United States
kS^laMIjk Environmental Protection
^J^iniiil m11 Agency
EPA/690/R-11/013F
Final
3-31-2011
Provisional Peer-Reviewed Toxicity Values for
1 -Bromo-3 -fluorobenzene
(CASRN 1073-06-9)
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:
Chris Cubbison, PhD
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).
l

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TABLE OF CONTENTS
COMMONLY USED ABBREVIATIONS	iii
BACKGROUND	4
HISTORY	4
DISCLAIMERS	4
QUESTIONS REGARDING PPRTVS	5
REVIEW OF POTENTIALLY RELEVANT DATA (CANCER AND NONCANCER)	6
DERIVATION 01 PROVISIONAL VALUES	8
CANCER WEIGHT OF EVIDENCE (WOE) DESCRIPTOR	8
MODE-OF-ACTION DISCUSSION	8
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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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Final
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PROVISIONAL PEER-REVIEWED TOXICITY VALUES FOR
l-BROMO-3-FLUOROBENZENE (CASRN 1073-06-9)
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 Table (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 a
panel of six 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.
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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,
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 information could be found regarding the production or use of
l-bromo-3-fluorobenzene. This chemical belongs to the halogenated benzene class of
compounds. Table 1 provides the available physicochemical properties for 1-bromo-
3-fluorobenzene.
Table 1. Physicochemical Properties Table for l-Bromo-3-Fluorobenzenea
Property (unit)
Value
Boiling point (°C)
150
Molecular weight (g/mol)
174.998363
Vapor pressure (mmHg at 25°C)
2.840
Atmospheric OH rate constant
(cm3/molecule-sec at 25°C)
1.54 x 10~12
Solubility in water (mg/L at 25°C)
378
log P (octanol-water)
2.92
Henry's Law constant (atm-m3/mol at 25°C)
2.50 x 10~3
aChemIDPlus Lite; http://chem. sis.nlm.nih.gov/chemidplus/chemidlite.j sp
No Reference Dose (RfD), Reference Concentration (RfC), or cancer assessment for
l-bromo-3-fluorobenzene is included in the IRIS database (U.S. EPA, 201 lb) or on the Drinking
Water Standards and Health Advisories List (U.S. EPA, 2009). No RfD or RfC values are
reported in the HEAST (U.S. EPA, 201 la). The Chemical Assessments and Related Activities
(CARA) list (U.S. EPA, 1994) does not include a Health and Environmental Effects Profile
(HEEP) (U.S. EPA, 1987) for l-bromo-3-fluorobenzene. The toxicity of
l-bromo-3-fluorobenzene has not been reviewed by the ATSDR (2011) or the World Health
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Organization (WHO, 2011). CalEPA (2008, 2009a,b) has not derived toxicity values for
exposure to l-bromo-3-fluorobenzene. No occupational exposure limits for 1-bromo-
3-fluorobenzene have been derived by the American Conference of Governmental Industrial
Hygienists (ACGIH, 2011), the National Institute of Occupational Safety and Health (NIOSH,
2005), or the Occupational Safety and Health Administration (OSHA, 2011).
The HEAST (U.S. EPA, 201 la) has not reported an EPA (1986) cancer
weight-of-evidence classification for l-bromo-3-fluorobenzene and has not derived any toxicity
values. The International Agency for Research on Cancer (IARC, 2011) has not reviewed the
carcinogenic potential of l-bromo-3-fluorobenzene. l-Bromo-3-fluorobenzene is not included in
the 11th Report on Carcinogens (NTP, 2005a). CalEPA (2009c,d) has not prepared a quantitative
estimate of carcinogenic potential for l-bromo-3-fluorobenzene.
Literature searches were conducted on sources published from 1900 through March 2011
for studies relevant to the derivation of provisional toxicity values for l-bromo-3-fluorobenzene,
CAS No. 1073-06-9. Searches were conducted using 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
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, TRI, and 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 risk
assessment values: ACGIH, 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 (acute-, short-term-,
subchronic-, or chronic-duration) for development of toxicity values for 1-bromo-
3-fluorobenzene (see Table 2). A toxicological study review, conducted by the NTP, was
similarly unproductive (NTP, 2005b).
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Table 2. Summary of Potentially Relevant Data for l-Bromo-3-fluorobenzene (CASRN 1073-06-9)
Notes3
Category
Number of
Male/Female,
Species, Study
Type, Study
Duration
Dosimetryb
Critical Effects
NOAELb
BMDL/
BMCLb
LOAELb
Reference
Comments0
Human
1. Oral (mg/kg-day)b
None
2. Inhalation (mg/m )
None
Animal
1. Oral (mg/kg-day)b
None
2. Inhalation (mg/m )
None
aNotes: IRIS = utilized by IRIS, date of last update; PS = principal study, NPR = not peer reviewed, N/A= not applicable.
''Dosimetry: NOAEL, BMDL/BMCL, and LOAEL values are converted to adjusted daily dose, human equivalent dose (HED in mg/kg-day) or human equivalent concentration (HEC
in mg/m3) units. All exposure values of long-term exposure (4 weeks and longer) are converted from a discontinuous to a continuous (weekly) exposure. Values for inhalation (cancer and
noncancer) and oral (cancer only) are further converted to an HEC/HED. Values from animal developmental studies are not adjusted to a continuous exposure.
1
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DERIVATION OF PROVISIONAL VALUES
Limitations in the available data preclude development of both cancer and noncancer
toxicity values for l-bromo-3-fluorobenzene.
CANCER WEIGHT OF EVIDENCE (WOE) DESCRIPTOR
Limitations in the available data preclude development of a WOE descriptor for 1-bromo-
3-fluorobenzene.
MODE-OF-ACTION DISCUSSION
Limitations in the available data preclude determination of a mode-of-action discussion
for l-bromo-3-fluorobenzene.
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CalEPA (California Environmental Protection Agency). (2009c) Hot spots unit risk and cancer
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