2016
DOI: 10.1016/j.etap.2016.08.009
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Peroxisome proliferator-activated receptor gamma (PPARγ) in brown trout: Interference of estrogenic and androgenic inputs in primary hepatocytes

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Cited by 10 publications
(6 citation statements)
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“…These compounds affect the PPAR pathway either by directly binding the LBD or through direct transcriptional effects on PPARγ target genes, commonly resulting in metabolic disorders. Although previous studies have indicated that some exogenous steroids, including trenbolone acetate, inhibit PPARγ expression (Salehzadeh et al 2011; Chung et al 2012; Lopes et al 2016), these studies examined PPARγ expression in skeletal muscle and primary hepatocytes in mammals and fish. In contrast, in the present study, we observed an up‐regulation of PPARγ.…”
Section: Discussionmentioning
confidence: 99%
“…These compounds affect the PPAR pathway either by directly binding the LBD or through direct transcriptional effects on PPARγ target genes, commonly resulting in metabolic disorders. Although previous studies have indicated that some exogenous steroids, including trenbolone acetate, inhibit PPARγ expression (Salehzadeh et al 2011; Chung et al 2012; Lopes et al 2016), these studies examined PPARγ expression in skeletal muscle and primary hepatocytes in mammals and fish. In contrast, in the present study, we observed an up‐regulation of PPARγ.…”
Section: Discussionmentioning
confidence: 99%
“…In male zebrafish ( Danio rerio ), 4 ng/L EE2 exposure for 90 days post-fertilization was related to the build-up of adipocytes in the testis, suggesting signs of early obesity [ 40 ]. An in vitro study on the livers of brown trout indicated that EE2, as with other estrogenic compounds, interfered with the activity of PPAR-γ, with a significant (3-fold) decrease in response to 50 µM EE2 [ 15 ]. In adult male ten spotted live-bearer fish ( Cnesterodon decemmaculatus) , exposure to a concentration of EE2 up to 200 ng/L was associated with increased steatosis, necrosis, and disruption of acinar organization (effects detected starting from 100 ng/L EE2) [ 41 ].…”
Section: Environmental and Human Health Implications Of Edc Exposurementioning
confidence: 99%
“…EDCs interfere with many hormone-regulated physiological pathways and have complex effects on human and fish physiology due to the diversity of the hormone receptors and enzymes that they bind [ 10 ]. The detailed mechanisms by which ED compounds act is not completely understood, but many interact with nuclear receptors, such as the retinoid X receptor (RXR) [ 11 , 12 , 13 , 14 ], peroxisome proliferator-activated receptors (PPARs) [ 14 , 15 , 16 , 17 , 18 ] and estrogen receptors (ERs) [ 19 , 20 ]. The binding of EDCs to these and other receptors, as well as steroidogenic enzymes, can perturb normal physiological processes.…”
Section: Introductionmentioning
confidence: 99%
“…Androgens and estrogens are the primary types of sex steroids. Exogenous testosterone significantly inhibited the expression of PPAR γ in primary hepatocytes isolated from brown trout [ 11 ]. 17 β -Estradiol could regulate the expression of PPAR γ in human peripheral blood eosinophils [ 12 ].…”
Section: Interaction Between Ppars and Sex Steroidsmentioning
confidence: 99%