Optimizing a human relevant mouse model to study adverse health effects of PFAS
Project Number5R21ES035475-02
Former Number1R21ES035475-01
Contact PI/Project LeaderSCHLEZINGER, JENNIFER J
Awardee OrganizationBOSTON UNIVERSITY MEDICAL CAMPUS
Description
Abstract Text
PROJECT SUMMARY
Millions of Americans are exposed daily to per- and polyfluoroalkyl substances (PFAS) due to the current and
historical use of these chemicals in consumer and industrial products. PFAS exposure in humans is associated
with liver disease and serum hyperlipidemia (increased serum cholesterol, in particular). However, understanding
the mechanism(s) linking PFAS exposure to dyslipidemia is hindered by 1) the ability of PFAS to activate
peroxisome proliferator activated receptor α (PPARα), a receptor activated by fibrate drugs that reduces serum
triacylglycerides, 2) apparently disparate effects of PFAS on serum lipids in human and rodents (in which PFAS
can decrease serum lipids), 3) lack of understanding if/how PFAS congeners exert distinct effects on lipid
homeostasis, and 4) species differences in nuclear receptors that regulate PFAS-induced effects. Our
overarching objective is to determine the mechanisms by which PFAS disrupt systemic lipid homeostasis. Our
research focuses on nuclear receptors that are activated by PFAS and are directly involved in lipid regulation:
PPARα, constitutive androstane receptor (CAR), and pregnane X receptor (PXR). PPARα activation decreases
hepatic and serum lipids while CAR and PXR activation can have the opposite effect. There are two major
chemical classes of PFAS: perfluoroalkyl carboxylic acids (PFCA) and perfluoroalkyl sulfonic acids (PFSA). We
used a human-relevant model in vitro to show that PFCA and PFSA activate human PPARα (huPPARα) with
differing efficacies. Using mice expressing huPPARα and fed an American diet, we showed that: 1)
perfluorooctanoic acid (PFOA) activates hepatic huPPARα in vivo at body burdens found in humans, 2) CAR
and PXR also are strongly activated, 3) PFOA increases liver lipids and serum cholesterol, and 4) PFOA’s effects
are sex-dependent. Given the strength of the PFAS-induced CAR/PXR signal, the potential for CAR/PXR to
differentiate the effects of PFCAs and PFSAs, and that CAR/PXR also are activated in a species-specific manner,
we propose that the most human relevant in vivo model should be multi-humanized. Thus, our Specific Aims are
as follows. In Aim 1, we will refine our novel mouse model to investigate human relevant mechanisms of PFAS
action by incorporating human CAR (huCAR) and PXR (huPXR) into the huPPARα mouse and update our novel
“What we eat in America” diet. In Aim 2, we will test the contribution of huPPARα to PFAS-induced toxicological
effects in vivo in the context of huCAR and huPXR by comparing effects in huPPARα+:huCAR+:huPXR+ and
PPARαNull(mouse/human):huCAR+:huPXR+ mice exposed to human-relevant PFAS levels. We will test the hypotheses
that a) activation of PPARα by PFAS limits their capacity to stimulate hepatic steatosis and serum hyperlipidemia
by counteracting effects of CAR/PXR activation and b) PFAS structure will determine the balance of
huPPARα:huCAR/huPXR activation resulting in differences in toxicological effects. Results will fill critical gaps
by generating an in vivo, human-relevant model to investigate PFAS-induced, clinically-relevant disease and
providing novel insights into the mechanisms of action of PFAS in liver and intestine.
Public Health Relevance Statement
PROJECT NARRATIVE
Americans are exposed daily to per- and polyfluoroalkyl substances (PFAS) in their drinking water, food and
air. PFAS cause adverse birth outcomes, suppress vaccine responses, and induce metabolic disease in
people, although how this happens is unknown. We propose to determine how PFAS cause adverse health
effects, focusing on metabolic disease in humans, by developing tools that focus on essential molecular
regulators of lipids, the nuclear receptors PPARα, CAR and PXR.
National Institute of Environmental Health Sciences
CFDA Code
113
DUNS Number
604483045
UEI
FBYMGMHW4X95
Project Start Date
04-March-2024
Project End Date
28-February-2026
Budget Start Date
01-March-2025
Budget End Date
28-February-2026
Project Funding Information for 2025
Total Funding
$255,660
Direct Costs
$157,699
Indirect Costs
$97,961
Year
Funding IC
FY Total Cost by IC
2025
National Institute of Environmental Health Sciences
$255,660
Year
Funding IC
FY Total Cost by IC
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