Flumioxazin; Pesticide Tolerance, 11826-11831 [E8-4102]
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Federal Register / Vol. 73, No. 44 / Wednesday, March 5, 2008 / Rules and Regulations
Flexibility Act (RFA) (5 U.S.C. 601 et
seq.) do not apply.
This final rule 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 section 408(n)(4) of FFDCA. 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 6, 2000) do not apply
to this rule. In addition, This rule does
not 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).
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).
VII. Congressional Review Act
The Congressional Review Act, 5
U.S.C. 801 et seq., generally provides
that before a rule may take effect, the
agency promulgating the rule must
submit a rule report 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).
yshivers on PROD1PC62 with RULES
List of Subjects in 40 CFR Part 180
Environmental protection,
Administrative practice and procedure,
Agricultural commodities, Pesticides
and pests, Reporting and recordkeeping
requirements.
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Dated: February 14, 2008.
Donald R. Stubbs,
Acting 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 180.544 is amended by:
i. Revising the entries ‘‘canistel’’;
‘‘mango’’; ‘‘papaya’’; ‘‘sapodilla’’;
‘‘sapote, black’’; ‘‘sapote, mamey’’; and
‘‘star apple’’ in paragraph (a)(1).
I ii. Alphabetically adding commodities
to the table in paragraph (a)(1).
I iii. Removing the text from paragraph
(b) and reserving the heading.
I iv. Revising the tables in paragraphs
(d)(1) and (d)(2) to read as follows:
I
I
§ 180.544 Methoxyfenozide; tolerances for
residues.
Parts per million
Acerola ............................
*
*
*
Animal feed, nongrass,
group 18, forage .........
Animal feed, nongrass,
group 18, hay ..............
*
*
*
Avocado ..........................
Bean, dry, seed ..............
*
*
*
Bushberry subgroup 1307B ..............................
Canistel ...........................
*
*
*
Feijoa ..............................
*
*
*
Grass, forage, fodder
and hay, group 17, forage ..............................
Grass, forage, fodder
and hay, group 17, hay
Guava .............................
*
*
*
Jaboticaba ......................
*
*
*
Mango .............................
*
*
*
Onion, green, subgroup
3-07B ...........................
Papaya ............................
Passionfruit .....................
*
*
*
Peanut ............................
Peanut, hay ....................
Peanut, oil .......................
*
*
*
Sapodilla .........................
Sapote, black ..................
Sapote, mamey ..............
*
*
*
Star apple .......................
Starfruit ...........................
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Parts per million
*
*
*
Vegetable, tuberous and
corm, except potato,
subgroup 1D ...............
Wax jambu ......................
*
*
0.02
0.4
(b) Section 18 emergency exemptions.
[Reserved]
(c) Tolerances with regional
registrations. [Reserved]
(d) * * *
(1) * * *
Commodity
Parts per
million
Vegetable, bulb,
group 3-07 .....
Vegetable,
leaves of root
and tuber,
group 2 ..........
Vegetable, root
and tuber,
group 1 ..........
Expiration/
revocation
date
0.20
9/30/10
0.20
9/30/10
0.10
9/30/10
(2) * * *
(a) General. (1) * * *
Commodity
Commodity
Commodity
Parts per
million
0.4
*
*
50.0
*
*
150.0
*
0.6
0.24
*
3.0
0.6
*
*
0.4
*
*
18.0
*
*
*
30.0
0.4
*
0.4
*
0.6
*
Animal feed,
non-grass,
group 18 ........
Grain, cereal,
forage, fodder
and straw,
group 16 ........
Grass, forage,
fodder and
hay, group 17
Herb and spice,
group 19 ........
Vegetable, foliage of legume, group 7
Vegetable, legume, group 6
Expiration/
revocation
date
10.0
9/30/10
10.0
9/30/10
10.0
9/30/10
10.0
9/30/10
10.0
9/30/10
0.10
9/30/10
[FR Doc. E8–4027 Filed 3–4–08; 8:45 am]
BILLING CODE 6560–50–S
ENVIRONMENTAL PROTECTION
AGENCY
40 CFR Part 180
5.0
0.6
0.4
*
*
*
Sfmt 4700
*
0.02
55.0
0.04
*
0.6
0.6
0.6
*
0.6
0.4
[EPA–HQ–OPP–2007–0308; FRL–8352–5]
Flumioxazin; Pesticide Tolerance
Environmental Protection
Agency (EPA).
ACTION: Final rule.
AGENCY:
SUMMARY: This regulation establishes a
tolerance for residues of flumioxazin in
or on alfalfa, forage; alfalfa, hay;
asparagus; bean, dry seed; bushberry
subgroup 13-07B; melon, subgroup 9A;
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nut, tree, group 14; okra; and vegetable,
fruiting, group 8. The Interregional
Research Project #4 (IR-4) requested
these tolerances under the Federal Food,
Drug, and Cosmetic Act (FFDCA). This
regulation also modifies 40 CFR
180.568(b) by deleting existing timelimited tolerances in/on alfalfa, forage
and alfalfa, hay at 0.13 and 0.45 ppm,
respectively, made redundant by the
newly-established tolerances.
This regulation is effective
March 5, 2008. Objections and requests
for hearings must be received on or
before May 5, 2008, and must be filed
in accordance with the instructions
provided in 40 CFR part 178 (see also
Unit I.C. of the SUPPLEMENTARY
INFORMATION).
DATES:
EPA has established a
docket for this action under docket
identification (ID) number EPA–HQ–
OPP–2007–0308. To access the
electronic docket, go to https://
www.regulations.gov, select ‘‘Advanced
Search,’’ then ‘‘Docket Search.’’ Insert
the docket ID number where indicated
and select the ‘‘Submit’’ button. Follow
the instructions on the regulations.gov
website to view the docket index or
access available documents. All
documents in the docket are listed in
the docket index available in
regulations.gov. Although listed in the
index, some information is not publicly
available, e.g., Confidential Business
Information (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 in the electronic docket at
https://www.regulations.gov, or, if only
available in hard copy, at the OPP
Regulatory Public Docket in Rm. S–
4400, One Potomac Yard (South Bldg.),
2777 S. Crystal Dr., Arlington, VA. The
Docket Facility is open from 8:30 a.m.
to 4 p.m., Monday through Friday,
excluding legal holidays. The Docket
Facility telephone number is (703) 305–
5805.
ADDRESSES:
yshivers on PROD1PC62 with RULES
FOR FURTHER INFORMATION CONTACT:
Sidney Jackson, Registration Division
(7505P), Office of Pesticide Programs,
Environmental Protection Agency, 1200
Pennsylvania Ave., NW., Washington,
DC 20460–0001; telephone number:
(703) 305–7610; e-mail address:
jackson.sidney@epa.gov.
SUPPLEMENTARY INFORMATION:
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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 those engaged in the
following activities:
• Crop production (NAICS code 111),
e.g., agricultural workers; greenhouse,
nursery, and floriculture workers;
farmers.
• Animal production (NAICS code
112), e.g., cattle ranchers and farmers,
dairy cattle farmers, livestock farmers.
• Food manufacturing (NAICS code
311), e.g., agricultural workers; farmers;
greenhouse, nursery, and floriculture
workers; ranchers; pesticide applicators.
• Pesticide manufacturing (NAICS
code 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 to provide 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?
In addition to accessing an electronic
copy of this Federal Register document
through the electronic docket at https://
www.regulations.gov, you may access
this Federal Register document
electronically through the EPA Internet
under the ‘‘Federal Register’’ listings at
https://www.epa.gov/fedrgstr. You may
also access a frequently updated
electronic version of EPA’s tolerance
regulations at 40 CFR part 180 through
the Government Printing Office’s pilot
e-CFR site at https://www.gpoaccess.gov/
ecfr.
C. Can I File an Objection or Hearing
Request?
Under section 408(g) of FFDCA, 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
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proper receipt by EPA, you must
identify docket ID number EPA–HQ–
OPP–2007–0308 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
as required by 40 CFR part 178 on or
before May 5, 2008.
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 that does not
contain any CBI for inclusion in the
public docket that is described in
ADDRESSES. Information not marked
confidential pursuant to 40 CFR part 2
may be disclosed publicly by EPA
without prior notice. Submit this copy,
identified by docket ID number EPA–
HQ–OPP–2007–0308, by one of the
following methods:
• Federal eRulemaking Portal: https://
www.regulations.gov. Follow the on-line
instructions for submitting comments.
• Mail: Office of Pesticide Programs
(OPP) Regulatory Public Docket (7502P),
Environmental Protection Agency, 1200
Pennsylvania Ave., NW., Washington,
DC 20460–0001.
• Delivery: OPP Regulatory Public
Docket (7502P), Environmental
Protection Agency, Rm. S–4400, One
Potomac Yard (South Bldg.), 2777 S.
Crystal Dr., Arlington, VA. Deliveries
are only accepted during the Docket’s
normal hours of operation (8:30 a.m. to
4 p.m., Monday through Friday,
excluding legal holidays). Special
arrangements should be made for
deliveries of boxed information. The
Docket Facility telephone number is
(703) 305–5805.
II. Petition for Tolerance
In the Federal Registers of June 27,
2007, (72 FR 35237; FRL–8133–4) and
September 28, 2007; (72 FR 55204; FRL–
8147–1), EPA issued notices pursuant to
section 408(d)(3) of FFDCA, 21 U.S.C.
346a(d)(3), announcing the filing of
pesticide petitions (PP 6E7151 and PP
6F7092, respectively,) by the IR-4
Project Headquarters, 500 College Road
East, Suite 201 W, Princeton, NJ 08540
and the registrant, Valent U.S.A.
Corporation. The petitions requested
that 40 CFR 180.568 be amended by
establishing tolerances for residues of
the herbicide, flumioxazin, 2-[7-fluoro3,4-dihydro-3-oxo-4-(2-propynyl)-2H1,4-benzoxazin-6-yl]-4,5,6,7-tetrahydro1H-isoindole-1,3(2H)-dione in or on,
commodities alfalfa, forage at 1.0 parts
per million (ppm), alfalfa, hay at 2.0
ppm (PP 6F7092), asparagus, aronia
berry, buffalo currant, Chilean guava,
European barberry, highbush cranberry,
honeysuckle, jostaberry, juneberry,
lingonberry, native currant, salal, sea
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buckthorn, and okra at 0.02 ppm,
bushberry subgroup 13B at 0.02 ppm,
melon subgroup 9A at 0.02 parts per
million (ppm), dry bean at 0.10 ppm,
vegetable, fruiting, crop group 8 at 0.02
ppm, and nut, tree, crop group 14, at
0.02 ppm (PP 6E7151). These notices
referenced a summary of the petition
prepared by Valent U.S.A. Corporation,
the registrant, which is available to the
public in the docket, https://
www.regulations.gov.
There were no comments received in
response to the notices of filing.
Based upon review of the data
supporting the petitions, EPA has
revised certain proposed tolerance
levels and corrected commodity
definitions as follow:
1. The Agency determined that
adequate data are available to support
establishing a tolerance for the
bushberry subgroup 13–07B. IR–4
petitioned for a tolerance for bushberry
subgroup 13B as well as individual
tolerances on aronia berry, buffalo
currant, Chilean guava, European
barberry, highbush cranberry,
honeysuckle, jostaberry, juneberry,
lingonberry, native currant, salal, and
sea buckthorn (PP 6E7151). In the
Federal Register of December 7, 2007
(72 FR 69150–69158) (FRL–8340–6),
EPA issued a final rule that revised the
crop grouping regulations. As part of
this action, EPA expanded and revised
berries group 13. Changes to crop group
13 (berries) included adding new
commodities, revising existing
subgroups and creating new subgroups
(including a bushberry subgroup 13–
07B consisting of the commodities
requested in PP 6E7151 and cultivars,
varieties, and/or hybrids of these).
EPA indicated in the December 7,
2007 final rule as well as the earlier May
23, 2007 proposed rule (72 FR 28920–
28930) that, for existing petitions for
which a Notice of Filing had been
published, the Agency would attempt to
conform these petitions to the rule.
Therefore, consistent with this rule,
EPA is establishing tolerances on
Bushberry subgroup 13–07B. Bushberry
subgroup 13–07B consists of the berries
for which tolerances were requested in
PP 6E7151.
EPA concludes it is reasonable to
revise the petitioned-for tolerances so
that they agree with the recent crop
grouping revisions because:
i. Although the subgroup includes
several new commodities, these
commodities were proposed as
individual tolerances and are closely
related minor crops which contribute
little to overall dietary or aggregate
exposure and risk;
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ii. Flumixoazin exposure from these
added commodities was considered
when EPA conducted the dietary and
aggregate risk assessments supporting
this action; and
iii. The representative commodities
for the revised subgroup has not
changed.
2. The proposed tolerance for bean,
dry, was revised to bean, dry, seed and
the tolerance level revised from 0.06
ppm to 0.05 ppm.
III. Aggregate Risk Assessment and
Determination of Safety
Section 408(b)(2)(A)(i) of FFDCA
allows EPA to establish a tolerance (the
legal limit for a pesticide chemical
residue in or on a food) only if EPA
determines that the tolerance is ‘‘safe.’’
Section 408(b)(2)(A)(ii) of FFDCA
defines ‘‘safe’’ to mean that ‘‘there is a
reasonable certainty that no harm will
result from aggregate exposure to the
pesticide chemical residue, including
all anticipated dietary exposures and all
other exposures for which there is
reliable information.’’ This includes
exposure through drinking water and in
residential settings, but does not include
occupational exposure. Section
408(b)(2)(C) of FFDCA requires EPA to
give special consideration to exposure
of infants and children to the pesticide
chemical residue in establishing a
tolerance and to ‘‘ensure that there is a
reasonable certainty that no harm will
result to infants and children from
aggregate exposure to the pesticide
chemical residue....’’ These provisions
were added to FFDCA by the Food
Quality Protection Act (FQPA) of 1996.
Consistent with FFDCA section
408(b)(2)(D), and the factors specified in
FFDCA section 408(b)(2)(D), EPA has
reviewed the available scientific data
and other relevant information in
support of this action. EPA has
sufficient data to assess the hazards of
and to make a determination on
aggregate exposure for the petitioned-for
tolerance for residues of flumioxazin on
alfalfa, forage at 3.0 ppm; alfalfa, hay at
8.0 ppm; asparagus at 0.02 ppm;
bushberry subgroup 13–07B at 0.02
ppm; melon, subgroup 9A at 0.02 ppm;
bean, dry seed at 0.05 ppm; vegetable,
fruiting, group 8 at 0.02 ppm; okra at
0.02 ppm; and nut, tree, group 14, at
0.02 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 their
validity, completeness, and reliability as
well as the relationship of the results of
the studies to human risk. EPA has also
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considered available information
concerning the variability of the
sensitivities of major identifiable
subgroups of consumers, including
infants and children.
Flumioxazin has mild or no acute
toxicity when administered orally,
dermally, or by inhalation. It has little
or no toxicity with regard to eye
irritation or skin irritation. The
chemical, flumioxazin, was not a dermal
sensitizer. Subchronic and chronic
toxicity studies demonstrated that the
target organs of flumioxazin are the
liver, spleen and cardiovascular system.
Developmental effects were observed in
developmental rat studies. These effects
were fetal cardiovascular anomalies
(especially ventricular septal defects).
Flumioxazin has been classified as a
‘‘Not Likely Human Carcinogen,’’ based
on the lack of carcinogenicity in a 2–
year rat study, an 18–month mouse
study, and a battery of mutagenic
studies.
Specific information on the studies
received and the nature of the adverse
effects caused by flumioxazin as well as
the no-observed-adverse-effect-level
(NOAEL) and the lowest-observedadverse-effect-level (LOAEL) from the
toxicity studies can be found at https://
www.regulations.gov. in the document;
‘‘Flumioxazin; Human Health Risk
Assessment for the Proposed Food Use
of the Herbicide Flumioxazin on Alfalfa,
Asparagus, Dry Beans, Fruiting
Vegetables (Group 8, Including Okra),
Melons (Subgroup 9A), Bushberries
(Subgroup 13B), and Tree Nuts (Group
14), and a Request for an Amended Use
on Garlic,’’ dated 28 Nov. 2007. The
referenced document is available in the
docket established by this action, which
is described under ADDRESSES, and is
identified as EPA–HQ–OPP–2007–
0308–0003 in that docket.
B. Toxicological Endpoints
For hazards that have a threshold
below which there is no appreciable
risk, the toxicological level of concern
(LOC) is derived from the NOAEL in the
toxicology study identified as
appropriate for use in risk assessment.
However, if a NOAEL cannot be
determined, LOAEL is sometimes used
for risk assessment. Uncertainty/safety
factors (UFs) are used in conjunction
with the LOC to take into account
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. Safety is assessed for acute
and chronic risks by comparing
aggregate exposure to the pesticide to
the acute population adjusted dose
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(aPAD) and chronic population adjusted
dose (cPAD). The aPAD and cPAD are
calculated by dividing the LOC by all
applicable UFs. Short-term,
intermediate-term, and long-term risks
are evaluated by comparing aggregate
exposure to the LOC to ensure that the
margin of exposure (MOE) called for by
the product of all applicable UFs is not
exceeded.
For non-threshold risks, the Agency
assumes that any amount of exposure
will lead to some degree of risk and
estimates risk in terms of the probability
of occurrence of additional adverse
cases. Generally, cancer risks are
considered non-threshold. 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/fedrgstr/EPA-PEST/1997/
November/Day–26/p30948.htm.
A summary of the toxicological
endpoints for flumioxazin used for
human risk assessment can be found at
https://www.regulations.gov in
document; ‘‘Flumioxazin; Human
Health Risk Assessment for the
Proposed Food Use of the Herbicide
Flumioxazin on Alfalfa, Asparagus, Dry
Beans, Fruiting Vegetables (Group 8,
Including Okra), Melons (Subgroup 9A),
Bushberries (Subgroup 13B), and Tree
Nuts (Group 14), and a Request for an
Amended Use on Garlic,’’ dated 28 Nov.
2007 in docket ID number EPA–HQ–
OPP–2007–0308–0003.
C. Exposure Assessment
1. Dietary exposure from food and
feed uses. In evaluating dietary
exposure to flumioxazin, EPA
considered exposure under the
petitioned-for tolerances as well as all
existing flumioxazin tolerances in (40
CFR 180.568). EPA assessed dietary
exposures from flumioxazin 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. No such effect was identified
for the general population. However,
EPA identified potential acute effects,
e.g., cardiovascular effects in offspring,
for the population subgroup, females 13
to 49 years.
In estimating acute dietary exposure,
EPA used food consumption
information from the U.S. Department of
Agriculture (USDA) 1994–1996
Nationwide Continuing Surveys of Food
Intake by Individuals (CSFII). As to
residue levels in food, EPA assumed all
foods for which there are tolerances
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Jkt 214001
(current and proposed) were treated
(100% crop treated (%CT or PCT)
assumption) and contain tolerance-level
residues. Percent crop treated (PCT)
and/or anticipated residues were not
used in the acute risk assessment.
ii. Chronic exposure. In conducting
the chronic dietary exposure assessment
EPA used the food consumption data
from the USDA 1994–1996, and 1998
CSFII. As to residue levels in food, EPA
assumed all foods for which there are
tolerances (existing and proposed) were
treated (100% crop treated assumption)
and contain tolerance-level residues.
PCT and/or anticipated residues were
not used in the chronic risk assessment.
iii. Cancer. The Agency has
determined that flumioxazin is ‘‘not
likely to be a human carcinogen’’ based
on the lack of carcinogenicity in a 2–rat
study, an 18 month mouse study, and a
battery of mutagenic studies. Therefore,
a quantitative exposure assessment to
evaluate cancer risk is unnecessary.
2. Dietary exposure from drinking
water. The Agency lacks sufficient
monitoring data to complete a
comprehensive dietary exposure
analysis and risk assessment for
flumioxazin and its degradates, 482–HA
and APF, 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
environmental fate characteristics of
flumioxazin. 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 drinking
water concentrations (EDWCs) of
flumioxazin for acute exposures are
estimated to be 34 parts per billion
(ppb) for surface water and 48 ppb for
groundwater. The EECs for chronic
exposures are estimated to be 18 ppb for
surface water and 48 ppb for ground
water.
Modeled estimates of drinking water
concentrations were directly entered
into the dietary exposure model. For
acute dietary risk assessment, the water
concentration value of 48 ppb was used
to access the contribution to drinking
water. For chronic dietary risk
assessment, the water concentration of
value 48 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
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(e.g., for lawn and garden pest control,
indoor pest control, termiticides, and
flea and tick control on pets).
Flumioxazin is not registered for use
on any sites that would result in
residential exposure.
4. Cumulative effects from substances
with a common mechanism of toxicity.
Section 408(b)(2)(D)(v) of FFDCA
requires that, when considering whether
to establish, modify, or revoke a
tolerance, the Agency consider
‘‘available information’’ concerning the
cumulative effects of a particular
pesticide’s residues and ‘‘other
substances that have a common
mechanism of toxicity.’’
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
flumioxazin and any other substances
and flumioxazin 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 flumioxazin 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 EPA’s website 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 (‘‘10X’’) tenfold margin of
safety for infants and children in the
case of threshold effects to account for
pre-natal and post-natal 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. 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 FQPA safety
factor value based on the use of
traditional UFs and/or special FQPA
safety factors, as appropriate.
2. Pre-natal and post-natal sensitivity.
The pre-natal and post-natal toxicity
database for flumioxazin include the rat
and rabbit developmental toxicity
studies and the 2–generation
reproduction toxicity study in rats.
There is evidence of quantitative
susceptibility following oral and dermal
exposures to rats. Following in-utero
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exposures, developmental effects
(cardiovascular anomalies) were seen in
the absence of maternal toxicity. There
is no evidence (quantitative or
qualitative) of susceptibility following
in-utero oral exposure in rabbits. No
developmental toxicity was seen at the
highest dose tested (3x the Limit-Dose).
There is quantitative evidence of
susceptibility in the multi-generation
reproduction study where effects in
offspring were seen at doses lower than
those which induced effects in parental
animals.
Although increased pre-natal and
post-natal quantitative susceptibility
was seen in rats, the Agency concluded
that there is a low concern and no
residual uncertainties for pre-natal and/
or post-natal toxicity effects of
flumioxazin because:
i. Developmental toxicity (including
cardiovascular abnormalities) NOAELs
and LOAELs from pre-natal exposure
are well characterized after oral and
dermal exposure,
ii. The off-spring toxicity NOAEL and
LOAEL from post-natal exposure are
well characterized,
iii. The dose selected for risk
assessment is protective of all potential
effects.
3. Conclusion. EPA has determined
that reliable data show that it would be
safe for infants and children to reduce
the FQPA safety factor to 1X. That
decision is based on the following
findings:
i. The toxicity database for
flumioxazin is complete.
ii. There is no indication that
flumioxazin is a neurotoxic chemical
and there is no need for a
developmental neurotoxicity study or
additional UFs to account for
neurotoxicity.
iii. Although there is quantitative
evidence of increased susceptibility in
the prenatal developmental studies and
post-natal multi-generation study in
rats, EPA did not identify any residual
uncertainties after establishing toxicity
endpoints and traditional UFs to be
used in the risk assessment of
flumioxazin. The degree of concern for
pre-natal and/or post-natal toxicity is
low.
iv. There are no residual uncertainties
identified in the exposure databases.
The dietary food exposure assessments
were performed based on 100%CT and
tolerance-level residues for all
commodities. By using these screeninglevel assumptions, chronic exposures/
risks will not be underestimated. The
dietary drinking water assessment
utilizes values generated by models and
associated modeling parameters which
are designed to provide conservative,
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14:21 Mar 04, 2008
Jkt 214001
health protective, high-end estimates of
water concentrations. These
assessments will not underestimate the
exposure and risks posed by
flumioxazin.
E. Aggregate Risks and Determination of
Safety
Safety is assessed for acute and
chronic risks by comparing aggregate
exposure to the pesticide to the aPAD
and cPAD. The aPAD and cPAD are
calculated by dividing the LOC by all
applicable UFs. For linear cancer risks,
EPA calculates the probability of
additional cancer cases given aggregate
exposure. Short-term, intermediateterm, and long-term risks are evaluated
by comparing aggregate exposure to the
LOC to ensure that the MOE called for
by the product of all applicable UFs is
not exceeded.
1. Acute risk. Using the exposure
assumptions discussed in this unit for
acute exposure, the acute dietary
exposure from food and water to
flumioxazin will occupy 8.0% of the
aPAD at the 95th percentile of exposure
for the population group, females 13 to
49 years old (the only subpopulation for
which an acute endpoint was selected).
2. Chronic risk. Using the exposure
assumptions described in this unit for
chronic exposure, EPA has concluded
that exposure to flumixazim by the
general U.S. population and all
population subgroups have risk
estimates below LOC. Exposure to
flumioxazin from food and water will
utilize 18% of the cPAD for infants less
than 1 year old, the population group
with greatest exposure. The general U.S.
population utilize 6% of the cPAD.
There are no residential uses for
flumioxazin that result in chronic
residential exposure to flumioxazin.
3. Short-term and intermediate-term
risk. Short-term and intermediate-term
aggregate exposure takes into account
residential exposure plus chronic
exposure to food and water (considered
to be a background exposure level).
Flumioxazin is not registered for use
on any sites that would result in
residential exposure. Therefore, the
aggregate risk is the sum of the risk from
food and water, which do not exceed
the Agency’s LOC.
4. 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 flumioxazin
residues.
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IV. Other Considerations
A. Analytical Enforcement Methodology
Adequate enforcement methodology
(gas chromatography /nitrogenphosphorus detection) is available to
enforce the tolerance expression. The
method may be requested from: Chief,
Analytical Chemistry Branch,
Environmental Science Center, 701
Mapes Rd., Ft. Meade, MD 20755–5350;
telephone number: (410) 305–2905; email address: residuemethods@epa.gov.
B. International Residue Limits
There are no established or proposed
Canadian, Mexican or Codex maximum
residue levels (MRLs) for residues of
flumioxazin in plant commodities
subject to this action.
V. Conclusion
Therefore, tolerances are established
for residues of flumioxazin, 2-[7-fluoro3,4-dihydro-3-oxo-4-(2-propynyl)-2H1,4-benzoxazin-6-yl]-4,5,6,7-tetrahydro1H-isoindole-1,3(2H)-dione in or on,
commodities alfalfa, forage at 3.0 ppm;
alfalfa, hay at 8.0 ppm; asparagus at 0.02
ppm; bushberry subgroup 13–07B at
0.02 ppm; melon subgroup 9A at 0.02
ppm; bean, dry seed at 0.05 ppm;
vegetable, fruiting, except cucurbits
group 8 at 0.02 ppm; okra at 0.02 ppm;
and nut, tree, group 14, at 0.02 ppm.
VI. 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, 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) or Executive Order 13045,
entitled Protection of Children from
Environmental Health Risks and Safety
Risks (62 FR 19885, April 23, 1997).
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., nor does it require any special
considerations under Executive Order
12898, entitled Federal Actions to
Address Environmental Justice in
Minority Populations and Low-Income
Populations (59 FR 7629, February 16,
1994).
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Since tolerances and exemptions that
are established on the basis of a petition
under 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.
This final rule 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 section 408(n)(4) of FFDCA. 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 6, 2000) do not apply
to this rule. In addition, This rule does
not 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).
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).
VII. Congressional Review Act
The Congressional Review Act, 5
U.S.C. 801 et seq., generally provides
that before a rule may take effect, the
agency promulgating the rule must
submit a rule report 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
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14:21 Mar 04, 2008
Jkt 214001
and pests, Reporting and recordkeeping
requirements.
Dated: February 22, 2008.
Lois Rossi,
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 180.568 is amended by
alphabetically adding the following
commodities to the table in paragraph
(a), and by removing the text and
reserving paragraph (b) to read as
follows:
I
§ 180.568 Flumioxazin; tolerances for
residues.
(a) * * *
Commodity
Parts per million
Alfalfa, forage .................
Alfalfa, hay ......................
*
*
*
Asparagus .......................
Bean, dry seed ...............
Bushberry subgroup 13–
07B ..............................
*
*
*
Melon, subgroup 9A .......
Nut, tree, group 14 .........
Okra ................................
*
*
*
Vegetable, fruiting, group
8 ..................................
*
*
*
3.0
8.0
*
*
0.02
0.05
0.02
*
*
0.02
0.02
0.02
*
*
*
*
0.02
(b) Section 18 emergency exemptions.
[Reserved]
*
*
*
*
*
[FR Doc. E8–4102 Filed 3–4–08; 8:45 am]
BILLING CODE 6560–50–S
ENVIRONMENTAL PROTECTION
AGENCY
40 CFR Part 180
[EPA–HQ–OPP–2007–0302; FRL–8351–6]
Bifenazate; Pesticide Tolerance
Environmental Protection
Agency (EPA).
ACTION: Final rule.
AGENCY:
SUMMARY: This regulation establishes
tolerances for combined residues of
bifenazate and its metabolite,
diazinecarboxylic acid, 2-(4-methoxy[1,1’-biphenyl]-3-yl), 1-methylethyl ester
(expressed as bifenazate), in or on
acerola; black sapote; caneberry
subgroup 13-07A; canistel; feijoa; guava;
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11831
jaboticaba; longan; lychee; mango;
papaya; passionfruit; pea and bean,
succulent shelled, subgroup 6B;
pulasan; rambutan; sapodilla; sapote,
mamey; soybean, succulent shelled;
Spanish lime; star apple; starfruit;
vegetable, legume, edible-podded,
subgroup 6A; and wax jambu.
Interregional Research Project Number 4
(IR-4) requested these tolerances under
the Federal Food, Drug, and Cosmetic
Act (FFDCA). This regulation also
deletes existing bifenazate tolerances on
‘‘pea, edible podded, succulent’’ and
‘‘pea, garden, succulent’’, which are
superseded by the new tolerances on
‘‘vegetable, legume, edible-podded,
subgroup 6A’’ and ‘‘pea and bean,
succulent shelled, subgroup 6B’’,
respectively.
DATES: This regulation is effective
March 5, 2008. Objections and requests
for hearings must be received on or
before May 5, 2008, 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: EPA has established a
docket for this action under docket
identification (ID) number EPA–HQ–
OPP–2007–0302. To access the
electronic docket, go to https://
www.regulations.gov, select ‘‘Advanced
Search,’’ then ‘‘Docket Search.’’ Insert
the docket ID number where indicated
and select the ‘‘Submit’’ button. Follow
the instructions on the regulations.gov
website to view the docket index or
access available documents. All
documents in the docket are listed in
the docket index available in
regulations.gov. Although listed in the
index, some information is not publicly
available, e.g., Confidential Business
Information (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 in the electronic docket at
https://www.regulations.gov, or, if only
available in hard copy, at the OPP
Regulatory Public Docket in Rm. S–
4400, One Potomac Yard (South Bldg.),
2777 S. Crystal Dr., Arlington, VA. The
Docket Facility is open from 8:30 a.m.
to 4 p.m., Monday through Friday,
excluding legal holidays. The Docket
Facility telephone number is (703) 305–
5805.
FOR FURTHER INFORMATION CONTACT:
Susan Stanton, Registration Division
(7505P), Office of Pesticide Programs,
Environmental Protection Agency, 1200
Pennsylvania Ave., NW., Washington,
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[Federal Register Volume 73, Number 44 (Wednesday, March 5, 2008)]
[Rules and Regulations]
[Pages 11826-11831]
From the Federal Register Online via the Government Printing Office [www.gpo.gov]
[FR Doc No: E8-4102]
-----------------------------------------------------------------------
ENVIRONMENTAL PROTECTION AGENCY
40 CFR Part 180
[EPA-HQ-OPP-2007-0308; FRL-8352-5]
Flumioxazin; Pesticide Tolerance
AGENCY: Environmental Protection Agency (EPA).
ACTION: Final rule.
-----------------------------------------------------------------------
SUMMARY: This regulation establishes a tolerance for residues of
flumioxazin in or on alfalfa, forage; alfalfa, hay; asparagus; bean,
dry seed; bushberry subgroup 13-07B; melon, subgroup 9A;
[[Page 11827]]
nut, tree, group 14; okra; and vegetable, fruiting, group 8. The
Interregional Research Project 4 (IR-4) requested these
tolerances under the Federal Food, Drug, and Cosmetic Act (FFDCA). This
regulation also modifies 40 CFR 180.568(b) by deleting existing time-
limited tolerances in/on alfalfa, forage and alfalfa, hay at 0.13 and
0.45 ppm, respectively, made redundant by the newly-established
tolerances.
DATES: This regulation is effective March 5, 2008. Objections and
requests for hearings must be received on or before May 5, 2008, 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: EPA has established a docket for this action under docket
identification (ID) number EPA-HQ-OPP-2007-0308. To access the
electronic docket, go to https://www.regulations.gov, select ``Advanced
Search,'' then ``Docket Search.'' Insert the docket ID number where
indicated and select the ``Submit'' button. Follow the instructions on
the regulations.gov website to view the docket index or access
available documents. All documents in the docket are listed in the
docket index available in regulations.gov. Although listed in the
index, some information is not publicly available, e.g., Confidential
Business Information (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 in the electronic docket at https://www.regulations.gov, or,
if only available in hard copy, at the OPP Regulatory Public Docket in
Rm. S-4400, One Potomac Yard (South Bldg.), 2777 S. Crystal Dr.,
Arlington, VA. The Docket Facility is open from 8:30 a.m. to 4 p.m.,
Monday through Friday, excluding legal holidays. The Docket Facility
telephone number is (703) 305-5805.
FOR FURTHER INFORMATION CONTACT: Sidney Jackson, Registration Division
(7505P), Office of Pesticide Programs, Environmental Protection Agency,
1200 Pennsylvania Ave., NW., Washington, DC 20460-0001; telephone
number: (703) 305-7610; e-mail address: jackson.sidney@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 those
engaged in the following activities:
Crop production (NAICS code 111), e.g., agricultural
workers; greenhouse, nursery, and floriculture workers; farmers.
Animal production (NAICS code 112), e.g., cattle ranchers
and farmers, dairy cattle farmers, livestock farmers.
Food manufacturing (NAICS code 311), e.g., agricultural
workers; farmers; greenhouse, nursery, and floriculture workers;
ranchers; pesticide applicators.
Pesticide manufacturing (NAICS code 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 to
provide 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?
In addition to accessing an electronic copy of this Federal
Register document through the electronic docket at https://
www.regulations.gov, you may access this Federal Register document
electronically through the EPA Internet under the ``Federal Register''
listings at https://www.epa.gov/fedrgstr. You may also access a
frequently updated electronic version of EPA's tolerance regulations at
40 CFR part 180 through the Government Printing Office's pilot e-CFR
site at https://www.gpoaccess.gov/ecfr.
C. Can I File an Objection or Hearing Request?
Under section 408(g) of FFDCA, 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-2007-0308 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 as required by 40 CFR part 178 on or
before May 5, 2008.
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 that does not contain any CBI for inclusion in the public
docket that is described in ADDRESSES. Information not marked
confidential pursuant to 40 CFR part 2 may be disclosed publicly by EPA
without prior notice. Submit this copy, identified by docket ID number
EPA-HQ-OPP-2007-0308, by one of the following methods:
Federal eRulemaking Portal: https://www.regulations.gov.
Follow the on-line instructions for submitting comments.
Mail: Office of Pesticide Programs (OPP) Regulatory Public
Docket (7502P), Environmental Protection Agency, 1200 Pennsylvania
Ave., NW., Washington, DC 20460-0001.
Delivery: OPP Regulatory Public Docket (7502P),
Environmental Protection Agency, Rm. S-4400, One Potomac Yard (South
Bldg.), 2777 S. Crystal Dr., Arlington, VA. Deliveries are only
accepted during the Docket's normal hours of operation (8:30 a.m. to 4
p.m., Monday through Friday, excluding legal holidays). Special
arrangements should be made for deliveries of boxed information. The
Docket Facility telephone number is (703) 305-5805.
II. Petition for Tolerance
In the Federal Registers of June 27, 2007, (72 FR 35237; FRL-8133-
4) and September 28, 2007; (72 FR 55204; FRL-8147-1), EPA issued
notices pursuant to section 408(d)(3) of FFDCA, 21 U.S.C. 346a(d)(3),
announcing the filing of pesticide petitions (PP 6E7151 and PP 6F7092,
respectively,) by the IR-4 Project Headquarters, 500 College Road East,
Suite 201 W, Princeton, NJ 08540 and the registrant, Valent U.S.A.
Corporation. The petitions requested that 40 CFR 180.568 be amended by
establishing tolerances for residues of the herbicide, flumioxazin, 2-
[7-fluoro-3,4-dihydro-3-oxo-4-(2-propynyl)-2H-1,4-benzoxazin-6-yl]-
4,5,6,7-tetrahydro-1H-isoindole-1,3(2H)-dione in or on, commodities
alfalfa, forage at 1.0 parts per million (ppm), alfalfa, hay at 2.0 ppm
(PP 6F7092), asparagus, aronia berry, buffalo currant, Chilean guava,
European barberry, highbush cranberry, honeysuckle, jostaberry,
juneberry, lingonberry, native currant, salal, sea
[[Page 11828]]
buckthorn, and okra at 0.02 ppm, bushberry subgroup 13B at 0.02 ppm,
melon subgroup 9A at 0.02 parts per million (ppm), dry bean at 0.10
ppm, vegetable, fruiting, crop group 8 at 0.02 ppm, and nut, tree, crop
group 14, at 0.02 ppm (PP 6E7151). These notices referenced a summary
of the petition prepared by Valent U.S.A. Corporation, the registrant,
which is available to the public in the docket, https://
www.regulations.gov.
There were no comments received in response to the notices of
filing.
Based upon review of the data supporting the petitions, EPA has
revised certain proposed tolerance levels and corrected commodity
definitions as follow:
1. The Agency determined that adequate data are available to
support establishing a tolerance for the bushberry subgroup 13-07B. IR-
4 petitioned for a tolerance for bushberry subgroup 13B as well as
individual tolerances on aronia berry, buffalo currant, Chilean guava,
European barberry, highbush cranberry, honeysuckle, jostaberry,
juneberry, lingonberry, native currant, salal, and sea buckthorn (PP
6E7151). In the Federal Register of December 7, 2007 (72 FR 69150-
69158) (FRL-8340-6), EPA issued a final rule that revised the crop
grouping regulations. As part of this action, EPA expanded and revised
berries group 13. Changes to crop group 13 (berries) included adding
new commodities, revising existing subgroups and creating new subgroups
(including a bushberry subgroup 13-07B consisting of the commodities
requested in PP 6E7151 and cultivars, varieties, and/or hybrids of
these).
EPA indicated in the December 7, 2007 final rule as well as the
earlier May 23, 2007 proposed rule (72 FR 28920-28930) that, for
existing petitions for which a Notice of Filing had been published, the
Agency would attempt to conform these petitions to the rule. Therefore,
consistent with this rule, EPA is establishing tolerances on Bushberry
subgroup 13-07B. Bushberry subgroup 13-07B consists of the berries for
which tolerances were requested in PP 6E7151.
EPA concludes it is reasonable to revise the petitioned-for
tolerances so that they agree with the recent crop grouping revisions
because:
i. Although the subgroup includes several new commodities, these
commodities were proposed as individual tolerances and are closely
related minor crops which contribute little to overall dietary or
aggregate exposure and risk;
ii. Flumixoazin exposure from these added commodities was
considered when EPA conducted the dietary and aggregate risk
assessments supporting this action; and
iii. The representative commodities for the revised subgroup has
not changed.
2. The proposed tolerance for bean, dry, was revised to bean, dry,
seed and the tolerance level revised from 0.06 ppm to 0.05 ppm.
III. Aggregate Risk Assessment and Determination of Safety
Section 408(b)(2)(A)(i) of FFDCA allows EPA to establish a
tolerance (the legal limit for a pesticide chemical residue in or on a
food) only if EPA determines that the tolerance is ``safe.'' Section
408(b)(2)(A)(ii) of FFDCA defines ``safe'' to mean that ``there is a
reasonable certainty that no harm will result from aggregate exposure
to the pesticide chemical residue, including all anticipated dietary
exposures and all other exposures for which there is reliable
information.'' This includes exposure through drinking water and in
residential settings, but does not include occupational exposure.
Section 408(b)(2)(C) of FFDCA requires EPA to give special
consideration to exposure of infants and children to the pesticide
chemical residue in establishing a tolerance and to ``ensure that there
is a reasonable certainty that no harm will result to infants and
children from aggregate exposure to the pesticide chemical
residue....'' These provisions were added to FFDCA by the Food Quality
Protection Act (FQPA) of 1996.
Consistent with FFDCA section 408(b)(2)(D), and the factors
specified in FFDCA section 408(b)(2)(D), EPA has reviewed the available
scientific data and other relevant information in support of this
action. EPA has sufficient data to assess the hazards of and to make a
determination on aggregate exposure for the petitioned-for tolerance
for residues of flumioxazin on alfalfa, forage at 3.0 ppm; alfalfa, hay
at 8.0 ppm; asparagus at 0.02 ppm; bushberry subgroup 13-07B at 0.02
ppm; melon, subgroup 9A at 0.02 ppm; bean, dry seed at 0.05 ppm;
vegetable, fruiting, group 8 at 0.02 ppm; okra at 0.02 ppm; and nut,
tree, group 14, at 0.02 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 their
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.
Flumioxazin has mild or no acute toxicity when administered orally,
dermally, or by inhalation. It has little or no toxicity with regard to
eye irritation or skin irritation. The chemical, flumioxazin, was not a
dermal sensitizer. Subchronic and chronic toxicity studies demonstrated
that the target organs of flumioxazin are the liver, spleen and
cardiovascular system. Developmental effects were observed in
developmental rat studies. These effects were fetal cardiovascular
anomalies (especially ventricular septal defects).
Flumioxazin has been classified as a ``Not Likely Human
Carcinogen,'' based on the lack of carcinogenicity in a 2-year rat
study, an 18-month mouse study, and a battery of mutagenic studies.
Specific information on the studies received and the nature of the
adverse effects caused by flumioxazin as well as the no-observed-
adverse-effect-level (NOAEL) and the lowest-observed-adverse-effect-
level (LOAEL) from the toxicity studies can be found at https://
www.regulations.gov. in the document; ``Flumioxazin; Human Health Risk
Assessment for the Proposed Food Use of the Herbicide Flumioxazin on
Alfalfa, Asparagus, Dry Beans, Fruiting Vegetables (Group 8, Including
Okra), Melons (Subgroup 9A), Bushberries (Subgroup 13B), and Tree Nuts
(Group 14), and a Request for an Amended Use on Garlic,'' dated 28 Nov.
2007. The referenced document is available in the docket established by
this action, which is described under ADDRESSES, and is identified as
EPA-HQ-OPP-2007-0308-0003 in that docket.
B. Toxicological Endpoints
For hazards that have a threshold below which there is no
appreciable risk, the toxicological level of concern (LOC) is derived
from the NOAEL in the toxicology study identified as appropriate for
use in risk assessment. However, if a NOAEL cannot be determined, LOAEL
is sometimes used for risk assessment. Uncertainty/safety factors (UFs)
are used in conjunction with the LOC to take into account 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. Safety is assessed for acute and chronic
risks by comparing aggregate exposure to the pesticide to the acute
population adjusted dose
[[Page 11829]]
(aPAD) and chronic population adjusted dose (cPAD). The aPAD and cPAD
are calculated by dividing the LOC by all applicable UFs. Short-term,
intermediate-term, and long-term risks are evaluated by comparing
aggregate exposure to the LOC to ensure that the margin of exposure
(MOE) called for by the product of all applicable UFs is not exceeded.
For non-threshold risks, the Agency assumes that any amount of
exposure will lead to some degree of risk and estimates risk in terms
of the probability of occurrence of additional adverse cases.
Generally, cancer risks are considered non-threshold. 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/fedrgstr/EPA-PEST/1997/November/Day-26/p30948.htm.
A summary of the toxicological endpoints for flumioxazin used for
human risk assessment can be found at https://www.regulations.gov in
document; ``Flumioxazin; Human Health Risk Assessment for the Proposed
Food Use of the Herbicide Flumioxazin on Alfalfa, Asparagus, Dry Beans,
Fruiting Vegetables (Group 8, Including Okra), Melons (Subgroup 9A),
Bushberries (Subgroup 13B), and Tree Nuts (Group 14), and a Request for
an Amended Use on Garlic,'' dated 28 Nov. 2007 in docket ID number EPA-
HQ-OPP-2007-0308-0003.
C. Exposure Assessment
1. Dietary exposure from food and feed uses. In evaluating dietary
exposure to flumioxazin, EPA considered exposure under the petitioned-
for tolerances as well as all existing flumioxazin tolerances in (40
CFR 180.568). EPA assessed dietary exposures from flumioxazin 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. No such effect was
identified for the general population. However, EPA identified
potential acute effects, e.g., cardiovascular effects in offspring, for
the population subgroup, females 13 to 49 years.
In estimating acute dietary exposure, EPA used food consumption
information from the U.S. Department of Agriculture (USDA) 1994-1996
Nationwide Continuing Surveys of Food Intake by Individuals (CSFII). As
to residue levels in food, EPA assumed all foods for which there are
tolerances (current and proposed) were treated (100% crop treated (%CT
or PCT) assumption) and contain tolerance-level residues. Percent crop
treated (PCT) and/or anticipated residues were not used in the acute
risk assessment.
ii. Chronic exposure. In conducting the chronic dietary exposure
assessment EPA used the food consumption data from the USDA 1994-1996,
and 1998 CSFII. As to residue levels in food, EPA assumed all foods for
which there are tolerances (existing and proposed) were treated (100%
crop treated assumption) and contain tolerance-level residues. PCT and/
or anticipated residues were not used in the chronic risk assessment.
iii. Cancer. The Agency has determined that flumioxazin is ``not
likely to be a human carcinogen'' based on the lack of carcinogenicity
in a 2-rat study, an 18 month mouse study, and a battery of mutagenic
studies. Therefore, a quantitative exposure assessment to evaluate
cancer risk is unnecessary.
2. Dietary exposure from drinking water. The Agency lacks
sufficient monitoring data to complete a comprehensive dietary exposure
analysis and risk assessment for flumioxazin and its degradates, 482-HA
and APF, 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 environmental fate characteristics of flumioxazin. 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 drinking water concentrations (EDWCs) of flumioxazin for
acute exposures are estimated to be 34 parts per billion (ppb) for
surface water and 48 ppb for groundwater. The EECs for chronic
exposures are estimated to be 18 ppb for surface water and 48 ppb for
ground water.
Modeled estimates of drinking water concentrations were directly
entered into the dietary exposure model. For acute dietary risk
assessment, the water concentration value of 48 ppb was used to access
the contribution to drinking water. For chronic dietary risk
assessment, the water concentration of value 48 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).
Flumioxazin is not registered for use on any sites that would
result in residential exposure.
4. Cumulative effects from substances with a common mechanism of
toxicity. Section 408(b)(2)(D)(v) of FFDCA requires that, when
considering whether to establish, modify, or revoke a tolerance, the
Agency consider ``available information'' concerning the cumulative
effects of a particular pesticide's residues and ``other substances
that have a common mechanism of toxicity.''
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 flumioxazin and any other
substances and flumioxazin 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 flumioxazin 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 EPA's website 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 (``10X'') tenfold margin of safety for infants and
children in the case of threshold effects to account for pre-natal and
post-natal 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. 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 FQPA safety factor value based on the use of
traditional UFs and/or special FQPA safety factors, as appropriate.
2. Pre-natal and post-natal sensitivity. The pre-natal and post-
natal toxicity database for flumioxazin include the rat and rabbit
developmental toxicity studies and the 2-generation reproduction
toxicity study in rats. There is evidence of quantitative
susceptibility following oral and dermal exposures to rats. Following
in-utero
[[Page 11830]]
exposures, developmental effects (cardiovascular anomalies) were seen
in the absence of maternal toxicity. There is no evidence (quantitative
or qualitative) of susceptibility following in-utero oral exposure in
rabbits. No developmental toxicity was seen at the highest dose tested
(3x the Limit-Dose). There is quantitative evidence of susceptibility
in the multi-generation reproduction study where effects in offspring
were seen at doses lower than those which induced effects in parental
animals.
Although increased pre-natal and post-natal quantitative
susceptibility was seen in rats, the Agency concluded that there is a
low concern and no residual uncertainties for pre-natal and/or post-
natal toxicity effects of flumioxazin because:
i. Developmental toxicity (including cardiovascular abnormalities)
NOAELs and LOAELs from pre-natal exposure are well characterized after
oral and dermal exposure,
ii. The off-spring toxicity NOAEL and LOAEL from post-natal
exposure are well characterized,
iii. The dose selected for risk assessment is protective of all
potential effects.
3. Conclusion. EPA has determined that reliable data show that it
would be safe for infants and children to reduce the FQPA safety factor
to 1X. That decision is based on the following findings:
i. The toxicity database for flumioxazin is complete.
ii. There is no indication that flumioxazin is a neurotoxic
chemical and there is no need for a developmental neurotoxicity study
or additional UFs to account for neurotoxicity.
iii. Although there is quantitative evidence of increased
susceptibility in the prenatal developmental studies and post-natal
multi-generation study in rats, EPA did not identify any residual
uncertainties after establishing toxicity endpoints and traditional UFs
to be used in the risk assessment of flumioxazin. The degree of concern
for pre-natal and/or post-natal toxicity is low.
iv. There are no residual uncertainties identified in the exposure
databases. The dietary food exposure assessments were performed based
on 100%CT and tolerance-level residues for all commodities. By using
these screening-level assumptions, chronic exposures/risks will not be
underestimated. The dietary drinking water assessment utilizes values
generated by models and associated modeling parameters which are
designed to provide conservative, health protective, high-end estimates
of water concentrations. These assessments will not underestimate the
exposure and risks posed by flumioxazin.
E. Aggregate Risks and Determination of Safety
Safety is assessed for acute and chronic risks by comparing
aggregate exposure to the pesticide to the aPAD and cPAD. The aPAD and
cPAD are calculated by dividing the LOC by all applicable UFs. For
linear cancer risks, EPA calculates the probability of additional
cancer cases given aggregate exposure. Short-term, intermediate-term,
and long-term risks are evaluated by comparing aggregate exposure to
the LOC to ensure that the MOE called for by the product of all
applicable UFs is not exceeded.
1. Acute risk. Using the exposure assumptions discussed in this
unit for acute exposure, the acute dietary exposure from food and water
to flumioxazin will occupy 8.0% of the aPAD at the 95th percentile of
exposure for the population group, females 13 to 49 years old (the only
subpopulation for which an acute endpoint was selected).
2. Chronic risk. Using the exposure assumptions described in this
unit for chronic exposure, EPA has concluded that exposure to
flumixazim by the general U.S. population and all population subgroups
have risk estimates below LOC. Exposure to flumioxazin from food and
water will utilize 18% of the cPAD for infants less than 1 year old,
the population group with greatest exposure. The general U.S.
population utilize 6% of the cPAD. There are no residential uses for
flumioxazin that result in chronic residential exposure to flumioxazin.
3. Short-term and intermediate-term risk. Short-term and
intermediate-term aggregate exposure takes into account residential
exposure plus chronic exposure to food and water (considered to be a
background exposure level).
Flumioxazin is not registered for use on any sites that would
result in residential exposure. Therefore, the aggregate risk is the
sum of the risk from food and water, which do not exceed the Agency's
LOC.
4. 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 flumioxazin residues.
IV. Other Considerations
A. Analytical Enforcement Methodology
Adequate enforcement methodology (gas chromatography /nitrogen-
phosphorus detection) is available to enforce the tolerance expression.
The method may be requested from: Chief, Analytical Chemistry Branch,
Environmental Science Center, 701 Mapes Rd., Ft. Meade, MD 20755-5350;
telephone number: (410) 305-2905; e-mail address:
residuemethods@epa.gov.
B. International Residue Limits
There are no established or proposed Canadian, Mexican or Codex
maximum residue levels (MRLs) for residues of flumioxazin in plant
commodities subject to this action.
V. Conclusion
Therefore, tolerances are established for residues of flumioxazin,
2-[7-fluoro-3,4-dihydro-3-oxo-4-(2-propynyl)-2H-1,4-benzoxazin-6-yl]-
4,5,6,7-tetrahydro-1H-isoindole-1,3(2H)-dione in or on, commodities
alfalfa, forage at 3.0 ppm; alfalfa, hay at 8.0 ppm; asparagus at 0.02
ppm; bushberry subgroup 13-07B at 0.02 ppm; melon subgroup 9A at 0.02
ppm; bean, dry seed at 0.05 ppm; vegetable, fruiting, except cucurbits
group 8 at 0.02 ppm; okra at 0.02 ppm; and nut, tree, group 14, at 0.02
ppm.
VI. 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, 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) or Executive Order 13045, entitled Protection of Children
from Environmental Health Risks and Safety Risks (62 FR 19885, April
23, 1997). 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., nor does it require any special considerations
under Executive Order 12898, entitled Federal Actions to Address
Environmental Justice in Minority Populations and Low-Income
Populations (59 FR 7629, February 16, 1994).
[[Page 11831]]
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.
This final rule 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 section 408(n)(4) of FFDCA. 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 6, 2000) do not apply to this rule. In addition, This
rule does not 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).
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).
VII. Congressional Review Act
The Congressional Review Act, 5 U.S.C. 801 et seq., generally
provides that before a rule may take effect, the agency promulgating
the rule must submit a rule report 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: February 22, 2008.
Lois Rossi,
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 180.568 is amended by alphabetically adding the following
commodities to the table in paragraph (a), and by removing the text and
reserving paragraph (b) to read as follows:
Sec. 180.568 Flumioxazin; tolerances for residues.
(a) * * *
------------------------------------------------------------------------
Commodity Parts per million
------------------------------------------------------------------------
Alfalfa, forage...................................... 3.0
Alfalfa, hay......................................... 8.0
* * * * *
Asparagus............................................ 0.02
Bean, dry seed....................................... 0.05
Bushberry subgroup 13-07B............................ 0.02
* * * * *
Melon, subgroup 9A................................... 0.02
Nut, tree, group 14.................................. 0.02
Okra................................................. 0.02
* * * * *
Vegetable, fruiting, group 8......................... 0.02
* * * * *
------------------------------------------------------------------------
(b) Section 18 emergency exemptions. [Reserved]
* * * * *
[FR Doc. E8-4102 Filed 3-4-08; 8:45 am]
BILLING CODE 6560-50-S