Flonicamid; Pesticide Tolerances, 13805-13809 [2019-06690]
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Federal Register / Vol. 84, No. 67 / Monday, April 8, 2019 / Rules and Regulations
ENVIRONMENTAL PROTECTION
AGENCY
40 CFR Part 180
[EPA–HQ–OPP–2018–0273; FRL–9990–52]
Flonicamid; Pesticide Tolerances
Environmental Protection
Agency (EPA).
ACTION: Final rule.
AGENCY:
This regulation establishes a
crop group tolerance for residues of
flonicamid in or on the commodities in
sunflower subgroup 20B. Interregional
Research Project Number 4 (IR–4)
requested these tolerances under the
Federal Food, Drug, and Cosmetic Act
(FFDCA).
SUMMARY:
This regulation is effective April
8, 2019. Objections and requests for
hearings must be received on or before
June 7, 2019, and must be filed in
accordance with the instructions
provided in 40 CFR part 178 (see also
Unit I.C. of the SUPPLEMENTARY
INFORMATION).
DATES:
The docket for this action,
identified by docket identification (ID)
number EPA–HQ–OPP–2018–0273, 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 is (202) 566–1744,
and the telephone number for the OPP
Docket is (703) 305–5805. Please review
the visitor instructions and additional
information about the docket available
at https://www.epa.gov/dockets.
FOR FURTHER INFORMATION CONTACT:
Michael L. Goodis, Registration Division
(7505P), Office of Pesticide Programs,
Environmental Protection Agency, 1200
Pennsylvania Ave. NW, Washington, DC
20460–0001; main telephone number:
(703) 305–7090; email address:
RDFRNotices@epa.gov.
SUPPLEMENTARY INFORMATION:
ADDRESSES:
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. The following
list of North American Industrial
Classification System (NAICS) codes is
not intended to be exhaustive, but rather
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13805
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).
• Hand Delivery: To make special
arrangements for hand delivery or
delivery of boxed information, please
follow the instructions at https://
www.epa.gov/dockets/contacts.html.
B. How can I get electronic access to
other related information?
II. Summary of Petitioned-For
Tolerance
You may access a frequently updated
electronic version of EPA’s tolerance
regulations at 40 CFR part 180 through
the Government Printing Office’s e-CFR
site at https://www.ecfr.gov/cgi-bin/textidx?&c=ecfr&tpl=/ecfrbrowse/Title40/
40tab_02.tpl.
In the Federal Register of July 24,
2018 (83 FR 34968) (FRL–9980–31),
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 8E8667) by
Interregional Research Project Number 4
(IR–4), Rutgers, The State University of
New Jersey, 500 College Road East,
Suite 201W, Princeton, NJ 08540. The
petition requests to establish a tolerance
in 40 CFR part 180 for residues of the
insecticide flonicamid, including its
metabolites and degradates, determined
by measuring only the sum of
flonicamid, N-(cyanomethyl)-4(trifluoromethyl)-3pyridinecarboxamide, and its
metabolites, TFNA (4trifluoromethylnicotinic acid), TFNAAM (4-trifluoromethylnicotinamide),
and TFNG N-(4trifluoromethylnicotinoyl)glycine,
calculated as the stoichiometric
equivalent of flonicamid, in or on the
commodities in sunflower subgroup 20B
at 0.70 parts per million (ppm). That
document referenced a summary of the
petition prepared by ISK Bioscience
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.
C. How can I file an objection or hearing
request?
Under FFDCA section 408(g), 21
U.S.C. 346a, 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–2018–0273 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 June 7, 2019. Addresses for mail
and hand delivery of objections and
hearing requests are provided in 40 CFR
178.25(b).
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–
2018–0273, 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.
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Additional instructions on commenting
or visiting the docket, along with more
information about dockets generally, is
available at https://www.epa.gov/
dockets.
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
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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 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 flonicamid
including exposure resulting from the
tolerances established by this action.
EPA’s assessment of exposures and risks
associated with flonicamid follows.
A. Toxicological Profile
EPA has evaluated the available
toxicity database 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.
Flonicamid and its metabolites of
concern demonstrated low toxicity in
acute oral toxicity studies. Flonicamid
showed no systemic toxicity in a 28-day
dermal study at the limit dose. Feeding
studies in rats and dogs show the
kidney and liver are the target organs for
flonicamid toxicity. In repeat-dose
subchronic and chronic oral toxicity
studies, the consistently observed
adverse effect in rats and mice were
kidney toxicity (i.e., hyaline deposition
and nephritis); in dogs, vomiting and
increased percentage of reticulocytes (an
indicator for potential anemia).
Further detail of the toxicological
profile for flonicamid is discussed in
Unit III.A. of the final rule published in
the Federal Register of July 23, 2018 (83
FR 34775) (FRL–9977–82).
Specific information on the studies
received and the nature of the adverse
effects caused by flonicamid 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 in document,
‘‘SUBJECT: Flonicamid. Human Health
Risk Assessment for the Establishment
of Permanent Tolerances in or on
Sunflower Subgroup 20B’’ at pages 18–
19 in docket ID number EPA–HQ–OPP–
2018–0273.
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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 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://
www2.epa.gov/pesticide-science-andassessing-pesticide-risks/assessinghuman-health-risk-pesticides.
A summary of the toxicological
endpoints for flonicamid used for
human risk assessment is discussed in
Unit III.B. of the final rule published in
the Federal Register of July 23, 2018 (83
FR 34775) (FRL–9977–82).
C. Exposure Assessment
1. Dietary exposure from food and
feed uses. In evaluating dietary
exposure to flonicamid, EPA considered
exposure under the petitioned-for
tolerances as well as all existing
flonicamid tolerances in 40 CFR
180.613. EPA assessed dietary
exposures from flonicamid 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. No such effects were
identified in the toxicological studies
for flonicamid; therefore, a quantitative
acute dietary exposure assessment is
unnecessary.
ii. Chronic exposure. In conducting
the chronic dietary exposure
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assessment, EPA used the food
consumption data from the United
States Department of Agriculture
(USDA) 2003–2008 National Health and
Nutrition Examination Survey, What We
Eat in America (NHANES/WWEIA). The
chronic dietary (food and drinking
water) exposure assessment was
conducted using the Dietary Exposure
Evaluation Model software with the
Food Commodity Intake Database
(DEEM–FCID), Version 3.16. As to
residue levels in food, an unrefined
chronic dietary exposure assessment
was conducted for all proposed and
established food uses of flonicamid.
Tolerance-level residues were combined
with 100 percent crop treated (PCT)
estimates. Separate tolerances
established for potato granules/flakes,
tomato paste, and tomato puree were
based on processing studies (processing
factor set to 1.0 for these commodities)
and DEEM default processing factors
were used for the other processed
commodities.
iii. Cancer. Flonicamid has been
determined to have suggestive evidence
of carcinogenicity, but not sufficient to
assess human carcinogenic potential.
The Agency has determined that
quantification of risk using a non-linear
approach (i.e., using a chronic reference
dose) adequately accounts for all
chronic toxicity, including
carcinogenicity that could result from
exposure to flonicamid. Therefore, the
chronic reference dose is considered
protective for carcinogenic effects.
iv. Anticipated residue and percent
crop treated (PCT) information. EPA did
not use anticipated residue and/or PCT
information in the dietary assessment
for flonicamid. Tolerance-level residues
and/or 100 PCT were assumed for all
food commodities.
2. Dietary exposure from drinking
water. The Agency used screening-level
water exposure models in the dietary
exposure analysis and risk assessment
for flonicamid in drinking water. These
simulation models take into account
data on the physical, chemical, and fate/
transport characteristics of flonicamid.
Further information regarding EPA
drinking water models used in pesticide
exposure assessment can be found at
https://www2.epa.gov/pesticide-scienceand-assessing-pesticide-risks/aboutwater-exposure-models-used-pesticide.
The drinking water assessment was
conducted using a total toxic residue
approach, which considers the parent
compound and its major degradates of
concern.
Based on the Pesticide Root Zone
Model Ground Water (PRZM GW),
version 1.0, the estimated drinking
water concentration (EDWC) of
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flonicamid for chronic exposure for
non-cancer assessment is estimated to
be 9.92 parts per billion (ppb) for
ground water. The EDWC for surface
water chronic exposure, derived using
the Pesticide in Water Calculator (PWC
version 1.52), is 0.94 ppb.
Modeled estimates of drinking water
concentrations were directly entered
into the dietary exposure model. For
chronic dietary risk assessment, the
water concentration of value 9.92 ppb
was used 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,
indoor pest control, termiticides, and
flea and tick control on pets).
Flonicamid is not registered for any
specific use patterns that would result
in residential exposure. Further
information regarding EPA standard
assumptions and generic inputs for
residential exposures may be found at
https://www2.epa.gov/pesticide-scienceand-assessing-pesticide-risks/standardoperating-procedures-residentialpesticide.
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 flonicamid to
share a common mechanism of toxicity
with any other substances, and
flonicamid does not appear to produce
a toxic metabolite produced by other
substances. For the purposes of this
tolerance action, therefore, EPA has
assumed that flonicamid 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://
www2.epa.gov/pesticide-science-andassessing-pesticide-risks/cumulativeassessment-risk-pesticides.
D. Safety Factor for Infants and
Children
1. In general. 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
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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 (SF). In applying
this provision, EPA either retains the
default value of 10X, or uses a different
additional safety factor when reliable
data available to EPA support the choice
of a different factor.
2. Prenatal and postnatal sensitivity.
The prenatal and postnatal toxicity
database for flonicamid includes
prenatal developmental toxicity studies
in rats and rabbits and a multigeneration
reproduction toxicity study in rats.
There is no evidence that flonicamid
results in increased susceptibility
(qualitative or quantitative) in utero in
rats or rabbits in the prenatal
developmental studies or in young rats
in the multi-generation reproduction
study. No developmental effects were
seen in rabbits. In the multi-generation
reproduction study, developmental
delays in the offspring (decreased body
weights, delayed sexual maturation)
were seen only in the presence of
parental toxicity (kidney and blood
effects). Also, there are clear NOAELs
and LOAELs for all effects. The degree
of concern for prenatal and/or post-natal
susceptibility is, therefore, low due to
the lack of evidence of qualitative and
quantitative susceptibility.
3. Conclusion. EPA has determined
that reliable data show the safety of
infants and children would be
adequately protected if the FQPA SF
were reduced to 1x, except where
assessing risks from inhalation exposure
as discussed below. Those decisions are
based on the following findings:
i. The toxicity database for flonicamid
is essentially complete, except for an
outstanding subchronic 28-day
inhalation study. In the absence of a
subchronic inhalation study, EPA has
retained a 10X FQPA SF to assess risks
from inhalation exposure, although at
present, residential inhalation exposure
is not expected from existing or pending
uses of flonicamid.
ii. There is no indication that
flonicamid is a neurotoxic chemical. As
discussed in Unit III.A. of the final rule
published in the Federal Register of
July 23, 2018 (83 FR 34775) (FRL–9977–
82), EPA has concluded that the clinical
signs observed from available acute and
subchronic neurotoxicity studies were
not the result of a neurotoxic
mechanism. Therefore, there is no need
for a developmental neurotoxicity study
or additional UFs to account for
neurotoxicity.
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iii. There is no evidence that
flonicamid results in increased
susceptibility in in utero rats or rabbits
in the prenatal developmental studies or
in young rats in the 2-generation
reproduction study.
iv. There are no residual uncertainties
identified in the exposure databases.
The chronic dietary food exposure
assessment was based on 100 PCT,
tolerance-level residues and where
applicable, default processing factors.
EPA made conservative (protective)
assumptions in the ground and surface
water modeling used to assess exposure
to flonicamid in drinking water. These
assessments will not underestimate the
exposure and risks posed by flonicamid.
E. Aggregate Risks and Determination of
Safety
EPA determines whether acute and
chronic dietary pesticide exposures are
safe by comparing aggregate exposure
estimates to the acute PAD (aPAD) and
chronic PAD (cPAD). For linear cancer
risks, EPA calculates the lifetime
probability of acquiring cancer given the
estimated aggregate exposure. Short-,
intermediate-, and chronic-term risks
are evaluated by comparing the
estimated aggregate 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. No adverse effect resulting from
a single oral exposure was identified
and no acute dietary endpoint was
selected. Therefore, flonicamid is not
expected to pose an acute risk.
2. Chronic risk. Using the exposure
assumptions described in this unit for
chronic exposure, EPA has concluded
that chronic exposure to flonicamid
from food and water will utilize 64% of
the cPAD for children 1–2 years old, the
population group receiving the greatest
exposure. There are no residential uses
for flonicamid.
3. Short- and Intermediate-term risks.
Short- and intermediate-term aggregate
exposures take into account short- and
intermediate-term residential exposures
plus chronic exposure to food and water
(considered to be a background
exposure level). Flonicamid is not
registered for any use patterns that
would result in short- and intermediateterm residential exposures.
4. Aggregate cancer risk for U.S.
population. Based on the information
referenced in Unit III.A., EPA has
concluded that the cPAD is protective of
possible cancer effects from flonicamid,
and as evidenced in Unit III.E.2,
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aggregate exposure to flonicamid is
below the cPAD. As a result, EPA
concludes that there is not an aggregate
cancer risk from exposures to
flonicamid.
5. 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 flonicamid
residues.
IV. Other Considerations
A. Analytical Enforcement Methodology
Adequate enforcement methodology
is available to enforce the tolerance
expression. FMC Method No. P–3561M,
a liquid chromatography-tandem mass
spectrometry (LC/MS/MS) method, is an
acceptable enforcement method for
flonicamid and its metabolites in plant
commodities. The method determines
residues of flonicamid and its
metabolites TFNA-AM, TFNA, and
TFNG. The method has been sufficiently
validated in five diverse crops. The
limit of quantitation (LOQ) is 0.01 ppm.
The limit of detection (LOD) can be
estimated as one-third the LOQ.
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
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.
There are no Codex maximum residue
limits (MRLs) for flonicamid and its
metabolites in/on sunflower subgroup
20B.
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V. Conclusion
Therefore, tolerances are established
for residues of flonicamid, N(cyanomethyl)-4-(trifluoromethyl)-3pyridinecarboxamide, and its
metabolites, TFNA (4trifluoromethylnicotinic acid), TFNAAM (4-trifluoromethylnicotinamide),
and TFNG, N-(4trifluoromethylnicotinoyl)glycine,
calculated as the stoichiometric
equivalent of flonicamid, in or on
sunflower subgroup 20B at 0.70 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
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),), nor is it considered a
regulatory action under Executive Order
13771, entitled ‘‘Reducing Regulations
and Controlling Regulatory Costs’’ (82
FR 9339, February 3, 2017). 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 tolerances 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
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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: March 26, 2019.
Michael Goodis,
Director, Registration Division, Office of
Pesticide Programs.
Therefore, 40 CFR chapter I is
amended as follows:
PART 180—[AMENDED]
1. The authority citation for part 180
continues to read as follows:
■
Authority: 21 U.S.C. 321(q), 346a and 371.
2. In § 180.613, add alphabetically the
entry ‘‘Sunflower subgroup 20B’’ to the
table in paragraph (a)(1) to read as
follows:
■
§ 180.613 Flonicamid; tolerances for
residues.
(a) * * *
(1) * * *
E:\FR\FM\08APR1.SGM
08APR1
Federal Register / Vol. 84, No. 67 / Monday, April 8, 2019 / Rules and Regulations
recordings), please send an email to
FCC504@fcc.gov or call the Consumer &
Government Affairs Bureau at (202)
418–0530 (VOICE), (202) 418–0432
*
*
*
*
*
Sunflower subgroup 20B ......
0.70 (TTY).
This document does not contain
*
*
*
*
*
information collection requirements
subject to the Paperwork Reduction Act
*
*
*
*
*
of 1995, Public Law 104–13. In addition,
[FR Doc. 2019–06690 Filed 4–5–19; 8:45 am]
therefore, it does not contain any
BILLING CODE 6560–50–P
proposed information collection burden
‘‘for small business concerns with fewer
than 25 employees,’’ pursuant to the
FEDERAL COMMUNICATIONS
Small Business Paperwork Relief Act of
COMMISSION
2002, Public Law 107–198, see 44 U.S.C.
3506(c)(4). Provisions of the Regulatory
47 CFR Part 73
Flexibility Act of 1980, 5 U.S.C. 601–
[MB Docket No. 19–18; RM–11823; DA 19–
612, do not apply to this proceeding.
225]
The Commission will send a copy of
Television Broadcasting Services
this Report and Order in a report to be
Gadsden and Hoover, Alabama
sent to Congress and the Government
Accountability Office pursuant to the
AGENCY: Federal Communications
Congressional review Act, see 5 U.S.C.
Commission.
801(a)(1)(A).
ACTION: Final rule.
List of Subjects in 47 CFR Part 73
SUMMARY: At the request of ION Media
License Company, LLC. (ION), licensee
Television.
of television station WPXH–TV, channel
Federal Communications Commission.
45, Gadsden, Alabama (WPXH), the
Commission has before it an unopposed Thomas Horan,
Chief of Staff, Media Bureau.
Notice of Proposed Rulemaking to
amend the Post-Transition Table of DTV Final Rule
Allotments by changing WPXH’s
community of license from Gadsden to
For the reasons discussed in the
Hoover, Alabama. The Commission
preamble, the Federal Communications
believes that the proposed reallotment is Commission amends 47 CFR part 73 as
consistent with the Commission’s
follows:
second allotment priority by providing
Hoover with its first local transmission
PART 73—RADIO BROADCAST
service. The Commission also notes that SERVICE
the proposed reallotment will not
deprive Gadsden of its sole broadcast
■ 1. The authority citation for part 73
station because it will continue to be
continues to read as follows:
served by station WTJP–TV, licensed to
Authority: 47 U.S.C. 154, 303, 334, 336,
Trinity Christian Center of Santa Ana,
and 339.
Inc. on channel 26 at Gadsden. We also
grant ION’s requested waiver of the
§ 73.622 [Amended]
Commission’s rules.
■ 2. Section 73.622(i), the PostDATES: Effective April 8, 2019.
Transition Table of DTV Allotments
FOR FURTHER INFORMATION CONTACT:
under Alabama, is amended by
Joyce Bernstein, Media Bureau, at
removing Gadsden, channel 45, and
Joyce.Bernstein@fcc.gov.
adding, in alphabetical order, Hoover,
SUPPLEMENTARY INFORMATION: This is a
channel 45.
synopsis of the Commission’s Report
and Order, MB Docket No. 19–18; RM–
[FR Doc. 2019–06674 Filed 4–5–19; 8:45 am]
11823; DA 19–225, adopted March 28,
BILLING CODE 6712–01–P
2019, and released March 28, 2019. The
full text of this document is available for
public inspection and copying during
normal business hours in the FCC’s
Reference Information Center at Portals
II, CY–A257, 445 12th Street SW,
Washington, DC, 20554, or online at
https://apps.fcc.gov/ecfs/. To request
materials in accessible formats (braille,
large print, computer diskettes, or audio
jbell on DSK30RV082PROD with RULES
Commodity
VerDate Sep<11>2014
15:49 Apr 05, 2019
Parts per
million
Jkt 247001
PO 00000
Frm 00015
Fmt 4700
Sfmt 4700
13809
DEPARTMENT OF THE INTERIOR
Fish and Wildlife Service
50 CFR Part 17
[Docket No. FWS–HQ–ES–2018–0096;
4500030113]
RIN 1018–BD72
Endangered and Threatened Wildlife
and Plants; Adding 16 Species,
Removing One Species, and Updating
Entries for 17 Species on the List of
Endangered and Threatened Wildlife
Fish and Wildlife Service,
Interior.
ACTION: Final rule; correcting
amendments.
AGENCY:
We, the U.S. Fish and
Wildlife Service (Service), are amending
the List of Endangered and Threatened
Wildlife (List) by adding 16 species (gulf
grouper, island grouper, common
guitarfish, blackchin guitarfish,
daggernose shark, Brazilian guitarfish,
striped smoothhound shark, spiny
angelshark, Argentine angelshark,
narrownose smoothhound shark, Maui
dolphin, Hector’s dolphin, giant manta
ray, oceanic whitetip shark, Taiwanese
humpback dolphin, and chambered
nautilus) and by removing one species
(Puget Sound-Georgia Basin distinct
population segment (DPS) of canary
rockfish). We are also updating the
entries for the following six species by
adding critical habitat designation
citations: Gulf of Maine DPS of Atlantic
sturgeon, New York Bight DPS of
Atlantic sturgeon, Chesapeake Bay DPS
of Atlantic sturgeon, South Atlantic DPS
of Atlantic sturgeon, Carolina DPS of
Atlantic sturgeon, and Main Hawaiian
Islands Insular DPS of false killer whale.
Lastly, we are updating the genus name
for the Saimaa subspecies of ringed seal.
The above amendments are based on
previously published determinations by
the National Marine Fisheries Service
(NMFS) of the National Oceanic and
Atmospheric Administration,
Department of Commerce, which has
jurisdiction for these species. We are
also adding nonsubstantive corrections
to entries for 10 other species on the
List: Three foreign coral species, dusky
sea snake, Banggai cardinalfish, the
Tanzanian DPS of African coelacanth,
Nassau grouper, and three angelshark
species. We added these 10 species to
the List in 2016, but the entries did not
include the Federal Register citations
for the final listing rule, as is our
standard practice when we add new
entries to the List. The changes being
made via this rule simply provide
SUMMARY:
E:\FR\FM\08APR1.SGM
08APR1
Agencies
[Federal Register Volume 84, Number 67 (Monday, April 8, 2019)]
[Rules and Regulations]
[Pages 13805-13809]
From the Federal Register Online via the Government Publishing Office [www.gpo.gov]
[FR Doc No: 2019-06690]
[[Page 13805]]
-----------------------------------------------------------------------
ENVIRONMENTAL PROTECTION AGENCY
40 CFR Part 180
[EPA-HQ-OPP-2018-0273; FRL-9990-52]
Flonicamid; Pesticide Tolerances
AGENCY: Environmental Protection Agency (EPA).
ACTION: Final rule.
-----------------------------------------------------------------------
SUMMARY: This regulation establishes a crop group tolerance for
residues of flonicamid in or on the commodities in sunflower subgroup
20B. Interregional Research Project Number 4 (IR-4) requested these
tolerances under the Federal Food, Drug, and Cosmetic Act (FFDCA).
DATES: This regulation is effective April 8, 2019. Objections and
requests for hearings must be received on or before June 7, 2019, 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-2018-0273, 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 is (202) 566-1744, and the telephone number for the OPP
Docket is (703) 305-5805. Please review the visitor instructions and
additional information about the docket available at https://www.epa.gov/dockets.
FOR FURTHER INFORMATION CONTACT: Michael L. Goodis, Registration
Division (7505P), Office of Pesticide Programs, Environmental
Protection Agency, 1200 Pennsylvania Ave. NW, Washington, DC 20460-
0001; main telephone number: (703) 305-7090; 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 Government
Printing Office's e-CFR site at https://www.ecfr.gov/cgi-bin/text-idx?&c=ecfr&tpl=/ecfrbrowse/Title40/40tab_02.tpl.
C. How can I file an objection or hearing request?
Under FFDCA section 408(g), 21 U.S.C. 346a, 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-2018-0273 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
June 7, 2019. Addresses for mail and hand delivery of objections and
hearing requests are provided in 40 CFR 178.25(b).
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-2018-0273, 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/contacts.html.
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 24, 2018 (83 FR 34968) (FRL-9980-
31), 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
8E8667) by Interregional Research Project Number 4 (IR-4), Rutgers, The
State University of New Jersey, 500 College Road East, Suite 201W,
Princeton, NJ 08540. The petition requests to establish a tolerance in
40 CFR part 180 for residues of the insecticide flonicamid, including
its metabolites and degradates, determined by measuring only the sum of
flonicamid, N-(cyanomethyl)-4-(trifluoromethyl)-3-pyridinecarboxamide,
and its metabolites, TFNA (4-trifluoromethylnicotinic acid), TFNA-AM
(4-trifluoromethylnicotinamide), and TFNG N-(4-
trifluoromethylnicotinoyl)glycine, calculated as the stoichiometric
equivalent of flonicamid, in or on the commodities in sunflower
subgroup 20B at 0.70 parts per million (ppm). That document referenced
a summary of the petition prepared by ISK Bioscience 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 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
[[Page 13806]]
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 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 flonicamid including exposure
resulting from the tolerances established by this action. EPA's
assessment of exposures and risks associated with flonicamid follows.
A. Toxicological Profile
EPA has evaluated the available toxicity database 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.
Flonicamid and its metabolites of concern demonstrated low toxicity
in acute oral toxicity studies. Flonicamid showed no systemic toxicity
in a 28-day dermal study at the limit dose. Feeding studies in rats and
dogs show the kidney and liver are the target organs for flonicamid
toxicity. In repeat-dose subchronic and chronic oral toxicity studies,
the consistently observed adverse effect in rats and mice were kidney
toxicity (i.e., hyaline deposition and nephritis); in dogs, vomiting
and increased percentage of reticulocytes (an indicator for potential
anemia).
Further detail of the toxicological profile for flonicamid is
discussed in Unit III.A. of the final rule published in the Federal
Register of July 23, 2018 (83 FR 34775) (FRL-9977-82).
Specific information on the studies received and the nature of the
adverse effects caused by flonicamid 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 in document, ``SUBJECT: Flonicamid. Human Health
Risk Assessment for the Establishment of Permanent Tolerances in or on
Sunflower Subgroup 20B'' at pages 18-19 in docket ID number EPA-HQ-OPP-
2018-0273.
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 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://www2.epa.gov/pesticide-science-and-assessing-pesticide-risks/assessing-human-health-risk-pesticides.
A summary of the toxicological endpoints for flonicamid used for
human risk assessment is discussed in Unit III.B. of the final rule
published in the Federal Register of July 23, 2018 (83 FR 34775) (FRL-
9977-82).
C. Exposure Assessment
1. Dietary exposure from food and feed uses. In evaluating dietary
exposure to flonicamid, EPA considered exposure under the petitioned-
for tolerances as well as all existing flonicamid tolerances in 40 CFR
180.613. EPA assessed dietary exposures from flonicamid 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. No such effects were
identified in the toxicological studies for flonicamid; therefore, a
quantitative acute dietary exposure assessment is unnecessary.
ii. Chronic exposure. In conducting the chronic dietary exposure
assessment, EPA used the food consumption data from the United States
Department of Agriculture (USDA) 2003-2008 National Health and
Nutrition Examination Survey, What We Eat in America (NHANES/WWEIA).
The chronic dietary (food and drinking water) exposure assessment was
conducted using the Dietary Exposure Evaluation Model software with the
Food Commodity Intake Database (DEEM-FCID), Version 3.16. As to residue
levels in food, an unrefined chronic dietary exposure assessment was
conducted for all proposed and established food uses of flonicamid.
Tolerance-level residues were combined with 100 percent crop treated
(PCT) estimates. Separate tolerances established for potato granules/
flakes, tomato paste, and tomato puree were based on processing studies
(processing factor set to 1.0 for these commodities) and DEEM default
processing factors were used for the other processed commodities.
iii. Cancer. Flonicamid has been determined to have suggestive
evidence of carcinogenicity, but not sufficient to assess human
carcinogenic potential. The Agency has determined that quantification
of risk using a non-linear approach (i.e., using a chronic reference
dose) adequately accounts for all chronic toxicity, including
carcinogenicity that could result from exposure to flonicamid.
Therefore, the chronic reference dose is considered protective for
carcinogenic effects.
iv. Anticipated residue and percent crop treated (PCT) information.
EPA did not use anticipated residue and/or PCT information in the
dietary assessment for flonicamid. Tolerance-level residues and/or 100
PCT were assumed for all food commodities.
2. Dietary exposure from drinking water. The Agency used screening-
level water exposure models in the dietary exposure analysis and risk
assessment for flonicamid in drinking water. These simulation models
take into account data on the physical, chemical, and fate/transport
characteristics of flonicamid. Further information regarding EPA
drinking water models used in pesticide exposure assessment can be
found at https://www2.epa.gov/pesticide-science-and-assessing-pesticide-risks/about-water-exposure-models-used-pesticide.
The drinking water assessment was conducted using a total toxic
residue approach, which considers the parent compound and its major
degradates of concern.
Based on the Pesticide Root Zone Model Ground Water (PRZM GW),
version 1.0, the estimated drinking water concentration (EDWC) of
[[Page 13807]]
flonicamid for chronic exposure for non-cancer assessment is estimated
to be 9.92 parts per billion (ppb) for ground water. The EDWC for
surface water chronic exposure, derived using the Pesticide in Water
Calculator (PWC version 1.52), is 0.94 ppb.
Modeled estimates of drinking water concentrations were directly
entered into the dietary exposure model. For chronic dietary risk
assessment, the water concentration of value 9.92 ppb was used 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, indoor pest control,
termiticides, and flea and tick control on pets).
Flonicamid is not registered for any specific use patterns that
would result in residential exposure. Further information regarding EPA
standard assumptions and generic inputs for residential exposures may
be found at https://www2.epa.gov/pesticide-science-and-assessing-pesticide-risks/standard-operating-procedures-residential-pesticide.
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 flonicamid to share a common mechanism of
toxicity with any other substances, and flonicamid does not appear to
produce a toxic metabolite produced by other substances. For the
purposes of this tolerance action, therefore, EPA has assumed that
flonicamid 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://www2.epa.gov/pesticide-science-and-assessing-pesticide-risks/cumulative-assessment-risk-pesticides.
D. Safety Factor for Infants and Children
1. In general. 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 FQPA Safety
Factor (SF). In applying this provision, EPA either retains the default
value of 10X, or uses a different additional safety factor when
reliable data available to EPA support the choice of a different
factor.
2. Prenatal and postnatal sensitivity. The prenatal and postnatal
toxicity database for flonicamid includes prenatal developmental
toxicity studies in rats and rabbits and a multigeneration reproduction
toxicity study in rats. There is no evidence that flonicamid results in
increased susceptibility (qualitative or quantitative) in utero in rats
or rabbits in the prenatal developmental studies or in young rats in
the multi-generation reproduction study. No developmental effects were
seen in rabbits. In the multi-generation reproduction study,
developmental delays in the offspring (decreased body weights, delayed
sexual maturation) were seen only in the presence of parental toxicity
(kidney and blood effects). Also, there are clear NOAELs and LOAELs for
all effects. The degree of concern for prenatal and/or post-natal
susceptibility is, therefore, low due to the lack of evidence of
qualitative and quantitative susceptibility.
3. Conclusion. EPA has determined that reliable data show the
safety of infants and children would be adequately protected if the
FQPA SF were reduced to 1x, except where assessing risks from
inhalation exposure as discussed below. Those decisions are based on
the following findings:
i. The toxicity database for flonicamid is essentially complete,
except for an outstanding subchronic 28-day inhalation study. In the
absence of a subchronic inhalation study, EPA has retained a 10X FQPA
SF to assess risks from inhalation exposure, although at present,
residential inhalation exposure is not expected from existing or
pending uses of flonicamid.
ii. There is no indication that flonicamid is a neurotoxic
chemical. As discussed in Unit III.A. of the final rule published in
the Federal Register of July 23, 2018 (83 FR 34775) (FRL-9977-82), EPA
has concluded that the clinical signs observed from available acute and
subchronic neurotoxicity studies were not the result of a neurotoxic
mechanism. Therefore, there is no need for a developmental
neurotoxicity study or additional UFs to account for neurotoxicity.
iii. There is no evidence that flonicamid results in increased
susceptibility in in utero rats or rabbits in the prenatal
developmental studies or in young rats in the 2-generation reproduction
study.
iv. There are no residual uncertainties identified in the exposure
databases. The chronic dietary food exposure assessment was based on
100 PCT, tolerance-level residues and where applicable, default
processing factors. EPA made conservative (protective) assumptions in
the ground and surface water modeling used to assess exposure to
flonicamid in drinking water. These assessments will not underestimate
the exposure and risks posed by flonicamid.
E. Aggregate Risks and Determination of Safety
EPA determines whether acute and chronic dietary pesticide
exposures are safe by comparing aggregate exposure estimates to the
acute PAD (aPAD) and chronic PAD (cPAD). For linear cancer risks, EPA
calculates the lifetime probability of acquiring cancer given the
estimated aggregate exposure. Short-, intermediate-, and chronic-term
risks are evaluated by comparing the estimated aggregate 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. No adverse effect resulting from a single oral exposure
was identified and no acute dietary endpoint was selected. Therefore,
flonicamid is not expected to pose an acute risk.
2. Chronic risk. Using the exposure assumptions described in this
unit for chronic exposure, EPA has concluded that chronic exposure to
flonicamid from food and water will utilize 64% of the cPAD for
children 1-2 years old, the population group receiving the greatest
exposure. There are no residential uses for flonicamid.
3. Short- and Intermediate-term risks. Short- and intermediate-term
aggregate exposures take into account short- and intermediate-term
residential exposures plus chronic exposure to food and water
(considered to be a background exposure level). Flonicamid is not
registered for any use patterns that would result in short- and
intermediate-term residential exposures.
4. Aggregate cancer risk for U.S. population. Based on the
information referenced in Unit III.A., EPA has concluded that the cPAD
is protective of possible cancer effects from flonicamid, and as
evidenced in Unit III.E.2,
[[Page 13808]]
aggregate exposure to flonicamid is below the cPAD. As a result, EPA
concludes that there is not an aggregate cancer risk from exposures to
flonicamid.
5. 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 flonicamid residues.
IV. Other Considerations
A. Analytical Enforcement Methodology
Adequate enforcement methodology is available to enforce the
tolerance expression. FMC Method No. P-3561M, a liquid chromatography-
tandem mass spectrometry (LC/MS/MS) method, is an acceptable
enforcement method for flonicamid and its metabolites in plant
commodities. The method determines residues of flonicamid and its
metabolites TFNA-AM, TFNA, and TFNG. The method has been sufficiently
validated in five diverse crops. The limit of quantitation (LOQ) is
0.01 ppm. The limit of detection (LOD) can be estimated as one-third
the LOQ.
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:
[email protected].
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.
There are no Codex maximum residue limits (MRLs) for flonicamid and
its metabolites in/on sunflower subgroup 20B.
V. Conclusion
Therefore, tolerances are established for residues of flonicamid,
N-(cyanomethyl)-4-(trifluoromethyl)-3-pyridinecarboxamide, and its
metabolites, TFNA (4-trifluoromethylnicotinic acid), TFNA-AM (4-
trifluoromethylnicotinamide), and TFNG, N-(4-
trifluoromethylnicotinoyl)glycine, calculated as the stoichiometric
equivalent of flonicamid, in or on sunflower subgroup 20B at 0.70 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 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),), nor is it considered a
regulatory action under Executive Order 13771, entitled ``Reducing
Regulations and Controlling Regulatory Costs'' (82 FR 9339, February 3,
2017). 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 tolerances 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: March 26, 2019.
Michael Goodis,
Director, Registration Division, Office of Pesticide Programs.
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. In Sec. 180.613, add alphabetically the entry ``Sunflower subgroup
20B'' to the table in paragraph (a)(1) to read as follows:
Sec. 180.613 Flonicamid; tolerances for residues.
(a) * * *
(1) * * *
[[Page 13809]]
------------------------------------------------------------------------
Parts per
Commodity million
------------------------------------------------------------------------
* * * * *
Sunflower subgroup 20B.................................. 0.70
* * * * *
------------------------------------------------------------------------
* * * * *
[FR Doc. 2019-06690 Filed 4-5-19; 8:45 am]
BILLING CODE 6560-50-P