Picoxystrobin; Pesticide Tolerances, 39605-39610 [2018-17192]
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Federal Register / Vol. 83, No. 155 / Friday, August 10, 2018 / Rules and Regulations
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[FR Doc. 2018–17078 Filed 8–9–18; 8:45 am]
BILLING CODE 6560–50–P
ENVIRONMENTAL PROTECTION
AGENCY
40 CFR Part 180
[EPA–HQ–OPP–2017–0429; FRL–9980–47]
Picoxystrobin; Pesticide Tolerances
Environmental Protection
Agency (EPA).
ACTION: Final rule.
AGENCY:
This regulation establishes
tolerances for residues of picoxystrobin
in or on multiple commodities that are
identified and discussed later in this
document. E.I. DuPont De Nemours and
Company requested these tolerances
under the Federal Food, Drug, and
Cosmetic Act (FFDCA).
DATES: This regulation is effective
August 10, 2018. Objections and
requests for hearings must be received
on or before October 9, 2018, and must
be filed in accordance with the
instructions provided in 40 CFR part
178 (see also Unit I.C. of the
SUPPLEMENTARY INFORMATION).
ADDRESSES: The docket for this action,
identified by docket identification (ID)
number EPA–HQ–OPP–2017–0429, is
available at https://www.regulations.gov
or at the Office of Pesticide Programs
Regulatory Public Docket (OPP Docket)
in the Environmental Protection Agency
Docket Center (EPA/DC), West William
Jefferson Clinton Bldg., Rm. 3334, 1301
Constitution Ave. NW, Washington, DC
20460–0001. The Public Reading Room
is open from 8:30 a.m. to 4:30 p.m.,
Monday through Friday, excluding legal
holidays. The telephone number for the
Public Reading Room is (202) 566–1744,
and the telephone number for the OPP
Docket is (703) 305–5805. Please review
the visitor instructions and additional
information about the docket available
at https://www.epa.gov/dockets.
FOR FURTHER INFORMATION CONTACT:
Michael L. Goodis, P.E., Registration
Division (7505P), Office of Pesticide
Programs, Environmental Protection
Agency, 1200 Pennsylvania Ave. NW,
Washington, DC 20460–0001; main
telephone number: (703) 305–7090;
email address: RDFRNotices@epa.gov.
SUPPLEMENTARY INFORMATION:
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SUMMARY:
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
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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/textidx?&c=ecfr&tpl=/ecfrbrowse/Title40/
40tab_02.tpl. To access the OCSPP test
guidelines referenced in this document
electronically, please go to https://
www.epa.gov/ocspp and select ‘‘Test
Methods and Guidelines.’’
C. How can I file an objection or hearing
request?
Under FFDCA section 408(g), 21
U.S.C. 346a, any person may file an
objection to any aspect of this regulation
and may also request a hearing on those
objections. You must file your objection
or request a hearing on this regulation
in accordance with the instructions
provided in 40 CFR part 178. To ensure
proper receipt by EPA, you must
identify docket ID number EPA–HQ–
OPP–2017–0429 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 October 9, 2018. Addresses for
mail and hand delivery of objections
and hearing requests are provided in 40
CFR 178.25(b).
In addition to filing an objection or
hearing request with the Hearing Clerk
as described in 40 CFR part 178, please
submit a copy of the filing (excluding
any Confidential Business Information
(CBI)) for inclusion in the public docket.
Information not marked confidential
pursuant to 40 CFR part 2 may be
disclosed publicly by EPA without prior
notice. Submit the non-CBI copy of your
objection or hearing request, identified
by docket ID number EPA–HQ–OPP–
2017–0429, 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
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39605
information you consider to be CBI or
other information whose disclosure is
restricted by statute.
• Mail: OPP Docket, Environmental
Protection Agency Docket Center (EPA/
DC), (28221T), 1200 Pennsylvania Ave.
NW, Washington, DC 20460–0001.
• Hand Delivery: To make special
arrangements for hand delivery or
delivery of boxed information, please
follow the instructions at https://
www.epa.gov/dockets/contacts.html.
Additional instructions on
commenting or visiting the docket,
along with more information about
dockets generally, is available at https://
www.epa.gov/dockets.
II. Summary of Petitioned-For
Tolerance
In the Federal Register of November
27, 2017 (82 FR 56017) (FRL–9968–55),
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 7F8557) by E.I. Du
Pont De Nemours and Company,
Chestnut Run Plaza, 974 Centre Road,
Wilmington, DE 19805. The petition
requested 40 CFR 180.669 be amended
by establishing tolerances for residues of
the fungicide picoxystrobin, methyl
(aE)-a-(methoxymethylene)-2-[[[6(trifluoromethyl)-2pyridinyl]oxy]methyl]benzeneacetate, in
or on alfalfa, forage at 4 parts per
million (ppm); alfalfa, hay at 5 ppm;
alfalfa, seed at 9 ppm; almond hulls at
15 ppm; cotton, gin by-products at 40
ppm; cottonseed (Crop Subgroup 20C) at
4 ppm; grass, forage (Grown for Seed) at
40 ppm; grass, hay (Grown for Seed) at
80 ppm; head lettuce at 7 ppm; onion,
bulb (Crop Subgroup 3–07A) at 0.8 ppm;
onion, green (Crop Subgroup 3–07B) at
15 ppm; pea and bean, succulent
shelled (Crop Subgroup 6B) at 3 ppm;
peanut at 0.1 ppm; peanut, hay at 40
ppm; sunflower (Crop Subgroup 20B) at
3 ppm; tree nut except hulls (Crop
Group 14–12) at 0.15 ppm; vegetable,
brassica head and stem (Crop Group 5–
16) at 5 ppm; vegetable, cucurbit (Crop
Group 9) at 0.7 ppm; vegetable, fruiting
(Crop Group 8–10) at 1.5 ppm;
vegetable, leaf petiole (Crop Subgroup
22B) at 40 ppm; vegetable, leafy except
head lettuce (Crop Group 4–16) at 60
ppm; vegetable, leaves of root and tuber
(Crop Group 2) at 40 ppm; vegetable,
legume, edible podded (Crop Subgroup
6A) at 4 ppm; vegetable, root (Crop
Subgroup 1A) at 0.6 ppm; and vegetable,
tuberous and corm (Crop Subgroup 1C)
at 0.06 ppm. That document referenced
a summary of the petition prepared by
E.I. Du Pont De Nemours and Company,
the registrant, which is available in the
docket, https://www.regulations.gov.
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Comments were received on the notice
of filing. EPA’s response to these
comments is discussed in Unit IV.C.
Notice of this same petition was
provided again in the Federal Register
of January 26, 2018 (83 FR 3658) (FRL–
9971–46). The only difference between
the two notifications is that the second
notification spelled out the analytical
method, whereas the November 2017
notification used just the abbreviations.
Both documents provided notice for the
same petition and same tolerances. That
document is also available in the
docket, https://www.regulations.gov. One
comment was received on this second
notification, but it did not raise any
issues relevant to this rulemaking.
Based upon review of the data
supporting the petition, EPA is
establishing tolerances at levels lower
than requested, except for the
commodities of alfalfa forage, hay, and
seed, and using commodity terms
consistent with the Agency’s food and
feed commodity vocabulary. The
reasons for these changes are explained
in Unit IV.D.
III. Aggregate Risk Assessment and
Determination of Safety
Section 408(b)(2)(A)(i) of FFDCA
allows EPA to establish a tolerance (the
legal limit for a pesticide chemical
residue in or on a food) only if EPA
determines that the tolerance is ‘‘safe.’’
Section 408(b)(2)(A)(ii) of FFDCA
defines ‘‘safe’’ to mean that ‘‘there is a
reasonable certainty that no harm will
result from aggregate exposure to the
pesticide chemical residue, including
all anticipated dietary exposures and all
other exposures for which there is
reliable information.’’ This includes
exposure through drinking water and in
residential settings, but does not include
occupational exposure. Section
408(b)(2)(C) of FFDCA requires EPA to
give special consideration to exposure
of infants and children to the pesticide
chemical residue in establishing a
tolerance and to ‘‘ensure that there is a
reasonable certainty that no harm will
result to infants and children from
aggregate exposure to the pesticide
chemical residue . . . . ’’
Consistent with FFDCA section
408(b)(2)(D), and the factors specified in
FFDCA section 408(b)(2)(D), EPA has
reviewed the available scientific data
and other relevant information in
support of this action. EPA has
sufficient data to assess the hazards of
and to make a determination on
aggregate exposure for picoxystrobin
including exposure resulting from the
tolerances established by this action.
EPA’s assessment of exposures and risks
associated with picoxystrobin follows.
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A. Toxicological Profile
EPA has evaluated the available
toxicity data and considered its validity,
completeness, and reliability as well as
the relationship of the results of the
studies to human risk. EPA has also
considered available information
concerning the variability of the
sensitivities of major identifiable
subgroups of consumers, including
infants and children.
The most consistently observed
effects of picoxystrobin exposure across
species, genders, and treatment
durations were decreased body-weight,
body-weight gain and food
consumption, and diarrhea. The effects
on body-weight and food consumption
were consistent with the commonly
observed findings for compounds that
disrupt the mitochondria respiration
system and the resulting disruption of
energy production. Similar to some
other strobilurins, picoxystrobin causes
intestinal disturbance as indicated by
increased incidence of diarrhea or
duodenum mucosal thickening. These
intestinal effects appeared to be related
to the irritating action on the mucus
membranes as demonstrated by severe
eye irritation effect seen in the primary
eye irritation study on picoxystrobin.
In the rat, developmental toxicity was
expressed as misaligned 5th sternebrae
at doses causing maternal toxicity (i.e.
diarrhea and decreased body weight
gain, and food consumption). In the
rabbit, developmental toxicity seen at
doses causing maternal toxicity (i.e.
decreased body weight and clinical
signs of toxicity) consisted of long 13th
rib length and incompletely ossified
odontoids and 27 pre-pelvic vertebrae.
In the reproduction study, parental/
systemic toxicity manifested as
decreased body weight and body weight
gain in both the parents and offspring;
no reproductive toxicity was seen.
There was no evidence that
picoxystrobin directly affects the
nervous system; behavioral changes
observed in the acute and subchronic
neurotoxicity studies were attributed to
general malaise. Picoxystrobin has no
effects on the immune system in rats
and mice, and is not mutagenic or
genotoxic. No adverse dermal or
systemic effects were identified in the
rat following dermal exposure at the
limit-dose. In the inhalation toxicity
study, rats showed no portal of entry,
respiratory or systemic toxicity. Chronic
picoxystrobin exposure induced a
treatment-related increase in testicular
interstitial cell benign tumors in male
rats at the high-dose only. No tumors
were seen in female rats or in male and
female mice, and there is no mutagenic
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concern. Based on this information, EPA
has classified picoxystrobin as
‘‘suggestive evidence of carcinogenic
potential’’, for which quantification of
cancer risk based on a non-linear
approach (i.e., the chronic reference
doses (RfD)) is appropriate. Use of the
chronic RfD will adequately account for
all chronic toxicity, including
carcinogenicity, that could result from
exposure to picoxystrobin. Specific
information on the studies received and
the nature of the adverse effects caused
by picoxystrobin as well as the noobserved-adverse-effect-level (NOAEL)
and the lowest-observed-adverse-effectlevel (LOAEL) from the toxicity studies
can be found at https://
www.regulations.gov in document
‘‘Picoxystrobin: Human Health Risk
Assessment for Proposed New Uses on
Root Vegetables, Subgroup 1A;
Tuberous and Corm Vegetables,
Subgroup 1C; Leaves of Root and Tuber
Vegetables, Group 2; Bulb Onion,
Subgroup 3–07A; Green Onion,
Subgroup 3–07B; Leafy Vegetables,
except Head Lettuce, Group 4–16; Head
and Stem Brassica Vegetables, Group 5–
16; Edible Podded Legume Vegetables,
Subgroup 6A; Succulent Shelled Pea
and Bean, Subgroup 6B; Fruiting
Vegetables, Group 8–10; Cucurbit
Vegetables, Group 9; Tree Nuts, Group
14–12; Sunflower, Subgroup 20B;
Cottonseed, Subgroup 20C; Leaf Petiole
Vegetables, Subgroup 22B; Head
Lettuce; Almond; Alfalfa; Peanut; and
Grass, Forage, Fodder, and Hay, Group
17’’ in docket ID number EPA–HQ–
OPP–2017–0429.
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
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degree of risk. Thus, the Agency
estimates risk in terms of the probability
of an occurrence of the adverse effect
expected in a lifetime. For more
information on the general principles
EPA uses in risk characterization and a
complete description of the risk
assessment process, see https://
www2.epa.gov/pesticide-science-andassessing-pesticide-risks/assessing-
39607
human-health-risk-pesticides. A
summary of the toxicological endpoints
for picoxystrobin used for human risk
assessment is shown in Table 1 of this
unit.
TABLE 1—SUMMARY OF TOXICOLOGICAL DOSES AND ENDPOINTS FOR PICOXYSTROBIN FOR USE IN HUMAN HEALTH RISK
ASSESSMENT
Point of departure and
uncertainty/safety factors
Exposure/scenario
RfD, PAD, LOC for risk
assessment
Study and toxicological effects
Acute dietary (Females 13–50 years of age) ...
An acute dietary risk assessment is not required since no endpoint attributable to a single exposure was identified from the relevant studies.
Acute dietary (General population including infants and children).
UFA = 10x ...............................
UFH = 10x
FQPA SF/UFL = 10x
Acute RfD/aPAD = 0.2 mg/kg/
day.
Chronic dietary (All populations) ......................
NOAEL= 4.6 mg/kg/day UFA
= 10x.
UFH = 10x
FQPA SF = 1x
Chronic RfD = 0.046 mg/kg/
day.
cPAD = 0.046 mg/kg/day .......
Cancer (Oral, dermal, inhalation) .....................
‘‘Suggestive Evidence of Carcinogenic Potential’’ based on tumors in one species and one sex:
a treatment-related increase in testicular interstitial cell benign tumors in high dose male rats.
Quantification of cancer risk is based on a non-linear (i.e., RfD) approach.
Acute Neurotoxicity—Rat
LOAEL = 200 mg/kg/day
based on low arousal and
decreased motor activities
in males, decreased rearing
in females, in addition to
decreased bodyweight gain
and food consumption in
both sexes on Day 1.
Chronic Toxicity—Dog
LOAEL = 15.7 mg/kg/day
based on decreased body
weights, body weight gains,
and food consumption in
both sexes.
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). RfD = reference dose. UF = uncertainty factor. UFA = extrapolation from animal to human (interspecies). UFL = use of a LOAEL to extrapolate a NOAEL.
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C. Exposure Assessment
1. Dietary exposure from food and
feed uses. In evaluating dietary
exposure to picoxystrobin, EPA
considered exposure under the
petitioned-for tolerances as well as all
existing picoxystrobin tolerances in 40
CFR 180.669. EPA assessed dietary
exposures from picoxystrobin 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 picoxystrobin. In estimating acute
dietary exposure, EPA used food
consumption information from the
United States Department of Agriculture
(USDA) National Health and Nutrition
Examination Survey, What We Eat in
America, (NHANES/WWEIA). As to
residue levels in food, EPA’s
assumption of this dietary assessment
included tolerance-level residues for all
crops. In addition, default processing
factors and 100% percent crop treated
(PCT) were assumed for all
commodities.
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ii. Chronic exposure. In conducting
the chronic dietary exposure assessment
EPA used the food consumption data
from the USDA 1994–1996 and 1998
CSFII. As to residue levels in food, EPA
used tolerance-level residues for all
crops. In addition, default processing
factors and 100 PCT were assumed for
all commodities.
iii. Cancer. Based on the data
summarized in Unit III.A., EPA has
concluded that a linear (RfD) approach
is appropriate for assessing cancer risk
to picoxystrobin. Cancer risk was
assessed using the same exposure
estimates as discussed in Unit III.C.1.ii.,
chronic exposure.
iv. Anticipated residue and PCT
information. EPA did not use
anticipated residue and/or PCT
information in the dietary assessment
for picoxystrobin. Tolerance-level
residues and/or 100 PCT were assumed
for all food commodities.
2. Dietary exposure from drinking
water. The Agency used screening-level
water exposure models in the dietary
exposure analysis and risk assessment
for picoxystrobin in drinking water.
These simulation models take into
account data on the physical, chemical,
and fate/transport characteristics of
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picoxystrobin. 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 Surface Water
Concentration Calculator (SWCC) and
Pesticide Root Zone Model Ground
Water (PRZM GW), the estimated
drinking water concentrations (EDWCs)
of picoxystrobin for acute exposures are
estimated to be 15.7 parts per billion
(ppb) for surface water and 1.40 ppb for
ground water. Chronic exposures for
non-cancer assessments are estimated to
be 5.53 ppb for surface water and 1.36
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 15.7 ppb was
used to assess the contribution to
drinking water. For chronic dietary risk
assessment, the water concentration of
value 5.53 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,
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indoor pest control, termiticides, and
flea and tick control on pets).
Picoxystrobin is not registered for any
specific use patterns that would result
in residential exposure.
4. Cumulative effects from substances
with a common mechanism of toxicity.
Section 408(b)(2)(D)(v) of FFDCA
requires that, when considering whether
to establish, modify, or revoke a
tolerance, the Agency consider
‘‘available information’’ concerning the
cumulative effects of a particular
pesticide’s residues and ‘‘other
substances that have a common
mechanism of toxicity.’’ EPA has not
found picoxystrobin to share a common
mechanism of toxicity with any other
substances, and picoxystrobin does not
appear to produce a toxic metabolite
produced by other substances. For the
purposes of this tolerance action,
therefore, EPA has assumed that
picoxystrobin does not have a common
mechanism of toxicity with other
substances. For information regarding
EPA’s efforts to determine which
chemicals have a common mechanism
of toxicity and to evaluate the
cumulative effects of such chemicals,
see EPA’s website at https://
www.epa.gov/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
Food Quality Protection Act Safety
Factor (FQPA SF). In applying this
provision, EPA either retains the default
value of 10X, or uses a different
additional safety factor when reliable
data available to EPA support the choice
of a different factor.
2. Prenatal and postnatal sensitivity.
The prenatal and postnatal toxicity
studies include rat and rabbit prenatal
developmental studies in addition to
reproduction and fertility effects studies
in rats. In the rat- and rabbitdevelopmental toxicity studies,
developmental toxicity was expressed
as skeletal variations at doses causing
maternal toxicity (i.e. diarrhea,
decreased body-weight, body-weight
gain, food consumption, and clinical
signs of toxicity). In the reproduction
study, parental/systemic toxicity
manifested as decreased body-weight
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and body-weight gain in both the
parents and offspring. No evidence of
increased susceptibility/sensitivity is
seen in any of these studies.
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 for chronic dietary.
For acute dietary exposures for the
general population, including infants
and children where the acute
neurotoxicity study is used as an
endpoint for risk assessment, EPA is
retaining a 10x FQPA SF. That decision
is based on the following findings:
i. The toxicity database for
picoxystrobin is complete, except for
the lack of a NOAEL in the acute
neurotoxicity test, which is used to
establish a toxicological endpoint for
acute dietary exposure scenarios.
ii. Although there is some effect on
behavior after exposure to
picoxystrobin, EPA has concluded that
picoxystrobin is not a neurotoxic
chemical due to lack of
neuropathological findings; there is no
need for a developmental neurotoxicity
study or additional UFs to account for
neurotoxicity.
iii. There is no evidence that
picoxystrobin 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 dietary food exposure assessments
were performed based on 100 PCT and
tolerance-level residues. EPA made
conservative (protective) assumptions in
the ground and surface water modeling
used to assess exposure to picoxystrobin
in drinking water. These assessments
will not underestimate the exposure and
risks posed by picoxystrobin.
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
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picoxystrobin will occupy 23% 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 picoxystrobin
from food and water will utilize 36% of
the cPAD for children 1–2 years old, the
population group receiving the greatest
exposure. There are no residential uses
for picoxystrobin.
3. Short- and intermediate-term risk.
Short- and intermediate-term aggregate
exposure takes into account residential
exposure plus chronic exposure to food
and water (considered to be a
background exposure level). Because no
short-term or intermediate-term adverse
effect was identified and picoxystrobin
is not registered for any residential uses,
picoxystrobin is not expected to pose a
short- or intermediate-term risk.
4. Aggregate cancer risk for U.S.
population. The Agency considers the
chronic aggregate risk assessment,
making use of the cPAD, to be protective
of any aggregate cancer risk. As chronic
risks are below the Agency’s level of
concern, the Agency concludes there is
no cancer risk of concern from aggregate
exposure to picoxystrobin.
5. Determination of safety. Based on
these risk assessments, EPA concludes
that there is a reasonable certainty that
no harm will result to the general
population, or to infants and children
from aggregate exposure to
picoxystrobin residues.
IV. Other Considerations
A. Analytical Enforcement Methodology
Adequate enforcement methodology
(high-performance liquid
chromatography with tandem mass
spectrometry (HPLC/ESI–MS/MS)) is
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).
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The Codex Alimentarius is a joint
United Nations Food and Agriculture
Organization/World Health
Organization food standards program,
and it is recognized as an international
food safety standards-setting
organization in trade agreements to
which the United States is a party. EPA
may establish a tolerance that is
different from a Codex MRL; however,
FFDCA section 408(b)(4) requires that
EPA explain the reasons for departing
from the Codex level. The Codex has not
established a MRL for picoxystrobin.
daltland on DSKBBV9HB2PROD with RULES
C. Response to Comments
Comments were received in response
to the Notices of Filing of E.I. Du Pont
De Nemours and Company’s petition.
Two comments were filed within the
comment period, one irrelevant and one
expressing confusion about whether this
action duplicated a previous action. The
comment copied an excerpt from a
tolerance rulemaking that was finalized
in 2012; the tolerances requested in this
petition are not the same as those
finalized in 2012. Several other
comments were submitted after the
comment period had closed.
D. Revisions to Petitioned-For
Tolerances
The Agency has revised several of the
commodity definitions to be consistent
with the food and feed commodity
vocabulary the Agency uses to establish
tolerances. The Agency is also
establishing tolerance levels that are
slightly lower than the petitioner
requested because Agency calculated
tolerances (except alfalfa and sorghum)
using proportionality to extrapolate data
which would be reflective of a 1x
maximum annual application rate rather
the exaggerated application rates in the
field trial studies for the following
commodities: Almond hulls at 15 ppm
to almond, hulls at 7.0 ppm; cotton, gin
by-products at 40 ppm to cotton gin
byproducts at 20 ppm; cottonseed (Crop
Subgroup 20C) at 4 ppm to cottonseed
subgroup 20C at 2.0 ppm; head lettuce
at 7 ppm to lettuce, head at 4.0 ppm;
onion, bulb (Crop Subgroup 3–07A) at
0.8 ppm to onion, bulb, subgroup 3–07A
at 0.50 ppm; onion, green (Crop
Subgroup 3–07B) at 15 ppm to onion,
green, subgroup 3–07B at 10 ppm; pea
and bean, succulent shelled (Crop
Subgroup 6B) at 3 ppm to pea and bean,
succulent shelled, subgroup 6B at 0.90
ppm; peanut at 0.1 ppm to 0.05 ppm;
peanut, hay at 40 ppm to 30 ppm;
sunflower (Crop Subgroup 20B) at 3
ppm to sunflower subgroup 20B to 2.0
ppm; tree nut except hulls (Crop Group
14–12) at 0.15 ppm to nut, tree, group
14–12 at 0.08 ppm; vegetable, brassica
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Jkt 244001
head and stem (Crop Group 5–16) at 5
ppm to vegetable, brassica, head and
stem, group 5–16 at 2.0 ppm; vegetable,
cucurbit (Crop Group 9) at 0.7 ppm to
vegetable, cucurbit, group 9 at 0.30
ppm; vegetable, fruiting (Crop Group 8–
10) at 1.5 ppm to vegetable, fruiting,
group 8–10 at 0.70 ppm; vegetable, leaf
petiole (Crop Subgroup 22B) at 40 ppm
to leaf petiole vegetable subgroup 22B at
20 ppm; vegetable, leafy except head
lettuce (Crop Group 4–16) at 60 ppm to
vegetable, leafy, group 4–16, except
lettuce, head at 30 ppm; vegetable,
leaves of root and tuber (Crop Group 2)
at 40 ppm to vegetable, leaves of root
and tuber, group 2 at 30 ppm; vegetable,
legume, edible podded (Crop Subgroup
6A) at 4 ppm to vegetable, legume,
edible podded, subgroup 6A at 2.0 ppm;
vegetable, root (Crop Subgroup 1A) at
0.6 ppm to vegetable, root, subgroup 1A
at 0.50 ppm; and vegetable, tuberous
and corm (Crop Subgroup 1C) at 0.06
ppm to vegetable, tuberous and corm,
subgroup 1C at 0.03 ppm.
For alfalfa, forage, hay, and seed, the
tolerances have been modified to
represent the appropriate number of
significant figures; however, the
numerical value is no different than
requested by the petition.
The petition requested ‘‘grass, forage
(Grown for Seed)’’ at 40 ppm and ‘‘grass,
hay (Grown for Seed)’’ at 80 ppm.
Because ‘‘grass grown for seed’’ is
ambiguous, the Agency is establishing
individual tolerances for the hay and
forage forms of specific grasses for
which residue data were submitted and
that are grown for seed purposes:
Bluegrass, forage at 30 ppm; bluegrass,
hay at 60 ppm, bromegrass, forage at 30
ppm; bromegrass, hay at 60 ppm; fescue,
forage at 30 ppm; fescue, hay at 60 ppm;
orchardgrass, forage at 30 ppm;
orchardgrass, hay at 60 ppm; ryegrass,
forage at 30 ppm; ryegrass, hay at 60
ppm; switchgrass, forage at 30 ppm; and
switchgrass, hay at 60 ppm.
EPA is also establishing tolerances for
beet, sugar, dried pulp at 1.5 ppm and
potato, wet peel at 0.10 ppm, pursuant
to 40 CFR 180.40(f)(1)(i)(A). These
tolerances are necessary to cover
concentrated residues in processed
commodities of raw agricultural
commodities contained in subgroups 1A
and 1C, respectively.
V. Conclusion
Therefore, tolerances are established
for residues of picoxystrobin, methyl
(aE)-a-(methoxymethylene)-2-[[[6(trifluoromethyl)-2pyridinyl]oxy]methyl]benzeneacetate, in
or on alfalfa, forage at 4.0 ppm; alfalfa,
hay at 5.0 ppm; alfalfa, seed at 9.0 ppm;
almond, hulls at 7.0 ppm; beet, sugar,
PO 00000
Frm 00029
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39609
dried pulp at 1.5 ppm; bluegrass, forage
at 30 ppm; bluegrass, hay at 60 ppm;
bromegrass, forage at 30 ppm;
bromegrass, hay at 60 ppm; cotton, gin
byproducts at 20 ppm; cottonseed
subgroup 20C at 2.0 ppm; fescue, forage
at 30 ppm; fescue, hay at 60 ppm; leaf
petiole vegetable subgroup 22B at 20
ppm; lettuce, head at 4.0 ppm; nut, tree,
group 14–12 at 0.08 ppm; onion, bulb,
subgroup 3–07A at 0.50 ppm; onion,
green, subgroup 3–07B at 10 ppm;
orchardgrass, forage at 30 ppm;
orchardgrass, hay at 60 ppm; pea and
bean, succulent shelled, subgroup 6B at
0.90 ppm; peanut at 0.05 ppm; peanut,
hay at 30 ppm; potato, wet peel at 0.10
ppm; ryegrass, forage at 30 ppm;
ryegrass, hay at 60 ppm; sunflower
subgroup 20B to 2.0 ppm; switchgrass,
forage at 30 ppm; switchgrass, hay at 60
ppm; vegetable, brassica, head and stem,
group 5–16 at 2.0 ppm; vegetable,
cucurbit, group 9 at 0.30 ppm;
vegetable, fruiting, group 8–10 at 0.70
ppm; vegetable, leafy, group 4–16,
except lettuce, head at 30 ppm;
vegetable, leaves of root and tuber,
group 2 at 30 ppm; vegetable, legume,
edible podded, subgroup 6A at 2.0 ppm;
vegetable, root, subgroup 1A at 0.50
ppm; and vegetable, tuberous and corm,
subgroup 1C at 0.03 ppm.
VI. Statutory and Executive Order
Reviews
This action establishes tolerances
under FFDCA section 408(d) in
response to a petition submitted to the
Agency. The Office of Management and
Budget (OMB) has exempted these types
of actions from review under Executive
Order 12866, entitled ‘‘Regulatory
Planning and Review’’ (58 FR 51735,
October 4, 1993). Because this action
has been exempted from review under
Executive Order 12866, this action is
not subject to Executive Order 13211,
entitled ‘‘Actions Concerning
Regulations That Significantly Affect
Energy Supply, Distribution, or Use’’ (66
FR 28355, May 22, 2001) or Executive
Order 13045, entitled ‘‘Protection of
Children from Environmental Health
Risks and Safety Risks’’ (62 FR 19885,
April 23, 1997), nor is it considered a
regulatory action under Executive Order
13771, entitled ‘‘Reducing Regulations
and Controlling Regulatory Costs’’ (82
FR 9339, February 3, 2017). This action
does not contain any information
collections subject to OMB approval
under the Paperwork Reduction Act
(PRA) (44 U.S.C. 3501 et seq.), nor does
it require any special considerations
under Executive Order 12898, entitled
‘‘Federal Actions to Address
Environmental Justice in Minority
Populations and Low-Income
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Populations’’ (59 FR 7629, February 16,
1994).
Since tolerances and exemptions that
are established on the basis of a petition
under FFDCA section 408(d), such as
the tolerances in this final rule, do not
require the issuance of a proposed rule,
the requirements of the Regulatory
Flexibility Act (RFA) (5 U.S.C. 601 et
seq.), do not apply.
This action directly regulates growers,
food processors, food handlers, and food
retailers, not States or tribes, nor does
this action alter the relationships or
distribution of power and
responsibilities established by Congress
in the preemption provisions of FFDCA
section 408(n)(4). As such, the Agency
has determined that this action will not
have a substantial direct effect on States
or tribal governments, on the
relationship between the national
government and the States or tribal
governments, or on the distribution of
power and responsibilities among the
various levels of government or between
the Federal Government and Indian
tribes. Thus, the Agency has determined
that Executive Order 13132, entitled
‘‘Federalism’’ (64 FR 43255, August 10,
1999) and Executive Order 13175,
entitled ‘‘Consultation and Coordination
with Indian Tribal Governments’’ (65 FR
67249, November 9, 2000) do not apply
to this action. In addition, this action
does not impose any enforceable duty or
contain any unfunded mandate as
described under Title II of the Unfunded
Mandates Reform Act (UMRA) (2 U.S.C.
1501 et seq.).
This action does not involve any
technical standards that would require
Agency consideration of voluntary
consensus standards pursuant to section
12(d) of the National Technology
Transfer and Advancement Act
(NTTAA) (15 U.S.C. 272 note).
VII. Congressional Review Act
daltland on DSKBBV9HB2PROD with RULES
Pursuant to the Congressional Review
Act (5 U.S.C. 801 et seq.), EPA will
submit a report containing this rule and
other required information to the U.S.
Senate, the U.S. House of
Representatives, and the Comptroller
General of the United States prior to
publication of the rule in the Federal
Register. This action is not a ‘‘major
rule’’ as defined by 5 U.S.C. 804(2).
List of Subjects in 40 CFR Part 180
Environmental protection,
Administrative practice and procedure,
Agricultural commodities, Pesticides
and pests, Reporting and recordkeeping
requirements.
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16:07 Aug 09, 2018
Jkt 244001
Dated: July 25, 2018.
Michael Goodis,
Director, Registration Division, Office of
Pesticide Programs.
Parts per
million
Commodity
Lettuce, head ..............................
*
*
*
*
Nut, tree, group 14–12 ...............
Onion, bulb, subgroup 3–07A ....
Onion, green, subgroup 3–07B ..
Orchardgrass, forage ..................
Orchardgrass, hay ......................
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 § 180.669, add alphabetically the
following commodities: Alfalfa, forage;
Alfalfa, hay; Alfalfa, seed; Almond,
hulls; Beet, sugar, dried pulp; Bluegrass,
forage; Bluegrass, hay; Bromegrass,
forage; Bromegrass, hay; Cotton, gin
byproducts; Cottonseed subgroup 20C;
Fescue, forage; Fescue, hay; Leaf petiole
vegetable subgroup 22B; Lettuce, head;
Nut, tree, group 14–12; Onion, bulb,
subgroup 3–07A; Onion, green,
subgroup 3–07B; Orchardgrass, forage;
Orchardgrass, hay; Pea and bean,
succulent shelled, subgroup 6B; Peanut;
Peanut, hay; Potato, wet peel; Ryegrass,
forage; Ryegrass, hay; Sunflower
subgroup 20B; Switchgrass, forage;
Switchgrass, hay; Vegetable, brassica,
head and stem, group 5–16; Vegetable,
cucurbit, group 9; Vegetable, fruiting,
group 8–10; Vegetable, leafy, group 4–
16, except lettuce, head; Vegetable,
leaves of root and tuber, group 2;
Vegetable, legume, edible podded,
subgroup 6A; Vegetable, root, subgroup
1A; and Vegetable, tuberous and corm,
subgroup 1C to the table in paragraph
(a) to read as follows:
■
4.0
*
0.08
0.50
10
30
60
*
*
*
*
Pea and bean, succulent
shelled, subgroup 6B ..............
Peanut ........................................
Peanut, hay ................................
Potato, wet peel ..........................
*
*
*
*
*
Ryegrass, forage ........................
Ryegrass, hay .............................
*
*
*
*
*
Sunflower subgroup 20B ............
Switchgrass, forage ....................
Switchgrass, hay ........................
*
*
*
*
*
Vegetable, brassica, head and
stem, group 5–16 ....................
Vegetable, cucurbit, group 9 ......
*
*
*
*
*
Vegetable, fruiting, group 8–10 ..
Vegetable, leafy, group 4–16,
except lettuce, head ................
Vegetable, leaves of root and
tuber, group 2 .........................
Vegetable, legume, edible podded, subgroup 6A ...................
Vegetable, root, subgroup 1A ....
Vegetable, tuberous and corm,
subgroup 1C ...........................
*
§ 180.669 Picoxystrobin; tolerances for
residues.
*
(a) * * *
0.90
0.05
30
0.10
*
*
*
*
*
*
30
60
2.0
30
60
2.0
0.30
*
0.70
30
30
2.0
0.50
0.03
*
*
[FR Doc. 2018–17192 Filed 8–9–18; 8:45 am]
Parts per
million
Commodity
Alfalfa, forage .............................
Alfalfa, hay ..................................
Alfalfa, seed ................................
Almond, hulls ..............................
4.0
5.0
9.0
7.0
*
*
*
*
Beet, sugar, dried pulp ...............
Bluegrass, forage .......................
Bluegrass, hay ............................
Bromegrass, forage ....................
Bromegrass, hay ........................
*
*
*
*
*
Cotton, gin byproducts ...............
Cottonseed subgroup 20C .........
*
*
*
*
*
Fescue, forage ............................
Fescue, hay ................................
*
1.5
30
60
30
60
BILLING CODE 6560–50–P
FEDERAL COMMUNICATIONS
COMMISSION
47 CFR Part 11
[PS Docket Nos. 15–94, 15–91; FCC 18–
94]
Emergency Alert System; Wireless
Emergency Alerts
Federal Communications
Commission.
20 ACTION: Final rule.
AGENCY:
*
*
*
*
Leaf petiole vegetable subgroup
22B ..........................................
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2.0
In this document, the Federal
Communications Commission (FCC or
30
60 Commission) adopts changes to its rules
governing the Emergency Alert System
(EAS) to facilitate ‘‘Live Code Tests’’ of
*
the EAS; permit use of the EAS
20 Attention Signal and EAS Header Code
SUMMARY:
E:\FR\FM\10AUR1.SGM
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Agencies
[Federal Register Volume 83, Number 155 (Friday, August 10, 2018)]
[Rules and Regulations]
[Pages 39605-39610]
From the Federal Register Online via the Government Publishing Office [www.gpo.gov]
[FR Doc No: 2018-17192]
-----------------------------------------------------------------------
ENVIRONMENTAL PROTECTION AGENCY
40 CFR Part 180
[EPA-HQ-OPP-2017-0429; FRL-9980-47]
Picoxystrobin; Pesticide Tolerances
AGENCY: Environmental Protection Agency (EPA).
ACTION: Final rule.
-----------------------------------------------------------------------
SUMMARY: This regulation establishes tolerances for residues of
picoxystrobin in or on multiple commodities that are identified and
discussed later in this document. E.I. DuPont De Nemours and Company
requested these tolerances under the Federal Food, Drug, and Cosmetic
Act (FFDCA).
DATES: This regulation is effective August 10, 2018. Objections and
requests for hearings must be received on or before October 9, 2018,
and must be filed in accordance with the instructions provided in 40
CFR part 178 (see also Unit I.C. of the SUPPLEMENTARY INFORMATION).
ADDRESSES: The docket for this action, identified by docket
identification (ID) number EPA-HQ-OPP-2017-0429, is available at https://www.regulations.gov or at the Office of Pesticide Programs Regulatory
Public Docket (OPP Docket) in the Environmental Protection Agency
Docket Center (EPA/DC), West William Jefferson Clinton Bldg., Rm. 3334,
1301 Constitution Ave. NW, Washington, DC 20460-0001. The Public
Reading Room is open from 8:30 a.m. to 4:30 p.m., Monday through
Friday, excluding legal holidays. The telephone number for the Public
Reading Room is (202) 566-1744, and the telephone number for the OPP
Docket is (703) 305-5805. Please review the visitor instructions and
additional information about the docket available at https://www.epa.gov/dockets.
FOR FURTHER INFORMATION CONTACT: Michael L. Goodis, P.E., Registration
Division (7505P), Office of Pesticide Programs, Environmental
Protection Agency, 1200 Pennsylvania Ave. NW, Washington, DC 20460-
0001; main telephone number: (703) 305-7090; email address:
[email protected].
SUPPLEMENTARY INFORMATION:
I. General Information
A. Does this action apply to me?
You may be potentially affected by this action if you are an
agricultural producer, food manufacturer, or pesticide manufacturer.
The following list of North American Industrial Classification System
(NAICS) codes is not intended to be exhaustive, but rather provides a
guide to help readers determine whether this document applies to them.
Potentially affected entities may include:
Crop production (NAICS code 111).
Animal production (NAICS code 112).
Food manufacturing (NAICS code 311).
Pesticide manufacturing (NAICS code 32532).
B. How can I get electronic access to other related information?
You may access a frequently updated electronic version of EPA's
tolerance regulations at 40 CFR part 180 through the Government
Printing Office's e-CFR site at https://www.ecfr.gov/cgi-bin/text-idx?&c=ecfr&tpl=/ecfrbrowse/Title40/40tab_02.tpl. To access the OCSPP
test guidelines referenced in this document electronically, please go
to https://www.epa.gov/ocspp and select ``Test Methods and Guidelines.''
C. How can I file an objection or hearing request?
Under FFDCA section 408(g), 21 U.S.C. 346a, any person may file an
objection to any aspect of this regulation and may also request a
hearing on those objections. You must file your objection or request a
hearing on this regulation in accordance with the instructions provided
in 40 CFR part 178. To ensure proper receipt by EPA, you must identify
docket ID number EPA-HQ-OPP-2017-0429 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
October 9, 2018. Addresses for mail and hand delivery of objections and
hearing requests are provided in 40 CFR 178.25(b).
In addition to filing an objection or hearing request with the
Hearing Clerk as described in 40 CFR part 178, please submit a copy of
the filing (excluding any Confidential Business Information (CBI)) for
inclusion in the public docket. Information not marked confidential
pursuant to 40 CFR part 2 may be disclosed publicly by EPA without
prior notice. Submit the non-CBI copy of your objection or hearing
request, identified by docket ID number EPA-HQ-OPP-2017-0429, by one of
the following methods:
Federal eRulemaking Portal: https://www.regulations.gov.
Follow the online instructions for submitting comments. Do not submit
electronically any information you consider to be CBI or other
information whose disclosure is restricted by statute.
Mail: OPP Docket, Environmental Protection Agency Docket
Center (EPA/DC), (28221T), 1200 Pennsylvania Ave. NW, Washington, DC
20460-0001.
Hand Delivery: To make special arrangements for hand
delivery or delivery of boxed information, please follow the
instructions at https://www.epa.gov/dockets/contacts.html.
Additional instructions on commenting or visiting the docket, along
with more information about dockets generally, is available at https://www.epa.gov/dockets.
II. Summary of Petitioned-For Tolerance
In the Federal Register of November 27, 2017 (82 FR 56017) (FRL-
9968-55), 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
7F8557) by E.I. Du Pont De Nemours and Company, Chestnut Run Plaza, 974
Centre Road, Wilmington, DE 19805. The petition requested 40 CFR
180.669 be amended by establishing tolerances for residues of the
fungicide picoxystrobin, methyl ([alpha]E)-[alpha]-(methoxymethylene)-
2-[[[6-(trifluoromethyl)-2-pyridinyl]oxy]methyl]benzeneacetate, in or
on alfalfa, forage at 4 parts per million (ppm); alfalfa, hay at 5 ppm;
alfalfa, seed at 9 ppm; almond hulls at 15 ppm; cotton, gin by-products
at 40 ppm; cottonseed (Crop Subgroup 20C) at 4 ppm; grass, forage
(Grown for Seed) at 40 ppm; grass, hay (Grown for Seed) at 80 ppm; head
lettuce at 7 ppm; onion, bulb (Crop Subgroup 3-07A) at 0.8 ppm; onion,
green (Crop Subgroup 3-07B) at 15 ppm; pea and bean, succulent shelled
(Crop Subgroup 6B) at 3 ppm; peanut at 0.1 ppm; peanut, hay at 40 ppm;
sunflower (Crop Subgroup 20B) at 3 ppm; tree nut except hulls (Crop
Group 14-12) at 0.15 ppm; vegetable, brassica head and stem (Crop Group
5-16) at 5 ppm; vegetable, cucurbit (Crop Group 9) at 0.7 ppm;
vegetable, fruiting (Crop Group 8-10) at 1.5 ppm; vegetable, leaf
petiole (Crop Subgroup 22B) at 40 ppm; vegetable, leafy except head
lettuce (Crop Group 4-16) at 60 ppm; vegetable, leaves of root and
tuber (Crop Group 2) at 40 ppm; vegetable, legume, edible podded (Crop
Subgroup 6A) at 4 ppm; vegetable, root (Crop Subgroup 1A) at 0.6 ppm;
and vegetable, tuberous and corm (Crop Subgroup 1C) at 0.06 ppm. That
document referenced a summary of the petition prepared by E.I. Du Pont
De Nemours and Company, the registrant, which is available in the
docket, https://www.regulations.gov.
[[Page 39606]]
Comments were received on the notice of filing. EPA's response to these
comments is discussed in Unit IV.C.
Notice of this same petition was provided again in the Federal
Register of January 26, 2018 (83 FR 3658) (FRL-9971-46). The only
difference between the two notifications is that the second
notification spelled out the analytical method, whereas the November
2017 notification used just the abbreviations. Both documents provided
notice for the same petition and same tolerances. That document is also
available in the docket, https://www.regulations.gov. One comment was
received on this second notification, but it did not raise any issues
relevant to this rulemaking.
Based upon review of the data supporting the petition, EPA is
establishing tolerances at levels lower than requested, except for the
commodities of alfalfa forage, hay, and seed, and using commodity terms
consistent with the Agency's food and feed commodity vocabulary. The
reasons for these changes are explained in Unit IV.D.
III. Aggregate Risk Assessment and Determination of Safety
Section 408(b)(2)(A)(i) of FFDCA allows EPA to establish a
tolerance (the legal limit for a pesticide chemical residue in or on a
food) only if EPA determines that the tolerance is ``safe.'' Section
408(b)(2)(A)(ii) of FFDCA defines ``safe'' to mean that ``there is a
reasonable certainty that no harm will result from aggregate exposure
to the pesticide chemical residue, including all anticipated dietary
exposures and all other exposures for which there is reliable
information.'' This includes exposure through drinking water and in
residential settings, but does not include occupational exposure.
Section 408(b)(2)(C) of FFDCA requires EPA to give special
consideration to exposure of infants and children to the pesticide
chemical residue in establishing a tolerance and to ``ensure that there
is a reasonable certainty that no harm will result to infants and
children from aggregate exposure to the pesticide chemical residue . .
. . ''
Consistent with FFDCA section 408(b)(2)(D), and the factors
specified in FFDCA section 408(b)(2)(D), EPA has reviewed the available
scientific data and other relevant information in support of this
action. EPA has sufficient data to assess the hazards of and to make a
determination on aggregate exposure for picoxystrobin including
exposure resulting from the tolerances established by this action.
EPA's assessment of exposures and risks associated with picoxystrobin
follows.
A. Toxicological Profile
EPA has evaluated the available toxicity data and considered its
validity, completeness, and reliability as well as the relationship of
the results of the studies to human risk. EPA has also considered
available information concerning the variability of the sensitivities
of major identifiable subgroups of consumers, including infants and
children.
The most consistently observed effects of picoxystrobin exposure
across species, genders, and treatment durations were decreased body-
weight, body-weight gain and food consumption, and diarrhea. The
effects on body-weight and food consumption were consistent with the
commonly observed findings for compounds that disrupt the mitochondria
respiration system and the resulting disruption of energy production.
Similar to some other strobilurins, picoxystrobin causes intestinal
disturbance as indicated by increased incidence of diarrhea or duodenum
mucosal thickening. These intestinal effects appeared to be related to
the irritating action on the mucus membranes as demonstrated by severe
eye irritation effect seen in the primary eye irritation study on
picoxystrobin.
In the rat, developmental toxicity was expressed as misaligned 5th
sternebrae at doses causing maternal toxicity (i.e. diarrhea and
decreased body weight gain, and food consumption). In the rabbit,
developmental toxicity seen at doses causing maternal toxicity (i.e.
decreased body weight and clinical signs of toxicity) consisted of long
13th rib length and incompletely ossified odontoids and 27 pre-pelvic
vertebrae. In the reproduction study, parental/systemic toxicity
manifested as decreased body weight and body weight gain in both the
parents and offspring; no reproductive toxicity was seen.
There was no evidence that picoxystrobin directly affects the
nervous system; behavioral changes observed in the acute and subchronic
neurotoxicity studies were attributed to general malaise. Picoxystrobin
has no effects on the immune system in rats and mice, and is not
mutagenic or genotoxic. No adverse dermal or systemic effects were
identified in the rat following dermal exposure at the limit-dose. In
the inhalation toxicity study, rats showed no portal of entry,
respiratory or systemic toxicity. Chronic picoxystrobin exposure
induced a treatment-related increase in testicular interstitial cell
benign tumors in male rats at the high-dose only. No tumors were seen
in female rats or in male and female mice, and there is no mutagenic
concern. Based on this information, EPA has classified picoxystrobin as
``suggestive evidence of carcinogenic potential'', for which
quantification of cancer risk based on a non-linear approach (i.e., the
chronic reference doses (RfD)) is appropriate. Use of the chronic RfD
will adequately account for all chronic toxicity, including
carcinogenicity, that could result from exposure to picoxystrobin.
Specific information on the studies received and the nature of the
adverse effects caused by picoxystrobin as well as the no-observed-
adverse-effect-level (NOAEL) and the lowest-observed-adverse-effect-
level (LOAEL) from the toxicity studies can be found at https://www.regulations.gov in document ``Picoxystrobin: Human Health Risk
Assessment for Proposed New Uses on Root Vegetables, Subgroup 1A;
Tuberous and Corm Vegetables, Subgroup 1C; Leaves of Root and Tuber
Vegetables, Group 2; Bulb Onion, Subgroup 3-07A; Green Onion, Subgroup
3-07B; Leafy Vegetables, except Head Lettuce, Group 4-16; Head and Stem
Brassica Vegetables, Group 5-16; Edible Podded Legume Vegetables,
Subgroup 6A; Succulent Shelled Pea and Bean, Subgroup 6B; Fruiting
Vegetables, Group 8-10; Cucurbit Vegetables, Group 9; Tree Nuts, Group
14-12; Sunflower, Subgroup 20B; Cottonseed, Subgroup 20C; Leaf Petiole
Vegetables, Subgroup 22B; Head Lettuce; Almond; Alfalfa; Peanut; and
Grass, Forage, Fodder, and Hay, Group 17'' in docket ID number EPA-HQ-
OPP-2017-0429.
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
[[Page 39607]]
degree of risk. Thus, the Agency estimates risk in terms of the
probability of an occurrence of the adverse effect expected in a
lifetime. For more information on the general principles EPA uses in
risk characterization and a complete description of the risk assessment
process, see https://www2.epa.gov/pesticide-science-and-assessing-pesticide-risks/assessing-human-health-risk-pesticides. A summary of
the toxicological endpoints for picoxystrobin used for human risk
assessment is shown in Table 1 of this unit.
Table 1--Summary of Toxicological Doses and Endpoints for Picoxystrobin for Use in Human Health Risk Assessment
----------------------------------------------------------------------------------------------------------------
Point of departure and
Exposure/scenario uncertainty/safety RfD, PAD, LOC for risk Study and toxicological
factors assessment effects
----------------------------------------------------------------------------------------------------------------
Acute dietary (Females 13-50 years of An acute dietary risk assessment is not required since no endpoint
age). attributable to a single exposure was identified from the relevant
studies.
--------------------------------------------------------------------------
Acute dietary (General population UFA = 10x.............. Acute RfD/aPAD = 0.2 mg/ Acute Neurotoxicity--
including infants and children). UFH = 10x.............. kg/day. Rat
FQPA SF/UFL = 10x...... LOAEL = 200 mg/kg/day
based on low arousal
and decreased motor
activities in males,
decreased rearing in
females, in addition
to decreased
bodyweight gain and
food consumption in
both sexes on Day 1.
Chronic dietary (All populations).... NOAEL= 4.6 mg/kg/day Chronic RfD = 0.046 mg/ Chronic Toxicity--Dog
UFA = 10x. kg/day. LOAEL = 15.7 mg/kg/day
UFH = 10x.............. cPAD = 0.046 mg/kg/day. based on decreased
FQPA SF = 1x........... body weights, body
weight gains, and food
consumption in both
sexes.
--------------------------------------------------------------------------
Cancer (Oral, dermal, inhalation).... ``Suggestive Evidence of Carcinogenic Potential'' based on tumors in one
species and one sex: a treatment-related increase in testicular
interstitial cell benign tumors in high dose male rats. Quantification
of cancer risk is based on a non-linear (i.e., RfD) approach.
----------------------------------------------------------------------------------------------------------------
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). RfD = reference dose. UF = uncertainty factor.
UFA = extrapolation from animal to human (interspecies). UFL = use of a LOAEL to extrapolate a NOAEL.
C. Exposure Assessment
1. Dietary exposure from food and feed uses. In evaluating dietary
exposure to picoxystrobin, EPA considered exposure under the
petitioned-for tolerances as well as all existing picoxystrobin
tolerances in 40 CFR 180.669. EPA assessed dietary exposures from
picoxystrobin 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 picoxystrobin. In estimating acute dietary exposure, EPA used food
consumption information from the United States Department of
Agriculture (USDA) National Health and Nutrition Examination Survey,
What We Eat in America, (NHANES/WWEIA). As to residue levels in food,
EPA's assumption of this dietary assessment included tolerance-level
residues for all crops. In addition, default processing factors and
100% percent crop treated (PCT) were assumed for all commodities.
ii. Chronic exposure. In conducting the chronic dietary exposure
assessment EPA used the food consumption data from the USDA 1994-1996
and 1998 CSFII. As to residue levels in food, EPA used tolerance-level
residues for all crops. In addition, default processing factors and 100
PCT were assumed for all commodities.
iii. Cancer. Based on the data summarized in Unit III.A., EPA has
concluded that a linear (RfD) approach is appropriate for assessing
cancer risk to picoxystrobin. Cancer risk was assessed using the same
exposure estimates as discussed in Unit III.C.1.ii., chronic exposure.
iv. Anticipated residue and PCT information. EPA did not use
anticipated residue and/or PCT information in the dietary assessment
for picoxystrobin. Tolerance-level residues and/or 100 PCT were assumed
for all food commodities.
2. Dietary exposure from drinking water. The Agency used screening-
level water exposure models in the dietary exposure analysis and risk
assessment for picoxystrobin in drinking water. These simulation models
take into account data on the physical, chemical, and fate/transport
characteristics of picoxystrobin. 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 Surface Water Concentration Calculator (SWCC) and
Pesticide Root Zone Model Ground Water (PRZM GW), the estimated
drinking water concentrations (EDWCs) of picoxystrobin for acute
exposures are estimated to be 15.7 parts per billion (ppb) for surface
water and 1.40 ppb for ground water. Chronic exposures for non-cancer
assessments are estimated to be 5.53 ppb for surface water and 1.36 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 15.7 ppb was used to
assess the contribution to drinking water. For chronic dietary risk
assessment, the water concentration of value 5.53 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,
[[Page 39608]]
indoor pest control, termiticides, and flea and tick control on pets).
Picoxystrobin is not registered for any specific use patterns that
would result in residential exposure.
4. Cumulative effects from substances with a common mechanism of
toxicity. Section 408(b)(2)(D)(v) of FFDCA requires that, when
considering whether to establish, modify, or revoke a tolerance, the
Agency consider ``available information'' concerning the cumulative
effects of a particular pesticide's residues and ``other substances
that have a common mechanism of toxicity.'' EPA has not found
picoxystrobin to share a common mechanism of toxicity with any other
substances, and picoxystrobin does not appear to produce a toxic
metabolite produced by other substances. For the purposes of this
tolerance action, therefore, EPA has assumed that picoxystrobin does
not have a common mechanism of toxicity with other substances. For
information regarding EPA's efforts to determine which chemicals have a
common mechanism of toxicity and to evaluate the cumulative effects of
such chemicals, see EPA's website at https://www.epa.gov/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 Food Quality
Protection Act Safety Factor (FQPA SF). In applying this provision, EPA
either retains the default value of 10X, or uses a different additional
safety factor when reliable data available to EPA support the choice of
a different factor.
2. Prenatal and postnatal sensitivity. The prenatal and postnatal
toxicity studies include rat and rabbit prenatal developmental studies
in addition to reproduction and fertility effects studies in rats. In
the rat- and rabbit-developmental toxicity studies, developmental
toxicity was expressed as skeletal variations at doses causing maternal
toxicity (i.e. diarrhea, decreased body-weight, body-weight gain, food
consumption, and clinical signs of toxicity). In the reproduction
study, parental/systemic toxicity manifested as decreased body-weight
and body-weight gain in both the parents and offspring. No evidence of
increased susceptibility/sensitivity is seen in any of these studies.
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 for chronic dietary. For acute dietary
exposures for the general population, including infants and children
where the acute neurotoxicity study is used as an endpoint for risk
assessment, EPA is retaining a 10x FQPA SF. That decision is based on
the following findings:
i. The toxicity database for picoxystrobin is complete, except for
the lack of a NOAEL in the acute neurotoxicity test, which is used to
establish a toxicological endpoint for acute dietary exposure
scenarios.
ii. Although there is some effect on behavior after exposure to
picoxystrobin, EPA has concluded that picoxystrobin is not a neurotoxic
chemical due to lack of neuropathological findings; there is no need
for a developmental neurotoxicity study or additional UFs to account
for neurotoxicity.
iii. There is no evidence that picoxystrobin 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 dietary food exposure assessments were performed based
on 100 PCT and tolerance-level residues. EPA made conservative
(protective) assumptions in the ground and surface water modeling used
to assess exposure to picoxystrobin in drinking water. These
assessments will not underestimate the exposure and risks posed by
picoxystrobin.
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 picoxystrobin will occupy 23% 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
picoxystrobin from food and water will utilize 36% of the cPAD for
children 1-2 years old, the population group receiving the greatest
exposure. There are no residential uses for picoxystrobin.
3. Short- and intermediate-term risk. Short- and intermediate-term
aggregate exposure takes into account residential exposure plus chronic
exposure to food and water (considered to be a background exposure
level). Because no short-term or intermediate-term adverse effect was
identified and picoxystrobin is not registered for any residential
uses, picoxystrobin is not expected to pose a short- or intermediate-
term risk.
4. Aggregate cancer risk for U.S. population. The Agency considers
the chronic aggregate risk assessment, making use of the cPAD, to be
protective of any aggregate cancer risk. As chronic risks are below the
Agency's level of concern, the Agency concludes there is no cancer risk
of concern from aggregate exposure to picoxystrobin.
5. Determination of safety. Based on these risk assessments, EPA
concludes that there is a reasonable certainty that no harm will result
to the general population, or to infants and children from aggregate
exposure to picoxystrobin residues.
IV. Other Considerations
A. Analytical Enforcement Methodology
Adequate enforcement methodology (high-performance liquid
chromatography with tandem mass spectrometry (HPLC/ESI-MS/MS)) is
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:
[email protected].
B. International Residue Limits
In making its tolerance decisions, EPA seeks to harmonize U.S.
tolerances with international standards whenever possible, consistent
with U.S. food safety standards and agricultural practices. EPA
considers the international maximum residue limits (MRLs) established
by the Codex Alimentarius Commission (Codex), as required by FFDCA
section 408(b)(4).
[[Page 39609]]
The Codex Alimentarius is a joint United Nations Food and Agriculture
Organization/World Health Organization food standards program, and it
is recognized as an international food safety standards-setting
organization in trade agreements to which the United States is a party.
EPA may establish a tolerance that is different from a Codex MRL;
however, FFDCA section 408(b)(4) requires that EPA explain the reasons
for departing from the Codex level. The Codex has not established a MRL
for picoxystrobin.
C. Response to Comments
Comments were received in response to the Notices of Filing of E.I.
Du Pont De Nemours and Company's petition. Two comments were filed
within the comment period, one irrelevant and one expressing confusion
about whether this action duplicated a previous action. The comment
copied an excerpt from a tolerance rulemaking that was finalized in
2012; the tolerances requested in this petition are not the same as
those finalized in 2012. Several other comments were submitted after
the comment period had closed.
D. Revisions to Petitioned-For Tolerances
The Agency has revised several of the commodity definitions to be
consistent with the food and feed commodity vocabulary the Agency uses
to establish tolerances. The Agency is also establishing tolerance
levels that are slightly lower than the petitioner requested because
Agency calculated tolerances (except alfalfa and sorghum) using
proportionality to extrapolate data which would be reflective of a 1x
maximum annual application rate rather the exaggerated application
rates in the field trial studies for the following commodities: Almond
hulls at 15 ppm to almond, hulls at 7.0 ppm; cotton, gin by-products at
40 ppm to cotton gin byproducts at 20 ppm; cottonseed (Crop Subgroup
20C) at 4 ppm to cottonseed subgroup 20C at 2.0 ppm; head lettuce at 7
ppm to lettuce, head at 4.0 ppm; onion, bulb (Crop Subgroup 3-07A) at
0.8 ppm to onion, bulb, subgroup 3-07A at 0.50 ppm; onion, green (Crop
Subgroup 3-07B) at 15 ppm to onion, green, subgroup 3-07B at 10 ppm;
pea and bean, succulent shelled (Crop Subgroup 6B) at 3 ppm to pea and
bean, succulent shelled, subgroup 6B at 0.90 ppm; peanut at 0.1 ppm to
0.05 ppm; peanut, hay at 40 ppm to 30 ppm; sunflower (Crop Subgroup
20B) at 3 ppm to sunflower subgroup 20B to 2.0 ppm; tree nut except
hulls (Crop Group 14-12) at 0.15 ppm to nut, tree, group 14-12 at 0.08
ppm; vegetable, brassica head and stem (Crop Group 5-16) at 5 ppm to
vegetable, brassica, head and stem, group 5-16 at 2.0 ppm; vegetable,
cucurbit (Crop Group 9) at 0.7 ppm to vegetable, cucurbit, group 9 at
0.30 ppm; vegetable, fruiting (Crop Group 8-10) at 1.5 ppm to
vegetable, fruiting, group 8-10 at 0.70 ppm; vegetable, leaf petiole
(Crop Subgroup 22B) at 40 ppm to leaf petiole vegetable subgroup 22B at
20 ppm; vegetable, leafy except head lettuce (Crop Group 4-16) at 60
ppm to vegetable, leafy, group 4-16, except lettuce, head at 30 ppm;
vegetable, leaves of root and tuber (Crop Group 2) at 40 ppm to
vegetable, leaves of root and tuber, group 2 at 30 ppm; vegetable,
legume, edible podded (Crop Subgroup 6A) at 4 ppm to vegetable, legume,
edible podded, subgroup 6A at 2.0 ppm; vegetable, root (Crop Subgroup
1A) at 0.6 ppm to vegetable, root, subgroup 1A at 0.50 ppm; and
vegetable, tuberous and corm (Crop Subgroup 1C) at 0.06 ppm to
vegetable, tuberous and corm, subgroup 1C at 0.03 ppm.
For alfalfa, forage, hay, and seed, the tolerances have been
modified to represent the appropriate number of significant figures;
however, the numerical value is no different than requested by the
petition.
The petition requested ``grass, forage (Grown for Seed)'' at 40 ppm
and ``grass, hay (Grown for Seed)'' at 80 ppm. Because ``grass grown
for seed'' is ambiguous, the Agency is establishing individual
tolerances for the hay and forage forms of specific grasses for which
residue data were submitted and that are grown for seed purposes:
Bluegrass, forage at 30 ppm; bluegrass, hay at 60 ppm, bromegrass,
forage at 30 ppm; bromegrass, hay at 60 ppm; fescue, forage at 30 ppm;
fescue, hay at 60 ppm; orchardgrass, forage at 30 ppm; orchardgrass,
hay at 60 ppm; ryegrass, forage at 30 ppm; ryegrass, hay at 60 ppm;
switchgrass, forage at 30 ppm; and switchgrass, hay at 60 ppm.
EPA is also establishing tolerances for beet, sugar, dried pulp at
1.5 ppm and potato, wet peel at 0.10 ppm, pursuant to 40 CFR
180.40(f)(1)(i)(A). These tolerances are necessary to cover
concentrated residues in processed commodities of raw agricultural
commodities contained in subgroups 1A and 1C, respectively.
V. Conclusion
Therefore, tolerances are established for residues of
picoxystrobin, methyl ([alpha]E)-[alpha]-(methoxymethylene)-2-[[[6-
(trifluoromethyl)-2-pyridinyl]oxy]methyl]benzeneacetate, in or on
alfalfa, forage at 4.0 ppm; alfalfa, hay at 5.0 ppm; alfalfa, seed at
9.0 ppm; almond, hulls at 7.0 ppm; beet, sugar, dried pulp at 1.5 ppm;
bluegrass, forage at 30 ppm; bluegrass, hay at 60 ppm; bromegrass,
forage at 30 ppm; bromegrass, hay at 60 ppm; cotton, gin byproducts at
20 ppm; cottonseed subgroup 20C at 2.0 ppm; fescue, forage at 30 ppm;
fescue, hay at 60 ppm; leaf petiole vegetable subgroup 22B at 20 ppm;
lettuce, head at 4.0 ppm; nut, tree, group 14-12 at 0.08 ppm; onion,
bulb, subgroup 3-07A at 0.50 ppm; onion, green, subgroup 3-07B at 10
ppm; orchardgrass, forage at 30 ppm; orchardgrass, hay at 60 ppm; pea
and bean, succulent shelled, subgroup 6B at 0.90 ppm; peanut at 0.05
ppm; peanut, hay at 30 ppm; potato, wet peel at 0.10 ppm; ryegrass,
forage at 30 ppm; ryegrass, hay at 60 ppm; sunflower subgroup 20B to
2.0 ppm; switchgrass, forage at 30 ppm; switchgrass, hay at 60 ppm;
vegetable, brassica, head and stem, group 5-16 at 2.0 ppm; vegetable,
cucurbit, group 9 at 0.30 ppm; vegetable, fruiting, group 8-10 at 0.70
ppm; vegetable, leafy, group 4-16, except lettuce, head at 30 ppm;
vegetable, leaves of root and tuber, group 2 at 30 ppm; vegetable,
legume, edible podded, subgroup 6A at 2.0 ppm; vegetable, root,
subgroup 1A at 0.50 ppm; and vegetable, tuberous and corm, subgroup 1C
at 0.03 ppm.
VI. Statutory and Executive Order Reviews
This action establishes tolerances under FFDCA section 408(d) in
response to a petition submitted to the Agency. The Office of
Management and Budget (OMB) has exempted these types of actions from
review under Executive Order 12866, entitled ``Regulatory Planning and
Review'' (58 FR 51735, October 4, 1993). Because this action has been
exempted from review under Executive Order 12866, this action is not
subject to Executive Order 13211, entitled ``Actions Concerning
Regulations That Significantly Affect Energy Supply, Distribution, or
Use'' (66 FR 28355, May 22, 2001) or Executive Order 13045, entitled
``Protection of Children from Environmental Health Risks and Safety
Risks'' (62 FR 19885, April 23, 1997), nor is it considered a
regulatory action under Executive Order 13771, entitled ``Reducing
Regulations and Controlling Regulatory Costs'' (82 FR 9339, February 3,
2017). This action does not contain any information collections subject
to OMB approval under the Paperwork Reduction Act (PRA) (44 U.S.C. 3501
et seq.), nor does it require any special considerations under
Executive Order 12898, entitled ``Federal Actions to Address
Environmental Justice in Minority Populations and Low-Income
[[Page 39610]]
Populations'' (59 FR 7629, February 16, 1994).
Since tolerances and exemptions that are established on the basis
of a petition under FFDCA section 408(d), such as the tolerances in
this final rule, do not require the issuance of a proposed rule, the
requirements of the Regulatory Flexibility Act (RFA) (5 U.S.C. 601 et
seq.), do not apply.
This action directly regulates growers, food processors, food
handlers, and food retailers, not States or tribes, nor does this
action alter the relationships or distribution of power and
responsibilities established by Congress in the preemption provisions
of FFDCA section 408(n)(4). As such, the Agency has determined that
this action will not have a substantial direct effect on States or
tribal governments, on the relationship between the national government
and the States or tribal governments, or on the distribution of power
and responsibilities among the various levels of government or between
the Federal Government and Indian tribes. Thus, the Agency has
determined that Executive Order 13132, entitled ``Federalism'' (64 FR
43255, August 10, 1999) and Executive Order 13175, entitled
``Consultation and Coordination with Indian Tribal Governments'' (65 FR
67249, November 9, 2000) do not apply to this action. In addition, this
action does not impose any enforceable duty or contain any unfunded
mandate as described under Title II of the Unfunded Mandates Reform Act
(UMRA) (2 U.S.C. 1501 et seq.).
This action does not involve any technical standards that would
require Agency consideration of voluntary consensus standards pursuant
to section 12(d) of the National Technology Transfer and Advancement
Act (NTTAA) (15 U.S.C. 272 note).
VII. Congressional Review Act
Pursuant to the Congressional Review Act (5 U.S.C. 801 et seq.),
EPA will submit a report containing this rule and other required
information to the U.S. Senate, the U.S. House of Representatives, and
the Comptroller General of the United States prior to publication of
the rule in the Federal Register. This action is not a ``major rule''
as defined by 5 U.S.C. 804(2).
List of Subjects in 40 CFR Part 180
Environmental protection, Administrative practice and procedure,
Agricultural commodities, Pesticides and pests, Reporting and
recordkeeping requirements.
Dated: July 25, 2018.
Michael Goodis,
Director, Registration Division, Office of Pesticide Programs.
Therefore, 40 CFR chapter I is amended as follows:
PART 180--[AMENDED]
0
1. The authority citation for part 180 continues to read as follows:
Authority: 21 U.S.C. 321(q), 346a and 371.
0
2. In Sec. 180.669, add alphabetically the following commodities:
Alfalfa, forage; Alfalfa, hay; Alfalfa, seed; Almond, hulls; Beet,
sugar, dried pulp; Bluegrass, forage; Bluegrass, hay; Bromegrass,
forage; Bromegrass, hay; Cotton, gin byproducts; Cottonseed subgroup
20C; Fescue, forage; Fescue, hay; Leaf petiole vegetable subgroup 22B;
Lettuce, head; Nut, tree, group 14-12; Onion, bulb, subgroup 3-07A;
Onion, green, subgroup 3-07B; Orchardgrass, forage; Orchardgrass, hay;
Pea and bean, succulent shelled, subgroup 6B; Peanut; Peanut, hay;
Potato, wet peel; Ryegrass, forage; Ryegrass, hay; Sunflower subgroup
20B; Switchgrass, forage; Switchgrass, hay; Vegetable, brassica, head
and stem, group 5-16; Vegetable, cucurbit, group 9; Vegetable,
fruiting, group 8-10; Vegetable, leafy, group 4-16, except lettuce,
head; Vegetable, leaves of root and tuber, group 2; Vegetable, legume,
edible podded, subgroup 6A; Vegetable, root, subgroup 1A; and
Vegetable, tuberous and corm, subgroup 1C to the table in paragraph (a)
to read as follows:
Sec. 180.669 Picoxystrobin; tolerances for residues.
(a) * * *
------------------------------------------------------------------------
Parts per
Commodity million
------------------------------------------------------------------------
Alfalfa, forage............................................. 4.0
Alfalfa, hay................................................ 5.0
Alfalfa, seed............................................... 9.0
Almond, hulls............................................... 7.0
* * * * *
Beet, sugar, dried pulp..................................... 1.5
Bluegrass, forage........................................... 30
Bluegrass, hay.............................................. 60
Bromegrass, forage.......................................... 30
Bromegrass, hay............................................. 60
* * * * *
Cotton, gin byproducts...................................... 20
Cottonseed subgroup 20C..................................... 2.0
* * * * *
Fescue, forage.............................................. 30
Fescue, hay................................................. 60
* * * * *
Leaf petiole vegetable subgroup 22B......................... 20
Lettuce, head............................................... 4.0
* * * * *
Nut, tree, group 14-12...................................... 0.08
Onion, bulb, subgroup 3-07A................................. 0.50
Onion, green, subgroup 3-07B................................ 10
Orchardgrass, forage........................................ 30
Orchardgrass, hay........................................... 60
* * * * *
Pea and bean, succulent shelled, subgroup 6B................ 0.90
Peanut...................................................... 0.05
Peanut, hay................................................. 30
Potato, wet peel............................................ 0.10
* * * * *
Ryegrass, forage............................................ 30
Ryegrass, hay............................................... 60
* * * * *
Sunflower subgroup 20B...................................... 2.0
Switchgrass, forage......................................... 30
Switchgrass, hay............................................ 60
* * * * *
Vegetable, brassica, head and stem, group 5-16.............. 2.0
Vegetable, cucurbit, group 9................................ 0.30
* * * * *
Vegetable, fruiting, group 8-10............................. 0.70
Vegetable, leafy, group 4-16, except lettuce, head.......... 30
Vegetable, leaves of root and tuber, group 2................ 30
Vegetable, legume, edible podded, subgroup 6A............... 2.0
Vegetable, root, subgroup 1A................................ 0.50
Vegetable, tuberous and corm, subgroup 1C................... 0.03
* * * * *
------------------------------------------------------------------------
* * * * *
[FR Doc. 2018-17192 Filed 8-9-18; 8:45 am]
BILLING CODE 6560-50-P