Environmental pollution affects molecular and biochemical responses during gonadal maturation of Astyanax fasciatus (Teleostei: Characiformes: Characidae)

Endocrine disrupting compounds (EDCs) have the potential to alter fish reproduction at various levels of organization. The aim of this study was to assess the impact of a natural environment with heavily anthropogenic influence on the physiological processes involved in reproduction in the freshwate...

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Autor principal: Tolussi, C.E
Otros Autores: Gomes, A.D.O, Kumar, A., Ribeiro, C.S, Nostro, F.L.L, Bain, P.A, de Souza, G.B, Cuña, R.D, Honji, R.M, Moreira, R.G
Formato: Capítulo de libro
Lenguaje:Inglés
Publicado: Academic Press 2018
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024 7 |2 scopus  |a 2-s2.0-85030309074 
024 7 |2 cas  |a estradiol, 50-28-2; Biomarkers; Endocrine Disruptors; Estradiol; Vitellogenins; Water Pollutants, Chemical 
040 |a Scopus  |b spa  |c AR-BaUEN  |d AR-BaUEN 
030 |a EESAD 
100 1 |a Tolussi, C.E. 
245 1 0 |a Environmental pollution affects molecular and biochemical responses during gonadal maturation of Astyanax fasciatus (Teleostei: Characiformes: Characidae) 
260 |b Academic Press  |c 2018 
270 1 0 |m Tolussi, C.E.; Laboratório de Metabolismo e Reprodução de Organismos Aquáticos, Departamento de Fisiologia, Instituto de Biociências, Universidade de São Paulo. Rua do Matão, Trav.14, n° 321, Brazil; email: ctolussi@usp.br 
506 |2 openaire  |e Política editorial 
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504 |a Gomes, A.D., Tolussi, C.E., Ribeiro, C.S., Honji, R.M., Moreira, R.G., The role of ovarian steroids in reproductive plasticity in Hoplias malabaricus (Teleostei: characiformes: Erythrinidae) in tropical reservoirs with different degrees of pollution (2015) Gen. Comp. Endocrinol., 222, pp. 1-10 
504 |a Gomes, A.D., Tolussi, C.E., Boëchat, I.G., Pompêo, M.L.M., Cortez, M.P.T., Honji, R.M., Moreira, R.G., Fatty acid composition of tropical fish depends on reservoir trophic status and fish feeding habit (2016) Lipids, 51, pp. 1193-1206 
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504 |a Jobling, S., Williams, R., Johnson, A., Taylor, A., Gross-Sorokin, M., Nolan, M., Tyler, C.R., Brighty, G., Predicted exposures to steroid estrogens in U.K. rivers correlate with widespread sexual disruption in wild fish populations (2006) Environ. Health Persp., 114, pp. 32-39 
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504 |a Kinney, C.A., Furlong, E.T., Werner, S.L., Cahill, J.D., Presence and distribution of wastewater-derived pharmaceuticals in soil irrigated with reclaimed water (2006) Environ. Toxicol. Chem., 25, pp. 317-326 
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504 |a Moncaut, N., Lo Nostro, F., Maggese, M.C., Vitellogenin detection in surface mucus of the South American cichlid fish Cichlasoma dimerus (Heckel, 1840) induced by estradiol-17β. Effects on liver and gonads (2003) Aquat. Toxicol., 63, pp. 127-137 
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520 3 |a Endocrine disrupting compounds (EDCs) have the potential to alter fish reproduction at various levels of organization. The aim of this study was to assess the impact of a natural environment with heavily anthropogenic influence on the physiological processes involved in reproduction in the freshwater fish lambari (Astyanax fasciatus) using different biomarkers. Adult males and females were collected in different seasons from two distinct sites in the same watershed: Ponte Nova Reservoir (PN) considered a pristine or small anthropogenic influence reference point; and Billings Reservoir (Bil), subjected to a large anthropogenic impact. Biological indices, such as hepatosomatic index and gonadosomatic index (GSI), gonadal histomorphology, fecundity, and biomarkers such as plasma levels of estradiol (E2) as well as hepatic gene expression of its alfa nuclear receptor (ERα), were analyzed. Hepatic vitellogenin (VTG) gene expression was evaluated in both sexes, as an indicator of xenoestrogen exposure. Females collected at PN presented a typical annual variation reflected in GSI, whereas for those sampled at Bil the index did not change through the seasons. The higher concentration of E2 in males collected at Bil during spring/2013, together with the detection of VTG gene expression, suggest the presence of EDCs in the water. These EDCs may have also influenced fecundity of females from Bil, which was higher during winter and spring/2013. Gene expression of ERα and ovarian morphology did not differ between fish from both sites. Water conditions from Bil reservoir impacted by anthropic activity clearly interfered mainly with biomarkers of biological effect such as plasma E2 levels and absolute and relative fecundity, but also altered biomarkers of exposure as VTG gene expression. These facts support the notion that waterborne EDCs are capable of causing estrogenic activity in A. fasciatus. © 2017 Elsevier Inc.  |l eng 
536 |a Detalles de la financiación: Fundação de Amparo à Pesquisa do Estado de São Paulo, FAPESP, 2014/01866-4, 12/50371-2, 2011/15453-5 
536 |a Detalles de la financiación: Universidad de Buenos Aires, UBA 
536 |a Detalles de la financiación: Consejo Nacional de Investigaciones Científicas y Técnicas, CONICET, 2013/50480-9 
536 |a Detalles de la financiación: This work was supported by FAPESP ( Fundação de Amparo à Pesquisa do Estado de São Paulo ) [Research Grant: 12/50371-2 , a Ph.D. scholarship: 2011/15453-5 and a scholarship stage through the International Research Project: 2014/01866-4 ] FAPESP-CONICET ( Consejo Nacional de Investigaciones Científicas y Técnicas, Argentina ) [ 2013/50480-9 ]. We thank the Laboratorio de Ecotoxicología Acuática at Universidad de Buenos Aires, Argentina; and Contaminant Biogeochemistry and Environmental Toxicology group of Common Wealth Scientific and Industrial Research Organization at Adelaide, Australia. The authors also thank the fishermen (Evaldo Bizarrias and Milton Nunes de Santana), and the LAMEROA team for their help with sampling and IB/USP for providing logistics and facilities for the study. 
593 |a Laboratório de Metabolismo e Reprodução de Organismos Aquáticos, Departamento de Fisiologia, Instituto de Biociências, Universidade de São Paulo. Rua do Matão, Trav.14, n° 321, São Paulo, SP 05508-090, Brazil 
593 |a Environmental Contaminant Mitigation and Technologies Program, CSIRO Land and Water, Private Bag No. 2, Glen Osmond, SA 5064, Australia 
593 |a Departamento de Biologia e Zootecnia, Universidade Estadual Paulista Júlio de Mesquita Filho, Campus de Ilha Solteira, Rua Monção, n°226, Ilha Solteira, 15385-000, Brazil 
593 |a Laboratorio de Ecotoxicología Acuática, Departamento de Biodiversidad y Biología Experimental, Facultad de Ciencias Exactas y Naturales, Universidad de Buenos Aires & IBBEA, CONICET-UBA, Ciudad Universitaria (C1428EHA), Buenos Aires, Argentina 
593 |a Centro de Aquicultura (CAUNESP). Universidade Estadual Paulista Júlio de Mesquita Filho, V. Acesso Prof. Paulo Donato Castelane s/n, Jaboticabal, SP 14884-900, Brazil 
690 1 0 |a ANTHROPOGENIC IMPACT 
690 1 0 |a CHARACIDAE 
690 1 0 |a ENDOCRINE DISRUPTING COMPOUNDS 
690 1 0 |a ESTRADIOL 
690 1 0 |a GENE EXPRESSION 
690 1 0 |a OOCYTE MATURATION 
690 1 0 |a VITELLOGENIN 
690 1 0 |a ENDOCRINE DISRUPTOR 
690 1 0 |a ESTRADIOL 
690 1 0 |a ESTROGEN RECEPTOR ALPHA 
690 1 0 |a VITELLOGENIN 
690 1 0 |a BIOLOGICAL MARKER 
690 1 0 |a ENDOCRINE DISRUPTOR 
690 1 0 |a ESTRADIOL 
690 1 0 |a FRESH WATER 
690 1 0 |a VITELLOGENIN 
690 1 0 |a ANTHROPOGENIC EFFECT 
690 1 0 |a BIOCHEMISTRY 
690 1 0 |a BIOMARKER 
690 1 0 |a ENDOCRINE DISRUPTOR 
690 1 0 |a ESTROGENIC COMPOUND 
690 1 0 |a GENE EXPRESSION 
690 1 0 |a MATURATION 
690 1 0 |a MOLECULAR ANALYSIS 
690 1 0 |a PHYSIOLOGICAL RESPONSE 
690 1 0 |a POLLUTION EFFECT 
690 1 0 |a TELEOST 
690 1 0 |a ADULT 
690 1 0 |a ANIMAL EXPERIMENT 
690 1 0 |a ANIMAL TISSUE 
690 1 0 |a ANTHROPOMETRIC PARAMETERS 
690 1 0 |a ASTYANAX FASCIATUS 
690 1 0 |a BRAZIL 
690 1 0 |a CHARACIDAE 
690 1 0 |a CHARACIFORMES 
690 1 0 |a CONTROLLED STUDY 
690 1 0 |a ESTRADIOL BLOOD LEVEL 
690 1 0 |a ESTROGEN ACTIVITY 
690 1 0 |a FEMALE 
690 1 0 |a FERTILITY 
690 1 0 |a GENE EXPRESSION 
690 1 0 |a GONAD DEVELOPMENT 
690 1 0 |a GONADOSOMATIC INDEX 
690 1 0 |a HEPATOSOMATIC INDEX 
690 1 0 |a MALE 
690 1 0 |a NONHUMAN 
690 1 0 |a OOCYTE DEVELOPMENT 
690 1 0 |a OVARY DEVELOPMENT 
690 1 0 |a POLLUTION 
690 1 0 |a REVIEW 
690 1 0 |a SEASONAL VARIATION 
690 1 0 |a TELEOST 
690 1 0 |a WATERSHED 
690 1 0 |a ANALYSIS 
690 1 0 |a ANIMAL 
690 1 0 |a CHARACIDAE 
690 1 0 |a CHEMISTRY 
690 1 0 |a DRUG EFFECTS 
690 1 0 |a ENVIRONMENTAL MONITORING 
690 1 0 |a GONAD 
690 1 0 |a GROWTH, DEVELOPMENT AND AGING 
690 1 0 |a METABOLISM 
690 1 0 |a ORGANOGENESIS 
690 1 0 |a PATHOLOGY 
690 1 0 |a PROCEDURES 
690 1 0 |a REPRODUCTION 
690 1 0 |a SEASON 
690 1 0 |a TOXICITY 
690 1 0 |a WATER POLLUTANT 
690 1 0 |a ASTYANAX FASCIATUS 
690 1 0 |a CHARACIDAE 
690 1 0 |a CHARACIFORMES 
690 1 0 |a TELEOSTEI 
690 1 0 |a ANIMALS 
690 1 0 |a BIOMARKERS 
690 1 0 |a BRAZIL 
690 1 0 |a CHARACIDAE 
690 1 0 |a ENDOCRINE DISRUPTORS 
690 1 0 |a ENVIRONMENTAL MONITORING 
690 1 0 |a ESTRADIOL 
690 1 0 |a FEMALE 
690 1 0 |a FERTILITY 
690 1 0 |a FRESH WATER 
690 1 0 |a GENE EXPRESSION 
690 1 0 |a GONADS 
690 1 0 |a MALE 
690 1 0 |a ORGANOGENESIS 
690 1 0 |a REPRODUCTION 
690 1 0 |a SEASONS 
690 1 0 |a VITELLOGENINS 
690 1 0 |a WATER POLLUTANTS, CHEMICAL 
700 1 |a Gomes, A.D.O. 
700 1 |a Kumar, A. 
700 1 |a Ribeiro, C.S. 
700 1 |a Nostro, F.L.L. 
700 1 |a Bain, P.A. 
700 1 |a de Souza, G.B. 
700 1 |a Cuña, R.D. 
700 1 |a Honji, R.M. 
700 1 |a Moreira, R.G. 
773 0 |d Academic Press, 2018  |g v. 147  |h pp. 926-934  |p Ecotoxicol. Environ. Saf.  |x 01476513  |w (AR-BaUEN)CENRE-4483  |t Ecotoxicology and Environmental Safety 
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