Changes in hematological parameters of cichlasoma dimerus (Teleostei, Perciformes) exposed to sublethal concentrations of 4-tert-octylphenol

Stress response involves various physiological changes, including alteration in hematological parameters closely related to the response of fish to the environment. 4-tert-octylphenol (OP) is one of the worldwide-used surfactants and can pollute the aquatic environment, both marine and freshwater. P...

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Autor principal: Vázquez, G.R
Otros Autores: Nostro, F.L
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Lenguaje:Inglés
Publicado: Springer New York LLC 2014
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024 7 |2 scopus  |a 2-s2.0-84899493599 
024 7 |2 cas  |a 4 tert octylphenol, 27193-28-8; alcohol, 64-17-5; water, 7732-18-5 
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100 1 |a Vázquez, G.R. 
245 1 0 |a Changes in hematological parameters of cichlasoma dimerus (Teleostei, Perciformes) exposed to sublethal concentrations of 4-tert-octylphenol 
260 |b Springer New York LLC  |c 2014 
270 1 0 |m Vázquez, G.R.; Lab. de Ecotoxicología Acuática, Dpto. de Biodiversidad Y Biología Experimental, Ciudad Universitaria, C1428EHA Buenos Aires, Argentina; email: grarey@bg.fcen.uba.ar 
506 |2 openaire  |e Política editorial 
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520 3 |a Stress response involves various physiological changes, including alteration in hematological parameters closely related to the response of fish to the environment. 4-tert-octylphenol (OP) is one of the worldwide-used surfactants and can pollute the aquatic environment, both marine and freshwater. Previous studies have already shown estrogenic effects of this compound in various wildlife species, e.g., it can disrupt the reproductive system of males organisms including fish. The purpose of this study was to evaluate the effects caused by sublethal concentrations of OP on hematological parameters as biomarkers to assess environmental stress. Adult males and females of Cichlasoma dimerus were exposed to waterborne OP during 60 days under semistatic conditions. Experimental groups consisted of control (ethanol 0.005%), OP 150, and OP 300 μg/L. OP caused hemodynamic stress in C. dimerus, which lead to normochromic and normocytic anemia, as well as erythrocytic pathologies such as a significant increase in erythroblasts and amitotic erythrocytes. All of the studied parameters can be used as biomarkers for the presence of xenobiotics in water. © Springer Science+Business Media 2014.  |l eng 
593 |a Lab. de Ecotoxicología Acuática, Dpto. de Biodiversidad Y Biología Experimental, Ciudad Universitaria, C1428EHA Buenos Aires, Argentina 
593 |a BIBBEA, CONICET-UBA, Buenos Aires, Argentina 
690 1 0 |a 4 TERT OCTYLPHENOL 
690 1 0 |a ALCOHOL 
690 1 0 |a BIOLOGICAL MARKER 
690 1 0 |a WATER 
690 1 0 |a XENOBIOTIC AGENT 
690 1 0 |a ADULT 
690 1 0 |a ANEMIA 
690 1 0 |a ANIMAL CELL 
690 1 0 |a ANIMAL EXPERIMENT 
690 1 0 |a ARTICLE 
690 1 0 |a CICHLASOMA DIMERUS 
690 1 0 |a CONCENTRATION (PARAMETERS) 
690 1 0 |a CONTROLLED STUDY 
690 1 0 |a ENVIRONMENTAL EXPOSURE 
690 1 0 |a ENVIRONMENTAL STRESS 
690 1 0 |a ERYTHROBLAST 
690 1 0 |a ERYTHROCYTE 
690 1 0 |a FEMALE 
690 1 0 |a FISH 
690 1 0 |a HEMATOLOGICAL PARAMETERS 
690 1 0 |a HEMODYNAMIC STRESS 
690 1 0 |a LEUKOCYTE 
690 1 0 |a MALE 
690 1 0 |a NONHUMAN 
690 1 0 |a PRIORITY JOURNAL 
690 1 0 |a SPECIES 
690 1 0 |a TELEOST 
690 1 0 |a CICHLASOMA 
690 1 0 |a PERCIFORMES 
690 1 0 |a TELEOSTEI 
690 1 0 |a ANIMALS 
690 1 0 |a BIOLOGICAL MARKERS 
690 1 0 |a CICHLIDS 
690 1 0 |a DOSE-RESPONSE RELATIONSHIP, DRUG 
690 1 0 |a ESTROGENS 
690 1 0 |a FEMALE 
690 1 0 |a MALE 
690 1 0 |a PHENOLS 
690 1 0 |a TOXICITY TESTS 
690 1 0 |a WATER POLLUTANTS, CHEMICAL 
700 1 |a Nostro, F.L. 
773 0 |d Springer New York LLC, 2014  |g v. 66  |h pp. 463-469  |k n. 3  |p Arch. Environ. Contam. Toxicol.  |x 00904341  |w (AR-BaUEN)CENRE-3813  |t Archives of Environmental Contamination and Toxicology 
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