epigenetic project5
TRANSCRIPT
Prenatal Bisphenol A (BPA) exposure on epigenetic changes in
fetal mouse tissues
Alice DouglasBartolomei Lab
STEER Summer 2016
The DOHaD Hypothesis: • Developmental Origins of Health and Disease-
– focuses on fetal origins of adult disorders that are influenced by the interaction of genetic background and environmental exposures such as nutrition, stress, pharmaceuticals and toxins
TIME Magazine 2010 Xin et al 2015
F1
Environmental Exposures and Health
Disease
Drugs
Diet
ExerciseStress
Chemicals
Bisphenol A (BPA)
www.ansci.wisc.edu
Where is it found?
www.wordpress.vermontlaw.edu
BPA as an endocrine disruptor
• Estrogen mimic
• Proposed modes of action– Genomic– Non-genomic
• Inappropriately activates or inhibits a cellular response
NIEHS
(Estrogen)
(BPA)
(ER)
What is the Mechanism?
Epigenetic Changes
DrugsDiet
ChemicalsExercise
Stress
Disease
Gene Expression
Epigenetics
• epi-from the Greek, “upon,” “on,” or “above” • chemical and structural modifications on DNA
that may impact gene expression– Example: DNA methylation
http://www.delawareneuroscience.org/Pages/Roth.htm
Previous Work in the Bartolomei Lab:
Metabolic changes in adulthood:• F1 males: fatter, glucose intolerant• F1 females: not affected
Behavior changes in adulthood:• F1 males: depressed-like state • F1 females: not tested
Susiarjo et al (2015) EndocrinologyUnpublished
Objective:
• Physiological changes in adult animals prompted search for molecular changes in relevant tissues during early development
BPA Exposure
DNA Methylation Changesin Liver and Brain?
Metabolic and Behavior Phenotype
Prenatal Exposure Paradigm
Xin et al 2015
www.ansci.wisc.edu
www.nzrr.org
Lower BPA- 50 μg/kg in feed (estimated 10 μg per kg body weight per day) Upper BPA-50 mg/kg in feed (estimated 10 mg per kg body weight per day)
Strengths of Experimental Set Up:
• Dosage• Route of exposure• Window of exposure
Dissection (F1, E12.5-13.5 and E17.5-18.5) Fetal liver, brain and placenta
RNA extraction
RFLP-allele specific PCR
DNA extraction
LUMA
SMC PCR (n=183)
LUMA
• Luminometric Assay (LUMA)-global DNA methylation– Restriction Enzymes: • MSPI: methylation insensitive • HPAII: methylation sensitive• Ratio of HPAII to MSPI gives % Methylation
www.epigenome.dept.showa.gunma-u.ac.jp
Comparing Liver and Brain: Mid-gestation Female
Control n=6(3) Lower Dose n=10(4) Upper Dose n=12(5)Average= 57.16% Average= 59.92% Average= 49.85%
Control n=6(4) Lower Dose n=6(2) Upper Dose n=7(4) Average= 68.49% Average= 69.62% Average= 68.37%
% M Liver
% M Brain
Each diamond=one embryoEach color=one litter
n.s.n.s.
n.s.n.s.
Statistical Test: t-test
Comparing Liver and Brain: Mid-gestation Male
Control n=7(4) Lower Dose n=12(4) Upper Dose n=17(6)Average= 50.96% Average= 60.01% Average= 59.08%
Control n=4(2) Lower Dose n=8(3) Upper Dose n=5(4) Average= 72.67% Average= 70.14% Average= 72.45%
% M Liver
% M Brain
n.s.n.s.
n.s.n.s.
Comparing Liver and Brain: Term Female
% M Brain% M Liver
Control n=11(3) Lower Dose n=13(3) Upper Dose n=3(2) Average= 59.04% Average= 53.12% Average= 54.92%
Control n=5(2) Lower Dose n=7(3) Upper Dose n=3(2) Average= 70.407% Average= 68.04% Average= 72.50%
n.s.
p < 0.05
n.s.n.s.
Comparing Liver and Brain: Term Male% M Liver % M Brain
Control n=6(3) Lower Dose n=12(4 Upper Dose n=8(2) Average= 61.31% Average= 57.39% Average= 51.75%
Control n=4(2) Lower Dose n=8(3) Upper Dose n=3(1) Average= 70.77 % Average= 67.70% Average= 71.27%
p < 0.05n.s.
n.s.n.s.
Conclusions:
• Tissue, sex, dose and age specific changes in response to BPA exposure– Female term liver DNA methylation is significantly
reduced in the lower dose exposure group– Male term liver DNA methylation is significantly
reduced in upper dose exposure group
BPA Exposure
Metabolic and Behavior Phenotype
DNA Methylation Changes
Is this causal?
Future Directions of Research:
• Adult tissue • Other compounds– combining compounds for more realistic multi-compound exposures
• Site specific DNA methylation and total expression changes – Dnmt expression level changes– Expression of Liver and Brain function genes
Acknowledgements:• The STEER Program: – Dr. Jeff Field– Dr. Maria Antonia-Andrews– Dr. Rich Pepino– Dr. Marilyn Howarth
• Dr. Marisa Bartolomei– Frances Xin– Erin Fischer– Jen Myers– Martha Stefaniak– The rest of the Bartolomei lab!
Works Cited:• DeBenedictis B, Guan H, Yang K. Prenatal Exposure to Bisphenol A Disrupts Mouse Fetal Liver
Maturation in a Sex-Specific Manner. Journal of Cellular Biochemistry 2015; 117:344-50.• Calafat AM, Kuklenyik Z, Reidy JA, Caudill SP, Ekong J, Needham LL. Urinary concentrations of
bisphenol A and 4-nonylphenol in a human reference population. Environmetnal Health Perspectives 2005;113:391–5.
• Gioiosa L, Palanza P, Parmigiani S, Vom Saal FS. Risk Evaluation of Endocrine-Disrupting Chemicals: Effects of Developmental Exposure to Low Doses of Bisphenol A on Behavior and Physiology in Mice (Mus musculus). Dose-Response 2015; 13:1-8.
• Hijazi A, Guan H, Cernea M, Yang K. Prenatal exposure to bisphenol A disrupts mouse fetal lung development. Faseb Journal 2015; 29:4968-77.
• Susiarjo M, Xin F, Bansal A, Stefaniak M, Li C, Simmons RA, Bartolomei MS. Bisphenol A Exposure Disrupts Metabolic Health Across Multiple Generations in the Mouse. Endocrinology 2015; 156:2049-58.
• Susiarjo M, Sasson I, Mesaros C, Bartolomei MS. Bisphenol A Exposure Disrupts Genomic Imprinting in the Mouse. PLOS Genetics 2013; 9:1-18.
• Whitehead R, Guan H, Arany E, Cernea M, Yang K. Prenatal exposure to bisphenol A alters mouse fetal pancreatic morphology and islet composition. Hormone Molecular Biology and Clinical Investigation 2016; 25:171-9.
• Xin F, Susiarjo M, Bartolomei MS. Multigenerational and transgenerational effects of endocrine disrupting chemicals: A role for altered epigenetic regulation? Seminars in Cell & Developmental Biology 2015; 43:66-75.
Questions?
Thanks!