L. Dinan et al., Screening of environmental contaminants for ecdysteroid agonist and antagonist activity using the Drosophila melanogaster B-II cell in vitro assay, ENV TOX CH, 20(9), 2001, pp. 2038-2046
The B-II bioassay was developed as a rapid and reliable toot for detecting
potential insect growth regulators acting as ecdysteroid receptor (ant)agon
ists. Based on an ecdysteroid-responsive cell line from Drosophila melanoga
ster, this microplate assay is ideally suited to the evaluation of environm
ental contaminants as potential endocrine disrupters. Data are presented fo
r about 80 potential environmental contaminants, including industrial chemi
cals, pesticides, pharmaceuticals, phytoestrogens, and vertebrate steroids,
and are compared with data for known (ant)agonists, Apart from androst-4-e
ne-3,17-dione (a weak antagonist), vertebrate steroids were inactive at con
centrations up to 10(-3) M. The vast majority of xenobiotics also showed no
(ant)agonist activity. Among the industrial chemicals, antagonistic activi
ty was observed for bisphenol A median effective concentration (EC50) of 1.
0 x 10(-4) M and diethylphthalate (EC50 of 2.0 x 10(-3) M). Some organochlo
rine compounds also showed weak antagonistic activity, including o,p ' -dic
hlorodiphenyldichloroethylene (DDE), p,p ' -DDE, dieldrin, and lindane (EC5
0 of 3.0 x 10(-5) M). For lindane, bisphenol A, and diethylphthalate, activ
ity is not associated with impurities in the samples and, for lindane and b
isphenol A at least, the compounds are able to compete with ecdysteroids fo
r the ligand binding site on the receptor complex, albeit at concentrations
very much higher than those found in the environment. The only pharmaceuti
cal showing any detectable antagonist activity was 17 alpha -ethynylestradi
ol. In the context of recent publications on potential endocrine disruption
in marine and freshwater arthropods, these findings suggest that, for some
compounds (e.g., diethylstilbestrol), ecdysteroid receptor-mediated respon
ses are unlikely to be involved in producing chronic effects. The B-II assa
y has a potentially valuable role to play in distinguishing between endocri
ne-mediated, which normally occur at submicromolar concentrations, and phar
macological effects in insects and crustaceans.