Mémoire numérisé par la Division de la gestion de documents et des archives de l'Université de Montréal.

Mémoire numérisé par la Division de la gestion de documents et des archives de l'Université de Montréal

Glyphosate-based herbicides are the dominant pesticide on the market and are utilized worldwide in both the agricultural and forestry industries. Their prevalence comes at a time when concern over the potential effects of pesticide application in amphibian spawning grounds is growing. The primary goal of this thesis was to determine if the glyphosate-based herbicide WeatherMax® has the potential to disrupt sexual differentiation and growth in the wood frog (Lithobates sylvaticus) in a pulse exposure at the predicted maximal environmental concentration (PMEC) of 2.88 mg acid equivalent per liter. This was carried out in laboratory, mesocosm and in-situ field exposures, in an attempt to determine how a potential disruption might vary between experimental environments. In this study, tadpoles from three split-wetlands targeted at the PMEC for WeatherMax were found to display no significant change in survival or growth, however gene expression of several genes involved in steroidogenesis during sexual differentiation (cyp19, cyp17, star, foxl2) were found to be affected. The effects on these genes appeared to be dependant on the exposure concentration of WeatherMax in each wetland, which varied even though all three wetlands were meant to target the PMEC. The wetland that was measured as having the highest herbicide concentration (PMEC 13) was found to have a female biased sex ratio. The results found in the field varied from those found in the more artificial exposures. In the laboratory the PMEC of WeatherMax experienced complete mortality, whereas in the mesocosms survival was not significantly affected. Sex ratios were unaffected in the laboratory, however at the PMEC there was a significant male bias in the mesocosms. The discrepancies in the results obtained from the different exposure types highlights the importance of real world exposures. That the same concentration that caused complete mortality in the laboratory caused sublethal effects in the field is of importance as it denotes that these endpoints may not be easily investigated in these synthetic exposures. This project is a part of the Long Term Experimental Wetlands Area (LEWA) and contributes to the body of information amassed therein on the impact of a glyphosate-based herbicide on amphibians in a wetland ecosystem.

Social interactions can have profound effects on the behavior, physiology, and overall fitness of an individual. An example of this in Lythrypnus dalli is the removal of a male from a social group resulting in a dominant female fish changing sex. The dominant female's transformation involves a suite of changes including brain, behavior, morphology, and physiology. Following the social trigger (male removal), sex-changing individuals' morphology, steroid levels, and changes in the behavior were quantified in the field and compared to results found previously in the laboratory. There were lower rates of aggressive and courtship behavior in the field, but the change in behavior over time had a similar pattern and there were parallels in morphology and steroid levels between lab and field sex changers. The brains of dominant females also responded to social change. Aromatase, an enzyme that converts testosterone into estrogen, and oxytocin, a neuropeptide found in mammals, have been associated with vertebrate social and reproductive behavior. The fish homologue of oxytocin, isotocin, and aromatase are both found in L. dalli. Upon removal of a male from the social group, L. dalli dominant females experienced a decrease in the number of preoptic area isotocin-immunoreactive cells over the course of sex change (7-10 days) and a decrease in brain aromatase activity (bAA) levels within hours, but not minutes, of male removal, while gonadal aromatase activity (gAA) decreased at a much slower time scale (beyond a week). Hours, but not minutes, after male removal, the sex-changing individual's bAA correlated with aggressive behavior increases and not the amount of time following male removal. Males that had just changed from female had different gonadal allocation and higher bAA levels than established males. Subordinate females had high gAA, but their bAA was between that of males and sex changers. In conclusion, dramatic changes in anatomy and neuroendocrine function can occur in response to social cues, individuals with similar reproductive behavior and external morphology can have large neuroendocrine and internal morphologic variation, and social interactions can affect steroid metabolism locally on a short time scale independent of gonadal modulation of steroids.

Numerous contaminants are present in mixtures in the aquatic environment. Among these are the azoles, a group of chemicals that includes both pharmaceuticals and pesticides. Azole fungicides are designed to inhibit lanosterol 14-demethylase (cytochrome P450 (CYP) 51), while other azoles are intended to inhibit aromatase (CYP19), i.e. the enzyme catalyzing biosynthesis of estrogens. In fish, a variety of CYP enzymes are involved in biotransformation of waterborne contaminants, and in metabolism of endogenous compounds including steroidal hormones. The induction of CYP1A protein and 7-ethoxyresorufin O-deethylase (EROD) activity are common biomarkers for exposure to aryl hydrocarbon receptor (AhR) agonists in fish. We developed an assay to measure inhibition of CYP1A activity (EROD) in three-spined stickleback and rainbow trout gill tissue ex vivo. Several azole fungicides were found to be potent inhibitors of CYP1A activity. A wastewater effluent containing high concentrations of pharmaceuticals was also shown to inhibit CYP1A activity. Further, several azoles inhibited CYP19 activity in rainbow trout brain microsomes in vitro. Azole mixtures reduced both CYP1A and CYP19 activity monotonically and in an additive way. Given the additive action of the azoles, studies to determine adverse effects of azole mixtures on CYP-regulated physiological functions in fish are needed. Induction of EROD and of gene expression of CYP1 in several organs was observed in an in vivo exposure with the same effluent shown to inhibit EROD. This finding could imply that there was a mixture of AhR agonists and CYP1A inhibitors in the effluent. Finally, wastewater treatment technologies were evaluated using biomarker responses in rainbow trout exposed to effluents of different treatments. The results from chemical analysis together with the biomarker results show that ozone and granulated active carbon treatment removed most pharmaceuticals, as well as AhR agonists and other chemicals present in the regular effluent. This part of the thesis demonstrates that biomarkers in fish such as induction of CYP1 gene expression are applicable to evaluate the efficiency of different treatment technologies for wastewater.

Glyphosate-based herbicides are the dominant pesticide on the market and are utilized worldwide in both the agricultural and forestry industries. Their prevalence comes at a time when concern over the potential effects of pesticide application in amphibian spawning grounds is growing. The primary goal of this thesis was to determine if the glyphosate-based herbicide WeatherMax® has the potential to disrupt sexual differentiation and growth in the wood frog (Lithobates sylvaticus) in a pulse exposure at the predicted maximal environmental concentration (PMEC) of 2.88 mg acid equivalent per liter. This was carried out in laboratory, mesocosm and in-situ field exposures, in an attempt to determine how a potential disruption might vary between experimental environments. In this study, tadpoles from three split-wetlands targeted at the PMEC for WeatherMax were found to display no significant change in survival or growth, however gene expression of several genes involved in steroidogenesis during sexual differentiation (cyp19, cyp17, star, foxl2) were found to be affected. The effects on these genes appeared to be dependant on the exposure concentration of WeatherMax in each wetland, which varied even though all three wetlands were meant to target the PMEC. The wetland that was measured as having the highest herbicide concentration (PMEC 13) was found to have a female biased sex ratio. The results found in the field varied from those found in the more artificial exposures. In the laboratory the PMEC of WeatherMax experienced complete mortality, whereas in the mesocosms survival was not significantly affected. Sex ratios were unaffected in the laboratory, however at the PMEC there was a significant male bias in the mesocosms. The discrepancies in the results obtained from the different exposure types highlights the importance of real world exposures. That the same concentration that caused complete mortality in the laboratory caused sublethal effects in the field is of importance as it denotes that these endpoints may not be easily investigated in these synthetic exposures. This project is a part of the Long Term Experimental Wetlands Area (LEWA) and contributes to the body of information amassed therein on the impact of a glyphosate-based herbicide on amphibians in a wetland ecosystem.

Glyphosate-based herbicides are the dominant pesticide on the market and are utilized worldwide in both the agricultural and forestry industries. Their prevalence comes at a time when concern over the potential effects of pesticide application in amphibian spawning grounds is growing. The primary goal of this thesis was to determine if the glyphosate-based herbicide WeatherMax® has the potential to disrupt sexual differentiation and growth in the wood frog (Lithobates sylvaticus) in a pulse exposure at the predicted maximal environmental concentration (PMEC) of 2.88 mg acid equivalent per liter. This was carried out in laboratory, mesocosm and in-situ field exposures, in an attempt to determine how a potential disruption might vary between experimental environments. In this study, tadpoles from three split-wetlands targeted at the PMEC for WeatherMax were found to display no significant change in survival or growth, however gene expression of several genes involved in steroidogenesis during sexual differentiation (cyp19, cyp17, star, foxl2) were found to be affected. The effects on these genes appeared to be dependant on the exposure concentration of WeatherMax in each wetland, which varied even though all three wetlands were meant to target the PMEC. The wetland that was measured as having the highest herbicide concentration (PMEC 13) was found to have a female biased sex ratio. The results found in the field varied from those found in the more artificial exposures. In the laboratory the PMEC of WeatherMax experienced complete mortality, whereas in the mesocosms survival was not significantly affected. Sex ratios were unaffected in the laboratory, however at the PMEC there was a significant male bias in the mesocosms. The discrepancies in the results obtained from the different exposure types highlights the importance of real world exposures. That the same concentration that caused complete mortality in the laboratory caused sublethal effects in the field is of importance as it denotes that these endpoints may not be easily investigated in these synthetic exposures. This project is a part of the Long Term Experimental Wetlands Area (LEWA) and contributes to the body of information amassed therein on the impact of a glyphosate-based herbicide on amphibians in a wetland ecosystem.