In vivo bioluminescence imaging to evaluate estrogenic activities of endocrine disrupters
Section snippets
Materials
Materials for cell culture were obtained from Invitrogen (Cergy-Pontoise, France). Luciferin was purchased from Promega (Charbonnières, France). Tribromoethanol (TBE), 17β estradiol (E2), ethynylestradiol (EE2), estrone (E1), genistein (Gen), 2,4′-dichlorodiphenyldichloroethylene (2,4′-DDE), and 4-tert-octylphenol (OP) were purchased from Sigma Chemical (Saint Quentin-Fallavier, France). Effectors were dissolved in dimethyl sulfoxide at 10−2 M.
Generation of stably transfected reporter cell lines
The stably transfected luciferase reporter MELN cell
MELN cell in vitro assay
A great number of compounds able to activate ERα were tested with the MELN cell in vitro assay. The typical dose–response curve of most estrogenic compounds in the MELN cell assay was a sigmoid curve leveling off at a value corresponding to the maximal inductive effect (Fig. 1). Maximum value, taken as 100, was obtained in presence of 10 nM E2 in cell medium; basal activity was 15% of maximal activity and presence of antagonist reduced transactivation [15], [22]. Since antiestrogens were able to
Discussion
In this study, bioluminescence-based measurements were performed to evaluate estrogenic activities of several estrogens and endocrine disrupters using in vitro and in vivo luciferase-expressing tumor cells. The optical reporter gene that we used in our oncology models is a modified version of that isolated from firefly P. pyralis. Luciferase enzyme produces light in presence of luciferin substrate, oxygen, and ATP [25]. in vitro, luciferase uses intracellular oxygen and ATP, and adding 0.3 μM
Acknowledgments
This research was supported by INSERM (ATC), Montpellier 1 University (BQR), l’ARC and la Ligue de lutte contre le cancer (RA). The authors thank Michel Brissac for help in performing animal experiments.
References (27)
Xenoendocrine disrupters-environmental impacts
Toxicol. Lett.
(1998)- et al.
Reporter cell lines to study the estrogenic effects of xenoestrogens
Sci. Total Environ.
(1999) - et al.
Detection of estrogenic activity in sediment-associated compounds using in vitro reporter gene assays
Sci. Total Environ.
(2002) - et al.
MVLN cells: a bioluminescent MCE-7-derived cell line to study the modulation of estrogenic activity
J. Steroid Biochem. Mol. Biol.
(1993) - et al.
Comparison of an array of in vitro assays for the assessment of the estrogenic potential of natural and synthetic estrogens, phytoestrogens and xenoestrogens
Toxicology
(2001) - et al.
Clinical characteristics and pharmacokinetics of purified soy isoflavones: single-dose administration to healthy men
Am. J. Clin. Nutr.
(2002) Chemistries and colors of bioluminescent reactions: a review
Gene
(1996)Insights from the study of animals lacking functional estrogen receptor
Science
(1994)- et al.
Comparison of the ligand binding specificity and transcript tissue distribution of estrogen receptors alpha and beta
Endocrinology
(1997) In vitro bioassays for assessing estrogenic substances
Environ. Sci. Technol.
(1997)
Identification of estrogenic chemicals in STW effluent. 1. chemical fractionation and in vitro biological screening
Environ. Sci. Technol.
Identification of environmental chemicals with estrogenic activity using a combination of in vitro assays
Environ. Health Perspect.
Development of a stably transfected estrogen receptor-mediated luciferase reporter gene assay in the human T47D breast cancer cell line
Toxicol. Sci.
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