Young EDC Scientists Showcase Seminar July 1, 2020
Impacts of Chemical Mixtures Isolated from Household Dust on - - PowerPoint PPT Presentation
Impacts of Chemical Mixtures Isolated from Household Dust on - - PowerPoint PPT Presentation
Impacts of Chemical Mixtures Isolated from Household Dust on Metabolic Health Chris Kassotis, PhD Postdoctoral Fellow Duke University @cdkassotis Young EDC Scientists Showcase Seminar July 1, 2020 Prevalence and Consequences of
Prevalence and Consequences of Obesity Epidemic in US, Globally
Ø Currently ~40% of US adult
population is obese.
Ø ~9% infants/toddlers Ø ~19% of 2-19 year-olds
Ø >$265B in US health care costs on
- besity related illnesses (2015)
Ø ~8% of total US health care costs
(>12% in NC, OH, WI; 2018)
Ø Increased comorbidities
Ø T2D, CVD, hypertension
Ø Interventions have produced only
modest effects
Potential Role of Chemicals in Increasing Obesity Rates in Humans
Ø First posited in 2002, despite
decades of experimental evidence.
Ø Challenges caloric intake,
activity, genetics as sufficient factors to explain magnitude/speed of observed trend.
Ø Summarizes wealth of animal
evidence on antibiotics, PCBs, plastics, pharmaceuticals, pesticides, organophosphates, heavy metals, etc.
Baillie-Hamilton et al. 2002, J Alt Comp Med
Potential Mechanisms of Metabolic Dysfunction
Ø Numerous potential mechanisms
- f metabolic disruption:
Ø Adipocyte commitment from
MSCs
Ø Adipocyte differentiation from
precursor cells
Ø
Increased pre-adipocyte proliferation
Ø
Increased lipid uptake Ø Shifting energy balance to
favor calorie storage
Ø Altering basal metabolic rate Ø Altering hormonal control of
appetite and satiety
Ø Altering brain circuitry that
controls food intake, energy expenditure
Heindel et al. 2017, Repro Tox
Adipocyte Differentiation Process
Nagy et al. 2011, Mol Med
Other pathways: Myoblasts Osteoblasts Chondroblasts Resemble brown/developing white adipose cell Resemble mature white adipose cell
Adipocyte commitment Adipocyte differentiation
3T3-L1 Pre-adipocyte Adipogenesis Assay
Ø Swiss albino mouse embryonic fibroblast cell line – committed
pre-adipocytes
Ø Extensively used over decades to evaluate adipogenesis
Ø
Mechanisms of adipocyte differentiation well understood
Ø
This assay, particularly coupled with PPARγ reporter gene assays, has proven a reliable in vitro model for metabolic disruption in vivo.
Differentiation cocktail: 5% NCS -> FBS, 1 µg/mL insulin, 800 mM IBMX
Adipogenesis Assay Measures
§
Triglyceride accumulation
§
AdipoRed - hydrophilic fluorescent dye (Nile Red)
§
Partitions into lipid droplets in the cells, fluoresces
§
Cell proliferation/cytotoxicity
§
NucBlue DNA dye (Hoechst 33342)
§
Partitions into nuclei and fluoresces upon binding DNA
Cancer in the Environment (CIE) Cohort
Ø N=137 adult participants recruited from
central NC.
Ø Demographic, lifestyle, and environment
information collected via questionnaire.
Ø Clinical data abstracted from medical records. Ø Visited participants’ homes and collected dust
samples as a measure of long-term exposure.
Ø ~200 mg dust sieved to <500 μm, solvent extracted
in 50:50 DCM:hexane, concentrated under N2 gas.
Ø Half of extract evaporated and reconstituted in
DMSO for bioassays, half purified further for mass spec analysis.
photo credit: Jared Lazarus Duke Photography
Chemical Exposure Markers: Indoor House Dust
Ø Household dust is a well-described reservoir for
chemicals leaching from consumer products and materials in home.
Ø Hundreds of contaminants have been measured
in dust globally – a complex environmental mixture
Ø Previous research has measured endocrine
bioactivities for various receptors by household dust extracts
Ø Residents chronically exposed to chemicals
present in dust via oral, dermal, and inhalation exposure routes.
Ø Research has demonstrated strong positive
correlations between chemicals in dust and internal chemical/metabolite concentrations in serum/urine.
Majority of Dust Extracts Promote Adipocyte Development at Low Concentrations (<1 mg)
Ø Majority of dust extracts promoted significant adipogenic activity
(~90%).
Ø >60% exhibited significant triglyceride accumulation Ø >70% exhibited significant pre-adipocyte proliferation
Kassotis et al. 2019, STOTEN
Rosiglitazone (10 uM) DMSO control Dust extract A 200 ug/well Dust extract B 110 ug/well
Adipogenesis Endpoints Shared and Distinct Across Dust Extracts
1000 1 10 100 1000 30 60 90 120 Dust Extract Quantity (µg/well) DNA Content Relative to Vehicle (%)
Dust-Induced Proliferation / Cytotoxicity
1000 10 100 1000
- 60
- 30
30 60 Dust Extract Quantity (µg/well) % DNA Content Relative to Vehicle
Dust-Induced Proliferation / Cytotoxicity
1000
ell
0.1 1 10 100 1000 10 20 30 40 50 60 Dust Extract Quantity (µg/well) DNA Content Relative to Vehicle (%)
Dust-Induced Proliferation / Cytotoxicity
High triglyceride accumulation High pre-adipocyte proliferation High triglyceride accumulation Minimal pre-adipocyte proliferation Minimal triglyceride accumulation High pre-adipocyte proliferation Kassotis et al. 2019, STOTEN
1 10 100 1000 50 100 150 200 250 Dust Extract Quantity (µg/well) Triglyceride Accumulation Per Cell (%)
Dust-Induced Triglyceride Accumulation per Cell
1000 1 10 100 1000 30 60 90 120 150 Dust Extract Quantity (µg/well) Triglyceride Accumulation Per Cell (%)
Dust-Induced Triglyceride Accumulation per Cell
1000 0.1 1 10 100 1000 10 20 30 40 50 Dust Extract Quantity (µg/well) Triglyceride Accumulation Per Cell (%)
Dust-Induced Triglyceride Accumulation per Cell
BFR and PFR Flame Retardants Associated with Increased Triglyceride Accumulation
Correlation Coefficients BFRs/PFRs Triglyceride Accumulation Pre-adipocyte Proliferation
BDE-47 0.244**
- 0.096
BDE-99 0.294**
- 0.124
BDE-100 0.339**
- 0.043
BDE-153 0.385**
- 0.049
BDE-154 0.394**
- 0.073
BDE-209 0.462** 0.060 TBB 0.324** 0.006 TBPH 0.341** 0.025 TCEP 0.343**
- 0.013
TDCIPP 0.397**
- 0.099
TCIPP 0.290**
- 0.041
TPHP 0.199*
- 0.011
Kassotis et al. 2019, STOTEN Spearman’s correlations: * p<0.05; ** p<0.01
Regression Analyses of Health Outcomes and House Dust Extract Bioactivities
Ø Thyroid stimulating hormone in adult
residents positively correlated with adipogenic activity of their house dust (normalized by concentration); free triiodothyronine (T3) and thyroxine (T4) negatively correlated.
Ø TRβ antagonism promoting
adipogenesis a likely factor in the TH suppression
Ø Performed regressions controlling
for sex, age, race, and education as potential confounders.
Ø Triglyceride accumulation efficacy
was significantly associated with resident BMI.
Kassotis et al. 2019, STOTEN
Putative Role of Thyroid Receptor β Antagonism in Adipogenic Activity
Ø GR (dexamethasone) and PPARγ
(rosiglitazone) are potent and efficacious regulators of adipogenesis.
Ø 1-850 (non-specific TRβ isoform antagonist)
also significantly promotes adipocyte differentiation.
Kassotis et al. 2017, Sci Rep
20 40 60 80 50 100 150 200 350 400
TRβ Antagonism (% Inhibition of EC80 T3) Triglyceride Accumulation Per Cell (%) TRβ Antagonism and 3T3-L1 Dust-Induced Triglycerides
rs = 0.447 p < 0.0001
Ø Triglyceride accumulation (3T3-L1
cells) significantly correlated with TRβ antagonism in dust extracts.
Ø
Not correlated with pre-adipocyte proliferation
Kassotis et al. 2019, STOTEN
Contributory Role of TRβ Antagonism in Adipogenic Activity
Ø Two experiments bolster causative
link between TRβ and triglyceride accumulation in 3T3-L1 cells:
Ø Ligand recovery experiment. Dust +
T3 (TR agonist):
Ø
Addition of T3 inhibited dust- induced triglyceride accumulation for 7 of 9 samples. Ø siRNA knock-down of TRa/β:
Ø
TR knock-down inhibited dust- induced triglyceride accumulation for 7 of 9 samples (two trending).
CE095 CE143 CE134 CE124 CE151 CE152 CE114 CE117 CE133 50 100 150 200 250
Dust Sample % Triglycerides to Dust Control
Dust-Induced Triglycerides - TR siRNA Knock-Down
* **
#
*
#
*
# Each grouping: Dust alone, Dust+Negative Control siRNA, Dust+TRα/β siRNA CE095 CE114 CE117 CE143 CE133 CE134 CE124 CE151 CE152 25 50 75 100 125 150 Dust Sample Triglyceride Accumulation Per Cell (%)
Low-Dose Dust-Induced Triglycerides - T3 Recovery
** ** * ** ** **
#
*
Kassotis et al. 2019, STOTEN
Ethoxylated Surfactants are Common Environmental Contaminants
Ø
High-production volume chemicals
Ø
>13 million metric tons, 2008
Ø
>$33 billion global revenues, 2014
Ø
Used widely in laundry detergents, hard- surface cleaners, paints, cosmetics, agriculture.
Ø
Common environmental contaminants
Ø
Widely reported at μg/L conc. in water column (wastewater)
Ø
Detected with high frequency in indoor house dust samples
Ø
Tested the ability of various ethoxylated surfactants to promote adipogenesis
Ø
6 APEO/AEO surfactants with varying alkyl chain lengths (carbon backbones C11-16)
Ø
Select NPEOs with varying average ethoxylate chain lengths (2, 4, 6, 10, 20)
Alkyl chain length Ethoxylate chain length
Various Alkyl Chain Length Surfactants Induce Adipogenesis to Varying Degrees
- 4
- 10
- 9
- 8
- 7
- 6
- 5
- 4
50 100 150 200
Concentration (M) Triglyceride Accumulation Per Cell (%)
Triglyceride Accumulation per Cell
* * ** * *
C E
ylated Surfactants
Kassotis et al. 2019, Tox Sci
- 4
Cetyl alcohol ethoxylate Nonylphenol ethoxylate (4) Octylphenol ethoxlate (3) Lauryl alcohol ethoxylate Tomadol 1-9 Tridecyl alcohol ethoxylate
Ø Six ethoxylated surfactants (alkyl lengths 11-16) all induced triglyceride
accumulation in 3T3-L1 cells.
Ø
Cetyl alcohol and NPEO induced greater maximal accumulation than the rosiglitazone control.
Ø 4/6 surfactants induced pre-adipocyte proliferation.
- 9
- 8
- 7
- 6
- 5
- 4
- 50
50 100 150 200
Concentration (M) DNA Content Relative to Vehicle (%)
Cell Proliferation/Cytotoxicity
* * * *
B C E
yl Length Ethoxylated
(C11) (C12) (C13) (C14) (C15) (C16) (C15) (C16) (C15) (C16)
Nonylphenol Ethoxylates Induce Chain- Length Dependent Adipogenic Effects
- 4
- 10
- 9
- 8
- 7
- 6
- 5
- 4
25 50 75 100 125 150
Concentration (M) Triglyceride Accumulation Per Cell (%)
Triglyceride Accumulation per Cell
* * * ** *
C E
Kassotis et al. 2019, Tox Sci
Ø NPEOs induced varied adipogenic responses. Ø Maximal response for medium-length (4/6) ethoxylate chains;
decreasing activity with decreasing or increasing chain number.
Ø
Activity for NPEO(20) indistinguishable from base (0).
- 4
Nonylphenol ethoxylate (0) Nonylphenol ethoxylate (1-2) Nonylphenol ethoxylate (4) Nonylphenol ethoxylate (6) Nonylphenol ethoxylate (9-10) Nonylphenol ethoxylate (20) ll
- 9
- 8
- 7
- 6
- 5
- 4
- 50
50 100 150 200
Concentration (M) DNA Content Relative to Vehicle (%)
Cell Proliferation/Cytotoxicity
* * * * *
B C E
5 10 15 20 25 50 100 150
Ethoxylate Chain Length & Adipogenicity
Ethoxylate Chain Length (EO #) Triglyceride Accumulation Per Cell (%)
(4) (6) (1.5) (4) (6) (1.5)
Next Steps: K99/R00 Research Aims
Ø Utilization of the zebrafish model to assess whether select
polyethoxylated surfactants (alcohol and alkylphenol) induce metabolic health effects following developmental exposure.
Ø Weight gain (gross), adipose depot development (adipocyte staining
and depot-specific quantification) Ø Identification of molecular mechanisms driving the adipogenic
effects of polyethoxylated surfactants across species.
Ø Human and zebrafish in vitro models, cell-based and cell-free
Ø Utilize affinity-directed analysis and HRMS to identify causative
adipogenic ligands in environmental samples.
Ø Confirmation in pre-adipocyte models; role of APEOs/AEOs
The Zebrafish Model (Danio rerio) for Metabolic Health Research
Ø
High genetic fidelity to humans – endocrine system is highly conserved, as is metabolic system
Ø
84% of genes known to be associated with human disease have zebrafish counterpart Ø
Molecular mechanisms underlying adipocyte and lipid depot development are highly conserved
Ø
Energy storage functions and morphology of adipose tissue
Ø
Genes associated with adipocyte differentiation, lipolysis, and endocrine function
Ø
Control of adipose distribution into anatomically/ physiologically/molecularly distinct depots Ø
Fish adipose tissue also contains a heterogeneous cell population, including adipocyte progenitor cells – similar to mammals
Ø
Imaging of whole-animal adipose imaging in mammals is limited, technically challenging, and generally low resolution
Minchin and Rawls 2017, Disease Mod Mech
Summary: Environmental Contaminants as Metabolic Disruptors
Ø Numerous common environmental contaminants and complex
environmental mixtures can disrupt metabolic health in vitro at environmentally-relevant concentrations.
Ø
Evidence that some environmental mixtures might promote adipogenesis through mechanisms other than PPARγ Ø In many mixtures, the causative chemicals promoting the activity have
yet to be determined.
Ø
Need for new analytical tools to isolate and identify
Ø
Need for better application of molecular databases to ease translation of in vitro data to potential in vivo health effects Ø Seems to be an association between the adipogenic activity exhibited by
house dust and the metabolic health of residents living in those homes.
Ø
This is not necessarily causative; could be a measure of altered behavior in individuals who are already overweight, contributing to different chemical burdens in the indoor environment
Acknowledgements
Ø Stapleton Lab
Ø
Heather Stapleton, PhD
Ø
Kate Hoffman, PhD
Ø
Nick Herkert, PhD
Ø
Erin Kollitz, PhD
Ø
Ellen Cooper, PhD
Ø
Allison Phillips, PhD
Ø
Stephanie Hammel, PhD
Ø
Matt Ruis
Ø
Kirsten Overdahl
Ø
Sam Hall
Ø
Jessica Levasseur
Ø
Emina Hodzic
Ø
Sharon Zhang
Ø
Funding
Ø
NIEHS R01 ES016099
Ø
NIEHS F32 ES027320
Ø
NIEHS K99 ES030405
Ø Collaborators
Duke:
Ø
Lee Ferguson, PhD NC State:
Ø
Seth Kullman, PhD
I’m Recruiting!
Ø Incoming Assistant
Professor in Institute of Environmental Health Sciences and Department
- f Pharmacology at
Wayne State University in Detroit, starting September 1!
Ø Recruiting grad