This work is licensed under a . Your use of this

This work is licensed under a Creative Commons Attribution-NonCommercial-ShareAlike License. Your use of this
material constitutes acceptance of that license and the conditions of use of materials on this site.
Copyright 2015, The Johns Hopkins University and Michael Trush. All rights reserved. Use of these materials
permitted only in accordance with license rights granted. Materials provided “AS IS”; no representations or
warranties provided. User assumes all responsibility for use, and all liability related thereto, and must independently
review all materials for accuracy and efficacy. May contain materials owned by others. User is responsible for
obtaining permissions for use from third parties as needed.
1
Section E
DES and BPA
The material in this video is subject to the copyright of the owners of the material and is being provided for educational purposes under
rules of fair use for registered students in this course only. No additional copies of the copyrighted work may be made or distributed.
Endocrine Active Chemicals: Natural and Synthetic
3
Diethylstilbesterol (DES)
! Clinical use and adverse human health effects
! Initial use: prevention of spontaneous abortion
! desPlex was promoted as agent that would enhance
health of babies
! Adverse effect
• Appearance of clear cell adenocarcinoma of the
vagina and cervix in exposed offspring of mothers
treated during pregnancy
! An initial small case-control study published by Herbst et
al. in 1971
This image
can not be
provided due
to copyright
DES ad from 1957
4
DES Case-Control
Study: Summary
of Data
Comparing
Patients with
Matched Controls
Source: Herbst et al. (1971). New Eng. J. Med.,
284, 878-881.
5
DES: Incidence by
Age of Clear Cell
Adenocarcinoma
at Diagnosis
among NativeBorn White
Resident Female
Subjects
This image can not be provided due
to copyright
6
DES: Effects of in Utero Exposure on Human Female Progeny
! Clear cell adenocarcinoma (malignant)
in young women
! 1.4/1,000–10,000
! Reproductive problems: 18%
! Structural abnormalities of the
cervicovaginal area
! Structural abnormalities of uterus
! Menstrual irregularities
! Possible adverse pregnancy
outcomes
! Spontaneous abortions, ectopic
pregnancies, and premature
delivery
! Possible increased risk for breast
cancer (recent)
! Possible transgenerational effects
(recent)
! http://www.cancer.gov/cancertopics/
factsheet/Risk/DES
7
DES: Effects of in Utero Exposure on Human Male Progeny
! Three times normal incidence
! Anatomic abnormalities of the reproductive tract
! Altered semen—including decreased sperm density, count, and motility
• But DES sons do not appear to be at increased risk for infertility (http://
www.cdc.gov/des/consumers/about/effects_sons.html)
! No apparent increased risk for neoplasms of the reproductive tract
8
How Does DES Work?
! DES is metabolized to reactive quinone metabolites
! Toxicity
! DNA damage
mutation
! DES is a potent estrogen
! Effects of estrogens are mediated through estrogen receptors (ER)
! DES alters gene expression
! Epigenetic changes that are transgenerational
• Altered DNA methylation (Science, 308, 1466, 2005)
9
DES Metabolism
HO
O
OH
O
P450-mediated
Diethylstilbestrol
DES quinone very reactive
Species differences
Tissue differences
10
! Two core
estrogen
receptors
! ERα
! ERβ:
expressed in
human fetal
tissues
! ERs control
cellular
response to
estrogens
Estrogen concentration
Binding to Estrogen Receptors
Critical period for
in utero exposure
to DES
Critical period
1
2
3
Pregnancy (trimester)
11
ERα- and ERβMediated Effects
Image source: Yager and Davidson. (2006). N Engl J
Med, 354:270–82.
12
Bisphenol A (BPA)
This image can not be provided due
to copyright
13
BPA Serum Concentrations
! Range of human exposure (US FDA,
2009)—from Rhomberg et al.,
Regulatory Toxicology and
Pharmacology, in press
! Mean dietary intake from foodcontact articles
! Children and adults: 0.1–0.2µg/kg-d
! Infants: 0.2–0.4µg/kg-d
! Human serum levels: 2–3ng/ml range
! FDA 2012 statement: baby bottles and
children’s drinking cups can no longer
contain BPA
! RfD (fact sheet on BPA)
! Oral = 20–50mg/kg-day (20–50ppb)
! Water = 100mg/l (100ppb)—one
teaspoon in an average 16,000gallon residential in-ground
swimming pool
14
Estrogen Receptors
! Two core estrogen receptors:
1. ERα
2. ERβ
! BPA binding to ERα is extremely weak: 1/1000–1/10,000 affinity compared to E2
! Estrogen receptor related receptor γ (ERRγ)
! Member of the ER gene family
! Function and natural ligand—unknown
! Does have tissue-specific expression
• Brain during development
• Brain, lung, many other tissues in adults
! BPA has a strong binding affinity for ERRγ
15
Mechanisms of BPA Effects: BPA Causes Epigenetic Changes
! Yellow:
agouti gene,
unmethylated
! Pseudoagouti:
agouti gene,
methylated
Source: Dolinoy et al. (2007). PNAS.
This image can
not be provided
due to copyright
16
Dietary Modification of BPA-Induced Methylation Pattern
Source: Dolinoy et al. (2007). PNAS.
17
BPA Effects on Mammary Gland Development in Rhesus Monkeys
This image can not be provided due
to copyright
18
Effects of BPA on
Follicle
Development in
Rhesus Monkeys
This image can not be provided due
to copyright
19