Boscalid; Pesticide Tolerance, 16553-16559 [E8-6264]
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16553
Federal Register / Vol. 73, No. 61 / Friday, March 28, 2008 / Rules and Regulations
Subpart C—Section 107 Attainment
Status Designations
revising the entry for Memphis, TN–AR
and footnote 2 to read as follows:
2. In § 81.304 the table for Arkansas—
Ozone (8-hour Standard) is amended by
§ 81.304
I
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Arkansas.
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ARKANSAS—OZONE (8-HOUR STANDARD)
Designation a
Category/classification
Designated area
Date 1
Memphis, TN–AR: (AQCR 018 Metropolitan Memphis Interstate) Crittenden County.
*
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Type
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Nonattainment ...............
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Date 1
Type
(2)
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Subpart 2/Moderate.
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a Includes
1 This
2 April
Indian Country located in each county or area, except as otherwise specified.
date is June 15, 2004, unless otherwise noted.
28, 2008.
*
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3. In § 81.343 the table for
Tennessee—Ozone (8-hour Standard) is
I
§ 81.343
amended by removing footnote 3 and
revising the entry for ‘‘Memphis, TN–
AR’’ to read as follows:
*
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Tennessee.
*
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TENNESSEE—OZONE (8-HOUR STANDARD)
Designation a
Category/classification
Designated area
Date 1
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Memphis, TN–AR: Shelby County ..............................
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Type
*
..........................
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Date 1
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Nonattainment ...............
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March 28, 2008
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Type
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Subpart 2/Moderate.
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*
a Includes
1 This
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Indian Country located in each county or area, except as otherwise specified.
date is June 15, 2004, unless otherwise noted.
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[FR Doc. E8–6287 Filed 3–27–08; 8:45 am]
BILLING CODE 6560–50–P
ENVIRONMENTAL PROTECTION
AGENCY
40 CFR Part 180
[EPA–HQ–OPP–2005–0145; FRL–8354–4]
Boscalid; Pesticide Tolerance
Environmental Protection
Agency (EPA).
ACTION: Final rule.
rwilkins on PROD1PC63 with RULES
AGENCY:
SUMMARY: This regulation establishes
tolerances for residues of boscalid in or
on caneberry subgroup 13A at 6.0 parts
per million (ppm); bushberry subgroup
13B at 13 ppm; cotton, undelinted seed
at 1.0 ppm; cotton, gin by-products at 55
ppm; avocado at 1.5 ppm; sapote, black
at 1.5 ppm; canistel at 1.5 ppm; sapote,
mamey at 1.5 ppm; mango at 1.5 ppm;
papaya at 1.5 ppm; sapodilla at 1.5 ppm;
and star apple at 1.5 ppm. It revokes the
existing berries, group 13 tolerance at
3.5 ppm because the two new caneberry
and bushberry tolerances cover all
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commodities in the berries, group 13.
Tolerances are being increased for
cucumber from 0.20 ppm to 0.5 ppm,
and vegetable, root, subgroup 1A, except
sugarbeet, garden beet, radish, and
turnip from 0.7 ppm to 1.0 ppm. BASF,
Inc requested these tolerance actions
under the Federal Food, Drug, and
Cosmetic Act (FFDCA). In addition, this
action establishes a time-limited
tolerance for residues of boscalid in or
on Endive, Belgian, in response to the
approval of a crisis exemption under
section 18 of the Federal Insecticide,
Fungicide, and Rodenticide Act (FIFRA)
authorizing the post harvest use of the
fungicide on Endive, Belgian to control
the fungal pathogen, scelerotinia
sclerotiorum. This regulation establishes
a maximum permissible level of
residues of boscalid in this food
commodity. The time-limited tolerance
expires and is revoked on December 31,
2009.
This regulation is effective
March 28, 2008. Objections and requests
for hearings must be received on or
before May 27, 2008, and must be filed
in accordance with the instructions
provided in 40 CFR part 178 (see also
DATES:
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Unit I.C. of the SUPPLEMENTARY
INFORMATION).
EPA has established a
docket for this action under docket
identification (ID) number EPA–HQ–
OPP–2005–0145. To access the
electronic docket, go to https://
www.regulations.gov, select ‘‘Advanced
Search,’’ then ‘‘Docket Search.’’ Insert
the docket ID number where indicated
and select the ‘‘Submit’’ button. Follow
the instructions on the regulations.gov
website to view the docket index or
access available documents. All
documents in the docket are listed in
the docket index available in
regulations.gov. Although listed in the
index, some information is not publicly
available, e.g., Confidential Business
Information (CBI) or other information
whose disclosure is restricted by statute.
Certain other material, such as
copyrighted material, is not placed on
the Internet and will be publicly
available only in hard copy form.
Publicly available docket materials are
available in the electronic docket at
https://www.regulations.gov, or, if only
available in hard copy, at the OPP
Regulatory Public Docket in Rm. S–
ADDRESSES:
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Federal Register / Vol. 73, No. 61 / Friday, March 28, 2008 / Rules and Regulations
4400, One Potomac Yard (South Bldg.),
2777 S. Crystal Dr., Arlington, VA. The
Docket Facility is open from 8:30 a.m.
to 4 p.m., Monday through Friday,
excluding legal holidays. The Docket
Facility telephone number is (703) 305–
5805.
FOR FURTHER INFORMATION CONTACT:
Bryant Crowe, Registration Division
(7505P), Office of Pesticide Programs,
Environmental Protection Agency, 1200
Pennsylvania Ave., NW., Washington,
DC 20460–0001; telephone number:
(703) 305–0025; e-mail address:
crowe.bryant@epa.gov.
SUPPLEMENTARY INFORMATION:
I. General Information
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A. Does this Action Apply to Me?
You may be potentially affected by
this action if you are an agricultural
producer, food manufacturer, or
pesticide manufacturer. Potentially
affected entities may include, but are
not limited to those engaged in the
following activities:
• Crop production (NAICS code 111),
e.g., agricultural workers; greenhouse,
nursery, and floriculture workers;
farmers.
• Animal production (NAICS code
112), e.g., cattle ranchers and farmers,
dairy cattle farmers, livestock farmers.
• Food manufacturing (NAICS code
311), e.g., agricultural workers; farmers;
greenhouse, nursery, and floriculture
workers; ranchers; pesticide applicators.
• Pesticide manufacturing (NAICS
code 32532), e.g., agricultural workers;
commercial applicators; farmers;
greenhouse, nursery, and floriculture
workers; residential users.
This listing is not intended to be
exhaustive, but rather to provide a guide
for readers regarding entities likely to be
affected by this action. Other types of
entities not listed in this unit could also
be affected. The North American
Industrial Classification System
(NAICS) codes have been provided to
assist you and others in determining
whether this action might apply to
certain entities. If you have any
questions regarding the applicability of
this action to a particular entity, consult
the person listed under FOR FURTHER
INFORMATION CONTACT.
B. How Can I Access Electronic Copies
of this Document?
In addition to accessing an electronic
copy of this Federal Register document
through the electronic docket at https://
www.regulations.gov, you may access
this Federal Register document
electronically through the EPA Internet
under the ‘‘Federal Register’’ listings at
https://www.epa.gov/fedrgstr. You may
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also access a frequently updated
electronic version of EPA’s tolerance
regulations at 40 CFR part 180 through
the Government Printing Office’s pilot
e-CFR site at https://www.gpoaccess.gov/
ecfr.
C. Can I File an Objection or Hearing
Request?
Under section 408(g) of FFDCA, any
person may file an objection to any
aspect of this regulation and may also
request a hearing on those objections.
You must file your objection or request
a hearing on this regulation in
accordance with the instructions
provided in 40 CFR part 178. To ensure
proper receipt by EPA, you must
identify docket ID number EPA–HQ–
OPP–2005–0145 in the subject line on
the first page of your submission. All
requests must be in writing, and must be
mailed or delivered to the Hearing Clerk
as required by 40 CFR part 178 on or
before May 27, 2008.
In addition to filing an objection or
hearing request with the Hearing Clerk
as described in 40 CFR part 178, please
submit a copy of the filing that does not
contain any CBI for inclusion in the
public docket that is described in
ADDRESSES. Information not marked
confidential pursuant to 40 CFR part 2
may be disclosed publicly by EPA
without prior notice. Submit this copy,
identified by docket ID number EPA–
HQ–OPP–2005–0145, by one of the
following methods:
• Federal eRulemaking Portal: https://
www.regulations.gov. Follow the on-line
instructions for submitting comments.
• Mail: Office of Pesticide Programs
(OPP) Regulatory Public Docket (7502P),
Environmental Protection Agency, 1200
Pennsylvania Ave., NW., Washington,
DC 20460–0001.
• Delivery: OPP Regulatory Public
Docket (7502P), Environmental
Protection Agency, Rm. S–4400, One
Potomac Yard (South Bldg.), 2777 S.
Crystal Dr., Arlington, VA. Deliveries
are only accepted during the Docket’s
normal hours of operation (8:30 a.m. to
4 p.m., Monday through Friday,
excluding legal holidays). Special
arrangements should be made for
deliveries of boxed information. The
Docket Facility telephone number is
(703) 305–5805.
II. Petition for Tolerance
In the Federal Register of February
15, 2006 (71 FR 7951) (FRL–7759–3),
EPA issued a notice pursuant to section
408(d)(3) of FFDCA, 21 U.S.C.
346a(d)(3), announcing the filing of a
pesticide petition (PP 5F6986) by BASF,
26 Davis Drive, P.O. Box 13528,
Research Triangle Park, NC 27709. The
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petition requested that 40 CFR 180.589
be amended by increasing the tolerance
for residues of the fungicide boscalid in
or on berries, crop group 13 from 3.5 to
8.0 ppm; and increasing the tolerance
for strawberries from 1.2 ppm to 4.0
ppm. That notice referenced a summary
of the petition prepared by BASF, the
registrant, which is available to the
public in the docket, https://
www.regulations.gov.
On April 4, 2007, in the Federal
Register (72 FR 16352) (FRL–8119–2),
EPA issued a notice pursuant to section
408(d)(3) of FFDCA, 21 U.S.C.
346a(d)(3), announcing the filing of a
pesticide petition (PP 6E7164) by
Interregional Research Project Number 4
(IR-4), 500 College Road East, Suite 201
W, Princeton, NJ 08540, proposes to
establish a tolerance for residues of the
fungicide boscalid in or on food
commodities avocado at 1.5 ppm;
sapote, black at 1.5 ppm; canistel at 1.5
ppm; sapote, mamey at 1.5 ppm; mango
at 1.5 ppm; papaya at 1.5 ppm; sapodilla
at 1.5 ppm; star apple at 1.5 ppm; and
herbs, fresh, subgroup 19A at 60.0 ppm.
Fresh herbs, subgroup 19A, tolerances
were subsequently withdrawn from this
petition, on February 6, 2008, by IR-4,
in accordance with 40 CFR 180.8. The
docket ID number EPA–HQ–OPP–2007–
0115, identifies this petition.
On June 27, 2007, EPA issued a notice
pertaining to boscalid announcing the
filing of a pesticide petition (PP
7F7169), (72 FR) (FRL–8133–4), by
BASF, 26 Davis Drive, P.O. Box 13528,
Research Triangle Park, NC 27709. The
petition, identified by the docket ID
number EPA–HQ–OPP–2007–0377,
requested that 40 CFR 180.589 amended
by increasing the tolerance for residues
of the fungicide boscalid in or on cotton,
undelinted seed at 1.0 ppm and cotton,
gin byproducts at 55.0 ppm. In the
Federal Register of February 13, 2008
(73 FR 7951) (FRL–7759–3), EPA issued
a notice pertaining to boscalid
announcing the filing of a pesticide
petition (PP 5F6986) by BASF. The
petition requested that 40 CFR 180.589
be amended by increasing the tolerance
for residues of the fungicide boscalid in
or on caneberry, crop group 13A at 6.0
ppm; bushberry, crop group 13B at 10.0
ppm; cucumber at 0.5 ppm; and
vegetable, root, subgroup 1A, except
sugar beet, garden beet, radish and
turnip at 1.0 ppm.
Each petition’s notice referenced a
summary of the petition prepared by the
registrant BASF, which is available to
the public in the docket, https://
www.regulations.gov. For the foregoing
petitions, there were no comments in
response to their notice of filing
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Based upon review of the data
supporting the petition, an increased
strawberry tolerance to 4.5 ppm is not
needed because EPA previously
increased the strawberry tolerance to 4.5
ppm via the rule published May 3, 2006
(71 FR 25956) (FRL–8064–4).
Furthermore, whereas the registrant
requested the tolerance for the entire
berry group 13 be increased from 3.5
ppm to 8.0 ppm, the Agency has
established a separate tolerance for each
of the two berry group 13 sub groups.
Thus, where there was one tolerance for
the entire group, there are now two
separate tolerances covering all crops in
the entire berry crop group 13. Thus, the
existing berries, group 13 tolerance is
being revoked because it is not needed.
BASF submitted field trial data on
cucumbers, mustard greens, and
sunflower. These field trials were
required as a condition for the
registration of boscalid on these crops.
BASF has also submitted supplemental
field trials on fruiting vegetables,
spearmint and peppermint, radishes,
stone fruits, and grapes, which were
conducted to support the use of boscalid
on these crops in Canada. Review of
these new data is the basis for the need
to increase the existing tolerances in or
on cucumber from 0.2 to 0.5 ppm, and
vegetable, root, subgroup 1A, except
sugarbeet, garden beet, radish, and
turnip from 0.7 to 1.0 ppm.
EPA is also establishing a timelimited tolerance for residues of the
fungicide boscalid in or on Endive,
Belgian at 16 ppm. This tolerance
expires and is revoked on December 31,
2009. The Agency is establishing this
time-limited tolerance in response to a
crisis exemption request under FIFRA
section 18 on behalf of the California
Environmental Protection Agency,
Department of Pesticide Regulation for
emergency use of boscalid as a post
harvest treatment on chicory roots to
control fungal growth of scelerotinia
sclerotiorum.
According to the applicant, the
dormant chicory roots are taken out of
cold storage and propagated in sheds
within a controlled environment to
stimulate bud development. These
edible buds are known as belgian
endive, and are marketed in grocery
stores throughout the year. Based on
information provided in the submission,
an emergency situation exists because
the pathogen, scelerotinia sclerotiorum,
resides in field soils and can grow on
the chicory root during cold storage,
which makes the produce unmarketable.
Vinclozolin had been registered for
control of this pest until it was
cancelled in 2001. Existing stocks of
vinclozolin were used until 2003, and
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there are currently no other fungicides
registered for the post harvest treatment
of chicory root to control fungal growth.
Further, the State claims that good
agricultural practices are not sufficient
to control this fungal pathogen.
As part of its assessment of the
emergency exemption request, EPA
assessed the potential risks presented by
the residues of boscalid in or on endive,
belgian, as discussed below. In doing so,
EPA considered the safety standard in
section 408 (b) (2) of the FFDCA, and
EPA decided that the necessary timelimited tolerance under section 408 (l)
(6) of the FFDCA would be consistent
with the safety standard and with
FIFRA section 18. Consistent with the
need to move quickly on the emergency
exemption in order to address the
urgent non-routine situation and to
ensure that the resulting food is safe and
lawful, EPA is issuing this time-limited
tolerance without notice and
opportunity for public comment as
provided in section 408 (l) (6) of the
FFDCA. Although, this time-limited
tolerance expires and is revoked on
December 31, 2009, under section 408
(l) (5) of the FFDCA, residues of the
pesticide not in excess of the amount
specified in the tolerance remaining in
or on endive, belgian after that date will
not be unlawful, provided the pesticide
is applied in a manner that was lawful
under FIFRA, and the residues do not
exceed a level that was authorized by
this time-limited tolerance at the time of
application. EPA will take action to
revoke this time-limited tolerance
earlier if any experience with, scientific
data, or other relevant information on
this pesticide indicates that the residues
are not safe.
Because this time-limited tolerance is
being approved under emergency
conditions, EPA has not made any
decisions about whether boscalid meets
EPA’s registration requirements for use
on endive, belgian or whether a
permanent tolerance for this use would
be appropriate. Under this
circumstance, EPA does not believe that
the time-limited tolerance serves as a
basis for registration of boscalid by a
State for special local needs under
FIFRA section 24(c). Nor does the timelimited tolerance serve as the basis for
any State other than California to use
this pesticide on this crop under section
18 of FIFRA without following all
provisions of EPA’s regulations
implementing FIFRA section 18 as
identified in 40 CFR part 166.
III. Aggregate Risk Assessment and
Determination of Safety
Section 408(b)(2)(A)(i) of FFDCA
allows EPA to establish a tolerance (the
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16555
legal limit for a pesticide chemical
residue in or on a food) only if EPA
determines that the tolerance is ‘‘safe.’’
Section 408(b)(2)(A)(ii) of FFDCA
defines ‘‘safe’’ to mean that ‘‘there is a
reasonable certainty that no harm will
result from aggregate exposure to the
pesticide chemical residue, including
all anticipated dietary exposures and all
other exposures for which there is
reliable information.’’ This includes
exposure through drinking water and in
residential settings, but does not include
occupational exposure. Section
408(b)(2)(C) of FFDCA requires EPA to
give special consideration to exposure
of infants and children to the pesticide
chemical residue in establishing a
tolerance and to ‘‘ensure that there is a
reasonable certainty that no harm will
result to infants and children from
aggregate exposure to the pesticide
chemical residue. * * * ’’ These
provisions were added to FFDCA by the
Food Quality Protection Act (FQPA) of
1996.
Consistent with FFDCA section 408(b)
(2) (D) and the factors specified in
FFDCA section 408(b) (2) (D), EPA has
reviewed the available scientific data
and other relevant information in
support of this action. EPA has
sufficient data to assess the hazards of
and to make a determination on
aggregate exposure for the petitioned-for
tolerances for residues of boscalid on
caneberry subgroup 13A, and bushberry
subgroup 13B, respectively at 6.0 and 13
ppm; cotton, undelinted seed at 1.0
ppm; cotton, gin byproducts at 55 ppm;
avocado at 1.5 ppm; sapote, black at 1.5
ppm; canistel at 1.5 ppm; sapote,
mamey at 1.5 ppm; mango at 1.5 ppm;
papaya at 1.5 ppm; sapodilla at 1.5 ppm;
star apple at 1.5 ppm; cucumber at 0.5
ppm; and vegetable, root, subgroup 1A,
except sugar beet, garden beet, radish
and turnip at 1.0 ppm, as well as the
time-limited tolerance for residues of
boscalid in or on endive, belgian at 16
ppm. EPA’s assessment of exposures
and risks associated with establishing
these tolerances follows.
A. Toxicological Profile
EPA has evaluated the available
toxicity data and considered its validity,
completeness, and reliability as well as
the relationship of the results of the
studies to human risk. EPA has also
considered available information
concerning the variability of the
sensitivities of major identifiable
subgroups of consumers, including
infants and children.
Animal studies indicate that repeat
dosing with boscalid results in effects in
the liver and/or thyroid in various
species. Mechanistic studies indicated
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that the thyroid effects were derivative
of enzymatic effects on the liver. The
boscalid database shows no effects that
were attributable to a single dose, and
thus boscalid is deemed not to pose an
acute risk. Testing involving in utero
and/or post-natal exposure of animals
shows no developmental or
reproductive effects; however, this
testing resulted in some findings of
qualitative or quantitative sensitivity
with regard to body weight effects in the
young.
The Agency determined that boscalid
shows suggestive evidence of
carcinogenicity. This finding is based on
the following weight of evidence
considerations. First, in male wistar
rats, there was a significant trend (but
not pairwise comparison) for the
combined thyroid adenomas and
carcinomas. This trend is driven by the
increase in adenomas. Second, in the
female rats, there was only a borderline
significant trend for thyroid adenomas
(there were no carcinomas). Third, the
mouse study was negative as were all of
the mutagenic tests. Consistent with this
weak evidence of carcinogenic effects,
the Agency concluded that a
quantitative risk and exposure
assessment for cancer (either linear lowdose extrapolation or margin of
exposure calculation) was not
appropriate.
Specific information on the studies
received and the nature of the adverse
effects caused by boscalid as well as the
no-observed-adverse-effect-level
(NOAEL) and the lowest-observedadverse-effect-level (LOAEL) from the
toxicity studies can be found at https://
www.regulations.gov. The referenced
documents are available in the docket
established by this action, which are
described under ADDRESSES, and are
identified as follows:
•Boscalid: Human Health Risk
Assessment for Section 3 Tolerance on
Endive, an Amendment to the
Tolerances for Strawberries and Berries,
Crop Group 13, and an Increase in
Tolerances in/on Cucumber and
Vegetable, Root, Subgroup 1A, except
Sugar Beet, Garden Beet, Radish, and
Turnip, dated 7-10-07.
• Boscalid: Addendum to the July 10,
2007 Human Risk Assessment to
Support a Section 3 Use on Endive, an
Amendment to the Tolerances for
Strawberries and Berries, Crop Group
13, and an Increase in Tolerances in/on
Cucumber and Vegetable, Root,
Subgroup 1A, except Sugar Beet, Garden
Beet, Radish, and Turnip.PC Code:
128008, Petition Nos: 5E7013, 5F6986,
DP Barcode: 34857, dated 2-13-08.
• Boscalid: Human Health Risk
Assessment to Support Proposed New
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Uses on Fresh Herbs (Herbs Subgroup
19A), Avocado, Black Sapote, Canistel,
Mamey Sapote, Mango, Papaya,
Sapodilla, Star Apple and Cotton. PC
Code: 128008; Petition Nos: 6E7164,
7F7169; DP Barcodes: 336182, 337369,
dated 2-13-08.
B. Toxicological Endpoints
For hazards that have a threshold
below which there is no appreciable
risk, the toxicological level of concern
(LOC) is derived from the highest dose
at which no adverse effects are observed
(the NOAEL) in the toxicology study
identified as appropriate for use in risk
assessment. However, if a NOAEL
cannot be determined, the lowest dose
at which adverse effects of concern are
identified (the LOAEL) is sometimes
used for risk assessment. Uncertainty/
safety factors (UFs) are used in
conjunction with the LOC to take into
account uncertainties inherent in the
extrapolation from laboratory animal
data to humans and in the variations in
sensitivity among members of the
human population as well as other
unknowns. Safety is assessed for acute
and chronic risks by comparing
aggregate exposure to the pesticide to
the acute population adjusted dose
(aPAD) and chronic population adjusted
dose (cPAD). The aPAD and cPAD are
calculated by dividing the LOC by all
applicable UFs. Short-term,
intermediate-term, and long-term risks
are evaluated by comparing aggregate
exposure to the LOC to ensure that the
margin of exposure (MOE) called for by
the product of all applicable UFs is not
exceeded.
For non-threshold risks, the Agency
assumes that any amount of exposure
will lead to some degree of risk and
estimates risk in terms of the probability
of occurrence of additional adverse
cases. Generally, cancer risks are
considered non-threshold. For more
information on the general principles
EPA uses in risk characterization and a
complete description of the risk
assessment process, see:
https://www.epa.gov/oppfead1/trac/
science
https://www.epa.gov/pesticides/
factsheets/riskassess.htm
https://www.epa.gov/pesticides/trac/
science/ aggregate.pdf
A summary of the toxicological
endpoints for boscalid used for human
risk assessment is discussed in Unit
III.B of the final boscalid rule published
in the Federal Register of July 30, 2003
(68 FR 44640) (FRL–7319–6).
C. Exposure Assessment
1. Dietary exposure from food and
feed uses. In evaluating dietary
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exposure to boscalid tolerances in (40
CFR 180.589), EPA assessed dietary
exposures from boscalid in food as
follows:
i. Acute exposure. There are no toxic
effects attributable to a single (acute)
exposure to boscalid; therefore an acute
reference dose was not established for
boscalid and an acute dietary exposure
assessment is not needed.
ii. Chronic exposure. In conducting
the chronic dietary exposure assessment
EPA used the food consumption data
from the United States Department of
Agriculture (USDA) Continuing Survey
of Food Intake by Individuals (CSFII)
1994–1996 and 1998. As to residue
levels in food, EPA assumed all foods
for which there are tolerances were
treated and contain tolerance-level
residues. The Agency did not use
anticipated residue estimates or percent
crop treated (PCT) information.
iii. Cancer. For the reasons described
in Unit III.A, the Agency concluded that
a quantitative risk and exposure
assessment for cancer (either linear lowdose extrapolation or margin of
exposure calculation) was not
appropriate.
2. Dietary exposure from drinking
water. The Agency lacks sufficient
monitoring data to complete a
comprehensive dietary exposure
analysis and risk assessment for
boscalid in drinking water. Because the
Agency does not have comprehensive
monitoring data, drinking water
concentration estimates are made by
reliance on simulation or modeling
taking into account data on the
environmental fate characteristics of
boscalid. Further information regarding
EPA drinking water models used in
pesticide exposure assessment can be
found at https://www.epa.gov/oppefed1/
models/water/index.htm.
Based on the FQPA Index Reservoir
Screening Tool (FIRST) and Screening
Concentration in Ground Water (SCIGROW) models, the maximum
estimated surface and ground drinking
water concentrations (EDWCs) of
boscalid for chronic exposures are 29.6
parts per billion (PPB) for surface water
and 0.63 ppb for ground water. Modeled
estimates of drinking water
concentrations were directly entered
into the dietary exposure model. The
chronic dietary risk assessment used the
surface water concentration value of
29.6 ppb to assess the contribution to
drinking water.
3. From non-dietary exposure. The
term ‘‘residential exposure’’ is used in
this document to refer to nonoccupational, non-dietary exposure
(e.g., for lawn and garden pest control,
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indoor pest control, termiticides, and
flea and tick control on pets).
Boscalid is registered for use on sites
that would result in residential
exposure. From boscalid, residential
exposure is only possible on golf
courses and at ‘‘U-Pick’’ farms and
orchards. A non-occupational dermal
post-application exposure/risk
assessment for these exposures was
conducted in the previous occupational
and residential exposure assessment
and is described in the final rule in the
Federal Register of July 30, 2003 (68 FR
44640) (FRL–7319–6).
4. Cumulative effects from substances
with a common mechanism of toxicity.
Section 408(b)(2)(D)(v) of FFDCA
requires that, when considering whether
to establish, modify, or revoke a
tolerance, the Agency consider
‘‘available information’’ concerning the
cumulative effects of a particular
pesticide’s residues and ‘‘other
substances that have a common
mechanism of toxicity.’’
Unlike other pesticides for which EPA
has followed a cumulative risk approach
based on a common mechanism of
toxicity, EPA has not made a common
mechanism of toxicity finding as to
boscalid and any other substances and
boscalid does not appear to produce a
toxic metabolite produced by other
substances. For the purposes of this
tolerance action, therefore, EPA has not
assumed that boscalid has a common
mechanism of toxicity with other
substances. For information regarding
EPA’s efforts to determine which
chemicals have a common mechanism
of toxicity and to evaluate the
cumulative effects of such chemicals,
see EPA’s website at https://
www.epa.gov/pesticides/cumulative.
D. Safety Factor for Infants and
Children
1. In general. Section 408 of FFDCA
provides that EPA shall apply an
additional (‘‘10X’’) tenfold margin of
safety for infants and children in the
case of threshold effects to account for
prenatal and postnatal toxicity and the
completeness of the database on toxicity
and exposure unless EPA determines
based on reliable data that a different
margin of safety will be safe for infants
and children. This additional margin of
safety is commonly referred to as the
FQPA safety factor. In applying this
provision, EPA either retains the default
value of 10X when reliable data do not
support the choice of a different factor,
or, if reliable data are available, EPA
uses a different additional FQPA safety
factor value based on the use of
traditional UFs and/or special FQPA
safety factors, as appropriate.
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2. Prenatal and postnatal sensitivity.
In the 2-generation reproduction study
in rats, body weight effects were seen in
the mid and high doses in the second
generation male pups. However, the
degree of concern is low for the
quantitative evidence of susceptibility
seen in this study, since the body
weight effects were seen in only one sex
and only after dosing for two
generations. There is a clear NOAEL for
the body weight effects seen in the rat
2-generation reproduction study and
EPA is regulating based on a point of
departure below where these effects are
seen.
In the developmental neurotoxicity
study, transient body weight effects
were seen in one sex at post-natal days
1–4 with the animals recovering by
post-natal day 11. Body weight effects
were also seen in the high dose, which
was the limit dose. The degree of
concern for these effects are low since
the effects are either transient in nature
or occurred at the limit dose and EPA
is regulating based on a point of
departure below where these effects are
seen.
While qualitative sensitivity was seen
in the rabbit developmental study, the
fetal effects were seen only at the limit
dose in the presence of maternal
toxicity. Further, since EPA is regulating
based on a point of departure which is
an order of magnitude below where
these effects are seen in the rabbit
developmental study, EPA concludes
that the qualitative sensitivity
evidenced in the fetuses in the rabbit
developmental study does not require
retention of the 10X children’s safety
factor.
3. Conclusion. The FQPA safety factor
has been reduced to 1X for boscalid for
the following reasons. First, EPA has a
complete toxicity database for boscalid.
The toxicity studies for boscalid show it
generally to have low mammalian
toxicity. Further, while data involving
the testing of young animals did show
increased quantitative sensitivity in the
young with regard to body weight
effects and qualitative sensitivity in one
developmental study, clear NOAELs
were identified for all of these effects.
Moreover, the body weight effects at the
LOAELs in these studies were either
transient or inconsistent and qualitative
sensitivity occurred at the limit dose in
the presence of maternal toxicity. EPA
concludes that there are no residual
uncertainties for pre-natal and/or postnatal toxicity. The NOAEL used for
various risk assessments would address
the body weight effects seen at higher
doses in the developmental and
reproductive studies. Finally, EPA has
conservatively estimated human
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16557
exposure to boscalid, relying on worst
case exposures in food (assuming all
registered crops contain residues at the
tolerance level), and conservative
models as well as pesticide-specific data
in estimating exposure from residues in
drinking water and from residential
uses.
E. Aggregate Risks and Determination of
Safety
Safety is assessed for acute and
chronic risks by comparing aggregate
exposure to the pesticide to the aPAD
and cPAD. The aPAD and cPAD are
calculated by dividing the LOC by all
applicable UFs. For linear cancer risks,
EPA calculates the probability of
additional cancer cases given aggregate
exposure. Short-term, intermediateterm, and long-term risks are evaluated
by comparing aggregate exposure to the
LOC to ensure that the MOE called for
by the product of all applicable UFs is
not exceeded.
1. Acute risk. There were no toxic
effects attributable to a single exposure
to boscalid, therefore, neither an acute
reference dose (aRfD) nor aPAD were
established and acute dietary risk
assessment and acute aggregate risk
assessment are not required for boscalid.
2. Chronic risk. The unrefined chronic
dietary risk assessment for boscalid was
made using tolerance level residues,
default and empirical processing factors
and 100% CT assumptions. Results of
this analysis indicate that chronic risk
from the dietary (food + drinking water)
exposure from boscalid will not exceed
EPA’s level of concern for the general
U.S. population, and all population
subgroups. The chronic dietary risk
estimate for the highest reported
exposed population subgroup, children
1-2 years old, is 33% of the cPAD.
Chronic residential exposure from
residues of boscalid is not expected;
therefore the aggregate chronic risk is
equivalent to the chronic dietary risk
described above.
3. Short-term risk. Short-term
aggregate exposure takes into account
residential exposure plus average
exposure to food and water (considered
to be a background exposure level).
Boscalid is currently registered for
uses that could result in short-term
residential exposure and the Agency has
determined that it is appropriate to
aggregate average food and water
exposures with short-term nonoccupational exposures for boscalid.
Using the exposure assumptions
described in this unit for short-term
exposures, EPA has concluded that
food, water, and residential exposures
aggregated result in aggregate MOEs,
which are below the Agency’s level of
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concern. MOEs for the U.S. population,
and all subpopulations of concern
exceed 1,000. The level of concern for
this assessment is for MOEs below 100.
4. Intermediate-term risk.
Intermediate-term aggregate exposure
takes into account residential exposure
plus chronic exposure to food and water
(considered to be a background
exposure level). Because no
intermediate term, non-occupational
exposures are anticipated from the use
of boscalid, an intermediate-term
aggregate risk assessment is not required
for boscalid.
5. Aggregate cancer risk for U.S.
population. Given the data showing no
more than weak evidence of
carcinogenic effects for boscalid, EPA
concludes that boscalid poses no greater
than a negligible risk of cancer.
6. Determination of safety. Based on
these risk assessments, EPA concludes
that there is a reasonable certainty that
no harm will result to the general
population, or to infants and children
from aggregate exposure to boscalid
residues.
IV. Other Considerations
A. Analytical Enforcement Methodology
Adequate enforcement methodology
(gas chromatographic with mass
spectrometric detection) is available to
enforce the tolerance expression. The
method may be requested from: Chief,
Analytical Chemistry Branch,
Environmental Science Center, 701
Mapes Rd., Ft. Meade, MD 20755–5350;
telephone number: (410) 305–2905; email address: residuemethods@epa.gov.
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B. International Residue Limits
There are currently no Codex
Maximum Residue Limits (MRLs) for
boscalid. Canada has established MRLs
for boscalid, but not for the crops that
are in this rule.
V. Conclusion
Therefore, this regulation establishes
tolerances for residues of boscalid,3pyridinecarboxamide, 2-chloro-N-(4’chloro[1,1’-biphenyl]-2-yl), in or on
caneberry subgroup 13A, and bushberry
subgroup 13B, respectively at 6.0 and 13
ppm; cotton, undelinted seed at 1.0
ppm; cotton, gin byproducts at 55 ppm;
avocado at 1.5 ppm; sapote, black at 1.5
ppm; canistel at 1.5 ppm; sapote,
mamey at 1.5 ppm; mango at 1.5 ppm;
papaya at 1.5 ppm; sapodilla at 1.5 ppm;
star apple at 1.5 ppm; cucumber at 0.5
ppm; and vegetable, root, subgroup 1A,
except sugar beet, garden beet, radish
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and turnip at 1.0 ppm. In addition, this
regulation establishes a time-limited
tolerance for residues of boscalid in or
on endive, belgian at 16 ppm.
VI. Statutory and Executive Order
Reviews
This final rule establishes a tolerance
under section 408(d) of FFDCA in
response to a petition submitted to the
Agency. The Office of Management and
Budget (OMB) has exempted these types
of actions from review under Executive
Order 12866, entitled Regulatory
Planning and Review (58 FR 51735,
October 4, 1993). Because this rule has
been exempted from review under
Executive Order 12866, this rule is not
subject to Executive Order 13211,
Actions Concerning Regulations That
Significantly Affect Energy Supply,
Distribution, or Use (66 FR 28355, May
22, 2001) or Executive Order 13045,
entitled Protection of Children from
Environmental Health Risks and Safety
Risks (62 FR 19885, April 23, 1997).
This final rule does not contain any
information collections subject to OMB
approval under the Paperwork
Reduction Act (PRA), 44 U.S.C. 3501 et
seq., nor does it require any special
considerations under Executive Order
12898, entitled Federal Actions to
Address Environmental Justice in
Minority Populations and Low-Income
Populations (59 FR 7629, February 16,
1994). Since tolerances and exemptions
that are established on the basis of a
petition under section 408(d) of FFDCA,
such as the tolerance in this final rule,
do not require the issuance of a
proposed rule, the requirements of the
Regulatory Flexibility Act (RFA) (5
U.S.C. 601 et seq.) do not apply.
This final rule directly regulates
growers, food processors, food handlers,
and food retailers, not States or tribes,
nor does this action alter the
relationships or distribution of power
and responsibilities established by
Congress in the preemption provisions
of section 408(n)(4) of FFDCA. As such,
the Agency has determined that this
action will not have a substantial direct
effect on States or tribal governments,
on the relationship between the national
government and the States or tribal
governments, or on the distribution of
power and responsibilities among the
various levels of government or between
the Federal Government and Indian
tribes. Thus, the Agency has determined
that Executive Order 13132, entitled
Federalism (64 FR 43255, August 10,
1999) and Executive Order 13175,
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Fmt 4700
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entitled Consultation and Coordination
with Indian Tribal Governments (65 FR
67249, November 6, 2000) do not apply
to this rule. In addition, This rule does
not impose any enforceable duty or
contain any unfunded mandate as
described under Title II of the Unfunded
Mandates Reform Act of 1995 (UMRA)
(Public Law 104–4). This action does
not involve any technical standards that
would require Agency consideration of
voluntary consensus standards pursuant
to section 12(d) of the National
Technology Transfer and Advancement
Act of 1995 (NTTAA), Public Law 104–
113, section 12(d) (15 U.S.C. 272 note).
VII. Congressional Review Act
The Congressional Review Act, 5
U.S.C. 801 et seq., generally provides
that before a rule may take effect, the
agency promulgating the rule must
submit a rule report to each House of
the Congress and to the Comptroller
General of the United States. EPA will
submit a report containing this rule and
other required information to the U.S.
Senate, the U.S. House of
Representatives, and the Comptroller
General of the United States prior to
publication of this final rule in the
Federal Register. This final rule is not
a ‘‘major rule’’ as defined by 5 U.S.C.
804(2).
List of Subjects in 40 CFR Part 180
Environmental protection,
Administrative practice and procedure,
Agricultural commodities, Pesticides
and pests, Reporting and recordkeeping
requirements.
Dated: March 18, 2008.
Lois Rossi,
Director, Registration Division, Office of
Pesticide Programs.
Therefore, 40 CFR chapter I is
amended as follows:
I
PART 180—[AMENDED]
1. The authority citation for part 180
continues to read as follows:
I
Authority: 21 U.S.C. 321(q), 346a and 371.
2. Section 180.589 is amended by
removing the entry for berry group 13,
and alphabetically adding the following
commodities to the table in paragraph
(a)(1), and by revising paragraph (b) to
read as follows:
I
§ 180.589
Boscalid; tolerance for residues.
(a) * * *
(1) * * *
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Commodity
Parts per million
*
*
*
*
*
Avocado .......................................................................................................................................
Bushberry, subgroup 13B ............................................................................................................
Caneberry, subgroup13A .............................................................................................................
Canistel ........................................................................................................................................
*
*
*
*
*
Cotton, gin byproducts .................................................................................................................
Cotton, undelinted seed ...............................................................................................................
Cucumber ....................................................................................................................................
*
*
*
*
*
Mango ..........................................................................................................................................
*
*
*
*
*
Papya ...........................................................................................................................................
Sapodilla ......................................................................................................................................
Sapote, black ...............................................................................................................................
Sapote, mamey ............................................................................................................................
Star Apple ....................................................................................................................................
*
*
*
*
*
Vegetable, root, subgroup 1A, except sugarbeet, garden beet, radish, and turnip
*
*
*
*
*
*
*
*
*
*
(b) Section 18 emergency exemptions.
A time-limited tolerance is established
for the residues of the fungicide
Commodity
boscalid, 2-chloro-N-(4’-chloro [1, 1’biphenyl]-2-yl)-3-pyridinecarboxamide
in connection with use of the pesticide
under a section 18 emergency
Parts per million
*
*
*
*
1.5
1.5
1.5
1.5
1.5
1.0
exemption granted by EPA. This
tolerance will expire and is revoked on
the date specified in the following table.
12/31/09
12/31/08
permissible level for residues of SAbscisic Acid, (S)-5-(1-hydroxy-2,6,6trimethyl-4-oxo-1-cyclohex-2-enyl)-3methyl-penta-(2Z,4E)-dienoic Acid. The
temporary tolerance exemption expires
on October 1, 2010.
BILLING CODE 6560–50–S
ENVIRONMENTAL PROTECTION
AGENCY
AGENCY:
This regulation is effective
March 28, 2008. Objections and requests
for hearings must be received on or
before May 27, 2008, and must be filed
in accordance with the instructions
provided in 40 CFR part 178 (see also
Unit I.C. of the SUPPLEMENTARY
INFORMATION).
SUMMARY: This regulation establishes a
temporary exemption from the
requirement of a tolerance for residues
of the biochemical pesticide S-Abscisic
Acid, (S)-5-(1-hydroxy-2,6,6-trimethyl4-oxo-1-cyclohex-2-enyl)-3-methylpenta-(2Z,4E)-dienoic Acid in or on
grapes when applied or used as a plant
regulator in accordance with the terms
of Experimental Use Permit 73049-EUP4. Valent Biosciences Corporation
submitted a petition to EPA under the
Federal Food, Drug, and Cosmetic Act
(FFDCA), as amended by the Food
Quality Protection Act of 1996 (FQPA),
requesting the temporary tolerance
exemption. This regulation eliminates
the need to establish a maximum
EPA has established a
docket for this action under docket
identification (ID) number EPA–HQ–
OPP–2008–0092. To access the
electronic docket, go to https://
www.regulations.gov, select ‘‘Advanced
Search,’’ then ‘‘Docket Search.’’ Insert
the docket ID number where indicated
and select the ‘‘Submit’’ button. Follow
the instructions on the regulations.gov
website to view the docket index or
access available documents. All
documents in the docket are listed in
the docket index available in
regulations.gov. Although listed in the
index, some information is not publicly
available, e.g., Confidential Business
Information (CBI) or other information
whose disclosure is restricted by statute.
Certain other material, such as
DATES:
40 CFR Part 180
[EPA–HQ–OPP–2008–0092; FRL–8357–4]
S-Abscisic Acid, Temporary Exemption
From the Requirement of a Tolerance
Environmental Protection
Agency (EPA).
ACTION: Final rule.
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1.5
16
2.0
[FR Doc. E8–6264 Filed 3–27–08; 8:45 am]
VerDate Aug<31>2005
55.0
1.0
0.5
Expiration/Revocation Date
Endive, Belgian
Tangerine
*
1.5
13.0
6.0
1.5
16:25 Mar 27, 2008
Jkt 214001
ADDRESSES:
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copyrighted material, is not placed on
the Internet and will be publicly
available only in hard copy form.
Publicly available docket materials are
available in the electronic docket at
https://www.regulations.gov, or, if only
available in hard copy, at the OPP
Regulatory Public Docket in Rm. S–
4400, One Potomac Yard (South Bldg.),
2777 S. Crystal Dr., Arlington, VA. The
Docket Facility is open from 8:30 a.m.
to 4 p.m., Monday through Friday,
excluding legal holidays. The Docket
Facility telephone number is (703) 305–
5805.
FOR FURTHER INFORMATION CONTACT:
Chris Pfeifer, Biopesticides and
Pollution Prevention Division (7511P),
Office of Pesticide Programs,
Environmental Protection Agency, 1200
Pennsylvania Ave., NW., Washington,
DC 20460–0001; telephone number:
703-308-0031; e-mail address:
pfeifer.chris@epa.gov.
SUPPLEMENTARY INFORMATION:
I. General Information
A. Does this Action Apply to Me?
You may be potentially affected by
this action if you are an agricultural
producer, food manufacturer, or
pesticide manufacturer. Potentially
affected entities may include, but are
not limited to:
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Agencies
[Federal Register Volume 73, Number 61 (Friday, March 28, 2008)]
[Rules and Regulations]
[Pages 16553-16559]
From the Federal Register Online via the Government Printing Office [www.gpo.gov]
[FR Doc No: E8-6264]
-----------------------------------------------------------------------
ENVIRONMENTAL PROTECTION AGENCY
40 CFR Part 180
[EPA-HQ-OPP-2005-0145; FRL-8354-4]
Boscalid; Pesticide Tolerance
AGENCY: Environmental Protection Agency (EPA).
ACTION: Final rule.
-----------------------------------------------------------------------
SUMMARY: This regulation establishes tolerances for residues of
boscalid in or on caneberry subgroup 13A at 6.0 parts per million
(ppm); bushberry subgroup 13B at 13 ppm; cotton, undelinted seed at 1.0
ppm; cotton, gin by-products at 55 ppm; avocado at 1.5 ppm; sapote,
black at 1.5 ppm; canistel at 1.5 ppm; sapote, mamey at 1.5 ppm; mango
at 1.5 ppm; papaya at 1.5 ppm; sapodilla at 1.5 ppm; and star apple at
1.5 ppm. It revokes the existing berries, group 13 tolerance at 3.5 ppm
because the two new caneberry and bushberry tolerances cover all
commodities in the berries, group 13. Tolerances are being increased
for cucumber from 0.20 ppm to 0.5 ppm, and vegetable, root, subgroup
1A, except sugarbeet, garden beet, radish, and turnip from 0.7 ppm to
1.0 ppm. BASF, Inc requested these tolerance actions under the Federal
Food, Drug, and Cosmetic Act (FFDCA). In addition, this action
establishes a time-limited tolerance for residues of boscalid in or on
Endive, Belgian, in response to the approval of a crisis exemption
under section 18 of the Federal Insecticide, Fungicide, and Rodenticide
Act (FIFRA) authorizing the post harvest use of the fungicide on
Endive, Belgian to control the fungal pathogen, scelerotinia
sclerotiorum. This regulation establishes a maximum permissible level
of residues of boscalid in this food commodity. The time-limited
tolerance expires and is revoked on December 31, 2009.
DATES: This regulation is effective March 28, 2008. Objections and
requests for hearings must be received on or before May 27, 2008, and
must be filed in accordance with the instructions provided in 40 CFR
part 178 (see also Unit I.C. of the SUPPLEMENTARY INFORMATION).
ADDRESSES: EPA has established a docket for this action under docket
identification (ID) number EPA-HQ-OPP-2005-0145. To access the
electronic docket, go to https://www.regulations.gov, select ``Advanced
Search,'' then ``Docket Search.'' Insert the docket ID number where
indicated and select the ``Submit'' button. Follow the instructions on
the regulations.gov website to view the docket index or access
available documents. All documents in the docket are listed in the
docket index available in regulations.gov. Although listed in the
index, some information is not publicly available, e.g., Confidential
Business Information (CBI) or other information whose disclosure is
restricted by statute. Certain other material, such as copyrighted
material, is not placed on the Internet and will be publicly available
only in hard copy form. Publicly available docket materials are
available in the electronic docket at https://www.regulations.gov, or,
if only available in hard copy, at the OPP Regulatory Public Docket in
Rm. S-
[[Page 16554]]
4400, One Potomac Yard (South Bldg.), 2777 S. Crystal Dr., Arlington,
VA. The Docket Facility is open from 8:30 a.m. to 4 p.m., Monday
through Friday, excluding legal holidays. The Docket Facility telephone
number is (703) 305-5805.
FOR FURTHER INFORMATION CONTACT: Bryant Crowe, Registration Division
(7505P), Office of Pesticide Programs, Environmental Protection Agency,
1200 Pennsylvania Ave., NW., Washington, DC 20460-0001; telephone
number: (703) 305-0025; e-mail address: crowe.bryant@epa.gov.
SUPPLEMENTARY INFORMATION:
I. General Information
A. Does this Action Apply to Me?
You may be potentially affected by this action if you are an
agricultural producer, food manufacturer, or pesticide manufacturer.
Potentially affected entities may include, but are not limited to those
engaged in the following activities:
Crop production (NAICS code 111), e.g., agricultural
workers; greenhouse, nursery, and floriculture workers; farmers.
Animal production (NAICS code 112), e.g., cattle ranchers
and farmers, dairy cattle farmers, livestock farmers.
Food manufacturing (NAICS code 311), e.g., agricultural
workers; farmers; greenhouse, nursery, and floriculture workers;
ranchers; pesticide applicators.
Pesticide manufacturing (NAICS code 32532), e.g.,
agricultural workers; commercial applicators; farmers; greenhouse,
nursery, and floriculture workers; residential users.
This listing is not intended to be exhaustive, but rather to
provide a guide for readers regarding entities likely to be affected by
this action. Other types of entities not listed in this unit could also
be affected. The North American Industrial Classification System
(NAICS) codes have been provided to assist you and others in
determining whether this action might apply to certain entities. If you
have any questions regarding the applicability of this action to a
particular entity, consult the person listed under FOR FURTHER
INFORMATION CONTACT.
B. How Can I Access Electronic Copies of this Document?
In addition to accessing an electronic copy of this Federal
Register document through the electronic docket at https://www.regulations.gov, you may access this Federal Register document
electronically through the EPA Internet under the ``Federal Register''
listings at https://www.epa.gov/fedrgstr. You may also access a
frequently updated electronic version of EPA's tolerance regulations at
40 CFR part 180 through the Government Printing Office's pilot e-CFR
site at https://www.gpoaccess.gov/ecfr.
C. Can I File an Objection or Hearing Request?
Under section 408(g) of FFDCA, any person may file an objection to
any aspect of this regulation and may also request a hearing on those
objections. You must file your objection or request a hearing on this
regulation in accordance with the instructions provided in 40 CFR part
178. To ensure proper receipt by EPA, you must identify docket ID
number EPA-HQ-OPP-2005-0145 in the subject line on the first page of
your submission. All requests must be in writing, and must be mailed or
delivered to the Hearing Clerk as required by 40 CFR part 178 on or
before May 27, 2008.
In addition to filing an objection or hearing request with the
Hearing Clerk as described in 40 CFR part 178, please submit a copy of
the filing that does not contain any CBI for inclusion in the public
docket that is described in ADDRESSES. Information not marked
confidential pursuant to 40 CFR part 2 may be disclosed publicly by EPA
without prior notice. Submit this copy, identified by docket ID number
EPA-HQ-OPP-2005-0145, by one of the following methods:
Federal eRulemaking Portal: https://www.regulations.gov.
Follow the on-line instructions for submitting comments.
Mail: Office of Pesticide Programs (OPP) Regulatory Public
Docket (7502P), Environmental Protection Agency, 1200 Pennsylvania
Ave., NW., Washington, DC 20460-0001.
Delivery: OPP Regulatory Public Docket (7502P),
Environmental Protection Agency, Rm. S-4400, One Potomac Yard (South
Bldg.), 2777 S. Crystal Dr., Arlington, VA. Deliveries are only
accepted during the Docket's normal hours of operation (8:30 a.m. to 4
p.m., Monday through Friday, excluding legal holidays). Special
arrangements should be made for deliveries of boxed information. The
Docket Facility telephone number is (703) 305-5805.
II. Petition for Tolerance
In the Federal Register of February 15, 2006 (71 FR 7951) (FRL-
7759-3), EPA issued a notice pursuant to section 408(d)(3) of FFDCA, 21
U.S.C. 346a(d)(3), announcing the filing of a pesticide petition (PP
5F6986) by BASF, 26 Davis Drive, P.O. Box 13528, Research Triangle
Park, NC 27709. The petition requested that 40 CFR 180.589 be amended
by increasing the tolerance for residues of the fungicide boscalid in
or on berries, crop group 13 from 3.5 to 8.0 ppm; and increasing the
tolerance for strawberries from 1.2 ppm to 4.0 ppm. That notice
referenced a summary of the petition prepared by BASF, the registrant,
which is available to the public in the docket, https://www.regulations.gov.
On April 4, 2007, in the Federal Register (72 FR 16352) (FRL-8119-
2), EPA issued a notice pursuant to section 408(d)(3) of FFDCA, 21
U.S.C. 346a(d)(3), announcing the filing of a pesticide petition (PP
6E7164) by Interregional Research Project Number 4 (IR-4), 500 College
Road East, Suite 201 W, Princeton, NJ 08540, proposes to establish a
tolerance for residues of the fungicide boscalid in or on food
commodities avocado at 1.5 ppm; sapote, black at 1.5 ppm; canistel at
1.5 ppm; sapote, mamey at 1.5 ppm; mango at 1.5 ppm; papaya at 1.5 ppm;
sapodilla at 1.5 ppm; star apple at 1.5 ppm; and herbs, fresh, subgroup
19A at 60.0 ppm. Fresh herbs, subgroup 19A, tolerances were
subsequently withdrawn from this petition, on February 6, 2008, by IR-
4, in accordance with 40 CFR 180.8. The docket ID number EPA-HQ-OPP-
2007-0115, identifies this petition.
On June 27, 2007, EPA issued a notice pertaining to boscalid
announcing the filing of a pesticide petition (PP 7F7169), (72 FR)
(FRL-8133-4), by BASF, 26 Davis Drive, P.O. Box 13528, Research
Triangle Park, NC 27709. The petition, identified by the docket ID
number EPA-HQ-OPP-2007-0377, requested that 40 CFR 180.589 amended by
increasing the tolerance for residues of the fungicide boscalid in or
on cotton, undelinted seed at 1.0 ppm and cotton, gin byproducts at
55.0 ppm. In the Federal Register of February 13, 2008 (73 FR 7951)
(FRL-7759-3), EPA issued a notice pertaining to boscalid announcing the
filing of a pesticide petition (PP 5F6986) by BASF. The petition
requested that 40 CFR 180.589 be amended by increasing the tolerance
for residues of the fungicide boscalid in or on caneberry, crop group
13A at 6.0 ppm; bushberry, crop group 13B at 10.0 ppm; cucumber at 0.5
ppm; and vegetable, root, subgroup 1A, except sugar beet, garden beet,
radish and turnip at 1.0 ppm.
Each petition's notice referenced a summary of the petition
prepared by the registrant BASF, which is available to the public in
the docket, https://www.regulations.gov. For the foregoing petitions,
there were no comments in response to their notice of filing
[[Page 16555]]
Based upon review of the data supporting the petition, an increased
strawberry tolerance to 4.5 ppm is not needed because EPA previously
increased the strawberry tolerance to 4.5 ppm via the rule published
May 3, 2006 (71 FR 25956) (FRL-8064-4). Furthermore, whereas the
registrant requested the tolerance for the entire berry group 13 be
increased from 3.5 ppm to 8.0 ppm, the Agency has established a
separate tolerance for each of the two berry group 13 sub groups. Thus,
where there was one tolerance for the entire group, there are now two
separate tolerances covering all crops in the entire berry crop group
13. Thus, the existing berries, group 13 tolerance is being revoked
because it is not needed.
BASF submitted field trial data on cucumbers, mustard greens, and
sunflower. These field trials were required as a condition for the
registration of boscalid on these crops. BASF has also submitted
supplemental field trials on fruiting vegetables, spearmint and
peppermint, radishes, stone fruits, and grapes, which were conducted to
support the use of boscalid on these crops in Canada. Review of these
new data is the basis for the need to increase the existing tolerances
in or on cucumber from 0.2 to 0.5 ppm, and vegetable, root, subgroup
1A, except sugarbeet, garden beet, radish, and turnip from 0.7 to 1.0
ppm.
EPA is also establishing a time-limited tolerance for residues of
the fungicide boscalid in or on Endive, Belgian at 16 ppm. This
tolerance expires and is revoked on December 31, 2009. The Agency is
establishing this time-limited tolerance in response to a crisis
exemption request under FIFRA section 18 on behalf of the California
Environmental Protection Agency, Department of Pesticide Regulation for
emergency use of boscalid as a post harvest treatment on chicory roots
to control fungal growth of scelerotinia sclerotiorum.
According to the applicant, the dormant chicory roots are taken out
of cold storage and propagated in sheds within a controlled environment
to stimulate bud development. These edible buds are known as belgian
endive, and are marketed in grocery stores throughout the year. Based
on information provided in the submission, an emergency situation
exists because the pathogen, scelerotinia sclerotiorum, resides in
field soils and can grow on the chicory root during cold storage, which
makes the produce unmarketable. Vinclozolin had been registered for
control of this pest until it was cancelled in 2001. Existing stocks of
vinclozolin were used until 2003, and there are currently no other
fungicides registered for the post harvest treatment of chicory root to
control fungal growth. Further, the State claims that good agricultural
practices are not sufficient to control this fungal pathogen.
As part of its assessment of the emergency exemption request, EPA
assessed the potential risks presented by the residues of boscalid in
or on endive, belgian, as discussed below. In doing so, EPA considered
the safety standard in section 408 (b) (2) of the FFDCA, and EPA
decided that the necessary time-limited tolerance under section 408 (l)
(6) of the FFDCA would be consistent with the safety standard and with
FIFRA section 18. Consistent with the need to move quickly on the
emergency exemption in order to address the urgent non-routine
situation and to ensure that the resulting food is safe and lawful, EPA
is issuing this time-limited tolerance without notice and opportunity
for public comment as provided in section 408 (l) (6) of the FFDCA.
Although, this time-limited tolerance expires and is revoked on
December 31, 2009, under section 408 (l) (5) of the FFDCA, residues of
the pesticide not in excess of the amount specified in the tolerance
remaining in or on endive, belgian after that date will not be
unlawful, provided the pesticide is applied in a manner that was lawful
under FIFRA, and the residues do not exceed a level that was authorized
by this time-limited tolerance at the time of application. EPA will
take action to revoke this time-limited tolerance earlier if any
experience with, scientific data, or other relevant information on this
pesticide indicates that the residues are not safe.
Because this time-limited tolerance is being approved under
emergency conditions, EPA has not made any decisions about whether
boscalid meets EPA's registration requirements for use on endive,
belgian or whether a permanent tolerance for this use would be
appropriate. Under this circumstance, EPA does not believe that the
time-limited tolerance serves as a basis for registration of boscalid
by a State for special local needs under FIFRA section 24(c). Nor does
the time-limited tolerance serve as the basis for any State other than
California to use this pesticide on this crop under section 18 of FIFRA
without following all provisions of EPA's regulations implementing
FIFRA section 18 as identified in 40 CFR part 166.
III. Aggregate Risk Assessment and Determination of Safety
Section 408(b)(2)(A)(i) of FFDCA allows EPA to establish a
tolerance (the legal limit for a pesticide chemical residue in or on a
food) only if EPA determines that the tolerance is ``safe.'' Section
408(b)(2)(A)(ii) of FFDCA defines ``safe'' to mean that ``there is a
reasonable certainty that no harm will result from aggregate exposure
to the pesticide chemical residue, including all anticipated dietary
exposures and all other exposures for which there is reliable
information.'' This includes exposure through drinking water and in
residential settings, but does not include occupational exposure.
Section 408(b)(2)(C) of FFDCA requires EPA to give special
consideration to exposure of infants and children to the pesticide
chemical residue in establishing a tolerance and to ``ensure that there
is a reasonable certainty that no harm will result to infants and
children from aggregate exposure to the pesticide chemical residue. * *
* '' These provisions were added to FFDCA by the Food Quality
Protection Act (FQPA) of 1996.
Consistent with FFDCA section 408(b) (2) (D) and the factors
specified in FFDCA section 408(b) (2) (D), EPA has reviewed the
available scientific data and other relevant information in support of
this action. EPA has sufficient data to assess the hazards of and to
make a determination on aggregate exposure for the petitioned-for
tolerances for residues of boscalid on caneberry subgroup 13A, and
bushberry subgroup 13B, respectively at 6.0 and 13 ppm; cotton,
undelinted seed at 1.0 ppm; cotton, gin byproducts at 55 ppm; avocado
at 1.5 ppm; sapote, black at 1.5 ppm; canistel at 1.5 ppm; sapote,
mamey at 1.5 ppm; mango at 1.5 ppm; papaya at 1.5 ppm; sapodilla at 1.5
ppm; star apple at 1.5 ppm; cucumber at 0.5 ppm; and vegetable, root,
subgroup 1A, except sugar beet, garden beet, radish and turnip at 1.0
ppm, as well as the time-limited tolerance for residues of boscalid in
or on endive, belgian at 16 ppm. EPA's assessment of exposures and
risks associated with establishing these tolerances follows.
A. Toxicological Profile
EPA has evaluated the available toxicity data and considered its
validity, completeness, and reliability as well as the relationship of
the results of the studies to human risk. EPA has also considered
available information concerning the variability of the sensitivities
of major identifiable subgroups of consumers, including infants and
children.
Animal studies indicate that repeat dosing with boscalid results in
effects in the liver and/or thyroid in various species. Mechanistic
studies indicated
[[Page 16556]]
that the thyroid effects were derivative of enzymatic effects on the
liver. The boscalid database shows no effects that were attributable to
a single dose, and thus boscalid is deemed not to pose an acute risk.
Testing involving in utero and/or post-natal exposure of animals shows
no developmental or reproductive effects; however, this testing
resulted in some findings of qualitative or quantitative sensitivity
with regard to body weight effects in the young.
The Agency determined that boscalid shows suggestive evidence of
carcinogenicity. This finding is based on the following weight of
evidence considerations. First, in male wistar rats, there was a
significant trend (but not pairwise comparison) for the combined
thyroid adenomas and carcinomas. This trend is driven by the increase
in adenomas. Second, in the female rats, there was only a borderline
significant trend for thyroid adenomas (there were no carcinomas).
Third, the mouse study was negative as were all of the mutagenic tests.
Consistent with this weak evidence of carcinogenic effects, the Agency
concluded that a quantitative risk and exposure assessment for cancer
(either linear low-dose extrapolation or margin of exposure
calculation) was not appropriate.
Specific information on the studies received and the nature of the
adverse effects caused by boscalid as well as the no-observed-adverse-
effect-level (NOAEL) and the lowest-observed-adverse-effect-level
(LOAEL) from the toxicity studies can be found at https://www.regulations.gov. The referenced documents are available in the
docket established by this action, which are described under ADDRESSES,
and are identified as follows:
Boscalid: Human Health Risk Assessment for Section 3
Tolerance on Endive, an Amendment to the Tolerances for Strawberries
and Berries, Crop Group 13, and an Increase in Tolerances in/on
Cucumber and Vegetable, Root, Subgroup 1A, except Sugar Beet, Garden
Beet, Radish, and Turnip, dated 7-10-07.
Boscalid: Addendum to the July 10, 2007 Human Risk
Assessment to Support a Section 3 Use on Endive, an Amendment to the
Tolerances for Strawberries and Berries, Crop Group 13, and an Increase
in Tolerances in/on Cucumber and Vegetable, Root, Subgroup 1A, except
Sugar Beet, Garden Beet, Radish, and Turnip.PC Code: 128008, Petition
Nos: 5E7013, 5F6986, DP Barcode: 34857, dated 2-13-08.
Boscalid: Human Health Risk Assessment to Support Proposed
New Uses on Fresh Herbs (Herbs Subgroup 19A), Avocado, Black Sapote,
Canistel, Mamey Sapote, Mango, Papaya, Sapodilla, Star Apple and
Cotton. PC Code: 128008; Petition Nos: 6E7164, 7F7169; DP Barcodes:
336182, 337369, dated 2-13-08.
B. Toxicological Endpoints
For hazards that have a threshold below which there is no
appreciable risk, the toxicological level of concern (LOC) is derived
from the highest dose at which no adverse effects are observed (the
NOAEL) in the toxicology study identified as appropriate for use in
risk assessment. However, if a NOAEL cannot be determined, the lowest
dose at which adverse effects of concern are identified (the LOAEL) is
sometimes used for risk assessment. Uncertainty/safety factors (UFs)
are used in conjunction with the LOC to take into account uncertainties
inherent in the extrapolation from laboratory animal data to humans and
in the variations in sensitivity among members of the human population
as well as other unknowns. Safety is assessed for acute and chronic
risks by comparing aggregate exposure to the pesticide to the acute
population adjusted dose (aPAD) and chronic population adjusted dose
(cPAD). The aPAD and cPAD are calculated by dividing the LOC by all
applicable UFs. Short-term, intermediate-term, and long-term risks are
evaluated by comparing aggregate exposure to the LOC to ensure that the
margin of exposure (MOE) called for by the product of all applicable
UFs is not exceeded.
For non-threshold risks, the Agency assumes that any amount of
exposure will lead to some degree of risk and estimates risk in terms
of the probability of occurrence of additional adverse cases.
Generally, cancer risks are considered non-threshold. For more
information on the general principles EPA uses in risk characterization
and a complete description of the risk assessment process, see:
https://www.epa.gov/oppfead1/trac/science
https://www.epa.gov/pesticides/factsheets/riskassess.htm
https://www.epa.gov/pesticides/trac/science/ aggregate.pdf
A summary of the toxicological endpoints for boscalid used for
human risk assessment is discussed in Unit III.B of the final boscalid
rule published in the Federal Register of July 30, 2003 (68 FR 44640)
(FRL-7319-6).
C. Exposure Assessment
1. Dietary exposure from food and feed uses. In evaluating dietary
exposure to boscalid tolerances in (40 CFR 180.589), EPA assessed
dietary exposures from boscalid in food as follows:
i. Acute exposure. There are no toxic effects attributable to a
single (acute) exposure to boscalid; therefore an acute reference dose
was not established for boscalid and an acute dietary exposure
assessment is not needed.
ii. Chronic exposure. In conducting the chronic dietary exposure
assessment EPA used the food consumption data from the United States
Department of Agriculture (USDA) Continuing Survey of Food Intake by
Individuals (CSFII) 1994-1996 and 1998. As to residue levels in food,
EPA assumed all foods for which there are tolerances were treated and
contain tolerance-level residues. The Agency did not use anticipated
residue estimates or percent crop treated (PCT) information.
iii. Cancer. For the reasons described in Unit III.A, the Agency
concluded that a quantitative risk and exposure assessment for cancer
(either linear low-dose extrapolation or margin of exposure
calculation) was not appropriate.
2. Dietary exposure from drinking water. The Agency lacks
sufficient monitoring data to complete a comprehensive dietary exposure
analysis and risk assessment for boscalid in drinking water. Because
the Agency does not have comprehensive monitoring data, drinking water
concentration estimates are made by reliance on simulation or modeling
taking into account data on the environmental fate characteristics of
boscalid. Further information regarding EPA drinking water models used
in pesticide exposure assessment can be found at https://www.epa.gov/oppefed1/models/water/index.htm.
Based on the FQPA Index Reservoir Screening Tool (FIRST) and
Screening Concentration in Ground Water (SCI-GROW) models, the maximum
estimated surface and ground drinking water concentrations (EDWCs) of
boscalid for chronic exposures are 29.6 parts per billion (PPB) for
surface water and 0.63 ppb for ground water. Modeled estimates of
drinking water concentrations were directly entered into the dietary
exposure model. The chronic dietary risk assessment used the surface
water concentration value of 29.6 ppb to assess the contribution to
drinking water.
3. From non-dietary exposure. The term ``residential exposure'' is
used in this document to refer to non-occupational, non-dietary
exposure (e.g., for lawn and garden pest control,
[[Page 16557]]
indoor pest control, termiticides, and flea and tick control on pets).
Boscalid is registered for use on sites that would result in
residential exposure. From boscalid, residential exposure is only
possible on golf courses and at ``U-Pick'' farms and orchards. A non-
occupational dermal post-application exposure/risk assessment for these
exposures was conducted in the previous occupational and residential
exposure assessment and is described in the final rule in the Federal
Register of July 30, 2003 (68 FR 44640) (FRL-7319-6).
4. Cumulative effects from substances with a common mechanism of
toxicity. Section 408(b)(2)(D)(v) of FFDCA requires that, when
considering whether to establish, modify, or revoke a tolerance, the
Agency consider ``available information'' concerning the cumulative
effects of a particular pesticide's residues and ``other substances
that have a common mechanism of toxicity.''
Unlike other pesticides for which EPA has followed a cumulative
risk approach based on a common mechanism of toxicity, EPA has not made
a common mechanism of toxicity finding as to boscalid and any other
substances and boscalid does not appear to produce a toxic metabolite
produced by other substances. For the purposes of this tolerance
action, therefore, EPA has not assumed that boscalid has a common
mechanism of toxicity with other substances. For information regarding
EPA's efforts to determine which chemicals have a common mechanism of
toxicity and to evaluate the cumulative effects of such chemicals, see
EPA's website at https://www.epa.gov/pesticides/cumulative.
D. Safety Factor for Infants and Children
1. In general. Section 408 of FFDCA provides that EPA shall apply
an additional (``10X'') tenfold margin of safety for infants and
children in the case of threshold effects to account for prenatal and
postnatal toxicity and the completeness of the database on toxicity and
exposure unless EPA determines based on reliable data that a different
margin of safety will be safe for infants and children. This additional
margin of safety is commonly referred to as the FQPA safety factor. In
applying this provision, EPA either retains the default value of 10X
when reliable data do not support the choice of a different factor, or,
if reliable data are available, EPA uses a different additional FQPA
safety factor value based on the use of traditional UFs and/or special
FQPA safety factors, as appropriate.
2. Prenatal and postnatal sensitivity. In the 2-generation
reproduction study in rats, body weight effects were seen in the mid
and high doses in the second generation male pups. However, the degree
of concern is low for the quantitative evidence of susceptibility seen
in this study, since the body weight effects were seen in only one sex
and only after dosing for two generations. There is a clear NOAEL for
the body weight effects seen in the rat 2-generation reproduction study
and EPA is regulating based on a point of departure below where these
effects are seen.
In the developmental neurotoxicity study, transient body weight
effects were seen in one sex at post-natal days 1-4 with the animals
recovering by post-natal day 11. Body weight effects were also seen in
the high dose, which was the limit dose. The degree of concern for
these effects are low since the effects are either transient in nature
or occurred at the limit dose and EPA is regulating based on a point of
departure below where these effects are seen.
While qualitative sensitivity was seen in the rabbit developmental
study, the fetal effects were seen only at the limit dose in the
presence of maternal toxicity. Further, since EPA is regulating based
on a point of departure which is an order of magnitude below where
these effects are seen in the rabbit developmental study, EPA concludes
that the qualitative sensitivity evidenced in the fetuses in the rabbit
developmental study does not require retention of the 10X children's
safety factor.
3. Conclusion. The FQPA safety factor has been reduced to 1X for
boscalid for the following reasons. First, EPA has a complete toxicity
database for boscalid. The toxicity studies for boscalid show it
generally to have low mammalian toxicity. Further, while data involving
the testing of young animals did show increased quantitative
sensitivity in the young with regard to body weight effects and
qualitative sensitivity in one developmental study, clear NOAELs were
identified for all of these effects. Moreover, the body weight effects
at the LOAELs in these studies were either transient or inconsistent
and qualitative sensitivity occurred at the limit dose in the presence
of maternal toxicity. EPA concludes that there are no residual
uncertainties for pre-natal and/or post-natal toxicity. The NOAEL used
for various risk assessments would address the body weight effects seen
at higher doses in the developmental and reproductive studies. Finally,
EPA has conservatively estimated human exposure to boscalid, relying on
worst case exposures in food (assuming all registered crops contain
residues at the tolerance level), and conservative models as well as
pesticide-specific data in estimating exposure from residues in
drinking water and from residential uses.
E. Aggregate Risks and Determination of Safety
Safety is assessed for acute and chronic risks by comparing
aggregate exposure to the pesticide to the aPAD and cPAD. The aPAD and
cPAD are calculated by dividing the LOC by all applicable UFs. For
linear cancer risks, EPA calculates the probability of additional
cancer cases given aggregate exposure. Short-term, intermediate-term,
and long-term risks are evaluated by comparing aggregate exposure to
the LOC to ensure that the MOE called for by the product of all
applicable UFs is not exceeded.
1. Acute risk. There were no toxic effects attributable to a single
exposure to boscalid, therefore, neither an acute reference dose (aRfD)
nor aPAD were established and acute dietary risk assessment and acute
aggregate risk assessment are not required for boscalid.
2. Chronic risk. The unrefined chronic dietary risk assessment for
boscalid was made using tolerance level residues, default and empirical
processing factors and 100% CT assumptions. Results of this analysis
indicate that chronic risk from the dietary (food + drinking water)
exposure from boscalid will not exceed EPA's level of concern for the
general U.S. population, and all population subgroups. The chronic
dietary risk estimate for the highest reported exposed population
subgroup, children 1-2 years old, is 33% of the cPAD. Chronic
residential exposure from residues of boscalid is not expected;
therefore the aggregate chronic risk is equivalent to the chronic
dietary risk described above.
3. Short-term risk. Short-term aggregate exposure takes into
account residential exposure plus average exposure to food and water
(considered to be a background exposure level).
Boscalid is currently registered for uses that could result in
short-term residential exposure and the Agency has determined that it
is appropriate to aggregate average food and water exposures with
short-term non-occupational exposures for boscalid. Using the exposure
assumptions described in this unit for short-term exposures, EPA has
concluded that food, water, and residential exposures aggregated result
in aggregate MOEs, which are below the Agency's level of
[[Page 16558]]
concern. MOEs for the U.S. population, and all subpopulations of
concern exceed 1,000. The level of concern for this assessment is for
MOEs below 100.
4. Intermediate-term risk. Intermediate-term aggregate exposure
takes into account residential exposure plus chronic exposure to food
and water (considered to be a background exposure level). Because no
intermediate term, non-occupational exposures are anticipated from the
use of boscalid, an intermediate-term aggregate risk assessment is not
required for boscalid.
5. Aggregate cancer risk for U.S. population. Given the data
showing no more than weak evidence of carcinogenic effects for
boscalid, EPA concludes that boscalid poses no greater than a
negligible risk of cancer.
6. Determination of safety. Based on these risk assessments, EPA
concludes that there is a reasonable certainty that no harm will result
to the general population, or to infants and children from aggregate
exposure to boscalid residues.
IV. Other Considerations
A. Analytical Enforcement Methodology
Adequate enforcement methodology (gas chromatographic with mass
spectrometric detection) is available to enforce the tolerance
expression. The method may be requested from: Chief, Analytical
Chemistry Branch, Environmental Science Center, 701 Mapes Rd., Ft.
Meade, MD 20755-5350; telephone number: (410) 305-2905; e-mail address:
residuemethods@epa.gov.
B. International Residue Limits
There are currently no Codex Maximum Residue Limits (MRLs) for
boscalid. Canada has established MRLs for boscalid, but not for the
crops that are in this rule.
V. Conclusion
Therefore, this regulation establishes tolerances for residues of
boscalid,3-pyridinecarboxamide, 2-chloro-N-(4'-chloro[1,1'-biphenyl]-2-
yl), in or on caneberry subgroup 13A, and bushberry subgroup 13B,
respectively at 6.0 and 13 ppm; cotton, undelinted seed at 1.0 ppm;
cotton, gin byproducts at 55 ppm; avocado at 1.5 ppm; sapote, black at
1.5 ppm; canistel at 1.5 ppm; sapote, mamey at 1.5 ppm; mango at 1.5
ppm; papaya at 1.5 ppm; sapodilla at 1.5 ppm; star apple at 1.5 ppm;
cucumber at 0.5 ppm; and vegetable, root, subgroup 1A, except sugar
beet, garden beet, radish and turnip at 1.0 ppm. In addition, this
regulation establishes a time-limited tolerance for residues of
boscalid in or on endive, belgian at 16 ppm.
VI. Statutory and Executive Order Reviews
This final rule establishes a tolerance under section 408(d) of
FFDCA in response to a petition submitted to the Agency. The Office of
Management and Budget (OMB) has exempted these types of actions from
review under Executive Order 12866, entitled Regulatory Planning and
Review (58 FR 51735, October 4, 1993). Because this rule has been
exempted from review under Executive Order 12866, this rule is not
subject to Executive Order 13211, Actions Concerning Regulations That
Significantly Affect Energy Supply, Distribution, or Use (66 FR 28355,
May 22, 2001) or Executive Order 13045, entitled Protection of Children
from Environmental Health Risks and Safety Risks (62 FR 19885, April
23, 1997). This final rule does not contain any information collections
subject to OMB approval under the Paperwork Reduction Act (PRA), 44
U.S.C. 3501 et seq., nor does it require any special considerations
under Executive Order 12898, entitled Federal Actions to Address
Environmental Justice in Minority Populations and Low-Income
Populations (59 FR 7629, February 16, 1994). Since tolerances and
exemptions that are established on the basis of a petition under
section 408(d) of FFDCA, such as the tolerance in this final rule, do
not require the issuance of a proposed rule, the requirements of the
Regulatory Flexibility Act (RFA) (5 U.S.C. 601 et seq.) do not apply.
This final rule directly regulates growers, food processors, food
handlers, and food retailers, not States or tribes, nor does this
action alter the relationships or distribution of power and
responsibilities established by Congress in the preemption provisions
of section 408(n)(4) of FFDCA. As such, the Agency has determined that
this action will not have a substantial direct effect on States or
tribal governments, on the relationship between the national government
and the States or tribal governments, or on the distribution of power
and responsibilities among the various levels of government or between
the Federal Government and Indian tribes. Thus, the Agency has
determined that Executive Order 13132, entitled Federalism (64 FR
43255, August 10, 1999) and Executive Order 13175, entitled
Consultation and Coordination with Indian Tribal Governments (65 FR
67249, November 6, 2000) do not apply to this rule. In addition, This
rule does not impose any enforceable duty or contain any unfunded
mandate as described under Title II of the Unfunded Mandates Reform Act
of 1995 (UMRA) (Public Law 104-4). This action does not involve any
technical standards that would require Agency consideration of
voluntary consensus standards pursuant to section 12(d) of the National
Technology Transfer and Advancement Act of 1995 (NTTAA), Public Law
104-113, section 12(d) (15 U.S.C. 272 note).
VII. Congressional Review Act
The Congressional Review Act, 5 U.S.C. 801 et seq., generally
provides that before a rule may take effect, the agency promulgating
the rule must submit a rule report to each House of the Congress and to
the Comptroller General of the United States. EPA will submit a report
containing this rule and other required information to the U.S. Senate,
the U.S. House of Representatives, and the Comptroller General of the
United States prior to publication of this final rule in the Federal
Register. This final rule is not a ``major rule'' as defined by 5
U.S.C. 804(2).
List of Subjects in 40 CFR Part 180
Environmental protection, Administrative practice and procedure,
Agricultural commodities, Pesticides and pests, Reporting and
recordkeeping requirements.
Dated: March 18, 2008.
Lois Rossi,
Director, Registration Division, Office of Pesticide Programs.
0
Therefore, 40 CFR chapter I is amended as follows:
PART 180--[AMENDED]
0
1. The authority citation for part 180 continues to read as follows:
Authority: 21 U.S.C. 321(q), 346a and 371.
0
2. Section 180.589 is amended by removing the entry for berry group 13,
and alphabetically adding the following commodities to the table in
paragraph (a)(1), and by revising paragraph (b) to read as follows:
Sec. 180.589 Boscalid; tolerance for residues.
(a) * * *
(1) * * *
[[Page 16559]]
----------------------------------------------------------------------------------------------------------------
Commodity Parts per million
----------------------------------------------------------------------------------------------------------------
* * * * *
Avocado.......................................................... 1.5
Bushberry, subgroup 13B.......................................... 13.0
Caneberry, subgroup13A........................................... 6.0
Canistel......................................................... 1.5
* * * * *
Cotton, gin byproducts........................................... 55.0
Cotton, undelinted seed.......................................... 1.0
Cucumber......................................................... 0.5
* * * * *
Mango............................................................ 1.5
* * * * *
Papya............................................................ 1.5
Sapodilla........................................................ 1.5
Sapote, black.................................................... 1.5
Sapote, mamey.................................................... 1.5
Star Apple....................................................... 1.5
* * * * *
Vegetable, root, subgroup 1A, except sugarbeet, garden beet, 1.0
radish, and turnip
* * * * *
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* * * * *
(b) Section 18 emergency exemptions. A time-limited tolerance is
established for the residues of the fungicide boscalid, 2-chloro-N-(4'-
chloro [1, 1'-biphenyl]-2-yl)-3-pyridinecarboxamide in connection with
use of the pesticide under a section 18 emergency exemption granted by
EPA. This tolerance will expire and is revoked on the date specified in
the following table.
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Commodity Parts per million Expiration/Revocation Date
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Endive, Belgian 16 12/31/09
Tangerine 2.0 12/31/08
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* * * * *
[FR Doc. E8-6264 Filed 3-27-08; 8:45 am]
BILLING CODE 6560-50-S