Fluindapyr; Pesticide Tolerances, 88657-88660 [2024-25917]
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Federal Register / Vol. 89, No. 217 / Friday, November 8, 2024 / Rules and Regulations
ENVIRONMENTAL PROTECTION
AGENCY
40 CFR Part 180
[EPA–HQ–OPP–2023–0062; FRL–12158–01–
OCSPP]
Fluindapyr; Pesticide Tolerances
Environmental Protection
Agency (EPA).
ACTION: Final rule.
AGENCY:
This regulation establishes
tolerances for residues of fluindapyr in
or on soybean, forage; soybean, hay;
soybean, hulls; and soybean, seed. FMC
Corporation requested these tolerances
under the Federal Food, Drug, and
Cosmetic Act (FFDCA).
DATES: This regulation is effective
November 8, 2024. Objections and
requests for hearings must be received
on or before January 7, 2025, 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: The docket for this action,
identified by docket identification (ID)
number EPA–HQ–OPP–2023–0062, is
available at https://www.regulations.gov
or at the Office of Pesticide Programs
Regulatory Public Docket (OPP Docket)
in the Environmental Protection Agency
Docket Center (EPA/DC), West William
Jefferson Clinton Bldg., Rm. 3334, 1301
Constitution Ave. NW, Washington, DC
20460–0001. The Public Reading Room
is open from 8:30 a.m. to 4:30 p.m.,
Monday through Friday, excluding legal
holidays. The telephone number for the
Public Reading Room, and for the OPP
Docket is (202) 566–1744. Please review
the visitor instructions and additional
information about the docket available
at https://www.epa.gov/dockets.
FOR FURTHER INFORMATION CONTACT:
Charles Smith, Registration Divison
(7505T), Office of Pesticide Programs,
Environmental Protection Agency, 1200
Pennsylvania Ave. NW, Washington, DC
20460–0001; main telephone number:
(202) 566–1030; email address:
RDFRNotices@epa.gov.
SUPPLEMENTARY INFORMATION:
SUMMARY:
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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. The following
list of North American Industrial
Classification System (NAICS) codes is
not intended to be exhaustive, but rather
provides a guide to help readers
determine whether this document
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applies to them. Potentially affected
entities may include:
• Crop production (NAICS code 111).
• Animal production (NAICS code
112).
• Food manufacturing (NAICS code
311).
• Pesticide manufacturing (NAICS
code 32532).
B. How can I get electronic access to
other related information?
You may access a frequently updated
electronic version of EPA’s tolerance
regulations at 40 CFR part 180 through
the Office of the Federal Register’s eCFR site at https://www.ecfr.gov/
current/title-40.
C. How can I file an objection or hearing
request?
Under FFDCA section 408(g), 21
U.S.C. 346a(g), 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–2023–0062 in the subject line on
the first page of your submission. All
objections and requests for a hearing
must be in writing and must be received
by the Hearing Clerk on or before
January 7, 2025. Addresses for mail and
hand delivery of objections and hearing
requests are provided in 40 CFR
178.25(b).
EPA’s Office of Administrative Law
Judges (OALJ), in which the Hearing
Clerk is housed, urges parties to file and
serve documents by electronic means
only, notwithstanding any other
particular requirements set forth in
other procedural rules governing those
proceedings. See ‘‘Revised Order Urging
Electronic Service and Filing’’, dated
June 22, 2023, which can be found at
https://www.epa.gov/system/files/
documents/2023-06/2023-06-22%20%20revised%20order%20urging%20
electronic%20filing%20and%20
service.pdf. Although EPA’s regulations
require submission via U.S. Mail or
hand delivery, EPA intends to treat
submissions filed via electronic means
as properly filed submissions; therefore,
EPA believes the preference for
submission via electronic means will
not be prejudicial. When submitting
documents to the OALJ electronically, a
person should utilize the OALJ e-filing
system at https://yosemite.epa.gov/oa/
eab/eab-alj_upload.nsf.
In addition to filing an objection or
hearing request with the Hearing Clerk
as described in 40 CFR part 178, please
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submit a copy of the filing (excluding
any Confidential Business Information
(CBI)) for inclusion in the public docket.
Information not marked confidential
pursuant to 40 CFR part 2 may be
disclosed publicly by EPA without prior
notice. Submit the non-CBI copy of your
objection or hearing request, identified
by docket ID number EPA–HQ–OPP–
2023–0062, by one of the following
methods:
• Federal eRulemaking Portal:
https://www.regulations.gov. Follow the
online instructions for submitting
comments. Do not submit electronically
any information you consider to be CBI
or other information whose disclosure is
restricted by statute.
• Mail: OPP Docket, Environmental
Protection Agency Docket Center (EPA/
DC), (28221T), 1200 Pennsylvania Ave.
NW, Washington, DC 20460–0001.
• Hand Delivery: To make special
arrangements for hand delivery or
delivery of boxed information, please
follow the instructions at https://
www.epa.gov/dockets/where-sendcomments-epa-dockets.
Additional instructions on
commenting or visiting the docket,
along with more information about
dockets generally, is available at https://
www.epa.gov/dockets.
II. Summary of Petitioned-For
Tolerance
In the Federal Register of July 5, 2023
(88 FR 42935) (FRL–10579–05–OCSPP),
EPA issued a document pursuant to
FFDCA section 408(d)(3), 21 U.S.C.
346a(d)(3), announcing the filing of a
pesticide petition (PP 2F9020) by FMC
Corporation, 2929 Walnut Street,
Philadelphia, PA 19104. The petition
requested that 40 CFR part 180 be
amended by establishing tolerances for
residues of the fungicide fluindapyr, in
or on soybean, forage at 15 parts per
million (ppm); soybean, hay at 30 ppm;
soybean, hulls at 0.6 ppm; soybean, seed
at 0.2 ppm. That document referenced a
summary of the petition prepared by
FMC Corporation, the registrant, which
is available in the docket, https://
www.regulations.gov. There were no
comments received in response to the
notice of filing.
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
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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. . . .’’
Consistent with FFDCA section
408(b)(2)(D), and the factors specified
therein, 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 fluindapyr,
including exposure resulting from the
tolerances established by this action.
EPA’s assessment of exposures and risks
associated with fluindapyr follows.
In an effort to streamline its
publications in the Federal Register,
EPA is not reprinting sections of the
rule that repeat what has been
previously published in tolerance
rulemakings for the same pesticide
chemical. Where scientific information
concerning a particular chemical
remains unchanged, the content of those
sections would not vary between
tolerance rulemakings, and EPA
considers referral back to those sections
as sufficient to provide an explanation
of the information EPA considered in
making its safety determination for the
new rulemaking.
EPA has previously published a
tolerance rulemaking for fluindapyr in
which EPA concluded, based on the
available information, that there is a
reasonable certainty that no harm would
result from aggregate exposure to
fluindapyr and established tolerances
for residues of that chemical. EPA is
incorporating previously published
sections from that rulemaking as
described further in this rule, as they
remain unchanged.
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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.
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Specific information on the studies
received and the nature of the adverse
effects caused by fluindapyr as well as
the no-observed-adverse-effect-level
(NOAEL) and the lowest-observedadverse-effect-level (LOAEL) from the
toxicity studies are discussed in the
final rule published in Unit III.A. of the
Federal Register of March 9, 2021 (86
FR 13459) (FRL–10019–19).
B. Toxicological Points of Departure/
Levels of Concern
Once a pesticide’s toxicological
profile is determined, EPA identifies
toxicological points of departure (POD)
and levels of concern (LOC) to use in
evaluating the risk posed by human
exposure to the pesticide. For hazards
that have a threshold below which there
is no appreciable risk, the toxicological
POD is used as the basis for derivation
of reference values for risk assessment.
PODs are developed based on a careful
analysis of the doses in each
toxicological study to determine the
dose at which no adverse effects are
observed (the NOAEL) and the lowest
dose at which adverse effects of concern
are identified (the LOAEL). Uncertainty/
safety factors are used in conjunction
with the POD to calculate a safe
exposure level—generally referred to as
a population-adjusted dose (PAD) or a
reference dose (RfD)—and a safe margin
of exposure (MOE). For non-threshold
risks, the Agency assumes that any
amount of exposure will lead to some
degree of risk. Thus, the Agency
estimates risk in terms of the probability
of an occurrence of the adverse effect
expected in a lifetime. 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/pesticide-science-andassessing-pesticide-risks/assessinghuman-health-risk-pesticides.
A summary of the toxicological
endpoints for fluindapyr used for
human risk assessment can be found at
https://www.regulations.gov in
document ‘‘Fluindapyr. Human Health
Risk Assessment for Section 3
Registration and Tolerance Requests for
Use on Soybeans and Proposed New
Uses on Sod Farms, Athletic Fields and
Residential Turfgrass and Lawns,’’
hereinafter ‘‘Fluindapyr Human Health
Risk Assessment’’ on pages 19–20 in
Docket ID number EPA–HQ–OPP–2023–
0062.
C. Exposure Assessment
1. Dietary exposure from food and
feed uses. In evaluating dietary
exposure to fluindapyr, EPA considered
exposure under the petitioned-for
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tolerances as well as all existing
fluindapyr tolerances in 40 CFR
180.716. EPA assessed dietary
exposures from fluindapyr in food as
follows:
i. Acute exposure. Quantitative acute
dietary exposure and risk assessments
are performed for a food-use pesticide,
if a toxicological study has indicated the
possibility of an effect of concern
occurring as a result of a 1-day or single
exposure. Such effects were identified
for fluindapyr. In estimating acute
dietary exposure, EPA used 2003–2008
food consumption information from the
United States Department of Agriculture
(USDA) Nationwide Health and
Nutrition Examination Survey, What We
Eat in America (NHANES/WWEIA). As
to residue levels in food, the acute
analysis assumed 100% crop treated
(PCT) for all commodities, highest
average field trial (HAFT) residue
values, empirical and default processing
factors, and anticipated livestock
residues based on calculated livestock
dietary burden and tissue transfer rates
from the livestock feeding studies.
ii. Chronic exposure. In conducting
the chronic dietary exposure assessment
EPA used 2005–2010 food consumption
data from the USDA’s NHANES/
WWEIA. As to residue levels in food,
chronic analysis assumed 100 PCT for
all commodities, field trial mean residue
values, empirical and default processing
factors and anticipated livestock dietary
burden and tissue transfer rates from the
livestock feeding studies and metabolite
ratios from the metabolism studies.
iii. Cancer. Based on the data
referenced in Unit III.A., EPA has
concluded that fluindapyr does not pose
a cancer risk to humans. Therefore, a
dietary exposure assessment for the
purpose of assessing cancer risk is
unnecessary.
2. Dietary exposure from drinking
water. The proposed uses do not result
in an increase in the estimated residue
levels in drinking water, so the
estimated drinking water concentration
used in the March 9, 2021, final rule is
the same as those used in this
assessment.
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,
indoor pest control, termiticides, and
flea and tick control on pets).
Fluindapyr is currently registered for
the following uses that could result in
residential exposures: turf in public
areas (i.e., golf courses and landscape
areas around public, intuitional, and
commercial properties). The currently
registered use on turf in public areas
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will result in short-term (1 to 30 days)
residential post-application dermal
exposures to adults. It will also result in
residential post-application exposure in
children 1 to less than 2 years old
(combined dermal and hand-to-mouth
exposure).
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.’’
EPA has not found fluindapyr to share
a common mechanism of toxicity with
any other substances, and fluindapyr
does not appear to produce a toxic
metabolite produced by other
substances. For the purposes of this
tolerance action, therefore, EPA has
assumed that fluindapyr does not have
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/pesticide-science-andassessing-pesticide-risks/cumulativeassessment-risk-pesticides.
D. Safety Factor for Infants and
Children
Section 408(b)(2)(C) of FFDCA
provides that EPA shall apply an
additional tenfold (10X) 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
Food Quality Protection Act (FQPA)
Safety Factor (SF). EPA is retaining the
10X FQPA SF or all exposure
assessments except acute and chronic
dietary exposure for the need of the
comparative thyroid assay (CTA). See
Unit III.D. of the March 9, 2021,
rulemaking for a discussion of the
Agency’s rationale for that
determination.
E. Aggregate Risks and Determination of
Safety
EPA determines whether acute and
chronic dietary pesticide exposures are
safe by comparing dietary exposure
estimates to the acute PAD (aPAD) and
chronic PAD (cPAD). Short-,
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intermediate-, and chronic-term
aggregate risks are evaluated by
comparing the estimated total food,
water, and residential exposure to the
appropriate PODs to ensure that an
adequate MOE exists.
1. Acute risk. An acute aggregate risk
assessment takes into account acute
exposure estimates from dietary
consumption of food and drinking
water. Using the exposure assumptions
discussed in this unit for acute
exposure, the acute dietary exposure
from food and water to fluindapyr will
occupy 9% of the aPAD for all infants
under 1 year old, the population group
receiving the greatest exposure.
2. Chronic risk. Using the exposure
assumptions described in this unit for
chronic exposure, EPA has concluded
that chronic exposure to fluindapyr
from food and water will utilize 44% of
the cPAD for infants under 1 year old
the population group receiving the
greatest exposure. Based on the
explanation in Unit III.C.3., regarding
residential use patterns, chronic
residential exposure to residues of
fluindapyr is not expected.
3. Short-term risk. Short-term
aggregate exposure takes into account
short-term residential exposure plus
chronic exposure to food and water
(considered to be a background
exposure level). Short-term and
intermediate-term endpoints are
identical, and so short-term aggregate
exposure would be considered
protective of intermediate-term
aggregate exposures. Regarding shortterm risk, the four population subgroups
assessed for residential post-application
exposures are: adults, youth 11 to less
than 16 years old, children 6 to less than
11 years old, and children 1 to less than
2 years old. Of the four population
subgroups, the children 1 to less than 2
years old represent the highest exposure
from post-application exposures
(combined dermal and hand-to-mouth
exposure). However, based on registered
use patterns, intermediate-term
exposure is not expected for the
residential exposure pathway.
Therefore, intermediate-term aggregate
risk is not estimated.
Using the exposure assumptions
described in this unit for short-term
exposures, EPA has concluded the
combined short-term food, water, and
residential exposures result in aggregate
MOEs for adults, children 11 to less
than 16 years old, children 6 to less than
11 years old, and children 1 to less than
2 years old of 2100, 6500, 5100, and
1100 respectively. Because EPA’s level
of concern for fluindapyr is a MOE of
1,000 or below, these MOEs are not of
concern.
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4. Aggregate cancer risk for U.S.
population. Based on the lack of
evidence of carcinogenicity in two
adequate rodent carcinogenicity studies,
fluindapyr is not expected to pose a
cancer risk to humans.
5. Determination of safety. Based on
the risk assessment and information
described above, 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 fluindapyr
residues.
IV. Other Considerations
A. Analytical Enforcement Methodology
For a discussion of the available
enforcement analytical methods, see
Unit IV.A. of the March 9, 2021,
rulemaking.
B. International Residue Limits
In making its tolerance decisions, EPA
seeks to harmonize U.S. tolerances with
international standards whenever
possible, consistent with U.S. food
safety standards and agricultural
practices. EPA considers the
international maximum residue limits
(MRLs) established by the Codex
Alimentarius Commission (Codex), as
required by FFDCA section 408(b)(4).
The Codex Alimentarius is a joint
United Nations Food and Agriculture
Organization/World Health
Organization food standards program,
and it is recognized as an international
food safety standards-setting
organization in trade agreements to
which the United States is a party. EPA
may establish a tolerance that is
different from a Codex MRL; however,
FFDCA section 408(b)(4) requires that
EPA explain the reasons for departing
from the Codex level.
The Codex has not established a MRL
for fluindapyr.
V. Conclusion
Therefore, tolerances are established
for residues of fluindapyr, (3(difluoromethyl)-N-(7-fluoro-1,1,3trimethyl-2,3-dihydro-1H-inden-4-yl)-1methyl-1H-pyrazole-4-carboxamide), in
or on Soybean, forage at 15 ppm;
Soybean, hay at 30 ppm; Soybean, hulls
at 0.6 ppm; and Soybean, seed at 0.2
ppm.
VI. Statutory and Executive Order
Reviews
This action establishes tolerances
under FFDCA section 408(d) 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
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Planning and Review’’ (58 FR 51735,
October 4, 1993). Because this action
has been exempted from review under
Executive Order 12866, this action is
not subject to Executive Order 13211,
entitled ‘‘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 action 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 FFDCA section 408(d), 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 action 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 FFDCA
section 408(n)(4). 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
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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 9, 2000), do not apply
to this action. In addition, this action
does not impose any enforceable duty or
contain any unfunded mandate as
described under Title II of the Unfunded
Mandates Reform Act (UMRA) (2 U.S.C.
1501 et seq.).
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
(NTTAA) (15 U.S.C. 272 note).
VII. Congressional Review Act
Pursuant to the Congressional Review
Act (5 U.S.C. 801 et seq.), 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 the rule in the Federal
Register. This action 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.
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Dated: October 31, 2024.
Charles Smith,
Director, Registration Division, Office of
Pesticide Programs.
Therefore, for the reasons stated in the
preamble, EPA is amending 40 CFR
chapter I as follows:
PART 180—TOLERANCES AND
EXEMPTIONS FOR PESTICIDE
CHEMICAL RESIDUES IN FOOD
1. The authority citation for part 180
continues to read as follows:
■
Authority: 21 U.S.C. 321(q), 346a and 371.
2. In § 180.716, amend table 1 to
paragraph (a)(1) by adding in
alphabetical order the entries ‘‘Soybean,
forage’’, ‘‘Soybean, hay’’, ‘‘Soybean,
hulls’’, and ‘‘Soybean, seed’’ to read as
follows:
■
§ 180.716 Fluindapyr; tolerances for
residues.
(a) * * *
(1) * * *
TABLE 1 TO PARAGRAPH (a)(1)
Parts per
million
Commodity
*
*
Soybean,
Soybean,
Soybean,
Soybean,
*
*
*
*
forage .......................
hay ............................
hulls ..........................
seed ..........................
*
*
*
[FR Doc. 2024–25917 Filed 11–7–24; 8:45 am]
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[Federal Register Volume 89, Number 217 (Friday, November 8, 2024)]
[Rules and Regulations]
[Pages 88657-88660]
From the Federal Register Online via the Government Publishing Office [www.gpo.gov]
[FR Doc No: 2024-25917]
[[Page 88657]]
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ENVIRONMENTAL PROTECTION AGENCY
40 CFR Part 180
[EPA-HQ-OPP-2023-0062; FRL-12158-01-OCSPP]
Fluindapyr; Pesticide Tolerances
AGENCY: Environmental Protection Agency (EPA).
ACTION: Final rule.
-----------------------------------------------------------------------
SUMMARY: This regulation establishes tolerances for residues of
fluindapyr in or on soybean, forage; soybean, hay; soybean, hulls; and
soybean, seed. FMC Corporation requested these tolerances under the
Federal Food, Drug, and Cosmetic Act (FFDCA).
DATES: This regulation is effective November 8, 2024. Objections and
requests for hearings must be received on or before January 7, 2025,
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: The docket for this action, identified by docket
identification (ID) number EPA-HQ-OPP-2023-0062, is available at
https://www.regulations.gov or at the Office of Pesticide Programs
Regulatory Public Docket (OPP Docket) in the Environmental Protection
Agency Docket Center (EPA/DC), West William Jefferson Clinton Bldg.,
Rm. 3334, 1301 Constitution Ave. NW, Washington, DC 20460-0001. The
Public Reading Room is open from 8:30 a.m. to 4:30 p.m., Monday through
Friday, excluding legal holidays. The telephone number for the Public
Reading Room, and for the OPP Docket is (202) 566-1744. Please review
the visitor instructions and additional information about the docket
available at https://www.epa.gov/dockets.
FOR FURTHER INFORMATION CONTACT: Charles Smith, Registration Divison
(7505T), Office of Pesticide Programs, Environmental Protection Agency,
1200 Pennsylvania Ave. NW, Washington, DC 20460-0001; main telephone
number: (202) 566-1030; email address: [email protected].
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.
The following list of North American Industrial Classification System
(NAICS) codes is not intended to be exhaustive, but rather provides a
guide to help readers determine whether this document applies to them.
Potentially affected entities may include:
Crop production (NAICS code 111).
Animal production (NAICS code 112).
Food manufacturing (NAICS code 311).
Pesticide manufacturing (NAICS code 32532).
B. How can I get electronic access to other related information?
You may access a frequently updated electronic version of EPA's
tolerance regulations at 40 CFR part 180 through the Office of the
Federal Register's e-CFR site at https://www.ecfr.gov/current/title-40.
C. How can I file an objection or hearing request?
Under FFDCA section 408(g), 21 U.S.C. 346a(g), 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-2023-0062 in the subject line on the first
page of your submission. All objections and requests for a hearing must
be in writing and must be received by the Hearing Clerk on or before
January 7, 2025. Addresses for mail and hand delivery of objections and
hearing requests are provided in 40 CFR 178.25(b).
EPA's Office of Administrative Law Judges (OALJ), in which the
Hearing Clerk is housed, urges parties to file and serve documents by
electronic means only, notwithstanding any other particular
requirements set forth in other procedural rules governing those
proceedings. See ``Revised Order Urging Electronic Service and
Filing'', dated June 22, 2023, which can be found at https://www.epa.gov/system/files/documents/2023-06/2023-06-22%20-%20revised%20order%20urging%20electronic%20filing%20and%20service.pdf.
Although EPA's regulations require submission via U.S. Mail or hand
delivery, EPA intends to treat submissions filed via electronic means
as properly filed submissions; therefore, EPA believes the preference
for submission via electronic means will not be prejudicial. When
submitting documents to the OALJ electronically, a person should
utilize the OALJ e-filing system at https://yosemite.epa.gov/oa/eab/eab-alj_upload.nsf.
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 (excluding any Confidential Business Information (CBI)) for
inclusion in the public docket. Information not marked confidential
pursuant to 40 CFR part 2 may be disclosed publicly by EPA without
prior notice. Submit the non-CBI copy of your objection or hearing
request, identified by docket ID number EPA-HQ-OPP-2023-0062, by one of
the following methods:
Federal eRulemaking Portal: https://www.regulations.gov.
Follow the online instructions for submitting comments. Do not submit
electronically any information you consider to be CBI or other
information whose disclosure is restricted by statute.
Mail: OPP Docket, Environmental Protection Agency Docket
Center (EPA/DC), (28221T), 1200 Pennsylvania Ave. NW, Washington, DC
20460-0001.
Hand Delivery: To make special arrangements for hand
delivery or delivery of boxed information, please follow the
instructions at https://www.epa.gov/dockets/where-send-comments-epa-dockets.
Additional instructions on commenting or visiting the docket, along
with more information about dockets generally, is available at https://www.epa.gov/dockets.
II. Summary of Petitioned-For Tolerance
In the Federal Register of July 5, 2023 (88 FR 42935) (FRL-10579-
05-OCSPP), EPA issued a document pursuant to FFDCA section 408(d)(3),
21 U.S.C. 346a(d)(3), announcing the filing of a pesticide petition (PP
2F9020) by FMC Corporation, 2929 Walnut Street, Philadelphia, PA 19104.
The petition requested that 40 CFR part 180 be amended by establishing
tolerances for residues of the fungicide fluindapyr, in or on soybean,
forage at 15 parts per million (ppm); soybean, hay at 30 ppm; soybean,
hulls at 0.6 ppm; soybean, seed at 0.2 ppm. That document referenced a
summary of the petition prepared by FMC Corporation, the registrant,
which is available in the docket, https://www.regulations.gov. There
were no comments received in response to the notice of filing.
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
[[Page 88658]]
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. . . .''
Consistent with FFDCA section 408(b)(2)(D), and the factors
specified therein, 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 fluindapyr, including exposure resulting from
the tolerances established by this action. EPA's assessment of
exposures and risks associated with fluindapyr follows.
In an effort to streamline its publications in the Federal
Register, EPA is not reprinting sections of the rule that repeat what
has been previously published in tolerance rulemakings for the same
pesticide chemical. Where scientific information concerning a
particular chemical remains unchanged, the content of those sections
would not vary between tolerance rulemakings, and EPA considers
referral back to those sections as sufficient to provide an explanation
of the information EPA considered in making its safety determination
for the new rulemaking.
EPA has previously published a tolerance rulemaking for fluindapyr
in which EPA concluded, based on the available information, that there
is a reasonable certainty that no harm would result from aggregate
exposure to fluindapyr and established tolerances for residues of that
chemical. EPA is incorporating previously published sections from that
rulemaking as described further in this rule, as they remain unchanged.
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.
Specific information on the studies received and the nature of the
adverse effects caused by fluindapyr as well as the no-observed-
adverse-effect-level (NOAEL) and the lowest-observed-adverse-effect-
level (LOAEL) from the toxicity studies are discussed in the final rule
published in Unit III.A. of the Federal Register of March 9, 2021 (86
FR 13459) (FRL-10019-19).
B. Toxicological Points of Departure/Levels of Concern
Once a pesticide's toxicological profile is determined, EPA
identifies toxicological points of departure (POD) and levels of
concern (LOC) to use in evaluating the risk posed by human exposure to
the pesticide. For hazards that have a threshold below which there is
no appreciable risk, the toxicological POD is used as the basis for
derivation of reference values for risk assessment. PODs are developed
based on a careful analysis of the doses in each toxicological study to
determine the dose at which no adverse effects are observed (the NOAEL)
and the lowest dose at which adverse effects of concern are identified
(the LOAEL). Uncertainty/safety factors are used in conjunction with
the POD to calculate a safe exposure level--generally referred to as a
population-adjusted dose (PAD) or a reference dose (RfD)--and a safe
margin of exposure (MOE). For non-threshold risks, the Agency assumes
that any amount of exposure will lead to some degree of risk. Thus, the
Agency estimates risk in terms of the probability of an occurrence of
the adverse effect expected in a lifetime. 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/pesticide-science-and-assessing-pesticide-risks/assessing-human-health-risk-pesticides.
A summary of the toxicological endpoints for fluindapyr used for
human risk assessment can be found at https://www.regulations.gov in
document ``Fluindapyr. Human Health Risk Assessment for Section 3
Registration and Tolerance Requests for Use on Soybeans and Proposed
New Uses on Sod Farms, Athletic Fields and Residential Turfgrass and
Lawns,'' hereinafter ``Fluindapyr Human Health Risk Assessment'' on
pages 19-20 in Docket ID number EPA-HQ-OPP-2023-0062.
C. Exposure Assessment
1. Dietary exposure from food and feed uses. In evaluating dietary
exposure to fluindapyr, EPA considered exposure under the petitioned-
for tolerances as well as all existing fluindapyr tolerances in 40 CFR
180.716. EPA assessed dietary exposures from fluindapyr in food as
follows:
i. Acute exposure. Quantitative acute dietary exposure and risk
assessments are performed for a food-use pesticide, if a toxicological
study has indicated the possibility of an effect of concern occurring
as a result of a 1-day or single exposure. Such effects were identified
for fluindapyr. In estimating acute dietary exposure, EPA used 2003-
2008 food consumption information from the United States Department of
Agriculture (USDA) Nationwide Health and Nutrition Examination Survey,
What We Eat in America (NHANES/WWEIA). As to residue levels in food,
the acute analysis assumed 100% crop treated (PCT) for all commodities,
highest average field trial (HAFT) residue values, empirical and
default processing factors, and anticipated livestock residues based on
calculated livestock dietary burden and tissue transfer rates from the
livestock feeding studies.
ii. Chronic exposure. In conducting the chronic dietary exposure
assessment EPA used 2005-2010 food consumption data from the USDA's
NHANES/WWEIA. As to residue levels in food, chronic analysis assumed
100 PCT for all commodities, field trial mean residue values, empirical
and default processing factors and anticipated livestock dietary burden
and tissue transfer rates from the livestock feeding studies and
metabolite ratios from the metabolism studies.
iii. Cancer. Based on the data referenced in Unit III.A., EPA has
concluded that fluindapyr does not pose a cancer risk to humans.
Therefore, a dietary exposure assessment for the purpose of assessing
cancer risk is unnecessary.
2. Dietary exposure from drinking water. The proposed uses do not
result in an increase in the estimated residue levels in drinking
water, so the estimated drinking water concentration used in the March
9, 2021, final rule is the same as those used in this assessment.
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, indoor pest control,
termiticides, and flea and tick control on pets). Fluindapyr is
currently registered for the following uses that could result in
residential exposures: turf in public areas (i.e., golf courses and
landscape areas around public, intuitional, and commercial properties).
The currently registered use on turf in public areas
[[Page 88659]]
will result in short-term (1 to 30 days) residential post-application
dermal exposures to adults. It will also result in residential post-
application exposure in children 1 to less than 2 years old (combined
dermal and hand-to-mouth exposure).
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.''
EPA has not found fluindapyr to share a common mechanism of
toxicity with any other substances, and fluindapyr does not appear to
produce a toxic metabolite produced by other substances. For the
purposes of this tolerance action, therefore, EPA has assumed that
fluindapyr does not have 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/pesticide-science-and-assessing-pesticide-risks/cumulative-assessment-risk-pesticides.
D. Safety Factor for Infants and Children
Section 408(b)(2)(C) of FFDCA provides that EPA shall apply an
additional tenfold (10X) 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 Food Quality Protection Act
(FQPA) Safety Factor (SF). EPA is retaining the 10X FQPA SF or all
exposure assessments except acute and chronic dietary exposure for the
need of the comparative thyroid assay (CTA). See Unit III.D. of the
March 9, 2021, rulemaking for a discussion of the Agency's rationale
for that determination.
E. Aggregate Risks and Determination of Safety
EPA determines whether acute and chronic dietary pesticide
exposures are safe by comparing dietary exposure estimates to the acute
PAD (aPAD) and chronic PAD (cPAD). Short-, intermediate-, and chronic-
term aggregate risks are evaluated by comparing the estimated total
food, water, and residential exposure to the appropriate PODs to ensure
that an adequate MOE exists.
1. Acute risk. An acute aggregate risk assessment takes into
account acute exposure estimates from dietary consumption of food and
drinking water. Using the exposure assumptions discussed in this unit
for acute exposure, the acute dietary exposure from food and water to
fluindapyr will occupy 9% of the aPAD for all infants under 1 year old,
the population group receiving the greatest exposure.
2. Chronic risk. Using the exposure assumptions described in this
unit for chronic exposure, EPA has concluded that chronic exposure to
fluindapyr from food and water will utilize 44% of the cPAD for infants
under 1 year old the population group receiving the greatest exposure.
Based on the explanation in Unit III.C.3., regarding residential use
patterns, chronic residential exposure to residues of fluindapyr is not
expected.
3. Short-term risk. Short-term aggregate exposure takes into
account short-term residential exposure plus chronic exposure to food
and water (considered to be a background exposure level). Short-term
and intermediate-term endpoints are identical, and so short-term
aggregate exposure would be considered protective of intermediate-term
aggregate exposures. Regarding short-term risk, the four population
subgroups assessed for residential post-application exposures are:
adults, youth 11 to less than 16 years old, children 6 to less than 11
years old, and children 1 to less than 2 years old. Of the four
population subgroups, the children 1 to less than 2 years old represent
the highest exposure from post-application exposures (combined dermal
and hand-to-mouth exposure). However, based on registered use patterns,
intermediate-term exposure is not expected for the residential exposure
pathway. Therefore, intermediate-term aggregate risk is not estimated.
Using the exposure assumptions described in this unit for short-
term exposures, EPA has concluded the combined short-term food, water,
and residential exposures result in aggregate MOEs for adults, children
11 to less than 16 years old, children 6 to less than 11 years old, and
children 1 to less than 2 years old of 2100, 6500, 5100, and 1100
respectively. Because EPA's level of concern for fluindapyr is a MOE of
1,000 or below, these MOEs are not of concern.
4. Aggregate cancer risk for U.S. population. Based on the lack of
evidence of carcinogenicity in two adequate rodent carcinogenicity
studies, fluindapyr is not expected to pose a cancer risk to humans.
5. Determination of safety. Based on the risk assessment and
information described above, 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 fluindapyr residues.
IV. Other Considerations
A. Analytical Enforcement Methodology
For a discussion of the available enforcement analytical methods,
see Unit IV.A. of the March 9, 2021, rulemaking.
B. International Residue Limits
In making its tolerance decisions, EPA seeks to harmonize U.S.
tolerances with international standards whenever possible, consistent
with U.S. food safety standards and agricultural practices. EPA
considers the international maximum residue limits (MRLs) established
by the Codex Alimentarius Commission (Codex), as required by FFDCA
section 408(b)(4). The Codex Alimentarius is a joint United Nations
Food and Agriculture Organization/World Health Organization food
standards program, and it is recognized as an international food safety
standards-setting organization in trade agreements to which the United
States is a party. EPA may establish a tolerance that is different from
a Codex MRL; however, FFDCA section 408(b)(4) requires that EPA explain
the reasons for departing from the Codex level.
The Codex has not established a MRL for fluindapyr.
V. Conclusion
Therefore, tolerances are established for residues of fluindapyr,
(3-(difluoromethyl)-N-(7-fluoro-1,1,3-trimethyl-2,3-dihydro-1H-inden-4-
yl)-1-methyl-1H-pyrazole-4-carboxamide), in or on Soybean, forage at 15
ppm; Soybean, hay at 30 ppm; Soybean, hulls at 0.6 ppm; and Soybean,
seed at 0.2 ppm.
VI. Statutory and Executive Order Reviews
This action establishes tolerances under FFDCA section 408(d) 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
[[Page 88660]]
Planning and Review'' (58 FR 51735, October 4, 1993). Because this
action has been exempted from review under Executive Order 12866, this
action is not subject to Executive Order 13211, entitled ``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 action
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 FFDCA section 408(d), 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 action 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 FFDCA section 408(n)(4). 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 9, 2000), do not apply to this action. In addition,
this action does not impose any enforceable duty or contain any
unfunded mandate as described under Title II of the Unfunded Mandates
Reform Act (UMRA) (2 U.S.C. 1501 et seq.).
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 (NTTAA) (15 U.S.C. 272 note).
VII. Congressional Review Act
Pursuant to the Congressional Review Act (5 U.S.C. 801 et seq.),
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
the rule in the Federal Register. This action 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: October 31, 2024.
Charles Smith,
Director, Registration Division, Office of Pesticide Programs.
Therefore, for the reasons stated in the preamble, EPA is amending
40 CFR chapter I as follows:
PART 180--TOLERANCES AND EXEMPTIONS FOR PESTICIDE CHEMICAL RESIDUES
IN FOOD
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. In Sec. 180.716, amend table 1 to paragraph (a)(1) by adding in
alphabetical order the entries ``Soybean, forage'', ``Soybean, hay'',
``Soybean, hulls'', and ``Soybean, seed'' to read as follows:
Sec. 180.716 Fluindapyr; tolerances for residues.
(a) * * *
(1) * * *
Table 1 to Paragraph (a)(1)
------------------------------------------------------------------------
Parts per
Commodity million
------------------------------------------------------------------------
* * * * *
------------------------------------------------------------------------
Soybean, forage............................................ 15
Soybean, hay............................................... 30
Soybean, hulls............................................. 0.6
Soybean, seed.............................................. 0.2
------------------------------------------------------------------------
* * * * *
[FR Doc. 2024-25917 Filed 11-7-24; 8:45 am]
BILLING CODE 6560-50-P