Printer Friendly

The Mouse Uterotrophic Assay: A Reevaluation of its Validity in Assessing the Estrogenicity of Bisphenol A.

The prevalence of synthetic chemicals in our environment that are capable of mimicking the female hormone estrogen is a growing concern. One such chemical, bisphenol A (BPA), has been shown to leach from a variety of resin-based and plastic products, including dental sealants and food and beverage containers, in concentrations that are sufficient to induce cell proliferation in vitro. The response to BPA in vivo has been varied; thus the aims of this study were to investigate a) whether BPA has an estrogenic effect in CD-1 mice, a strain that is useful for developmental studies; and b) whether the uterotrophic assay is a valid means of determining the estrogenicity of BPA by comparing it with other end points measured in the uterus. Immature female CD-1 mice were exposed to BPA in concentrations ranging from 0.1 to 100 mg/kg body weight for 3 days. Results showed that BPA induced a significant increase in the height of luminal epithelial cells within the uterus at concentrations of 5, 75, and 100 mg/kg and that BPA induced lactoferrin at concentrations of 75 and 100 mg/kg. A uterotrophic response (increase in uterine wet weight) was induced by 100 mg/kg BPA only. Further, the proportion of mice showing vaginal opening was greater after exposure to 0.1 and 100 mg/kg BPA, relative to the control animals and those receiving intermediate doses of BPA. These results demonstrate that BPA induces changes in the mouse uterus that differ depending on the exposure dose and the end point measured, and reveal that certain tissue effects show a nonmonotonic relationship with dose. These data also demonstrate that BPA induces estrogenic changes in the uterus of the CD-1 mouse, and highlight the need to reevaluate the validity of the mouse uterotrophic assay as an end point for determining the estrogenicity of suspected environmental estrogens. Key words: bisphenol A, CD-1 mouse, endocrine disruptors, lactoferrin, morphometrics, nonmonotonic dose-response curves, uterotrophic assay. Environ Health Perfect 109:55-60 (2001). [Online 12 December 2000]

Estrogens exert a powerful influence on the development, regulation, and endocrine control of the female genital tract and mammary glands. Their capacity to induce cell proliferation in estrogen-target tissues underlies the critical role that these steroid hormones also play in carcinogenesis. Therefore, the disturbing revelation that synthetic chemicals have the capacity to mimic the effects of estrogens presents a very real concern for human health, particularly when exposure occurs at stages of tissue organization and development such as in prenatal or neonatal individuals. The fact that these chemicals do not necessarily share a similar structure to estrogen is further confounding. One such chemical is bisphenol A (BPA). This monomer is used in the manufacture of polycarbonates and epoxy resins from which a plethora of products are generated, including food and beverage containers, dental sealants, and babies' bottles. The propensity of BPA to leach from such products under normal conditions (1-5) highlights the need to investigate its potential for inducing developmental and reproductive abnormalities in humans.

Numerous studies conducted in vitro attest to the estrogenic character of BPA. This chemical has been shown to induce cell proliferation in MCF-7 cells (2,6,7), stimulate the release of prolactin from pituitary GH3 cells (8), and induce transcriptional activation of the estrogen receptor (ER) in both yeast-based assays (9) and human embryonal kidney cells via the estrogen response element (10). BPA has also been shown to up-regulate the expression of vitellogenin mRNA in primary hepatocytes derived from male Xenopus laevis (11). However, few studies have addressed the effects of in utero exposure to environmentally relevant doses of BPA in vivo. One study in male CF-1 mice described a significant increase in adult prostate weight after in utero exposure to BPA concentrations as low as 2 and 20 [micro]g (12). Although this research establishes effective doses of BPA in males using prostate weight as an end point, it is limited when extrapolating to studies in the female reproductive tract. Because this is the focus of our work, it is imperative to establish a dose-response range in female mice using an appropriate end point in a classical estrogen-target organ such as the uterus.

One established method for determining the estrogenicity of a chemical is the rodent uterotrophic assay, which measures an increase in wet weight of the uterus (13). Yet, a review of this method reveals a confounding range of results that points to species-specific and even strain-specific differences in the magnitude of the uterotrophic response to BPA. Fischer 344 rats (ovariectomized), the strain that is most sensitive to BPA exposure, exhibit an approximately 2-fold increase in uterine wet weight after 3 days exposure to 0.3 mg/kg BPA delivered via a subcutaneous implant (14). Sprague Dawley rats (ovariectomized) exhibit less sensitivity because the same dose elicits no effect (14); 10 mg/kg BPA administered orally for 4 days induces a 1.4-fold increase in wet weight (15). Immature Alpk:AP rats exhibit a uterotrophic response to 400 mg/kg BPA as evidenced by 1.3-fold and 1.5-fold increases in wet weight after oral garage and subcutaneous injection, respectively (16). The few studies conducted in mice reflect a greater uterotrophic resistance to BPA. Immature CFLP mice do not respond to 3 days subcutaneous injection of 0.5 mg BPA/mouse (approximately 16.7 mg/kg), yet 5 mg (approximately 167 mg/kg) causes toxicity to the animals (17). CD-1 mice show particular resistance to the effects of estradiol on the basis of testicular measurements (18), and they may be equally unresponsive to estrogen mimics such as BPA.

These data clearly demonstrate the absence of a systematic dose-response curve to BPA in any species or strain of rodent. In this paper we address the topic of susceptibility to BPA using the immature CD-1 mouse as a model. Because CD-1 mice are outbred for large litter size, they are useful for studies on the developmental and reproductive consequences of environmental hormones. Therefore, there is a need to establish the suitability of this strain for toxicology studies in female development and reproduction. In addition, we investigated the validity of the classical mouse uterotrophic assay because much of the confounding data regarding the effect of BPA in vivo is based on this method. We accomplished this by comparing the changes in uterine wet weight with three other end points that reflect estrogenic activity within the uterus, namely epithelial cell morphology, induction of the estrogen-inducible protein lactoferrin, and expression of proliferating cell nuclear antigen (PCNA).

Materials and Methods

Animals. Immature female CD-1 mice (Charles River Laboratories, Wilmington, MA) were maintained in a temperature-controlled room on a 14 hr light: 10 hr dark cycle in the Tufts University-New England Medical Center animal facility. Mice were fed RMH 3000 rodent diet (Agway Inc., Syracuse, NY) that tested negligible for estrogenicity, and water was supplied from glass bottles only. Cages and bedding also tested negative for estrogenicity using the E-SCREEN assay (19). All experimental procedures were approved by the Tufts University-New England Medical Center Animal Research Committee.

Vaginal opening. Before 23-day-old female mice were exposed to dimethyl sulfoxide (DMSO), BPA, or estradiol ([E.sub.2]), they were checked to see if their vaginas had opened. This typically occurs in mice around 35 days of age under the influence of estrogens and represents the initial stages of attaining sexual maturity. Before sacrifice at 26 days of age, mice were checked for vaginal opening again. We established two populations: one in which the vagina showed the beginning of a perforation but was not completely canalized (termed partial opening), and another showing complete canalization and patency (termed complete opening).

Uterotrophic assay. At 23 days of age, mice were weighed and divided randomly into 10 experimental groups (n = 4-22). We performed morphometric analyses on a subset of these animals (n = 4-12) that were randomly chosen. Nine of the groups were implanted with Alzet osmotic pumps (Alza Corp., Palo Alto, CA) containing either DMSO (vehicle), BPA, or [E.sub.2] (Sigma, St. Louis, MO); another group acted as an untreated control (no pumps were implanted). BPA and [E.sub.2] were dissolved in DMSO, and the pumps were prepared in accordance with the manufacturer's instructions to deliver BPA to mice in concentrations of 0.1, 0.5, 1, 5, 50, 75, and 100 mg/kg body weight/day, and [E.sub.2] at a concentration of 5.0 [micro]g/kg body weight/day. This dose of [E.sub.2] has been shown to induce a 2-fold increase in uterine wet weight (20). Pumps were implanted subcutaneously in mice under aseptic conditions. After 3 days mice were weighed and sacrificed by cervical dislocation, and their uteri were dissected out. Each uterus was blotted and the wet weight recorded. Data were expressed as a percentage of the body weight.


The uteri were immediately fixed in 4% formaldehyde in 0.1 M phosphate buffered saline (PBS; pH 7.4) for 10 hr. One horn of each uterus was dissected transversely into three segments. Tissue was processed through a series of alcohols and xylene, infiltrated with Paraplast paraffin (Fisher, Pittsburgh, PA) under vacuum, and embedded in paraffin. Five-micron sections were cut on a Sorvall JB-4 microtome (DuPont, Wilmington, DE), mounted on Superfrost positive charged slides (Fisher) and stained to determine a) changes in the luminal and glandular epithelium by morphometric analysis; b) immunolocalization of lactoferrin, an estrogen-inducible protein; and c) immunolocalization of PCNA to assess cell proliferation.

Morphometric analyses. Sections of uterus were stained with hematoxylin and eosin and prepared for light microscopy. The relative area of the uterine endometrium occupied by the mucosa (luminal epithelium, glandular epithelium, and lamina propria) and myometrium, and the height of the luminal epithelium were determined using the program Bioscan Optimus (Version 1.13; Media Cybernetics, Silver Springs, MD). We measured relative areas of uterine tissue compartments using the 10x objective and epithelial cell height using the 20x objective. For epithelial cell height, we measured only areas of epithelium in which the nucleus and basement membrane of single cuboidal/columnar epithelial cells could be seen. Four areas in each of three transverse sections of uterus were analyzed per animal. For the parameter of epithelial cell height, four measurements were made within four areas of the three transverse sections of each uterus per animal.


Lactoferrin. Lactoferrin was localized within the uterine epithelium by immunofluorescence (21). Sections were hydrated and microwaved in 10 mM citrate buffer (pH 6) for antigen retrieval (22); nonspecific binding was blocked with 5% normal goat serum and 5% normal rabbit serum in 0.01 M PBS. Sections were incubated overnight at 4 [degrees] C in a humid chamber with a rabbit antibody raised to mouse lactoferrin (monoclonal IgG, 1:100; supplied by Christina Teng, National Institute of Environmental Health Sciences, Research Triangle Park, NC). Biotinylated goat antirabbit IgG (1:400; Roche Diagnostics Corp., Indianapolis, IN) was applied to sections, and lactoferrin was visualized by streptavidin Alexa Fluor conjugate (Molecular Probes, Eugene, OR). Sections were counterstained with Hoechst 33258 (1:1000; Sigma) and mounted in glycerol/0.01 M PBS (1:1). Fluorescent images were captured using a SPOT-Real Time digital camera (Diagnostic Instruments, Inc., Sterling Heights, MI) attached to a Zeiss Axioskop (Carl Zeiss, Inc., Thornwood, NY) and analyzed in the SPOT-Real Time program.

We semiquantitatively determined (using the 20x objective) the expression of lactoferrin within the luminal and glandular epithelium of the uterus by assessing the intensity of staining within both the apical and basal regions of the cells. The intensity of staining ranged from 0 to 3, with 3 representing the most intense staining, similar to that observed in the estradiol group. The four scores (luminal apical, luminal basal, glandular apical, and glandular basal) were summed; thus maximal staining was represented by a score of 12. Four areas in each of the three transverse sections of uterus were analyzed per animal.

PCNA. Immunohistochemical staining of PCNA was performed using the avidinbiotin-immunoperoxidase method. Sections were hydrated and microwaved in 10 mM citrate buffer (pH 6) for antigen retrieval; both endogenous peroxidase and nonspecific binding were then blocked with 0.3% [H.sub.2][0.sub.2] in methanol and 1.5% normal goat serum in 0.01 M PBS, respectively. Sections were incubated overnight in a humid chamber at 4 [degrees] C with anti-PCNA mouse antibody (monoclonal IgM; Beckman Coulter, Miami, FL) at a dilution of 1:500. Mouse IgM preimmune serum was used at the same concentration as the primary antibody to provide an isotypic control. We applied the biotinylated secondary antibody (IgM) and avidin-peroxidase (Vectastain ABC Kit; Vector Laboratories, Burlingame, CA) to sections according to the manufacturer's instructions and visualized peroxidase activity by diaminobenzidine (Sigma). Sections were lightly counterstained with hematoxylin and prepared for light microscopy.

The expression of PCNA within the luminal epithelium of the uterus was determined by densitometric image analysis using Scion Image (Scion Corporation, Frederick, MD). Video images of the sections were captured using the 40x objective and calibrated so that the cytoplasm read 0 (0%) average gray value (AGV) and the darkest nucleus read 255 (100%) AGV. Those nuclei with an AGV near 217 (representing 15% of the highest intensity range) were counted as positive for PCNA. Data are presented as the number of PCNA-positive stained nuclei per 1,000 [micro]m basement membrane. We assessed a total length of 5000-10,000 [micro]m basement membrane from three cross-sectional areas of the uterus per animal.

Statistical Analysis

There was no significant difference between the control group and vehicle group for all variables, so data were pooled; analysis was then performed against these combined data. We analyzed uterine wet weight (as a percentage of body weight) and the relative area of luminal and glandular epithelium by one-way analysis of variance using a Tukey's post hoc comparison. Body weight, uterine wet weight (absolute), the relative area of lamina propria and myometrium, epithelial cell height, and PCNA labeling were analyzed by a Kruskal-Wallis test because data were not normally distributed. Lactoferrin induction was analyzed by a Kruskal-Wallis test, as this data was nonparametric in nature. We determined differences between the control group relative to each treatment group using Bonferroni-adjusted Mann-Whitney tests, and evaluated the percentage of mice showing vaginal opening on day 26 (sacrifice) using a two-sample Z test. The analysis compared the control group to each treatment group. Results were considered significant at p [is less than] 0.05. We performed a Pearson's correlation test on the body weight and uterine wet weight data for each treatment group; results were considered significant at p [is less than] 0.01.


There was an overall significant difference between the control group and the experimental treatments (BPA groups and [E.sub.2]) for body weight (p [is less than] 0.05), uterine wet weight (p [is less than] 0.0001), uterine wet weight per body weight (p [is less than] 0.0001), relative area of luminal epithelium (p [is less than] 0.0001), relative area of lamina propria (p [is less than] 0.0001), height of the luminal epithelial cells (p [is less than] 0.0001), and lactoferrin expression (p [is less than] 0.0001). The Pearson's correlation test revealed a significant correlation between body weight and uterine wet weight after exposure to 75 mg/kg BPA and estradiol only (p [is less than] 0.01). There was no significant difference between the control group and experimental treatment groups for the relative area of glandular epithelium and myometrium and PCNA labeling. All data are presented in Tables 1, 2, and 3.
Table 1. Body weight, uterine wet weight (expressed as absolute values
and as a percentage of body weight), and the percentage of mice showing
vaginal opening at sacrifice in immature CD-1 mice implanted for 3 days
with subcutaneous pumps containing DMSO vehicle, BPA, or [E.sub.2].

 Body weight Uterine wet weight
Treatment (mg) (mg)

Control 15.89 [+ or -] 0.38 19.01 [+ or -] 1.16
[E.sub.2] 16.90 [+ or -] 1.06 77.62 [+ or -] 4.97(*)
 (5 [micro]g/kg)
0.1 mg/kg BPA 17.50 [+ or -] 0.72 24.30 [+ or -] 4.11
0.5 mg/kg BPA 17.80 [+ or -] 0.32(*) 20.35 [+ or -] 1.40
1 mg/kg BPA 16.22 [+ or -] 0.35 16.08 [+ or -] 1.84
5 mg/kg BPA 16.32 [+ or -] 0.63 15.54 [+ or -] 1.89
50 mg/kg BPA 15.82 [+ or -] 0.64 19.13 [+ or -] 1.40
75 mg/kg BPA 14.92 [+ or -] 0.50 23.74 [+ or -] 1.94
100 mg/kg BPA 14.39 [+ or -] 0.44(*) 29.08 [+ or -] 2.87(*)

 opening at
 day 26 (%)
 Uterine wet weight
Treatment (per body weight) Complete

Control 0.1195 [+ or -] [0.0064.sup.ab] 27 (13/48)
[E.sub.2] 0.4612 [+ or -] [0.0159.sup.c] 91 (20/22)(*)
 (5 [micro]g/kg)
0.1 mg/kg BPA 0.1374 [+ or -] [0.0020.sup.abd] 100 (5/5)(*)
0.5 mg/kg BPA 0.1143 [+ or -] [0.0078.sup.ab] 55 (6/11)
1 mg/kg BPA 0.0984 [+ or -] [0.0096.sup.ab] 45 (5/11)
5 mg/kg BPA 0.0938 [+ or -] [0.0086.sup.a] 41 (7/17)
50 mg/kg BPA 0.1236 [+ or -] [0.0105.sup.ab] 24 (4/17)
75 mg/kg BPA 0.1580 [+ or -] [] 67 (4/6)
100 mg/kg BPA 0.2013 [+ or -] [0.0169.sup.d] 100 (6/6)(*)

 opening at
 day 26 (%)

 Complete and
Treatment partial

Control 40 (19/48)
[E.sub.2] 95 (21/22)(*)
 (5 [micro]g/kg)
0.1 mg/kg BPA 100 (5/5)(*)
0.5 mg/kg BPA 64 (7/11)
1 mg/kg BPA 45 (5/11)
5 mg/kg BPA 47 (8/17)
50 mg/kg BPA 59 (10/17)
75 mg/kg BPA 67 (4/6)
100 mg/kg BPA 100 (6/6)(*)

Values for each group are expressed as mean [+ or -] SEM. The control
group represents pooled data from the control and vehicle groups. For
uterine wet weight (per body weight), mean values with no superscripts
in common are significantly different (p < 0.05).

(*) Significantly different from the control group (p < 0.05).
Table 2. Morphometric analyses of uterine tissue from immature CD-1
mice implanted for 3 days with subcutaneous pumps containing DMSO
vehicle, BPA, or [E.sub.2].

 Relative area (%)

Treatment Luminal epithelium Glandular epithelium

Control 12.11 [+ or -] [0.78.sup.a] 1.69 [+ or -] [0.17.sup.a]
[E.sub.2] 25.98 [+ or -] [1.09.sup.b] 1.34 [+ or -] [0.19.sup.a]
 (5 [micro]
0.1 mg/kg 11.76 [+ or -] [1.12.sup.a] 2.07 [+ or -] [0.55.sup.a]
0.5 mg/kg 15.07 [+ or -] [1.84.sup.a] 1.33 [+ or -] [0.30.sup.a]
1 mg/kg BPA 11.77 [+ or -] [1.92.sup.a] 1.77 [+ or -] [0.37.sup.a]
5 mg/kg BPA 12.36 [+ or -] [0.88.sup.a] 2.10 [+ or -] [0.33.sup.a]
50 mg/kg BPA 12.93 [+ or -] [0.71.sup.a] 1.30 [+ or -] [0.21.sup.a]
75 mg/kg BPA 12.61 [+ or -] [0.97.sup.a] 1.95 [+ or -] [0.39.sup.a]
100 mg/kg 15.45 [+ or -] [1.27.sup.a] 1.80 [+ or -] [0.40.sup.a]
 Relative area (%)

Treatment Lamina propria Myometrium

Control 48.52 [+ or -] 1.38 36.93 [+ or -] 1.83
[E.sub.2] 40.16 [+ or -] 1.28(*) 33.78 [+ or -] 1.26
 (5 [micro]
0.1 mg/kg 51.83 [+ or -] 3.07 35.50 [+ or -] 3.74
0.5 mg/kg 50.50 [+ or -] 1.10 33.75 [+ or -] 1.78
1 mg/kg BPA 49.69 [+ or -] 0.81 36.78 [+ or -] 2.23
5 mg/kg BPA 42.27 [+ or -] 1.46(*) 43.05 [+ or -] 2.37
50 mg/kg BPA 48.01 [+ or -] 1.56 37.75 [+ or -] 1.65
75 mg/kg BPA 53.00 [+ or -] 0.56 32.44 [+ or -] 0.80
100 mg/kg 49.17 [+ or -] 4.24 34.56 [+ or -] 4.81

Treatment Height of epithelium

Control 14.39 [+ or -] 0.54
[E.sub.2] 26.31 [+ or -] 1.12(*)
 (5 [micro]
0.1 mg/kg 14.56 [+ or -] 1.11
0.5 mg/kg 16.46 [+ or -] 0.92
1 mg/kg BPA 15.83 [+ or -] 0.76
5 mg/kg BPA 16.46 [+ or -] 0.60(*)
50 mg/kg BPA 16.13 [+ or -] 0.47
75 mg/kg BPA 20.43 [+ or -] 0.97(*)
100 mg/kg 23.46 [+ or -] 0.74(*)

Values for each group are expressed as mean [+ or -] SEM. For luminal
epithelium and glandular epithelium, mean values within each column
with no superscripts in common are significantly different (p < 0.05).

(*) Significantly different from the control group (p < 0.05).
Table 3. Labeling of PCNA and lactoferrin within the uterus of the
immature CD-1 mice implanted for 3 days with subcutaneous pumps
containing DMSO vehicle, BPA, or [E.sub.2].

 PCNA labeled Luminal and ferrin
 luminal glandular expre-
Treatment epithelium(a) epithelium(b) ssion(c)

Control 20.75 [+ or -] 3.79 1.62 [+ or -] 0.25 0
[E.sub.2] (5 21.79 [+ or -] 5.34 8.18 [+ or -] 0.99(*) 100
0.1 mg/kg BPA NA NA NA
0.5 mg/kg BPA 22.29 [+ or -] 10.85 1.28 [+ or -] 0.26 0
1 mg/kg BPA 30.64 [+ or -] 7.93 1.79 [+ or -] 1.15 17
5 mg/kg BPA 30.64 [+ or -] 12.57 1.18 [+ or -] 0.47 0
50 mg/kg BPA 20.37 [+ or -] 8.16 2.36 [+ or -] 0.71 33
75 mg/kg BPA NA 7.67 [+ or -] 1.26(*) 100
100 mg/kg BPA NA 8.71 [+ or -] 0.60(*) 100

NA, not available. Values for each group are expressed as mean
[+ or -] SEM.

(a) Number of labeled cells/1,000 [micro]m basement membrane.
(b) Arbitrary units to a maximum of 12. (c) Score > 4 out of a possible
12 (%). (*) Significantly different from the control group (p < 0.05).

Vaginal Opening

The proportion of mice showing vaginal opening (completely open and partially open combined) on day 26 after 3 days exposure to DMSO, BPA, or [E.sub.2] was significantly different between groups (Table 1). Relative to the control group, a greater proportion of mice exposed to 0.1 mg/kg BPA (p [is less than] 0.0001), 100 mg/kg BPA (p [is less than] 0.0001), and [E.sub.2] (p [is less than] 0.0001) showed vaginal opening. Although not statistically significant (p = 0.0512), mice exposed to 75 mg/kg BPA also showed an increased incidence of vaginal opening (completely open and partially opened combined) relative to the control group.

Body Weight

BPA induced a significant increase in body weight at a concentration of 0.5 mg/kg (p [is less than] 0.05) and a significant decrease in body weight at 100 mg/kg (p [is less than] 0.05; Table 1). These represented changes in body weight of 12% and 10%, respectively.

Uterotrophic Assay

The administration of BPA at concentrations of 0.1-75 mg/kg body weight had no effect on the wet weight of the uterus relative to the control group. There was a 53% increase in uterine wet weight in response to 100 mg/kg body weight BPA (p [is less than] 0.05) and a 308% increase in uterine wet weight in response to [E.sub.2] (positive control group; p [is less than] 0.0001) relative to the control group. Wet weight of the uterus, calculated as a percentage of the body weight, showed a similar pattern of change (Table 1, Figure 1).


Uterine Morphology

Luminal epithelium. The relative area of luminal epithelium within the uterus was not affected by BPA at any concentration. [E.sub.2] treatment induced a significant increase in this parameter by 115% relative to the control group (p [is less than] 0.0001) (Table 2, Figure 1).

The uterus exhibited an increase in epithelial cell height in response to BPA at concentrations of 5 (p [is less than] 0.05), 75, and 100 mg/kg (p [is less than] 0.0001), which represents increases of 14, 42, and 63%, respectively. Although not statistically significant (p = 0.056), epithelial cell height also increased in response to 50 mg/kg BPA. Treatment with [E.sub.2] induced an 83% increase (p [is less than] 0.0001) in epithelial cell height relative to the control group (Table 2, Figures 1 and 2).


Glandular epithelium. The relative area of glandular epithelium within the uterus was not affected by treatment with BPA or [E.sub.2] at any concentration compared to the control group (Table 2).

Lamina propria and myometrium. Compared to the control group, the relative area of lamina propria within the uterus was not affected by any concentration of BPA except 5 mg/kg (p [is less than] 0.01); [E.sub.2] also induced a significant decrease in the relative area of lamina propria (p [is less than] 0.01). The relative area of myometrium within the uterus was not affected by treatment with BPA or [E.sub.2] at any concentration (Table 2).


Within the luminal and glandular epithelium of the uterus, BPA induced a significant increase in the expression of lactoferrin by 373% at a concentration of 75 mg/kg (p [is less than] 0.01) and by 438% at a concentration of 100 mg/kg (p [is less than] 0.01) relative to the control group. In some animals, lactoferrin expression was induced at a concentration of 50 mg/kg BPA, although this was not statistically significant (Figure 3). At all lower BPA concentrations, lactoferrin expression was not induced. The expression of lactoferrin was increased by 405% in the [E.sub.2] group (p [is less than] 0.01), whereas the control group showed no response (Table 3, Figure 3).



There was no significant difference in the expression of PCNA in the luminal epithelium between treatment groups (Table 3).


BPA has the capacity to induce proliferative and stimulatory changes in estrogen target tissues that are analogous to those induced by estrogens. These effects have been identified in various strains of rat after exposure to concentrations from 0.3 to 800 mg BPM/kg body weight. The ensuing morphologic changes include proliferation of mammary gland epithelium (23), cell proliferation and cornification of the vagina (14,24), and an increase in the wet weight, epithelial cell height, and mucous secretion of the uterus (14,16). In the present study we have demonstrated that CD-1 mice are also responsive to BPA and that concentrations from 5 to 100 mg/kg body weight can induce a statistically significant increase in the height of luminal epithelial cells; we have also demonstrated that 0.1 mg/kg BPA can induce vaginal opening. Only 100 mg/kg BPA can induce a uterotrophic response. These changes were not accompanied by a change in the relative area of uterus occupied by luminal epithelium, glandular epithelium, lamina propria (except at 5 mg/kg BPA), and muscle, which demonstrates that the relationship between different tissue compartments within the uterus remain the same with BPA treatment. In contrast, the [E.sub.2] group did show a significant increase in both epithelial cell height and relative area of epithelium within the uterus. This demonstrates that the single [E.sub.2] dose used in the study (known to induce a maximal response) has a more profound effect than the BPA doses that were assayed.

Although this study demonstrates that BPA induces changes in the mouse reproductive tract at doses as low as 0.1 mg/kg, it highlights the phenomenon that each end point measured reflects a different dose-response profile. The data for uterine wet weight suggest a U-shaped profile because weight is increased at 0.1 (although not statistically significant) and 100 mg/kg BPA, yet drops between 1 and 5 mg/kg BPA. Similarly, incidence of vaginal opening is significantly increased at 0.1 mg/kg BPA and again at 100 mg/kg BPA. Lactoferrin expression shows a profile in which the middle concentrations of BPA (e.g., 1 mg/kg) increase this variable, whereas doses on either side have absolutely no effect until they reach 75 and 100 mg/kg. These data suggest that exposure to BPA induces a nonmonotonic response in the reproductive parameters measured, a finding that is consistent with other studies in which [E.sub.2] and the potent estrogen diethylstilbestrol (DES) induce an inverted U-shaped dose-response curve for prostate weight (25).

The glycoprotein lactoferrin has been detected in significant amounts in the lactating mammary gland (21,26), uterus, uterine luminal fluid, cervix, vagina, ovary, and oviduct of the mouse (21,27,28). A member of the transferrin family, lactoferrin is thought to provide bacteriocidal protection for gametes (possibly both male and female) in the uterus due to its chelating properties (29,30) and may be implicated in fetal growth and development (31). The expression of lactoferrin in the mouse is under estrogenic control and shows fluctuations in concentration during the estrous cycle (32), and in response to DES in a time- and dose-dependent manner (21,33). As such, lactoferrin is often used as a marker of estrogen action. In the present study we demonstrated that 75 and 100 mg/kg BPA induced a [is greater than] 300% increase in the immunolocalization of lactoferrin in both the luminal and glandular epithelium of the uterus. This increase is of the same magnitude as that induced by [E.sub.2] in the current study and as described in previous work (27), demonstrating the estrogenic nature of BPA in vivo. The difference in the sensitivity of individual mice to BPA, which was particularly evident in the measurement of lactoferrin expression in the 50 mg/kg BPA group, may be a consequence of intrauterine position during development. The intrauterine position has been shown to determine the level of endogenous estrogens to which a developing fetus is exposed on the basis of position relative to either a male or a female (34,35).

The null effect of BPA on the expression of PCNA within the mouse uterus was most likely due to high variation within treatment groups. In retrospect, labeling of bromodeoxy uridine (BrdU) may have provided a more accurate account of cell proliferation because it specifically indicates DNA synthesis, whereas PCNA is also expressed in cells involved in RNA transcription and cell repair (36). PCNA has been shown to increase expression within the mouse uterine epithelium during development (37) and pregnancy (38). In one study Karlsson et al. (39) describe a decrease in PCNA expression in luminal epithelial cells of the rat uterus in response to tamoxifen and toremifene that is concomitant with an increase in the expression of BrdU.

One of the aims of this study was to provide insight into effective doses of BPA in vivo such that subsequent studies on the effects of in utero exposure on development and reproduction could be undertaken. The current study revealed reproductive changes within the immature CD-1 mouse (vaginal opening) following 3 days exposure to BPA at 0.1 mg/kg body weight. Yet recent work in CF-1 mice, a strain also outbred for large litter size, has revealed that in utero exposure to 2.4 [micro]g BPA/kg body weight significantly advances the onset of puberty in females (35). Despite the lack of data on the effects of BPA exposure on female reproductive tract morphology in that study, the comparison with our study demonstrates that caution must be exercised in extrapolating the effective dose for in utero exposure from studies carried out in immature or adult animals.

Earlier estimations of the estrogenic potency of BPA suggested that this chemical was a "weak" estrogen mimic, exhibiting a relative binding affinity to both the ER-[Alpha] and [Beta] approximately 1:2,000 that of 17[Beta]-estradiol (6,40). Because these are in vitro studies, they do not take into account factors such as uptake, transportation, and metabolism of BPA specific to the live animal, which modify the concentration of chemical available to bind the ER or other serum proteins such as albumin, sex hormone-binding globulin, and corticosteroid-binding globulin (12,40-42). BPA binds both human sex steroid-binding protein (0.01%) and trout sex steroid-binding protein (0.1%) with low affinity relative to [[sup.3]H] dihydrotestosterone, and to rat [Alpha]-fetoprotein with negligible affinity (43). The presence of [Alpha]-fetoprotein is particularly important during fetal and neonatal development because it is believed to prevent early exposure of the organism to endogenous estrogens, thus preventing inappropriate sexual differentiation of the brain (44). The pharmacokinetics of BPA most likely acts to increase its effective concentration in circulation, making it more readily available to the ER and thus enhancing its estrogenic activity relative to the protein-bound estradiol.

The uterotrophic assay has been traditionally used to establish the estrogenic activity of sex steroids and suspected environmental estrogens (13,45). Our present study reveals that BPA is able to induce a uterotrophic effect, that is, an increase in wet weight of the uterus, at only the highest concentration used (100 mg/kg body weight). This assay suggests that BPA is not a very potent estrogen mimic in the CD-1 mouse, although at 5 mg/kg body weight, BPA induced a significant increase in the height of luminal epithelial cells. These data demonstrate that the uterotrophic assay is of limited value in determining the estrogenicity of a suspected environmental estrogen because changes at the cellular level were observed at significantly lower doses than those at which a change in wet weight occurred. Moreover, there was a significant effect on vaginal opening at even lower BPA doses (0.1 mg/kg body weight).

In conclusion, this work contributes to the body of evidence showing that BPA acts as an estrogen in vivo by inducing cellular and biochemical changes in the mouse uterus that are consistent with estrogenic activity. Also, BPA was capable of inducing changes in vaginal opening, uterine wet weight, epithelial cell height, and lactoferrin expression in the CD-1 mouse, which establishes that this strain is suitable for investigating the effects of in utero exposure to BPA on development and reproduction. Finally, this work argues against using the mouse uterotrophic assay as an end point for determining estrogenicity of synthetic chemicals, and demonstrates that it is essential to develop alternative, more sensitive in vivo assays.


(1.) Paseiro-Losada P, Simal-Lozano J, Paz-Abuin S, Lopez-Mahia P, Simal-Gandara J. Kinetics of the hydrolysis of bisphenol A diglycidyl ether (BADGE) in water-based food simulants. J Anal Chem 345:527-532 (1993).

(2.) Brotons JA, Olea-Serrano MF, Villalobos M, Olea N. Xenoestrogens released from lacquer coating in food cans. Environ Health Perspect 103:608-612 (1994).

(3.) Olea N, Pulgar R, Perez P, Olea-Serrano F, Rivas A, Novillo-Fertrell A, Pedraza V, Soto AM, Sonnenschein C. Estrogenicity of resin-based composites and sealants used in dentistry. Environ Health Perspect 104:298-305 (1996).

(4.) Biles JE, McNeal TP, Begley TH, Hollifield HC. Determination of bisphenol-A in reusable polycarbonate food-contact plastics and migration to food simulating liquids. J Agric Food Chem 45:3541-3544 (1997).

(5.) Lambert C, Larroque M. Chromatographic analysis of water and wine samples for phenolic compounds released from food-contact epoxy resins. J Chromatogr Sci 35:57-62 (1997).

(6.) Krishnan AV, Starhis P, Permuth SF, Tokes L, Feldman D. Bisphenol-A: an estrogenic substance is released from polycarbonate flasks during autoclaving. Endocrinology 132:2279-2286 (1993).

(7.) Soto AM, Sonnenschein C, Chung KL, Fernandez MF, Olea N, Olea-Serrano F. The E-SCREEN assay as a tool to identify estrogens: an update on estrogenic environmental pollutants. Environ Health Perspect 103(suppl 7):113-122 (1995).

(8.) Steinmetz R, Brown NG, Allen DL, Bigsby RM, Ben-Jonathan N. The environmental estrogen bisphenol A stimulates prolactin release in vitro and in vivo. Endocrinology 138:1780-1786 (1997).

(9.) Gaido KW, Leonard LS, Lovell S, Gould JC, Babai D, Portier CJ. Evaluation of chemicals with endocrine modulating activity in a yeast-based steroid hormone receptor gene transcription assay. Toxicol Appl Pharmacol 143:205-212 (1997).

(10.) Kuiper GG, Carlsson B, Grandien K, Enmark E, Haggblad J, Nilsson S, Gustafsson JA. Comparison of the ligand binding specificity and transcript tissue distribution of estrogen receptors alpha and beta. Endocrinology 138:863-870 (1997).

(11.) Kloas W, Lutz I, Einspanier R. Amphibians as a model to study endocrine disruptors: II. Estrogenic activity of environmental chemicals in vitro and in vivo. Sci Total Environ 225:59-68 (1999).

(12.) Nagel SC, vom Saal FS, Thayer KA, Dhar MG, Boechler M, Welshons WV. Relative binding affinity-serum modified access (RBA-SMA) assay predicts the relative in vivo bioactivity of the xenoestrogens bisphenol A and octylphenol. Environ Health Perspect 105:70-76 (1997).

(13.) Evans JS, Varney RF, Koch FC. The mouse uterine wet weight method for the assay of estrogens. Endocrinology 28:747-752 (1941).

(14.) Steinmetz R, Mitchner NA, Grant A, Allen DL, Bigsby RM, Ben-Jonathan N. The xenoestrogen bisphenol A induces growth, differentiation, and c-fos gene expression in the female reproductive tract. Endocrinology 139:2741-2747 (1998).

(15.) Dodge JA, Glasebrook AL, Magee DE, Phillips DL, Sato M, Short LL, Bryant HU. Environmental estrogens: effects on cholesterol lowering and bone in the ovariectomized rat. J Steroid Biochem Mol Biol 59:155-161 (1996).

(16.) Ashby J, Tinwell H. Uterotropic activity of bisphenol-A in the immature rat Environ Health Perspect 106:719-721 (1998).

(17.) Coldham NG, Dave M, Sivapathasundaram S, McDonnell DP, Connor C, Sauer MJ. Evaluation of a recombinant yeast cell estrogen screening assay. Environ Health Perspect 105:734-742 (1997).

(18.) Spearow JL, Doemeny P, Sara R, Leffler R, Barkley M. Genetic variation in susceptibility to endocrine disruption by estrogen in mice. Science 285:1259-1261 (1999).

(19.) Soto AM, Lin T-M, Justicia H, Silvia RM, Sonnenschein C. An "in culture" bioassay to assess the estrogenicity of xenobiotics. In: Chemically-Induced Alterations in Sexual Development: The Wildlife/Human Connection (Colborn T, Clement C, eds). Princeton, NJ:Princeton Scientific Publishing Co., 1992;295-309.

(20.) Korach KS, Metzler M, McLachlan JA. Estrogenic activity in vivo and in vitro of some diethylstilbestrol metabolites and analogs. Proc Natl Acad Sci USA 75:468-471 (1978).

(21.) Teng CT, Pentecost BT, Chen YH, Newbold RR, Eddy EM, McLachlan JA. Lactotransferrin gene expression in the mouse uterus and mammary gland. Endocrinology 124:992-999 (1989).

(22.) Munoz de Toro MM, Luque EH. Effect of microwave pretreatment on proliferating cell nuclear antigen (PCNA) immunolocalization in paraffin sections. J Histotech 18:11-14 (1995).

(23.) Colerangle JB, Roy D. Profound effects of the weak environmental estrogen-like chemical bisphenol A on the growth of the mammary gland of Noble rats. J Steroid Biochem Mol Biol 60:153-160 (1997).

(24.) Dodds EC, Lawson W. Synthetic estrogenic agents without the phenanthrene nucleus. Nature 137:996 (1936).

(25.) vom Saal FS, Timms BG, Montano MM, Palanza P, Thayer KA, Nagel SC, Ganjam VK, Parmigiani S, Welshons WV. Prostate enlargement in mice due to fetal exposure to low doses of estradiol or diethylstilbestrol and opposite effects at high doses. Proc Natl Acad Sci USA 94:2056-2061 (1997).

(26.) Groves ML. Minor milk proteins and enzymes. In: Milk Proteins: Chemistry and Molecular Biology, Vol 2 (McKenzie HA, ed). New York:Academic Press, 1971;367-418.

(27.) Teng CT, Walker MP, Bhattacharyya SN, Klapper DG, DiAugustine RP, McLachlan JA. Purificaton and properties of an oestrogen-stimulated mouse uterine glycoprotein (approx. 70 kDa). Biochem J 240(2):413-422 (1986).

(28.) Pentecost BT, Teng CT. Lactotransferrin is the major estrogen inducible protein of mouse uterine secretions. J Biol Chem 262:10134-10139 (1987).

(29.) Arnold RR, Cole MF, McGhee JR. A bactericidal effect for human lactoferrin. Science 197(4300):263-285 (1977).

(30.) Aisen P, Listowsky I. Iron transport and storage proteins. Annu Rev Biochem 49:357-393 (1980).

(31.) Buhi WC, Ducsay CA, Bazer FW, Roberts RM. Iron transfer between the phosphatase uteroferrin and transferrin and its possible role in iron metabolism of the fetal pig. J Biol Chem 257:1712-1723 (1982).

(32.) Newbold RR, Teng CT, Beckman WC, Jefferson WN, Hanson RB, Miller JV, McLachlan JA. Fluctuations of lactoferrin protein and messenger ribonucleic acid in the reproductive tract of the mouse during the estrous cycle. Biol Reprod 47:903-915 (1992).

(33.) Newbold RR, Hanson RB, Jefferson WN. Ontogeny of lactoferrin in the developing mouse uterus: a marker of early hormone response. Biol Reprod 56:1147-1157 (1997).

(34.) Nonneman DJ, Ganjam VK, Welshons WV, vom Saal FS. Intrauterine position effects on steroid metabolism and steroid receptors of reproductive organs in male mice. Biol Reprod 47:723-729 (1992).

(35.) Howdeshell KL, Hotchkiss AK, Thayer KA, Vandenbergh JG, vom Saal FS. Environmentally relevant prenatal exposure to bisphenol A accelerates puberty in CF-1 mice. Nature 401(6755):763-764 (2000).

(36.) Kelman Z. PCNA: structure, functions and interactions. Oncogene 14:629-640 (1997).

(37.) Li S. Relationship between cellular DNA synthesis, PCNA expression and sex steroid hormone receptor status in the developing mouse ovary, uterus and oviduct. Histochemistry 102:405-413 (1994).

(38.) Ogle TF, George P, Dai D. Progesterone and estrogen regulation of rat decidual cell expression of proliferating cell nuclear antigen. Biol Reprod 59:444-450 (1998).

(39.) Karlsson S, Iatropoulos MJ, Williams GM, Kangas L, Nieminen L. The proliferation in uterine compartments of intact rats of two different strains exposed to high doses of tamoxifen or toremifene. Toxicol Pathol 26(6):759-768 (1998).

(40.) Kuiper GGJM, Lemmen JG, Carlsson B, Corton JC, Safe SH, Van Der Saag PT, van der Burg B, Gustafsson J. Interaction of estrogenic chemicals and phytoestrogens with estrogen receptor beta. Endocrinology 139:4252-4263 (1998).

(41.) Damassa DA, Lin TM, Sonnenschein C, Soto AM. Biological effects of sex hormone-binding globulin on androgen-induced proliferation and androgen metabolism in LNCaP prostate cells. Endocrinology 129:75-84 (1991).

(42.) Hammond GL. Potential functions of plasma steriod-binding proteins. Trends Endocrinol Metab 6:298-304 (1995).

(43.) Milligan SR, Khan O, Nash M. Competitive binding of xenobiotic oestrogens of rat alpha-fetoprotein and to sex steroid binding proteins in human and rainbow trout (Oncorhynchus mykiss) plasma. Gen Comp Endocrinol 112:89-95 (1998).

(44.) Dohler KD, Jarzab B. The influence of hormones and hormone antagonists on sexual differentiation of the brain. In: Chemically-Induced Alterations in Sexual and Functional Development: The Wildlife/Human Connection. (Colborn T, Clement C, eds). Princeton, NJ:Princeton Scientific Publishing Co., 1992;231-259.

(45.) Gellert RJ, Lewis J, Petra PH. Neonatal treatment with sex steroids: relationship between the uterotropic response and the estrogen "receptor" in prepubertal rats. Endocrinology 100(2):520-528 (1977).

Caroline M. Markey, Cheryl L. Michaelson, Electra C. Veson, Carlos Sonnenschein, and Ana M. Soto

Department of Anatomy and Cellular Biology, Tuffs University School of Medicine, Boston, Massachusetts, USA

Address correspondence to A. Soto, Department of Anatomy and Cellular Biology, Tufts University School of Medicine, Boston, Massachusetts 02111-1800 USA. Telephone: (617) 636-6954. Fax: (617) 636-6536.

We thank P. Kwan for technical advice on immunohistochemistry and D. Damassa for invaluable advice on the statistical analysis of data.

This work was supported by NIH-ES grant 08314

Received 2 May 2000; accepted 19 September 2000.
COPYRIGHT 2001 National Institute of Environmental Health Sciences
No portion of this article can be reproduced without the express written permission from the copyright holder.
Copyright 2001, Gale Group. All rights reserved. Gale Group is a Thomson Corporation Company.

Article Details
Printer friendly Cite/link Email Feedback
Author:Soto, Ana M.
Publication:Environmental Health Perspectives
Date:Jan 1, 2001
Previous Article:Spatial and Temporal Distribution of Airborne Bacillus thuringiensis var. kurstaki during an Aerial Spray Program for Gypsy Moth Eradication.
Next Article:Evaluation of Fish Models of Soluble Epoxide Hydrolase Inhibition.

Related Articles
Immature Rat Uterotrophic Assay of Bisphenol A.
"In vitro and in vivo estrogenicity of UV screens": response. (Correspondence).
Confirmation of uterotrophic activity for 4-MBC in the immature rat. (Correspondence).
Increasing the sensitivity of the rodent uterotrophic assay to estrogens, with particular reference to Bisphenol A. (Commentary).
Predictive value of the uterotrophic assay for genistein carcinogenicity in the neonatal mouse: relevance to infants consuming soy-based formula....
The mouse uterotrophic assay: other end points. (Correspondence).
The rodent uterotrophic assay: response to Ashby and Newbold et al. (Correspondence).
A critical review of methods for comparing estrogenic activity of endogenous and exogenous chemicals in human milk and infant formula. (Research...
The intact immature rodent uterotrophic bioassay: possible effects on assay sensitivity of vomeronasal signals from male rodents and strain...
In vivo imaging of activated estrogen receptors in utero by estrogens and bisphenol A.

Terms of use | Privacy policy | Copyright © 2021 Farlex, Inc. | Feedback | For webmasters