United States
Environmental Protection
1=1 m m Agency
Provisional Peer-Reviewed Toxicity Values for
Stearyl Acetate
(CASRN 822-23-1)
EPA/690/R-10/022F
Final
9-20-2010
Superfund Health Risk Technical Support Center
National Center for Environmental Assessment
Office of Research and Development
U.S. Environmental Protection Agency
Cincinnati, OH 45268
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AUTHORS, CONTRIBUTORS, AND REVIEWERS
CHEMICAL MANAGER:
Jon Reid, National Center for Environmental Assessment, Cincinnati, OH
DRAFT DOCUMENT PREPARED BY:
National Center for Environmental Assessment, Cincinnati, OH
This document was externally peer-reviewed under contract to:
Eastern Research Group, Inc.
110 Hartwell Avenue
Lexington, MA 02421-3136
Questions regarding the contents of this document may be directed to the U.S. EPA Office of
Research and Development's National Center for Environmental Assessment, Superfund Health
Risk Technical Support Center (513-569-7300)
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TABLE OF CONTENTS
COMMONLY USED ABBREVIATIONS	iii
BACKGROUND	1
HISTORY	1
DISCLAIMERS	1
QUESTIONS REGARDING PPRTVs	2
INTRODUCTION	2
REVIEW OF POTENTIALLY RELEVANT DATA (CANCER AND NONCANCER)	3
DERIVATION 01 PROVISIONAL VALUES	3
CANCER WOE DESCRIPTOR	3
MODE-OF-ACTION DISCUSSION	3
REFERENCES	4
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COMMONLY USED ABBREVIATIONS
BMC
benchmark concentration
BMD
benchmark dose
BMCL
benchmark concentration lower bound 95% confidence interval
BMDL
benchmark dose lower bound 95% confidence interval
HEC
human equivalent concentration
HED
human equivalent dose
IUR
inhalation unit risk
LOAEL
lowest-observed-adverse-effect level
LOAELadj
LOAEL adjusted to continuous exposure duration
LOAELhec
LOAEL adjusted for dosimetric differences across species to a human
NOAEL
no-ob served-adverse-effect level
NOAELadj
NOAEL adjusted to continuous exposure duration
NOAELhec
NOAEL adjusted for dosimetric differences across species to a human
NOEL
no-ob served-effect level
OSF
oral slope factor
p-IUR
provisional inhalation unit risk
p-OSF
provisional oral slope factor
p-RfC
provisional reference concentration (inhalation)
p-RfD
provisional reference dose (oral)
POD
point of departure
RfC
reference concentration (inhalation)
RfD
reference dose (oral)
UF
uncertainty factor
UFa
animal-to-human uncertainty factor
UFC
composite uncertainty factor
UFd
incomplete-to-complete database uncertainty factor
UFh
interhuman uncertainty factor
UFl
LOAEL-to-NOAEL uncertainty factor
UFS
subchronic-to-chronic uncertainty factor
WOE
weight of evidence
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PROVISIONAL PEER-REVIEWED TOXICITY VALUES FOR
STEARYL ACETATE (CASRN 822-23-1)
BACKGROUND
History
On December 5, 2003, the U.S. Environmental Protection Agency's (EPA) Office of
Superfund Remediation and Technology Innovation (OSRTI) revised its hierarchy of human
health toxicity values for Superfund risk assessments, establishing the following three tiers as the
new hierarchy:
1)	EPA's Integrated Risk Information System (IRIS).
2)	Provisional Peer-Reviewed Toxicity Values (PPRTVs) used in EPA's Superfund
Program.
3)	Other (peer-reviewed) toxicity values, including
>	Minimal Risk Levels produced by the Agency for Toxic Substances and Disease
Registry (ATSDR),
>	California Environmental Protection Agency (CalEPA) values, and
>	EPA Health Effects Assessment Summary (HEAST) values.
A PPRTV is defined as a toxicity value derived for use in the Superfund Program when
such a value is not available in EPA's IRIS. PPRTVs are developed according to a Standard
Operating Procedure (SOP) and are derived after a review of the relevant scientific literature
using the same methods, sources of data, and Agency guidance for value derivation generally
used by the EPA IRIS Program. All provisional toxicity values receive internal review by two
EPA scientists and external peer review by three independently selected scientific experts.
PPRTVs differ from IRIS values in that PPRTVs do not receive the multiprogram consensus
review provided for IRIS values. This is because IRIS values are generally intended to be used
in all EPA programs, while PPRTVs are developed specifically for the Superfund Program.
Because new information becomes available and scientific methods improve over time,
PPRTVs are reviewed on a 5-year basis and updated into the active database. Once an IRIS
value for a specific chemical becomes available for Agency review, the analogous PPRTV for
that same chemical is retired. It should also be noted that some PPRTV documents conclude that
a PPRTV cannot be derived based on inadequate data.
DISCLAIMERS
Users of this document should first check to see if any IRIS values exist for the chemical
of concern before proceeding to use a PPRTV. If no IRIS value is available, staff in the regional
Superfund and Resource Conservation and Recovery Act (RCRA) program offices are advised to
carefully review the information provided in this document to ensure that the PPRTVs used are
appropriate for the types of exposures and circumstances at the Superfund site or RCRA facility
in question. PPRTVs are periodically updated; therefore, users should ensure that the values
contained in the PPRTV are current at the time of use.
It is important to remember that a provisional value alone tells very little about the
adverse effects of a chemical or the quality of evidence on which the value is based. Therefore,
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users are strongly encouraged to read the entire PPRTV document and understand the strengths
and limitations of the derived provisional values. PPRTVs are developed by the EPA Office of
Research and Development's National Center for Environmental Assessment, Superfund Health
Risk Technical Support Center for OSRTI. Other EPA programs or external parties who may
choose of their own initiative to use these PPRTVs are advised that Superfund resources will not
generally be used to respond to challenges of PPRTVs used in a context outside of the Superfund
Program.
QUESTIONS REGARDING PPRTVs
Questions regarding the contents of the PPRTVs and their appropriate use (e.g., on
chemicals not covered, or whether chemicals have pending IRIS toxicity values) may be directed
to the EPA Office of Research and Development's National Center for Environmental
Assessment, Superfund Health Risk Technical Support Center (513-569-7300), or OSRTI.
INTRODUCTION
No reference dose (RfD), reference concentration (RfC), or cancer assessment for stearyl
acetate is included on the United States Environmental Protection Agency (U.S. EPA) IRIS
database (U.S. EPA, 2010) or on the Drinking Water Standards and Health Advisories List
(U.S. EPA, 2009). The HEAST reported no RfD or RfC values (U.S. EPA, 2003). The
Chemical Assessments and Related Activities (CARA) list (U.S. EPA, 1994) did not include a
Health and Environmental Effects Profile (HEEP) for stearyl acetate. The toxicity of stearyl
acetate has not been reviewed by ATSDR (2008) or the World Health Organization (WHO,
2010). CalEPA (2008) has not derived toxicity values for exposure to stearyl acetate. No
occupational exposure limits for stearyl acetate have been derived by the American Conference
of Governmental Industrial Hygienists (ACGIH, 2010), the National Institute of Occupational
Safety and Health (NIOSH, 2005), or the Occupational Safety and Health Administration
(OSHA, 2010).
The HEAST (U.S. EPA, 2003) does not report any values for stearyl acetate. Stearyl
acetate has not been evaluated under the 2005 Guidelines for Carcinogen Risk Assessment
(U.S. EPA, 2005). The International Agency for Research on Cancer (IARC, 2010) has not
reviewed the carcinogenic potential of stearyl acetate. Stearyl acetate is not included in the
11th Report on Carcinogens (NTP, 2005). CalEPA (2009) has not prepared a quantitative
estimate of carcinogenic potential for stearyl acetate.
Literature searches were conducted on sources published from 1900 through May 2010
for studies relevant to the derivation of provisional toxicity values for stearyl acetate, CAS No.
822-23-1. Searches were conducted with EPA's Health and Environmental Research Online
(HERO) evergreen database of scientific literature. HERO searches the following databases:
AGRICOLA; American Chemical Society; BioOne; Cochrane Library; DOE: Energy
Information Administration, Information Bridge, and Energy Citations Database; EBSCO:
Academic Search Complete; GeoRef Preview; GPO: Government Printing Office;
Informaworld; IngentaConnect; J-STAGE: Japan Science & Technology; JSTOR: Mathematics
& Statistics and Life Sciences; NSCEP/NEPIS (EPA publications available through the National
Service Center for Environmental Publications [NSCEP] and National Environmental
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Publications Internet Site [NEPIS] database); PubMed: MEDLINE and CANCERLIT databases;
SAGE; Science Direct; Scirus; Scitopia; SpringerLink; TOXNET (Toxicology Data Network):
ANEUPL, CCRIS, ChemlDplus, CIS, CRISP, DART, EMIC, EPIDEM, ETICBACK, FEDRIP,
GENE-TOX, HAPAB, HEEP, HMTC, HSDB, IRIS, ITER, LactMed, Multi-Database Search,
NIOSH, NTIS, PESTAB, PPBIB, RISKLINE, and TRI; TSCATS; Virtual Health Library; Web
of Science (searches Current Content database among others); World Health Organization; and
Worldwide Science. The following databases outside of HERO were searched for toxicity
assessment values: ACGM, AT SDR, CalEPA, EPA IRIS, EPA HEAST, EPA HEEP, EPA OW,
EPA TSCATS/TSCATS2, NIOSH, NTP, OSHA, and RTECS.
REVIEW OF POTENTIALLY RELEVANT DATA
(CANCER AND NONCANCER)
The literature search revealed no human or animal studies, either acute, short term, or
chronic, for stearyl acetate
DERIVATION OF PROVISIONAL VALUES
Limitations in the available data preclude development of both cancer and noncancer
toxicity values.
CANCER WOE DESCRIPTOR
Limitations in the available data preclude development of a WOE descriptor.
MODE-OF-ACTION DISCUSSION
Limitations in the available data preclude determination of a mode-of-action discussion.
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REFERENCES
ACGIH (American Conference of Governmental Industrial Hygienists). (2010) Threshold limit
values for chemical substances and physical agents and biological exposure indices. Cincinnati,
OH. As cited in HSDB (Hazardous Substances Data Bank). Available online at
http://toxnet.nlm.nih.eov/cei-bin/sis/htmleen7HSDB. Accessed on May 6, 2010.
ATSDR (Agency for Toxic Substances and Disease Registry). (2008) Toxicological profile
information sheet. U.S. Department of Health and Human Services, Public Health Service.
Available online at http://www.atsdr.cdc.eov/toxprofiles/index.asp. Accessed on May 6, 2010.
CalEPA (California Environmental Protection Agency). (2008) Office of Environmental Health
Hazard Assessment. Search Chronic RELs. Available online at
http ://www. arb. ca. eov/toxics/healthval/chronic.pdf and
http://www.oehha.ca.gov/air/chronic rets/AllChrels.html. Accessed on May 6, 2010.
CalEPA (California Environmental Protection Agency). (2009) Office of Environmental Health
Hazard Assessment. Hot Spots Unit Risk and Cancer Potency Values. Available online at
http://www.oehha.ca.gov/air/hot spots/2009/AppendixA.pdf. Accessed on May 6, 2010.
IARC (International Agency for Research on Cancer). (2010) IARC Monographs on the
evaluation of carcinogenic risks to humans. Available online at
http://monoeraphs.iarc.fr/ENG/Monoeraphs/PDFS/index.php. Accessed on May 6, 2010.
NIOSH (National Institute for Occupational Safety and Health). (2005) NIOSH Pocket Guide
to Chemical Hazards. Index by CASRN. Available online at
http://www.cdc.gov/niosh/npg/npgdcas.html. Accessed on May 6, 2010.
NTP (National Toxicology Program). (2005) 11th Report on Carcinogens. U.S. Department of
Health and Human Services, Public Health Service, National Institutes of Health, Research
Triangle Park, NC. Available online at http://ntp.niehs.nih.gov/ntp/roc/tocl 1 .html. Accessed on
May 6, 2010.
OSHA (Occupational Safety and Health Administration). (2010) OSHA Standard 1915.1000
for Air Contaminants. Part Z, Toxic and Hazardous Substances. Available online at
http://www.osha.gov/pls/oshaweb/owadisp.show document?p table STANDARDS&p id=102
86. Accessed on May 6, 2010.
U.S. EPA (U.S. Environmental Protection Agency). (1994) Chemical Assessments and Related
Activities (CARA). Office of Health and Environmental Assessment, Washington, DC.
December 1994; EPA/600/R94904.
U.S. EPA (U.S. Environmental Protection Agency). (2003) Health Effects Assessment
Summary Tables (HEAST). Prepared by the Office of Research and Development, National
Center for Environmental Assessment, Cincinnati OH for the Office of Emergency and Remedial
Response, Washington, DC. Available online at http://epa-heast.ornl.gov/. Accessed May
6, 2010.
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U.S. EPA (U.S. Environmental Protection Agency). (2005) Guidelines for carcinogen risk
assessment. Risk Assessment Forum, Washington, DC; EPA/630/P-03/001F. Federal Register
70(66): 17765-17817.
U.S. EPA (U.S. Environmental Protection Agency). (2009) 2009 Edition of the Drinking Water
Standards and Health Advisories. Office of Water, Washington, DC; EPA 822-R-09-011.
Available online at http://www.epa.gov/waterscience/criteria/drinkine/dwstandards2009.pdf.
Accessed May 6, 2010.
U.S. EPA (U.S. Environmental Protection Agency). (2010) Integrated Risk Information System
(IRIS). Office of Research and Development, National Center for Environmental Assessment,
Washington, DC. Available online at http://www.epa.gov/iris/. Accessed May 6, 2010.
WHO (World Health Organization). (2010) Online catalogs for the Environmental Health
Criteria Series. Available online at http://www.who.int/ipcs/publications/ehc/en/. Accessed
May 6, 2010.
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