Methyl Bromide; Pesticide Tolerances for Emergency Exemptions, 8758-8764 [2018-04193]
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[FR Doc. 2018–04094 Filed 2–28–18; 8:45 am]
BILLING CODE 6560–50–P
ENVIRONMENTAL PROTECTION
AGENCY
40 CFR Part 180
[EPA–HQ–OPP–2017–0447; FRL–9971–19]
Methyl Bromide; Pesticide Tolerances
for Emergency Exemptions
This regulation establishes
time-limited tolerances for residues of
the fumigant methyl bromide, including
its metabolites and degradates in or on
post-harvest imported/domestic
agricultural commodities. This action is
in response to EPA’s granting
quarantine exemptions under the
Federal Insecticide, Fungicide, and
Rodenticide Act (FIFRA) authorizing
use of the pesticide on specified
agricultural commodities. This
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The docket for this action,
identified by docket identification (ID)
number EPA–HQ–OPP–2017–0447, 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
ADDRESSES:
Environmental Protection
Agency (EPA).
ACTION: Final rule.
AGENCY:
SUMMARY:
regulation establishes a maximum
permissible level for residues of methyl
bromide in or on these commodities.
The time-limited tolerances expire on
December 31, 2020.
DATES: This regulation is effective
March 1, 2018. Objections and requests
for hearings must be received on or
before April 30, 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).
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Docket is (703) 305–5805. Please review
the visitor instructions and additional
information about the docket available
at https://www.epa.gov/dockets.
FOR FURTHER INFORMATION CONTACT:
Michael Goodis, Director, 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).
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• Animal production (NAICS code
112).
• Food manufacturing (NAICS code
311).
• Pesticide manufacturing (NAICS
code 32532).
Additional instructions on
commenting or visiting the docket,
along with more information about
dockets generally, is available at https://
www.epa.gov/dockets.
B. How can I get electronic access to
other related information?
You may access a frequently updated
electronic version of 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.
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C. How can I file an objection or hearing
request?
Under section 408(g) of the Federal
Food, Drug, and Cosmetic Act (FFDCA),
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–2017–0447 in the subject line on
the first page of your submission. All
objections and requests for a hearing
must be in writing, and must be
received by the Hearing Clerk on or
before April 30, 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–
2017–0447, 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.
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II. Background and Statutory Findings
EPA, on its own initiative, in
accordance with FFDCA sections 408(e)
and 408(l)(6) of, 21 U.S.C. 346a(e) and
346a(1)(6), is establishing time-limited
tolerances for residues of methyl
bromide, in or on the following
agricultural commodities: Avocado at
5.0 parts per million (ppm); Banana at
5.0 ppm; Cactus at 3.0 ppm; Coconut,
copra at 8.0 ppm; Coffee, green bean at
150 ppm; Cola at 150 ppm; Cucurbit,
seed at 150 ppm; Fig at 10 ppm; Fruit,
berry and small fruit, group 13–07 at 5.0
ppm; Fruit, stone, group 12–12 at 5.0
ppm; Herbs and spices, group 19 at 35
ppm; Hibiscus, seed at 150 ppm; Ivy
gourd at 5.0 ppm; Kaffir lime, leaves at
0.50 ppm; Kenaf, seed at 150 ppm;
Longan at 5.0 ppm; Lychee at 5.0 ppm;
Oilseed group 20 at 150 ppm;
Peppermint, tops at 35 ppm; Pointed
gourd at 5.0 ppm; Pomegranate at 5.0
ppm; Rambutan at 5.0 ppm; Spanish
Lime 5.0 ppm; Spearmint, tops at 35
ppm; Stalk, stem and leaf petiole
vegetable group 22 at 0.50 ppm;
Tropical and subtropical fruits, edible
peel, group 23 at 10.0 ppm; Tropical
and subtropical fruits, inedible peel,
group 24 at 5.0 ppm; Vegetable, Head
and Stem Brassica, group 5–16 at 1.0
ppm; Vegetable, bulb, group 3–07 at 2.0
ppm; Vegetable, cucurbit, group 9 at 5.0
ppm; Vegetable, foliage of legume,
group 7 at 0.50 ppm; Vegetable fruiting,
group 8–10 at 7.0 ppm; Vegetable, leafy,
group 4–16 at 0.50 ppm; Vegetable
leaves of root and tuber, group 2 at 0.50
ppm; Vegetable, legume, group 6 at 3.0
ppm; Vegetable, root and tuber, group 1
at 3.0 ppm. These time-limited
tolerances expire on December 31, 2020.
Section 408(l)(6) of FFDCA requires
EPA to establish a time-limited
tolerance or exemption from the
requirement for a tolerance for pesticide
chemical residues in food that will
result from the use of a pesticide under
an emergency exemption granted by
EPA under FIFRA section 18. Such
tolerances can be established without
providing notice or period for public
comment. EPA does not intend for its
actions on FIFRA section 18 related
time-limited tolerances to set binding
precedents for the application of FFDCA
section 408 and the safety standard to
other tolerances and exemptions.
Section 408(e) of FFDCA allows EPA to
establish a tolerance or an exemption
from the requirement of a tolerance on
its own initiative, i.e., without having
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received any petition from an outside
party.
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. . . .’’
Section 18 of FIFRA authorizes EPA
to exempt any Federal or State agency
from any provision of FIFRA, if EPA
determines that ‘‘emergency conditions
exist which require such exemption.’’
EPA has established regulations
governing such emergency exemptions
in 40 CFR part 166.
III. Emergency Exemptions for Methyl
Bromide on Various Commodities and
FFDCA Tolerances
Quarantine exemptions were issued to
the Plant Protection and Quarantine
(PPQ) division of the United States
Department of Agriculture, Animal and
Plant Health Inspection Service (USDA/
APHIS), for the post-harvest use of the
fumigant methyl bromide on imported
and domestic commodities to target
invasive, non-indigenous quarantine
plant pests and to prevent the
introduction and/or spread of any new
or recently introduced foreign pest(s) to
any U.S. geographical location.
After having reviewed the
submissions, EPA determined that
emergency conditions existed for the
PPQ division of the USDA/APHIS, and
that the criteria for approval of these
quarantine exemptions were met. EPA
authorized quarantine exemptions
under FIFRA section 18 for the postharvest use of methyl bromide in or on
specified imported and domestic
agricultural commodities to eliminate
the threat of invasive plant pests.
As part of its evaluation of the
proposed quarantine emergency uses,
EPA assessed the potential risks
presented by residues of methyl
bromide in or on specified imported and
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domestic agricultural commodities. In
doing so, EPA considered the safety
standard in FFDCA section 408(b)(2),
and EPA decided that the necessary
time-limited tolerances under FFDCA
section 408(l)(6) would be consistent
with the safety standard and with
FIFRA section 18. Consistent with the
need to move quickly on the quarantine
exemption actions in order to address
urgent non-routine situations and to
ensure that the resulting food is safe and
lawful, EPA issued these time-limited
tolerances without notice and
opportunity for public comment as
provided in FFDCA section 408(l)(6).
Although these time-limited tolerances
expire on December 31, 2020, under
FFDCA section 408(l)(5), residues of the
pesticide not in excess of the amounts
specified in the tolerances remaining in
or on the specified agricultural
commodities after that date will not be
unlawful, provided the pesticide was
applied in a manner that was lawful
under FIFRA, and the residues do not
exceed levels that were authorized by
these time-limited tolerances at the time
of the applications. EPA will take action
to revoke these time-limited tolerances
earlier if any experience with, scientific
data on, or other relevant information
on this pesticide indicate that the
residues are not safe.
Because these time-limited tolerances
are being approved under emergency
conditions, EPA has not made any
decisions about whether methyl
bromide meets FIFRA’s registration
requirements for use on the specified
agricultural commodities or whether
permanent tolerances for these uses
would be appropriate. Under these
circumstances, EPA does not believe
that these time-limited tolerance
decisions serve as a basis for registration
of methyl bromide by a State for special
local needs under FIFRA section 24(c).
Nor do these tolerances by themselves
serve as the authority for persons other
than certified fumigators to use this
pesticide on the applicable crops under
FIFRA section 18 absent the
authorization of the quarantine
exemption issued to the Plant Protection
and Quarantine division of the United
States Department of Agriculture,
Animal and Plant Health Inspection
Service. For additional information
regarding the quarantine exemptions for
methyl bromide, contact the Agency’s
Registration Division at the address
provided under FOR FURTHER
INFORMATION CONTACT.
IV. 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 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 expected as a result
of these quarantine exemption requests
and the time-limited tolerances for
residues of methyl bromide on the
specified agricultural commodities.
EPA’s assessment of exposures and risks
associated with establishing these timelimited tolerances follows.
A. 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://
www.epa.gov/pesticide-science-andassessing-pesticide-risks/assessinghuman-health-risk-pesticides. Further,
the Agency’s exposure and risk
assessment for the emergency use of
methyl bromide on various agricultural
commodities is discussed in greater
detail in the following documents:
Methyl Bromide. Section 18 Emergency
Quarantine Exemption Use on
commodities Requested by the U.S.
Department of Agriculture/Animal and
Plant Health Inspection Service/Plant
Protection and Quarantine (USDA/
APHIS/PPQ) Division, May 02, 2017 and
Methyl Bromide: Human Health Risk
Assessment for the Section 18
Emergency Exemption Use on USDA
APHIS PPQ Commodities, September
13, 2013 are available in the docket at
the address provided under ADDRESSES.
A summary of the toxicological
endpoints for methyl bromide used for
human risk assessment is shown below
in Table 1 of this unit.
TABLE 1—SUMMARY OF TOXICOLOGICAL DOSES AND ENDPOINTS FOR METHYL BROMIDE FOR USE IN HUMAN HEALTH
RISK ASSESSMENT
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Exposure/scenario
Acute dietary (Females 13–50
years of age).
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Point of departure
and uncertainty/
safety factors
Dev. NOAEL = 14
mg/kg/day.
UF = 100x
FQPA SF = 1x
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RfD, PAD, LOC for
risk assessment
Study and toxicological effects
Acute RfD = 0.14
mg/kg/day.
aPAD = 0.14 mg/kg/
day
Developmental Toxicity—Rabbit (Inhalation).
LOAEL = 28 mg/kg/day based on agenesis of the gall bladder
and increased incidence of fused sternebrae.
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TABLE 1—SUMMARY OF TOXICOLOGICAL DOSES AND ENDPOINTS FOR METHYL BROMIDE FOR USE IN HUMAN HEALTH
RISK ASSESSMENT—Continued
Point of departure
and uncertainty/
safety factors
RfD, PAD, LOC for
risk assessment
Study and toxicological effects
Acute dietary (General population including infants and
children).
NOAEL = 90 mg/kg/
day.
UF = 100x
FQPA SF = 1x
Acute RfD = 0.9 mg/
kg/day.
aPAD = 0.9 mg/kg/
day
Acute neurotoxicity study—rat (Inhalation).
LOAEL = 314 mg/kg/day based on decreased activity, increase
in number of animals with drooping/half-closed eyelids and
alertness as measured in the Functional Observational Battery (FOB), decreased rears, decreased motor activity, increased piloerection and decreased body temperature.
Chronic dietary (All populations)
NOAEL = 2.2 mg/kg/
day.
UF = 100x
FQPA SF = 1x
Chronic RfD = 0.022
mg/kg/day.
cPAD = 0.022 mg/
kg/day
Chronic/carcinogenicity study—rats.
LOAEL = 11.1 mg/kg/day based on based on decreased body
weight, body weight gain and food consumption.
Exposure/scenario
Cancer (Oral, dermal, inhalation).
Classification: Not likely to be carcinogenic to humans.
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FQPA SF = Food Quality Protection Act Safety Factor. LOAEL = lowest-observed-adverse-effect-level. NOAEL = no-observed-adverse-effectlevel. PAD = population adjusted dose (a = acute, c = chronic). RfD = reference dose. UF =uncertainty factor.
B. Exposure Assessment
1. Dietary exposure from food and
feed uses. In evaluating dietary
exposure to methyl bromide, EPA
considered exposure under the timelimited tolerances established by this
action as well as all existing methyl
bromide tolerances in 40 CFR 180.124.
EPA assessed dietary exposures from
methyl bromide in food as follows:
i. Acute exposure. Acute effects were
identified for methyl bromide. 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). For purposes of
this acute exposure assessment, EPA
calculated residue levels based on
dissipation and time-to-market data,
assumed 100 percent crop treated (PCT)
and assumed that no residues were
present in any processed commodity
where heating was involved.
ii. Chronic exposure. In conducting
the chronic dietary exposure assessment
EPA used the food consumption data
from the USDA 2003–2008 NHANES/
WWEIA. To estimate chronic exposure
from residues in food, EPA calculated
residue levels based on dissipation and
time-to-market data, assumed 100%
crop treated, and assumed that no
residues were present in any processed
commodity where heating was involved.
For the chronic exposure assessment,
consumption data were averaged for the
entire U.S. population and within
population subgroups.
iii. Cancer. Based on the data
summarized in Unit IV.A., Table 1, EPA
has concluded that methyl bromide
does not pose a cancer risk to humans.
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Therefore, a dietary exposure
assessment for the purpose of assessing
cancer risk in unnecessary.
EPA reviewed numerous residue trials
submitted by industry (controlled
fumigation trials) in support of the
reregistration of methyl bromide.
Residue levels were calculated using
residue decline curves for each
commodity assuming first order kinetics
and taking into account minimum
predicted time intervals between
fumigation and market availability.
USDA APHIS requested uses on
additional crops, providing detailed use
pattern data. For these crops, residue
levels were translated from similar
commodities having residue trial data,
considering use patterns and taking into
account time intervals between
fumigation and market availability.
2. Dietary exposure from drinking
water. The Agency used screening level
water exposure models in the dietary
exposure analysis and risk assessment
for methyl bromide in drinking water.
These simulation models take into
account data on the physical, chemical,
and fate/transport characteristics of
methyl bromide. 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.
The methyl bromide Estimated
Drinking Water Concentration was
derived from groundwater estimates.
Based on data from the database of
pesticides in groundwater (U.S. EPA,
1992), two wells in California (out of
20,429 wells monitored in Florida,
California, and Hawaii) had methyl
bromide levels of 2.5 and 6.4
microgram/Liter (mg/L). The highest
groundwater monitoring value of 6.4
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parts per billion (ppb) was used for both
the acute and chronic (non-cancer)
assessments. Concentrations of methyl
bromide in surface water are considered
negligible due to the rapid dissipation of
methyl bromide from water to the air
(half-life of 73 minutes).
Modeled estimates of drinking water
concentrations were directly entered
into the dietary exposure model.
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).
Methyl bromide is a restricted use
pesticide and is not registered for any
specific residential use patterns;
however, there is potential for
residential bystander inhalation
exposure in and around port areas
where post-harvest commodity
fumigation treatments takes place.
Buffers have been implemented on all
methyl bromide labels, which reduce
bystander exposures to levels that do
not exceed the Agency’s level of
concern.
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
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substances that have a common
mechanism of toxicity.’’
EPA has not found methyl bromide to
share a common mechanism of toxicity
with any other substances, and methyl
bromide does not appear to produce a
toxic metabolite produced by other
substances. For the purposes of this
tolerance action, therefore, EPA has
assumed that methyl bromide 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.
C. 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 SF when reliable data
available to EPA support the choice of
a different factor.
2. Prenatal and postnatal sensitivity.
No evidence of increased quantitative or
qualitative susceptibility was observed
in developmental toxicity studies in rats
or rabbits. The rabbit inhalation
developmental study also did not
indicate susceptibility to the young as
the dams and the offspring had identical
NOAEL and LOAEL values.
Therefore, toxicity studies on adults
will not underestimate the risks methyl
bromide poses to children.
3. Conclusion. EPA has determined
that reliable data show that 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 methyl
bromide is complete.
ii. There is no indication that methyl
bromide is a neurotoxic chemical and
there is no need for a developmental
neurotoxicity study or additional UFs to
account for neurotoxicity.
iii. There is no evidence that methyl
bromide results in increased
susceptibility in in utero rats or rabbits
in the prenatal developmental studies.
In the rat developmental inhalation
study there was no indication of
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susceptibility to the young, at doses up
to 70 ppm. The rabbit inhalation
developmental study also did not
indicate susceptibility to the young, as
the dams and the offspring had identical
NOAEL and LOAEL values.
iv. There are no residual uncertainties
identified in the exposure databases.
The use of inhalation studies to assess
dietary risks is a conservative
(protective) approach since inhalation
exposure is expected to lead to a higher
internal dose than dietary exposure
since chemicals will enter the
circulatory system before many of the
detoxification processes associated with
oral exposure (e.g. first pass effect)
occur. Therefore, these assessments will
not underestimate the exposure and
risks posed by methyl bromide.
D. 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) presented in Unit
IV.A. Table 1. Short-, intermediate-, and
chronic-term risks are evaluated by
comparing the estimated aggregate food,
water, and residential exposure to the
appropriate PODs in Table 1 to ensure
that an adequate MOE exists.
1. Acute risk. Using the exposure
assumptions discussed in Unit IV.B. for
acute exposure, the acute dietary
exposure from food and water to methyl
bromide will occupy 3.5% of the aPAD
for children 1–2 years old, the
population group receiving the greatest
exposure. The Agency has determined
that dietary risk estimates for aggregate
acute exposure through food and water
to methyl bromide are below the
Agency’s level of concern for the U.S.
population and all population
subgroups. There is also potential for
inhalation exposure to residential
bystanders. However, since the dietary
contribution to acute aggregate risk is
negligible, EPA has determined that the
mitigation measures EPA required in the
2006 Tolerance Reassessment and Risk
Management Decision (TRED) for
Methyl Bromide, and Reregistration
Eligibility Decision (RED) for Methyl
Bromide’s Commodity Uses to protect
residential bystanders will ensure that
acute aggregate risks do not exceed
EPA’s level of concern.
2. Chronic risk. Using the exposure
assumptions described in Unit IV.B. for
chronic exposure, EPA has concluded
that chronic exposure to methyl
bromide from food and water will
utilize 43% of the cPAD for (children 1–
2 years old) the population group
receiving the greatest exposure. Based
PO 00000
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Fmt 4700
Sfmt 4700
on the explanation in the unit regarding
residential use patterns, chronic
residential exposure to residues of
methyl bromide is not expected.
Although there is potential for
inhalation exposure to residential
bystanders, EPA did not aggregate
short-, intermediate-term, or chronic
dietary and inhalation exposures to
methyl bromide because endpoints for
dietary and inhalation exposures for
these durations are not based on
common toxicological effects. Methyl
bromide is not registered for use in
residential settings; therefore,
residential exposures from the direct
use of methyl bromide in residential
areas is not expected.
3. Short-term risk. Short-term risk is
assessed based on short-term residential
exposure plus chronic dietary exposure.
Methyl bromide is not registered for use
in residential settings; therefore,
residential handler exposures from the
direct use of methyl bromide in
residential areas is not expected. EPA
did not aggregate short-, intermediateterm, or chronic dietary and inhalation
exposures to methyl bromide because
endpoints for dietary and inhalation
exposures for these durations are not
based on common toxicological effects.
4. Intermediate-term risk.
Intermediate-term risk is assessed based
on intermediate-term residential
exposure plus chronic dietary exposure.
Methyl bromide is not registered for use
in residential settings; therefore,
residential handler exposures from the
direct use of methyl bromide in
residential areas is not expected. EPA
did not aggregate short-, intermediateterm, or chronic dietary and inhalation
exposures to methyl bromide because
endpoints for dietary and inhalation
exposures for these durations are not
based on common toxicological effects.
5. Aggregate cancer risk for U.S.
population. Based on the lack of
evidence of carcinogenicity in two
adequate rodent carcinogenicity studies,
methyl bromide 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 methyl
bromide residues.
V. Other Considerations
A. Analytical Enforcement Methodology
An adequate enforcement
methodology (King headspace method,
J. Agricultural Food Chemistry, Vol 29,
No. 5, pp 1003–1005) is available to
enforce the tolerance expression. This
E:\FR\FM\01MRR1.SGM
01MRR1
8763
Federal Register / Vol. 83, No. 41 / Thursday, March 1, 2018 / Rules and Regulations
method is a gas chromatography/
electron capture (GC/EC) method that
was validated in 1987 in the EPA
Environmental Chemistry Laboratory
(D168869, L. Cheng, 27–OCT–1992).
The headspace procedure for
determining methyl bromide has been
forwarded to FDA for inclusion in PAM
Vol. II. This method is adequate for data
collection and for tolerance enforcement
on plant and processed food
commodities.
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.
Methyl bromide Codex MRLs have
been established for several
commodities; however, there are no
Codex MRLs for any of the commodities
that are the subject of this quarantine
action. Therefore, at this time, there are
no harmonization issues.
VI. Conclusion
Therefore, time-limited tolerances are
established for residues of the fumigant
methyl bromide, including its
metabolites and degradates, in or on
specified agricultural imported/
domestic commodities. These tolerances
expire on December 31, 2020.
VII. Statutory and Executive Order
Reviews
amozie on DSK30RV082PROD with RULES
This action establishes tolerances
under FFDCA sections 408(e) and
408(l)(6). 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 in accordance with
FFDCA sections 408(e) and 408(l)(6),
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).
VIII. 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 13, 2018.
Donna S. Davis,
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. In § 180.124, revise paragraph (b) to
read as follows:
■
§ 180.124
residues.
Methyl bromide; tolerances for
*
*
*
*
*
(b) Section 18 emergency exemptions.
Time-limited tolerances as listed in the
following table are established for
residues of the fumigant methyl
bromide, including its metabolites and
degradates, in or on the specified
agricultural commodities, resulting from
use of the pesticide pursuant to FIFRA
section 18 emergency exemptions.
Compliance with the tolerance levels
specified below is to be determined by
measuring only methyl bromide. These
tolerances expire and are revoked on the
date indicated in the table.
Parts per
million
Commodity
Avocado ........................................................................................................................................................
Banana .........................................................................................................................................................
Cactus ...........................................................................................................................................................
Coconut, copra .............................................................................................................................................
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E:\FR\FM\01MRR1.SGM
5.0
5.0
3.0
8.0
01MRR1
Expiration date
December
December
December
December
31,
31,
31,
31,
2020.
2020.
2020.
2020.
8764
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Parts per
million
Commodity
Coffee, green bean .......................................................................................................................................
Cola ..............................................................................................................................................................
Cucurbit, seed ...............................................................................................................................................
Fig .................................................................................................................................................................
Fruit, berry and small fruit, group 13–07 ......................................................................................................
Fruit, stone, group 12–12 .............................................................................................................................
Herb and spice, group 19 .............................................................................................................................
Hibiscus, seed ..............................................................................................................................................
Ivy gourd .......................................................................................................................................................
Kaffir lime, leaves .........................................................................................................................................
Kenaf, seed ..................................................................................................................................................
Longan ..........................................................................................................................................................
Lychee ..........................................................................................................................................................
Oilseed group 20 ..........................................................................................................................................
Peppermint, tops ...........................................................................................................................................
Pointed gourd ...............................................................................................................................................
Pomegranate ................................................................................................................................................
Rambutan .....................................................................................................................................................
Spanish lime .................................................................................................................................................
Spearmint, tops .............................................................................................................................................
Stalk, stem and leaf petiole vegetable group 22 ..........................................................................................
Tropical and subtropical fruits, edible peel, group 23 ..................................................................................
Tropical and subtropical fruits, inedible peel, group 24 ...............................................................................
Vegetable, bulb, group 3–07 ........................................................................................................................
Vegetable, cucurbit, group 9 ........................................................................................................................
Vegetable, foliage of legume, group 7 .........................................................................................................
Vegetable, fruiting, group 8–10 ....................................................................................................................
Vegetable, Head and Stem Brassica, group 5–16 .......................................................................................
Vegetable, leafy, group 4–16 .......................................................................................................................
Vegetable, leaves of root and tuber, group 2 ..............................................................................................
Vegetable, legume, group 6 .........................................................................................................................
Vegetable, root and tuber, group 1 ..............................................................................................................
*
*
*
*
*
[FR Doc. 2018–04193 Filed 2–28–18; 8:45 am]
BILLING CODE 6560–50–P
DEPARTMENT OF COMMERCE
National Oceanic and Atmospheric
Administration
50 CFR Part 648
[Docket No. 170713663–8176–02]
RIN 0648–BH04
Fisheries of the Northeastern United
States; Atlantic Mackerel, Squid, and
Butterfish Fisheries; Specifications
National Marine Fisheries
Service (NMFS), National Oceanic and
Atmospheric Administration (NOAA),
Commerce.
ACTION: Final rule.
AGENCY:
NMFS implements longfin
squid, Illex squid, and butterfish
specifications for the 2018 fishing year
and projected specifications for fishing
years 2019 and 2020. This action is
necessary to specify catch levels for the
squid and butterfish fisheries based
upon updated information on stock
status. These specifications are intended
to promote the sustainable utilization
amozie on DSK30RV082PROD with RULES
SUMMARY:
VerDate Sep<11>2014
17:58 Feb 28, 2018
Jkt 244001
and conservation of the squid and
butterfish resources.
DATES: Effective April 2, 2018.
ADDRESSES: Copies of supporting
documents used by the Mid-Atlantic
Fishery Management Council, including
the Environmental Assessment (EA), the
Regulatory Impact Review (RIR), and the
Regulatory Flexibility Act (RFA)
analysis are available from: Dr.
Christopher M. Moore, Executive
Director, Mid-Atlantic Fishery
Management Council, 800 North State
Street, Suite 201, Dover, DE 19901,
telephone (302) 674–2331. The EA/RIR/
RFA analysis is also accessible via the
internet at www.regulations.gov/
#!docketDetail;D=NOAA-NMFS-20170089. Stock assessment reports and
assessment update reports for all species
are available online at:
www.nefsc.noaa.gov/saw/reviews_
report_options.php. Performance reports
for the Atlantic mackerel, squid, and
butterfish fisheries are available online
at: https://www.mafmc.org/msb.
FOR FURTHER INFORMATION CONTACT:
Douglas Christel, Fishery Policy
Analyst, (978) 281–9141.
SUPPLEMENTARY INFORMATION:
Background
The regulations implementing the
Atlantic Mackerel, Squid, and Butterfish
PO 00000
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150
150
150
10
5.0
5.0
35
150
5.0
0.50
150
5.0
5.0
150
35
5.0
5.0
5.0
5.0
35
0.50
10
5.0
2.0
5.0
0.50
7.0
1.0
0.50
0.50
3.0
3.0
Expiration date
December
December
December
December
December
December
December
December
December
December
December
December
December
December
December
December
December
December
December
December
December
December
December
December
December
December
December
December
December
December
December
December
31,
31,
31,
31,
31,
31,
31,
31,
31,
31,
31,
31,
31,
31,
31,
31,
31,
31,
31,
31,
31,
31,
31,
31,
31,
31,
31,
31,
31,
31,
31,
31,
2020.
2020.
2020.
2020.
2020.
2020.
2020.
2020.
2020.
2020.
2020.
2020.
2020.
2020.
2020.
2020.
2020.
2020.
2020.
2020.
2020.
2020.
2020.
2020.
2020.
2020.
2020.
2020.
2020.
2020.
2020.
2020.
Fishery Management Plan (FMP) require
the Mid-Atlantic Council’s Atlantic
Mackerel, Squid, and Butterfish
Monitoring Committee to develop
specification recommendations for each
species based upon the ABC advice of
the Council’s SSC. The FMP regulations
also require the specification of annual
catch limits (ACLs) and accountability
measure (AM) provisions for butterfish.
Both squid species are exempt from the
ACL/AM requirements because they
have a life cycle of less than one year.
In addition, the regulations require the
specification of domestic annual harvest
(DAH), domestic annual processing
(DAP), total allowable level of foreign
fishing (TALFF), joint venture
processing (JVP), commercial and
recreational annual catch targets (ACT),
the butterfish mortality cap in the
longfin squid fishery, and initial
optimum yield (IOY) for both squid
species.
On December 13, 2017, NMFS
published a proposed rule (82 FR
58583) for the 2018–2020 squid and
butterfish specifications recommended
by the Council. The proposed rule for
this action included additional
background on specifications and the
details of how the Council derived its
recommended specifications for longfin
and Illex squid and butterfish. Those
E:\FR\FM\01MRR1.SGM
01MRR1
Agencies
[Federal Register Volume 83, Number 41 (Thursday, March 1, 2018)]
[Rules and Regulations]
[Pages 8758-8764]
From the Federal Register Online via the Government Publishing Office [www.gpo.gov]
[FR Doc No: 2018-04193]
-----------------------------------------------------------------------
ENVIRONMENTAL PROTECTION AGENCY
40 CFR Part 180
[EPA-HQ-OPP-2017-0447; FRL-9971-19]
Methyl Bromide; Pesticide Tolerances for Emergency Exemptions
AGENCY: Environmental Protection Agency (EPA).
ACTION: Final rule.
-----------------------------------------------------------------------
SUMMARY: This regulation establishes time-limited tolerances for
residues of the fumigant methyl bromide, including its metabolites and
degradates in or on post-harvest imported/domestic agricultural
commodities. This action is in response to EPA's granting quarantine
exemptions under the Federal Insecticide, Fungicide, and Rodenticide
Act (FIFRA) authorizing use of the pesticide on specified agricultural
commodities. This regulation establishes a maximum permissible level
for residues of methyl bromide in or on these commodities. The time-
limited tolerances expire on December 31, 2020.
DATES: This regulation is effective March 1, 2018. Objections and
requests for hearings must be received on or before April 30, 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-2017-0447, is available at https://www.regulations.gov or at the Office of Pesticide Programs Regulatory
Public Docket (OPP Docket) in the Environmental Protection Agency
Docket Center (EPA/DC), West William Jefferson Clinton Bldg., Rm. 3334,
1301 Constitution Ave. NW, Washington, DC 20460-0001. The Public
Reading Room is open from 8:30 a.m. to 4:30 p.m., Monday through
Friday, excluding legal holidays. The telephone number for the Public
Reading Room is (202) 566-1744, and the telephone number for the OPP
Docket is (703) 305-5805. Please review the visitor instructions and
additional information about the docket available at https://www.epa.gov/dockets.
FOR FURTHER INFORMATION CONTACT: Michael Goodis, Director, 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:
[emsp14]Crop production (NAICS code 111).
[[Page 8759]]
[emsp14]Animal production (NAICS code 112).
[emsp14]Food manufacturing (NAICS code 311).
[emsp14]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 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 section 408(g) of the Federal Food, Drug, and Cosmetic Act
(FFDCA), 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-
2017-0447 in the subject line on the first page of your submission. All
objections and requests for a hearing must be in writing, and must be
received by the Hearing Clerk on or before April 30, 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-2017-0447, 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. Background and Statutory Findings
EPA, on its own initiative, in accordance with FFDCA sections
408(e) and 408(l)(6) of, 21 U.S.C. 346a(e) and 346a(1)(6), is
establishing time-limited tolerances for residues of methyl bromide, in
or on the following agricultural commodities: Avocado at 5.0 parts per
million (ppm); Banana at 5.0 ppm; Cactus at 3.0 ppm; Coconut, copra at
8.0 ppm; Coffee, green bean at 150 ppm; Cola at 150 ppm; Cucurbit, seed
at 150 ppm; Fig at 10 ppm; Fruit, berry and small fruit, group 13-07 at
5.0 ppm; Fruit, stone, group 12-12 at 5.0 ppm; Herbs and spices, group
19 at 35 ppm; Hibiscus, seed at 150 ppm; Ivy gourd at 5.0 ppm; Kaffir
lime, leaves at 0.50 ppm; Kenaf, seed at 150 ppm; Longan at 5.0 ppm;
Lychee at 5.0 ppm; Oilseed group 20 at 150 ppm; Peppermint, tops at 35
ppm; Pointed gourd at 5.0 ppm; Pomegranate at 5.0 ppm; Rambutan at 5.0
ppm; Spanish Lime 5.0 ppm; Spearmint, tops at 35 ppm; Stalk, stem and
leaf petiole vegetable group 22 at 0.50 ppm; Tropical and subtropical
fruits, edible peel, group 23 at 10.0 ppm; Tropical and subtropical
fruits, inedible peel, group 24 at 5.0 ppm; Vegetable, Head and Stem
Brassica, group 5-16 at 1.0 ppm; Vegetable, bulb, group 3-07 at 2.0
ppm; Vegetable, cucurbit, group 9 at 5.0 ppm; Vegetable, foliage of
legume, group 7 at 0.50 ppm; Vegetable fruiting, group 8-10 at 7.0 ppm;
Vegetable, leafy, group 4-16 at 0.50 ppm; Vegetable leaves of root and
tuber, group 2 at 0.50 ppm; Vegetable, legume, group 6 at 3.0 ppm;
Vegetable, root and tuber, group 1 at 3.0 ppm. These time-limited
tolerances expire on December 31, 2020.
Section 408(l)(6) of FFDCA requires EPA to establish a time-limited
tolerance or exemption from the requirement for a tolerance for
pesticide chemical residues in food that will result from the use of a
pesticide under an emergency exemption granted by EPA under FIFRA
section 18. Such tolerances can be established without providing notice
or period for public comment. EPA does not intend for its actions on
FIFRA section 18 related time-limited tolerances to set binding
precedents for the application of FFDCA section 408 and the safety
standard to other tolerances and exemptions. Section 408(e) of FFDCA
allows EPA to establish a tolerance or an exemption from the
requirement of a tolerance on its own initiative, i.e., without having
received any petition from an outside party.
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. . .
.''
Section 18 of FIFRA authorizes EPA to exempt any Federal or State
agency from any provision of FIFRA, if EPA determines that ``emergency
conditions exist which require such exemption.'' EPA has established
regulations governing such emergency exemptions in 40 CFR part 166.
III. Emergency Exemptions for Methyl Bromide on Various Commodities and
FFDCA Tolerances
Quarantine exemptions were issued to the Plant Protection and
Quarantine (PPQ) division of the United States Department of
Agriculture, Animal and Plant Health Inspection Service (USDA/APHIS),
for the post-harvest use of the fumigant methyl bromide on imported and
domestic commodities to target invasive, non-indigenous quarantine
plant pests and to prevent the introduction and/or spread of any new or
recently introduced foreign pest(s) to any U.S. geographical location.
After having reviewed the submissions, EPA determined that
emergency conditions existed for the PPQ division of the USDA/APHIS,
and that the criteria for approval of these quarantine exemptions were
met. EPA authorized quarantine exemptions under FIFRA section 18 for
the post-harvest use of methyl bromide in or on specified imported and
domestic agricultural commodities to eliminate the threat of invasive
plant pests.
As part of its evaluation of the proposed quarantine emergency
uses, EPA assessed the potential risks presented by residues of methyl
bromide in or on specified imported and
[[Page 8760]]
domestic agricultural commodities. In doing so, EPA considered the
safety standard in FFDCA section 408(b)(2), and EPA decided that the
necessary time-limited tolerances under FFDCA section 408(l)(6) would
be consistent with the safety standard and with FIFRA section 18.
Consistent with the need to move quickly on the quarantine exemption
actions in order to address urgent non-routine situations and to ensure
that the resulting food is safe and lawful, EPA issued these time-
limited tolerances without notice and opportunity for public comment as
provided in FFDCA section 408(l)(6). Although these time-limited
tolerances expire on December 31, 2020, under FFDCA section 408(l)(5),
residues of the pesticide not in excess of the amounts specified in the
tolerances remaining in or on the specified agricultural commodities
after that date will not be unlawful, provided the pesticide was
applied in a manner that was lawful under FIFRA, and the residues do
not exceed levels that were authorized by these time-limited tolerances
at the time of the applications. EPA will take action to revoke these
time-limited tolerances earlier if any experience with, scientific data
on, or other relevant information on this pesticide indicate that the
residues are not safe.
Because these time-limited tolerances are being approved under
emergency conditions, EPA has not made any decisions about whether
methyl bromide meets FIFRA's registration requirements for use on the
specified agricultural commodities or whether permanent tolerances for
these uses would be appropriate. Under these circumstances, EPA does
not believe that these time-limited tolerance decisions serve as a
basis for registration of methyl bromide by a State for special local
needs under FIFRA section 24(c). Nor do these tolerances by themselves
serve as the authority for persons other than certified fumigators to
use this pesticide on the applicable crops under FIFRA section 18
absent the authorization of the quarantine exemption issued to the
Plant Protection and Quarantine division of the United States
Department of Agriculture, Animal and Plant Health Inspection Service.
For additional information regarding the quarantine exemptions for
methyl bromide, contact the Agency's Registration Division at the
address provided under FOR FURTHER INFORMATION CONTACT.
IV. 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 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 expected as a result of these quarantine exemption requests
and the time-limited tolerances for residues of methyl bromide on the
specified agricultural commodities. EPA's assessment of exposures and
risks associated with establishing these time-limited tolerances
follows.
A. 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://www.epa.gov/pesticide-science-and-assessing-pesticide-risks/assessing-human-health-risk-pesticides. Further, the Agency's exposure and risk assessment for
the emergency use of methyl bromide on various agricultural commodities
is discussed in greater detail in the following documents: Methyl
Bromide. Section 18 Emergency Quarantine Exemption Use on commodities
Requested by the U.S. Department of Agriculture/Animal and Plant Health
Inspection Service/Plant Protection and Quarantine (USDA/APHIS/PPQ)
Division, May 02, 2017 and Methyl Bromide: Human Health Risk Assessment
for the Section 18 Emergency Exemption Use on USDA APHIS PPQ
Commodities, September 13, 2013 are available in the docket at the
address provided under ADDRESSES. A summary of the toxicological
endpoints for methyl bromide used for human risk assessment is shown
below in Table 1 of this unit.
Table 1--Summary of Toxicological Doses and Endpoints for Methyl Bromide 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 (Females 13-50 Dev. NOAEL = 14 mg/ Acute RfD = 0.14 mg/ Developmental Toxicity--Rabbit
years of age). kg/day. kg/day. (Inhalation).
UF = 100x........... aPAD = 0.14 mg/kg/ LOAEL = 28 mg/kg/day based on
FQPA SF = 1x........ day. agenesis of the gall bladder and
increased incidence of fused
sternebrae.
----------------------------------------------------------------------------------------------------------------
[[Page 8761]]
Acute dietary (General population NOAEL = 90 mg/kg/day Acute RfD = 0.9 mg/ Acute neurotoxicity study--rat
including infants and children). UF = 100x........... kg/day. (Inhalation).
FQPA SF = 1x........ aPAD = 0.9 mg/kg/ LOAEL = 314 mg/kg/day based on
day. decreased activity, increase in
number of animals with drooping/
half-closed eyelids and alertness
as measured in the Functional
Observational Battery (FOB),
decreased rears, decreased motor
activity, increased piloerection
and decreased body temperature.
----------------------------------------------------------------------------------------------------------------
Chronic dietary (All populations) NOAEL = 2.2 mg/kg/ Chronic RfD = 0.022 Chronic/carcinogenicity study--
day. mg/kg/day. rats.
UF = 100x........... cPAD = 0.022 mg/kg/ LOAEL = 11.1 mg/kg/day based on
FQPA SF = 1x........ day. based on decreased body weight,
body weight gain and food
consumption.
----------------------------------------------------------------------------------------------------------------
Cancer (Oral, dermal, inhalation) Classification: Not likely to be carcinogenic to humans.
----------------------------------------------------------------------------------------------------------------
FQPA SF = Food Quality Protection Act Safety Factor. LOAEL = lowest-observed-adverse-effect-level. NOAEL = no-
observed-adverse-effect-level. PAD = population adjusted dose (a = acute, c = chronic). RfD = reference dose.
UF =uncertainty factor.
B. Exposure Assessment
1. Dietary exposure from food and feed uses. In evaluating dietary
exposure to methyl bromide, EPA considered exposure under the time-
limited tolerances established by this action as well as all existing
methyl bromide tolerances in 40 CFR 180.124.
EPA assessed dietary exposures from methyl bromide in food as
follows:
i. Acute exposure. Acute effects were identified for methyl
bromide. 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). For purposes of this
acute exposure assessment, EPA calculated residue levels based on
dissipation and time-to-market data, assumed 100 percent crop treated
(PCT) and assumed that no residues were present in any processed
commodity where heating was involved.
ii. Chronic exposure. In conducting the chronic dietary exposure
assessment EPA used the food consumption data from the USDA 2003-2008
NHANES/WWEIA. To estimate chronic exposure from residues in food, EPA
calculated residue levels based on dissipation and time-to-market data,
assumed 100% crop treated, and assumed that no residues were present in
any processed commodity where heating was involved. For the chronic
exposure assessment, consumption data were averaged for the entire U.S.
population and within population subgroups.
iii. Cancer. Based on the data summarized in Unit IV.A., Table 1,
EPA has concluded that methyl bromide does not pose a cancer risk to
humans. Therefore, a dietary exposure assessment for the purpose of
assessing cancer risk in unnecessary.
EPA reviewed numerous residue trials submitted by industry
(controlled fumigation trials) in support of the reregistration of
methyl bromide. Residue levels were calculated using residue decline
curves for each commodity assuming first order kinetics and taking into
account minimum predicted time intervals between fumigation and market
availability. USDA APHIS requested uses on additional crops, providing
detailed use pattern data. For these crops, residue levels were
translated from similar commodities having residue trial data,
considering use patterns and taking into account time intervals between
fumigation and market availability.
2. Dietary exposure from drinking water. The Agency used screening
level water exposure models in the dietary exposure analysis and risk
assessment for methyl bromide in drinking water. These simulation
models take into account data on the physical, chemical, and fate/
transport characteristics of methyl bromide. 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.
The methyl bromide Estimated Drinking Water Concentration was
derived from groundwater estimates. Based on data from the database of
pesticides in groundwater (U.S. EPA, 1992), two wells in California
(out of 20,429 wells monitored in Florida, California, and Hawaii) had
methyl bromide levels of 2.5 and 6.4 microgram/Liter ([mu]g/L). The
highest groundwater monitoring value of 6.4 parts per billion (ppb) was
used for both the acute and chronic (non-cancer) assessments.
Concentrations of methyl bromide in surface water are considered
negligible due to the rapid dissipation of methyl bromide from water to
the air (half-life of 73 minutes).
Modeled estimates of drinking water concentrations were directly
entered into the dietary exposure model.
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).
Methyl bromide is a restricted use pesticide and is not registered
for any specific residential use patterns; however, there is potential
for residential bystander inhalation exposure in and around port areas
where post-harvest commodity fumigation treatments takes place. Buffers
have been implemented on all methyl bromide labels, which reduce
bystander exposures to levels that do not exceed the Agency's level of
concern.
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
[[Page 8762]]
substances that have a common mechanism of toxicity.''
EPA has not found methyl bromide to share a common mechanism of
toxicity with any other substances, and methyl bromide does not appear
to produce a toxic metabolite produced by other substances. For the
purposes of this tolerance action, therefore, EPA has assumed that
methyl bromide 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.
C. 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 SF when reliable data
available to EPA support the choice of a different factor.
2. Prenatal and postnatal sensitivity. No evidence of increased
quantitative or qualitative susceptibility was observed in
developmental toxicity studies in rats or rabbits. The rabbit
inhalation developmental study also did not indicate susceptibility to
the young as the dams and the offspring had identical NOAEL and LOAEL
values.
Therefore, toxicity studies on adults will not underestimate the
risks methyl bromide poses to children.
3. Conclusion. EPA has determined that reliable data show that 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 methyl bromide is complete.
ii. There is no indication that methyl bromide is a neurotoxic
chemical and there is no need for a developmental neurotoxicity study
or additional UFs to account for neurotoxicity.
iii. There is no evidence that methyl bromide results in increased
susceptibility in in utero rats or rabbits in the prenatal
developmental studies. In the rat developmental inhalation study there
was no indication of susceptibility to the young, at doses up to 70
ppm. The rabbit inhalation developmental study also did not indicate
susceptibility to the young, as the dams and the offspring had
identical NOAEL and LOAEL values.
iv. There are no residual uncertainties identified in the exposure
databases. The use of inhalation studies to assess dietary risks is a
conservative (protective) approach since inhalation exposure is
expected to lead to a higher internal dose than dietary exposure since
chemicals will enter the circulatory system before many of the
detoxification processes associated with oral exposure (e.g. first pass
effect) occur. Therefore, these assessments will not underestimate the
exposure and risks posed by methyl bromide.
D. 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) presented in Unit IV.A. Table
1. Short-, intermediate-, and chronic-term risks are evaluated by
comparing the estimated aggregate food, water, and residential exposure
to the appropriate PODs in Table 1 to ensure that an adequate MOE
exists.
1. Acute risk. Using the exposure assumptions discussed in Unit
IV.B. for acute exposure, the acute dietary exposure from food and
water to methyl bromide will occupy 3.5% of the aPAD for children 1-2
years old, the population group receiving the greatest exposure. The
Agency has determined that dietary risk estimates for aggregate acute
exposure through food and water to methyl bromide are below the
Agency's level of concern for the U.S. population and all population
subgroups. There is also potential for inhalation exposure to
residential bystanders. However, since the dietary contribution to
acute aggregate risk is negligible, EPA has determined that the
mitigation measures EPA required in the 2006 Tolerance Reassessment and
Risk Management Decision (TRED) for Methyl Bromide, and Reregistration
Eligibility Decision (RED) for Methyl Bromide's Commodity Uses to
protect residential bystanders will ensure that acute aggregate risks
do not exceed EPA's level of concern.
2. Chronic risk. Using the exposure assumptions described in Unit
IV.B. for chronic exposure, EPA has concluded that chronic exposure to
methyl bromide from food and water will utilize 43% of the cPAD for
(children 1-2 years old) the population group receiving the greatest
exposure. Based on the explanation in the unit regarding residential
use patterns, chronic residential exposure to residues of methyl
bromide is not expected. Although there is potential for inhalation
exposure to residential bystanders, EPA did not aggregate short-,
intermediate-term, or chronic dietary and inhalation exposures to
methyl bromide because endpoints for dietary and inhalation exposures
for these durations are not based on common toxicological effects.
Methyl bromide is not registered for use in residential settings;
therefore, residential exposures from the direct use of methyl bromide
in residential areas is not expected.
3. Short-term risk. Short-term risk is assessed based on short-term
residential exposure plus chronic dietary exposure. Methyl bromide is
not registered for use in residential settings; therefore, residential
handler exposures from the direct use of methyl bromide in residential
areas is not expected. EPA did not aggregate short-, intermediate-term,
or chronic dietary and inhalation exposures to methyl bromide because
endpoints for dietary and inhalation exposures for these durations are
not based on common toxicological effects.
4. Intermediate-term risk. Intermediate-term risk is assessed based
on intermediate-term residential exposure plus chronic dietary
exposure. Methyl bromide is not registered for use in residential
settings; therefore, residential handler exposures from the direct use
of methyl bromide in residential areas is not expected. EPA did not
aggregate short-, intermediate-term, or chronic dietary and inhalation
exposures to methyl bromide because endpoints for dietary and
inhalation exposures for these durations are not based on common
toxicological effects.
5. Aggregate cancer risk for U.S. population. Based on the lack of
evidence of carcinogenicity in two adequate rodent carcinogenicity
studies, methyl bromide 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 methyl bromide residues.
V. Other Considerations
A. Analytical Enforcement Methodology
An adequate enforcement methodology (King headspace method, J.
Agricultural Food Chemistry, Vol 29, No. 5, pp 1003-1005) is available
to enforce the tolerance expression. This
[[Page 8763]]
method is a gas chromatography/electron capture (GC/EC) method that was
validated in 1987 in the EPA Environmental Chemistry Laboratory
(D168869, L. Cheng, 27-OCT-1992). The headspace procedure for
determining methyl bromide has been forwarded to FDA for inclusion in
PAM Vol. II. This method is adequate for data collection and for
tolerance enforcement on plant and processed food commodities.
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.
Methyl bromide Codex MRLs have been established for several
commodities; however, there are no Codex MRLs for any of the
commodities that are the subject of this quarantine action. Therefore,
at this time, there are no harmonization issues.
VI. Conclusion
Therefore, time-limited tolerances are established for residues of
the fumigant methyl bromide, including its metabolites and degradates,
in or on specified agricultural imported/domestic commodities. These
tolerances expire on December 31, 2020.
VII. Statutory and Executive Order Reviews
This action establishes tolerances under FFDCA sections 408(e) and
408(l)(6). 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 in accordance
with FFDCA sections 408(e) and 408(l)(6), 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).
VIII. 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 13, 2018.
Donna S. Davis,
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. In Sec. 180.124, revise paragraph (b) to read as follows:
Sec. [emsp14]180.124 Methyl bromide; tolerances for residues.
* * * * *
(b) Section 18 emergency exemptions. Time-limited tolerances as
listed in the following table are established for residues of the
fumigant methyl bromide, including its metabolites and degradates, in
or on the specified agricultural commodities, resulting from use of the
pesticide pursuant to FIFRA section 18 emergency exemptions. Compliance
with the tolerance levels specified below is to be determined by
measuring only methyl bromide. These tolerances expire and are revoked
on the date indicated in the table.
------------------------------------------------------------------------
Parts per
Commodity million Expiration date
------------------------------------------------------------------------
Avocado..................... 5.0 December 31, 2020.
Banana...................... 5.0 December 31, 2020.
Cactus...................... 3.0 December 31, 2020.
Coconut, copra.............. 8.0 December 31, 2020.
[[Page 8764]]
Coffee, green bean.......... 150 December 31, 2020.
Cola........................ 150 December 31, 2020.
Cucurbit, seed.............. 150 December 31, 2020.
Fig......................... 10 December 31, 2020.
Fruit, berry and small 5.0 December 31, 2020.
fruit, group 13-07.
Fruit, stone, group 12-12... 5.0 December 31, 2020.
Herb and spice, group 19.... 35 December 31, 2020.
Hibiscus, seed.............. 150 December 31, 2020.
Ivy gourd................... 5.0 December 31, 2020.
Kaffir lime, leaves......... 0.50 December 31, 2020.
Kenaf, seed................. 150 December 31, 2020.
Longan...................... 5.0 December 31, 2020.
Lychee...................... 5.0 December 31, 2020.
Oilseed group 20............ 150 December 31, 2020.
Peppermint, tops............ 35 December 31, 2020.
Pointed gourd............... 5.0 December 31, 2020.
Pomegranate................. 5.0 December 31, 2020.
Rambutan.................... 5.0 December 31, 2020.
Spanish lime................ 5.0 December 31, 2020.
Spearmint, tops............. 35 December 31, 2020.
Stalk, stem and leaf petiole 0.50 December 31, 2020.
vegetable group 22.
Tropical and subtropical 10 December 31, 2020.
fruits, edible peel, group
23.
Tropical and subtropical 5.0 December 31, 2020.
fruits, inedible peel,
group 24.
Vegetable, bulb, group 3-07. 2.0 December 31, 2020.
Vegetable, cucurbit, group 9 5.0 December 31, 2020.
Vegetable, foliage of 0.50 December 31, 2020.
legume, group 7.
Vegetable, fruiting, group 8- 7.0 December 31, 2020.
10.
Vegetable, Head and Stem 1.0 December 31, 2020.
Brassica, group 5-16.
Vegetable, leafy, group 4-16 0.50 December 31, 2020.
Vegetable, leaves of root 0.50 December 31, 2020.
and tuber, group 2.
Vegetable, legume, group 6.. 3.0 December 31, 2020.
Vegetable, root and tuber, 3.0 December 31, 2020.
group 1.
------------------------------------------------------------------------
* * * * *
[FR Doc. 2018-04193 Filed 2-28-18; 8:45 am]
BILLING CODE 6560-50-P