A Rapid In Vivo System for Defining Biological Responses ...Assessing Biological - Nanomaterials...
Transcript of A Rapid In Vivo System for Defining Biological Responses ...Assessing Biological - Nanomaterials...
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Robert Tanguay
Department of Environmental and Molecular Toxicology
Environmental Health Sciences Center
Oregon Nanoscience and Microtechnologies Institute (ONAMI)
- Safer Nanomaterials and Nanomanufacturing Initiative
A Rapid In Vivo System for DefiningBiological Responses to
Nanomaterials
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Proactively guide the development of inherently
safer nanomaterials
• Identify the physicochemical properties that
drive behaviors – take a global view
• Think nanoscience
• Develop predictive “behavioral models” from
experimental data.
The Opportunities
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Nanomaterial
synthesis
Test
Properties
Redesign
Material
Nanoparticles have widely tunable properties - the key is
to enhance performance and safety at the same time.
Structure/Property Relationships:
Physicochemical properties and biological responses
Designing Safer Nanoparticles
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• Much in common with the small molecule challenge
• One material at a time approach will ultimately fail
• Generalizations cannot be made…yet
• We need (MUCH) more data
• We need paradigm shift in how we assess hazard
• Very little of this early data will be directly used for risk
assessment.
The Nano Challenge
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How a material “behaves” absolutely depends on its physical properties
Agglomeration
Dissolution
Biological Fate
Environmental Interactions
Biological Responses
Goal is to predict these behaviors from inherent properties
Environmental Fate
Biological Interactions
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Biologic
Inputs
Normal
Biologic
Function
Exposure
Tissue Dose
Biologic Interaction
Perturbation
Low Dose
Biology is a System that Responds
Adapted from the National Academy
Toxicity Testing for the 21st Century
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Biologic
Inputs
Normal
Biologic
Function
Adaptive Stress
Responses
Early Cellular
Changes
Exposure
Tissue Dose
Biologic Interaction
Perturbation
Higher Dose
Biology is a System that Responds
Adapted from the National Academy
Toxicity Testing for the 21st Century
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Biologic
Inputs
Normal
Biologic
Function
Morbidity
and
Mortality
Cell
Injury
Adaptive Stress
Responses
Early Cellular
Changes
Exposure
Tissue Dose
Biologic Interaction
Perturbation
Higher yet
Biology is a System that Responds
Adapted from the National Academy
Toxicity Testing for the 21st Century
Entry Point = Toxicity Pathway
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Toxicity Pathways
Toxicity Pathway: A cellular responsepathway that, when sufficientlyperturbed, is expected to result in anadverse effect. National Academy Toxicity Testing for the 21st Century
• We need to identify these toxicity pathways
• Determine if NP perturb them
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• In vitro
– Continuous cell culture system
– Primary cell culture system
• In vivo
– Whole animal studies
– Rodents- slow and expensive
– Zebrafish
– Flies and worms – non vertebrates
Nanomaterial Biological Assessments Platforms
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“There are blind spots”
ProliferationCell deathMetabolismGene expressionPhenotypic change
Response
Cell-Based Approaches
- Advantages - quick, easy and cheap
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What blind spots?
• Different cell-cell interactions cannot be evaluated
• Indirect effects cannot be evaluated
• Cells in culture can only respond using their unique
repertoire of expressed gene products – limited
potential targets
• Practical problem…what cells do you choose?
• Tremendous potential for missed data
• In vivo models can offer complementary data…….12
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Example
Cultured endothelial cells
Expose and collect “omics data”
Hundreds of gene expression changes
Are these gene expression changes related to an adverse
outcome? Do they represent an adaptive response?
What decisions can be made based solely on this information?13
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Systems Biological Approach- early embryonic development -
• Generally more responsive to insult… because
Most dynamic life stage…and the full signaling repertoire
is expressed and active, therefore fewer blind spots..
Highest potential to detect interactions
• If a chemical or nanomaterial is developmentally toxic it
must influence the activity of a molecular pathway or
process.. i.e. hit or influence a “Toxicity Pathway”
• Use the biological response to identify the “Toxicity
Pathway”
Why?
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• Share many developmental, anatomical, and
physiological characteristics with mammals
• Molecular signaling is conserved across species
• Technical advantages of cell culture - power of in vivo
• Amenable to rapid whole animal mechanistic evaluations
• Focus on responses, then identity the “Toxicity Pathway”
underlying it - immediately relevant
Why We Use Zebrafish
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Development Stages of Assessments
3 min
1. 25hr
6 hr
19 hr
24hr
48hr120 hr
4 hr
Zebrafish.mov
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Tier 1: Toxicity Screening
• Toxicity testing whole organisms– In vivo - zebrafish
Tier 2: Cellular Targets andDistribution
• Defined in vivo
– Fluorescent nanomateials
– Targeted assays
Tier 3: Molecular Expression
• Genomic Responses– Whole animal gene expression
profiles
Define Structure Activity Relationships
hearteye
Assessing Biological - NanomaterialsInteractions and responses
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Test
Materials
Screening for responses 1-5 days
Toxicity Testing (First Steps)
1 Embryo/well
A large adult colony
is required to support
testing laboratory
Remove Chorions
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1 cell
stage
24 hpf
Alternate Exposure Route - Microinjection
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• Signaling pathways and molecular events are
conserved
• ..But fish are not rodents or humans
• Consequences of disrupted signaling often
species specific
• ……..the mechanism by which a “target” is hit is
likely conserved, but the consequence of the
“hit” may be distinct
Consider Startpoints – Not Endpoints
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Example of Toxicity Endpoints
PERICARDIAL
EDEMA
SHORTENED
SNOUT
YOLK SAC
EDEMA
HEAD
EDEMA
TCDD
CONTROL
GAS BLADDER
UNINFLATED
GAS BLADDER
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Early Life StageResponses to Ethanol
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Interpreting Common Endpoints
Common endpoints revealed by chemical, nanomaterial
and genetic screening
Pericardial edema
Yolk sac edema
Reduced growth
Bent body axis
Lack of swim bladder inflation
Mortality
Common nonspecific = 23
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AHR Signaling Pathway
AhR2
AIPhsp 90
hsp 90
AhR
AIPhsp 90
hsp 90
hsp 90
hsp 90
TCDD
TCDD
Nucleus
DRE TCDD-Responsive Genes
AhR2
ARNT
1
AIP
ARNT
AhR
AIP
hsp 90
hsp 90
TCDD
TCDD
Toxicity ?
mRNAs
Increased expression
Xenobiotic
metabolizing
enzymes
AhR1a+
2a, 2b, 2c
ARNT1
AhR1b
Cytoplasm
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AAAAAAA(n) mRNAAUG
Antisense
Morpholin
o
Morpholino Gene Repression –General approach
Assess Gene Functions - in vivo
Translational Repression- Protein levels reduced
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AAAAAAA(n) mRNAAUG
Antisense
Morpholin
o
Morpholino Gene Repression –General approach
Assess Gene Functions - in vivo
Translational Repression- Protein levels reduced
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AAAAAAA(n) mRNAAUG
Antisense
Morpholin
o
Morpholino Gene Repression –General approach
Assess Gene Functions - in vivo
Translational Repression- Protein levels reduced
Since genome is sequenced
any gene can be targeted in days!
3 hpf
A B C
3 hpf
A B C
Morpholino knock-down
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ARNT1 and AHR2 are Necessary for TCDD ToxicityRepression of ARNT1 OR AHR2 Makes Fish Non-
responsive to TCDD
ARNT1AHR2
TCDD
DRE TCDD-Responsive Genes
ARNT1AHR2
TCDD
DRE TCDD-Responsive Genes
No Toxic Response
No Toxic Response
ARNT1AHR2
TCDD
TCDD-Responsive GenesDRE Mortality
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Early Behavioral
Assessments
Tier 1 continued
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Spontaneous BehaviorSpontaneous Behavior
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TOUCH
RESPONSE
Probing the CNS…….
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Normal Twitch
Spasm
Touch Responses
Non-responsive
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Over 200 fully evaluated through tier 1.
C60, C60(OH)24, C70, SWCNT, DWCNT, dendrimers, metal
oxides, Q-dots, gold nanoparticles, viral derived……
Nanoparticles Assessed - to Date
Test
Materials
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Morphological
Malformations
i.e. pericardial edema, yolk sac edema, body axis
fin malformations, eye diameter
Circulation
Heart beat (rate)
Developmental progression
Embryo viability
Behavioral
spontaneous movement (18-24 hpf) onset and
frequency
touch response (27 hpf)
motility
High Content Tier 1 Endpoints(Assessed between 24 and 120 hpf)
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• Embryo Production
• Embryo handling
• Microinjections
• Plate reader based assays
• Behavioral assays
Automation: To Increase Throughput
Our Recent Technical Advances
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C60 Exposures and Response
C60
Control
300 ppb C60200 ppb C60
100 ppb C60
C60
Concentration(ppb)
Control 20 100 200 300 400 500
0
20
40
60
80
100 ******
***
*
MortalityPericardial EdemaYolk Sac EdemaFin Malformation
Carbon Fullerenes:
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Light Exposure Increases C60 Toxicity
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Antioxidants
Depletion
(i.e. GSH)
Oxidative Stress?
Lipid peroxidation Cell Death
Gene
Expression
Changes
Protein
Damage/
Dysfunction
Oxidative Stress Response (Tier 2)
C60
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GSH Precursor -NAC Offers Partial Protection
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The Antioxidant Ascorbic AcidOffers Partial Protection
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Chemical Depletion of GlutathioneEmbryos Are More Sensitive to C60
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N A C NAC + C60
B S O BSO + C60
DEM + C60D E M
C o n t r o l
Oxidative Environment Impacts In vivo Cellular Death Response
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• Goal: to develop a method for detecting andquantifying C60 associated with biological andaqueous samples.
• Analytical quantification of C60 using LC-MS(Collaboration with Dr. Carl Isaacson and Dr.Jennifer Field – OSU EMT)
• Pooled 100 embryos per replicate
• Use of 13C-labeled C60 surrogate to calculate lossesduring extraction method.
C60 Dose Determination
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C60 Embryo Water
Hours of Exposure
0 2 4 6 8 10 12 14
Co
nc
en
tra
tio
n (
pp
b)
0
50
100
150
200
250
300
50 ppb
100 ppb
200 ppb 400 ppb
*
C60 Embryo Water
Hours of Exposure
0 2 4 6 8 10 12 14
Co
nc
en
tra
tio
n (
pp
b)
0
50
100
150
200
250
300
50 ppb
100 ppb
200 ppb 400 ppb
*
Water Concentration Declines Over Time
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C60
Mass in Embryos
Hours of Exposure
0 2 4 6 8 10 12 14
0.0
0.1
0.4
0.5
50 ppb
100 ppb
200 ppb
400 ppb
*
*
LC50
C60 Tissue Concentration
The C60 LD50 in embryonic zebrafish is 0.1 ng/mg.
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General approach
• We focus on EC100 (i.e. 100 % cardiovascular
effect @ 5 days)
• Focus on early responses…when the endpoint is
not visible
Example
• Zebrafish oligo arrays used to evaluate gene
expression changes following exposure
• 200 ppb C60 and 1% DMSO controls
• Expression evaluated at 12 & 24 hrs post
exposure
Global Gene Expression (Tier 3)
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7.69%
7.69%
18.8%
24.36%
11.54%
14.5%
2.56%
7.69%2.56%
2.56%
16.2%
21.6%
21.6%
1.35%
1.35% 10.8%
5.4%
14.86%
6.76%
8.42%
9.47%
29.5%
18.9%
1%
6.31%8.42% 3.15%
6.31%
8.42%
22.45%26.53%
16.33%
6.12%
4.08%6.12%
14.29%
4.08%
Signal transduction
Cytoskeleton/cytosolic processing
Stress Response
Unknown
Development
Immune function
Metabolism
Transcription
Cell cycle/chromatin/RNA/DNA processing
Protein processing
Transport
36 hpf Elevated
36 hpf Reduced
Results by Functional Category
47
48 hpf Elevated
36 hpf Reduced
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• Cannot (yet) predict biological responses
• Many advantage by evaluating
interactions/responses in vivo
- multiple levels of organization
• Zebrafish: a discovery platform to define
nanomaterial/biological Interactions from diverse
sources
• Opportunities to define structure response
relationships
• Extremely well-suited for whole animal
mechanistic studies.
Conclusions
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• Efficient dissemination of shared materials
• Reduce the randomness of assessments
• Data sharing infrastructure
• Comparative analysis with shared data
• Define mode of actions of responsive NPs
• Develop predictive behavior models
• Test predictive models
Current Nano Needs
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Acknowledgements
• Dr. Stacey Harper
• Crystal Usenko
• Lisa Truong
• Kate Saili
• Dr. Jennifer Field
• Dr. Carl Isaacson
• Air Force Research Laboratory, AFRL - FA8650-05-1-5041
• NIEHS P30 Environmental Health and Sciences Center
• NIEHS T32 Toxicology Training Grant
RD-833320
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