to Inform EPA's Upcoming IRIS
Toxicological Review
of Inorganic Arsenic
SESSION 4:
Roundtable Discussion on
Planning and Scoping
Tuesday, January 8 &
Wednesday, January 9
RTP, North Carolina
Hosted by EPA's National Center
for Environmental Assessment
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Identifying Client Needs: Draft planning and
scoping summary discussion
What are client needs for the Toxicological Review
of iAs?
Discuss key themes from the workshop to be
considered during the development of the draft
Toxicological Review of iAs.
*>EPA
United States
Environmental Protection
Agency
Key Themes from Sessions 1-3 of the iAs Public
Stakeholder Workshop
Reeder Sams
U.S. EPA/ORD/NCEA
Research Triangle Park, NC
Office of Research and Development Disclaimer: the views expressed in this presentation are those of the speaker
National Center for Environmental Assessment and do not necessarily represent the views or policies oftheM.S. EPA.
Public Stakeholder Workshop to Inform EPA's Upcoming IRIS Toxicological Review of Inorganic Arsenic
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e pp/x
v'criA Key Themes from Introduction
United States
Environmental Protection
Agency
> Partnership and outreach
> Engagement of stakeholders, including at-
risk populations
> Consideration of at-risk populations in scope
&EPA Key Themes - Session 1
Applying Systematic Review
> Process that is transparent and reproducible
> Iterative process with combination of search
strategies
> Relevancy - use previous iAs work to guide,
engage stakeholders grappling with iAs
issues
> Set up key questions - e.g., focus on low-
dose effects?
> Consider bias - e.g., negative data bias
> Feasibility (time and resources)
Office of Research and Development
Natinnal Hpntpr fnr Fnvirnnmpntal iewecmpnt
Public Stakeholder Workshop to Inform EPA's Upcoming IRIS Toxicological Review of Inorganic Arsenic
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oEPA Key Themes - Session 2
United States
Environi
Agency
Environmental Protection Hazard ID
> Susceptibility factors - in utero,
smoking/carcinogens, diet, genetic variation,
metabolism
> Effects low-level exposure is major question
and challenge for epi studies
> Aggregate exposure; concern over
misclassification of exposure
&EPA Key Themes - Session 2
United States
Environi
Agency
Environmental Protection MOA
> Consider a MOA analysis as an organizing
principle
> Lack of speciation data at target tissues
> Key biological processes/chemical stressors
that influence MOAs
> Multiple MOAs and multiple targets - dose
plays important role in MOA
> Aggregate exposure; concern over
misclassification of exposure
> Complex metabolism
Public Stakeholder Workshop to Inform EPA's Upcoming IRIS Toxicological Review of Inorganic Arsenic
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SEPA Key Themes - Session 3
~z,~ Relevant Factors for D-R
> Arsenic speciation and importance of
chemical nomenclature
> Aggregate exposure (e.g., diet,
contamination ) vs. "sole source" exposure
> Exposure in U.S. population
> Uncertainty in the exposure - life stage, dose
> Misclassification of exposure in studies
> Biomarkers of exposure (proteomics,
epigenetics, transcriptomics) - utility for
D-R?
> Bioavailability/bioaccumulation
Office of Research and Development
Matinnal rpntorfnr Pnuirnnmantal flccoccmont
&EPA Key Themes - Session 3
United States _ _ __ __
Approaches to D-R
> Multi-tumor modeling - feasible in time-frame?
> PBPK - challenge of animal-human
extrapolations, metabolism, and
polymorphisms
> Factors impacting D-R: MOA/TK, iAs
speciation, exposure estimation, susceptible
populations (e.g. age, ethnicity)
> Treat iAs speciation as a mixture for D-R?
> Uncertainty - probability
distribution/sensitivity analyses, MOA
organization
Public Stakeholder Workshop to Inform EPA's Upcoming IRIS Toxicological Review of Inorganic Arsenic
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SEPA Key Themes - Session 3
irlM" Extrapolation Approaches to D-R
> Need extrapolations to U.S. population, high
dose to low dose, and interspecies/in vitro
extrapolations - consider value added
> Human PBPK model - simplify exposure to
"total load" of iAs?
> Low dose extrapolation is to a lower
response level; a dose-response
characterization approach
Office of Research and Development
Matinnal rpntorfnr Pnuirnnmantal flccoccmont
Public Stakeholder Workshop to Inform EPA's Upcoming IRIS Toxicological Review of Inorganic Arsenic
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Key Themes From Sessions 1-3
Mike Waalkes
Key Themes From Sessions 1-3
Early life as a critical period of susceptibility
to inorganic arsenic
- Remarkable concordance between human and
rodent data in terms of carcinogenesis
Sensitivity and sites
Cannot be ignored
- Basis not known
- Other diseases need further exploration
Public Stakeholder Workshop to Inform EPA's Upcoming IRIS Toxicological Review of Inorganic Arsenic
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Key Themes From Sessions 1-3
The role of biomethylation in inorganic
arsenic
- Susceptibility factor
Poor tissue and target site dosimetry for
inorganic arsenic in humans
- We do not know what gets where with regards
to target cells
Or what is generated where
Urinary metabolites poor substitute
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Identifying Client Needs: Draft planning and
scoping summary discussion
What are client needs for the Toxicological Review
of iAs?
Recommendations for revisions to the planning
and scoping summary to adequately
address stakeholder input.
EPA ARSENIC WORKSHOP
PRESENTATION TO U.S.
ENVIRONMENTAL PROTECTION AGENCY
RESEARCH TRIANGLE PARK, NC
JANUAR? 8-9, 2013
SAMUEL M. COHEN, M.D., PH.D.
DEPARTMENT OF PATHOLOGY AND MICROBIOLOGY
UNIVERSITY OF NEBRASKA MEDICAL CENTER
OMAHA, NE 6819 8-31 35
Public Stakeholder Workshop to Inform EPA's Upcoming IRIS Toxicological Review of Inorganic Arsenic
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MODE OF ACTION
Metabolism and kinetics
Genotoxicity vs. non-genotoxicity
Cellular responses
Critical review of the literature
Cancer and non-cancer
65
CLASSIC PATHWAY
FOR ARSENIC METABOLISM
Putative Pathway for Arsenic Metabolism
9 2e" CH3* o 2e-
M -ie II
OHAsOH ~OH jksOH *«-CH3AsOH
J)H OH OH
L
As As MMA
CH3+
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THIOLATED ARSENICALS
?
HO"^s
r oh
OH
iAsv
in-vitro
cecum
MU / OH
OH S
iAsVSi H0-JL
. MU / SH
-> O SH
!
i
^ / SH
OH
MMDTAV
-As-.
HO j ^SH
OH
iAsvS2
iAs S3 H3C"/S>
H.C'f
I H>C
/*Ab\
SH nun
/ SH
SH
WIMTTAV
DMDTA
Pinyayev et al., Chem. Res. Toxicol., 24:475-7,2011.
TOXICITY OT ARSENIC METABOLITES
IN UROTHELIUM IN VITRO,
EXPRESSED AS LC50 VALUES (fiM)
Cell Line
As111
Asv
MMA1"
MMAV
DMA111
DMAV
TMAO
DMMTAV*
MYP3
(Rat)
0.75
3.4
0.42
3000
0.38
600
1600
1.3
ITI
(Human)
8.3
34.6
0.9
2700
1.0
230
14000
1.4
* DMMTAV
- Dimethyl monothiol arsenic acid
Public Stakeholder Workshop to Inform EPA's Upcoming IRIS Toxicological Review of Inorganic Arsenic
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RECENT DEVELOPMENTS IN RESE ARCH
OF ARSENIC METABOLISM
Asll! methyl transferase (As3Mt):
Glutathione in reaction mixture has little effect on methylation
Strongly favors classical pathway (Does not support
Hayakama's proposed pathway)
DMA is poor substrate for human enzyme
Explains lack of TMAO formation in humans
Thiol analogs:
Formed primarily by a chemical reaction of oxyarsenicals with H2S
Primarily from Gl bacteria, but also in tissues
Rapidly transported into cells and rapidly converted chemically to
trivalent oxyarsenicals
Explains their high cytotoxicity compared to pentavalent
oxyarsenical analogs
69
INTRAMITOCHONDRIAL GRANULES IN
MOUSE UROTHELIUM
Public Stakeholder Workshop to Inform EPA's Upcoming IRIS Toxicological Review of Inorganic Arsenic
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I NT RAC YT OPL ASM IC GRANULES IN UROTHELIAL
CELLS OF PML PATIENTS TREATED WITH As203
% %
>
* 4* * -
& . { '
**
% »
J -
¦> ./«
> * (* . /
¦ J' V /
/ *
? ..-p
71
MODE OF ACTION OF DMAV
Public Stakeholder Workshop to Inform EPA's Upcoming IRIS Toxicological Review of Inorganic Arsenic
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UROTHELIAL CYTOTOXICITY AND
PROLIFERATION INDUCED BY DMAV IN RATS
GENE EXPRESSION IN DI11J REN 1 HUMAN
CELL TYPES INDUCED BY ARSENICALS
HBECs (bronchial)
HEK001 (skin) 1T1 (bladder)
Cell death & survival
Cell death & survival
Cell growth & proliferation
Cell growth & proliferation
Cell-cell signaling
Cell-cell signaling
Cell movement
Cell movement
Cell development
DNA replication & repairs
Small molecule bioschemistry
Cell cycle
Cell assembly & organization
Lipid metabolism
74
Public Stakeholder Workshop to Inform EPA's Upcoming IRIS Toxicological Review of Inorganic Arsenic
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RELEVANCE TO HUMANS
Clinical Manifestations and Arsenic Methylation After a Rare Subacute Arsenic Poisoning Accident
Y. Xu, Y. Wang, Q. Zheng, B. Li, X. Li, Y. Jin, X. Lv, G. Qu, and G. Sun.
Toxicol. Sciences, 10: 278-284, 2008.
Observations
High exposure
DMAV & TMAO in urine
Hematuria in 1/3 of exposed group
HUMAN CHRONIC BRONCHITIS SKIN: ACTINIC KERATOSIS
IN VIVO CYTOTOXICITY OF
INORGANIC ARSENIC
Threshold is 1 ppm elemental
Rats and mice
Males and females
Arsenite and arsenate
Detection method:
Histopathology
Labeling index
Scanning electron microscopy
Genomics
27
Public Stakeholder Workshop to Inform EPA's Upcoming IRIS Toxicolbgicail Review of Inorganic Arsenic
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IN VITRO CYTOTOXICITY OF
INORGANIC ARSENIC
Threshold approximately 0.2 |jM
Urothelial cells (rats and humans)
Bronchial epithelial cells (humans)
Keratinocytes (humans and mice)
Less than 0.2 pM - Adaptive
0.2-1.0 pM - Cytotoxicity
Greater than 10 |jM - Lethal
ARSENIC RESEARCH
LITERATURE PRECAUTIONS (1/2)
Analytical methods
Arsenic form:
As111 vs. Asv
Inorganic vs. methylated vs. other organics
Concentrations (in vitro) and doses (in vivo):
Environmental drinking water concentration of 10 |jg/L
(0.2 |jM) is not systemic or tissue concentration
Many claim in vitro studies with "environmentally
relevant concentrations of 10 M9/L"
Concentrations of trivalents >10 |jM in vitro are
meaningless; lethal dose
78
Public Stakeholder Workshop to Inform EPA's Upcoming IRIS Toxicological Review of Inorganic Arsenic
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ARSENIC RESEARCH
LITERATURE PRECAUTIONS (2/2)
Cell types:
Must use epithelial cells
Lung tiProblasts do not represent cell of origin for iung cancer
Malignant cell lines (e.g., osteosarcoma) have limited value
without corroboration
Primary cell vs. established cell lines:
Established cell lines have multiple differences compared to
normal, especially p53
in vitro vs. in vivo:
Trivalent arsenicals bound to rat hemoglobin
Oxidative stress in vitro (Gentry et al 2010)
No oxidative stress in vivo (Clewell et ai 2011) (Suzuki et al.,
submitted) 79
INTERACTION OF
ARSENICALS WITH RAT HEMOGLOBIN
In Vitro In ViVo
As111 + Hb * As111 Hb Asv + Hb * DMA111 Hb
MMA111 + Hb»¦ MMAI!!Hb MMAV + Hb DMA111 Hb
DMA111 + Hb-* DMA111Hb DMAV + Hb ~ DMA111 Hb
Feeding Asv, MMAvor DMAvto rats produces DMAHiHb
80
Public Stakeholder Workshop to Inform EPA's Upcoming IRIS Toxicological Review of Inorganic Arsenic
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BIOLOGICAL EFFECTS OF ARSENIC
81
Mode of Action for
Inorganic Arsenic: Working Hypothesis
Cancer
Non-Cancer
Ingestion of Arsenic
Conversion to Trivalent Arsenicals
(iAsln, AAMAIM, DMA"1)
Interaction with Critical
Cellular Sulfhydryl Groups
Threshold *
Cytotoxicity
Cell death>.
Ingestion of Arsenic
'J'
Conversion to Trivalent Arsenicals
(iAsm, MMA"!, DMA"1)
Interaction with Critical
Cellular Sulfhydryl Groups
Threshold »
Cytotoxicity y Non-cancer
effects
Regenerative Proliferation
1
Carcinoma
82
Public Stakeholder Workshop to Inform EPA's Upcoming IRIS Toxicological Review of Inorganic Arsenic
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PUBLIC STAKEHOLDER WORKSHOP TO
INFORM EPA's UPCOMING IRIS
TOXICOLOGICAL REVIEW OF
INORGANIC ARSENIC
Michele Roberts
Environmental Justice Health Alliance
January 9, 2013
Environmental Justice
Public Stakeholder Workshop to Inform EPA's Upcoming IRIS Toxicological Review of Inorganic Arsenic
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Why other sources matter in
toxicological assessments
Studies show the need to protect the
Bell Curve
RECENTLY published in Environmental Health
Perspectives, "Beyond Uncertainty Factors:
Protecting the Bell Curve
"some individuals have predisposing risk
factors that make them uniquely sensitive to
the effects of these environmental stressors."
(Schmidt, 2012 at: http://ehp.niehs.nih.gov/2013/01/121-
a26/)
Public Stakeholder Workshop to Inform EPA's Upcoming IRIS Toxicological Review of Inorganic Arsenic
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Health professionals call for broad
reform
Dr. David Bellinger, Harvard Medical School
Professor stated: "The assessment of effect
modifiers should drive the study design. As it
stands now, analysis of potential modifiers is
usually something tacked on at the end of the
main study..."
Dr. Bellinger concludes that toxicological reviews
need to identify the most susceptible people and
quantify their added risk in order to make
appropriate management decisions.
Social Stressors
Poverty
-access to nutritional food
-access to health care and prenatal care
-housing conditions
Racism
Public Stakeholder Workshop to Inform EPA's Upcoming IRIS Toxicological Review of Inorganic Arsenic
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Arsenic and Cardiovascular Disease
2012 systemic review on arsenic exposure and
hypertension found an increasing trend in the
odds of hypertension with increasing arsenic
exposure. (Abhyankar et. al, 2012)
Abhyankar found that "low" arsenic exposure
imposed a more than 50% increase in the risk of
hypertension.
Another study, Zhang et. al (2012) found
substantially elevated risk with low exposure to
arsenic.
Cardiovascular Disease Among African
Americans
Race/Ethnic Group Differences
Heart Disease Age-Adjusted Death Rates by Race/Ethnicity
California, 2000 -2008
2000
2001
2002
2003
2004
2005
2006
2007
2008
Black
351.2
347.3
347.1
331.3
304.5
302.1
301.8
280.4
262.2
Pacific Islander
317.3
306.0
241.2
269.4
230.1
216.4
215.0
220.1
219.0
White
251.8
248.2
240.2
236.4
218.1
211.1
206.6
196.2
187.3
Hispanic
184.8
177.0
165.4
163.3
150.3
148.5
143.8
130.1
127.4
American Indian
192.6
170.3
142.0
150.1
133.7
123.0
123.8
110.1
93.8
Asian
150.2
144.7
142.0
132.1
117.0
114.5
115.6
106.5
103.9
Two or More Races
34.1
25.5
22.7
64.7
58.7
58.0
58.2
60.9
65.8
_
*s^C'Sla
Q American Indian
O Two
or More Races
Public Stakeholder Workshop to Inform EPA's Upcoming IRIS Toxicological Review of Inorganic Arsenic
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Scientific Studies call for Reform
Study by researchers of the University of North
Carolina, (Mo et al, 2011) findings suggest the need for
an integrative mode of action in humans, with many
results supporting numerous other studies that have
found chronic arsenic exposure can cause cancer,
cardiovascular disease and diabetes.
Arsenic associated with diabetes mellitus,
cerebrovascular disease and other potentially fatal
diseases that are more prevalent in African Americans
(Meliker et al, 2007).
Conclusion and next steps
Arsenic exposure can exacerbate cardiovascular
disease as evidenced by a large body of science
and standard medical tests.
African Americans are at elevated risks of
preliminary and advanced stages of
cardiovascular disease and have higher mortality
rates from heart disease across the age span,
with young and middle aged having more
disproportionate elevations in death rates.
Public Stakeholder Workshop to Inform EPA's Upcoming IRIS Toxicological Review of Inorganic Arsenic
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Conclusion and next steps
Evidence of arsenic's cardiovascular toxicity and
elevated risk among African Americans is
substantial persuasive, and sufficient to rely on in
risk assessments of arsenic.
EPA's evaluation of arsenic must take under
consideration and explicitly address the
disproportionate health burden exposure
imposes on African Americans.
The elevated risks must be incorporated in
quantitative evaluations of noncancer toxicity
and be addressed in public policy.
Thank you!
Public Stakeholder Workshop to Inform EPA's Upcoming IRIS Toxicological Review of Inorganic Arsenic
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Recommendations
Mike Waalkes
Recommendations
In general, humans appear more sensitive than
rodents to inorganic arsenic
- Clear with cancer
Other diseases (?)
- Should be considered in review
Public Stakeholder Workshop to Inform EPA's Upcoming IRIS Toxicological Review of Inorganic Arsenic
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Recommendations
Since inorganic arsenic is associated with
multiple, diverse diseases
- Review should keep an open mind to the possibility
of multiple modes of action
Recommendations
There is a good evidence that inorganic arsenic
as well as various metabolites are toxicologically
active
- Review should keep an open mind to the possibility
of multiple species being active
Public Stakeholder Workshop to Inform EPA's Upcoming IRIS Toxicological Review of Inorganic Arsenic
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Methods for Identifying, Evaluating,
and Synthesizing Literature
Public Comments
m
O
5
¦o ¦£*
-=
£0 Tf
* |
rtl «£
2 *
3 I
ii
0016
EC
o
s
ciam
0.005
0 000
NRC 2001
Risk Estimate
\
MORTALITY = 4.9>c10"3 4.7x1 O^xC,
Fig. 3
tODTlIlK
0 50 too 150 200 250
Cmea/i Mean County Arsenic Concentration (ng/L)
. While male bladder cancer lifednne mortality one by Mean, mric rancemriaticm ("U.I
with median arsenic le'-'eli of £-3 §igfl_ ill drinking wafer).
Public Stakeholder Workshop to Inform EPA's Upcoming IRIS Toxicological Review of Inorganic Arsenic
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SMRs for Bladder and Lung Cancers for Low and High Arsenic Villages
by Mean Village Well Water Arsenic Level (ug/L)
Low Arsenic
High Arsenic
Linear (Low Arsenic)
1200
1100
W
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