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Medicinas Complementárias
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1.
Aquat Toxicol ; 105(1-2): 136-50, 2011 Sep.
Artículo en Inglés | MEDLINE | ID: mdl-21722617

RESUMEN

Produced water (PW), a by-product of the oil-production process, contains large amount of alkylphenols (APs) and other harmful oil compounds. In the last 20 years, there have been increasing concerns regarding the environmental impact of large increases in the amounts of PW released into the North Sea. We have previously shown that low levels of APs can induce disruption of the endocrine and reproductive systems of Atlantic cod (Gadus morhua). The aims of this follow-up study were to: (i) identify the lowest observable effect concentration of APs; (ii) study the effects of exposure to real PW, obtained from a North Sea oil-production platform; and (iii) study the biological mechanism of endocrine disruption in female cod. Fish were fed with feed paste containing several concentrations of four different APs (4-tert-butylphenol, 4-n-pentylphenol, 4-n-hexylphenol and 4-n-heptylphenol) or real PW for 20 weeks throughout the normal period of vitellogenesis in Atlantic cod from October to January. Male and female cod, exposed to AP and PW, were compared to unexposed fish and to fish fed paste containing 17ß-oestradiol (E(2)). Approximately 60% of the females and 96% of the males in the unexposed groups were mature at the end of the experiment. Our results show that exposure to APs and E(2) have different effects depending on the developmental stage of the fish. We observed that juvenile females are advanced into puberty and maturation, while gonad development was delayed in both maturing females and males. The AP-exposed groups contained increased numbers of mature females, and significant differences between the untreated group and the AP-treated groups were seen down to a dose of 4 µg AP/kg body weight. In the high-dose AP and the E(2) exposed groups, all females matured and no juveniles were seen. These results suggest that AP-exposure can affect the timing of the onset of puberty in fish even at extremely low concentrations. Importantly, similar effects were not seen in the fish that were exposed to real PW.


Asunto(s)
Ovario/efectos de los fármacos , Fenoles/toxicidad , Desarrollo Sexual/efectos de los fármacos , Contaminantes Químicos del Agua/toxicidad , Animales , Aromatasa/metabolismo , Relación Dosis-Respuesta a Droga , Disruptores Endocrinos/toxicidad , Sistema Endocrino/efectos de los fármacos , Sistema Endocrino/metabolismo , Estradiol/sangre , Femenino , Hormona Folículo Estimulante/genética , Hormona Folículo Estimulante/metabolismo , Gadus morhua , Hormona Luteinizante/genética , Hormona Luteinizante/metabolismo , Masculino , Ovario/crecimiento & desarrollo , Ovario/metabolismo , ARN Mensajero/metabolismo , Estaciones del Año , Razón de Masculinidad , Maduración Sexual/efectos de los fármacos , Testosterona/sangre , Vitelogeninas/metabolismo
2.
Mar Environ Res ; 70(5): 383-94, 2010 Dec.
Artículo en Inglés | MEDLINE | ID: mdl-20846718

RESUMEN

Produced water (PW) contains numerous toxic compounds of natural origin, such as dispersed oil, metals, alkylphenols (APs), and polycyclic aromatic hydrocarbons (PAHs). In addition, PW also contains many different chemicals which have been added during the oil production process. In the study described here, cod were exposed to real PW collected from an oil production platform in the North Sea. This was done in order to best recreate the most realistic field-exposure regime in which fish will be affected by a wide range of chemicals. The biological effects found in this study therefore cannot be assigned to one group of chemicals alone, but are the result of exposure to the complex chemical mixture found in real PW. Since APs are well known to cause endocrine disruption in marine organisms, we focused our chemical analysis on APs in an attempt to better understand the long-term effects of APs from PW on the biology of fish. In this study, cod were exposed to several concentrations of real PW and 17ß-oestradiol (E(2)), a natural oestrogen, at different developmental stages. Cod were exposed to PW either during the embryo and early larvae stage (up to 3 months of age) or during the early juvenile stage (from 3 to 6 months of age). Results showed that, in general, APs bioconcentrate in fish tissue in a dose and developmental stage dependent manner during PW exposure. However, juveniles appeared able to effectively metabolise the short chain APs. Importantly, PW exposure had no effect on embryo survival or hatching success. However, 1% PW clearly interfered with the development of normal larval pigmentation. After hatching most of the larvae exposed to 1% PW failed to begin feeding and died of starvation. This inability to feed may be linked to the increased incidence of jaw deformities seen in these larvae. In addition, cod exposed to 1% PW, had significantly higher levels of the biomarkers vitellogenin and CYP1A in plasma and liver, respectively. No similar effects were seen in cod exposed to either 0.1% or 0.01% PW.


Asunto(s)
Embrión no Mamífero/efectos de los fármacos , Gadus morhua/embriología , Residuos Industriales/análisis , Hidrocarburos Policíclicos Aromáticos/toxicidad , Contaminantes Químicos del Agua/toxicidad , Animales , Embrión no Mamífero/anomalías , Embrión no Mamífero/metabolismo , Industria Procesadora y de Extracción , Femenino , Gadus morhua/anomalías , Gadus morhua/crecimiento & desarrollo , Larva/efectos de los fármacos , Larva/crecimiento & desarrollo , Larva/metabolismo , Masculino , Óvulo/efectos de los fármacos , Petróleo/toxicidad , Agua de Mar/química
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