Azoxystrobin; Pesticide Tolerance, 25961-25966 [06-4157]
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Federal Register / Vol. 71, No. 85 / Wednesday, May 3, 2006 / Rules and Regulations
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Although listed in the index, some
The Congressional Review Act, 5
information is not publicly available,
U.S.C. 801 et seq., as added by the Small *
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i.e., CBI or other information whose
Business Regulatory Enforcement
disclosure is restricted by statute.
Fairness Act of 1996, generally provides Radish, roots ............................
0.1
Certain other material, such as
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that before a rule may take effect, the
copyrighted material, is not placed on
agency promulgating the rule must
Turnip, roots .............................
0.1 the Internet and will be publicly
submit a rule report, which includes a
available only in hard copy form.
*
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copy of the rule, to each House of the
Publicly available docket materials are
Congress and to the Comptroller General Vegetable, root and tuber,
available either electronically in
of the United States. EPA will submit a
leaves, Group 2 ....................
0.1 EDOCKET or in hard copy at the Public
report containing this rule and other
Information and Records Integrity
required information to the U.S. Senate, [FR Doc. 06–4158 Filed 5–2–06; 8:45 am]
Branch (PIRIB), Rm. 119, Crystal Mall
the U.S. House of Representatives, and
#2, 1801 S. Bell St., Arlington, VA. This
BILLING CODE 6560–50–S
the Comptroller General of the United
docket facility is open from 8:30 a.m. to
States prior to publication of this final
4 p.m., Monday through Friday,
rule in the Federal Register. This final
ENVIRONMENTAL PROTECTION
excluding legal holidays. The docket
rule is not a ‘‘major rule’’ as defined by
AGENCY
telephone number is (703) 305–5805.
5 U.S.C. 804(2).
• Important Note: OPP will be
40 CFR Part 180
moving to a new location the first week
List of Subjects in 40 CFR Part 180
of May 2006. As a result, from Friday,
[EPA–HQ–OPP–2005–0540; FRL–8063–2]
Environmental protection,
April 28 to Friday, May 5, 2006, the
Administrative practice and procedure,
OPP Regulatory Public Docket will NOT
Azoxystrobin; Pesticide Tolerance
Agricultural commodities, Pesticides
be accepting any deliveries at the
and pests, Reporting and recordkeeping AGENCY: Environmental Protection
Crystal Mall #2 address and this facility
Agency (EPA).
requirements.
will be closed to the public. Beginning
ACTION: Final rule.
Dated: April 24, 2006.
on May 8, 2006, the OPP Regulatory
Public Docket will reopen at 8:30 a.m.
Lois Rossi,
SUMMARY: This regulation establishes
and deliveries will be accepted in Rm.
Acting Director, Registration Division, Office
tolerances for combined residues of
S–4400, One Potomac Yard (South
of Pesticide Programs.
azoxystrobin, [methyl(E)-2-(2-(6-(2Building), 2777 S. Crystal Drive,
cyanophenoxy) pyrimidin-4-yloxy)
I Therefore, 40 CFR chapter I is
Arlington, VA 22202. The mail code for
phenyl)-3-methoxyacrylate] and the Zamended as follows:
isomer of azoxystrobin, [methyl(Z)-2-(2- the mailing address will change to
(7502P), but will otherwise remain the
PART 180—[AMENDED]
(6-(2-cyanophenoxy) pyrimidin-4same. The OPP Regulatory Public
yloxy)phenyl)-3 methoxyacrylate] in or
I 1. The authority citation for part 180
Docket telephone number and hours of
on Herb Subgroup 19A, fresh leaves;
continues to read as follows:
Herb Subgroup 19A, dried leaves; Spice operation will remain the same after the
move.
Authority: 21 U.S.C. 321(q), 346a and 371.
Subgroup 19B, except black pepper;
FOR FURTHER INFORMATION CONTACT:
Rapeseed, seed; Rapeseed, Indian;
I 2. Section 180.589 is amended in the
Barbara Madden, Registration Division
Mustard, Indian, seed; Mustard, field,
table to paragraph (a)(1) by revising the
(7505C), Office of Pesticide Programs,
seed; Mustard, seed; Flax, seed;
entry for strawberry, and in the table to
Environmental Protection Agency, 1200
Sunflower, seed; Safflower, seed;
paragraph (d) by revising the entries for;
Pennsylvania Ave., NW., Washington,
Crambe, seed. Interregional Research
beet, garden, roots; beet, sugar, roots;
Project Number 4 (IR–4) requested these DC 20460–0001; telephone number:
radish, roots; turnip, roots and
(703) 305–6463; e-mail address:
vegetables, root and tuber, leaves, group tolerances under the Federal Food,
madden.barbara@epa.gov.
Drug, and Cosmetic Act (FFDCA), as
2 in the table in paragraph (d):
amended by the Food Quality Protection SUPPLEMENTARY INFORMATION:
§ 180.589 Boscalid; tolerance for residues. Act of 1996 (FQPA).
I. General Information
(a) * * *
DATES: This regulation is effective May
3, 2006. Objections and requests for
A. Does this Action Apply to Me?
Parts per
hearings must be received on or before
Commodity
You may be potentially affected by
million
July 3, 2006.
this action if you are an agricultural
ADDRESSES: To submit a written
*
*
*
*
*
producer, food manufacturer, or
objection or hearing request follow the
pesticide manufacturer. Potentially
Strawberry ................................
4.5 detailed instructions as provided in
affected entities may include, but are
*
*
*
*
*
Unit VI. of the SUPPLEMENTARY
not limited to:
INFORMATION. EPA has established a
• Crop production (NAICS 111), e.g.,
docket for this action under Docket
agricultural workers; greenhouse,
*
*
*
*
*
identification (ID) number EPA–HQ–
nursery, and floriculture workers;
(d) * * *
OPP–2005–0540. All documents in the
farmers.
docket are listed on the regulations.gov
• Animal production (NAICS 112),
Parts per
Web site. (EDOCKET, EPA’s electronic
e.g., cattle ranchers and farmers, dairy
Commodity
million
public docket and comment system was cattle farmers, livestock farmers.
replaced on November 25, 2005, by an
• Food manufacturing (NAICS 311),
*
*
*
*
*
enhanced federal-wide electronic docket e.g., agricultural workers; farmers;
greenhouse, nursery, and floriculture
Beet, garden, roots ...................
0.1 management and comment system
Beet, sugar, roots .....................
0.1 located at https://www.regulations.gov.
workers; ranchers; pesticide applicators.
VIII. Congressional Review Act
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Federal Register / Vol. 71, No. 85 / Wednesday, May 3, 2006 / Rules and Regulations
• Pesticide manufacturing (NAICS
32532), e.g., agricultural workers;
commercial applicators; farmers;
greenhouse, nursery, and floriculture
workers; residential users.
This listing is not intended to be
exhaustive, but rather provides a guide
for readers regarding entities likely to be
affected by this action. Other types of
entities not listed in this unit could also
be affected. The North American
Industrial Classification System
(NAICS) codes have been provided to
assist you and others in determining
whether this action might apply to
certain entities. If you have any
questions regarding the applicability of
this action to a particular entity, consult
the person listed under FOR FURTHER
INFORMATION CONTACT.
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B. How Can I Access Electronic Copies
of this Document and Other Related
Information?
In addition to using EDOCKET (https://
www.epa.gov/edocket), you may access
this Federal Register document
electronically through the EPA Internet
under the ‘‘Federal Register’’ listings at
https://www.epa.gov/fedrgstr. A
frequently updated electronic version of
40 CFR part 180 is available at E-CFR
Beta Site Two at https://
www.gpoaccess.gov/ecfr. To access the
OPPTS Harmonized Guidelines
referenced in this document, go directly
to the guidelines at https://www.epa.gpo/
opptsfrs/home/guidelin.htm.
II. Background and Statutory Findings
In the Federal Register of March 8,
2006 (71 FR 11624) (FRL–7765–5), EPA
issued a notice pursuant to section
408(d)(3) of FFDCA, 21 U.S.C.
346a(d)(3), announcing the filing of a
pesticide petitions (PP 3E6637, 3E6749,
and 4E6823) by Interregional Research
Project #4 (IR–4), 681 US Highway #1
South, North Brunswick, NJ 08902–
3390. The petitions requested that 40
CFR 180.507 be amended by
establishing a tolerance for combined
residues of the fungicide azoxystrobin,
(methyl (E)-2-(2-[6-(2cyanophenoxy)pyrimidin-4yloxy]phenyl)-3-methoxyacrylate) and
the Z isomer of azoxystrobin, (methyl
(Z)-2-(2-[6-(2-cyanophenoxy)pyrimidin4-yloxy]phenyl)-3-methoxyacrylate), in
or on Herb Subgroup 19A, fresh leaves
at 50 parts per million (ppm) (PP
4E6823); Herb Subgroup 19A, dried
leaves at 260 ppm (PP 4E6823); Spice
Subgroup 19B, except black pepper at
38 ppm (PP 3E6637); Rapeseed, seed at
0.5 ppm (PP 3E6749); Rapeseed, Indian
at 0.5 ppm (PP 3E6749); Mustard,
Indian, seed at 0.5 ppm (PP 3E6749);
Mustard, field, seed at 0.5 ppm (PP
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3E6749); Mustard, seed at 0.5 ppm (PP
3E6749); Flax, seed at 0.5 ppm (PP
3E6749); Sunflower, seed at 0.5 ppm (PP
3E6749); Safflower, seed at 0.5 ppm (PP
3E6749); and Crambe, seed at 0.5 ppm
(PP 3E6749). That notice included a
summary of the petition prepared by
Syngenta, the registrant on behalf of the
Interregional Research Project Number 4
(IR–4). One comment was received on
the notice of filing. EPA’s response to
this comment is discussed in Unit IV.C.
EPA is also deleting the tolerance
established for coriander, leaves in
§ 180.507(a), since it is being replaced
by establishing the Herb Subgroup 19A
and Spice Subgroup 19B.
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....’’
EPA performs a number of analyses to
determine the risks from aggregate
exposure to pesticide residues. For
further discussion of the regulatory
requirements of section 408 of the
FFDCA and a complete description of
the risk assessment process, see https://
www.epa.gov/fedrgstr/EPA-PEST/1997/
November/Day-26/p30948.htm.
III. Aggregate Risk Assessment and
Determination of Safety
Consistent with section 408(b)(2)(D)
of FFDCA, 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,
consistent with section 408(b)(2) of
FFDCA, for tolerances for combined
residues of azoxystrobin, [methyl(E)-2(2-(6-(2-cyanophenoxy) pyrimidin-4yloxy) phenyl)-3-methoxyacrylate] and
the Z-isomer of azoxystrobin,
[methyl(Z)-2-(2-(6-(2-cyanophenoxy)
pyrimidin-4-yloxy)phenyl)-3
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methoxyacrylate] on Herb Subgroup
19A, fresh leaves at 50 ppm; Herb
Subgroup 19A, dried leaves at 260 ppm;
Spice Subgroup 19B, except black
pepper at 38 ppm; rapeseed, seed at 0.5
ppm; Rapeseed, Indian at 0.5 ppm;
Mustard, Indian, seed at 0.5 ppm;
Mustard, field, seed at 0.5 ppm;
Mustard, seed at 0.5 ppm; Flax, seed at
0.5 ppm; Sunflower, seed at 0.5 ppm;
Safflower, seed at 0.5 ppm; and Crambe,
seed at 0.5 ppm. EPA’s assessment of
exposures and risks associated with
establishing the tolerance 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. Specific
information on the studies received and
the nature of the toxic effects caused by
azoxystrobin 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.epa.gov/
fedrgstr/EPA-PEST/2000/September/
Day-29/p25051.htm
B. Toxicological Endpoints
For hazards that have a threshold
below which there is no appreciable
risk, the dose at which no adverse
effects are observed (the NOAEL) from
the toxicology study identified as
appropriate for use in risk assessment is
used to estimate the toxicological level
of concern (LOC). However, the lowest
dose at which adverse effects of concern
are identified (the LOAEL) is sometimes
used for risk assessment if no NOAEL
was achieved in the toxicology study
selected. An uncertainty factor (UF) is
applied to reflect uncertainties inherent
in the extrapolation from laboratory
animal data to humans and in the
variations in sensitivity among members
of the human population as well as
other unknowns.
The linear default risk methodology
(Q*) is the primary method currently
used by the Agency to quantify nonthreshold hazards such as cancer. The
Q* approach assumes that any amount
of exposure will lead to some degree of
cancer risk, estimates risk in terms of
the probability of occurrence of
additional cancer cases. More
information can be found on the general
principles EPA uses in risk
characterization at https://www.epa.gov/
pesticides/health/human.htm.
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A summary of the toxicological
endpoints for azoxystrobin used for
human risk assessment is discussed in
Unit III.B. of the final rule published in
the Federal Register of September 29,
2000 (65 FR 58404) (FRL–6749–1).
C. Exposure Assessment
1. Dietary exposure from food and
feed uses. Tolerances have been
established (40 CFR 180.507) for the
combined residues of azoxystrobin,
(methyl (E)-2-(2-[6-(2cyanophenoxy)pyrimidin-4yloxy]phenyl-3-methoxyacrylate) and
the Z isomer of azoxystrobin, (methyl
(Z)-2-(2-[6-(2-cyanophenoxy)pyrimidin4-yloxy]phenyl)-3-methoxyacrylate), in
or on a variety of raw agricultural
commodities. In addition, tolerances for
livestock commodities have been
established for the residues of
azoxystrobin (methyl(E)-2-(2-(6-(2cyanophenoxy)pyrimidin-4yloxy)phenyl)-3-methoxyacrylate) in or
on milk; meat, fat, and meat byproducts
(mbyp) of cattle, goat, hog, horse, and
sheep. Risk assessments were conducted
by EPA to assess dietary exposures from
azoxystrobin 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.
In conducting the acute dietary
exposure assessment, EPA used the
Dietary Exposure Evaluation Model
software with the Food Commodity
Intake Database (DEEM-FCIDTM,
Version 2.03), which incorporates food
consumption data as reported by
respondents in the United States
Department of Agriculture (USDA)
1994–1996 and 1998 nationwide
Continuing Surveys of Food Intake by
Individuals (CSFII), and accumulated
exposure to the chemical for each
commodity. The following assumptions
were made for the acute exposure
assessments: One hundred percent of
proposed and registered crops are
treated with azoxystrobin (100% CT)
and tolerance-level residues for all
commodities.
ii. Chronic exposure. In conducting
the chronic dietary exposure
assessment, EPA used the DEEMFCIDTM, Version 2.03, which
incorporates food consumption data as
reported by respondents in the USDA
1994–1996 and 1998 nationwide CSFII,
and accumulated exposure to the
chemical for each commodity. The
following assumptions were made for
the chronic exposure assessments: One
hundred percent of proposed and
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registered crops are treated with
azoxystrobin (100% CT) and tolerancelevel residues for all commodities.
iii. Cancer. Azoxystrobin is classified
as ‘‘not likely to be a human
carcinogen.’’ Therefore, a cancer dietary
exposure assessment was not
performed.
2. Dietary exposure from drinking
water. The Agency lacks sufficient
monitoring exposure data to complete a
comprehensive dietary exposure
analysis and risk assessment for
azoxystrobin in drinking water. Because
the Agency does not have
comprehensive monitoring data,
drinking water concentration estimates
are made by reliance on simulation or
modeling taking into account data on
the physical characteristics of
azoxystrobin. 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 FQPA Index Reservoir
Screening Tool (FIRST) and screening
concentration in ground water (SCIGROW) models, the estimated
environmental concentrations (EECs) of
azoxystrobin for acute exposures are
estimated to be 170 parts per billion
(ppb) for surface water and 3.1 ppb for
ground water. The EECs for chronic
exposures are estimated to be 33 ppb for
surface water and 3.1 ppb for ground
water.
The drinking water estimates are
based upon the crop with the highest
application rate (turf). The use of
azoxystrobin on turf has the highest
single and yearly application rate at 0.55
pound/active ingredient/Acre (lb ai/A)
and 5 lb ai/A/year, respectively, this
application rate was used in the FIRST
and SCI-GROW models to estimate the
concentrations of this chemical in
surface water and ground water,
respectively.
Modeled estimates of drinking water
concentrations were directly entered
into the dietary exposure model (DEEMFCIDTM). For acute dietary risk
assessment, the peak water
concentration value of 107 ppb was
used to access the contribution to
drinking water. For chronic dietary risk
assessment, the annual average
concentration of 33 ppb was used to
access the contribution to drinking
water.
3. From non-dietary exposure. The
term ‘‘residential exposure’’ is used in
this document to refer to nonoccupational, non-dietary exposure
(e.g., for lawn and garden pest control,
indoor pest control, termiticides, and
flea and tick control on pets).
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25963
Azoxystrobin is currently registered
for use on the following residential nondietary sites: Residential turfgrass and
ornamentals, as well as indoor surfaces.
The risk assessment was conducted
using the following residential exposure
assumptions:
Residential handlers may receive
short-term dermal and inhalation
exposure to azoxystrobin when mixing,
loading and applying the formulations.
Adults and children may be exposed to
azoxystrobin residues from dermal
contact with foliage/surfaces during
post-application activities. Toddlers
may receive short- and intermediateterm oral exposure from incidental
ingestion during post-application
activities.
Inhalation daily doses for residential
handlers were calculated for the WDG
formulation using data for mixing,
loading and applying a liquid. Based on
PHED, unit exposure values from other
handler scenarios with these
formulation types, the exposure from a
WDG is expected to be less than that of
handling a liquid. The open mixing,
loading, and applying liquid using a low
pressure handwand (PHED) handler
scenario was evaluated. The residential
exposure and risk assessment for turf
and ornamentals was conducted using
the application rate for turf because it is
the highest use rate.
Exposures were estimated for
residential handler activities including:
Mix, load and spot application of liquid
formulation (low-pressure hand
sprayer), and mix, load and broadcast
application of liquid formulation
(garden hose-end sprayer). In addition,
short-term exposures were estimated for
infants and children for post-application
exposure scenarios resulting from
indoor surface treatment including:
Toddlers’ incidental ingestion of
pesticide residues on hard indoor
surfaces from hand-to-mouth transfer,
and toddlers’ incidental ingestion of
pesticide residues on carpet/textile
indoor surfaces from hand-to-mouth
transfer. Intermediate-term exposures
were also estimated for infants and
children for residential post-application
oral exposures.
The exposure estimates are based on
some upper-percentile (i.e., maximum
application rate, initial amount of
transferrable residue and duration of
exposure) and some central tendency
(i.e., surface area, hand-to-mouth
activity, and body weight) assumptions
and are considered to be representative
of high-end exposures. The
uncertainties associated with this
assessment stem from the use of an
assumed amount of pesticide available
from turf, and assumptions regarding
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transfer of chemical residues and handto mouth activity. The estimated
exposures are believed to be reasonable
high-end estimates.
4. Cumulative effects from substances
with a common mechanism of toxicity.
Section 408(b)(2)(D)(v) of the 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.’’
Unlike other pesticides for which EPA
has followed a cumulative risk approach
based on a common mechanism of
toxicity, EPA has not made a common
mechanism of toxicity finding as to
azoxystrobin and any other substances
and azoxystrobin does not appear to
produce a toxic metabolite produced by
other substances. For the purposes of
this tolerance action, therefore, EPA has
not assumed that azoxystrobin has 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 the policy statements
released by EPA’s Office of Pesticide
Programs concerning common
mechanism determinations and
procedures for cumulating effects from
substances found to have a common
mechanism on EPA’s Web site at https://
www.epa.gov/pesticides/cumulative.
D. Safety Factor for Infants and
Children
1. In general. Section 408 of FFDCA
provides that EPA shall apply an
additional tenfold 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 data base on
toxicity and exposure unless EPA
determines based on reliable data that a
different margin of safety will be safe for
infants and children. Margins of safety
are incorporated into EPA risk
assessments either directly through use
of a MOE analysis or through using
uncertainty (safety) factors in
calculating a dose level that poses no
appreciable risk to humans. In applying
this provision, EPA either retains the
default value of 10X when reliable data
do not support the choice of a different
factor, or, if reliable data are available,
EPA uses a different additional safety
factor value based on the use of
traditional uncertainty factors and/or
special FQPA safety factors, as
appropriate.
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2. Prenatal and postnatal sensitivity.
The developmental and reproductive
toxicity data, from a Prenatal
Development Study in Rats, a Prenatal
Development Study in Rabbits, and a 2–
Generation Reproductive Toxicity Study
in Rats, did not indicate increased
susceptibility of young rats or rabbits to
in utero and/or postnatal exposure.
3. Conclusion. There is a complete
toxicity database for azoxystrobin and
exposure data are complete or are
estimated based on data that reasonably
account for potential exposures. The
Agency has determined that the 10X
FQPA safety factor to protect infants
and children should be removed (that is,
set to 1) because, in addition to the
completeness of the toxicological
database and the lack of increased
susceptibility of young rats and rabbits
to pre- and postnatal exposure to
azoxystrobin, the unrefined acute and
chronic dietary exposure estimates will
overestimate dietary exposure from
food, and ground water and surface
water modeling data produce upperbound concentration estimates. The
residential post-application assessment
is based upon the residential standard
operational procedures (SOPs). The
assessment is based upon surrogate
study data. These data are reliable and
are not expected to underestimate risk
to adults or children. The residential
SOPs are based upon reasonable ‘‘worstcase’’ assumptions and are not expected
to underestimate risk.
E. Aggregate Risks and Determination of
Safety
The Agency currently has two ways to
estimate total aggregate exposure to a
pesticide from food, drinking water, and
residential uses. First, a screening
assessment can be used, in which the
Agency calculates drinking water levels
of comparison (DWLOCs) which are
used as a point of comparison against
estimated drinking water concentrations
(EDWCs). The DWLOC values are not
regulatory standards for drinking water,
but are theoretical upper limits on a
pesticide’s concentration in drinking
water in light of total aggregate exposure
to a pesticide in food and residential
uses. More information on the use of
DWLOCs in dietary aggregate risk
assessments can be found at https://
www.epa.gov/oppfead1/trac/science/
screeningsop.pdf.
More recently the Agency has used
another approach to estimate aggregate
exposure through food, residential and
drinking water pathways. In this
approach, modeled surface water and
ground water EDWCs are directly
incorporated into the dietary exposure
analysis, along with food. This provides
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a more realistic estimate of exposure
because actual body weights and water
consumption from the CSFII are used.
The combined food and water exposures
are then added to estimated exposure
from residential sources to calculate
aggregate risks. The resulting exposure
and risk estimates are still considered to
be high end, due to the assumptions
used in developing drinking water
modeling inputs.
1. Acute risk. Using the exposure
assumptions discussed in this unit for
acute exposure, the acute dietary
exposure from food and water to
azoxystrobin will occupy 27% of the
aPAD for the U.S. population, 24% of
the aPAD for females 13 years and older,
23% of the aPAD for infants (<1 year
old), and 74% of the aPAD for children
1–2 years old, the subpopulation at
greatest exposure. Therefore, EPA does
not expect the aggregate exposure to
exceed 100% of the aPAD.
2. Chronic risk. Using the exposure
assumptions described in this unit for
chronic exposure, EPA has concluded
that exposure to azoxystrobin from food
and water will utilize 28% of the cPAD
for the U.S. population, 19% of the
cPAD for All infants (<1 year old), and
70% of the cPAD for children 1–2 years
old, the subpopulation at greatest
exposure. Based on the use pattern,
chronic residential exposure to residues
of azoxystrobin is not expected.
Therefore, EPA does not expect the
aggregate exposure to exceed 100% of
the cPAD.
3. Short-term risk. Short-term
aggregate exposure takes into account
residential exposure plus chronic
exposure to food and water (considered
to be a background exposure level).
Azoxystrobin is currently registered for
use that could result in short-term
residential exposure and the Agency has
determined that it is appropriate to
aggregate chronic food, water and shortterm exposures for azoxystrobin.
Using the exposure assumptions
described in this unit for short-term
exposures, EPA has concluded that
food, water and residential exposures
aggregated result in aggregate MOEs of
500 for the U.S. population, 550 for
youth 13–19 years old, 200 for all
infants less than 1 year old, 120 for
children 1 to 2 years old and 580 for
females 13–49 years old. These
aggregate MOEs do not exceed the
Agency’s level of concern, a MOE of
100, for aggregate exposure to food,
water and residential uses.
4. Intermediate-term risk.
Intermediate-term aggregate exposure
takes into account residential exposure
plus chronic exposure to food and water
(considered to be a background
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Federal Register / Vol. 71, No. 85 / Wednesday, May 3, 2006 / Rules and Regulations
exposure level) of the risk from food and
water, which do not exceed the
Agency’s level of concern. Azoxystrobin
is currently registered for use(s) that
could result in intermediate-term
residential exposure and the Agency has
determined that it is appropriate to
aggregate chronic food, water and
intermediate-term exposures for
azoxystrobin.
Using the exposure assumptions
described in this unit for intermediateterm exposures, EPA has concluded that
food, water and residential exposures
aggregated result in aggregate MOEs of
120 for children 1 to 2 years old. These
aggregate MOEs do not exceed the
Agency’s level of concern, a MOE of
100, for aggregate exposure to food,
water and residential uses.
5. Aggregate cancer risk for U.S.
population. Azoxystrobin has been
classified as not likely to be
carcinogenic to humans. Therefore,
azoxystrobin is expected to pose at most
a negligible cancer risk.
6. Determination of safety. Based on
these risk assessments, EPA concludes
that there is a reasonable certainty that
no harm will result to the general
population, and to infants and children
from aggregate exposure to azoxystrobin
residues.
IV. Other Considerations
A. Analytical Enforcement Methodology
Adequate methodology is available for
enforcement of these tolerances. The gas
chromatography/nitrogen phosphorous
detector (GC/NPD) method (RAM 243/
04) has undergone a method validation
by the EPA analytical laboratory. EPA
comments have been incorporated and
the revised method (designated RAM
243) will be submitted to FDA for
inclusion in PAM, Volume II as an
enforcement method. 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; e-mail address:
residuemethods@epa.gov.
B. International Residue Limits
There are no Codex, Canadian, or
Mexican MRLs for azoxystrobin in or on
the proposed commodities. Therefore,
harmonization of tolerances is not an
issue.
sroberts on PROD1PC70 with RULES
C. Response to Comments
One comment was received from a
private citizen who opposed the
manufacturing and selling of this
product due to potential effects on the
environment. This comment is
considered irrelevant because the safety
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18:14 May 02, 2006
Jkt 208001
standard for approving tolerances under
section 408 of the FFDCA focuses on
potential harms to human health and
does not permit consideration of effects
on the environment.
V. Conclusion
Therefore, tolerances are established
for combined residues of azoxystrobin,
[methyl(E)-2-(2-(6-(2-cyanophenoxy)
pyrimidin-4-yloxy) phenyl)-3methoxyacrylate] and the Z-isomer of
azoxystrobin, [methyl(Z)-2-(2-(6-(2cyanophenoxy) pyrimidin-4yloxy)phenyl)-3 methoxyacrylate] on
Herb Subgroup 19A, fresh leaves at 50
ppm; Herb Subgroup 19A, dried leaves
at 260 ppm; Spice Subgroup 19B, except
black pepper at 38 ppm; Rapeseed, seed
at 0.5 ppm; Rapeseed, Indian at 0.5
ppm; Mustard, Indian, seed at 0.5 ppm;
Mustard, field, seed at 0.5 ppm;
Mustard, seed at 0.5 ppm; Flax, seed at
0.5 ppm; Sunflower, seed at 0.5 ppm;
Safflower, seed at 0.5 ppm; and Crambe,
seed at 0.5 ppm.
VI. Objections and Hearing Requests
Under section 408(g) of FFDCA, as
amended by FQPA, any person may file
an objection to any aspect of this
regulation and may also request a
hearing on those objections. The EPA
procedural regulations which govern the
submission of objections and requests
for hearings appear in 40 CFR part 178.
Although the procedures in those
regulations require some modification to
reflect the amendments made to FFDCA
by FQPA, EPA will continue to use
those procedures, with appropriate
adjustments, until the necessary
modifications can be made. The new
section 408(g) of FFDCA provides
essentially the same process for persons
to ‘‘object’’ to a regulation for an
exemption from the requirement of a
tolerance issued by EPA under new
section 408(d) of FFDCA, as was
provided in the old sections 408 and
409 of FFDCA. However, the period for
filing objections is now 60 days, rather
than 30 days.
A. What Do I Need to Do to File an
Objection or Request a Hearing?
You must file your objection or
request a hearing on this regulation in
accordance with the instructions
provided in this unit and in 40 CFR part
178. To ensure proper receipt by EPA,
you must identify docket ID number
EPA–HQ–OPP–2005–0540 in the subject
line on the first page of your
submission. All requests must be in
writing, and must be mailed or
delivered to the Hearing Clerk on or
before July 3, 2006.
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Fmt 4700
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25965
1. Filing the request. Your objection
must specify the specific provisions in
the regulation that you object to, and the
grounds for the objections (40 CFR
178.25). If a hearing is requested, the
objections must include a statement of
the factual issue(s) on which a hearing
is requested, the requestor’s contentions
on such issues, and a summary of any
evidence relied upon by the objector (40
CFR 178.27). Information submitted in
connection with an objetion or hearing
request may be claimed confidential by
marking any part or all of that
information as CBI. Information so
marked will not be disclosed except in
accordance with procedures set forth in
40 CFR part 2. A copy of the
information that does not contain CBI
must be submitted for inclusion in the
public record. Information not marked
confidential may be disclosed publicly
by EPA without prior notice.
Mail your written request to: Office of
the Hearing Clerk (1900L),
Environmental Protection Agency, 1200
Pennsylvania Ave., NW., Washington,
DC 20460–0001. You may also deliver
your request to the Office of the Hearing
Clerk in Suite 350, 1099 14th St., NW.,
Washington, DC 20005. The Office of
the Hearing Clerk is open from 8 a.m.
to 4 p.m., Monday through Friday,
excluding legal holidays. The telephone
number for the Office of the Hearing
Clerk is (202) 564–6255.
2. Copies for the Docket. In addition
to filing an objection or hearing request
with the Hearing Clerk as described in
Unit VI.A., you should also send a copy
of your request to the PIRIB for its
inclusion in the official record that is
described in ADDRESSES. Mail your
copies, identified by docket ID number
EPA–HQ–OPP–2005–0540, to: Public
Information and Records Integrity
Branch, Information Technology and
Resource Management Division (7502C),
Office of Pesticide Programs,
Environmental Protection Agency, 1200
Pennsylvania Ave., NW., Washington,
DC 20460–0001. In person or by courier,
bring a copy to the location of the PIRIB
described in ADDRESSES.
B. When Will the Agency Grant a
Request for a Hearing?
A request for a hearing will be granted
if the Administrator determines that the
material submitted shows the following:
There is a genuine and substantial issue
of fact; there is a reasonable possibility
that available evidence identified by the
requestor would, if established resolve
one or more of such issues in favor of
the requestor, taking into account
uncontested claims or facts to the
contrary; and resolution of the factual
issue(s) in the manner sought by the
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Federal Register / Vol. 71, No. 85 / Wednesday, May 3, 2006 / Rules and Regulations
sroberts on PROD1PC70 with RULES
requestor would be adequate to justify
the action requested (40 CFR 178.32).
VII. Statutory and Executive Order
Reviews
This final rule establishes a tolerance
under section 408(d) of FFDCA 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 rule has
been exempted from review under
Executive Order 12866 due to its lack of
significance, this rule is not subject to
Executive Order 13211, Actions
Concerning Regulations That
Significantly Affect Energy Supply,
Distribution, or Use (66 FR 28355, May
22, 2001). This final rule does not
contain any information collections
subject to OMB approval under the
Paperwork Reduction Act (PRA), 44
U.S.C. 3501 et seq., or impose any
enforceable duty or contain any
unfunded mandate as described under
Title II of the Unfunded Mandates
Reform Act of 1995 (UMRA) (Public
Law 104–4). 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); or OMB review or any Agency
action under Executive Order 13045,
entitled Protection of Children from
Environmental Health Risks and Safety
Risks (62 FR 19885, April 23, 1997).
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 of 1995
(NTTAA), Public Law 104–113, section
12(d) (15 U.S.C. 272 note). Since
tolerances and exemptions that are
established on the basis of a petition
under section 408(d) of FFDCA, such as
the tolerance in this final rule, do not
require the issuance of a proposed rule,
the requirements of the Regulatory
Flexibility Act (RFA) (5 U.S.C. 601 et
seq.) do not apply. In addition, the
Agency has determined that this action
will not have a substantial direct effect
on States, on the relationship between
the national government and the States,
or on the distribution of power and
responsibilities among the various
levels of government, as specified in
Executive Order 13132, entitled
Federalism (64 FR 43255, August 10,
1999). Executive Order 13132 requires
EPA to develop an accountable process
to ensure ‘‘meaningful and timely input
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18:14 May 02, 2006
Jkt 208001
by State and local officials in the
development of regulatory policies that
have federalism implications.’’ ‘‘Policies
that have federalism implications’’ is
defined in the Executive order to
include regulations that have
‘‘substantial direct effects on the States,
on the relationship between the national
government and the States, or on the
distribution of power and
responsibilities among the various
levels of government.’’ This final rule
directly regulates growers, food
processors, food handlers and food
retailers, not States. This action does not
alter the relationships or distribution of
power and responsibilities established
by Congress in the preemption
provisions of section 408(n)(4) of
FFDCA. For these same reasons, the
Agency has determined that this rule
does not have any ‘‘tribal implications’’
as described in Executive Order 13175,
entitled Consultation and Coordination
with Indian Tribal Governments (65 FR
67249, November 6, 2000). Executive
Order 13175, requires EPA to develop
an accountable process to ensure
‘‘meaningful and timely input by tribal
officials in the development of
regulatory policies that have tribal
implications.’’ ‘‘Policies that have tribal
implications’’ is defined in the
Executive order to include regulations
that have ‘‘substantial direct effects on
one or more Indian tribes, on the
relationship between the Federal
Government and the Indian tribes, or on
the distribution of power and
responsibilities between the Federal
Government and Indian tribes.’’ This
rule will not have substantial direct
effects on tribal governments, on the
relationship between the Federal
Government and Indian tribes, or on the
distribution of power and
responsibilities between the Federal
Government and Indian tribes, as
specified in Executive Order 13175.
Thus, Executive Order 13175 does not
apply to this rule.
VIII. Congressional Review Act
The Congressional Review Act, 5
U.S.C. 801 et seq., as added by the Small
Business Regulatory Enforcement
Fairness Act of 1996, generally provides
that before a rule may take effect, the
agency promulgating the rule must
submit a rule report, which includes a
copy of the rule, to each House of the
Congress and to the Comptroller General
of the United States. 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 this final
rule in the Federal Register. This final
PO 00000
Frm 00048
Fmt 4700
Sfmt 4700
rule 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: April 25, 2006.
Lois Rossi,
Director, Registration Division, Office of
Pesticide Programs.
Therefore, 40 CFR chapter I is
amended as follows:
I
PART 180—[AMENDED]
1. The authority citation for part 180
continues to read as follows:
I
Authority: 21 U.S.C. 321(q), 346a and 371.
2. Section 180.507 is amended by
deleting the entries for ‘‘Herb subgroup
19A, dried, except chive,’’ and ‘‘Herb
subgroup 19A, fresh, except chive,’’ and
by alphabetically adding the following
commodities to the table in paragraph
(a) to read as follows:
I
§ 180.507
(a) *
Azoxystrobin.
* *
Commodity
Parts per million
*
*
*
Crambe, seed .................
*
*
*
Flax, seed .......................
*
*
*
Herb Subgroup 19A,
dried leaves .................
Herb Subgroup 19A,
fresh leaves .................
*
*
*
Mustard, field, seed ........
Mustard, Indian, seed .....
Mustard, seed .................
*
*
*
Rapeseed, Indian ...........
Rapeseed, seed .............
*
*
*
Safflower, seed ...............
*
*
*
Spice Subgroup 19B, except black pepper .......
*
*
*
Sunflower, seed ..............
*
*
*
*
*
*
*
*
*
*
*
*
*
0.5
0.5
260
50
*
*
0.5
0.5
0.5
*
*
0.5
0.5
*
*
*
*
*
*
*
*
0.5
38
0.5
*
[FR Doc. 06–4157 Filed 5–2–06; 8:45 am]
BILLING CODE 6560–50–S
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Agencies
[Federal Register Volume 71, Number 85 (Wednesday, May 3, 2006)]
[Rules and Regulations]
[Pages 25961-25966]
From the Federal Register Online via the Government Printing Office [www.gpo.gov]
[FR Doc No: 06-4157]
-----------------------------------------------------------------------
ENVIRONMENTAL PROTECTION AGENCY
40 CFR Part 180
[EPA-HQ-OPP-2005-0540; FRL-8063-2]
Azoxystrobin; Pesticide Tolerance
AGENCY: Environmental Protection Agency (EPA).
ACTION: Final rule.
-----------------------------------------------------------------------
SUMMARY: This regulation establishes tolerances for combined residues
of azoxystrobin, [methyl(E)-2-(2-(6-(2-cyanophenoxy) pyrimidin-4-yloxy)
phenyl)-3-methoxyacrylate] and the Z-isomer of azoxystrobin,
[methyl(Z)-2-(2-(6-(2-cyanophenoxy) pyrimidin-4-yloxy)phenyl)-3
methoxyacrylate] in or on Herb Subgroup 19A, fresh leaves; Herb
Subgroup 19A, dried leaves; Spice Subgroup 19B, except black pepper;
Rapeseed, seed; Rapeseed, Indian; Mustard, Indian, seed; Mustard,
field, seed; Mustard, seed; Flax, seed; Sunflower, seed; Safflower,
seed; Crambe, seed. Interregional Research Project Number 4 (IR-4)
requested these tolerances under the Federal Food, Drug, and Cosmetic
Act (FFDCA), as amended by the Food Quality Protection Act of 1996
(FQPA).
DATES: This regulation is effective May 3, 2006. Objections and
requests for hearings must be received on or before July 3, 2006.
ADDRESSES: To submit a written objection or hearing request follow the
detailed instructions as provided in Unit VI. of the SUPPLEMENTARY
INFORMATION. EPA has established a docket for this action under Docket
identification (ID) number EPA-HQ-OPP-2005-0540. All documents in the
docket are listed on the regulations.gov Web site. (EDOCKET, EPA's
electronic public docket and comment system was replaced on November
25, 2005, by an enhanced federal-wide electronic docket management and
comment system located at https://www.regulations.gov. Follow the on-
line instructions.) Although listed in the index, some information is
not publicly available, i.e., CBI or other information whose disclosure
is restricted by statute. Certain other material, such as copyrighted
material, is not placed on the Internet and will be publicly available
only in hard copy form. Publicly available docket materials are
available either electronically in EDOCKET or in hard copy at the
Public Information and Records Integrity Branch (PIRIB), Rm. 119,
Crystal Mall 2, 1801 S. Bell St., Arlington, VA. This docket
facility is open from 8:30 a.m. to 4 p.m., Monday through Friday,
excluding legal holidays. The docket telephone number is (703) 305-
5805.
Important Note: OPP will be moving to a new location the
first week of May 2006. As a result, from Friday, April 28 to Friday,
May 5, 2006, the OPP Regulatory Public Docket will NOT be accepting any
deliveries at the Crystal Mall 2 address and this facility
will be closed to the public. Beginning on May 8, 2006, the OPP
Regulatory Public Docket will reopen at 8:30 a.m. and deliveries will
be accepted in Rm. S-4400, One Potomac Yard (South Building), 2777 S.
Crystal Drive, Arlington, VA 22202. The mail code for the mailing
address will change to (7502P), but will otherwise remain the same. The
OPP Regulatory Public Docket telephone number and hours of operation
will remain the same after the move.
FOR FURTHER INFORMATION CONTACT: Barbara Madden, Registration Division
(7505C), Office of Pesticide Programs, Environmental Protection Agency,
1200 Pennsylvania Ave., NW., Washington, DC 20460-0001; telephone
number: (703) 305-6463; e-mail address: madden.barbara@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.
Potentially affected entities may include, but are not limited to:
Crop production (NAICS 111), e.g., agricultural workers;
greenhouse, nursery, and floriculture workers; farmers.
Animal production (NAICS 112), e.g., cattle ranchers and
farmers, dairy cattle farmers, livestock farmers.
Food manufacturing (NAICS 311), e.g., agricultural
workers; farmers; greenhouse, nursery, and floriculture workers;
ranchers; pesticide applicators.
[[Page 25962]]
Pesticide manufacturing (NAICS 32532), e.g., agricultural
workers; commercial applicators; farmers; greenhouse, nursery, and
floriculture workers; residential users.
This listing is not intended to be exhaustive, but rather provides
a guide for readers regarding entities likely to be affected by this
action. Other types of entities not listed in this unit could also be
affected. The North American Industrial Classification System (NAICS)
codes have been provided to assist you and others in determining
whether this action might apply to certain entities. If you have any
questions regarding the applicability of this action to a particular
entity, consult the person listed under FOR FURTHER INFORMATION
CONTACT.
B. How Can I Access Electronic Copies of this Document and Other
Related Information?
In addition to using EDOCKET (https://www.epa.gov/edocket), you may
access this Federal Register document electronically through the EPA
Internet under the ``Federal Register'' listings at https://www.epa.gov/
fedrgstr. A frequently updated electronic version of 40 CFR part 180 is
available at E-CFR Beta Site Two at https://www.gpoaccess.gov/ecfr. To
access the OPPTS Harmonized Guidelines referenced in this document, go
directly to the guidelines at https://www.epa.gpo/opptsfrs/home/
guidelin.htm.
II. Background and Statutory Findings
In the Federal Register of March 8, 2006 (71 FR 11624) (FRL-7765-
5), EPA issued a notice pursuant to section 408(d)(3) of FFDCA, 21
U.S.C. 346a(d)(3), announcing the filing of a pesticide petitions (PP
3E6637, 3E6749, and 4E6823) by Interregional Research Project
4 (IR-4), 681 US Highway 1 South, North Brunswick, NJ
08902-3390. The petitions requested that 40 CFR 180.507 be amended by
establishing a tolerance for combined residues of the fungicide
azoxystrobin, (methyl (E)-2-(2-[6-(2-cyanophenoxy)pyrimidin-4-
yloxy]phenyl)-3-methoxyacrylate) and the Z isomer of azoxystrobin,
(methyl (Z)-2-(2-[6-(2-cyanophenoxy)pyrimidin-4-yloxy]phenyl)-3-
methoxyacrylate), in or on Herb Subgroup 19A, fresh leaves at 50 parts
per million (ppm) (PP 4E6823); Herb Subgroup 19A, dried leaves at 260
ppm (PP 4E6823); Spice Subgroup 19B, except black pepper at 38 ppm (PP
3E6637); Rapeseed, seed at 0.5 ppm (PP 3E6749); Rapeseed, Indian at 0.5
ppm (PP 3E6749); Mustard, Indian, seed at 0.5 ppm (PP 3E6749); Mustard,
field, seed at 0.5 ppm (PP 3E6749); Mustard, seed at 0.5 ppm (PP
3E6749); Flax, seed at 0.5 ppm (PP 3E6749); Sunflower, seed at 0.5 ppm
(PP 3E6749); Safflower, seed at 0.5 ppm (PP 3E6749); and Crambe, seed
at 0.5 ppm (PP 3E6749). That notice included a summary of the petition
prepared by Syngenta, the registrant on behalf of the Interregional
Research Project Number 4 (IR-4). One comment was received on the
notice of filing. EPA's response to this comment is discussed in Unit
IV.C.
EPA is also deleting the tolerance established for coriander,
leaves in Sec. 180.507(a), since it is being replaced by establishing
the Herb Subgroup 19A and Spice Subgroup 19B.
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....''
EPA performs a number of analyses to determine the risks from
aggregate exposure to pesticide residues. For further discussion of the
regulatory requirements of section 408 of the FFDCA and a complete
description of the risk assessment process, see https://www.epa.gov/
fedrgstr/EPA-PEST/1997/November/Day-26/p30948.htm.
III. Aggregate Risk Assessment and Determination of Safety
Consistent with section 408(b)(2)(D) of FFDCA, 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, consistent with section
408(b)(2) of FFDCA, for tolerances for combined residues of
azoxystrobin, [methyl(E)-2-(2-(6-(2-cyanophenoxy) pyrimidin-4-yloxy)
phenyl)-3-methoxyacrylate] and the Z-isomer of azoxystrobin,
[methyl(Z)-2-(2-(6-(2-cyanophenoxy) pyrimidin-4-yloxy)phenyl)-3
methoxyacrylate] on Herb Subgroup 19A, fresh leaves at 50 ppm; Herb
Subgroup 19A, dried leaves at 260 ppm; Spice Subgroup 19B, except black
pepper at 38 ppm; rapeseed, seed at 0.5 ppm; Rapeseed, Indian at 0.5
ppm; Mustard, Indian, seed at 0.5 ppm; Mustard, field, seed at 0.5 ppm;
Mustard, seed at 0.5 ppm; Flax, seed at 0.5 ppm; Sunflower, seed at 0.5
ppm; Safflower, seed at 0.5 ppm; and Crambe, seed at 0.5 ppm. EPA's
assessment of exposures and risks associated with establishing the
tolerance 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. Specific information on the studies received and the nature
of the toxic effects caused by azoxystrobin 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.epa.gov/fedrgstr/EPA-PEST/2000/September/Day-29/p25051.htm
B. Toxicological Endpoints
For hazards that have a threshold below which there is no
appreciable risk, the dose at which no adverse effects are observed
(the NOAEL) from the toxicology study identified as appropriate for use
in risk assessment is used to estimate the toxicological level of
concern (LOC). However, the lowest dose at which adverse effects of
concern are identified (the LOAEL) is sometimes used for risk
assessment if no NOAEL was achieved in the toxicology study selected.
An uncertainty factor (UF) is applied to reflect uncertainties inherent
in the extrapolation from laboratory animal data to humans and in the
variations in sensitivity among members of the human population as well
as other unknowns.
The linear default risk methodology (Q*) is the primary method
currently used by the Agency to quantify non-threshold hazards such as
cancer. The Q* approach assumes that any amount of exposure will lead
to some degree of cancer risk, estimates risk in terms of the
probability of occurrence of additional cancer cases. More information
can be found on the general principles EPA uses in risk
characterization at https://www.epa.gov/pesticides/health/human.htm.
[[Page 25963]]
A summary of the toxicological endpoints for azoxystrobin used for
human risk assessment is discussed in Unit III.B. of the final rule
published in the Federal Register of September 29, 2000 (65 FR 58404)
(FRL-6749-1).
C. Exposure Assessment
1. Dietary exposure from food and feed uses. Tolerances have been
established (40 CFR 180.507) for the combined residues of azoxystrobin,
(methyl (E)-2-(2-[6-(2-cyanophenoxy)pyrimidin-4-yloxy]phenyl-3-
methoxyacrylate) and the Z isomer of azoxystrobin, (methyl (Z)-2-(2-[6-
(2-cyanophenoxy)pyrimidin-4-yloxy]phenyl)-3-methoxyacrylate), in or on
a variety of raw agricultural commodities. In addition, tolerances for
livestock commodities have been established for the residues of
azoxystrobin (methyl(E)-2-(2-(6-(2-cyanophenoxy)pyrimidin-4-
yloxy)phenyl)-3-methoxyacrylate) in or on milk; meat, fat, and meat
byproducts (mbyp) of cattle, goat, hog, horse, and sheep. Risk
assessments were conducted by EPA to assess dietary exposures from
azoxystrobin 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.
In conducting the acute dietary exposure assessment, EPA used the
Dietary Exposure Evaluation Model software with the Food Commodity
Intake Database (DEEM-FCID\TM\, Version 2.03), which incorporates food
consumption data as reported by respondents in the United States
Department of Agriculture (USDA) 1994-1996 and 1998 nationwide
Continuing Surveys of Food Intake by Individuals (CSFII), and
accumulated exposure to the chemical for each commodity. The following
assumptions were made for the acute exposure assessments: One hundred
percent of proposed and registered crops are treated with azoxystrobin
(100% CT) and tolerance-level residues for all commodities.
ii. Chronic exposure. In conducting the chronic dietary exposure
assessment, EPA used the DEEM-FCID\TM\, Version 2.03, which
incorporates food consumption data as reported by respondents in the
USDA 1994-1996 and 1998 nationwide CSFII, and accumulated exposure to
the chemical for each commodity. The following assumptions were made
for the chronic exposure assessments: One hundred percent of proposed
and registered crops are treated with azoxystrobin (100% CT) and
tolerance-level residues for all commodities.
iii. Cancer. Azoxystrobin is classified as ``not likely to be a
human carcinogen.'' Therefore, a cancer dietary exposure assessment was
not performed.
2. Dietary exposure from drinking water. The Agency lacks
sufficient monitoring exposure data to complete a comprehensive dietary
exposure analysis and risk assessment for azoxystrobin in drinking
water. Because the Agency does not have comprehensive monitoring data,
drinking water concentration estimates are made by reliance on
simulation or modeling taking into account data on the physical
characteristics of azoxystrobin. 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 FQPA Index Reservoir Screening Tool (FIRST) and
screening concentration in ground water (SCI-GROW) models, the
estimated environmental concentrations (EECs) of azoxystrobin for acute
exposures are estimated to be 170 parts per billion (ppb) for surface
water and 3.1 ppb for ground water. The EECs for chronic exposures are
estimated to be 33 ppb for surface water and 3.1 ppb for ground water.
The drinking water estimates are based upon the crop with the
highest application rate (turf). The use of azoxystrobin on turf has
the highest single and yearly application rate at 0.55 pound/active
ingredient/Acre (lb ai/A) and 5 lb ai/A/year, respectively, this
application rate was used in the FIRST and SCI-GROW models to estimate
the concentrations of this chemical in surface water and ground water,
respectively.
Modeled estimates of drinking water concentrations were directly
entered into the dietary exposure model (DEEM-FCID\TM\). For acute
dietary risk assessment, the peak water concentration value of 107 ppb
was used to access the contribution to drinking water. For chronic
dietary risk assessment, the annual average concentration of 33 ppb was
used to access the contribution to drinking water.
3. From non-dietary exposure. The term ``residential exposure'' is
used in this document to refer to non-occupational, non-dietary
exposure (e.g., for lawn and garden pest control, indoor pest control,
termiticides, and flea and tick control on pets).
Azoxystrobin is currently registered for use on the following
residential non-dietary sites: Residential turfgrass and ornamentals,
as well as indoor surfaces. The risk assessment was conducted using the
following residential exposure assumptions:
Residential handlers may receive short-term dermal and inhalation
exposure to azoxystrobin when mixing, loading and applying the
formulations. Adults and children may be exposed to azoxystrobin
residues from dermal contact with foliage/surfaces during post-
application activities. Toddlers may receive short- and intermediate-
term oral exposure from incidental ingestion during post-application
activities.
Inhalation daily doses for residential handlers were calculated for
the WDG formulation using data for mixing, loading and applying a
liquid. Based on PHED, unit exposure values from other handler
scenarios with these formulation types, the exposure from a WDG is
expected to be less than that of handling a liquid. The open mixing,
loading, and applying liquid using a low pressure handwand (PHED)
handler scenario was evaluated. The residential exposure and risk
assessment for turf and ornamentals was conducted using the application
rate for turf because it is the highest use rate.
Exposures were estimated for residential handler activities
including: Mix, load and spot application of liquid formulation (low-
pressure hand sprayer), and mix, load and broadcast application of
liquid formulation (garden hose-end sprayer). In addition, short-term
exposures were estimated for infants and children for post-application
exposure scenarios resulting from indoor surface treatment including:
Toddlers' incidental ingestion of pesticide residues on hard indoor
surfaces from hand-to-mouth transfer, and toddlers' incidental
ingestion of pesticide residues on carpet/textile indoor surfaces from
hand-to-mouth transfer. Intermediate-term exposures were also estimated
for infants and children for residential post-application oral
exposures.
The exposure estimates are based on some upper-percentile (i.e.,
maximum application rate, initial amount of transferrable residue and
duration of exposure) and some central tendency (i.e., surface area,
hand-to-mouth activity, and body weight) assumptions and are considered
to be representative of high-end exposures. The uncertainties
associated with this assessment stem from the use of an assumed amount
of pesticide available from turf, and assumptions regarding
[[Page 25964]]
transfer of chemical residues and hand-to mouth activity. The estimated
exposures are believed to be reasonable high-end estimates.
4. Cumulative effects from substances with a common mechanism of
toxicity. Section 408(b)(2)(D)(v) of the 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.''
Unlike other pesticides for which EPA has followed a cumulative
risk approach based on a common mechanism of toxicity, EPA has not made
a common mechanism of toxicity finding as to azoxystrobin and any other
substances and azoxystrobin does not appear to produce a toxic
metabolite produced by other substances. For the purposes of this
tolerance action, therefore, EPA has not assumed that azoxystrobin has
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 the policy statements released by EPA's Office of
Pesticide Programs concerning common mechanism determinations and
procedures for cumulating effects from substances found to have a
common mechanism on EPA's Web site at https://www.epa.gov/pesticides/
cumulative.
D. Safety Factor for Infants and Children
1. In general. Section 408 of FFDCA provides that EPA shall apply
an additional tenfold 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 data base on toxicity and exposure
unless EPA determines based on reliable data that a different margin of
safety will be safe for infants and children. Margins of safety are
incorporated into EPA risk assessments either directly through use of a
MOE analysis or through using uncertainty (safety) factors in
calculating a dose level that poses no appreciable risk to humans. In
applying this provision, EPA either retains the default value of 10X
when reliable data do not support the choice of a different factor, or,
if reliable data are available, EPA uses a different additional safety
factor value based on the use of traditional uncertainty factors and/or
special FQPA safety factors, as appropriate.
2. Prenatal and postnatal sensitivity. The developmental and
reproductive toxicity data, from a Prenatal Development Study in Rats,
a Prenatal Development Study in Rabbits, and a 2-Generation
Reproductive Toxicity Study in Rats, did not indicate increased
susceptibility of young rats or rabbits to in utero and/or postnatal
exposure.
3. Conclusion. There is a complete toxicity database for
azoxystrobin and exposure data are complete or are estimated based on
data that reasonably account for potential exposures. The Agency has
determined that the 10X FQPA safety factor to protect infants and
children should be removed (that is, set to 1) because, in addition to
the completeness of the toxicological database and the lack of
increased susceptibility of young rats and rabbits to pre- and
postnatal exposure to azoxystrobin, the unrefined acute and chronic
dietary exposure estimates will overestimate dietary exposure from
food, and ground water and surface water modeling data produce upper-
bound concentration estimates. The residential post-application
assessment is based upon the residential standard operational
procedures (SOPs). The assessment is based upon surrogate study data.
These data are reliable and are not expected to underestimate risk to
adults or children. The residential SOPs are based upon reasonable
``worst-case'' assumptions and are not expected to underestimate risk.
E. Aggregate Risks and Determination of Safety
The Agency currently has two ways to estimate total aggregate
exposure to a pesticide from food, drinking water, and residential
uses. First, a screening assessment can be used, in which the Agency
calculates drinking water levels of comparison (DWLOCs) which are used
as a point of comparison against estimated drinking water
concentrations (EDWCs). The DWLOC values are not regulatory standards
for drinking water, but are theoretical upper limits on a pesticide's
concentration in drinking water in light of total aggregate exposure to
a pesticide in food and residential uses. More information on the use
of DWLOCs in dietary aggregate risk assessments can be found at https://
www.epa.gov/oppfead1/trac/science/screeningsop.pdf.
More recently the Agency has used another approach to estimate
aggregate exposure through food, residential and drinking water
pathways. In this approach, modeled surface water and ground water
EDWCs are directly incorporated into the dietary exposure analysis,
along with food. This provides a more realistic estimate of exposure
because actual body weights and water consumption from the CSFII are
used. The combined food and water exposures are then added to estimated
exposure from residential sources to calculate aggregate risks. The
resulting exposure and risk estimates are still considered to be high
end, due to the assumptions used in developing drinking water modeling
inputs.
1. Acute risk. Using the exposure assumptions discussed in this
unit for acute exposure, the acute dietary exposure from food and water
to azoxystrobin will occupy 27% of the aPAD for the U.S. population,
24% of the aPAD for females 13 years and older, 23% of the aPAD for
infants (<1 year old), and 74% of the aPAD for children 1-2 years old,
the subpopulation at greatest exposure. Therefore, EPA does not expect
the aggregate exposure to exceed 100% of the aPAD.
2. Chronic risk. Using the exposure assumptions described in this
unit for chronic exposure, EPA has concluded that exposure to
azoxystrobin from food and water will utilize 28% of the cPAD for the
U.S. population, 19% of the cPAD for All infants (<1 year old), and 70%
of the cPAD for children 1-2 years old, the subpopulation at greatest
exposure. Based on the use pattern, chronic residential exposure to
residues of azoxystrobin is not expected. Therefore, EPA does not
expect the aggregate exposure to exceed 100% of the cPAD.
3. Short-term risk. Short-term aggregate exposure takes into
account residential exposure plus chronic exposure to food and water
(considered to be a background exposure level). Azoxystrobin is
currently registered for use that could result in short-term
residential exposure and the Agency has determined that it is
appropriate to aggregate chronic food, water and short-term exposures
for azoxystrobin.
Using the exposure assumptions described in this unit for short-
term exposures, EPA has concluded that food, water and residential
exposures aggregated result in aggregate MOEs of 500 for the U.S.
population, 550 for youth 13-19 years old, 200 for all infants less
than 1 year old, 120 for children 1 to 2 years old and 580 for females
13-49 years old. These aggregate MOEs do not exceed the Agency's level
of concern, a MOE of 100, for aggregate exposure to food, water and
residential uses.
4. Intermediate-term risk. Intermediate-term aggregate exposure
takes into account residential exposure plus chronic exposure to food
and water (considered to be a background
[[Page 25965]]
exposure level) of the risk from food and water, which do not exceed
the Agency's level of concern. Azoxystrobin is currently registered for
use(s) that could result in intermediate-term residential exposure and
the Agency has determined that it is appropriate to aggregate chronic
food, water and intermediate-term exposures for azoxystrobin.
Using the exposure assumptions described in this unit for
intermediate-term exposures, EPA has concluded that food, water and
residential exposures aggregated result in aggregate MOEs of 120 for
children 1 to 2 years old. These aggregate MOEs do not exceed the
Agency's level of concern, a MOE of 100, for aggregate exposure to
food, water and residential uses.
5. Aggregate cancer risk for U.S. population. Azoxystrobin has been
classified as not likely to be carcinogenic to humans. Therefore,
azoxystrobin is expected to pose at most a negligible cancer risk.
6. Determination of safety. Based on these risk assessments, EPA
concludes that there is a reasonable certainty that no harm will result
to the general population, and to infants and children from aggregate
exposure to azoxystrobin residues.
IV. Other Considerations
A. Analytical Enforcement Methodology
Adequate methodology is available for enforcement of these
tolerances. The gas chromatography/nitrogen phosphorous detector (GC/
NPD) method (RAM 243/04) has undergone a method validation by the EPA
analytical laboratory. EPA comments have been incorporated and the
revised method (designated RAM 243) will be submitted to FDA for
inclusion in PAM, Volume II as an enforcement method. 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; e-mail address: residuemethods@epa.gov.
B. International Residue Limits
There are no Codex, Canadian, or Mexican MRLs for azoxystrobin in
or on the proposed commodities. Therefore, harmonization of tolerances
is not an issue.
C. Response to Comments
One comment was received from a private citizen who opposed the
manufacturing and selling of this product due to potential effects on
the environment. This comment is considered irrelevant because the
safety standard for approving tolerances under section 408 of the FFDCA
focuses on potential harms to human health and does not permit
consideration of effects on the environment.
V. Conclusion
Therefore, tolerances are established for combined residues of
azoxystrobin, [methyl(E)-2-(2-(6-(2-cyanophenoxy) pyrimidin-4-yloxy)
phenyl)-3-methoxyacrylate] and the Z-isomer of azoxystrobin,
[methyl(Z)-2-(2-(6-(2-cyanophenoxy) pyrimidin-4-yloxy)phenyl)-3
methoxyacrylate] on Herb Subgroup 19A, fresh leaves at 50 ppm; Herb
Subgroup 19A, dried leaves at 260 ppm; Spice Subgroup 19B, except black
pepper at 38 ppm; Rapeseed, seed at 0.5 ppm; Rapeseed, Indian at 0.5
ppm; Mustard, Indian, seed at 0.5 ppm; Mustard, field, seed at 0.5 ppm;
Mustard, seed at 0.5 ppm; Flax, seed at 0.5 ppm; Sunflower, seed at 0.5
ppm; Safflower, seed at 0.5 ppm; and Crambe, seed at 0.5 ppm.
VI. Objections and Hearing Requests
Under section 408(g) of FFDCA, as amended by FQPA, any person may
file an objection to any aspect of this regulation and may also request
a hearing on those objections. The EPA procedural regulations which
govern the submission of objections and requests for hearings appear in
40 CFR part 178. Although the procedures in those regulations require
some modification to reflect the amendments made to FFDCA by FQPA, EPA
will continue to use those procedures, with appropriate adjustments,
until the necessary modifications can be made. The new section 408(g)
of FFDCA provides essentially the same process for persons to
``object'' to a regulation for an exemption from the requirement of a
tolerance issued by EPA under new section 408(d) of FFDCA, as was
provided in the old sections 408 and 409 of FFDCA. However, the period
for filing objections is now 60 days, rather than 30 days.
A. What Do I Need to Do to File an Objection or Request a Hearing?
You must file your objection or request a hearing on this
regulation in accordance with the instructions provided in this unit
and in 40 CFR part 178. To ensure proper receipt by EPA, you must
identify docket ID number EPA-HQ-OPP-2005-0540 in the subject line on
the first page of your submission. All requests must be in writing, and
must be mailed or delivered to the Hearing Clerk on or before July 3,
2006.
1. Filing the request. Your objection must specify the specific
provisions in the regulation that you object to, and the grounds for
the objections (40 CFR 178.25). If a hearing is requested, the
objections must include a statement of the factual issue(s) on which a
hearing is requested, the requestor's contentions on such issues, and a
summary of any evidence relied upon by the objector (40 CFR 178.27).
Information submitted in connection with an objetion or hearing request
may be claimed confidential by marking any part or all of that
information as CBI. Information so marked will not be disclosed except
in accordance with procedures set forth in 40 CFR part 2. A copy of the
information that does not contain CBI must be submitted for inclusion
in the public record. Information not marked confidential may be
disclosed publicly by EPA without prior notice.
Mail your written request to: Office of the Hearing Clerk (1900L),
Environmental Protection Agency, 1200 Pennsylvania Ave., NW.,
Washington, DC 20460-0001. You may also deliver your request to the
Office of the Hearing Clerk in Suite 350, 1099 14th St., NW.,
Washington, DC 20005. The Office of the Hearing Clerk is open from 8
a.m. to 4 p.m., Monday through Friday, excluding legal holidays. The
telephone number for the Office of the Hearing Clerk is (202) 564-6255.
2. Copies for the Docket. In addition to filing an objection or
hearing request with the Hearing Clerk as described in Unit VI.A., you
should also send a copy of your request to the PIRIB for its inclusion
in the official record that is described in ADDRESSES. Mail your
copies, identified by docket ID number EPA-HQ-OPP-2005-0540, to: Public
Information and Records Integrity Branch, Information Technology and
Resource Management Division (7502C), Office of Pesticide Programs,
Environmental Protection Agency, 1200 Pennsylvania Ave., NW.,
Washington, DC 20460-0001. In person or by courier, bring a copy to the
location of the PIRIB described in ADDRESSES.
B. When Will the Agency Grant a Request for a Hearing?
A request for a hearing will be granted if the Administrator
determines that the material submitted shows the following: There is a
genuine and substantial issue of fact; there is a reasonable
possibility that available evidence identified by the requestor would,
if established resolve one or more of such issues in favor of the
requestor, taking into account uncontested claims or facts to the
contrary; and resolution of the factual issue(s) in the manner sought
by the
[[Page 25966]]
requestor would be adequate to justify the action requested (40 CFR
178.32).
VII. Statutory and Executive Order Reviews
This final rule establishes a tolerance under section 408(d) of
FFDCA 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 rule has been
exempted from review under Executive Order 12866 due to its lack of
significance, this rule is not subject to Executive Order 13211,
Actions Concerning Regulations That Significantly Affect Energy Supply,
Distribution, or Use (66 FR 28355, May 22, 2001). This final rule does
not contain any information collections subject to OMB approval under
the Paperwork Reduction Act (PRA), 44 U.S.C. 3501 et seq., or impose
any enforceable duty or contain any unfunded mandate as described under
Title II of the Unfunded Mandates Reform Act of 1995 (UMRA) (Public Law
104-4). 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); or OMB review or any Agency action under Executive
Order 13045, entitled Protection of Children from Environmental Health
Risks and Safety Risks (62 FR 19885, April 23, 1997). 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 of 1995
(NTTAA), Public Law 104-113, section 12(d) (15 U.S.C. 272 note). Since
tolerances and exemptions that are established on the basis of a
petition under section 408(d) of FFDCA, such as the tolerance in this
final rule, do not require the issuance of a proposed rule, the
requirements of the Regulatory Flexibility Act (RFA) (5 U.S.C. 601 et
seq.) do not apply. In addition, the Agency has determined that this
action will not have a substantial direct effect on States, on the
relationship between the national government and the States, or on the
distribution of power and responsibilities among the various levels of
government, as specified in Executive Order 13132, entitled Federalism
(64 FR 43255, August 10, 1999). Executive Order 13132 requires EPA to
develop an accountable process to ensure ``meaningful and timely input
by State and local officials in the development of regulatory policies
that have federalism implications.'' ``Policies that have federalism
implications'' is defined in the Executive order to include regulations
that have ``substantial direct effects on the States, on the
relationship between the national government and the States, or on the
distribution of power and responsibilities among the various levels of
government.'' This final rule directly regulates growers, food
processors, food handlers and food retailers, not States. This action
does not alter the relationships or distribution of power and
responsibilities established by Congress in the preemption provisions
of section 408(n)(4) of FFDCA. For these same reasons, the Agency has
determined that this rule does not have any ``tribal implications'' as
described in Executive Order 13175, entitled Consultation and
Coordination with Indian Tribal Governments (65 FR 67249, November 6,
2000). Executive Order 13175, requires EPA to develop an accountable
process to ensure ``meaningful and timely input by tribal officials in
the development of regulatory policies that have tribal implications.''
``Policies that have tribal implications'' is defined in the Executive
order to include regulations that have ``substantial direct effects on
one or more Indian tribes, on the relationship between the Federal
Government and the Indian tribes, or on the distribution of power and
responsibilities between the Federal Government and Indian tribes.''
This rule will not have substantial direct effects on tribal
governments, on the relationship between the Federal Government and
Indian tribes, or on the distribution of power and responsibilities
between the Federal Government and Indian tribes, as specified in
Executive Order 13175. Thus, Executive Order 13175 does not apply to
this rule.
VIII. Congressional Review Act
The Congressional Review Act, 5 U.S.C. 801 et seq., as added by the
Small Business Regulatory Enforcement Fairness Act of 1996, generally
provides that before a rule may take effect, the agency promulgating
the rule must submit a rule report, which includes a copy of the rule,
to each House of the Congress and to the Comptroller General of the
United States. 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 this final rule in the Federal Register. This final
rule 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: April 25, 2006.
Lois Rossi,
Director, Registration Division, Office of Pesticide Programs.
0
Therefore, 40 CFR chapter I is amended as follows:
PART 180--[AMENDED]
0
1. The authority citation for part 180 continues to read as follows:
Authority: 21 U.S.C. 321(q), 346a and 371.
0
2. Section 180.507 is amended by deleting the entries for ``Herb
subgroup 19A, dried, except chive,'' and ``Herb subgroup 19A, fresh,
except chive,'' and by alphabetically adding the following commodities
to the table in paragraph (a) to read as follows:
Sec. 180.507 Azoxystrobin.
(a) * * *
------------------------------------------------------------------------
Commodity Parts per million
------------------------------------------------------------------------
* * * * *
Crambe, seed......................................... 0.5
* * * * *
Flax, seed........................................... 0.5
* * * * *
Herb Subgroup 19A, dried leaves...................... 260
Herb Subgroup 19A, fresh leaves...................... 50
* * * * *
Mustard, field, seed................................. 0.5
Mustard, Indian, seed................................ 0.5
Mustard, seed........................................ 0.5
* * * * *
Rapeseed, Indian..................................... 0.5
Rapeseed, seed....................................... 0.5
* * * * *
Safflower, seed...................................... 0.5
* * * * *
Spice Subgroup 19B, except black pepper.............. 38
* * * * *
Sunflower, seed...................................... 0.5
* * * * *
------------------------------------------------------------------------
* * * * *
[FR Doc. 06-4157 Filed 5-2-06; 8:45 am]
BILLING CODE 6560-50-S