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1.
Mar Pollut Bull ; 124(2): 743-752, 2017 Nov 30.
Artigo em Inglês | MEDLINE | ID: mdl-28552249

RESUMO

Our previous study in 2011 reported the detection of BPA and PFAAs in 20 species of marine and freshwater fishes. With an emerging evidence to suggest the metabolic-disrupting effects of BPA/PFAAs in animals, the present study was aimed to provide a time-trend analysis to determine the current concentrations of PFAAs and BPA in 20 commercially available Hong Kong species of fishes. Since the manufacture and use of BPA is being prohibited in most nations, the introduction of BPA alternatives has recently been incorporated in the markets. Therefore, the concentrations of BPB, BPF and BPS were determined. In the present study, all freshwater and seawater fish samples showed quantified concentrations [>Limit of Quantification (LOQ<0.5ng/g)] of BPA. BPF was detected in some marine (yellow seafin, bigeye, goldspotted rabbitfish, snubnose pompano, tongue sole, Bleeker's grouper and orange-spotted grouper) and freshwater fishes (mud carp, crucian carp, tilapia, catfish, mandarin fish, grass carp, grey mullet and spotted snakehead). Two of the compounds, BPS and BPB could only be identified in the marine fishes (snubnose pompano, yellow seafin). In PFAA analysis, PFOA, PFDA, PFOS, PFUdA and PFDoA were found in most of the marine and freshwater fishes. PFOS and PFOA were shown to be the two predominant PFAAs in fishes. On the basis of the measured concentrations of bisphenols, BPs (BPA, BPB, BPF, BPS) and PFAAs, the average daily intake for BPs (20.5-31.5ng/kgb.w./day) and PFAAs (1.17-1.83ng/kgb.w./day) were calculated and found to be lower than values of tolerable daily intake (TDI) established in Europe. However, as compared with our previous study in 2011, the present study revealed an approximate 10-fold increase in the concentrations of BPA in the fish samples. Although the hazard ratio of consuming fishes for BPA and PFAA exposure is expected to remain low, possible additive metabolic-disrupting effect of BPA and its analogues as well PFAAs should be taken into consideration for human health risk assessment.


Assuntos
Compostos Benzidrílicos/análise , Peixes , Hidrocarbonetos Fluorados/análise , Fenóis/análise , Alimentos Marinhos/análise , Animais , Carpas , Água Doce , Hong Kong , Água do Mar , Tilápia
2.
Reprod Toxicol ; 31(4): 409-17, 2011 May.
Artigo em Inglês | MEDLINE | ID: mdl-21182934

RESUMO

Bisphenol A (BPA) is used in the manufacture of many products and is ubiquitous in the environment. Adverse effects of BPA on animal reproductive health have been reported, however most of the studies relied on the approaches in the assessment of conventional histology and anatomical features. The mechanistic actions of BPA are not clear. In the present study, a murine model was used to study potential effects of BPA exposure during perinatal and postnatal periods on endocrine functions of hypothalamic-pituitary-gonadal (HPG)-axis. At the hypothalamic-pituitary level, BPA exposure resulted in the up-regulation of the expression levels of KiSS-1, GnRH and FSH mRNA in both male and female pups. At the gonadal levels, BPA caused inhibition in the expressions of testicular steroidogenic enzymes and the synthesis of testosterone in the male pups. Conversely exposure to BPA resulted in a greater aromatase expression level and the synthesis of estrogen in the female pups. BPA is a weak estrogen agonist and its effects reported on animal studies are difficult to reconcile with mechanistic action of estrogen. In this study we hypothesized that the effects of BPA on reproductive dysfunction may be due to its actions on gonadal steroidogenesis and so the anomalous releases of endogenous steroid hormones. This non-ER-mediated effect is more potent in affecting the feedback regulatory circuits in the HPG-axis.


Assuntos
Disruptores Endócrinos/toxicidade , Poluentes Ambientais/toxicidade , Sistema Hipotálamo-Hipofisário/efeitos dos fármacos , Ovário/efeitos dos fármacos , Fenóis/toxicidade , Reprodução/efeitos dos fármacos , Testículo/efeitos dos fármacos , Fatores Etários , Envelhecimento , Análise de Variância , Animais , Compostos Benzidrílicos , Relação Dose-Resposta a Droga , Feminino , Regulação da Expressão Gênica no Desenvolvimento/efeitos dos fármacos , Idade Gestacional , Hormônios Esteroides Gonadais/biossíntese , Gonadotropinas Hipofisárias/metabolismo , Sistema Hipotálamo-Hipofisário/crescimento & desenvolvimento , Sistema Hipotálamo-Hipofisário/metabolismo , Masculino , Camundongos , Nível de Efeito Adverso não Observado , Ovário/crescimento & desenvolvimento , Ovário/metabolismo , Gravidez , Efeitos Tardios da Exposição Pré-Natal , RNA Mensageiro/metabolismo , Receptores Acoplados a Proteínas G/efeitos dos fármacos , Receptores Acoplados a Proteínas G/genética , Receptores de Peptídeos/efeitos dos fármacos , Receptores de Peptídeos/genética , Receptores de Esteroides/efeitos dos fármacos , Receptores de Esteroides/genética , Testículo/crescimento & desenvolvimento , Testículo/metabolismo
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