Fluopyram; Pesticide Tolerances, 12015-12024 [2016-05025]
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Federal Register / Vol. 81, No. 45 / Tuesday, March 8, 2016 / Rules and Regulations
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stoichiometric equivalent of zoxamide
in or on the raw agricultural commodity
ginseng at 0.30 ppm and vegetable,
tuberous and corm, subgroup 1C at 0.06
ppm. In addition, tolerances are
established for residues, determined by
measuring only zoxamide (3,5-dichloroN-(3-chloro-1-ethyl-1-methyl-2oxypropyl)-4-methylbenzamide, in or on
raw agricultural commodity tomato
subgroup 8–10A at 2.0 ppm and fruit,
small vine climbing, except fuzzy
kiwifruit, subgroup 13–07F at 5.0 ppm.
Lastly, upon the establishment of the
aforementioned tolerances, the
established tolerances for grape at 3.0
ppm; tomato at 2.0 ppm; and potato at
0.060 ppm are removed as unnecessary.
VI. Statutory and Executive Order
Reviews
This action establishes tolerances
under FFDCA section 408(d) in
response to a petition submitted to the
Agency. The Office of Management and
Budget (OMB) has exempted these types
of actions from review under Executive
Order 12866, entitled ‘‘Regulatory
Planning and Review’’ (58 FR 51735,
October 4, 1993). Because this action
has been exempted from review under
Executive Order 12866, this action is
not subject to Executive Order 13211,
entitled ‘‘Actions Concerning
Regulations That Significantly Affect
Energy Supply, Distribution, or Use’’ (66
FR 28355, May 22, 2001) or Executive
Order 13045, entitled ‘‘Protection of
Children from Environmental Health
Risks and Safety Risks’’ (62 FR 19885,
April 23, 1997). This action does not
contain any information collections
subject to OMB approval under the
Paperwork Reduction Act (PRA) (44
U.S.C. 3501 et seq.), nor does it require
any special considerations under
Executive Order 12898, entitled
‘‘Federal Actions to Address
Environmental Justice in Minority
Populations and Low-Income
Populations’’ (59 FR 7629, February 16,
1994).
Since tolerances and exemptions that
are established on the basis of a petition
under FFDCA section 408(d), such as
the tolerance in this final rule, do not
require the issuance of a proposed rule,
the requirements of the Regulatory
Flexibility Act (RFA) (5 U.S.C. 601 et
seq.), do not apply.
This action directly regulates growers,
food processors, food handlers, and food
retailers, not States or tribes, nor does
this action alter the relationships or
distribution of power and
responsibilities established by Congress
in the preemption provisions of FFDCA
section 408(n)(4). As such, the Agency
has determined that this action will not
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have a substantial direct effect on States
or tribal governments, on the
relationship between the national
government and the States or tribal
governments, or on the distribution of
power and responsibilities among the
various levels of government or between
the Federal Government and Indian
tribes. Thus, the Agency has determined
that Executive Order 13132, entitled
‘‘Federalism’’ (64 FR 43255, August 10,
1999) and Executive Order 13175,
entitled ‘‘Consultation and Coordination
with Indian Tribal Governments’’ (65 FR
67249, November 9, 2000) do not apply
to this action. In addition, this action
does not impose any enforceable duty or
contain any unfunded mandate as
described under Title II of the Unfunded
Mandates Reform Act (UMRA) (2 U.S.C.
1501 et seq.).
This action does not involve any
technical standards that would require
Agency consideration of voluntary
consensus standards pursuant to section
12(d) of the National Technology
Transfer and Advancement Act
(NTTAA) (15 U.S.C. 272 note).
VII. Congressional Review Act
Pursuant to the Congressional Review
Act (5 U.S.C. 801 et seq.), EPA will
submit a report containing this rule and
other required information to the U.S.
Senate, the U.S. House of
Representatives, and the Comptroller
General of the United States prior to
publication of the rule in the Federal
Register. This action is not a ‘‘major
rule’’ as defined by 5 U.S.C. 804(2).
List of Subjects in 40 CFR Part 180
Environmental protection,
Administrative practice and procedure,
Agricultural commodities, Pesticides
and pests, Reporting and recordkeeping
requirements.
Dated: February 25, 2016.
Susan Lewis,
Director, Registration Division, Office of
Pesticide Programs.
Therefore, 40 CFR chapter I is
amended as follows:
PART 180—[AMENDED]
1. The authority citation for part 180
continues to read as follows:
■
Authority: 21 U.S.C. 321(q), 346a and 371.
2. In § 180.567:
a. In the table in paragraph (a)(1):
i. Add alphabetically entries for
‘‘Fruit, small vine climbing’’ and
‘‘Tomato subgroup 8–10A’’; and
■ ii. Remove the entries for ‘‘Grape’’ and
‘‘Tomato’’; and
■ b. In the table in paragraph (a)(2):
■
■
■
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i. Add alphabetically entries for
‘‘Ginseng’’ and ‘‘Vegetable, tuberous and
corm’’; and
■ ii. Remove the entry ‘‘Potato’’.
The additions read as follows:
■
§ 180.567 Zoxamide; tolerances for
residues.
(a) * * *
(1) * * *
Parts per
million
Commodity
Fruit, small vine climbing, except
fuzzy kiwifruit, subgroup 13–
07F ..........................................
*
*
*
5.0
*
*
Tomato subgroup 8–10A ............
*
*
*
2.0
*
*
(2) * * *
Parts per
million
Commodity
Ginseng ......................................
*
*
*
*
0.30
*
Vegetable, tuberous and corm,
subgroup 1C ...........................
*
*
*
*
0.06
*
[FR Doc. 2016–04740 Filed 3–7–16; 8:45 am]
BILLING CODE 6560–50–P
ENVIRONMENTAL PROTECTION
AGENCY
40 CFR Part 180
[EPA–HQ–OPP–2015–0443; FRL–9943–21]
Fluopyram; Pesticide Tolerances
Environmental Protection
Agency (EPA).
ACTION: Final rule.
AGENCY:
This regulation establishes,
amends, and deletes tolerances for
residues of fluopyram in or on multiple
commodities which are identified and
discussed later in this document. Bayer
CropScience requested these tolerances
under the Federal Food, Drug, and
Cosmetic Act (FFDCA).
DATES: This regulation is effective
March 8, 2016. Objections and requests
for hearings must be received on or
before May 9, 2016, 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)
SUMMARY:
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number EPA–HQ–OPP–2015–0443, 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:
Susan Lewis, Registration Division
(7505P), Office of Pesticide Programs,
Environmental Protection Agency, 1200
Pennsylvania Ave. NW., Washington,
DC 20460–0001; main telephone
number: (703) 305–7090; email address:
RDFRNotices@epa.gov.
SUPPLEMENTARY INFORMATION:
I. General Information
A. Does this action apply to me?
You may be potentially affected by
this action if you are an agricultural
producer, food manufacturer, or
pesticide manufacturer. The following
list of North American Industrial
Classification System (NAICS) codes is
not intended to be exhaustive, but rather
provides a guide to help readers
determine whether this document
applies to them. Potentially affected
entities may include:
• Crop production (NAICS code 111).
• Animal production (NAICS code
112).
• Food manufacturing (NAICS code
311).
• Pesticide manufacturing (NAICS
code 32532).
B. How can I get electronic access to
other related information?
asabaliauskas on DSK3SPTVN1PROD with RULES
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
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provided in 40 CFR part 178. To ensure
proper receipt by EPA, you must
identify docket ID number EPA–HQ–
OPP–2015–0443 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 May 9, 2016. 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–
2015–0443, 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.
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 August 26,
2015 (80 FR 51759) (FRL–9931–74),
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 4F8284) by Bayer
CropScience, 2 T. W. Alexander Drive,
Research Triangle Park, North Carolina
27709. The petition requested that 40
CFR 180.661 be amended by
establishing tolerances for residues of
the fungicide fluopyram in or on the
raw agricultural commodities artichoke,
globe at 4.0 parts per million; aspirated
grain fractions at 50.0 ppm; peanut hay
at 40.0 ppm; hops at 60.0 ppm; root
vegetables, except beet, sugar, root, crop
subgroup 1B at 0.30 ppm; tuberous and
corm vegetables, crop subgroup 1C at
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0.10 ppm; potato wet peel at 0.30 ppm;
vegetables, leaves of root and tuber, crop
group 2 at 30.0 ppm; bulb vegetables,
bulb onion (crop subgroup 3–07A) at
0.30 ppm; bulb vegetables, green onions
(crop subgroup 3–07B) at 15.0 ppm;
leafy greens (crop subgroup 4A),
without spinach at 20.0 ppm; leafy
greens (crop subgroup 4A) spinach at
40.0 ppm; leafy petioles subgroup,
celery (crop subgroup 4B) at 20.0 ppm;
brassica leafy vegetables: Head and stem
(crop subgroup 5A) at 4.0 ppm; brassica
leafy vegetables: Leafy greens (crop
subgroup 5B) at 50.0 ppm; soybean
forage at 9.0 ppm; soybean hay at 30.0
ppm; legume vegetables: Edible podded
(crop subgroup 6A) at 4.0 ppm; legume
vegetables: Succulent shelled peas and
beans (crop subgroup 6B) at 0.20 ppm;
legume vegetables: Dried shelled peas
and beans (crop subgroup 6C) at 0.70
ppm; vegetable, foliage of legume
vegetables, forage, hay and vines, forage
(crop group 7) at 90.0 ppm; fruiting
vegetables, tomato subgroup (crop
subgroup 8–10A) at 1.00 ppm; fruiting
vegetables, pepper/eggplant subgroup
(crop subgroup 8–10B) at 3.00 ppm;
cucurbit vegetables (crop group 9A),
melon subgroup at 0.90 ppm; cucurbit
vegetables (crop group 9B), cucumber/
squash subgroup at 0.30 ppm; citrus
fruits (crop group 10–10) at 0.90 ppm;
citrus oil at 8.0 ppm; pome fruit (crop
group 11–10) at 2.0 ppm; stone fruit
(crop group 12–12A), cherry subgroup at
2.00 ppm; stone fruit (crop group 12–
12B), peach subgroup at 1.00 ppm; stone
fruit (crop group 12–12C), plum
subgroup at 0.50 ppm; berries and small
fruit: Caneberry (crop subgroup 13–07A)
at 5.0 ppm; berries and small fruit:
Bushberry (crop subgroup 13–07B) at
7.0 ppm; raisins at 4.0 ppm; berries and
small fruit, small fruit vine climbing,
except fuzzy kiwi (crop subgroup 13–
07F) at 1.5 ppm; berries and small fruit:
Low growing berry (crop subgroup 13–
07G) at 2.0 ppm; sorghum, grain at 1.5
ppm; wheat milled by-products at 2.0
ppm; grass forage, fodder and hay:
Forage (crop group 17) at 80.0 ppm;
herb crop (crop subgroup 19A) at 70.0
ppm; dill seed at 70.00 ppm; herbs,
dried at 400 ppm; oilseeds, rapeseed,
canola (crop subgroup 20A) at 0.70
ppm; oilseeds, sunflower, seed (crop
subgroup 20B) at 0.70 ppm; and
oilseeds: Cottonseed (crop subgroup
20C) at 0.80 ppm and in or on the
animal commodities chicken, meat
byproducts at 0.40 ppm; chicken, fat at
0.15 ppm; chicken, meat at 0.10 ppm;
goat, fat at 4.00 ppm; and goat, meat at
4.00 ppm. Bayer CropScience also
requests to establish a tolerance in 40
CFR 180.661 for indirect or inadvertent
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residues of the fungicide fluopyram in
or on the raw agricultural commodity
sugarcane, cane at 0.08 ppm. The
petition also requested to amend
tolerances in 40 CFR 180.661 for
residues of the fungicide fluopyram in
or on the raw agricultural commodities
peanut at 0.20 ppm; sugar beet, roots at
0.09 ppm; soybean, seed at 0.30 ppm;
soybean forage at 9.0 ppm; soybean hay
at 30.0 ppm; tree nuts (crop group 14)
at 0.04 ppm; almond hulls at 10.00 ppm;
grain, cereal, except rice and sorghum
(crop group 15) at 0.90 ppm; cereal
grain, except rice, forage, fodder and
straw (crop group 16) at 20.0 ppm; and
cotton gin by-product at 30.00 ppm and
in or on the animal commodities cattle,
meat byproducts at 40.00 ppm; cattle,
fat at 4.00 ppm; cattle, meat at 4.00
ppm; milk, cattle at 2.00 ppm; eggs,
chicken at 0.20 ppm; hog, meat
byproducts at 0.40 ppm; hog, fat at 0.04
ppm; hog, meat at 0.04 ppm; horse, meat
byproducts at 40.00 ppm; horse, fat at
4.00 ppm; horse, meat at 4.00 ppm; goat,
meat byproducts at 40.00 ppm; sheep,
meat byproducts at 40.00 ppm; sheep,
fat at 4.00 ppm; and sheep, meat at 4.00
ppm. Bayer CropScience also requests to
delete tolerances in 40 CFR 180.661 for
residues of the fungicide fluopyram in
or on the raw agricultural commodities
apple at 0.30 ppm; bean, dry at 0.09
ppm; beet, sugar, roots at 0.04 ppm;
apple wet pomace at 0.60 ppm; cherry
at 0.60 ppm; grape, wine at 2.0 ppm;
potato at 0.02 ppm; strawberry at 1.5
ppm; and watermelon at 1.0 ppm. That
document referenced a summary of the
petition prepared by Bayer CropScience,
the registrant, which is available in the
docket, https://www.regulations.gov.
There were no comments received in
response to the notice of filing.
Based upon review of the data
supporting the petition, EPA is issuing
some tolerances that vary from the
fluopyram tolerances as requested. The
reasons for these changes are explained
in Unit IV.C.
III. Aggregate Risk Assessment and
Determination of Safety
Section 408(b)(2)(A)(i) of FFDCA
allows EPA to establish a tolerance (the
legal limit for a pesticide chemical
residue in or on a food) only if EPA
determines that the tolerance is ‘‘safe.’’
Section 408(b)(2)(A)(ii) of FFDCA
defines ‘‘safe’’ to mean that ‘‘there is a
reasonable certainty that no harm will
result from aggregate exposure to the
pesticide chemical residue, including
all anticipated dietary exposures and all
other exposures for which there is
reliable information.’’ This includes
exposure through drinking water and in
residential settings, but does not include
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occupational exposure. Section
408(b)(2)(C) of FFDCA requires EPA to
give special consideration to exposure
of infants and children to the pesticide
chemical residue in establishing a
tolerance and to ‘‘ensure that there is a
reasonable certainty that no harm will
result to infants and children from
aggregate exposure to the pesticide
chemical residue . . . .’’
Consistent with FFDCA section
408(b)(2)(D), and the factors specified in
FFDCA section 408(b)(2)(D), EPA has
reviewed the available scientific data
and other relevant information in
support of this action. EPA has
sufficient data to assess the hazards of
and to make a determination on
aggregate exposure for fluopyram
including exposure resulting from the
tolerances established by this action.
EPA’s assessment of exposures and risks
associated with fluopyram 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.
Decreased body weight and liver
effects were the common and frequent
findings in the fluopyram subchronic
and chronic oral toxicity studies in rats,
mice, and dogs, and they appeared to be
the most sensitive effects. Liver effects
were characterized by increased liver
weight, hepatocellular hypertrophy,
hepatocellular vacuolation, increased
mitosis and hepatocellular necrosis.
Thyroid effects were found at dose
levels similar to those that produced
liver effects in rats and mice; these
effects consisted of follicular cell
hypertrophy, increased thyroid weight,
and hyperplasia at dose levels greater
than or equal to 100 milligrams/
kilogram/day (mg/kg/day). Changes in
thyroid hormone levels were also seen
in a subchronic toxicity study. In male
mice, there was an increased incidence
of thyroid adenomas.
Although increased liver tumors were
observed in female rats in the
carcinogenicity study, EPA has
concluded that fluopyram is ‘‘Not Likely
to be Carcinogenic to Humans’’ at doses
that do not induce cellular proliferation
in the liver or thyroid glands. This
classification was based on convincing
evidence that non-genotoxic modes of
action for liver tumors in rats and
thyroid tumors in mice have been
established and that the carcinogenic
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effects have been demonstrated as a
result of a mode of action dependent on
activation of the CAR/PXR receptors.
The Agency is using a point of
departure for regulating fluopyram
(NOAEL of 1.2 mg/kg/day) that is below
the doses that cause cell proliferation in
the liver (11 mg/kg/day) and subsequent
liver tumor formation (89 mg/kg/day);
therefore, the Agency concludes that
exposure to fluopyram will not be
carcinogenic. Moreover, fluopyram is
not genotoxic or mutagenic.
Fluopyram is not a developmental
toxicant, nor did it adversely affect
reproductive parameters. No evidence of
qualitative or quantitative susceptibility
was observed in developmental studies
in rats and rabbits or in a
multigeneration study in rats.
In an acute neurotoxicity study,
transient decreased motor activity was
seen only on the day of treatment, but
no other findings demonstrating
neurotoxicity were observed. In
addition, no neurotoxicity was observed
in the subchronic neurotoxicity study in
the presence of other systemic adverse
effects. Fluopyram did not produce
treatment-related effects on the immune
system.
Fluopyram has low acute toxicity via
the oral, dermal, and inhalation routes
of exposure. Fluopyram is not a skin or
eye irritant or sensitizer under the
conditions of the murine lymph node
assay. Specific information on the
studies received and the nature of the
adverse effects caused by fluopyram as
well as the no-observed-adverse-effectlevel (NOAEL) and the lowest-observedadverse-effect-level (LOAEL) from the
toxicity studies can be found at https://
www.regulations.gov in the document
entitled: ‘‘Fluopyram: Human Health
Risk Assessment for Proposed New Uses
on Crop Subgroup 1B, Subgroup 1C,
Crop Group 2, Subgroup 3–07A,
Subgroup 3–07B, Subgroup 4A,
Subgroup 4B, Subgroup 5A, Subgroup
5B, Subgroup 6A, Subgroup 6B, Dried
Beans, Soybean, Subgroup 8–10A,
Subgroup 8–10B, Subgroup 9A,
Subgroup 9B, Subgroup 10–10, Group
11–10, Subgroup 12–12A, Subgroup 12–
12B, Subgroup 12–12C, Subgroup 13–
07A, Subgroup 13–07B, Subgroup 13–
07F, Subgroup 13–07G, Crop Group 15
(except corn and Rice), Crop Group 16,
Subgroup 19A, Dill Seed, Subgroup
20A, Subgroup 20B, Subgroup 20C,
Artichoke (Globe), Hops, and Sugarcane
(Rotated). Amended Tolerance Requests
for the Registered Uses due to Crop
Group/Subgroup Expansion Requests.
Proposed New Uses on Turf Grass,
Ornamentals, and Christmas trees, and
as a seed treatment to Peanuts’’ in
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docket ID number EPA–HQ–OPP–2015–
0443.
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://
iaspub.epa.gov/apex/pesticides/
f?p=chemicalsearch:1.
A summary of the toxicological
endpoints for fluopyram used for
human risk assessment is shown in
Table 1.
TABLE 1—SUMMARY OF TOXICOLOGICAL DOSES AND ENDPOINTS FOR FLUOPYRAM FOR USE IN HUMAN HEALTH RISK
ASSESSMENT
Exposure/scenario
Point of departure
and
uncertainty/safety
factors
RfD, PAD, LOC for
risk assessment
Study and toxicological effects
Acute RfD = 0.50
mg/kg/day.
aPAD = 0.50 mg/kg/
day.
Acute Neurotoxicity Study in Rats
LOAEL = 100 mg/kg/day based on decreased motor and locomotor activity in females. The LOAEL in males was 125 mg/
kg/day.
Acute dietary (General population including infants and
children).
NOAEL = 50 mg/kg/
day.
UFA = 10x
UFH =10x
FQPA SF = 1x
Acute dietary (Females 13–50
years of age).
An endpoint attributable to a single dose exposure has not been identified for this subpopulation.
Chronic dietary (All populations)
NOAEL = 1.2 mg/kg/
day.
UFA = 10x
UFH = 10x
FQPA SF = 1x
NOAEL = 14.5 mg/
kg/day.
UFA = 10x
UFH = 10x
FQPA SF = 1x
Chronic RfD = 0.012
mg/kg/day.
cPAD = 0.012 mg/
kg/day.
Combined Chronic/Carcinogenicity in Rats
LOAEL = 6.0 mg/kg/day based on follicular cell hypertrophy in
the thyroid, and increased liver weight with gross pathological and histopathological findings.
LOC for MOE = 100
NOAEL = 300 mg/
kg/day.
UFA = 10x
UFH = 10x
FQPA SF = 1x
NOAEL = 14.5 mg/
kg/day.
UFA = 10x
UFH = 10x
FQPA SF = 1x
Residential LOC for
MOE = 100.
Reproduction study in rats
LOAEL = 82.8 mg/kg/day based on clinical pathology changes,
decreased spleen and thymus weights, increased liver weight
and centrilobular hypertrophy in parents, and decreased
body weight and body weight gain with decreases in spleen
and thymus weights and slight delay in preputial separation
in offspring.
28-day dermal study in rats
LOAEL = 1000 mg/kg/day based on increased cholesterol (F),
increased prothrombin time (M).
Incidental oral short-term (1 to
30 days) and intermediateterm (1 to 6 months).
Dermal short-term (1 to 30
days) and intermediate-term
(1 to 6 months).
Inhalation short-term (1 to 30
days) and intermediate-term
(1–6 months).
Cancer (Oral, dermal, inhalation).
Residential LOC for
MOE = 100.
Reproduction study in rats
LOAEL = 82.8 mg/kg/day based on clinical chemistry changes
and increased kidney weight in parents, and decreased body
weight and body weight gain with decreases in spleen and
thymus weights in offspring.
‘‘Not Likely to be Carcinogenic to Humans’’ at doses that do not induce cellular proliferation in the liver or thyroid glands.
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FQPA SF = Food Quality Protection Act Safety Factor. LOAEL = lowest-observed-adverse-effect-level. LOC = level of concern. Mg/kg/day =
milligram/kilogram/day. MOE = margin of exposure. NOAEL = no-observed-adverse-effect-level. PAD = population adjusted dose (a = acute, c =
chronic). UF = uncertainty factor. UFA = extrapolation from animal to human (interspecies). UFH = potential variation in sensitivity among members of the human population (intraspecies).
C. Exposure Assessment
1. Dietary exposure from food and
feed uses. In evaluating dietary
exposure to fluopyram, EPA considered
exposure under the petitioned-for
tolerances as well as all existing
fluopyram tolerances in 40 CFR
180.661. EPA assessed dietary
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exposures from fluopyram 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
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for fluopyram. In estimating acute
dietary exposure, EPA used food
consumption information from the
United States Department of Agriculture
(USDA) 2003–2008 National Health and
Nutrition Examination Survey/What We
Eat in America (NHANES/WWEIA). As
to residue levels in food, EPA included
tolerance residue levels, the assumption
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of 100% crop treated, and processing
factors (empirical and default).
ii. Chronic exposure. In conducting
the chronic dietary exposure assessment
EPA used the food consumption data
from the USDA 2003–2008 NHANES/
WWEIA. As to residue levels in food,
EPA included average residue levels, %
crop treated, and processing factors
(empirical and default).
iii. Cancer. Based on the data
summarized in Unit III.A., EPA has
concluded that fluopyram does not pose
a cancer risk to humans at doses that do
not induce cellular proliferation in the
liver or thyroid glands. Therefore, a
dietary exposure assessment for the
purpose of assessing cancer risk is
unnecessary.
iv. Anticipated residue and percent
crop treated (PCT) information. Section
408(b)(2)(E) of FFDCA authorizes EPA
to use available data and information on
the anticipated residue levels of
pesticide residues in food and the actual
levels of pesticide residues that have
been measured in food. If EPA relies on
such information, EPA must require
pursuant to FFDCA section 408(f)(1)
that data be provided 5 years after the
tolerance is established, modified, or
left in effect, demonstrating that the
levels in food are not above the levels
anticipated. For the present action, EPA
will issue such data call-ins as are
required by FFDCA section 408(b)(2)(E)
and authorized under FFDCA section
408(f)(1). Data will be required to be
submitted no later than 5 years from the
date of issuance of these tolerances.
Section 408(b)(2)(F) of FFDCA states
that the Agency may use data on the
actual percent of food treated for
assessing chronic dietary risk only if:
• Condition a: The data used are
reliable and provide a valid basis to
show what percentage of the food
derived from such crop is likely to
contain the pesticide residue.
• Condition b: The exposure estimate
does not underestimate exposure for any
significant subpopulation group.
• Condition c: Data are available on
pesticide use and food consumption in
a particular area, the exposure estimate
does not understate exposure for the
population in such area.
In addition, the Agency must provide
for periodic evaluation of any estimates
used. To provide for the periodic
evaluation of the estimate of PCT as
required by FFDCA section 408(b)(2)(F),
EPA may require registrants to submit
data on PCT.
The Agency estimated the PCT for the
chronic dietary exposure assessment for
existing uses as follows:
Almonds 33%; apples 40%;
blackberries 55%; blueberries 54%;
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broccoli 24%; cantaloupes 22%; celery
60%; corn field 9%; corn, sweet 15%;
cucumbers 41%; dry beans/peas 7%;
fresh tomatoes 64%; grape wine 79%
(used for grape, wine and sherry); head
lettuce 67%; leaf lettuce 62%; oranges
39%; peaches 56%; pears 43%; peanuts
67%; potatoes 64%; processed tomatoes
57%; pumpkins 45%; snap beans 44%;
soybeans 17%; spinach 43%; squash
47%; strawberries 75%; sugar beets
48%; watermelons 54%; and wheat 17%
(from spring wheat at 17% and winter
wheat at 6%).
In most cases, EPA uses available data
from United States Department of
Agriculture/National Agricultural
Statistics Service (USDA/NASS),
proprietary market surveys, and the
National Pesticide Use Database for the
chemical/crop combination for the most
recent 6–7 years. EPA uses an average
PCT for chronic dietary risk analysis.
The average PCT figure for each existing
use is derived by combining available
public and private market survey data
for that use, averaging across all
observations, and rounding to the
nearest 5%, except for those situations
in which the average PCT is less than
one. In those cases, 1% is used as the
average PCT and 2.5% is used as the
maximum PCT. EPA uses a maximum
PCT for acute dietary risk analysis. The
maximum PCT figure is the highest
observed maximum value reported
within the recent 6 years of available
public and private market survey data
for the existing use and rounded up to
the nearest multiple of 5%.
The Agency believes that the three
conditions discussed in Unit III.C.1.iv.
have been met. With respect to
Condition a, PCT estimates are derived
from federal and private market survey
data, which are reliable and have a valid
basis. The Agency is reasonably certain
that the percentage of the food treated
is not likely to be an underestimation.
As to Conditions b and c, regional
consumption information and
consumption information for significant
subpopulations is taken into account
through EPA’s computer-based model
for evaluating the exposure of
significant subpopulations including
several regional groups. Use of this
consumption information in EPA’s risk
assessment process ensures that EPA’s
exposure estimate does not understate
exposure for any significant
subpopulation group and allows the
Agency to be reasonably certain that no
regional population is exposed to
residue levels higher than those
estimated by the Agency. Other than the
data available through national food
consumption surveys, EPA does not
have available reliable information on
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the regional consumption of food to
which fluopyram may be applied in a
particular area.
2. Dietary exposure from drinking
water. The Agency used screening-level
water exposure models in the dietary
exposure analysis and risk assessment
for fluopyram in drinking water. These
simulation models take into account
data on the physical, chemical, and fate/
transport characteristics of fluopyram.
Further information regarding EPA
drinking water models used in pesticide
exposure assessment can be found at
https://www.epa.gov/oppefed1/models/
water/index.htm.
Based on the Pesticide Root Zone
Model Ground Water (PRZM GW) and
the surface water concentration
calculator (SWCC), the estimated
drinking water concentrations (EDWCs)
of fluopyram for acute exposures are
estimated to be 50.6 parts per billion
(ppb) for surface water and 97.6 ppb for
ground water. The chronic exposures for
non-cancer assessments are estimated to
be 17.3 ppb for surface water and 90.5
ppb for ground water.
Modeled estimates of drinking water
concentrations were directly entered
into the dietary exposure model. For
acute dietary risk assessment, the water
concentration value of 97.6 ppb was
used to assess the contribution to
drinking water. For chronic dietary risk
assessment, the water concentration of
value 90.5 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).
Fluopyram is proposed for use that
could result in residential exposures:
golf course turf, residential lawns, fruit
trees, nut trees, ornamentals and
gardens. EPA assessed residential
exposure using the following
assumptions: short-term dermal, oral
(derived from incidental oral hand to
mouth post-application exposures to
treated lawn in children), and
inhalation exposures derived from
treating lawns by hose-end sprayers
(adults); residential post-application
exposures: adults and children (1 to <2
years old) dermal exposure to treated
turf during high contact lawn activities;
children (1 to <2 years old) incidental
oral exposure as a result of contacting
treated turf; adults and youths (11 to
<16 yr old) dermal exposure to treated
turf during mowing and golfing
activities; children (6 to <11 years old)
dermal exposure to treated turf during
golfing activities; and adults and
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children (6 to <11 years old) dermal
exposure to treated gardens. Further
information regarding EPA standard
assumptions and generic inputs for
residential exposures may be found at
https://www.epa.gov/pesticides/trac/
science/trac6a05.pdf.
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 fluopyram to share a common
mechanism of toxicity with any other
substances, and fluopyram does not
appear to produce a toxic metabolite
produced by other substances. For the
purposes of this tolerance action,
therefore, EPA has assumed that
fluopyram 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 Web site at https://
www.epa.gov/pesticides/cumulative.
D. Safety Factor for Infants and
Children
1. In general. Section 408(b)(2)(C) of
FFDCA provides that EPA shall apply
an additional tenfold (10X) margin of
safety for infants and children in the
case of threshold effects to account for
prenatal and postnatal toxicity and the
completeness of the database on toxicity
and exposure unless EPA determines
based on reliable data that a different
margin of safety will be safe for infants
and children. This additional margin of
safety is commonly referred to as the
FQPA Safety Factor (SF). In applying
this provision, EPA either retains the
default value of 10X, or uses a different
additional safety factor when reliable
data available to EPA support the choice
of a different factor.
2. Prenatal and postnatal sensitivity.
The available developmental toxicity
studies in rats and rabbits and the multigeneration reproduction in rats
demonstrate no evidence of increased
susceptibility in the developing or
young animals which were exposed
during pre- or post-natal periods.
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:
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i. The toxicity database for fluopyram
is complete.
ii. There is no indication that
fluopyram is a neurotoxic chemical.
Although transient decreases in motor
and locomotor activities in the acute
neurotoxicity study were seen on the
day of treatment and limited use of
hind-limbs and reduced motor activity
was seen in the rat chronic/
carcinogenicity study, there were no
other associated neurobehavioral or
histopathology changes found in other
studies in the fluopyram toxicity
database. The effects seen in the
chronic/carcinogenicity study were in
the presence of increased mortality and
morbidity such as general pallor and
emaciated appearance. Therefore, the
reduced motor activity and limited use
of hind-limbs seen in these two studies
were judged to be the consequence of
the systemic effects and not direct
neurotoxicity. Additionally there is no
need for a developmental neurotoxicity
study or additional UFs to account for
neurotoxicity.
iii. There is no evidence that
fluopyram results in increased
susceptibility in in utero rats or rabbits
in the prenatal developmental studies or
in young rats in the 2-generation
reproduction study.
iv. There are no residual uncertainties
identified in the exposure databases.
The acute dietary exposure assessment
was performed using conservative
exposure inputs, including tolerancelevel residues for all crops, whereas the
chronic dietary assessment included
average field-trial residue levels for all
crops. The acute dietary assessment
assumed 100 PCT, whereas the chronic
dietary assessment utilized average
percent crop treated numbers for several
crops. Both acute and chronic dietary
assessments incorporated empirical or
default processing factors. The dietary
exposure assessment also assumed that
all drinking water will contain
fluopyram at the highest EDWC levels
modeled by the Agency for ground or
surface water. Therefore, it can be
concluded that the dietary exposure
analysis does not underestimate risk
from acute and chronic dietary exposure
to fluopyram. While there is the
potential for handler and postapplication residential exposure, the
best data and approaches currently
available were used in the fluopyram
residential assessment. The Agency
used the current conservative
approaches for residential assessment,
many of which include recent upgrades
to the SOPs. The Agency believes that
the calculated risks represent
conservative estimates of exposure
because maximum application rates are
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used to define residue levels upon
which the calculations are based.
Therefore, residential exposures are
unlikely to be underestimated.
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
fluopyram will occupy 35% of the aPAD
for children 1–2 years 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 fluopyram from
food and water will utilize 81% of the
cPAD for children 1–2 years 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 fluopyram 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). Fluopyram 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
fluopyram.
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 from handler inhalation exposure
(the most conservative risk estimate) of
1,500 for adults. For children 1–2 years
old, post-application incidental oral
exposures aggregated with food and
drinking water resulted in an MOE of
1,500. Because EPA’s level of concern
for fluopyram is a MOE of 100 or below,
these MOEs are not of concern.
4. Intermediate-term risk.
Intermediate-term aggregate exposure
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takes into account intermediate-term
residential exposure plus chronic
exposure to food and water (considered
to be a background exposure level).
Intermediate-term residential exposure
is not expected given the intermittent
nature of applications in residential
settings.
5. Aggregate cancer risk for U.S.
population. As discussed in Unit III.A,
because the Agency is regulating
exposure to fluopyram at doses lower
than those that may induce cellular
proliferation in the liver or thyroid
glands, fluopyram is not expected to
pose a cancer risk to humans.
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 fluopyram
residues.
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IV. Other Considerations
A. Analytical Enforcement Methodology
The German multiresidue method
DFG Method S 19, a gas
chromatography with mass selective
detection (GC/MSD) method, is the
method for the enforcement of
tolerances for fluopyram residues in/on
crop commodities and a high
performance liquid chromatography
method with tandem mass spectrometry
detection (HPLC/MS/MS), Method
01079, has been accepted for the
enforcement of tolerances for residues of
fluopyram and its metabolite, AE
C656948-benzamide, in livestock
commodities. The validated limit of
quantitation (LOQ) is 0.01 ppm and the
calculated limit of detection (LOD) is
0.003 ppm for each analyte in each
matrix. The method was adequately
validated using cattle milk, fat, muscle,
liver, and kidney, and hen whole egg
fortified with fluopyram and AE
C656948-benzamide, each at 0.01 and
0.10 ppm. The method was subjected to
ILV using samples of beef muscle, beef
liver, eggs, and milk fortified with
fluopyram and AE C656948-benzamide,
each at 0.01 and 0.10 ppm.
Adequate enforcement methodology
DFG Method S 19 and Method 01079
are available to enforce the tolerance
expression.
The method may be requested from:
Chief, Analytical Chemistry Branch,
Environmental Science Center, 701
Mapes Rd., Ft. Meade, MD 20755–5350;
telephone number: (410) 305–2905;
email address: residuemethods@
epa.gov.
B. International Residue Limits
In making its tolerance decisions, EPA
seeks to harmonize U.S. tolerances with
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international standards whenever
possible, consistent with U.S. food
safety standards and agricultural
practices. EPA considers the
international maximum residue limits
(MRLs) established by the Codex
Alimentarius Commission (Codex), as
required by FFDCA section 408(b)(4).
The Codex Alimentarius is a joint
United Nations Food and Agriculture
Organization/World Health
Organization food standards program,
and it is recognized as an international
food safety standards-setting
organization in trade agreements to
which the United States is a party. EPA
may establish a tolerance that is
different from a Codex MRL; however,
FFDCA section 408(b)(4) requires that
EPA explain the reasons for departing
from the Codex level.
There are Codex maximum residue
levels MRLs established on berries
(blackberry and raspberry 3 ppm),
broccoli and Brussels sprouts (0.3 ppm),
dry beans (0.07 ppm), head cabbage
(0.15 ppm), carrot (0.4 ppm),
cauliflower (0.09 ppm), cherry (0.7
ppm), cucumber (0.5 ppm), dried grapes
(currants, raisins and sultanas 5 ppm),
grapes (2 ppm), leek (0.15 ppm), lettuce
(head and leaf 15 ppm), onion bulb
(0.07 ppm), peach subgroup (1 ppm),
peanut (0.03 ppm), plums (0.5 ppm),
pome fruits (0.5 ppm), potato (0.03
ppm), rapeseed (1 ppm), strawberry (0.4
ppm), sugar beet (0.04 ppm), tomato (0.4
ppm), and tree nuts (0.04 ppm).
The tolerance definitions are
harmonized among the US, Canada, and
Codex for all plant and livestock
commodities. In addition, the U.S.
tolerances for grape (within the fruit,
small vine climbing, except fuzzy
kiwifruit, subgroup 13–07F), peach
(within the fruit, stone, peach subgroup
12–12B), and plum (within the fruit,
stone, plum subgroup 12–12C) are
harmonized with the Codex MRLs for
grape, peach, and plum.
Harmonization with Codex MRLs for
berries (blackberry and raspberry 3
ppm), broccoli and Brussels sprouts (0.3
ppm), dry beans (0.70 ppm), head
cabbage (0.15 ppm), cauliflower (0.09
ppm), cherry (0.7 ppm), cucumber (0.5
ppm), leek (0.15 ppm), lettuce (head and
leaf 15 ppm), onion bulb (0.07 ppm),
peanut (0.03 ppm), pome fruits (0.5
ppm), potato (0.03 ppm), rapeseed (1
ppm), strawberry (0.4 ppm), sugar beet
(0.04 ppm), tomato (0.4 ppm), and tree
nuts (0.04 ppm) is not possible because
the Codex MRLs are lower than the
recommended U.S. tolerances. The U.S.
tolerances cannot be harmonized
because following the approved label
directions could result in residues above
the recommended tolerances. The U.S.
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tolerances for carrot and raisin are
higher than the Codex MRLs. EPA is not
harmonized with Codex in order to
remain harmonized with Canada.
The U.S. and Codex livestock MRLs
are not harmonized due to different
livestock dietary burdens. Fluopyram is
approved for use on more livestock feed
stuffs in the United States and thus
contributes to a greater portion of the
assessment of the livestock dietary
burden in the United States than in the
assessment of livestock dietary burden
supporting the Codex MRLs.
Harmonization could lead to tolerance
exceedances when the pesticide is used
legally in the United States.
C. Revisions to Petitioned-For
Tolerances
The petitioned-for tolerances differ
from the tolerances that EPA is
establishing for sugar beet roots, onion
bulbs, leafy greens subgroup 4A, crop
subgroup 6C, fruiting vegetables (8–
10B), melon subgroup 9A, citrus,
subgroup 13–07F, raisin, tree nuts, crop
group 15, herb subgroup 19A, dill seed,
and subgroup 20A.
For citrus, crop group 15, fruiting
vegetables (8–10B), onion bulbs,
rapeseed subgroup 20A, and tree nuts,
the Organization for Economic
Cooperation and Development (OECD)
statistical calculation procedures
applied to the field trial residue data
provided a different value than the
petitioned-for tolerances. Also, for crop
group 15 and subgroup 20A, the values
petitioner requested were based on a
data set that excluded a field trial (on
sorghum and canola, respectively) as an
outlier based on statistical tests.
However, the trials could not be
excluded by the Agency since there
were no abnormal field conditions.
While the petitioner requested a
tolerance for crop group 15, except rice
and sorghum, the Agency has
determined that a crop group 15
tolerance, except corn and rice is
appropriate. This is due to the wide
variation in residue levels from the
available data. The minimum residues
on sweet corn at 0.01 ppm and the
maximum residues on sorghum 3.2 ppm
differ by more than 5x; therefore, the
tolerance level (1.5 ppm) is not
appropriate to establish a crop group
tolerance with all the representative
crops. Rather, based on the available
data, EPA is establishing tolerances on
grain, cereal, except rice and corn,
group 15 at 4.0 ppm; and individual
tolerance on corn, field, grain at 0.02
ppm; corn, pop, grain at 0.02 ppm; and
corn, sweet, kernal plus cob with husks
removed at 0.01 ppm.
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Although the petitioner requested two
separate tolerances for commodities of
subgroup 4A, the available data support
a tolerance of 40 ppm for residues of
fluopyram in/on leafy greens subgroup
4A and at 20 ppm on leaf petioles
subgroup 4B.
The petitioner requested two separate
tolerances for herb subgroup 19A, fresh
and herbs, dried. Because subgroup 19A
covers both dried and fresh herbs, the
Agency is establishing a tolerance on
herb subgroup 19A at 40 ppm, based on
available data.
The petitioner has requested to
establish tolerances on vegetables,
legume; dried beans and peas, except
soybeans (subgroup 6C) at 0.70 ppm.
Because only data on dried beans is
available, there is not sufficient data to
support establishing a subgroup
tolerance. Therefore, based on the
available residue data for dried beans,
the Agency is establishing an individual
tolerance of 0.70 ppm on dried beans
only. EPA is establishing dry bean
tolerance at 0.70 ppm to harmonize with
Canada.
The petitioner had requested to
establish tolerances on vegetables,
cucurbit, cucumber/squash subgroup at
0.30 ppm and fruit, pome at 1.0 ppm.
Based on available data that reflect the
proposed use pattern, EPA is
establishing a tolerance on squash/
cucumber subgroup 9B at 0.60 ppm and
fruit, pome, group 11–10 at 0.80 ppm.
For harmonization purposes with
Canada, tolerances being established for
sugar beet, melon subgroup 9A, tree
nuts, and subgroup 13–07F are slightly
increased above the tolerance levels
requested for those commodities.
The requested grape, raisin tolerance
of 4.0 ppm is being reduced to 3.0 ppm
based on the highest average field trial
(HAFT) (0.948 ppm) for grape and
processing factor of 2.4.
Because use of fluopyram is limited to
Region 3 (Florida), the Agency is
establishing a tolerance with a regional
registration for inadvertent or indirect
residues of fluopyram on sugarcane,
cane (0.08 ppm) when sugarcane is used
as a rotational crop.
The requested tolerances for livestock
commodities were based on some
livestock feed stuffs that have been
withdrawn from the list of crops to be
treated with fluopyram. Based on a
recalculation of the livestock dietary
burden, the Agency is establishing
tolerances for livestock commodities
that are lower than requested.
In addition, the Agency has revised
several commodity terms to reflect the
current commodity definitions used by
the Agency and revised several
tolerance level values to be consistent
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with EPA’s practice of extending
tolerance values out to two significant
figures.
Although the petition requested a
tolerance for nut tree group 14, the
Agency is establishing a tolerance for
nut, tree 14–12 consistent with its stated
policy of not establishing tolerances for
pre-existing crop groups. See 77 FR
50617, 50619 (Aug. 22, 2012).
Finally, the requests for tolerances
were withdrawn for the following
commodities: Crop group 7 at 90.0 ppm;
crop group 17 at 80.0 ppm; peanut hay
at 40.0 ppm, soybean forage at 9.0 ppm;
and soybean hay at 30.0 ppm. A
separate tolerance for wheat, milled
byproducts is not needed as it is
covered by the crop group 15 tolerance.
V. Conclusion
Therefore, tolerances are established
for residues of fluopyram in or on
almond, hulls at 10 ppm; artichoke,
globe at 4.0 ppm, bean, dry at 0.70 ppm;
beet, sugar at 0.10 ppm; berry, low
growing, except cranberry, subgroup
13–07G at 2.0 ppm; brassica, head and
stem, subgroup 5A at 4.0 ppm; brassica,
leafy greens, subgroup 5B at 50 ppm;
bushberry subgroup 13–07B at 7.0 ppm;
grain, aspirated grain fractions at 50
ppm; caneberry subgroup 13–07A at 5.0
ppm; cereal, forage, fodder and straw,
group 16 at 20 ppm; cherry subgroup
12–12A at 2.0 ppm; citrus, oil at 8.0
ppm; corn, field, grain at 0.02 ppm;
corn, pop, grain at 0.02 ppm; corn,
sweet, kernel plus cob with husks
removed 0.01 ppm; cotton, gin
byproducts at 30 ppm; cottonseed
subgroup 20C at 0.80 ppm; dill, seed at
70 ppm; rapeseed subgroup 20A at 5.0
ppm; fruit, citrus, group 10–10 at 1.0
ppm; fruit, pome, group 11–10 at 0.80
ppm; fruit, small vine climbing, except
fuzzy kiwifruit, subgroup 13–07F at 2.0
ppm; grape, raisin at 3.0 ppm; grain,
cereal, group 15, except corn and rice at
4.0 ppm; grain, herb subgroup 19A at 40
ppm; hop, dried cones at 60 ppm; leaf
petioles subgroup 4B at 20 ppm; leafy
greens subgroup 4A at 40 ppm; melon
subgroup 9A at 1.0 ppm; nut, tree, group
14–12 at 0.05 ppm; onion, bulb,
subgroup 3–07A at 0.40 ppm; onion,
green, subgroup 3–07B at 15 ppm; pea
and bean, succulent shelled, subgroup
6B at 0.20 ppm; peach subgroup 12–12B
at 1.0 ppm; peanut at 0.20 ppm; potato,
wet peel at 0.30 ppm; pepper/eggplant
subgroup 8–10B at 4.0 ppm; plum
subgroup 12–12C at 0.50 ppm; soybean,
seed at 0.30 ppm; squash/cucumber
subgroup 9B at 0.60 ppm; sunflower
subgroup 20B at 0.70 ppm; tomato
subgroup 8–10A at 1.0 ppm; vegetable,
leaves of root and tuber, group 2 at 30
ppm; vegetable, legume, edible podded,
PO 00000
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Fmt 4700
Sfmt 4700
subgroup 6A at 4.0 ppm; vegetable, root,
except sugar beet, subgroup 1B at 0.30
ppm; and vegetable, tuberous and corm,
subgroup 1C at 0.10 ppm.
Tolerances are also established for
residues of fluopyram and its metabolite
2-(trifluoromethyl)benzamide,
expressed in parent equivalents for
cattle, fat at 0.70 ppm; cattle, meat at
0.80 ppm; cattle, meat byproducts at 7.5
ppm; egg at 0.08 ppm; goat, fat at 0.70
ppm; goat, meat at 0.80 ppm; goat, meat
byproducts at 7.5 ppm; hog, meat
byproducts at 0.20 ppm; horse, fat at
0.70 ppm; horse, meat at 0.80 ppm;
horse, meat byproducts at 7.5 ppm; milk
at 0.40 ppm; poultry, fat at 0.04 ppm;
poultry, meat at 0.04 ppm; poultry, meat
byproducts at 0.16 ppm; sheep, fat at
0.70 ppm; sheep, meat at 0.80 ppm; and
sheep, meat byproducts at 7.5 ppm.
In addition, the Agency is removing
tolerances for almond, hull; apple, wet
pomace; bean, dry; beet, sugar, root;
canola seed; cotton, gin byproducts;
cotton, undelinted seed; cherry; grape,
wine; grain, cereal, except rice, group
15; grain, cereal, forage, fodder, and
straw, group 16; nut, tree, group 14;
peanut; pistachio; potato; soybean
forage; soybean hay; soybean, seed;
strawberry; and watermelon because
they are superseded by other tolerances
being established in this action.
VI. Statutory and Executive Order
Reviews
This action establishes tolerances
under FFDCA section 408(d) in
response to a petition submitted to the
Agency. The Office of Management and
Budget (OMB) has exempted these types
of actions from review under Executive
Order 12866, entitled ‘‘Regulatory
Planning and Review’’ (58 FR 51735,
October 4, 1993). Because this action
has been exempted from review under
Executive Order 12866, this action is
not subject to Executive Order 13211,
entitled ‘‘Actions Concerning
Regulations That Significantly Affect
Energy Supply, Distribution, or Use’’ (66
FR 28355, May 22, 2001) or Executive
Order 13045, entitled ‘‘Protection of
Children from Environmental Health
Risks and Safety Risks’’ (62 FR 19885,
April 23, 1997). 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).
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Since tolerances and exemptions that
are established on the basis of a petition
under FFDCA section 408(d), such as
the tolerance in this final rule, do not
require the issuance of a proposed rule,
the requirements of the Regulatory
Flexibility Act (RFA) (5 U.S.C. 601 et
seq.), do not apply.
This action directly regulates growers,
food processors, food handlers, and food
retailers, not States or tribes, nor does
this action alter the relationships or
distribution of power and
responsibilities established by Congress
in the preemption provisions of FFDCA
section 408(n)(4). As such, the Agency
has determined that this action will not
have a substantial direct effect on States
or tribal governments, on the
relationship between the national
government and the States or tribal
governments, or on the distribution of
power and responsibilities among the
various levels of government or between
the Federal Government and Indian
tribes. Thus, the Agency has determined
that Executive Order 13132, entitled
‘‘Federalism’’ (64 FR 43255, August 10,
1999) and Executive Order 13175,
entitled ‘‘Consultation and Coordination
with Indian Tribal Governments’’ (65 FR
67249, November 9, 2000) do not apply
to this action. In addition, this action
does not impose any enforceable duty or
contain any unfunded mandate as
described under Title II of the Unfunded
Mandates Reform Act (UMRA) (2 U.S.C.
1501 et seq.).
This action does not involve any
technical standards that would require
Agency consideration of voluntary
consensus standards pursuant to section
12(d) of the National Technology
Transfer and Advancement Act
(NTTAA) (15 U.S.C. 272 note).
asabaliauskas on DSK3SPTVN1PROD with RULES
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.
VerDate Sep<11>2014
16:05 Mar 07, 2016
Jkt 238001
Dated: March 1, 2016.
G. Jeffery Herndon,
Acting 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. Section 180.661 is revised to read
as follows:
■
§ 180.661 Fluopyram; tolerances for
residues.
(a) General. (1) Tolerances are
established for residues of the fungicide
Fluopyram, N-[2-[3-chloro-5(trifluoromethyl)-2-pyridinyl]ethyl]-2(trifluoromethyl)benzamide, including
its metabolites and degradates in or on
the commodities in the table below.
Compliance with the tolerance levels
specified in the table is to be
determined by measuring only
fluopyram in or on the commodity.
Commodity
Almond, hulls ..............................
Artichoke, globe ..........................
Banana 1 .....................................
Bean, dry ....................................
Beet, sugar .................................
Berry, low growing, except cranberry, subgroup 13–07G .........
Brassica, head and stem, subgroup 5A .................................
Brassica, leafy greens, subgroup
5B ............................................
Bushberry subgroup 13–07B ......
Caneberry subgroup 13–07A .....
Cherry subgroup 12–12A ...........
Citrus, oil .....................................
Corn, field, grain .........................
Corn, pop, grain ..........................
Corn, sweet, kernel plus cob
with husks removed ................
Cotton, gin byproducts ...............
Cottonseed subgroup 20C .........
Dill, seed .....................................
Fruit, citrus, group 10–10 ...........
Fruit, pome, group 11–10 ...........
Fruit, small vine climbing, except
fuzzy kiwifruit, subgroup 13–
07F ..........................................
Grain, aspirated grain fractions ..
Grain, cereal, forage, fodder and
straw, group 16 .......................
Grain, cereal, group 15, except
corn and rice ...........................
Grape, raisin ...............................
Herb subgroup 19A ....................
Hop, dried cones ........................
Leafy greens subgroup 4A .........
Leafy petioles subgroup 4B ........
Melon subgroup 9A ....................
Nut, tree, group 14–12 ...............
Onion, bulb, subgroup 3–07A ....
Onion, green, subgroup 3–07B ..
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Commodity
Pea and bean, succulent
shelled, subgroup 6B ..............
Peach subgroup 12–12B ............
Peanut ........................................
Pepper/eggplant subgroup 8–
10B ..........................................
Plum subgroup 12–12C ..............
Potato, wet peel ..........................
Rapeseed subgroup 20A ............
Soybean, seed ............................
Squash/cucumber subgroup 9B
Sunflower subgroup 20B ............
Tomato subgroup 8–10A ............
Vegetable, leaves of root and
tuber, group 2 .........................
Vegetable, legume, edible podded, subgroup 6A ...................
Vegetable, root, except sugar
beet, subgroup 1B ..................
Vegetable, tuberous and corm,
subgroup 1C ...........................
1 There
12023
Parts per
million
0.20
1.0
0.20
4.0
0.50
0.30
5.0
0.30
0.60
0.70
1.0
30
4.0
0.30
0.10
are no U.S. registrations.
(2) Tolerances are established for
residues of the fungicide fluopyram, N[2-[3-chloro-5-(trifluoromethyl)-2pyridinyl]ethyl]-2(trifluoromethyl)benzamide, including
its metabolites and degradates.
Parts per
Compliance with the tolerance levels
million
specified in the table below is to be
10 determined by measuring only the sum
4.0 of fluopyram and its metabolite, 21.0 (trifluoromethyl)benzamide, calculated
0.70 as the stoichiometric equivalent of
0.10 fluopyram, in or on the commodity.
2.0
Commodity
4.0
50
7.0
5.0
2.0
8.0
0.02
0.02
0.01
30
0.80
70
1.0
0.80
2.0
50
Cattle, fat ....................................
Cattle, meat ................................
Cattle, meat byproducts .............
Egg .............................................
Goat, fat ......................................
Goat, meat ..................................
Goat, meat byproducts ...............
Hog, fat .......................................
Hog, meat ...................................
Hog, meat byproducts ................
Horse, fat ....................................
Horse, meat ................................
Horse, meat byproducts .............
Milk .............................................
Poultry, fat ..................................
Poultry, meat ..............................
Poultry, meat byproducts ............
Sheep, fat ...................................
Sheep, meat ...............................
Sheep, meat byproducts ............
Parts per
million
0.70
0.80
7.5
0.08
0.70
0.80
7.5
0.20
0.02
0.20
0.70
0.80
7.5
0.40
0.04
0.04
0.20
0.70
0.80
7.5
20
4.0
3.0
40
60
40
20
1.0
0.05
0.40
15
(b) Section 18 emergency exemptions.
[Reserved]
(c) Tolerances with regional
registrations. Tolerances with regional
registration, as defined in § 180.1(1), are
established for indirect or inadvertent
residues of fungicide fluopyram, N-[2[3-chloro-5-(trifluoromethyl)-2pyridinyl]ethyl]-2(trifluoromethyl)benzamide, including
E:\FR\FM\08MRR1.SGM
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Federal Register / Vol. 81, No. 45 / Tuesday, March 8, 2016 / Rules and Regulations
its metabolites and degradates, in or on
the commodities in the table below.
Compliance with the tolerance levels
specified in the table is to be
determined by measuring only
fluopyram in or on the commodity.
Commodity
Parts per
million
Sugarcane, cane ........................
0.08
(d) Indirect or inadvertent residues. It
is recommended that tolerances be
established for indirect or inadvertent
residues of fungicide fluopyram, N-[2[3-chloro-5-(trifluoromethyl)-2pyridinyl]ethyl]-2(trifluoromethyl)benzamide, including
its metabolites and degradates, in or on
the commodities in the table below.
Compliance with the tolerance levels
specified in the table is to be
determined by measuring only
fluopyram in or on the commodity.
Commodity
Parts per
million
Alfalfa, forage .............................
Alfalfa, hay ..................................
Soybean, seed ............................
0.45
1.1
0.10
[FR Doc. 2016–05025 Filed 3–7–16; 8:45 am]
BILLING CODE 6560–50–P
Applicability date: The corrections
indicated in this document are
applicable beginning January 1, 2016.
FOR FURTHER INFORMATION CONTACT: Lisa
Ohrin Wilson (410) 786–8852, or
Matthew Edgar (410) 786–0698, for
issues related to physician self-referral
updates. Jessica Bruton, (410) 786–5991
for all other issues.
SUPPLEMENTARY INFORMATION:
I. Background
In FR Doc. 2015–28005 (80 FR 70886
through 71386), the final rule entitled
‘‘Medicare Program; Revisions to
Payment Policies Under the Physician
Fee Schedule and Other Revisions to
Part B for CY 2016’’ (hereinafter referred
to as the CY 2016 PFS final rule with
comment period), there were a number
of technical and typographical errors
that are identified and corrected in
section IV., the Correction of Errors. The
effective date for the rule was January 1,
2016, except for the definition of
‘‘ownership or investment interest’’ in
§ 411.362(a), which has an effective date
of January 1, 2017. These corrections are
applicable as of January 1, 2016. We
note that Addenda B and C to the CY
2016 PFS final rule with comment
period as corrected by this correcting
amendment are available on the CMS
Web site at https://www.cms.gov//
PhysicianFeeSched/.
DEPARTMENT OF HEALTH AND
HUMAN SERVICES
II. Summary of Errors
Centers for Medicare & Medicaid
Services
On page 70894, we inadvertently
omitted a sentence from the first
comment summary regarding applying
the same overrides used for the MP RVU
calculations to the PE calculations.
On page 70894, we inadvertently
omitted a clause from the response
summary regarding the overrides that
also apply to the MP RVU calculation in
the development of PE RVUs.
On page 70898, due to data errors
made in the ratesetting process, many of
the values contained in Table 4:
Calculation of PE RVUs under
Methodology for Selected Codes, are
incorrect.
On page 70953, we inadvertently
included language regarding the
application of the equipment utilization
assumption.
On page 70971,
a. Due to a typographical error, the
work RVU for CPT code 76945 was
listed incorrectly. As a result, the work
RVU for CPT code 76948 was also
inadvertently listed incorrectly.
b. Due to a typographical error, we
inadvertently referred to CPT code
76948 rather than CPT code 76945.
A. Summary of Errors in the Preamble
42 CFR Parts 405, 410, 411, 414, 425,
and 495
[CMS–1631–F2]
RIN 0938–AS40
Medicare Program; Revisions to
Payment Policies Under the Physician
Fee Schedule and Other Revisions to
Part B for CY 2016; Corrections
Centers for Medicare &
Medicaid Services (CMS), HHS.
ACTION: Final rule; correcting
amendment.
AGENCY:
This document corrects
technical and typographical errors that
appeared in the final rule with comment
period published in the November 16,
2015 Federal Register (80 FR 70886
through 71386) entitled ‘‘Medicare
Program; Revisions to Payment Policies
Under the Physician Fee Schedule and
Other Revisions to Part B for CY 2016.’’
DATES: Effective date: This correcting
document is effective March 7, 2016.
asabaliauskas on DSK3SPTVN1PROD with RULES
SUMMARY:
VerDate Sep<11>2014
16:05 Mar 07, 2016
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Fmt 4700
Sfmt 4700
On page 70992, due to a typographical
error in Table 13—CY 2016 Actions on
Codes with CY 2015 Interim Final
RVUs, the CY 2016 work RVU for CPT
code 76948 was incorrectly displayed.
On page 71317, we inadvertently
included language in our comment
discussion on the issue regarding
compensation arrangements.
On page 71357,
a. Due to data errors, we incorrectly
stated the estimated CY 2016 net
reduction in expenditures.
b. Due to data errors, we incorrectly
stated the reduction to the conversion
factor.
c. Due to data errors, we incorrectly
stated the CY 2016 PFS conversion
factors. As a result, many of the values
in Table 60—Calculation of the CY 2016
PFS Conversion Factor, are incorrect.
d. Due to data errors, we incorrectly
stated the CY 2016 PFS anesthesia
conversion factors. As a result, many of
the values in Table 61—Calculation of
the CY 2016 PFS Anesthesia Conversion
Factor, are incorrect.
On pages 71358 through 71359, due to
data errors, many of the values in Table
62—CY 2016 PFS Estimated Impact On
Total Allowed Charges By Specialty, are
incorrect.
On pages 71359 through 71360, due to
data errors, many of the values in Table
63— Impact on CY 2016 Payment for
Selected Procedures, are incorrect.
On page 71369,
a. Due to data errors, we incorrectly
stated the CY 2016 national payment
amount in the nonfacility setting for
CPT code 99203.
b. Due to data errors, we incorrectly
stated the CY 2016 proposed beneficiary
coinsurance for CPT code 99203.
B. Summary of Errors in Regulation Text
On page 71375 of the CY 2016 PFS
final rule with comment period, we
made a typographical error in
§ 411.357(d)(1)(iv). In this paragraph, we
inadvertently included the word ‘‘for’’.
On page 71377 of the CY 2016 PFS
final rule with comment period, we
made a typographical error in
§ 411.357(x)(1)(vi)(A). In this paragraph,
we inadvertently omitted the word
‘‘directly’’.
C. Summary and Correction of Errors in
the Addenda on the CMS Web site
Due to the errors identified and
summarized in section II.A and B of this
document, we are correcting errors in
the work, PE or MP RVUs (or
combinations of these RVUs) in
Addendum B: CY 2016 Relative Value
Units (RVUs) And Related Information
Used In Determining Final Medicare
Payments and Addendum C: CY 2016
E:\FR\FM\08MRR1.SGM
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Agencies
[Federal Register Volume 81, Number 45 (Tuesday, March 8, 2016)]
[Rules and Regulations]
[Pages 12015-12024]
From the Federal Register Online via the Government Publishing Office [www.gpo.gov]
[FR Doc No: 2016-05025]
-----------------------------------------------------------------------
ENVIRONMENTAL PROTECTION AGENCY
40 CFR Part 180
[EPA-HQ-OPP-2015-0443; FRL-9943-21]
Fluopyram; Pesticide Tolerances
AGENCY: Environmental Protection Agency (EPA).
ACTION: Final rule.
-----------------------------------------------------------------------
SUMMARY: This regulation establishes, amends, and deletes tolerances
for residues of fluopyram in or on multiple commodities which are
identified and discussed later in this document. Bayer CropScience
requested these tolerances under the Federal Food, Drug, and Cosmetic
Act (FFDCA).
DATES: This regulation is effective March 8, 2016. Objections and
requests for hearings must be received on or before May 9, 2016, 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)
[[Page 12016]]
number EPA-HQ-OPP-2015-0443, 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: Susan Lewis, Registration Division
(7505P), Office of Pesticide Programs, Environmental Protection Agency,
1200 Pennsylvania Ave. NW., Washington, DC 20460-0001; main telephone
number: (703) 305-7090; email address: RDFRNotices@epa.gov.
SUPPLEMENTARY INFORMATION:
I. General Information
A. Does this action apply to me?
You may be potentially affected by this action if you are an
agricultural producer, food manufacturer, or pesticide manufacturer.
The following list of North American Industrial Classification System
(NAICS) codes is not intended to be exhaustive, but rather provides a
guide to help readers determine whether this document applies to them.
Potentially affected entities may include:
Crop production (NAICS code 111).
Animal production (NAICS code 112).
Food manufacturing (NAICS code 311).
Pesticide manufacturing (NAICS code 32532).
B. How can I get electronic access to other related information?
You may access a frequently updated electronic version of EPA's
tolerance regulations at 40 CFR part 180 through the Government
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-2015-0443 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
May 9, 2016. 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-2015-0443, 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.
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 August 26, 2015 (80 FR 51759) (FRL-9931-
74), 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
4F8284) by Bayer CropScience, 2 T. W. Alexander Drive, Research
Triangle Park, North Carolina 27709. The petition requested that 40 CFR
180.661 be amended by establishing tolerances for residues of the
fungicide fluopyram in or on the raw agricultural commodities
artichoke, globe at 4.0 parts per million; aspirated grain fractions at
50.0 ppm; peanut hay at 40.0 ppm; hops at 60.0 ppm; root vegetables,
except beet, sugar, root, crop subgroup 1B at 0.30 ppm; tuberous and
corm vegetables, crop subgroup 1C at 0.10 ppm; potato wet peel at 0.30
ppm; vegetables, leaves of root and tuber, crop group 2 at 30.0 ppm;
bulb vegetables, bulb onion (crop subgroup 3-07A) at 0.30 ppm; bulb
vegetables, green onions (crop subgroup 3-07B) at 15.0 ppm; leafy
greens (crop subgroup 4A), without spinach at 20.0 ppm; leafy greens
(crop subgroup 4A) spinach at 40.0 ppm; leafy petioles subgroup, celery
(crop subgroup 4B) at 20.0 ppm; brassica leafy vegetables: Head and
stem (crop subgroup 5A) at 4.0 ppm; brassica leafy vegetables: Leafy
greens (crop subgroup 5B) at 50.0 ppm; soybean forage at 9.0 ppm;
soybean hay at 30.0 ppm; legume vegetables: Edible podded (crop
subgroup 6A) at 4.0 ppm; legume vegetables: Succulent shelled peas and
beans (crop subgroup 6B) at 0.20 ppm; legume vegetables: Dried shelled
peas and beans (crop subgroup 6C) at 0.70 ppm; vegetable, foliage of
legume vegetables, forage, hay and vines, forage (crop group 7) at 90.0
ppm; fruiting vegetables, tomato subgroup (crop subgroup 8-10A) at 1.00
ppm; fruiting vegetables, pepper/eggplant subgroup (crop subgroup 8-
10B) at 3.00 ppm; cucurbit vegetables (crop group 9A), melon subgroup
at 0.90 ppm; cucurbit vegetables (crop group 9B), cucumber/squash
subgroup at 0.30 ppm; citrus fruits (crop group 10-10) at 0.90 ppm;
citrus oil at 8.0 ppm; pome fruit (crop group 11-10) at 2.0 ppm; stone
fruit (crop group 12-12A), cherry subgroup at 2.00 ppm; stone fruit
(crop group 12-12B), peach subgroup at 1.00 ppm; stone fruit (crop
group 12-12C), plum subgroup at 0.50 ppm; berries and small fruit:
Caneberry (crop subgroup 13-07A) at 5.0 ppm; berries and small fruit:
Bushberry (crop subgroup 13-07B) at 7.0 ppm; raisins at 4.0 ppm;
berries and small fruit, small fruit vine climbing, except fuzzy kiwi
(crop subgroup 13-07F) at 1.5 ppm; berries and small fruit: Low growing
berry (crop subgroup 13-07G) at 2.0 ppm; sorghum, grain at 1.5 ppm;
wheat milled by-products at 2.0 ppm; grass forage, fodder and hay:
Forage (crop group 17) at 80.0 ppm; herb crop (crop subgroup 19A) at
70.0 ppm; dill seed at 70.00 ppm; herbs, dried at 400 ppm; oilseeds,
rapeseed, canola (crop subgroup 20A) at 0.70 ppm; oilseeds, sunflower,
seed (crop subgroup 20B) at 0.70 ppm; and oilseeds: Cottonseed (crop
subgroup 20C) at 0.80 ppm and in or on the animal commodities chicken,
meat byproducts at 0.40 ppm; chicken, fat at 0.15 ppm; chicken, meat at
0.10 ppm; goat, fat at 4.00 ppm; and goat, meat at 4.00 ppm. Bayer
CropScience also requests to establish a tolerance in 40 CFR 180.661
for indirect or inadvertent
[[Page 12017]]
residues of the fungicide fluopyram in or on the raw agricultural
commodity sugarcane, cane at 0.08 ppm. The petition also requested to
amend tolerances in 40 CFR 180.661 for residues of the fungicide
fluopyram in or on the raw agricultural commodities peanut at 0.20 ppm;
sugar beet, roots at 0.09 ppm; soybean, seed at 0.30 ppm; soybean
forage at 9.0 ppm; soybean hay at 30.0 ppm; tree nuts (crop group 14)
at 0.04 ppm; almond hulls at 10.00 ppm; grain, cereal, except rice and
sorghum (crop group 15) at 0.90 ppm; cereal grain, except rice, forage,
fodder and straw (crop group 16) at 20.0 ppm; and cotton gin by-product
at 30.00 ppm and in or on the animal commodities cattle, meat
byproducts at 40.00 ppm; cattle, fat at 4.00 ppm; cattle, meat at 4.00
ppm; milk, cattle at 2.00 ppm; eggs, chicken at 0.20 ppm; hog, meat
byproducts at 0.40 ppm; hog, fat at 0.04 ppm; hog, meat at 0.04 ppm;
horse, meat byproducts at 40.00 ppm; horse, fat at 4.00 ppm; horse,
meat at 4.00 ppm; goat, meat byproducts at 40.00 ppm; sheep, meat
byproducts at 40.00 ppm; sheep, fat at 4.00 ppm; and sheep, meat at
4.00 ppm. Bayer CropScience also requests to delete tolerances in 40
CFR 180.661 for residues of the fungicide fluopyram in or on the raw
agricultural commodities apple at 0.30 ppm; bean, dry at 0.09 ppm;
beet, sugar, roots at 0.04 ppm; apple wet pomace at 0.60 ppm; cherry at
0.60 ppm; grape, wine at 2.0 ppm; potato at 0.02 ppm; strawberry at 1.5
ppm; and watermelon at 1.0 ppm. That document referenced a summary of
the petition prepared by Bayer CropScience, the registrant, which is
available in the docket, https://www.regulations.gov. There were no
comments received in response to the notice of filing.
Based upon review of the data supporting the petition, EPA is
issuing some tolerances that vary from the fluopyram tolerances as
requested. The reasons for these changes are explained in Unit IV.C.
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 fluopyram including exposure
resulting from the tolerances established by this action. EPA's
assessment of exposures and risks associated with fluopyram 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.
Decreased body weight and liver effects were the common and
frequent findings in the fluopyram subchronic and chronic oral toxicity
studies in rats, mice, and dogs, and they appeared to be the most
sensitive effects. Liver effects were characterized by increased liver
weight, hepatocellular hypertrophy, hepatocellular vacuolation,
increased mitosis and hepatocellular necrosis. Thyroid effects were
found at dose levels similar to those that produced liver effects in
rats and mice; these effects consisted of follicular cell hypertrophy,
increased thyroid weight, and hyperplasia at dose levels greater than
or equal to 100 milligrams/kilogram/day (mg/kg/day). Changes in thyroid
hormone levels were also seen in a subchronic toxicity study. In male
mice, there was an increased incidence of thyroid adenomas.
Although increased liver tumors were observed in female rats in the
carcinogenicity study, EPA has concluded that fluopyram is ``Not Likely
to be Carcinogenic to Humans'' at doses that do not induce cellular
proliferation in the liver or thyroid glands. This classification was
based on convincing evidence that non-genotoxic modes of action for
liver tumors in rats and thyroid tumors in mice have been established
and that the carcinogenic effects have been demonstrated as a result of
a mode of action dependent on activation of the CAR/PXR receptors. The
Agency is using a point of departure for regulating fluopyram (NOAEL of
1.2 mg/kg/day) that is below the doses that cause cell proliferation in
the liver (11 mg/kg/day) and subsequent liver tumor formation (89 mg/
kg/day); therefore, the Agency concludes that exposure to fluopyram
will not be carcinogenic. Moreover, fluopyram is not genotoxic or
mutagenic.
Fluopyram is not a developmental toxicant, nor did it adversely
affect reproductive parameters. No evidence of qualitative or
quantitative susceptibility was observed in developmental studies in
rats and rabbits or in a multigeneration study in rats.
In an acute neurotoxicity study, transient decreased motor activity
was seen only on the day of treatment, but no other findings
demonstrating neurotoxicity were observed. In addition, no
neurotoxicity was observed in the subchronic neurotoxicity study in the
presence of other systemic adverse effects. Fluopyram did not produce
treatment-related effects on the immune system.
Fluopyram has low acute toxicity via the oral, dermal, and
inhalation routes of exposure. Fluopyram is not a skin or eye irritant
or sensitizer under the conditions of the murine lymph node assay.
Specific information on the studies received and the nature of the
adverse effects caused by fluopyram 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 entitled: ``Fluopyram: Human Health
Risk Assessment for Proposed New Uses on Crop Subgroup 1B, Subgroup 1C,
Crop Group 2, Subgroup 3-07A, Subgroup 3-07B, Subgroup 4A, Subgroup 4B,
Subgroup 5A, Subgroup 5B, Subgroup 6A, Subgroup 6B, Dried Beans,
Soybean, Subgroup 8-10A, Subgroup 8-10B, Subgroup 9A, Subgroup 9B,
Subgroup 10-10, Group 11-10, Subgroup 12-12A, Subgroup 12-12B, Subgroup
12-12C, Subgroup 13-07A, Subgroup 13-07B, Subgroup 13-07F, Subgroup 13-
07G, Crop Group 15 (except corn and Rice), Crop Group 16, Subgroup 19A,
Dill Seed, Subgroup 20A, Subgroup 20B, Subgroup 20C, Artichoke (Globe),
Hops, and Sugarcane (Rotated). Amended Tolerance Requests for the
Registered Uses due to Crop Group/Subgroup Expansion Requests. Proposed
New Uses on Turf Grass, Ornamentals, and Christmas trees, and as a seed
treatment to Peanuts'' in
[[Page 12018]]
docket ID number EPA-HQ-OPP-2015-0443.
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://iaspub.epa.gov/apex/pesticides/f?p=chemicalsearch:1.
A summary of the toxicological endpoints for fluopyram used for
human risk assessment is shown in Table 1.
Table 1--Summary of Toxicological Doses and Endpoints for Fluopyram for Use in Human Health Risk Assessment
----------------------------------------------------------------------------------------------------------------
Point of departure
Exposure/scenario and uncertainty/ RfD, PAD, LOC for Study and toxicological effects
safety factors risk assessment
----------------------------------------------------------------------------------------------------------------
Acute dietary (General population NOAEL = 50 mg/kg/day Acute RfD = 0.50 mg/ Acute Neurotoxicity Study in Rats
including infants and children). UFA = 10x........... kg/day. LOAEL = 100 mg/kg/day based on
UFH =10x............ aPAD = 0.50 mg/kg/ decreased motor and locomotor
FQPA SF = 1x........ day. activity in females. The LOAEL in
males was 125 mg/kg/day.
------------------------------------------------------------------------------
Acute dietary (Females 13-50 An endpoint attributable to a single dose exposure has not been identified
years of age). for this subpopulation.
------------------------------------------------------------------------------
Chronic dietary (All populations) NOAEL = 1.2 mg/kg/ Chronic RfD = 0.012 Combined Chronic/Carcinogenicity
day. mg/kg/day. in Rats
UFA = 10x........... cPAD = 0.012 mg/kg/ LOAEL = 6.0 mg/kg/day based on
UFH = 10x........... day. follicular cell hypertrophy in
FQPA SF = 1x........ the thyroid, and increased liver
weight with gross pathological
and histopathological findings.
Incidental oral short-term (1 to NOAEL = 14.5 mg/kg/ LOC for MOE = 100.. Reproduction study in rats
30 days) and intermediate-term day. LOAEL = 82.8 mg/kg/day based on
(1 to 6 months). UFA = 10x........... clinical pathology changes,
UFH = 10x........... decreased spleen and thymus
FQPA SF = 1x........ weights, increased liver weight
and centrilobular hypertrophy in
parents, and decreased body
weight and body weight gain with
decreases in spleen and thymus
weights and slight delay in
preputial separation in
offspring.
Dermal short-term (1 to 30 days) NOAEL = 300 mg/kg/ Residential LOC for 28-day dermal study in rats
and intermediate-term (1 to 6 day. MOE = 100. LOAEL = 1000 mg/kg/day based on
months). UFA = 10x........... increased cholesterol (F),
UFH = 10x........... increased prothrombin time (M).
FQPA SF = 1x........
Inhalation short-term (1 to 30 NOAEL = 14.5 mg/kg/ Residential LOC for Reproduction study in rats
days) and intermediate-term (1-6 day. MOE = 100. LOAEL = 82.8 mg/kg/day based on
months). UFA = 10x........... clinical chemistry changes and
UFH = 10x........... increased kidney weight in
FQPA SF = 1x........ parents, and decreased body
weight and body weight gain with
decreases in spleen and thymus
weights in offspring.
------------------------------------------------------------------------------
Cancer (Oral, dermal, inhalation) ``Not Likely to be Carcinogenic to Humans'' at doses that do not induce
cellular proliferation in the liver or thyroid glands.
----------------------------------------------------------------------------------------------------------------
FQPA SF = Food Quality Protection Act Safety Factor. LOAEL = lowest-observed-adverse-effect-level. LOC = level
of concern. Mg/kg/day = milligram/kilogram/day. MOE = margin of exposure. NOAEL = no-observed-adverse-effect-
level. PAD = population adjusted dose (a = acute, c = chronic). UF = uncertainty factor. UFA = extrapolation
from animal to human (interspecies). UFH = potential variation in sensitivity among members of the human
population (intraspecies).
C. Exposure Assessment
1. Dietary exposure from food and feed uses. In evaluating dietary
exposure to fluopyram, EPA considered exposure under the petitioned-for
tolerances as well as all existing fluopyram tolerances in 40 CFR
180.661. EPA assessed dietary exposures from fluopyram 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 fluopyram. In estimating acute dietary exposure, EPA used food
consumption information from the United States Department of
Agriculture (USDA) 2003-2008 National Health and Nutrition Examination
Survey/What We Eat in America (NHANES/WWEIA). As to residue levels in
food, EPA included tolerance residue levels, the assumption
[[Page 12019]]
of 100% crop treated, and processing factors (empirical and default).
ii. Chronic exposure. In conducting the chronic dietary exposure
assessment EPA used the food consumption data from the USDA 2003-2008
NHANES/WWEIA. As to residue levels in food, EPA included average
residue levels, % crop treated, and processing factors (empirical and
default).
iii. Cancer. Based on the data summarized in Unit III.A., EPA has
concluded that fluopyram does not pose a cancer risk to humans at doses
that do not induce cellular proliferation in the liver or thyroid
glands. Therefore, a dietary exposure assessment for the purpose of
assessing cancer risk is unnecessary.
iv. Anticipated residue and percent crop treated (PCT) information.
Section 408(b)(2)(E) of FFDCA authorizes EPA to use available data and
information on the anticipated residue levels of pesticide residues in
food and the actual levels of pesticide residues that have been
measured in food. If EPA relies on such information, EPA must require
pursuant to FFDCA section 408(f)(1) that data be provided 5 years after
the tolerance is established, modified, or left in effect,
demonstrating that the levels in food are not above the levels
anticipated. For the present action, EPA will issue such data call-ins
as are required by FFDCA section 408(b)(2)(E) and authorized under
FFDCA section 408(f)(1). Data will be required to be submitted no later
than 5 years from the date of issuance of these tolerances.
Section 408(b)(2)(F) of FFDCA states that the Agency may use data
on the actual percent of food treated for assessing chronic dietary
risk only if:
Condition a: The data used are reliable and provide a
valid basis to show what percentage of the food derived from such crop
is likely to contain the pesticide residue.
Condition b: The exposure estimate does not underestimate
exposure for any significant subpopulation group.
Condition c: Data are available on pesticide use and food
consumption in a particular area, the exposure estimate does not
understate exposure for the population in such area.
In addition, the Agency must provide for periodic evaluation of any
estimates used. To provide for the periodic evaluation of the estimate
of PCT as required by FFDCA section 408(b)(2)(F), EPA may require
registrants to submit data on PCT.
The Agency estimated the PCT for the chronic dietary exposure
assessment for existing uses as follows:
Almonds 33%; apples 40%; blackberries 55%; blueberries 54%;
broccoli 24%; cantaloupes 22%; celery 60%; corn field 9%; corn, sweet
15%; cucumbers 41%; dry beans/peas 7%; fresh tomatoes 64%; grape wine
79% (used for grape, wine and sherry); head lettuce 67%; leaf lettuce
62%; oranges 39%; peaches 56%; pears 43%; peanuts 67%; potatoes 64%;
processed tomatoes 57%; pumpkins 45%; snap beans 44%; soybeans 17%;
spinach 43%; squash 47%; strawberries 75%; sugar beets 48%; watermelons
54%; and wheat 17% (from spring wheat at 17% and winter wheat at 6%).
In most cases, EPA uses available data from United States
Department of Agriculture/National Agricultural Statistics Service
(USDA/NASS), proprietary market surveys, and the National Pesticide Use
Database for the chemical/crop combination for the most recent 6-7
years. EPA uses an average PCT for chronic dietary risk analysis. The
average PCT figure for each existing use is derived by combining
available public and private market survey data for that use, averaging
across all observations, and rounding to the nearest 5%, except for
those situations in which the average PCT is less than one. In those
cases, 1% is used as the average PCT and 2.5% is used as the maximum
PCT. EPA uses a maximum PCT for acute dietary risk analysis. The
maximum PCT figure is the highest observed maximum value reported
within the recent 6 years of available public and private market survey
data for the existing use and rounded up to the nearest multiple of 5%.
The Agency believes that the three conditions discussed in Unit
III.C.1.iv. have been met. With respect to Condition a, PCT estimates
are derived from federal and private market survey data, which are
reliable and have a valid basis. The Agency is reasonably certain that
the percentage of the food treated is not likely to be an
underestimation. As to Conditions b and c, regional consumption
information and consumption information for significant subpopulations
is taken into account through EPA's computer-based model for evaluating
the exposure of significant subpopulations including several regional
groups. Use of this consumption information in EPA's risk assessment
process ensures that EPA's exposure estimate does not understate
exposure for any significant subpopulation group and allows the Agency
to be reasonably certain that no regional population is exposed to
residue levels higher than those estimated by the Agency. Other than
the data available through national food consumption surveys, EPA does
not have available reliable information on the regional consumption of
food to which fluopyram may be applied in a particular area.
2. Dietary exposure from drinking water. The Agency used screening-
level water exposure models in the dietary exposure analysis and risk
assessment for fluopyram in drinking water. These simulation models
take into account data on the physical, chemical, and fate/transport
characteristics of fluopyram. Further information regarding EPA
drinking water models used in pesticide exposure assessment can be
found at https://www.epa.gov/oppefed1/models/water/index.htm.
Based on the Pesticide Root Zone Model Ground Water (PRZM GW) and
the surface water concentration calculator (SWCC), the estimated
drinking water concentrations (EDWCs) of fluopyram for acute exposures
are estimated to be 50.6 parts per billion (ppb) for surface water and
97.6 ppb for ground water. The chronic exposures for non-cancer
assessments are estimated to be 17.3 ppb for surface water and 90.5 ppb
for ground water.
Modeled estimates of drinking water concentrations were directly
entered into the dietary exposure model. For acute dietary risk
assessment, the water concentration value of 97.6 ppb was used to
assess the contribution to drinking water. For chronic dietary risk
assessment, the water concentration of value 90.5 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).
Fluopyram is proposed for use that could result in residential
exposures: golf course turf, residential lawns, fruit trees, nut trees,
ornamentals and gardens. EPA assessed residential exposure using the
following assumptions: short-term dermal, oral (derived from incidental
oral hand to mouth post-application exposures to treated lawn in
children), and inhalation exposures derived from treating lawns by
hose-end sprayers (adults); residential post-application exposures:
adults and children (1 to <2 years old) dermal exposure to treated turf
during high contact lawn activities; children (1 to <2 years old)
incidental oral exposure as a result of contacting treated turf; adults
and youths (11 to <16 yr old) dermal exposure to treated turf during
mowing and golfing activities; children (6 to <11 years old) dermal
exposure to treated turf during golfing activities; and adults and
[[Page 12020]]
children (6 to <11 years old) dermal exposure to treated gardens.
Further information regarding EPA standard assumptions and generic
inputs for residential exposures may be found at https://www.epa.gov/pesticides/trac/science/trac6a05.pdf.
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 fluopyram
to share a common mechanism of toxicity with any other substances, and
fluopyram does not appear to produce a toxic metabolite produced by
other substances. For the purposes of this tolerance action, therefore,
EPA has assumed that fluopyram 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 Web site
at https://www.epa.gov/pesticides/cumulative.
D. Safety Factor for Infants and Children
1. In general. Section 408(b)(2)(C) of FFDCA provides that EPA
shall apply an additional tenfold (10X) margin of safety for infants
and children in the case of threshold effects to account for prenatal
and postnatal toxicity and the completeness of the database on toxicity
and exposure unless EPA determines based on reliable data that a
different margin of safety will be safe for infants and children. This
additional margin of safety is commonly referred to as the FQPA Safety
Factor (SF). In applying this provision, EPA either retains the default
value of 10X, or uses a different additional safety factor when
reliable data available to EPA support the choice of a different
factor.
2. Prenatal and postnatal sensitivity. The available developmental
toxicity studies in rats and rabbits and the multi-generation
reproduction in rats demonstrate no evidence of increased
susceptibility in the developing or young animals which were exposed
during pre- or post-natal periods.
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 fluopyram is complete.
ii. There is no indication that fluopyram is a neurotoxic chemical.
Although transient decreases in motor and locomotor activities in the
acute neurotoxicity study were seen on the day of treatment and limited
use of hind-limbs and reduced motor activity was seen in the rat
chronic/carcinogenicity study, there were no other associated
neurobehavioral or histopathology changes found in other studies in the
fluopyram toxicity database. The effects seen in the chronic/
carcinogenicity study were in the presence of increased mortality and
morbidity such as general pallor and emaciated appearance. Therefore,
the reduced motor activity and limited use of hind-limbs seen in these
two studies were judged to be the consequence of the systemic effects
and not direct neurotoxicity. Additionally there is no need for a
developmental neurotoxicity study or additional UFs to account for
neurotoxicity.
iii. There is no evidence that fluopyram results in increased
susceptibility in in utero rats or rabbits in the prenatal
developmental studies or in young rats in the 2-generation reproduction
study.
iv. There are no residual uncertainties identified in the exposure
databases. The acute dietary exposure assessment was performed using
conservative exposure inputs, including tolerance-level residues for
all crops, whereas the chronic dietary assessment included average
field-trial residue levels for all crops. The acute dietary assessment
assumed 100 PCT, whereas the chronic dietary assessment utilized
average percent crop treated numbers for several crops. Both acute and
chronic dietary assessments incorporated empirical or default
processing factors. The dietary exposure assessment also assumed that
all drinking water will contain fluopyram at the highest EDWC levels
modeled by the Agency for ground or surface water. Therefore, it can be
concluded that the dietary exposure analysis does not underestimate
risk from acute and chronic dietary exposure to fluopyram. While there
is the potential for handler and post-application residential exposure,
the best data and approaches currently available were used in the
fluopyram residential assessment. The Agency used the current
conservative approaches for residential assessment, many of which
include recent upgrades to the SOPs. The Agency believes that the
calculated risks represent conservative estimates of exposure because
maximum application rates are used to define residue levels upon which
the calculations are based. Therefore, residential exposures are
unlikely to be underestimated.
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 fluopyram will occupy 35% of the aPAD for children 1-2 years 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
fluopyram from food and water will utilize 81% of the cPAD for children
1-2 years 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 fluopyram 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). Fluopyram 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 fluopyram.
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 from handler
inhalation exposure (the most conservative risk estimate) of 1,500 for
adults. For children 1-2 years old, post-application incidental oral
exposures aggregated with food and drinking water resulted in an MOE of
1,500. Because EPA's level of concern for fluopyram is a MOE of 100 or
below, these MOEs are not of concern.
4. Intermediate-term risk. Intermediate-term aggregate exposure
[[Page 12021]]
takes into account intermediate-term residential exposure plus chronic
exposure to food and water (considered to be a background exposure
level). Intermediate-term residential exposure is not expected given
the intermittent nature of applications in residential settings.
5. Aggregate cancer risk for U.S. population. As discussed in Unit
III.A, because the Agency is regulating exposure to fluopyram at doses
lower than those that may induce cellular proliferation in the liver or
thyroid glands, fluopyram is not expected to pose a cancer risk to
humans.
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 fluopyram residues.
IV. Other Considerations
A. Analytical Enforcement Methodology
The German multiresidue method DFG Method S 19, a gas
chromatography with mass selective detection (GC/MSD) method, is the
method for the enforcement of tolerances for fluopyram residues in/on
crop commodities and a high performance liquid chromatography method
with tandem mass spectrometry detection (HPLC/MS/MS), Method 01079, has
been accepted for the enforcement of tolerances for residues of
fluopyram and its metabolite, AE C656948-benzamide, in livestock
commodities. The validated limit of quantitation (LOQ) is 0.01 ppm and
the calculated limit of detection (LOD) is 0.003 ppm for each analyte
in each matrix. The method was adequately validated using cattle milk,
fat, muscle, liver, and kidney, and hen whole egg fortified with
fluopyram and AE C656948-benzamide, each at 0.01 and 0.10 ppm. The
method was subjected to ILV using samples of beef muscle, beef liver,
eggs, and milk fortified with fluopyram and AE C656948-benzamide, each
at 0.01 and 0.10 ppm.
Adequate enforcement methodology DFG Method S 19 and Method 01079
are available to enforce the tolerance expression.
The method may be requested from: Chief, Analytical Chemistry
Branch, Environmental Science Center, 701 Mapes Rd., Ft. Meade, MD
20755-5350; telephone number: (410) 305-2905; email address:
residuemethods@epa.gov.
B. International Residue Limits
In making its tolerance decisions, EPA seeks to harmonize U.S.
tolerances with international standards whenever possible, consistent
with U.S. food safety standards and agricultural practices. EPA
considers the international maximum residue limits (MRLs) established
by the Codex Alimentarius Commission (Codex), as required by FFDCA
section 408(b)(4). The Codex Alimentarius is a joint United Nations
Food and Agriculture Organization/World Health Organization food
standards program, and it is recognized as an international food safety
standards-setting organization in trade agreements to which the United
States is a party. EPA may establish a tolerance that is different from
a Codex MRL; however, FFDCA section 408(b)(4) requires that EPA explain
the reasons for departing from the Codex level.
There are Codex maximum residue levels MRLs established on berries
(blackberry and raspberry 3 ppm), broccoli and Brussels sprouts (0.3
ppm), dry beans (0.07 ppm), head cabbage (0.15 ppm), carrot (0.4 ppm),
cauliflower (0.09 ppm), cherry (0.7 ppm), cucumber (0.5 ppm), dried
grapes (currants, raisins and sultanas 5 ppm), grapes (2 ppm), leek
(0.15 ppm), lettuce (head and leaf 15 ppm), onion bulb (0.07 ppm),
peach subgroup (1 ppm), peanut (0.03 ppm), plums (0.5 ppm), pome fruits
(0.5 ppm), potato (0.03 ppm), rapeseed (1 ppm), strawberry (0.4 ppm),
sugar beet (0.04 ppm), tomato (0.4 ppm), and tree nuts (0.04 ppm).
The tolerance definitions are harmonized among the US, Canada, and
Codex for all plant and livestock commodities. In addition, the U.S.
tolerances for grape (within the fruit, small vine climbing, except
fuzzy kiwifruit, subgroup 13-07F), peach (within the fruit, stone,
peach subgroup 12-12B), and plum (within the fruit, stone, plum
subgroup 12-12C) are harmonized with the Codex MRLs for grape, peach,
and plum.
Harmonization with Codex MRLs for berries (blackberry and raspberry
3 ppm), broccoli and Brussels sprouts (0.3 ppm), dry beans (0.70 ppm),
head cabbage (0.15 ppm), cauliflower (0.09 ppm), cherry (0.7 ppm),
cucumber (0.5 ppm), leek (0.15 ppm), lettuce (head and leaf 15 ppm),
onion bulb (0.07 ppm), peanut (0.03 ppm), pome fruits (0.5 ppm), potato
(0.03 ppm), rapeseed (1 ppm), strawberry (0.4 ppm), sugar beet (0.04
ppm), tomato (0.4 ppm), and tree nuts (0.04 ppm) is not possible
because the Codex MRLs are lower than the recommended U.S. tolerances.
The U.S. tolerances cannot be harmonized because following the approved
label directions could result in residues above the recommended
tolerances. The U.S. tolerances for carrot and raisin are higher than
the Codex MRLs. EPA is not harmonized with Codex in order to remain
harmonized with Canada.
The U.S. and Codex livestock MRLs are not harmonized due to
different livestock dietary burdens. Fluopyram is approved for use on
more livestock feed stuffs in the United States and thus contributes to
a greater portion of the assessment of the livestock dietary burden in
the United States than in the assessment of livestock dietary burden
supporting the Codex MRLs. Harmonization could lead to tolerance
exceedances when the pesticide is used legally in the United States.
C. Revisions to Petitioned-For Tolerances
The petitioned-for tolerances differ from the tolerances that EPA
is establishing for sugar beet roots, onion bulbs, leafy greens
subgroup 4A, crop subgroup 6C, fruiting vegetables (8-10B), melon
subgroup 9A, citrus, subgroup 13-07F, raisin, tree nuts, crop group 15,
herb subgroup 19A, dill seed, and subgroup 20A.
For citrus, crop group 15, fruiting vegetables (8-10B), onion
bulbs, rapeseed subgroup 20A, and tree nuts, the Organization for
Economic Cooperation and Development (OECD) statistical calculation
procedures applied to the field trial residue data provided a different
value than the petitioned-for tolerances. Also, for crop group 15 and
subgroup 20A, the values petitioner requested were based on a data set
that excluded a field trial (on sorghum and canola, respectively) as an
outlier based on statistical tests. However, the trials could not be
excluded by the Agency since there were no abnormal field conditions.
While the petitioner requested a tolerance for crop group 15,
except rice and sorghum, the Agency has determined that a crop group 15
tolerance, except corn and rice is appropriate. This is due to the wide
variation in residue levels from the available data. The minimum
residues on sweet corn at 0.01 ppm and the maximum residues on sorghum
3.2 ppm differ by more than 5x; therefore, the tolerance level (1.5
ppm) is not appropriate to establish a crop group tolerance with all
the representative crops. Rather, based on the available data, EPA is
establishing tolerances on grain, cereal, except rice and corn, group
15 at 4.0 ppm; and individual tolerance on corn, field, grain at 0.02
ppm; corn, pop, grain at 0.02 ppm; and corn, sweet, kernal plus cob
with husks removed at 0.01 ppm.
[[Page 12022]]
Although the petitioner requested two separate tolerances for
commodities of subgroup 4A, the available data support a tolerance of
40 ppm for residues of fluopyram in/on leafy greens subgroup 4A and at
20 ppm on leaf petioles subgroup 4B.
The petitioner requested two separate tolerances for herb subgroup
19A, fresh and herbs, dried. Because subgroup 19A covers both dried and
fresh herbs, the Agency is establishing a tolerance on herb subgroup
19A at 40 ppm, based on available data.
The petitioner has requested to establish tolerances on vegetables,
legume; dried beans and peas, except soybeans (subgroup 6C) at 0.70
ppm. Because only data on dried beans is available, there is not
sufficient data to support establishing a subgroup tolerance.
Therefore, based on the available residue data for dried beans, the
Agency is establishing an individual tolerance of 0.70 ppm on dried
beans only. EPA is establishing dry bean tolerance at 0.70 ppm to
harmonize with Canada.
The petitioner had requested to establish tolerances on vegetables,
cucurbit, cucumber/squash subgroup at 0.30 ppm and fruit, pome at 1.0
ppm. Based on available data that reflect the proposed use pattern, EPA
is establishing a tolerance on squash/cucumber subgroup 9B at 0.60 ppm
and fruit, pome, group 11-10 at 0.80 ppm.
For harmonization purposes with Canada, tolerances being
established for sugar beet, melon subgroup 9A, tree nuts, and subgroup
13-07F are slightly increased above the tolerance levels requested for
those commodities.
The requested grape, raisin tolerance of 4.0 ppm is being reduced
to 3.0 ppm based on the highest average field trial (HAFT) (0.948 ppm)
for grape and processing factor of 2.4.
Because use of fluopyram is limited to Region 3 (Florida), the
Agency is establishing a tolerance with a regional registration for
inadvertent or indirect residues of fluopyram on sugarcane, cane (0.08
ppm) when sugarcane is used as a rotational crop.
The requested tolerances for livestock commodities were based on
some livestock feed stuffs that have been withdrawn from the list of
crops to be treated with fluopyram. Based on a recalculation of the
livestock dietary burden, the Agency is establishing tolerances for
livestock commodities that are lower than requested.
In addition, the Agency has revised several commodity terms to
reflect the current commodity definitions used by the Agency and
revised several tolerance level values to be consistent with EPA's
practice of extending tolerance values out to two significant figures.
Although the petition requested a tolerance for nut tree group 14,
the Agency is establishing a tolerance for nut, tree 14-12 consistent
with its stated policy of not establishing tolerances for pre-existing
crop groups. See 77 FR 50617, 50619 (Aug. 22, 2012).
Finally, the requests for tolerances were withdrawn for the
following commodities: Crop group 7 at 90.0 ppm; crop group 17 at 80.0
ppm; peanut hay at 40.0 ppm, soybean forage at 9.0 ppm; and soybean hay
at 30.0 ppm. A separate tolerance for wheat, milled byproducts is not
needed as it is covered by the crop group 15 tolerance.
V. Conclusion
Therefore, tolerances are established for residues of fluopyram in
or on almond, hulls at 10 ppm; artichoke, globe at 4.0 ppm, bean, dry
at 0.70 ppm; beet, sugar at 0.10 ppm; berry, low growing, except
cranberry, subgroup 13-07G at 2.0 ppm; brassica, head and stem,
subgroup 5A at 4.0 ppm; brassica, leafy greens, subgroup 5B at 50 ppm;
bushberry subgroup 13-07B at 7.0 ppm; grain, aspirated grain fractions
at 50 ppm; caneberry subgroup 13-07A at 5.0 ppm; cereal, forage, fodder
and straw, group 16 at 20 ppm; cherry subgroup 12-12A at 2.0 ppm;
citrus, oil at 8.0 ppm; corn, field, grain at 0.02 ppm; corn, pop,
grain at 0.02 ppm; corn, sweet, kernel plus cob with husks removed 0.01
ppm; cotton, gin byproducts at 30 ppm; cottonseed subgroup 20C at 0.80
ppm; dill, seed at 70 ppm; rapeseed subgroup 20A at 5.0 ppm; fruit,
citrus, group 10-10 at 1.0 ppm; fruit, pome, group 11-10 at 0.80 ppm;
fruit, small vine climbing, except fuzzy kiwifruit, subgroup 13-07F at
2.0 ppm; grape, raisin at 3.0 ppm; grain, cereal, group 15, except corn
and rice at 4.0 ppm; grain, herb subgroup 19A at 40 ppm; hop, dried
cones at 60 ppm; leaf petioles subgroup 4B at 20 ppm; leafy greens
subgroup 4A at 40 ppm; melon subgroup 9A at 1.0 ppm; nut, tree, group
14-12 at 0.05 ppm; onion, bulb, subgroup 3-07A at 0.40 ppm; onion,
green, subgroup 3-07B at 15 ppm; pea and bean, succulent shelled,
subgroup 6B at 0.20 ppm; peach subgroup 12-12B at 1.0 ppm; peanut at
0.20 ppm; potato, wet peel at 0.30 ppm; pepper/eggplant subgroup 8-10B
at 4.0 ppm; plum subgroup 12-12C at 0.50 ppm; soybean, seed at 0.30
ppm; squash/cucumber subgroup 9B at 0.60 ppm; sunflower subgroup 20B at
0.70 ppm; tomato subgroup 8-10A at 1.0 ppm; vegetable, leaves of root
and tuber, group 2 at 30 ppm; vegetable, legume, edible podded,
subgroup 6A at 4.0 ppm; vegetable, root, except sugar beet, subgroup 1B
at 0.30 ppm; and vegetable, tuberous and corm, subgroup 1C at 0.10 ppm.
Tolerances are also established for residues of fluopyram and its
metabolite 2-(trifluoromethyl)benzamide, expressed in parent
equivalents for cattle, fat at 0.70 ppm; cattle, meat at 0.80 ppm;
cattle, meat byproducts at 7.5 ppm; egg at 0.08 ppm; goat, fat at 0.70
ppm; goat, meat at 0.80 ppm; goat, meat byproducts at 7.5 ppm; hog,
meat byproducts at 0.20 ppm; horse, fat at 0.70 ppm; horse, meat at
0.80 ppm; horse, meat byproducts at 7.5 ppm; milk at 0.40 ppm; poultry,
fat at 0.04 ppm; poultry, meat at 0.04 ppm; poultry, meat byproducts at
0.16 ppm; sheep, fat at 0.70 ppm; sheep, meat at 0.80 ppm; and sheep,
meat byproducts at 7.5 ppm.
In addition, the Agency is removing tolerances for almond, hull;
apple, wet pomace; bean, dry; beet, sugar, root; canola seed; cotton,
gin byproducts; cotton, undelinted seed; cherry; grape, wine; grain,
cereal, except rice, group 15; grain, cereal, forage, fodder, and
straw, group 16; nut, tree, group 14; peanut; pistachio; potato;
soybean forage; soybean hay; soybean, seed; strawberry; and watermelon
because they are superseded by other tolerances being established in
this action.
VI. Statutory and Executive Order Reviews
This action establishes tolerances under FFDCA section 408(d) in
response to a petition submitted to the Agency. The Office of
Management and Budget (OMB) has exempted these types of actions from
review under Executive Order 12866, entitled ``Regulatory Planning and
Review'' (58 FR 51735, October 4, 1993). Because this action has been
exempted from review under Executive Order 12866, this action is not
subject to Executive Order 13211, entitled ``Actions Concerning
Regulations That Significantly Affect Energy Supply, Distribution, or
Use'' (66 FR 28355, May 22, 2001) or Executive Order 13045, entitled
``Protection of Children from Environmental Health Risks and Safety
Risks'' (62 FR 19885, April 23, 1997). 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).
[[Page 12023]]
Since tolerances and exemptions that are established on the basis
of a petition under FFDCA section 408(d), such as the tolerance in this
final rule, do not require the issuance of a proposed rule, the
requirements of the Regulatory Flexibility Act (RFA) (5 U.S.C. 601 et
seq.), do not apply.
This action directly regulates growers, food processors, food
handlers, and food retailers, not States or tribes, nor does this
action alter the relationships or distribution of power and
responsibilities established by Congress in the preemption provisions
of FFDCA section 408(n)(4). As such, the Agency has determined that
this action will not have a substantial direct effect on States or
tribal governments, on the relationship between the national government
and the States or tribal governments, or on the distribution of power
and responsibilities among the various levels of government or between
the Federal Government and Indian tribes. Thus, the Agency has
determined that Executive Order 13132, entitled ``Federalism'' (64 FR
43255, August 10, 1999) and Executive Order 13175, entitled
``Consultation and Coordination with Indian Tribal Governments'' (65 FR
67249, November 9, 2000) do not apply to this action. In addition, this
action does not impose any enforceable duty or contain any unfunded
mandate as described under Title II of the Unfunded Mandates Reform Act
(UMRA) (2 U.S.C. 1501 et seq.).
This action does not involve any technical standards that would
require Agency consideration of voluntary consensus standards pursuant
to section 12(d) of the National Technology Transfer and Advancement
Act (NTTAA) (15 U.S.C. 272 note).
VII. Congressional Review Act
Pursuant to the Congressional Review Act (5 U.S.C. 801 et seq.),
EPA will submit a report containing this rule and other required
information to the U.S. Senate, the U.S. House of Representatives, and
the Comptroller General of the United States prior to publication of
the rule in the Federal Register. This action is not a ``major rule''
as defined by 5 U.S.C. 804(2).
List of Subjects in 40 CFR Part 180
Environmental protection, Administrative practice and procedure,
Agricultural commodities, Pesticides and pests, Reporting and
recordkeeping requirements.
Dated: March 1, 2016.
G. Jeffery Herndon,
Acting 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. Section 180.661 is revised to read as follows:
Sec. 180.661 Fluopyram; tolerances for residues.
(a) General. (1) Tolerances are established for residues of the
fungicide Fluopyram, N-[2-[3-chloro-5-(trifluoromethyl)-2-
pyridinyl]ethyl]-2-(trifluoromethyl)benzamide, including its
metabolites and degradates in or on the commodities in the table below.
Compliance with the tolerance levels specified in the table is to be
determined by measuring only fluopyram in or on the commodity.
------------------------------------------------------------------------
Parts per
Commodity million
------------------------------------------------------------------------
Almond, hulls............................................... 10
Artichoke, globe............................................ 4.0
Banana \1\.................................................. 1.0
Bean, dry................................................... 0.70
Beet, sugar................................................. 0.10
Berry, low growing, except cranberry, subgroup 13-07G....... 2.0
Brassica, head and stem, subgroup 5A........................ 4.0
Brassica, leafy greens, subgroup 5B......................... 50
Bushberry subgroup 13-07B................................... 7.0
Caneberry subgroup 13-07A................................... 5.0
Cherry subgroup 12-12A...................................... 2.0
Citrus, oil................................................. 8.0
Corn, field, grain.......................................... 0.02
Corn, pop, grain............................................ 0.02
Corn, sweet, kernel plus cob with husks removed............. 0.01
Cotton, gin byproducts...................................... 30
Cottonseed subgroup 20C..................................... 0.80
Dill, seed.................................................. 70
Fruit, citrus, group 10-10.................................. 1.0
Fruit, pome, group 11-10.................................... 0.80
Fruit, small vine climbing, except fuzzy kiwifruit, subgroup 2.0
13-07F.....................................................
Grain, aspirated grain fractions............................ 50
Grain, cereal, forage, fodder and straw, group 16........... 20
Grain, cereal, group 15, except corn and rice............... 4.0
Grape, raisin............................................... 3.0
Herb subgroup 19A........................................... 40
Hop, dried cones............................................ 60
Leafy greens subgroup 4A.................................... 40
Leafy petioles subgroup 4B.................................. 20
Melon subgroup 9A........................................... 1.0
Nut, tree, group 14-12...................................... 0.05
Onion, bulb, subgroup 3-07A................................. 0.40
Onion, green, subgroup 3-07B................................ 15
Pea and bean, succulent shelled, subgroup 6B................ 0.20
Peach subgroup 12-12B....................................... 1.0
Peanut...................................................... 0.20
Pepper/eggplant subgroup 8-10B.............................. 4.0
Plum subgroup 12-12C........................................ 0.50
Potato, wet peel............................................ 0.30
Rapeseed subgroup 20A....................................... 5.0
Soybean, seed............................................... 0.30
Squash/cucumber subgroup 9B................................. 0.60
Sunflower subgroup 20B...................................... 0.70
Tomato subgroup 8-10A....................................... 1.0
Vegetable, leaves of root and tuber, group 2................ 30
Vegetable, legume, edible podded, subgroup 6A............... 4.0
Vegetable, root, except sugar beet, subgroup 1B............. 0.30
Vegetable, tuberous and corm, subgroup 1C................... 0.10
------------------------------------------------------------------------
\1\ There are no U.S. registrations.
(2) Tolerances are established for residues of the fungicide
fluopyram, N-[2-[3-chloro-5-(trifluoromethyl)-2-pyridinyl]ethyl]-2-
(trifluoromethyl)benzamide, including its metabolites and degradates.
Compliance with the tolerance levels specified in the table below is to
be determined by measuring only the sum of fluopyram and its
metabolite, 2-(trifluoromethyl)benzamide, calculated as the
stoichiometric equivalent of fluopyram, in or on the commodity.
------------------------------------------------------------------------
Parts per
Commodity million
------------------------------------------------------------------------
Cattle, fat................................................. 0.70
Cattle, meat................................................ 0.80
Cattle, meat byproducts..................................... 7.5
Egg......................................................... 0.08
Goat, fat................................................... 0.70
Goat, meat.................................................. 0.80
Goat, meat byproducts....................................... 7.5
Hog, fat.................................................... 0.20
Hog, meat................................................... 0.02
Hog, meat byproducts........................................ 0.20
Horse, fat.................................................. 0.70
Horse, meat................................................. 0.80
Horse, meat byproducts...................................... 7.5
Milk........................................................ 0.40
Poultry, fat................................................ 0.04
Poultry, meat............................................... 0.04
Poultry, meat byproducts.................................... 0.20
Sheep, fat.................................................. 0.70
Sheep, meat................................................. 0.80
Sheep, meat byproducts...................................... 7.5
------------------------------------------------------------------------
(b) Section 18 emergency exemptions. [Reserved]
(c) Tolerances with regional registrations. Tolerances with
regional registration, as defined in Sec. 180.1(1), are established
for indirect or inadvertent residues of fungicide fluopyram, N-[2-[3-
chloro-5-(trifluoromethyl)-2-pyridinyl]ethyl]-2-
(trifluoromethyl)benzamide, including
[[Page 12024]]
its metabolites and degradates, in or on the commodities in the table
below. Compliance with the tolerance levels specified in the table is
to be determined by measuring only fluopyram in or on the commodity.
------------------------------------------------------------------------
Parts per
Commodity million
------------------------------------------------------------------------
Sugarcane, cane............................................ 0.08
------------------------------------------------------------------------
(d) Indirect or inadvertent residues. It is recommended that
tolerances be established for indirect or inadvertent residues of
fungicide fluopyram, N-[2-[3-chloro-5-(trifluoromethyl)-2-
pyridinyl]ethyl]-2-(trifluoromethyl)benzamide, including its
metabolites and degradates, in or on the commodities in the table
below. Compliance with the tolerance levels specified in the table is
to be determined by measuring only fluopyram in or on the commodity.
------------------------------------------------------------------------
Parts per
Commodity million
------------------------------------------------------------------------
Alfalfa, forage............................................ 0.45
Alfalfa, hay............................................... 1.1
Soybean, seed.............................................. 0.10
------------------------------------------------------------------------
[FR Doc. 2016-05025 Filed 3-7-16; 8:45 am]
BILLING CODE 6560-50-P