L un-ionized ammonia or 6.43mg/L total ammonia-nitrogen) as determined from the 1986 study, which was used to determine the ammonia water quality criteria by the U.S. Environmental Protection Agency. Our results should be considered in the next revision of water quality criteria.