Fluensulfone; Pesticide Tolerances, 24042-24048 [2019-10793]
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Federal Register / Vol. 84, No. 101 / Friday, May 24, 2019 / Rules and Regulations
ENVIRONMENTAL PROTECTION
AGENCY
40 CFR Part 180
[EPA–HQ–OPP–2017–0572; FRL–9992–69]
Fluensulfone; Pesticide Tolerances
Environmental Protection
Agency (EPA).
ACTION: Final rule.
AGENCY:
This regulation establishes
and amends tolerances for residues of
fluensulfone in or on multiple
commodities which are identified and
discussed later in this document.
Makhteshim Agan of North America
(d/b/a ADAMA) requested these
tolerances and tolerance amendments
under the Federal Food, Drug, and
Cosmetic Act (FFDCA).
DATES: This regulation is effective May
24, 2019. Objections and requests for
hearings must be received on or before
July 23, 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).
SUMMARY:
The docket for this action,
identified by docket identification (ID)
number EPA–HQ–OPP–2017–0572, 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 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:
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ADDRESSES:
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
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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/textidx?&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–2017–0572 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 July
23, 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–
2017–0572, 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/
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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 February
27, 2018 (83 FR 8408) (FRL–9972–17),
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 7F8614) by
Makhteshim Agan of North America
d/b/a ADAMA, 3120 Highlands Blvd.,
Suite 100, Raleigh, NC 27604. The
petition requested that 40 CFR part 180
be amended by establishing tolerances
for residues of the nematicide,
fluensulfone, including its metabolites
and degradates, in or on the following
commodities: Citrus dried pulp at 0.4
parts per million (ppm); Crop Group 10–
10, citrus fruit at 0.15 ppm; peanut at
0.15 ppm; peanut, hay at 8.0 ppm; and
peanut, meal at 0.30 ppm. That
document referenced a summary of the
petition prepared by Makhteshim Agan
of North America, the registrant, which
is available in docket ID number EPA–
HQ–OPP–2017–0572 at https://
www.regulations.gov. One comment was
received on the notice of filing. EPA’s
response to this comment is discussed
in Unit IV.C.
In the Federal Register of May 18,
2018 (83 FR 23247) (FRL–9976–87),
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 7F8650) by
Makhteshim Agan of North America,
d/b/a ADAMA, 3120 Highlands Blvd.,
Suite 100, Raleigh, NC 27604. The
petition requested to amend the
tolerances in 40 CFR 180.680 for
residues of the nematicide, fluensulfone
and its metabolite BSA expressed as
fluensulfone equivalents, in or on Berry,
low growing, subgroup 13–07G at 0.5
parts per million (ppm); Brassica, head
and stem, subgroup 5A at 1.5 ppm;
Brassica, leafy greens, subgroup 5B at 20
ppm; Potato, chips at 2 ppm; Potato,
granules/flakes at 2 ppm; Tomato, paste
at 1.5 ppm; Vegetables, cucurbits, group
9 at 0.7 ppm; Vegetables, fruiting, group
8–10 at 0.7 ppm; Vegetables, leafy,
except Brassica, group 4 at 4 ppm;
Vegetables, leaves of root and tuber,
group 2, except sugar beet at 50 ppm;
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Vegetables, root, except sugar beet,
subgroup 1B at 4 ppm; and Vegetables,
tuberous and corm, subgroup 1C at 0.8
ppm. That document referenced a
summary of the petition prepared by
Makhteshim Agan of North America, the
registrant, which is available in docket
ID number EPA–HQ–OPP–2018–0030 at
https://www.regulations.gov. There were
no comments received in response to
the notice of filing.
In the Federal Register of March 18,
2019 (84 FR 9737) (FRL–9989–71), 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 7F8650) by Makhteshim
Agan of North America, d/b/a ADAMA,
3120 Highlands Blvd., Suite 100,
Raleigh, NC 27604. The petition
requested to: (1) Amend the tolerance
expression in 40 CFR 180.680
paragraphs (a) and (d) to read
‘‘Tolerances are established for residues
of the nematicide fluensulfone,
including its metabolites and
degradates, in or on the commodities in
the table below. Compliance with the
tolerance levels specified in the
following table below is to be
determined by measuring only the sum
of fluensulfone, 5-chloro-2-[(3,4,4trifluoro-3-buten-1-yl)sulfonyl]thiazole
and its metabolite, 3,4,4-trifluoro-but-3ene-1-sulfonic acid, calculated as the
stoichiometric equivalent of
fluensulfone, in or on the commodity’’;
and (2) amend the tolerances in 40 CFR
180.680 for residues of the nematicide,
fluensulfone and its metabolite BSA
expressed as fluensulfone equivalents,
on the raw agricultural commodities as
follows: Almond hulls at 5 parts per
million (ppm); Fruit, pome, group 11 at
0.4 ppm; Fruit, small vine climbing
subgroup 13–07D at 0.8 ppm; Fruit,
stone, group 12 at 0.1 ppm; Grain cereal,
forage, fodder and straw, group 16 at 3
ppm; and, rotated wheat (inadvertent
residues with 90-day PBI): Grain, cereal,
group 15 at 0.05 ppm; Molasses at 0.3
ppm; and, rotated cereal grains
(inadvertent residues with 10-month
PBI): Nut, tree, group 14 at 0.04 ppm;
Sugarcane at 0.05 ppm and Wheat grain
(includes triticale) (Barley grain;
Buckwheat grain; Oat grain; and
Teosinte grain) at 0.1 ppm; Wheat bran
(Barley bran) at 0.14 ppm; Wheat forage
(Oat forage) at 6 ppm; Wheat germ at
0.10 ppm; Wheat hay (Barley hay and
Oat hay) at 15 ppm; Wheat middlings at
0.10 ppm; Wheat shorts at 0.11 ppm;
and, Wheat straw (Barley straw and Oat
straw) at 6 ppm. That document
referenced a summary of the petition
prepared by Makhteshim Agan of North
America, the registrant, which is
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available in docket ID number EPA–
HQ–OPP–2018–0793 at https://
www.regulations.gov. One comment was
received on the notice of filing. EPA’s
response to this comment is discussed
in Unit IV.C.
Based upon review of the data
supporting the petitions, EPA has
modified the levels at which tolerances
are being established as well as which
commodities will have tolerances. The
reasons for these changes are explained
in Unit IV.D.
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 fluensulfone
including exposure resulting from the
tolerances established by this action.
EPA’s assessment of exposures and risks
associated with fluensulfone 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.
A summary of the toxicological effects
of fluensulfone are discussed in the
final rule published in the Federal
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Register of April 13, 2018 (83 FR 15971)
(FRL–9975–76).
Specific information on the studies
received and the nature of the adverse
effects caused by fluensulfone 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 the document
titled ‘‘Fluensulfone—Aggregate Human
Health Risk Assessment in Support of
Section 3 Registration of New Uses on
Citrus and Peanut, and Change in the
Tolerance Expression’’ on pages 39–49
in docket ID number EPA–HQ–OPP–
2017–0572.
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 fluensulfone used for
human risk assessment is discussed in
Unit III.B. of the final rule published in
the Federal Register of June 1, 2016 (81
FR 34898) (FRL–9946–07).
C. Exposure Assessment
1. Dietary exposure from food and
feed uses. In evaluating dietary
exposure to fluensulfone, EPA
considered exposure under the
petitioned-for tolerances as well as all
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existing fluensulfone tolerances in 40
CFR 180.680. EPA assessed dietary
exposures from fluensulfone in food as
follows:
i. Acute exposure. Quantitative acute
dietary exposure and risk assessments
are performed for a food-use pesticide,
if a toxicological study has indicated the
possibility of an effect of concern
occurring as a result of a 1-day or single
exposure.
Such effects were identified for
fluensulfone. In estimating acute dietary
exposure, EPA used 2003–2008 food
consumption information from the
United States Department of Agriculture
(USDA) National Health and Nutrition
Examination Survey, What We Eat in
America, (NHANES/WWEIA). As to
residue levels in food, the acute dietary
risk assessment assumed toleranceequivalent residues and 100 percent
crop treated (PCT).
ii. Chronic exposure. In conducting
the chronic dietary exposure assessment
EPA used 2003–2008 food consumption
information from the USDA’s NHANES/
WWEIA. As to residue levels in food,
the chronic dietary risk assessment
assumed tolerance-equivalent residues
and 100 PCT.
iii. Cancer. Based on the data
summarized in Unit III.A., EPA has
concluded that a nonlinear RfD
approach is appropriate for assessing
cancer risk to fluensulfone. Cancer risk
was assessed using the same exposure
estimates as discussed in Unit III.C.1.ii.,
chronic exposure.
iv. Anticipated residue and PCT
information. EPA did not use
anticipated residue or PCT information
in the dietary assessment for
fluensulfone. Tolerance-equivalent
residue levels and 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 fluensulfone in drinking water.
These simulation models take into
account data on the physical, chemical,
and fate/transport characteristics of
fluensulfone. Further information
regarding EPA drinking water models
used in pesticide exposure assessment
can be found at https://www2.epa.gov/
pesticide-science-and-assessingpesticide-risks/about-water-exposuremodels-used-pesticide.
Based on the Pesticide Root Zone
Model/Exposure Analysis Modeling
System (PRZM/EXAMS) and Pesticide
Root Zone Model Ground Water (PRZM
GW) models, the estimated drinking
water concentrations (EDWCs) for acute
exposures are estimated to be 11.8 parts
per billion (ppb) for surface water and
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77.6 ppb for ground water and for
chronic exposures are estimated to be
0.173 ppb for surface water and 52.5
ppb for ground water. Modeled
estimates of drinking water
concentrations were directly entered
into the dietary exposure model. For the
acute dietary risk assessment, the water
concentration value of 77.6 ppb was
used to assess the contribution to
drinking water. For the chronic dietary
risk assessment, the water concentration
of value 52.5 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).
Fluensulfone is currently registered
for the following uses that could result
in residential exposures: Golf courses
and residential lawns. EPA assessed
residential exposure using the following
assumptions: No residential handler
exposure for fluensulfone is expected
because the products are not intended
for homeowner use. The product label
requires that handlers wear specific
clothing (e.g., long sleeve shirt/long
pants) and/or personal protective
equipment (PPE). The Agency has made
the assumption that the product is not
for homeowner use and is intended for
use by professional applicators. As a
result, a residential handler assessment
has not been conducted.
For adult residential post-application
exposure, the Agency evaluated dermal
post-application exposure only to
outdoor turf/lawn applications (high
contact activities). The Agency also
evaluated residential post-application
exposure for children via dermal and
hand-to-mouth routes of exposure,
resulting from treated outdoor turf/lawn
applications (high contact activities).
Further information regarding EPA
standard assumptions and generic
inputs for residential exposures may be
found at https://www2.epa.gov/pesticidescience-and-assessing-pesticide-risks/
standard-operating-proceduresresidential-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 fluensulfone to
share a common mechanism of toxicity
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with any other substances, and
fluensulfone does not appear to produce
a toxic metabolite produced by other
substances. For the purposes of this
tolerance action, therefore, EPA has
assumed that fluensulfone 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
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.
No evidence of increased quantitative or
qualitative susceptibility was seen in
developmental toxicity studies in rats
and rabbits. Fetal effects in those studies
occurred in the presence of maternal
toxicity and were not considered more
severe than the maternal effects.
However, there was evidence of
increased qualitative, but not
quantitative, susceptibility of pups in
the 2-generation reproduction study in
rats. Maternal effects observed in that
study were decreased body weight; at
the same dose, effects in offspring were
decreased pup weights, decreased
spleen weight, and increased pup loss
(post-natal day 1–4). Although there is
evidence of increased qualitative
susceptibility in the 2-generation
reproduction study in rats, there are no
residual uncertainties with regard to
pre- and post-natal toxicity following in
utero exposure to rats or rabbits and preand post-natal exposures to rats.
Considering the overall toxicity profile,
the clear NOAEL for the pup effects
observed in the 2-generation
reproduction study, and that the doses
selected for risk assessment are
protective of all effects in the toxicity
database including the offspring effects,
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the degree of concern for the
susceptibility is low.
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. That decision is
based on the following findings:
i. The toxicity database for
fluensulfone is complete.
ii. Evidence of potential neurotoxicity
was only seen following acute exposure
to fluensulfone and the current PODs
chosen for risk assessment are
protective of the effects observed. There
is no need for a developmental
neurotoxicity study or additional UFs to
account for neurotoxicity.
iii. There is no indication of
quantitative susceptibility in the
developmental and reproductive
toxicity studies, and there are no
residual uncertainties concerning preor post-natal toxicity. In addition, the
endpoints and doses chosen for risk
assessment are protective of the
qualitative susceptibility observed in
the 2-generation reproduction study.
iv. There are no residual uncertainties
identified in the exposure databases.
The dietary food exposure assessments
were performed based on 100 PCT and
tolerance-equivalent residue levels. EPA
made conservative (protective)
assumptions in the ground and surface
water modeling used to assess exposure
to fluensulfone in drinking water. EPA
used similarly conservative assumptions
to assess post-application exposure of
children as well as incidental oral
exposure of toddlers. These assessments
will not underestimate the exposure and
risks posed by fluensulfone.
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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. Using the exposure
assumptions discussed in this unit for
acute exposure, the acute dietary
exposure from food and water to
fluensulfone will occupy 9.4% of the
aPAD for all infants less than 1 year old,
the population group receiving the
greatest exposure.
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2. Chronic risk. Using the exposure
assumptions described in this unit for
chronic exposure, EPA has concluded
that chronic exposure to fluensulfone
from food and water will utilize 4.1% of
the cPAD for all infants less than 1 year
old, the population group receiving the
greatest exposure. Based on the
explanation in Unit III.C.3., regarding
residential use patterns, chronic
residential exposure to residues of
fluensulfone is not expected.
3. Short-term risk. Short-term
aggregate exposure takes into account
short-term residential exposure plus
chronic exposure to food and water
(considered to be a background
exposure level).
Fluensulfone is currently registered
for uses that could result in short-term
residential exposure, and the Agency
has determined that it is appropriate to
aggregate chronic exposure through food
and water with short-term residential
exposures to fluensulfone.
Using the exposure assumptions
described in this unit for short-term
exposures, EPA has concluded the
combined short-term food, water, and
residential exposures result in aggregate
MOEs of 5300 for adults and 2500 for
children. Because EPA’s level of
concern for fluensulfone is a MOE of
100 or below, these MOEs are not of
concern.
4. Intermediate-term risk.
Intermediate-term aggregate exposure
takes into account intermediate-term
residential exposure plus chronic
exposure to food and water (considered
to be a background exposure level).
An intermediate-term adverse effect
was identified; however, fluensulfone is
not registered for any use patterns that
would result in intermediate-term
residential exposure. Intermediate-term
risk is assessed based on intermediateterm residential exposure plus chronic
dietary exposure. Because there is no
intermediate-term residential exposure
and chronic dietary exposure has
already been assessed under the
appropriately protective cPAD (which is
at least as protective as the POD used to
assess intermediate-term risk), no
further assessment of intermediate-term
risk is necessary, and EPA relies on the
chronic dietary risk assessment for
evaluating intermediate-term risk for
fluensulfone.
5. Aggregate cancer risk for U.S.
population. EPA assessed cancer risk
using a non-linear approach (i.e., RfD)
since it adequately accounts for all
chronic toxicity, including
carcinogenicity, that could result from
exposure to fluensulfone. As the chronic
dietary endpoint and dose are protective
of potential cancer effects, fluensulfone
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is not expected to pose an aggregate
cancer risk.
6. Determination of safety. Based on
these risk assessments, EPA concludes
that there is a reasonable certainty that
no harm will result to the general
population, or to infants and children
from aggregate exposure to fluensulfone
residues.
IV. Other Considerations
A. Analytical Enforcement Methodology
An enforcement analytical method for
the BSA metabolite was previously
submitted and found to be acceptable.
The method extracts residues from
matrices into an acetonitrile-based
solvent, involves minimal cleanup, and
uses high-performance liquid
chromatography with tandem mass
spectrometric detection (LC–MS/MS) in
negative-ion mode to isolate, identify
and quantify residues. For all matrices
and analytes, the limit of quantitation
(LOQ), defined as the lowest level of
method validation (LLMV), was 0.01
ppm. With the change to the tolerance
expression, an enforcement method is
now needed for parent fluensulfone. A
method for analysis of fluensulfone
residues was previously submitted and
has been found to be suitable for
enforcement. The method is essentially
identical to that used for BSA analysis
but omits the cleanup step and uses LC–
MS/MS in the positive-ion mode for
isolation, identification, and
quantification of residues.
The FDA multi-residue protocols are
not suitable for the analysis of
fluensulfone or its metabolites BSA and
TSA. The Agency notes that QuEChERS
multi-residue method may be suitable
for the analysis of these compounds,
based on extraction solvents and cleanup strategies being similar to the
analytical method described above.
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.
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
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Organization/World Health
Organization food standards program,
and it is recognized as an international
food safety standards-setting
organization in trade agreements to
which the United States is a party. EPA
may establish a tolerance that is
different from a Codex MRL; however,
FFDCA section 408(b)(4) requires that
EPA explain the reasons for departing
from the Codex level.
The Codex has not established a MRL
for fluensulfone for citrus.
The Codex has established MRLs for
fluensulfone in or on some of the
commodities or parts of some of the
crop groups that are being revised in
this document. The U.S. tolerances are
harmonized with the Codex MRLs to the
extent possible. In several cases (below),
there is disharmony between U.S. crop
group tolerances and Codex MRLs for
Tolerance
(ppm) U.S.
Commodity
Brassica, leafy green, subgroup 5B ...........................................
Vegetables, cucurbits, group 9 ...................................................
Vegetables, leafy, except Brassica, group 4 ..............................
Vegetables, leaves of root and tuber, group 2, except sugar
beet.
Vegetables, root, except sugar beet, subgroup 1B ...................
C. Response to Comments
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One comment generally opposing the
use of fluensulfone was received in
response to the notice of filing for citrus
and peanut uses (EPA–HQ–OPP–2017–
0572). Although the Agency recognizes
that some individuals believe that
pesticides should be banned on
agricultural crops, the existing legal
framework provided by section 408 of
the Federal Food, Drug and Cosmetic
Act (FFDCA) authorizes EPA to
establish tolerances when it determines
that the tolerance is safe. Upon
consideration of the validity,
completeness, and reliability of the
available data as well as other factors
the FFDCA requires EPA to consider,
EPA has determined that these
fluensulfone tolerances are safe. The
commenter has provided no information
supporting a contrary conclusion.
One comment was received in
response to the notice of filing to amend
the tolerance expression for
fluensulfone to harmonize with the
Codex residue definition (EPA–HQ–
OPP–2018–0793). The commenter
supported the federal government
regulating the chemicals in pesticides
and specifically wanted EPA to set
higher safety standards for pesticides.
As explained in the previous paragraph,
EPA evaluated fluensulfone using the
existing safety standard in the FFDCA
and has determined that these
fluensulfone tolerances are safe.
D. Revisions to Petitioned-For
Tolerances
For stone fruit (Crop Group 12–12)
and sugarcane, the tolerances being
established by the Agency are derived
using the Organization for Economic
Cooperation and Development (OECD)
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0.70
4.0
50
4.0
MRL (mg/kg) Codex
1 (Group of leafy vegetables) 9 (Komatsuna).
0.3 (Melons, except watermelon).
1 (Group of leafy vegetables).
1 (Group of leafy vegetables) 10 (Turnip greens).
3 (Root and tuber vegetables).
MRL calculation procedures and based
on available residue data.
The tolerance for tree nuts is based on
the requested revision to the tolerance
expression. As such, it is the
combination of 0.01 ppm BSA and 0.01
ppm fluensulfone, resulting in the level
of 0.02 ppm as opposed to the proposed
0.04 ppm.
Inadvertent tolerances in barley bran
and wheat bran are being revised to 0.15
ppm (based on the OECD calculation
procedure rounding classes), rather than
the proposed tolerances at 0.14 ppm.
The petitioner had requested a higher
tolerance for inadvertent residues on
teosinte grain than the tolerance level
set for crop group 15, based on the
residue data used to establish the higher
tolerance for wheat grain. These higher
tolerances are based on residue data that
indicate higher tolerances are necessary
for crops for which the pesticide label
permits a shorter plant-back interval
(i.e., wheat, barley, buckwheat, oats).
For other crops, including teosinte, the
pesticide label establishes a longer
plant-back interval, and associated
residue data indicate that such intervals
result in lower residues on those crops.
It is this latter set of residue data and
the pesticide label instructions for
plant-back intervals that support the
crop group 15 tolerance as well as the
Agency’s conclusion that residues in
teosinte will be covered by the crop
group 15 tolerance. A tolerance in wheat
milled byproducts is being established
at 0.15 ppm (based on the OECD
calculation procedure rounding classes);
because a tolerance on wheat milled
byproducts covers residues in both
wheat shorts and wheat middlings,
tolerances on those individual
commodities are unnecessary.
PO 00000
Frm 00056
Fmt 4700
individual commodities covered by the
crop group. Because EPA has data
supporting the establishment of the crop
groups and no data that indicate a need
to establish separate individual
commodities, the effect is that
tolerances for some individual
commodities are not harmonized with
Codex MRLs.
Sfmt 4700
Although the petitioner did not
request a revision of the existing grape,
raisin tolerance, EPA is modifying that
tolerance to 1.5 ppm. As noted in 40
CFR 180.40(f)(1), EPA will not establish
crop group tolerances unless necessary
tolerances for processed foods are also
established. In this action, the petitioner
has requested an increase in the
tolerance for subgroup 13–07D, which
includes grape. Based on available data,
EPA has determined that an amended
tolerance for grape, raisin would be
necessary. This tolerance is derived
from the revised highest average field
trial (HAFT) of 0.49 ppm from the grape
field trials, using the revised residue
definition (fluensulfone + BSA, in terms
of fluensulfone), multiplied by the
median processing factor for raisins
from the processing study (2.7X),
resulting in 1.32 ppm; therefore, a
tolerance of 1.5 ppm in raisin is
appropriate.
For citrus, EPA used processing
factors of 233X for fluensulfone and
<0.5X for BSA in citrus oil. Application
of these processing factors and OECD
MRL rounding classes indicates that
residues will concentrate in dried pulp
at higher levels than requested as well
as in citrus oil. In accordance with 40
CFR 180.40(f)(1), EPA is establishing a
tolerance for fruit, citrus, group 10–10,
oil at 15 ppm. Based on the Agency’s
calculations, EPA is also establishing
the proposed tolerance for citrus, dried
pulp as a tolerance for fruit, citrus,
group 10–10, dried pulp at 0.9 ppm,
rather than 0.4 ppm.
Although the petitioner requested
tolerances on peanut commodities, after
EPA determined that the submitted field
trial data were not adequate to support
a tolerance the petitioner withdrew its
request for those tolerances; therefore,
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EPA is not establishing tolerances for
residues on peanut; peanut, hay; or
peanut, meal.
calculated as the stoichiometric
equivalent of fluensulfone, in or on the
commodity.’’
V. Conclusion
Therefore, tolerances are established
for residues of fluensulfone, and its
metabolite BSA expressed as
fluensulfone equivalents, in or on fruit,
citrus, group 10–10 at 0.3 ppm; fruit,
citrus, group 10–10, dried pulp at 0.9
ppm; and fruit, citrus, group 10–10, oil
at 15 ppm.
Additionally, existing tolerances
under paragraphs (a) and (d) are revised
as follows for residues of fluensulfone,
and its metabolite BSA expressed as
fluensulfone equivalents, as follows:
Paragraph (a): Almond, hulls at 5 ppm;
berry, low growing, subgroup 13–07G at
0.5 ppm; Brassica, head and stem,
subgroup 5A at 1.5 ppm; Brassica, leafy
greens, subgroup 5B at 20 ppm; fruit,
pome, group 11–10 at 0.4 ppm; fruit,
small, vine climbing, subgroup 13–07D
at 0.8 ppm; fruit, stone, group 12–12 at
0.15 ppm; grape, raisin at 1.5 ppm; nut,
tree, group 14–12 at 0.02 ppm; potato,
chips at 2 ppm; potato, granules/flakes
at 2 ppm; sugarcane, cane at 0.06 ppm;
sugarcane, molasses at 0.3 ppm; tomato,
paste at 1.5 ppm; vegetables, cucurbits,
group 9 at 0.7 ppm; vegetables, fruiting,
group 8–10 at 0.7 ppm; vegetables, leafy,
except Brassica, group 4 at 4 ppm;
vegetables, leaves of root and tuber,
group 2, except sugar beet at 50 ppm;
vegetables, root, except sugar beet,
subgroup 1B at 4 ppm; and vegetables,
tuberous and corm, subgroup 1C at 0.8
ppm; Paragraph (d): barley, bran at 0.15
ppm; barley, grain at 0.1 ppm; barley,
hay at 15 ppm; barley, straw at 6 ppm;
buckwheat, grain at 0.1 ppm; grain,
cereal, forage, fodder and straw, group
16 at 3 ppm; grain, cereal, group 15 at
0.05 ppm; oat, forage at 6 ppm; oat,
grain at 0.1 ppm; oat, hay at 15 ppm;
oat, straw at 6 ppm; wheat, bran at 0.15
ppm; wheat, forage at 6 ppm; wheat,
germ at 0.1 ppm; wheat, grain at 0.1
ppm; wheat, hay at 15 ppm; wheat,
milled byproducts at 0.15 ppm; and
wheat, straw at 6 ppm.
Lastly, the tolerance expressions for
fluensulfone currently established
under 40 CFR 180.680 (a) and (d) are
revised to read as follows ‘‘Tolerances
are established for residues of the
nematicide fluensulfone, including its
metabolites and degradates, in or on the
commodities in the table below.
Compliance with the tolerance levels
specified in the following table below is
to be determined by measuring only the
sum of fluensulfone, 5-chloro-2-[(3,4,4trifluoro-3-buten-1-yl)sulfonyl]thiazole
and its metabolite,
3,4,4-trifluoro-but-3-ene-1-sulfonic acid,
VI. Statutory and Executive Order
Reviews
This action establishes and modifies
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,
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16:08 May 23, 2019
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24047
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: May 16, 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. Revise § 180.680 to read as follows:
§ 180.680 Fluensulfone; tolerances for
residues.
(a) General. Tolerances are
established for residues of the
nematicide fluensulfone, including its
metabolites and degradates, in or on the
commodities in the table 1 to § 180.680.
Compliance with the tolerance levels
specified in the following table below is
to be determined by measuring only the
sum of fluensulfone, 5-chloro-2-[(3,4,4trifluoro-3-buten-1-yl)sulfonyl]thiazole
and its metabolite,
3,4,4-trifluoro-but-3-ene-1-sulfonic acid,
calculated as the stoichiometric
equivalent of fluensulfone, in or on the
commodity.
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TABLE 1 TO § 180.680
Parts
per
million
Commodity
khammond on DSKBBV9HB2PROD with RULES
Almond, hulls ....................................
Berry, low growing, subgroup 13–
07G ...............................................
Brassica, head and stem, subgroup
5A ..................................................
Brassica, leafy greens, subgroup 5B
Fruit, citrus, group 10–10 .................
Fruit, citrus, group 10–10, dried pulp
Fruit, citrus, group 10–10, oil ...........
Fruit, pome, group 11–10 .................
Fruit, small, vine climbing, subgroup
13–07D ..........................................
Fruit, stone, group 12–12 .................
Grape, raisin .....................................
Nut, tree, group 14–12 .....................
Potato, chips .....................................
Potato, granules/flakes .....................
Sugarcane, cane ..............................
Sugarcane, molasses .......................
Tomato, paste ...................................
Vegetables, cucurbits, group 9 .........
Vegetables, fruiting, group 8–10 ......
Vegetables, leafy, except Brassica,
group 4 ..........................................
Vegetables, leaves of root and
tuber, group 2, except sugar beet
VerDate Sep<11>2014
16:08 May 23, 2019
equivalent of fluensulfone, in or on the
commodity.
TABLE 1 TO § 180.680—Continued
Jkt 247001
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0.5
1.5
20
0.3
0.9
15
0.4
0.8
0.15
1.5
0.02
2
2
0.06
0.3
1.5
0.7
0.7
4
50
Parts
per
million
Commodity
Vegetables, root, except sugar beet,
subgroup 1B ..................................
Vegetables, tuberous and corm,
subgroup 1C .................................
Frm 00058
Fmt 4700
Sfmt 9990
Commodity
4
0.8
(b) Section 18 emergency exemptions.
[Reserved]
(c) Tolerances with regional
registrations. [Reserved]
(d) Indirect or inadvertent residues.
Tolerances are established for residues
of the nematicide fluensulfone,
including its metabolites and
degradates, in or on the commodities in
table 2 to § 180.680. Compliance with
the tolerance levels specified in the
following table below is to be
determined by measuring only the sum
of fluensulfone, 5-chloro-2-[(3,4,4trifluoro-3-buten-1-yl)sulfonyl]thiazole
and its metabolite,
3,4,4-trifluoro-but-3-ene-1-sulfonic acid,
calculated as the stoichiometric
PO 00000
TABLE 2 TO § 180.680
Parts
per
million
Barley, bran ......................................
Barley, grain .....................................
Barley, hay ........................................
Barley, straw .....................................
Buckwheat, grain ..............................
Grain, cereal, forage, fodder and
straw, group 16 .............................
Grain, cereal, group 15 ....................
Oat, forage ........................................
Oat, grain ..........................................
Oat, hay ............................................
Oat, straw .........................................
Wheat, bran ......................................
Wheat, forage ...................................
Wheat, germ .....................................
Wheat, grain .....................................
Wheat, hay .......................................
Wheat, milled byproducts .................
Wheat, straw .....................................
[FR Doc. 2019–10793 Filed 5–23–19; 8:45 am]
BILLING CODE 6560–50–P
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Agencies
[Federal Register Volume 84, Number 101 (Friday, May 24, 2019)]
[Rules and Regulations]
[Pages 24042-24048]
From the Federal Register Online via the Government Publishing Office [www.gpo.gov]
[FR Doc No: 2019-10793]
[[Page 24042]]
-----------------------------------------------------------------------
ENVIRONMENTAL PROTECTION AGENCY
40 CFR Part 180
[EPA-HQ-OPP-2017-0572; FRL-9992-69]
Fluensulfone; Pesticide Tolerances
AGENCY: Environmental Protection Agency (EPA).
ACTION: Final rule.
-----------------------------------------------------------------------
SUMMARY: This regulation establishes and amends tolerances for residues
of fluensulfone in or on multiple commodities which are identified and
discussed later in this document. Makhteshim Agan of North America (d/
b/a ADAMA) requested these tolerances and tolerance amendments under
the Federal Food, Drug, and Cosmetic Act (FFDCA).
DATES: This regulation is effective May 24, 2019. Objections and
requests for hearings must be received on or before July 23, 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-2017-0572, 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 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-2017-0572 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
July 23, 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-2017-0572, 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 February 27, 2018 (83 FR 8408) (FRL-
9972-17), 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
7F8614) by Makhteshim Agan of North America d/b/a ADAMA, 3120 Highlands
Blvd., Suite 100, Raleigh, NC 27604. The petition requested that 40 CFR
part 180 be amended by establishing tolerances for residues of the
nematicide, fluensulfone, including its metabolites and degradates, in
or on the following commodities: Citrus dried pulp at 0.4 parts per
million (ppm); Crop Group 10-10, citrus fruit at 0.15 ppm; peanut at
0.15 ppm; peanut, hay at 8.0 ppm; and peanut, meal at 0.30 ppm. That
document referenced a summary of the petition prepared by Makhteshim
Agan of North America, the registrant, which is available in docket ID
number EPA-HQ-OPP-2017-0572 at https://www.regulations.gov. One comment
was received on the notice of filing. EPA's response to this comment is
discussed in Unit IV.C.
In the Federal Register of May 18, 2018 (83 FR 23247) (FRL-9976-
87), 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
7F8650) by Makhteshim Agan of North America, d/b/a ADAMA, 3120
Highlands Blvd., Suite 100, Raleigh, NC 27604. The petition requested
to amend the tolerances in 40 CFR 180.680 for residues of the
nematicide, fluensulfone and its metabolite BSA expressed as
fluensulfone equivalents, in or on Berry, low growing, subgroup 13-07G
at 0.5 parts per million (ppm); Brassica, head and stem, subgroup 5A at
1.5 ppm; Brassica, leafy greens, subgroup 5B at 20 ppm; Potato, chips
at 2 ppm; Potato, granules/flakes at 2 ppm; Tomato, paste at 1.5 ppm;
Vegetables, cucurbits, group 9 at 0.7 ppm; Vegetables, fruiting, group
8-10 at 0.7 ppm; Vegetables, leafy, except Brassica, group 4 at 4 ppm;
Vegetables, leaves of root and tuber, group 2, except sugar beet at 50
ppm;
[[Page 24043]]
Vegetables, root, except sugar beet, subgroup 1B at 4 ppm; and
Vegetables, tuberous and corm, subgroup 1C at 0.8 ppm. That document
referenced a summary of the petition prepared by Makhteshim Agan of
North America, the registrant, which is available in docket ID number
EPA-HQ-OPP-2018-0030 at https://www.regulations.gov. There were no
comments received in response to the notice of filing.
In the Federal Register of March 18, 2019 (84 FR 9737) (FRL-9989-
71), 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
7F8650) by Makhteshim Agan of North America, d/b/a ADAMA, 3120
Highlands Blvd., Suite 100, Raleigh, NC 27604. The petition requested
to: (1) Amend the tolerance expression in 40 CFR 180.680 paragraphs (a)
and (d) to read ``Tolerances are established for residues of the
nematicide fluensulfone, including its metabolites and degradates, in
or on the commodities in the table below. Compliance with the tolerance
levels specified in the following table below is to be determined by
measuring only the sum of fluensulfone, 5-chloro-2-[(3,4,4-trifluoro-3-
buten-1-yl)sulfonyl]thiazole and its metabolite, 3,4,4-trifluoro-but-3-
ene-1-sulfonic acid, calculated as the stoichiometric equivalent of
fluensulfone, in or on the commodity''; and (2) amend the tolerances in
40 CFR 180.680 for residues of the nematicide, fluensulfone and its
metabolite BSA expressed as fluensulfone equivalents, on the raw
agricultural commodities as follows: Almond hulls at 5 parts per
million (ppm); Fruit, pome, group 11 at 0.4 ppm; Fruit, small vine
climbing subgroup 13-07D at 0.8 ppm; Fruit, stone, group 12 at 0.1 ppm;
Grain cereal, forage, fodder and straw, group 16 at 3 ppm; and, rotated
wheat (inadvertent residues with 90-day PBI): Grain, cereal, group 15
at 0.05 ppm; Molasses at 0.3 ppm; and, rotated cereal grains
(inadvertent residues with 10-month PBI): Nut, tree, group 14 at 0.04
ppm; Sugarcane at 0.05 ppm and Wheat grain (includes triticale) (Barley
grain; Buckwheat grain; Oat grain; and Teosinte grain) at 0.1 ppm;
Wheat bran (Barley bran) at 0.14 ppm; Wheat forage (Oat forage) at 6
ppm; Wheat germ at 0.10 ppm; Wheat hay (Barley hay and Oat hay) at 15
ppm; Wheat middlings at 0.10 ppm; Wheat shorts at 0.11 ppm; and, Wheat
straw (Barley straw and Oat straw) at 6 ppm. That document referenced a
summary of the petition prepared by Makhteshim Agan of North America,
the registrant, which is available in docket ID number EPA-HQ-OPP-2018-
0793 at https://www.regulations.gov. One comment was received on the
notice of filing. EPA's response to this comment is discussed in Unit
IV.C.
Based upon review of the data supporting the petitions, EPA has
modified the levels at which tolerances are being established as well
as which commodities will have tolerances. The reasons for these
changes are explained in Unit IV.D.
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 fluensulfone including exposure
resulting from the tolerances established by this action. EPA's
assessment of exposures and risks associated with fluensulfone 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.
A summary of the toxicological effects of fluensulfone are
discussed in the final rule published in the Federal Register of April
13, 2018 (83 FR 15971) (FRL-9975-76).
Specific information on the studies received and the nature of the
adverse effects caused by fluensulfone 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 the document titled ``Fluensulfone--Aggregate
Human Health Risk Assessment in Support of Section 3 Registration of
New Uses on Citrus and Peanut, and Change in the Tolerance Expression''
on pages 39-49 in docket ID number EPA-HQ-OPP-2017-0572.
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 fluensulfone used for
human risk assessment is discussed in Unit III.B. of the final rule
published in the Federal Register of June 1, 2016 (81 FR 34898) (FRL-
9946-07).
C. Exposure Assessment
1. Dietary exposure from food and feed uses. In evaluating dietary
exposure to fluensulfone, EPA considered exposure under the petitioned-
for tolerances as well as all
[[Page 24044]]
existing fluensulfone tolerances in 40 CFR 180.680. EPA assessed
dietary exposures from fluensulfone in food as follows:
i. Acute exposure. Quantitative acute dietary exposure and risk
assessments are performed for a food-use pesticide, if a toxicological
study has indicated the possibility of an effect of concern occurring
as a result of a 1-day or single exposure.
Such effects were identified for fluensulfone. In estimating acute
dietary exposure, EPA used 2003-2008 food consumption information from
the United States Department of Agriculture (USDA) National Health and
Nutrition Examination Survey, What We Eat in America, (NHANES/WWEIA).
As to residue levels in food, the acute dietary risk assessment assumed
tolerance-equivalent residues and 100 percent crop treated (PCT).
ii. Chronic exposure. In conducting the chronic dietary exposure
assessment EPA used 2003-2008 food consumption information from the
USDA's NHANES/WWEIA. As to residue levels in food, the chronic dietary
risk assessment assumed tolerance-equivalent residues and 100 PCT.
iii. Cancer. Based on the data summarized in Unit III.A., EPA has
concluded that a nonlinear RfD approach is appropriate for assessing
cancer risk to fluensulfone. Cancer risk was assessed using the same
exposure estimates as discussed in Unit III.C.1.ii., chronic exposure.
iv. Anticipated residue and PCT information. EPA did not use
anticipated residue or PCT information in the dietary assessment for
fluensulfone. Tolerance-equivalent residue levels and 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 fluensulfone in drinking water. These simulation models
take into account data on the physical, chemical, and fate/transport
characteristics of fluensulfone. 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.
Based on the Pesticide Root Zone Model/Exposure Analysis Modeling
System (PRZM/EXAMS) and Pesticide Root Zone Model Ground Water (PRZM
GW) models, the estimated drinking water concentrations (EDWCs) for
acute exposures are estimated to be 11.8 parts per billion (ppb) for
surface water and 77.6 ppb for ground water and for chronic exposures
are estimated to be 0.173 ppb for surface water and 52.5 ppb for ground
water. Modeled estimates of drinking water concentrations were directly
entered into the dietary exposure model. For the acute dietary risk
assessment, the water concentration value of 77.6 ppb was used to
assess the contribution to drinking water. For the chronic dietary risk
assessment, the water concentration of value 52.5 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).
Fluensulfone is currently registered for the following uses that
could result in residential exposures: Golf courses and residential
lawns. EPA assessed residential exposure using the following
assumptions: No residential handler exposure for fluensulfone is
expected because the products are not intended for homeowner use. The
product label requires that handlers wear specific clothing (e.g., long
sleeve shirt/long pants) and/or personal protective equipment (PPE).
The Agency has made the assumption that the product is not for
homeowner use and is intended for use by professional applicators. As a
result, a residential handler assessment has not been conducted.
For adult residential post-application exposure, the Agency
evaluated dermal post-application exposure only to outdoor turf/lawn
applications (high contact activities). The Agency also evaluated
residential post-application exposure for children via dermal and hand-
to-mouth routes of exposure, resulting from treated outdoor turf/lawn
applications (high contact activities). 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 fluensulfone to share a common mechanism of
toxicity with any other substances, and fluensulfone does not appear to
produce a toxic metabolite produced by other substances. For the
purposes of this tolerance action, therefore, EPA has assumed that
fluensulfone 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. No evidence of increased
quantitative or qualitative susceptibility was seen in developmental
toxicity studies in rats and rabbits. Fetal effects in those studies
occurred in the presence of maternal toxicity and were not considered
more severe than the maternal effects. However, there was evidence of
increased qualitative, but not quantitative, susceptibility of pups in
the 2-generation reproduction study in rats. Maternal effects observed
in that study were decreased body weight; at the same dose, effects in
offspring were decreased pup weights, decreased spleen weight, and
increased pup loss (post-natal day 1-4). Although there is evidence of
increased qualitative susceptibility in the 2-generation reproduction
study in rats, there are no residual uncertainties with regard to pre-
and post-natal toxicity following in utero exposure to rats or rabbits
and pre- and post-natal exposures to rats. Considering the overall
toxicity profile, the clear NOAEL for the pup effects observed in the
2-generation reproduction study, and that the doses selected for risk
assessment are protective of all effects in the toxicity database
including the offspring effects,
[[Page 24045]]
the degree of concern for the susceptibility is low.
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. That decision is based on the following
findings:
i. The toxicity database for fluensulfone is complete.
ii. Evidence of potential neurotoxicity was only seen following
acute exposure to fluensulfone and the current PODs chosen for risk
assessment are protective of the effects observed. There is no need for
a developmental neurotoxicity study or additional UFs to account for
neurotoxicity.
iii. There is no indication of quantitative susceptibility in the
developmental and reproductive toxicity studies, and there are no
residual uncertainties concerning pre- or post-natal toxicity. In
addition, the endpoints and doses chosen for risk assessment are
protective of the qualitative susceptibility observed in the 2-
generation reproduction study.
iv. There are no residual uncertainties identified in the exposure
databases. The dietary food exposure assessments were performed based
on 100 PCT and tolerance-equivalent residue levels. EPA made
conservative (protective) assumptions in the ground and surface water
modeling used to assess exposure to fluensulfone in drinking water. EPA
used similarly conservative assumptions to assess post-application
exposure of children as well as incidental oral exposure of toddlers.
These assessments will not underestimate the exposure and risks posed
by fluensulfone.
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. Using the exposure assumptions discussed in this
unit for acute exposure, the acute dietary exposure from food and water
to fluensulfone will occupy 9.4% of the aPAD for all infants less than
1 year old, the population group receiving the greatest exposure.
2. Chronic risk. Using the exposure assumptions described in this
unit for chronic exposure, EPA has concluded that chronic exposure to
fluensulfone from food and water will utilize 4.1% of the cPAD for all
infants less than 1 year old, the population group receiving the
greatest exposure. Based on the explanation in Unit III.C.3., regarding
residential use patterns, chronic residential exposure to residues of
fluensulfone is not expected.
3. Short-term risk. Short-term aggregate exposure takes into
account short-term residential exposure plus chronic exposure to food
and water (considered to be a background exposure level).
Fluensulfone is currently registered for uses that could result in
short-term residential exposure, and the Agency has determined that it
is appropriate to aggregate chronic exposure through food and water
with short-term residential exposures to fluensulfone.
Using the exposure assumptions described in this unit for short-
term exposures, EPA has concluded the combined short-term food, water,
and residential exposures result in aggregate MOEs of 5300 for adults
and 2500 for children. Because EPA's level of concern for fluensulfone
is a MOE of 100 or below, these MOEs are not of concern.
4. Intermediate-term risk. Intermediate-term aggregate exposure
takes into account intermediate-term residential exposure plus chronic
exposure to food and water (considered to be a background exposure
level).
An intermediate-term adverse effect was identified; however,
fluensulfone is not registered for any use patterns that would result
in intermediate-term residential exposure. Intermediate-term risk is
assessed based on intermediate-term residential exposure plus chronic
dietary exposure. Because there is no intermediate-term residential
exposure and chronic dietary exposure has already been assessed under
the appropriately protective cPAD (which is at least as protective as
the POD used to assess intermediate-term risk), no further assessment
of intermediate-term risk is necessary, and EPA relies on the chronic
dietary risk assessment for evaluating intermediate-term risk for
fluensulfone.
5. Aggregate cancer risk for U.S. population. EPA assessed cancer
risk using a non-linear approach (i.e., RfD) since it adequately
accounts for all chronic toxicity, including carcinogenicity, that
could result from exposure to fluensulfone. As the chronic dietary
endpoint and dose are protective of potential cancer effects,
fluensulfone is not expected to pose an aggregate cancer risk.
6. Determination of safety. Based on these risk assessments, EPA
concludes that there is a reasonable certainty that no harm will result
to the general population, or to infants and children from aggregate
exposure to fluensulfone residues.
IV. Other Considerations
A. Analytical Enforcement Methodology
An enforcement analytical method for the BSA metabolite was
previously submitted and found to be acceptable. The method extracts
residues from matrices into an acetonitrile-based solvent, involves
minimal cleanup, and uses high-performance liquid chromatography with
tandem mass spectrometric detection (LC-MS/MS) in negative-ion mode to
isolate, identify and quantify residues. For all matrices and analytes,
the limit of quantitation (LOQ), defined as the lowest level of method
validation (LLMV), was 0.01 ppm. With the change to the tolerance
expression, an enforcement method is now needed for parent
fluensulfone. A method for analysis of fluensulfone residues was
previously submitted and has been found to be suitable for enforcement.
The method is essentially identical to that used for BSA analysis but
omits the cleanup step and uses LC-MS/MS in the positive-ion mode for
isolation, identification, and quantification of residues.
The FDA multi-residue protocols are not suitable for the analysis
of fluensulfone or its metabolites BSA and TSA. The Agency notes that
QuEChERS multi-residue method may be suitable for the analysis of these
compounds, based on extraction solvents and clean-up strategies being
similar to the analytical method described above.
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
[[Page 24046]]
Organization/World Health Organization food standards program, and it
is recognized as an international food safety standards-setting
organization in trade agreements to which the United States is a party.
EPA may establish a tolerance that is different from a Codex MRL;
however, FFDCA section 408(b)(4) requires that EPA explain the reasons
for departing from the Codex level.
The Codex has not established a MRL for fluensulfone for citrus.
The Codex has established MRLs for fluensulfone in or on some of
the commodities or parts of some of the crop groups that are being
revised in this document. The U.S. tolerances are harmonized with the
Codex MRLs to the extent possible. In several cases (below), there is
disharmony between U.S. crop group tolerances and Codex MRLs for
individual commodities covered by the crop group. Because EPA has data
supporting the establishment of the crop groups and no data that
indicate a need to establish separate individual commodities, the
effect is that tolerances for some individual commodities are not
harmonized with Codex MRLs.
------------------------------------------------------------------------
Tolerance
Commodity (ppm) U.S. MRL (mg/kg) Codex
------------------------------------------------------------------------
Brassica, leafy green, subgroup 5B 20 1 (Group of leafy
vegetables) 9
(Komatsuna).
Vegetables, cucurbits, group 9.... 0.70 0.3 (Melons, except
watermelon).
Vegetables, leafy, except 4.0 1 (Group of leafy
Brassica, group 4. vegetables).
Vegetables, leaves of root and 50 1 (Group of leafy
tuber, group 2, except sugar beet. vegetables) 10
(Turnip greens).
Vegetables, root, except sugar 4.0 3 (Root and tuber
beet, subgroup 1B. vegetables).
------------------------------------------------------------------------
C. Response to Comments
One comment generally opposing the use of fluensulfone was received
in response to the notice of filing for citrus and peanut uses (EPA-HQ-
OPP-2017-0572). Although the Agency recognizes that some individuals
believe that pesticides should be banned on agricultural crops, the
existing legal framework provided by section 408 of the Federal Food,
Drug and Cosmetic Act (FFDCA) authorizes EPA to establish tolerances
when it determines that the tolerance is safe. Upon consideration of
the validity, completeness, and reliability of the available data as
well as other factors the FFDCA requires EPA to consider, EPA has
determined that these fluensulfone tolerances are safe. The commenter
has provided no information supporting a contrary conclusion.
One comment was received in response to the notice of filing to
amend the tolerance expression for fluensulfone to harmonize with the
Codex residue definition (EPA-HQ-OPP-2018-0793). The commenter
supported the federal government regulating the chemicals in pesticides
and specifically wanted EPA to set higher safety standards for
pesticides. As explained in the previous paragraph, EPA evaluated
fluensulfone using the existing safety standard in the FFDCA and has
determined that these fluensulfone tolerances are safe.
D. Revisions to Petitioned-For Tolerances
For stone fruit (Crop Group 12-12) and sugarcane, the tolerances
being established by the Agency are derived using the Organization for
Economic Cooperation and Development (OECD) MRL calculation procedures
and based on available residue data.
The tolerance for tree nuts is based on the requested revision to
the tolerance expression. As such, it is the combination of 0.01 ppm
BSA and 0.01 ppm fluensulfone, resulting in the level of 0.02 ppm as
opposed to the proposed 0.04 ppm.
Inadvertent tolerances in barley bran and wheat bran are being
revised to 0.15 ppm (based on the OECD calculation procedure rounding
classes), rather than the proposed tolerances at 0.14 ppm.
The petitioner had requested a higher tolerance for inadvertent
residues on teosinte grain than the tolerance level set for crop group
15, based on the residue data used to establish the higher tolerance
for wheat grain. These higher tolerances are based on residue data that
indicate higher tolerances are necessary for crops for which the
pesticide label permits a shorter plant-back interval (i.e., wheat,
barley, buckwheat, oats). For other crops, including teosinte, the
pesticide label establishes a longer plant-back interval, and
associated residue data indicate that such intervals result in lower
residues on those crops. It is this latter set of residue data and the
pesticide label instructions for plant-back intervals that support the
crop group 15 tolerance as well as the Agency's conclusion that
residues in teosinte will be covered by the crop group 15 tolerance. A
tolerance in wheat milled byproducts is being established at 0.15 ppm
(based on the OECD calculation procedure rounding classes); because a
tolerance on wheat milled byproducts covers residues in both wheat
shorts and wheat middlings, tolerances on those individual commodities
are unnecessary.
Although the petitioner did not request a revision of the existing
grape, raisin tolerance, EPA is modifying that tolerance to 1.5 ppm. As
noted in 40 CFR 180.40(f)(1), EPA will not establish crop group
tolerances unless necessary tolerances for processed foods are also
established. In this action, the petitioner has requested an increase
in the tolerance for subgroup 13-07D, which includes grape. Based on
available data, EPA has determined that an amended tolerance for grape,
raisin would be necessary. This tolerance is derived from the revised
highest average field trial (HAFT) of 0.49 ppm from the grape field
trials, using the revised residue definition (fluensulfone + BSA, in
terms of fluensulfone), multiplied by the median processing factor for
raisins from the processing study (2.7X), resulting in 1.32 ppm;
therefore, a tolerance of 1.5 ppm in raisin is appropriate.
For citrus, EPA used processing factors of 233X for fluensulfone
and <0.5X for BSA in citrus oil. Application of these processing
factors and OECD MRL rounding classes indicates that residues will
concentrate in dried pulp at higher levels than requested as well as in
citrus oil. In accordance with 40 CFR 180.40(f)(1), EPA is establishing
a tolerance for fruit, citrus, group 10-10, oil at 15 ppm. Based on the
Agency's calculations, EPA is also establishing the proposed tolerance
for citrus, dried pulp as a tolerance for fruit, citrus, group 10-10,
dried pulp at 0.9 ppm, rather than 0.4 ppm.
Although the petitioner requested tolerances on peanut commodities,
after EPA determined that the submitted field trial data were not
adequate to support a tolerance the petitioner withdrew its request for
those tolerances; therefore,
[[Page 24047]]
EPA is not establishing tolerances for residues on peanut; peanut, hay;
or peanut, meal.
V. Conclusion
Therefore, tolerances are established for residues of fluensulfone,
and its metabolite BSA expressed as fluensulfone equivalents, in or on
fruit, citrus, group 10-10 at 0.3 ppm; fruit, citrus, group 10-10,
dried pulp at 0.9 ppm; and fruit, citrus, group 10-10, oil at 15 ppm.
Additionally, existing tolerances under paragraphs (a) and (d) are
revised as follows for residues of fluensulfone, and its metabolite BSA
expressed as fluensulfone equivalents, as follows: Paragraph (a):
Almond, hulls at 5 ppm; berry, low growing, subgroup 13-07G at 0.5 ppm;
Brassica, head and stem, subgroup 5A at 1.5 ppm; Brassica, leafy
greens, subgroup 5B at 20 ppm; fruit, pome, group 11-10 at 0.4 ppm;
fruit, small, vine climbing, subgroup 13-07D at 0.8 ppm; fruit, stone,
group 12-12 at 0.15 ppm; grape, raisin at 1.5 ppm; nut, tree, group 14-
12 at 0.02 ppm; potato, chips at 2 ppm; potato, granules/flakes at 2
ppm; sugarcane, cane at 0.06 ppm; sugarcane, molasses at 0.3 ppm;
tomato, paste at 1.5 ppm; vegetables, cucurbits, group 9 at 0.7 ppm;
vegetables, fruiting, group 8-10 at 0.7 ppm; vegetables, leafy, except
Brassica, group 4 at 4 ppm; vegetables, leaves of root and tuber, group
2, except sugar beet at 50 ppm; vegetables, root, except sugar beet,
subgroup 1B at 4 ppm; and vegetables, tuberous and corm, subgroup 1C at
0.8 ppm; Paragraph (d): barley, bran at 0.15 ppm; barley, grain at 0.1
ppm; barley, hay at 15 ppm; barley, straw at 6 ppm; buckwheat, grain at
0.1 ppm; grain, cereal, forage, fodder and straw, group 16 at 3 ppm;
grain, cereal, group 15 at 0.05 ppm; oat, forage at 6 ppm; oat, grain
at 0.1 ppm; oat, hay at 15 ppm; oat, straw at 6 ppm; wheat, bran at
0.15 ppm; wheat, forage at 6 ppm; wheat, germ at 0.1 ppm; wheat, grain
at 0.1 ppm; wheat, hay at 15 ppm; wheat, milled byproducts at 0.15 ppm;
and wheat, straw at 6 ppm.
Lastly, the tolerance expressions for fluensulfone currently
established under 40 CFR 180.680 (a) and (d) are revised to read as
follows ``Tolerances are established for residues of the nematicide
fluensulfone, including its metabolites and degradates, in or on the
commodities in the table below. Compliance with the tolerance levels
specified in the following table below is to be determined by measuring
only the sum of fluensulfone, 5-chloro-2-[(3,4,4-trifluoro-3-buten-1-
yl)sulfonyl]thiazole and its metabolite,
3,4,4[hyphen]trifluoro[hyphen]but[hyphen]3[hyphen]ene[hyphen]1[hyphen]su
lfonic acid, calculated as the stoichiometric equivalent of
fluensulfone, in or on the commodity.''
VI. Statutory and Executive Order Reviews
This action establishes and modifies 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: May 16, 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. Revise Sec. 180.680 to read as follows:
Sec. 180.680 Fluensulfone; tolerances for residues.
(a) General. Tolerances are established for residues of the
nematicide fluensulfone, including its metabolites and degradates, in
or on the commodities in the table 1 to Sec. 180.680. Compliance with
the tolerance levels specified in the following table below is to be
determined by measuring only the sum of fluensulfone, 5-chloro-2-
[(3,4,4-trifluoro-3-buten-1-yl)sulfonyl]thiazole and its metabolite,
3,4,4[hyphen]trifluoro[hyphen]but[hyphen]3[hyphen]ene[hyphen]1[hyphen]su
lfonic acid, calculated as the stoichiometric equivalent of
fluensulfone, in or on the commodity.
[[Page 24048]]
Table 1 to Sec. 180.680
------------------------------------------------------------------------
Parts
Commodity per
million
------------------------------------------------------------------------
Almond, hulls.................................................. 5
Berry, low growing, subgroup 13-07G............................ 0.5
Brassica, head and stem, subgroup 5A........................... 1.5
Brassica, leafy greens, subgroup 5B............................ 20
Fruit, citrus, group 10-10..................................... 0.3
Fruit, citrus, group 10-10, dried pulp......................... 0.9
Fruit, citrus, group 10-10, oil................................ 15
Fruit, pome, group 11-10....................................... 0.4
Fruit, small, vine climbing, subgroup 13-07D................... 0.8
Fruit, stone, group 12-12...................................... 0.15
Grape, raisin.................................................. 1.5
Nut, tree, group 14-12......................................... 0.02
Potato, chips.................................................. 2
Potato, granules/flakes........................................ 2
Sugarcane, cane................................................ 0.06
Sugarcane, molasses............................................ 0.3
Tomato, paste.................................................. 1.5
Vegetables, cucurbits, group 9................................. 0.7
Vegetables, fruiting, group 8-10............................... 0.7
Vegetables, leafy, except Brassica, group 4.................... 4
Vegetables, leaves of root and tuber, group 2, except sugar 50
beet..........................................................
Vegetables, root, except sugar beet, subgroup 1B............... 4
Vegetables, tuberous and corm, subgroup 1C..................... 0.8
------------------------------------------------------------------------
(b) Section 18 emergency exemptions. [Reserved]
(c) Tolerances with regional registrations. [Reserved]
(d) Indirect or inadvertent residues. Tolerances are established
for residues of the nematicide fluensulfone, including its metabolites
and degradates, in or on the commodities in table 2 to Sec. 180.680.
Compliance with the tolerance levels specified in the following table
below is to be determined by measuring only the sum of fluensulfone, 5-
chloro-2-[(3,4,4-trifluoro-3-buten-1-yl)sulfonyl]thiazole and its
metabolite,
3,4,4[hyphen]trifluoro[hyphen]but[hyphen]3[hyphen]ene[hyphen]1[hyphen]su
lfonic acid, calculated as the stoichiometric equivalent of
fluensulfone, in or on the commodity.
Table 2 to Sec. 180.680
------------------------------------------------------------------------
Parts
Commodity per
million
------------------------------------------------------------------------
Barley, bran................................................... 0.15
Barley, grain.................................................. 0.1
Barley, hay.................................................... 15
Barley, straw.................................................. 6
Buckwheat, grain............................................... 0.1
Grain, cereal, forage, fodder and straw, group 16.............. 3
Grain, cereal, group 15........................................ 0.05
Oat, forage.................................................... 6
Oat, grain..................................................... 0.1
Oat, hay....................................................... 15
Oat, straw..................................................... 6
Wheat, bran.................................................... 0.15
Wheat, forage.................................................. 6
Wheat, germ.................................................... 0.1
Wheat, grain................................................... 0.1
Wheat, hay..................................................... 15
Wheat, milled byproducts....................................... 0.15
Wheat, straw................................................... 6
------------------------------------------------------------------------
[FR Doc. 2019-10793 Filed 5-23-19; 8:45 am]
BILLING CODE 6560-50-P