Submitted by PPG Zoologia (zoologia-pg@pucrs.br) on 2018-06-29T17:28:48Z No. of bitstreams: 1 Dissertac?a?o_Mestrado_Raphaela_ (003).pdf: 1487803 bytes, checksum: 85e14999295df94278920f21e8362c4d (MD5) / Approved for entry into archive by Sheila Dias (sheila.dias@pucrs.br) on 2018-07-09T11:35:44Z (GMT) No. of bitstreams: 1 Dissertac?a?o_Mestrado_Raphaela_ (003).pdf: 1487803 bytes, checksum: 85e14999295df94278920f21e8362c4d (MD5) / Made available in DSpace on 2018-07-09T11:42:43Z (GMT). No. of bitstreams: 1 Dissertac?a?o_Mestrado_Raphaela_ (003).pdf: 1487803 bytes, checksum: 85e14999295df94278920f21e8362c4d (MD5) Previous issue date: 2018-02-26 / Coordena??o de Aperfei?oamento de Pessoal de N?vel Superior - CAPES / The increase of environmental pollutants sources directly affects the ecosystem and human health, mainly due to loss of soil and water quality. Among these toxic agents are included endocrine disruptors, which can cause changes in biochemical pathways and physiological changes in organisms. Studies with different forms of bisphenols, compounds present in many products of human consumption and the environment, had already demonstrated extremely adverse effects on behavior and gene expression of targets related to neural and endocrine systems during development. The zebrafish, Danio rerio, is an excellent model organism for studying neurotoxicity, due to its advantages with respect to specific aspects of their development and a low maintenance cost when compared to other vertebrate model organisms. This work proposes the investigation of the effects of bisphenol A (BPA), its chlorinated derivatives and its substitutes (BPS and BPF), toxicological and behavioral parameters combined with characterization of its potential underlying cellular and molecular mechanisms such as cell death and proteins and gene expression in the nervous and endocrine systems. After the embryo and larvae were exposed to different concentrations of BPA and its derivatives, morphological analyzes and embryo survival were carried out, as well as behavioral tests of locomotion and cognitive evaluation of the larvae. In the concentrantion curve of the different bisphenolic compounds, no significant difference was observed in the survival, teratogenesis and hatching of the animals, however, a significant increase was detected in the exploratory parameters of the BPA and BPF groups. When comparing the aversive behavior of the BPA with the DMSO, there was no statistical difference between the groups, whereas in the BPS an improvement in the escape response of the larvae occurred. Additionally, behavioral and locomotor activity analyzes will be performed in adult animals previously treated with the compounds studied during the initial development. In this way, it is expected to contribute to the current knowledge of neurotoxicity mechanisms related to endocrine disruption caused by contaminants of the bisphenol family. / O crescimento das fontes de poluentes ambientais afeta diretamente o ecossistema e a sa?de humana, principalmente devido ? perda da qualidade do solo e da ?gua. Entre estes agentes t?xicos, est?o inclu?dos os disruptores end?crinos, os quais podem acarretar diversas mudan?as em vias bioqu?micas e altera??es fisiol?gicas em organismos. Estudos com diferentes formas de bisfen?is, compostos presentes em diversos produtos de consumo humano e inclusive no ambiente devido ? contamina??o por efluentes industriais, j? apresentaram efeitos extremamente nocivos na regula??o da express?o de genes relacionados ao sistema neural e end?crino durante o desenvolvimento, al?m de altera??es comportamentais severas. O zebrafish, Danio rerio, ? um excelente organismo modelo para estudar neurotoxicidade, uma vez que possui vantagens em rela??o a aspectos espec?ficos do seu desenvolvimento e um custo reduzido de manuten??o quando comparado a outros vertebrados modelos. Este projeto prop?s o estudo dos efeitos do bisfenol A (BPA), seus derivados clorados e substitutivos (BPS e BPF), sobre par?metros de embriotoxicidade e comportamento, buscando tamb?m caracterizar os mecanismos celulares e moleculares dos potenciais efeitos observados avaliando morte celular e n?veis de prote?nas e express?o de genes alvos em embri?es e larvas de zebrafish. Para tanto, ap?s a exposi??o dos embri?es e larvas a diferentes concentra??es de BPA e seus derivados, foram realizadas an?lises morfol?gicas e sobreviv?ncia dos embri?es; ensaios comportamentais de locomo??o e avalia??o cognitiva das larvas. Ao realizar a curva de concentra??o dos diferentes compostos bisfen?licos, n?o foi observada diferen?a significativa na sobreviv?ncia, teratog?nese e eclos?o dos animais, por?m, ao analisar o comportamento explorat?rio dos animais tratados com BPA e BPF foi detectado um aumento significativo nos par?metros explorat?rios das larvas. Ao compararmos o comportamento aversivo do BPA com o controle tratado com o ve?culo DMSO, n?o existiu diferen?a estat?stica entre os grupos, enquanto no BPS ocorreu uma melhora na resposta de escape das larvas. Adicionalmente, ser?o realizadas an?lises comportamentais e de atividade locomotora em animais adultos previamente tratados com os compostos estudados durante o desenvolvimento inicial. Desta forma, espera-se contribuir para o conhecimento atual dos mecanismos de neurotoxicidade relacionados ? disrup??o end?crina causada por contaminantes da fam?lia dos bisfen?is.

O glifosato-Roundup é um herbicida amplamente utilizado em diversas culturas agrícolas. Sua toxicidade reprodutiva está relacionada com a inibição da proteína StAR e da enzima aromatase, causando in vitro redução significativa da produção de testosterona e estradiol. Este trabalho teve como objetivo verificar esse efeito in vivo, utilizando-se ratos Wistar machos pré-púberes como modelo experimental. Utilizou-se 68 machos tratados dos 23 aos 53 dias de idade com as doses de 0, 5, 50 e 250 mg/kg de peso vivo por gavagem uma vez ao dia. Foram avaliados a progressão da puberdade, o desenvolvimento corporal, a produção hormonal de testosterona, estradiol e corticosterona, morfologia testicular e da glândula adrenal, função renal e hepática e histopatologia renal e hepática. As análises estatísticas utilizadas foram a análise de variâncias de uma via ANOVA, de duas vias MANOVA ou Kruskall-Walis e pós-testes de Tukey-Kramer, Fisher ou de Dun. O herbicida glyphosate-Roundup alterou de forma significativa a progressão da puberdade de forma dose dependente, bem como se observou a redução na produção de testosterona e alterações na morfologia dos túbulos seminíferos. A morfologia da glândula adrenal e a produção de corticosterona não foram afetadas pelas doses utilizadas nesse estudo. Observou-se comprometimento da função renal e alterações patológicas nesse órgão. Não foram evidenciadas alterações hepáticas. O crescimento corporal dos animais não foi influenciado pelo tratamento. Pode-se concluir que esse herbicida é um potente disruptor endócrino in vivo, causando distúrbios no desenvolvimento reprodutivo e na produção hormonal dos animais. / The glyphosate-Roundup is a widely pesticide used in several culturas agrícolas. Its reproductive toxicity is associated to inhibition of StAR protein and aromatase enzime that cause in vitro significantly reduction in testosterone and estradiol production. The objective of this study was to evaluate the in vivo effects of inhibition of StAR protein and aromatase enzyme, using prepubertal male Wistar rats like experimental model. 68 animals were exposed once a day by gavage to glyphosate-Roundup in following doses: 0, 5, 50 or 250 mg/kg of body weight. The end points were puberty progression, body development, testosterone, estradiol and corticosterona productions and testicular and adrenal morphology, renal and liver function and histopatology. The statistical analysis used were one-way ANOVA, multi-way ANOVA or Kruskall-Walis and posthoc tests of Tukey-Kramer, Fisher or Dun. The herbicide glyphosate-Roundup changed significantly the puberty progression in dose-dependent manner, as well reduction in testosterone production and alterations in testicular morphology. There were not observed alterations in adrenal morphology or corticosterone production in the doses used in this study. The renal function and histopatology were altered in treated groups while liver function wasn\'t. The body development was not influenced by the exposure. In conclusion, glyphosate-Roundup is a potent endocrine disruptor in vivo that cause problems in reproductive development and hormonal synthesis in exposure animals.

Les perturbateurs endocriniens (PE) sont une préoccupation majeure de par leurs effets sur les grandes fonctions physiologiques des organismes etparticulièrement sur la fonction de reproduction. Chez les vertébrés, la reproduction est sous le contrôle d’un axe neuroendocrinien nommé axegonadotrope. Celui-ci comprend différents acteurs cérébraux (gonadolibérines et kisspeptines), hypophysaires (gonadotropines) et gonadiques(stéroïdes sexuels) dont la mise en place et le fonctionnement sont régulés finement. Parmi les mécanismes de régulation, les stéroïdes vont jouer unrôle important en effectuant des boucles de rétrocontrôle. Les PE mimant ces stéroïdes sont donc potentiellement capables d’impacter ces régulations.L’objectif de ce travail était d’évaluer les effets d’un xénooestrogène sur les mises en place des acteurs cérébraux impliqués dans l’axe gonadotrope chezle bar européen (Dicentrarchus labrax). Nous avons d’abord décrit l’ontogénèse des systèmes à kisspeptine, à gonadolibérine et à gonadotropine aucours du développement larvaire. Nous avons mis en évidence une régulation différentielle de ces acteurs suggérant un rôle durant ce processusdéveloppemental. De plus, nous montrons que le 17α-éthinylestradiol (EE2) est capable de perturber l'ontogenèse des systèmes à GnRH2 et à GnRH3au cours des stades précoces du développement larvaire.Ces données constituent une base permettant l’évaluation des effets des PE sur l’ontogénèse des systèmes neuroendocriniens. / Endocrine disruptors (EDs) are a major concern because of their effects on the main physiological functions, particularly on the reproductive function.In vertebrates, reproduction is under the control of a neuroendocrine axis called hypothalamic-pituitary-gonadal (HPG) axis. It includes various actors atthe brain (gonadotropin releasing hormones (GnRH) and kisspeptins), pituitary (gonadotropic hormones) and gonadal (sex steroids) levels. Theirdévelopment and functioning are finely regulated. Among the regulators, steroids play an important role by performing feedback loops. EDs mimickingsteroids are therefore potentially able to impact these regulations. The objective of this work was to evaluate the effects of xenoestrogens on theimplementation of cerebral actors involved in the HPG axis in the European sea bass (Dicentrarchus labrax). We first described the ontogeny of thekisspeptin, GnRH and gonadotropin systems during larval development. We have highlighted a differential regulation of these actors suggesting a roleduring this developmental process. In addition, we show that 17α-ethinylestradiol (EE2) is able to disrupt the ontogeny of GnRH2 and GnRH3 systemsduring the early stages of larval development.These data provide a basis for evaluation of the EDs effects on the ontogeny of neuroendocrine systems.

The first objective of this thesis was to investigate effects of endocrine disruptors on the developing brain and gonads of bird embryos. The substances studied were the insecticide methoxychlor, and nine UV-filters (3-benzylidene camphor (3BC), 4 methyl benzylidene camphor (4MBC), benzophenone (BP) 1,2 and 3, 4 hydroxy benzophenone (4 HB), 4 dihydroxy benzophenone (4DHB), benzyl salicylate (BS), and ethyl-4-aminobenzoate Et-PABA)), commonly used in cosmetic products. Some of these substances have no estrogenic effect in vitro, but have been shown to be estrogenic in vivo. The PCB-mixture Clophen A50 is a well-known inducer of biotransformation enzymes and was co-administered with methoxychlor and the UV-filters 3BC and 4MBC. Exposure to 3BC or 4MBC caused ovotestis formation and malformations of the Müllerian ducts in Japanese quail embryos. Co-exposure to one of these compounds and Clophen A50 enhanced the effects, indicating that Clophen A50 potentiates the effects of the UV-filters. Embryonic co-exposure to Clophen A50 and methoxychlor caused a disturbed male sexual behaviour. The metabolites of methoxychlor are estrogen receptor (ER)α-selective, which indicates that the effects on behaviour following embryonic treatment were mediated by ERα. Another objective in this thesis was to localize estrogen receptors (ERs) in the brain of adult and embryonic Japanese quail. The ER localization provides a basis for mechanistic studies on effects of endocrine disruptors, by the identification of estrogen-responsive areas in the brain. We found that ERβ, not previously implicated in sex-differentiation of the brain, was the only ER-subtype present in a sexually dimorphic brain area during differentiation. In conclusion, the estrogenic effects of 3BC, 4MBC and methoxychlor were increased by co-exposure to PCB. These results raise concern since many wildlife species, as well as humans, carry large body burdens of persistent organic pollutants like PCBs, which potentially can interact and enhance the effects of other endocrine disruptors.

Oestrogens are produced by aromatisation of androgens by the aromatase enzyme. In the vertebrate brain this synthesis has vital functions in nerve protection, cell proliferation and nerve development during injury respectively brain development. Brain oestrogens are also crucial in activating certain reproductive and aggressive behaviours in mammals and birds. Teleosts have remarkably high activity of brain aromatase (bAA) compared to mammals and birds; 100-1000 times higher in brain regions like the hypothalamus, pre-optic area and optic tectum. The role of brain oestrogens in teleost behaviour is, however, less clear than in e.g. songbirds and rodents. This thesis studies the potential role of brain aromatase and brain oestrogens in the reproductive behaviour of the guppy male (Poecilia reticulata), how guppy brain aromatase responds to steroids and is distributed in the adult brain. The thesis shows that male behaviour can be affected by brain aromatase. Reduction of bAA by aromatase inhibitor treatment reduced the sexual behaviours sigmoid display and gonopodium swinging (I) and oestrogen receptor blocking with an oestrogen antagonist reduced the number of successful mating attempts (II). The anatomical study (IV) showed that brain aromatase is distributed in areas of the adult guppy brain that are connected to reproductive control and behaviour in vertebrates. Guppy bAA is stimulated by both androgens and oestrogens (III) but is more sensitive to oestrogens, especially in males, and could thus be used as an indicator of endocrine disruption at low concentrations found in the environment. The thesis can also conclude that females possess more brain aromatase than males, and that although it is expressed in the same pattern throughout the brain in both genders the enzymatic activity is differently distributed between the sexes. / Aromatase and androgens in fish reproductive behaviour

Exposure to xenoestrogens during development has been shown to impair sexual differentiation in various species. The major aim of this thesis was to elucidate the respective roles of the two estrogen receptors ERα and ERβ in normal and disrupted differentiation of sex organs and copulatory behavior in the Japanese quail (Coturnix japonica). The expression of ERα mRNA was much stronger than that of ERβ mRNA in the gonads and Müllerian ducts (embryonic oviducts) in early embryos. By contrast, ERβ seemed to be predominantly expressed in regions of the embryonic brain that are associated with male sexual behavior. Embryos were exposed to the selective ERα agonists propyl-pyrazole-triol (PPT) and 16α-lactone-estradiol (16α-LE2). The estrogens 17β-estradiol (E2) and 17α-ethynylestradiol (EE2), which activate both ERα and ERβ, were used as positive controls. All substances impaired reproductive organ differentiation. The effects observed included oviductal malformations in females and partial development of oviducts in males. All substances also induced testis feminization (ovotestis) in male embryos. The male copulatory behavior was severely impaired by the positive controls but was unaffected by PPT and 16α-LE2 at doses that disrupted sex organ differentiation. A higher dose of 16α-LE2 significantly suppressed the behavior. However, it is possible that this effect was caused by cross-activation of ERβ. The substances also induced hepatic expression of mRNA encoding the egg-yolk proteins vitellogenin II and very low-density apolipoprotein II, which are commonly used as indicators of estrogen exposure. In conclusion, the results suggest that ERα is important for female reproductive organ differentiation. Excess activation of ERα by xenoestrogens impairs differentiation in both females and males and induces hepatic expression of egg-yolk proteins. The results also indicate that ERα alone cannot mediate demasculinization of male copulatory behavior in quail, although further studies are needed to test this hypothesis.

Due to a policy of no release, oil sands process-affected water (OSPW) produced by the surface-mining oil sands industry in North Eastern Alberta, Canada, is stored on-site in tailings ponds. There is concern regarding the toxic effects of OSPW on aquatic organisms. Knowledge of the chemical composition and toxicity of OSPW is limited. Research is necessary for potential remediation and release of OSPW back into the environment. Due to the large volume and persistency of OSPW, active efforts are necessary for the remediation of OSPW before release and habitat reclamation. Currently, ozonation is considered one possible method for remediation of OSPW by reducing the concentrations of dissolved organic compounds, including naphthenic acids (NAs), which are considered among the primary toxic constituents. However, further work is needed to evaluate the effectiveness of ozonation in reducing the toxicity of OSPW and to ensure that ozonation does not increase the toxicity of OSPW. The overall objective of this work was to determine the toxic effects of OSPW on endocrine disruption and embryo development, using both in vitro and in vivo models, and the effectiveness of ozone treatment for reducing the toxicity of OSPW. In the first study, untreated and ozone-treated OSPW were examined for effects on sex steroid production using the H295R cell line steroidogenesis Assay. The results indicate that exposure to untreated OSPW can significantly decrease synthesis of testosterone (T) and increase synthesis of 17β-estradiol (E2) by 0.55±0.06 and 2.0±0.13-fold, respectively, compared to that of control groups (ρ < 0.05). These effects were due to increased aromatase enzyme activity and decreased E2 metabolism. The results also suggest that ozonation is an effective treatment to reduce concentrations of NAs in OSPW without altering steroidogenesis. In the second study, the T47D-kbluc (estrogen responsive) and MDA-kb2 (androgen responsive) cell assays were used to determine whether OSPW might act as either agonists or antagonists of the estrogen receptor (ER) or androgen receptor (AR), respectively. The estrogenic responses to untreated OSPW were significantly greater by 2.6±0.22-fold compared to control group (ρ < 0.05). Exposure to untreated OSPW produced significant antiandrogenic response in the presence of 0.01, 0.05 and 0.1 nM T by 16±6.5%, 47±7.6% and 75±9.7%, respectively, of that of the corresponding concentrations of T alone (ρ < 0.05). The results suggest that compounds in the dissolved organic fraction of OSPW have estrogenic and anti-androgenic properties, acting as ER agonists and/or AR antagonists. Ozonation of the OSPW partially mitigated the antiandrogenicity but had no effect on the estrogenicity of OSPW. In the third study, the endocrine-disrupting effects of OSPW and ozone-treated OSPW were determined by quantifying relative changes in the abundances of transcripts of genes along the brain-gonad-liver (BGL) axis in male and female fathead minnows (Pimephales promelas). The results indicate that OSPW has endocrine-disrupting effects at all levels of BGL axis and these effects of impaired expression of genes along the BGL axis are sex specific. For example, exposure to OSPW resulted in significantly greater abundances of transcripts of vtg (Vitellogenin), chg-l (Choriogenin L) and chg-h (Choriogenin H minor) by 4.9±1.2, 5.4±1.5 and 3.4±0.78-fold, respectively, compared to those of control groups (ρ < 0.05) in livers from male fathead minnow. However, in livers from female fathead minnows, exposure to OSPW resulted in significantly lesser abundances of transcripts of vtg, chg-l and chg-h by 0.002±0.0011, 0.022±0.007 and 0.036±0.024-fold, respectively, compared to those of control fish (ρ < 0.05). Ozonation of OSPW attenuated the effects on abundances of transcripts of some genes, and the attenuation was more prominent in males than in females. However, impact of ozonation on endocrine-disrupting effects of OSPW was less evident than in the in vitro studies described in Chapter 2 and 3. The results also provide a mechanistic basis for the endocrine-disrupting effects of OSPW from other studies, including impaired reproduction of fathead minnows exposed to OSPW. In the final study the effects of untreated, ozone-treated, and activated charcoal-treated OSPW (OSPW, O3-OSPW, and AC-OSPW) on the survival, growth, and development of embryos of fathead minnows were determined. Compared to the control group, which had an embryo survival rate of 98±2.1%, survival was significantly less when exposed to OSPW (44±7.1%; ρ < 0.05). Eggs exposed to untreated OSPW exhibited a significantly greater rate of premature hatching, and embryos exhibited more frequent spontaneous movements. Incidences of hemorrhage (50±3.4%), pericardial edema (56±7.1%), and malformation of the spine (38±5.4%) were significantly greater in embryos exposed to OSPW compared to control group (ρ < 0.05). Significantly greater concentrations of ROS (1.7±0.11-fold), and greater abundances of transcripts cyp3a, gst, sod, casp9, and apopen (2.4±0.34, 2.2±0.26, 3.1±0.74, 3.3±0.57 and 2.4±0.25-fold, respectively) compared to control groups (ρ < 0.05), indicated that exposure to OSPW caused oxidative stress, which can result in damage to mitochondria and promote activation of caspase enzymes and apoptotic cell death. Removal of dissolved organic constituents in OSPW by ozone treatment, or by activated charcoal, significantly attenuated all of the adverse effects associated with untreated OSPW. The results suggest that the organic fraction of OSPW can negatively impact the development of fathead minnow embryos through oxidative stress and apoptosis, and that ozonation attenuates this developmental toxicity. Overall, the findings from the research described in this thesis provide novel and important insights into the toxicity and mechanisms of the toxicity of OSPW with respect to endocrine disruption and development of embryos of fish. In addition, the research provides compelling evidence that ozonation might be an effective method for accelerating the remediation of OSPW. The results of the research might help regulators develop effective strategies for reclamation, remediation and potential release of OSPW back to the environment.

Fluoxetine (FLX), the active ingredient of Prozac™, is a member of the selective serotonin reuptake inhibitor (SSRI) class of anti-depressant drugs and is present in aquatic environments worldwide. Previous studies reported that FLX is an endocrine disruptor in fish, bioconcentrating in tissues including the brain. Evidence implicates that serotonin influences the activity of the hypothalamo-pituitary-interrenal (HPI) stress axis, thus exposure to FLX may disrupt the teleost stress response. This study examined in vitro cortisol production in rainbow trout (Oncorhynchus mykiss) head kidney/interrenal cells exposed to FLX and 14C-pregnenolone metabolism in head kidney microsome preparations of FLX-exposed trout. Results indicated that cells exposed in vitro to increasing concentrations of FLX had lower cortisol production and cell viability (versus control) and microsomes isolated from trout exposed to 54 μg/L FLX had higher pregnenolone metabolism versus those of control and low FLX-exposed (0.54 μg/L) trout.

The overall objective of the research conducted and described in this thesis was to develop an environmentally relevant bioassay to assess the effects of complex effluents on a sentinel fish species. A short-term fathead minnow (FHM) reproductive bioassay was utilized to assess the effects of industrial effluents on multiple levels of biological organization (sub-organismal to population endpoints). The FHM bioassay was tested in both lab and on-site investigations using an artificial stream system. The incorporation of trophic-transfer into the bioassay was also developed to quantify the importance of contaminated food as a source of exposure. This work was conducted in two key phases. Phase I focused on testing and developing the FHM bioassay, in the lab and on-site with pulp mill effluent (PME), to firstly document response patterns and, secondly, to conduct an investigation of cause study. Phase II focused on developing the trophic-transfer system to document responses to metal mine effluent (MME) in the lab and on-site in an artificial stream system. Development of the trophic-transfer system was also conducted during this phase to compare responses to standard water-only exposures. <p>In Phase I, exposure to PME in both the lab and field studies resulted in disruptions in egg production and spawning events. By focusing on identifying response patterns I was able to determine that the effects observed were indicative of an estrogenic response. I was also able to identify a process stream that was the potential cause of responses observed after exposure to final effluent. Isolation of this process stream will assist the mill in developing approaches for future mitigation. The results from this research will also provide additional data for the environmental effects monitoring (EEM) program for pulp and paper and investigation of cause studies on a national basis. <p> In Phase II, in both the field and laboratory investigations, significant decreases in reproductive output (egg production and spawning events) were observed in the water-only system exposures. Significant decreases in hatching success and increases in deformities were observed in the trophic-transfer system only, suggesting that the combination of both food and water was important in assessing the effects on the F1 generation. Overall, the responses in the trophic-transfer system were not comparable between the lab and field studies. In the lab study, significant decreases in reproductive output occurred, compared to the field study where significant increases in egg production and spawning events occurred. In addition, the effects on the F1 generation in the field study were not as severe as those observed in the lab investigation. It was concluded that the presence of reference water and the environment within the trophic-transfer system were responsible for this reduction in toxicity. <p> Phases I and II of this research have made significant contributions to artificial stream development within Canada for the assessment of industrial effluents and their effects on aquatic biota. The results from these studies have also demonstrated that environmentally relevant testing is essential if we are to accurately assess effects on aquatic biota. Future development and application of this bioassay should be towards developing a standardized approach for not only assessing the effects of industrial effluents in a comparative manner, but also in investigation of cause studies.

Fluoxetine (FLX), the active ingredient of Prozac™, is a member of the selective serotonin reuptake inhibitor (SSRI) class of anti-depressant drugs and is present in aquatic environments worldwide. Previous studies reported that FLX is an endocrine disruptor in fish, bioconcentrating in tissues including the brain. Evidence implicates that serotonin influences the activity of the hypothalamo-pituitary-interrenal (HPI) stress axis, thus exposure to FLX may disrupt the teleost stress response. This study examined in vitro cortisol production in rainbow trout (Oncorhynchus mykiss) head kidney/interrenal cells exposed to FLX and 14C-pregnenolone metabolism in head kidney microsome preparations of FLX-exposed trout. Results indicated that cells exposed in vitro to increasing concentrations of FLX had lower cortisol production and cell viability (versus control) and microsomes isolated from trout exposed to 54 μg/L FLX had higher pregnenolone metabolism versus those of control and low FLX-exposed (0.54 μg/L) trout.