E-SCREEN

E-SCREEN is a cell proliferation assay based on the enhanced proliferation of human breast cancer cells (MCF-7) in the presence of estrogen active substances. The E-Screen test is a reliable tool to easily and rapidly assess estrogenic activity of suspected xenoestrogens (singly or in combination). This bioassay that measures estrogen-induced increase of the number of human breast cancer cell, which it is biologically equivalent to the increase of mitotic activity in tissues of the genital tract, was originally developed by Soto et al.

The E-screen test

The E-screen cell proliferation assay is performed with the human MCF-7 breast cancer cell line, an established estrogenic cell line that endogenously expresses ERα.

File:Culture multiwell plate.png

A culture multiwell plate

Human MCF-7 are cultivated in Dulbecco’s modified Eagle’s medium (DMEM) with fetal bovine serum (FBS) and phenol red as buffer tracer (culture medium), at 37 °C, in an atmosphere of 5% CO₂ and 95% air under saturating humidity. To accomplish the E-SCREEN assay the cells are trypsinized and plated in well culture plates. Cells are allowed to attach for 24 h, and the 4 seeding medium is then removed and replaced with the experimental culture medium (phenol red free DMEM with charcoal dextran treated fetal bovine serum -steroid-free-).

A tissue culture hood

For assaying suspected estrogen active substances, a range of concentrations of the test compound is added to the experimental medium. In each experiment, the cells are exposed to a dilution series of 17β-estradiol (0.1 pM–1000 pM) for providing a positive control (standard dose-response curve), and treated only with hormone-free medium as a negative control. The bioassay ends on day 6 (late exponential phase) by removing the media from the wells and fixing the cells with trichloroacetic acid. After incubation (30 min; 4 °C) the trichloroacetic acid is removed by washing the plates under a gentle stream of cold water. After drying the plates at 40 °C the cell protein is stained with sulforhodamine B (SRB). After incubation (10 min) the dye is washed off with aqueous acetic acid (1%) and the plates are dried again at 40 °C. Finally, bound dye is solubilized with tris-buffer and incubated (20 min; 4 °C) and the absorbance is read at 492 nm.

The estrogenic activity results are expressed as mean ± standard deviation of the proliferative effect (PE), which represents the maximum proliferation induced by the test compound, and is the ratio between the highest cell number achieved with the sample or 17-β-estradiol and the cell number in the control group:

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The estrogenic activity of a sample is evaluated by determining the relative efficacy of stimulation, called the relative proliferative effect (RPE%). The RPE compares the maximum proliferation induced by a sample with that induced by 17-β-estradiol:

$\quad RPE\%={(PE-1)sample \over (PE-1)17\ Beta\ estradiol}\cdot 100$

The RPE can be used to define full agonists for ER, between 80% and 100% relative proliferation. Partial and weak agonists induce a relative cell proliferation from 25% up to 80%, or 10% to 25%, respectively.

Shortcomings/Limitations: One of the limitations for determining estrogenicity of chemicals by checking the proliferation of ER positive MCF-7 cell line is that mitogens other than estrogens can also influence cell proliferation thus rendering non-specific responses by chemicals.

The rationality for the use of this cell line is that:

1. It is a cell line of endocrine origin and is ER positive
2. Expresses aromatase and 5α-reductase like other steroidogenic cells
3. Possesses endogenous aromatase activity which converts androgens to estrogens and
4. Can elicit an estrogen-induced response involving both genomic and non-genomic pathways.

Mechanisms of action

The biological effects of estrogens (and xenoestrogens) are mediated through the estrogen receptor (ER). Estrogen receptors, which belong to a large superfamily of nuclear receptors, are transcription factors that induce transcription of target genes after binding to specific DNA sequences in their promoter.

Estrogen receptor 1 (ERα)

Estrogen receptor 2 (ERβ)

There are two isoforms (ERα and ERβ):

1. The ERα is present in the uterus, and it is thought to drive the uterotropic response, since the uteri of the ERα "knock-out" mice do not respond to the estrogen administration.
2. The ERβ is present in organs such as prostate, hypothalamic nuclei and pituitary gland.

It is also present, together with ERα in some human breast cancer cell lines.

The ER mediates most of the biological effects at the level of gene regulation by interacting through its site-specific DNA and with other coregulatory proteins. The classical mechanism of activation of ERs depends on ligand binding to the nuclear hormone receptors, after which the receptors dimerize and bind to estrogen response elements (EREs) located in the promoters of estrogen-responsive genes.

Nevertheless, basic scientific research shows that estrogens (and xenoestrogens) may also exert actions through nonnuclear steroid hormone receptors (e.g., membrane ERs), nonsteroid receptors (e.g., neurotransmitter receptors such as the serotonin receptor, dopamine receptor, norepinephrine receptor), orphan receptors [e.g., aryl hydrocarbon receptor (AhR)—an orphan receptor], enzymatic pathways involved in steroid biosynthesis and/or metabolism, and numerous other mechanisms that converge upon endocrine and reproductive systems.

Human health implications

Several reports suggest that xenoestrogens are clinically significant because they can mimic the effects of endogenous estrogen and directly or indirectly have been implicated in precocious puberty and other disorders of the reproductive system in wildlife and humans.

For example, many xenoestrogens are suspected to contribute to the development of breast cancer in women and prostate and testicular cancers in men, to reduce male fertility and to interact with the immune system.