Document ID: EPA-HQ-OPP-2017-0233-0033
Agency: epa
Document Type: Rule
Title: Pesticide Tolerances: Tetraniliprole
Posted Date: 2021-02-24T05:00Z

[Federal Register Volume 86, Number 35 (Wednesday, February 24, 2021)]
[Rules and Regulations]
[Pages 11133-11139]
From the Federal Register Online via the Government Publishing Office [www.gpo.gov]
[FR Doc No: 2021-03624]

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ENVIRONMENTAL PROTECTION AGENCY

40 CFR Part 180

[EPA-HQ-OPP-2017-0233; FRL-10005-77]

Tetraniliprole; Pesticide Tolerances

AGENCY: Environmental Protection Agency (EPA).

ACTION: Final rule.

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SUMMARY: This regulation establishes tolerances for residues of 
tetraniliprole in or on multiple commodities that are identified and 
discussed later in this document. Bayer CropScience requested these 
tolerances under the Federal Food, Drug, and Cosmetic Act (FFDCA).

DATES: This regulation is effective February 24, 2021. Objections and

[[Page 11134]]

requests for hearings must be received on or before April 26, 2021, 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-2017-0233, is available at http://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.
    Due to the public health concerns related to COVID-19, the EPA 
Docket Center (EPA/DC) and Reading Room is closed to visitors with 
limited exceptions. The staff continues to provide remote customer 
service via email, phone, and webform. For the latest status 
information on EPA/DC services and docket access, visit https://www.epa.gov/dockets.

FOR FURTHER INFORMATION CONTACT: Marietta Echeverria, 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:

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 
Publishing Office's e-CFR site at http://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-2017-0233 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 
April 26, 2021. 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-2017-0233, by one of 
the following methods:
     Federal eRulemaking Portal: http://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 http://www.epa.gov/dockets/contacts.html.
    Additional instructions on commenting or visiting the docket, along 
with more information about dockets generally, is available at http://www.epa.gov/dockets.

II. Summary of Petitioned-For Tolerance

    In the Federal Register of December 15, 2017 (82 FR 59604) (FRL-
9970-50), 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 
7F8558) by Bayer CropScience, 2 T.W. Alexander Drive, Research Triangle 
Park, NC 27709. The petition requested that 40 CFR part 180 be amended 
by establishing tolerances for residues of the insecticide, 
tetraniliprole in or on tuberous and corm vegetables, crop group 1C at 
0.015 parts per million (ppm); potato, wet peel at 0.02 ppm; leafy 
vegetables, crop group 4-16 at 20 ppm; Brassica head and stem 
vegetables, crop group 5-16 at 1.5 ppm; fruiting vegetables, crop group 
8-10 at 0.40 ppm; tomato paste at 1.5 ppm; citrus fruit, orange 
subgroup 10-10A at 0.50 ppm; citrus fruit, lemon/lime subgroup 10-10B 
at 0.80 ppm; citrus fruit, grapefruit subgroup 10-10C at 0.50 ppm; 
citrus oil at 4.0 ppm; pome fruit, crop group 11-10 at 0.40 ppm; stone 
fruit, crop group 12-12 at 1.0 ppm; plum, dried (prune) at 2.0 ppm; 
small fruit, vine climbing subgroup, except fuzzy kiwi, crop subgroup 
13-07F at 1.5 ppm; tree nuts, crop group 14-12 at 0.03 ppm; almond 
hulls at 4.0 ppm; corn, field, grain at 0.015 ppm; corn, field, forage 
at 4.0 ppm; corn, field, stover at 15 ppm; corn, pop, grain at 0.015 
ppm; corn, pop, stover at 15 ppm; corn, sweet, kernel plus cobs with 
husks removed at 0.01 ppm; corn, sweet, forage at 6.0 ppm; corn, sweet, 
stover at 20 ppm; cottonseed, crop group 20C at 0.40 ppm; cotton, gin 
byproducts at 30 ppm; soybean seed at 0.20 ppm; soybean hulls at 0.60 
ppm; aspirated grain fractions at 45 ppm; soybean forage at 0.07 ppm; 
soybean hay at 0.20 ppm; alfalfa, forage and hay at 0.06 ppm; forage, 
fodder and straw of cereal grains, crop group 16, except field, pop and 
sweet corn at 0.10 ppm; foliage of legume vegetables, crop group 7, 
except soybeans at 0.03 ppm; milk at 0.06 ppm; fat of cattle, horses, 
sheep and goats at 0.30 ppm; muscle of cattle, horses, sheep and goats 
at 0.03 ppm; meat by-products of cattle, horses, sheep and goats at 
0.30 ppm. That document referenced a summary of the petition prepared 
by Bayer CropScience, the registrant, which is available in the docket, 
http://www.regulations.gov. Comments were received on the notice of 
filing. EPA's response to these comments is discussed in Unit IV.C.
    Based upon review of the data supporting the petition, EPA has 
modified the levels at which tolerances are being established as well 
as some of the commodity definitions used. The reasons for these 
changes are explained in Unit IV.D.

[[Page 11135]]

III. Aggregate Risk Assessment and Determination of Safety

    Section 408(b)(2)(A)(i) of FFDCA allows EPA to establish a 
tolerance (the legal limit for a pesticide chemical residue in or on a 
food) only if EPA determines that the tolerance is ``safe.'' Section 
408(b)(2)(A)(ii) of FFDCA defines ``safe'' to mean that ``there is a 
reasonable certainty that no harm will result from aggregate exposure 
to the pesticide chemical residue, including all anticipated dietary 
exposures and all other exposures for which there is reliable 
information.'' This includes exposure through drinking water and in 
residential settings, but does not include occupational exposure. 
Section 408(b)(2)(C) of FFDCA requires EPA to give special 
consideration to exposure of infants and children to the pesticide 
chemical residue in establishing a tolerance and to ``ensure that there 
is a reasonable certainty that no harm will result to infants and 
children from aggregate exposure to the pesticide chemical residue. . . 
.''
    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 tetraniliprole including 
exposure resulting from the tolerances established by this action. 
EPA's assessment of exposures and risks associated with tetraniliprole 
follows.

A. Toxicological Profile

    EPA has evaluated the available toxicity data and considered its 
validity, completeness, and reliability as well as the relationship of 
the results of the studies to human risk. EPA has also considered 
available information concerning the variability of the sensitivities 
of major identifiable subgroups of consumers, including infants and 
children.
    The submitted animal toxicity studies on tetraniliprole demonstrate 
low toxicity, which is expected based on two factors. Tetraniliprole is 
an anthranilimide insecticide that targets the activation of insect 
ryanodine receptors, which leads to insect paralysis and death. In 
contrast, mammalian ryanodine receptors are substantially less 
sensitive (i.e., 350 to >2,500 times less sensitive) to the effects of 
anthranilic diamides than insect ryanodine receptors. Moreover, 
available data indicate that tetraniliprole has limited absorption at 
the higher dose levels (>20 mg/kg), which may contribute to the low 
toxicity seen in the animal testing.
    In subchronic toxicity studies (28-day and 90-day) in rats and 
mice, no adverse effects were seen at dose levels ranging from 
approximately 600 to 1,228 mg/kg/day. In the subchronic studies (28-day 
and 90-day) in dogs, an increase in the incidence and frequency of 
salivation was found, but this finding did not show a dose related-
response, was a common occurrence in dogs, and was not considered to be 
adverse.
    No systemic or dermal toxicity was seen in a 28-day dermal toxicity 
study at 1,000 mg/kg/day; this finding was consistent with rather low 
dermal absorption as the DAF for humans was estimated to be 
approximately 9% (upper limit).
    No adverse maternal or developmental effects were found at the 
limit dose (1,000 mg/kg/day) in the developmental toxicity studies in 
rats and rabbits. In the reproduction study, the offspring effect, 
slight decrease in pup weight near and above the limit dose, was found 
in the absence of any adverse parental effect. Because the potential 
increase in susceptibility occurred at the limit dose and on postnatal 
days (PND) 14 to 21 at which time the pups were exposed to the test 
material through both milk and food resulting in a higher compound 
intake, the Agency's concern for the potential risk to infants and 
children is low. Tetraniliprole did not cause any effects on 
reproductive parameters.
    The combined chronic/carcinogenicity study in rats showed a 
decrease in body weights, increased incidence of squamous cell 
hyperplasia in the cervix and vagina, and corpora lutea depletion in 
the ovary at the limit dose. In addition, a slight increase in the 
incidence of uterine tumor was observed at a dose slightly above the 
limit dose. No genotoxic potential was detected in the battery of 
genotoxicity studies. There were no treatment-related tumors seen in 
mice and no adverse effects were observed in male rats. The only 
adverse effects observed in female rats occurred at the limit dose, 
which was the only dose where pre-neoplastic or neoplastic lesions were 
observed. Furthermore, there is no concern for mutagenicity and none of 
the identified structurally-related compounds induced tumors in rats or 
mice. Based on the available data that indicates that the increased 
incidence of uterine tumor was seen in only one species (rat), one sex 
(female), and is only slightly outside of the historical control range, 
EPA has classified tetraniliprole as having ``suggestive evidence of 
carcinogenic potential.''
    Typically, for chemicals so classified, EPA recommends that a non-
linear or RfD approach be used because the RfD would be protective for 
all toxicity, including carcinogenicity. However, in the case of 
tetraniliprole, EPA determined that the existing data do not support 
establishing toxicity endpoints and that a qualitative assessment is 
more appropriate for assessing tetraniliprole. This analysis is 
discussed more fully in Unit III.B. below. Similarly, because of the 
suggestive nature of the carcinogenicity effects and the fact that the 
only tumor effects are seen at doses above the limit dose, EPA has 
determined that a qualitative risk assessment would be appropriate in 
this case to account for all toxicity including carcinogenicity.
    No acute and subchronic neurotoxicity studies were submitted for 
tetraniliprole because this requirement was waived. However, no 
evidence of neurotoxicity was seen in any of the other studies in the 
tetraniliprole database.
    Specific information on the studies received and the nature of the 
adverse effects caused by tetraniliprole 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 http://www.regulations.gov in the document titled ``Tetraniliprole: New Active 
Ingredient, First Food Use. Human Health Risk Assessment for the 
Establishment of Permanent Tolerances on Brassica Head and Stem 
Vegetables, Corn (Field, Pop and Sweet), Citrus Fruit, Fruiting 
Vegetables, Leafy Vegetables, Pome Fruit, Small Fruit Vine Growing 
(except Fuzzy Kiwifruit) including Grape, Soybean, Stone Fruit, Tree 
Nuts, and Tuberous and Corm Vegetables, Plus Registration for Seed 
Treatment Uses on Corn (Field, Pop and Sweet), Use on Tobacco, and Use 
on Golf Course Turf, Sport Fields, and Sod Farms'' on pages 33-69 in 
docket ID number EPA-HQ-OPP-2017-0233.

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

[[Page 11136]]

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 http://www2.epa.gov/pesticide-science-and-assessing-pesticide-risks/assessing-human-health-risk-pesticides.
    Based on a thorough analysis of the toxicology database of 
tetraniliprole, the Agency has determined that a qualitative risk 
assessment is more appropriate for tetraniliprole based on the 
following reasons:
     All the adverse effects (decrease in pup body weights and 
non-neoplastic uterine lesions, characterized by prolapsed vagina, 
squamous cell hyperplasia in the cervix) in rats were found at or 
slightly above the limit dose. Although informative for hazard 
characterization for purposes of risk assessment, a toxicity test dose 
at or above the limit dose of 1,000 mg/kg/day represents an exposure 
that is not expected to occur either daily or over an extended period 
of time and therefore is not relevant to exposure levels expected from 
the use of tetraniliprole.
     EPA determined that the body weight reduction effects seen 
in the 90-day and 1-year oral studies with the dog, (approximately 500 
mg/kg/day) were not robust enough to be employed as a toxicity endpoint 
for risk assessment, due to the marginal nature of those effects and 
the fact that the rat (for which effects were seen at the 1,000 mg/kg/
day, limit dose) was more sensitive, based on a human equivalent dose 
analysis.
     Available data indicate no potential inhalation risk of 
concern.
     Available data indicate no adverse systemic effects at the 
limit dose (1,000 mg/kg/day) for dermal exposure.
     Potential offspring susceptibility was not of concern as 
the decrease in pup weight seen in the reproduction study was marginal 
and occurred at or above the limit dose (890/1,032 mg/kg/day (males/
females)). In addition, the decrease occurred on postnatal days (PND) 
14 to 21, at which time the pups were likely to be exposed to the test 
material through both milk and feed resulting in a much higher compound 
intake.
     Finally, taking into account expected exposures, EPA does 
not anticipate dietary exposure levels to occur daily, or over an 
extended period of time that would reach levels anywhere near that of 
the limit dose (1,000 mg/kg/day). An unrefined chronic dietary (food 
only) exposure estimate of tetraniliprole was calculated using 
tolerance-level residues for all crops and assuming 100% crop treated, 
as well as default processing factors. The screening estimate indicated 
that the highest exposure group is children 1 to 2 years old, with an 
estimated exposure of 0.027 mg/kg/day. To reach a dose of 1,000 mg/kg/
day, an individual of this subpopulation would need to ingest 37,000 
times the estimated dietary exposure. Further, the highest current 
application rate is approximately 0.18 lb ai/acre; and in order to 
yield residues that would lead to dietary exposures of 1,000 mg/kg/day, 
the application rate would have to be greater than 6,000 lb ai/acre. 
Consequently, EPA does not believe that an effect at or about the limit 
dose is relevant to human health risk assessment for tetraniliprole.
    Taking all the foregoing into consideration, EPA has concluded that 
a qualitative analysis of tetraniliprole is appropriate.

C. Exposure Assessment

    1. Dietary exposure from food and feed uses. There is potential for 
exposure to tetraniliprole via food and feed based on the proposed 
uses. However, no adverse effects were observed in the submitted 
toxicological studies for tetraniliprole regardless of the route of 
exposure. Thus, no quantitative dietary exposure assessments are needed 
for EPA to conclude with reasonable certainty that dietary exposures to 
tetraniliprole do not pose a significant human health risk.
    2. Dietary exposure from drinking water. There are no residues of 
toxicological concern expected in drinking water from the use of 
tetraniliprole. Thus, no drinking water exposure assessments are needed 
for the Agency to conclude with reasonable certainty that drinking 
water exposures to tetraniliprole do not pose a significant human 
health risk.
    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).
    Based upon the proposed labels, EPA does not anticipate residential 
handler exposures. Tetraniliprole is being proposed for registration as 
a liquid formulation for use on golf course turf and sports fields that 
could result in residential post-application exposures. However, no 
adverse effects were observed in the submitted toxicological studies 
for tetraniliprole regardless of the route of exposure; therefore, a 
quantitative residential post-application exposure assessment was not 
conducted. Thus, no residential exposure assessments are needed for the 
Agency to conclude with reasonable certainty that residential exposures 
to tetraniliprole do not pose a significant human health risk.
    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 tetraniliprole to share a common mechanism of 
toxicity with any other substances, and tetraniliprole does not appear 
to produce a toxic metabolite produced by other substances. For the 
purposes of this tolerance action, therefore, EPA has assumed that 
tetraniliprole 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 http://www2.epa.gov/pesticide-science-and-assessing-pesticide-risks/cumulative-assessment-risk-pesticides.

D. Safety Factor for Infants and Children

    Section 408(b)(2)(C) requires the application of an additional 
tenfold margin of safety to account for potential risks to infants and 
children, in the case of threshold effects. For tetraniliprole, EPA has 
not identified any toxicological endpoints of concern associated with 
any threshold effects and is conducting a qualitative assessment. That 
qualitative assessment does not use safety factors for assessing risk, 
and no additional safety factor is needed for assessing risk to infants 
and children. EPA has also evaluated the available data and concluded 
that there are no residual uncertainties concerning the

[[Page 11137]]

potential risks to infants and children that would impact its 
conclusions about threshold effects.

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.
    No adverse effects were observed in the submitted toxicological 
studies at doses relevant to human health pesticide risk assessment for 
tetraniliprole regardless of the route of exposure. Effects observed in 
the data base (e.g., decreased body weight) were both marginal, and 
only seen at doses not expected to occur daily or over an extended 
period. Based on a lack of toxicity at exposure levels expected from 
approved application rates and an expectation that aggregate exposures 
to residues of tetraniliprole will not reach the levels required to 
cause any adverse effects, 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 tetraniliprole 
residues.

IV. Other Considerations

A. Analytical Enforcement Methodology

    An adequate analytical method (01414) which uses high-performance 
liquid chromatography with tandem mass spectrometry (HPLC/MS/MS) to 
quantitate residues of tetraniliprole in various crops is available for 
enforcement. An adequate HPLC/MS/MS method, Method FV-002-A16-01, is 
proposed as the enforcement method for determination of residues of 
tetraniliprole in livestock matrices. The methods 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.

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 any MRLs for tetraniliprole.

C. Response to Comments

    Five comments were received to the notice of filing. Four of the 
comments were not related specifically to tetraniliprole or pesticides 
in general, dealing instead with ``anti-environmental morons'', 
electric cars, and wind farms and their impact on birds and bats. The 
fifth comment was submitted on behalf of the Center for Biological 
Diversity that was primarily concerned about EPA's consideration of the 
impacts of tetraniliprole on the environment, pollinators, and 
endangered species. None of these comments are relevant to the Agency's 
evaluation of safety of the tetraniliprole tolerances under section 408 
of the FFDCA, which requires the Agency to evaluate the potential harms 
to human health, not effects on the environment.

D. Revisions to Petitioned-For Tolerances

    The Agency is establishing tolerances based on the Organization for 
Economic Cooperation and Development (OECD) rounding class practice and 
to reflect the preferred commodity definitions currently used by the 
Agency, which results in some variations between established tolerances 
and the tolerances the petitioner requested.
    For field corn and popcorn, the available data support a tolerance 
of 0.01 ppm, slightly lower than the petitioned-for tolerance (0.015 
ppm).
    The petitioner requested tolerances on dried fruit (prune) and 
potato wet peel. The available data indicates that residues on those 
commodities do not concentrate so the new tolerances on stone fruit 
group 12-12 (1.0 ppm) and vegetable, tuberous and corm, subgroup 1C 
(0.015 ppm), respectively, are adequate to cover residues in these 
commodities.
    For citrus fruits (subgroups 10-10A, 10B, and 10C), the Agency used 
the OECD statistical calculation procedures to determine the 
appropriate tolerance value based on the available field trial residue 
data, which resulted in a higher tolerance value for each of these 
subgroups than what the petitioner requested.
    Based on the highest average field trial (HAFT) (0.767 ppm) for 
lime and using a processing factor of 8.6, the Agency calculated that a 
tolerance of 7 ppm is necessary to cover residues in citrus oil. 
Similarly, based on the HAFT (0.136 ppm) for soybean seed and using a 
processing factor of 2.6, the Agency determined that a tolerance of 0.4 
ppm is appropriate for soybean hulls.
    Although the petitioner did not expressly identify certain 
tolerances as intended to cover indirect or inadvertent residues in 
rotational crops, because certain crops are only approved as crops that 
may be rotated into treated fields on the label, EPA is establishing 
tolerances for indirect or inadvertent residues for those commodities: 
alfalfa, forage at 0.015 ppm; alfalfa, hay at 0.06 ppm; cottonseed 
subgroup 20C at 0.4 ppm; cotton, gin byproducts at 30 ppm; grain, 
cereal, forage, fodder, and straw, group 16, except field corn, 
popcorn, and sweet corn at 0.1 ppm; and vegetable, foliage of legume, 
except soybean, subgroup 7A.
    All the proposed tolerances for livestock commodities were revised 
based on calculation of the dietary burden.

V. Conclusion

    Therefore, tolerances are established for residues of 
tetraniliprole, including its metabolites and degradates. Compliance 
with the tolerance levels is to be determined by measuring only 
tetraniliprole 1-(3-chloro-2-pyridinyl)-N-[4-cyano-2-methyl-6-
[(methylamino)carbonyl]phenyl]-3-[[5-(trifluoromethyl)-2H-tetrazol-2-
yl]methyl]-1H-pyrazole-5-carboxamide, in or on almond, hulls at 4 ppm; 
cattle, fat at 0.04 ppm; cattle, meat at 0.02 ppm; cattle, meat 
byproducts at 0.3 ppm; corn, field, forage at 4 ppm; corn, field, grain 
at 0.01 ppm; corn, field, stover at 15 ppm; corn, pop, grain at 0.01 
ppm; corn, pop, stover at 15 ppm; corn, sweet, forage at 6 ppm; corn, 
sweet, kernel plus cob with husks removed at 0.01 ppm; corn, sweet, 
stover at 20 ppm; fruit, citrus, group 10-10, oil at 7 ppm; fruit, 
pome, group 11-10 at 0.5 ppm; fruit, small vine climbing, except fuzzy 
kiwifruit, subgroup 13-07F at 1.5 ppm; fruit, stone, group 12-12 at 1 
ppm; goat, fat at 0.04 ppm; goat, meat at 0.02 ppm; goat, meat 
byproducts at 0.3 ppm; grain, aspirated fractions at 50 ppm; grapefruit

[[Page 11138]]

subgroup 10-10C at 0.9 ppm; horse, fat at 0.04 ppm; horse, meat at 0.02 
ppm; horse, meat byproducts at 0.3 ppm; lemon/lime subgroup 10-10B at 
1.5 ppm; milk at 0.05 ppm; nut, tree, group 14-12 at 0.03 ppm; orange 
subgroup 10-10A at 1 ppm; sheep, fat at 0.04 ppm; sheep, meat at 0.02 
ppm; sheep, meat byproducts at 0.3 ppm; soybean, forage 0.07 ppm; 
soybean, hay at 0.2 ppm; soybean, hulls at 0.4 ppm; soybean, seed at 
0.2 ppm; tomato, paste at 1.5 ppm; vegetable, brassica, head and stem, 
group 5-16 at 1.5 ppm; vegetable, fruiting, group 8-10 at 0.4 ppm; 
vegetable, leafy, group 4-16 at 20 ppm; and vegetable, tuberous and 
corm, subgroup 1C at 0.015 ppm.
    Additionally, tolerances are established for inadvertent residues 
of tetraniliprole, including its metabolites and degradates. Compliance 
with the tolerance levels is to be determined by measuring only 
tetraniliprole 1-(3-chloro-2-pyridinyl)-N-[4-cyano-2-methyl-6-
[(methylamino)carbonyl]phenyl]-3-[[5-(trifluoromethyl)-2H-tetrazol-2-
yl]methyl]-1H-pyrazole-5-carboxamide in or on alfalfa, forage at 0.015 
ppm; alfalfa, hay at 0.06 ppm; cotton, gin byproducts at 30 ppm; 
cottonseed subgroup 20C at 0.4 ppm; grain, cereal, forage, fodder and 
straw, group 16, except field corn, popcorn, and sweet corn at 0.1 ppm; 
and vegetable, foliage of legume, except soybean, subgroup 7A at 0.03 
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 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: January 19, 2021.
Edward Messina,
Acting Director, 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. Add Sec.  180.709 to read as follows:

Sec.  180.709  Tetraniliprole; tolerances for residues.

    (a) General. Tolerances are established for residues of 
tetraniliprole, including its metabolites and degradates, in or on the 
commodities in table 1 in this paragraph (a). Compliance with the 
tolerance levels specified in table 1 in this paragraph (a) is to be 
determined by measuring only tetraniliprole 1-(3-chloro-2-pyridinyl)-N-
[4-cyano-2-methyl-6-[(methylamino)carbonyl]phenyl]-3-[[5-
(trifluoromethyl)-2H-tetrazol-2-yl]methyl]-1H-pyrazole-5-carboxamide.

                        Table 1 to Paragraph (a)
------------------------------------------------------------------------
                                                             Parts per
                        Commodity                             million
------------------------------------------------------------------------
Almond, hulls...........................................               4
Cattle, fat.............................................            0.04
Cattle, meat............................................            0.02
Cattle, meat byproducts.................................             0.3
Corn, field, forage.....................................               4
Corn, field, grain......................................            0.01
Corn, field, stover.....................................              15

[[Page 11139]]

 
Corn, pop, grain........................................            0.01
Corn, pop, stover.......................................              15
Corn, sweet, forage.....................................               6
Corn, sweet, kernel plus cob with husks removed.........            0.01
Corn, sweet, stover.....................................              20
Fruit, citrus, group 10-10, oil.........................               7
Fruit, pome, group 11-10................................             0.5
Fruit, small vine climbing, except fuzzy kiwifruit,                  1.5
 subgroup 13-07F........................................
Fruit, stone, group 12-12...............................               1
Goat, fat...............................................            0.04
Goat, meat..............................................            0.02
Goat, meat byproducts...................................             0.3
Grain, aspirated fractions..............................              50
Grapefruit subgroup 10-10C..............................             0.9
Horse, fat..............................................            0.04
Horse, meat.............................................            0.02
Horse, meat byproducts..................................             0.3
Lemon/lime subgroup 10-10B..............................             1.5
Milk....................................................            0.05
Nut, tree, group 14-12..................................            0.03
Orange subgroup 10-10A..................................               1
Sheep, fat..............................................            0.04
Sheep, meat.............................................            0.02
Sheep, meat byproducts..................................             0.3
Soybean, forage.........................................            0.07
Soybean, hay............................................             0.2
Soybean, hulls..........................................             0.4
Soybean, seed...........................................             0.2
Tomato, paste...........................................             1.5
Vegetable, brassica, head and stem, group 5-16..........             1.5
Vegetable, fruiting, group 8-10.........................             0.4
Vegetable, leafy, group 4-16............................              20
Vegetable, tuberous and corm, subgroup 1C...............           0.015
------------------------------------------------------------------------

    (b)-(c) [Reserved]
    (d) Indirect or inadvertent residues. Tolerances are established 
for indirect or inadvertent residues of tetraniliprole, including its 
metabolites and degradates, in or on the commodities in table 2 in this 
paragraph (d). Compliance with the tolerance levels specified in table 
2 in this paragraph (d) is to be determined by measuring only 
tetraniliprole 1-(3-chloro-2-pyridinyl)-N-[4-cyano-2-methyl-6-
[(methylamino)carbonyl]phenyl]-3-[[5-(trifluoromethyl)-2H-tetrazol-2-
yl]methyl]-1H-pyrazole-5-carboxamide.

                        Table 2 to Paragraph (d)
------------------------------------------------------------------------
                                                             Parts per
                        Commodity                             million
------------------------------------------------------------------------
Alfalfa, forage.........................................           0.015
Alfalfa, hay............................................            0.06
Cotton, gin byproducts..................................              30
Cottonseed subgroup 20C.................................             0.4
Grain, cereal, forage, fodder and straw, group 16,                   0.1
 except field corn, popcorn and sweet corn..............
Vegetable, foliage of legume, except soybean, subgroup              0.03
 7A.....................................................
------------------------------------------------------------------------

[FR Doc. 2021-03624 Filed 2-23-21; 8:45 am]
BILLING CODE 6560-50-P