Orthosulfamuron; Pesticide Tolerance, 8928-8931 [07-898]
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8928
Federal Register / Vol. 72, No. 39 / Wednesday, February 28, 2007 / Rules and Regulations
(7505P), Office of Pesticide Programs,
Environmental Protection Agency, 1200
Pennsylvania Ave., NW., Washington,
DC 20460–0001; telephone number:
(703) 305–5697; e-mail address:
tompkins.jim@epa.gov.
ENVIRONMENTAL PROTECTION
AGENCY
40 CFR Part 180
[EPA–HQ–OPP–2007–0010; FRL–8113–4]
Orthosulfamuron; Pesticide Tolerance
SUPPLEMENTARY INFORMATION:
Environmental Protection
Agency (EPA).
ACTION: Final rule.
I. General Information
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AGENCY:
SUMMARY: This regulation establishes a
tolerance for residues of
orthosulfamuron in or on rice, grain and
rice, straw at 0.05 parts per million
(ppm). ISAGRO S.p.A., Centro Uffici S.
Siro — Fabbricato D — ALA 3, Via
Caldera, 21, 20153 Milano, Italy,
requested this tolerance 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
February 28, 2007. Objections and
requests for hearings must be received
on or before April 30, 2007, 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–2007–0010. 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: Jim
Tompkins, Registration Division
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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 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 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?
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 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, as
amended by FQPA, any person may file
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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.
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–2007–0010 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 April 30, 2007.
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 your
copies, identified by docket ID number
EPA–HQ–OPP–2007–0010, 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 telephone number is (703) 305–
5805.
II. Background and Statutory Findings
In the Federal Register of July 27,
2005 (70 FR 43421) (FRL–7727–8), 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 petition (PP 5F 6957) by
ISAGRO S.p.A., Centro Uffici S. Siro —
Fabbricato D — ALA 3, Via Caldera, 21,
20153 Milano, Italy. The petition
requested that 40 CFR part 180 be
amended by establishing a tolerance for
residues of the herbicide
orthosulfamuron in or on rice, grain and
rice, straw at 0.05 ppm. That notice
referenced a summary of the petition
prepared by ISAGRO S.p.A., Centro
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Uffici S. Siro — Fabbricato D — ALA 3,
Via Caldera, 21, 20153 Milano, Italy, the
registrant, that is included in the public
docket. There were no comments
received in response to the notice of
filing.
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 FFDCA
and a complete description of the risk
assessment process, see https://
www.epa.gov/fedrgstr/EPA–PEST/1997/
November/Day–26/p30948.htm.
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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 a tolerance for residues of
orthosulfamuron in or on rice, grain and
rice, straw at 0.05 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
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information on the studies received and
the nature of the toxic effects caused by
orthosulfamuron as well as the noobserved-adverse-effect-level (NOAEL)
and the lowest-observed-adverse-effectlevel (LOAEL) from the toxicity studies
can be found at https://
www.regulations.gov in document 0002
(pages 38–44) in docket ID number
EPA–HQ–OPP–2007–0010.
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://
docket.epa.gov/edkpub/index.jsp.
A summary of the toxicological
endpoints for orthosulfamuron used for
human risk assessment can be found at
https://www.regulations.gov in document
2 (pages 19–20) in docket ID number
EPA–HQ–OPP–2007–0010.
C. Exposure Assessment
1. Dietary exposure from food and
feed uses. Risk assessments were
conducted by EPA to assess dietary
exposures from orthosulfamuron 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 effects were
identified in the toxicological studies
for orthosulfamuron; therefore, a
quantitative acute dietary exposure
assessment was not performed.
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ii. Chronic exposure. In conducting
the chronic dietary exposure assessment
EPA used the Dietary Exposure
Evaluation Model software with the
Food Commodity Intake Database
(DEEM-FCIDTM), which incorporates
food consumption data as reported by
respondents in the U.S. 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 chronic
analysis is based on tolerance level
residues and 100% of the crop treated.
iii. Cancer. Orthosulfamuron is
classified as demonstrating ‘‘suggestive
evidence of carcinogenicity’’ based on
thyroid follicular cell adenomas
observed in male rats. The Agency has
concluded that quantification of human
cancer risk is not warranted and the
NOAEL selected for the chronic
reference dose (cRfD) is protective of
cancer effects.
iv. Anticipated residue and percent
crop treated (PCT) information. The
chronic dietary exposure analysis was
based on tolerance level residues and
100 PCT assumptions.
2. Dietary exposure from drinking
water. The Agency lacks sufficient
monitoring exposure data to complete a
comprehensive dietary exposure
analysis and risk assessment for
orthosulfamuron 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
orthosulfamuron. Further information
regarding EPA drinking water models
used in pesticide exposure assessment
can be found at https://docket.epa.gov/
edkpub/index.jsp
Based on the interim rice model and
screening concentration in groundwater
(SCI-GROW) models, the estimated
environmental concentration (EECs) of
orthosulfamuron in drinking water for
chronic exposures is estimated to be
40.5 parts per billion (ppb) for surface
water and 0.611 ppb for groundwater.
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).
Orthosulfamuron 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
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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
orthosulfamuron and any other
substances and orthosulfamuron 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
orthosulfamuron 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 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 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 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. 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 UFs and/
or special FQPA safety factors, as
appropriate.
2. Prenatal and postnatal sensitivity.
There is no concern for increased
quantitative and/or qualitative
susceptibility after exposure to
orthosulfamuron in developmental
toxicity studies in rats and rabbits, or a
reproduction study in rats. In the
developmental studies, there was no
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treatment-related maternal or
developmental toxicity observed. In the
reproduction study, decreased motor
activity was seen in 6–week old males
(F1) at 354.5 milligrams/kilograms/day
(mg/kg/day). However, the offspring
effects were observed in the presence of
maternal toxicity (kidney lesions), seen
in adult females of both generations (F0
and F1). The NOAEL (5 mg/kg/day)
selected for the cRfD is lower (70X) than
the dose at which the motor activity was
observed and; thus, considered
protective of the 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
orthosulfamuron is complete.
ii. There is no indication that
orthosulfamuron is a neurotoxic
chemical and there is no need for a
developmental neurotoxicity study or
additional UFs to account for
neurotoxicity.
iii. There is no evidence that
orthosulfamuron results in increased
susceptibility in in utero rats or rabbits
in the prenatal developmental studies or
in young rats in the 2-generation
reproduction study.
iv. There are no residual uncertainties
identified in the exposure databases.
The dietary food exposure assessments
were performed based on 100 PCT and
tolerance-level residues. Conservative
groundwater and surface water
modeling estimates were used. Similarly
conservative. These assessments will
not underestimate the exposure and
risks posed by orthosulfamuron.
E. Aggregate Risks and Determination of
Safety
1. Acute risk. Review of applicable
toxicity studies indicated that
orthosulfamuron is not expected to pose
an acute risk.
2. Short-term risk. Orthosulfamuron 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.
3. Intermediate-term risk.
Intermediate-term aggregate exposure
takes into account residential exposure
plus chronic exposure to food and water
(considered to be background exposure
level).
Orthosulfamuron 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.
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4. Chronic risk. EPA considers
chronic aggregate risk to consist of risks
resulting from exposure to residues in
food, drinking water, and residues
resulting from residential applications.
As there are no residential uses for
orthosulfamuron, chronic aggregate risk
consists of risks resulting from exposure
to residues in food and drinking water
alone, which do not exceed the
Agency’s LOC.
5. Aggregate cancer risk for U.S.
population. The long-term chronic risk
assessment outlined in this unit is
considered to be protective of cancer
effects.
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
orthosulfamuron residues.
IV. Other Considerations
A. Analytical Enforcement Methodology
An adequate high performance liquid
chromatography-mass spectrometry
analytical method for enforcement
purposes is available. The method may
be requested from: Chief, Analytical
Chemistry Branch, Environmental
Science Center, 701 Mapes Rd., Ft
Meade, Maryland 20755–5350.
Telephone number: (410) 305–2905; email address: residuemethods@epa.gov.
B. International Residue Limits
No Codex maximum residue limits
(MRLs) have been established for
residues of orthosulfamuron on any
crops at this time.
V. Conclusion
Therefore, the tolerance is established
for residues of orthosulfamuron, in or
on rice, grain and rice, straw at 0.05
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 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
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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’’
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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.
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 16, 2007.
James Jones,
Director, 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 180.625 is added to read as
follows:
I
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8931
§180.625 Orthosulfamuron; tolerances for
residues.
(a) General. Tolerances are
established for residues of
orthosulfamuron 1-(4,6dimethoxypyrimidin-2-yl)-3-[2(dimethylcarbamoyl)- phenylsulfamoyl]
urea) per se in or on the following
commodities:
Commodity
Parts per million
Rice, grain ......................
Rice, straw ......................
0.05
0.05
(b) Section 18 emergency exemptions.
[Reserved]
(c) Tolerances with regional
registrations. [Reserved]
(d) Indirect and inadvertant residues.
[Reserved]
[FR Doc. 07–898 Filed 2–23–07; 2:13 pm]
BILLING CODE 6560–50–S
DEPARTMENT OF THE INTERIOR
Fish and Wildlife Service
50 CFR Part 21
RIN 1018–AI92
Migratory Bird Permits; Take of
Migratory Birds by the Armed Forces
Fish and Wildlife Service,
Interior.
ACTION: Final rule.
AGENCY:
SUMMARY: The Migratory Bird Treaty Act
(MBTA) prohibits the taking, killing, or
possessing of migratory birds unless
permitted by regulations promulgated
by the Secretary of the Interior. While
some courts have held that the MBTA
does not apply to Federal agencies, in
July 2000, the United States Court of
Appeals for the District of Columbia
Circuit ruled that the prohibitions of the
MBTA do apply to Federal agencies,
and that a Federal agency’s taking and
killing of migratory birds without a
permit violated the MBTA. On March
13, 2002, the United States District
Court for the District of Columbia ruled
that military training exercises of the
Department of the Navy that
incidentally take migratory birds
without a permit violate the MBTA.
On December 2, 2002, the President
signed the 2003 National Defense
Authorization Act (Authorization Act).
Section 315 of the Authorization Act
provides that, not later than one year
after its enactment, the Secretary of the
Interior (Secretary) shall exercise his/
her authority under Section 704(a) of
the MBTA to prescribe regulations to
exempt the Armed Forces for the
E:\FR\FM\28FER1.SGM
28FER1
Agencies
[Federal Register Volume 72, Number 39 (Wednesday, February 28, 2007)]
[Rules and Regulations]
[Pages 8928-8931]
From the Federal Register Online via the Government Printing Office [www.gpo.gov]
[FR Doc No: 07-898]
[[Page 8928]]
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ENVIRONMENTAL PROTECTION AGENCY
40 CFR Part 180
[EPA-HQ-OPP-2007-0010; FRL-8113-4]
Orthosulfamuron; Pesticide Tolerance
AGENCY: Environmental Protection Agency (EPA).
ACTION: Final rule.
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SUMMARY: This regulation establishes a tolerance for residues of
orthosulfamuron in or on rice, grain and rice, straw at 0.05 parts per
million (ppm). ISAGRO S.p.A., Centro Uffici S. Siro -- Fabbricato D --
ALA 3, Via Caldera, 21, 20153 Milano, Italy, requested this tolerance
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 February 28, 2007. Objections and
requests for hearings must be received on or before April 30, 2007, 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-2007-0010. 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: Jim Tompkins, Registration Division
(7505P), Office of Pesticide Programs, Environmental Protection Agency,
1200 Pennsylvania Ave., NW., Washington, DC 20460-0001; telephone
number: (703) 305-5697; e-mail address: tompkins.jim@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 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 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?
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 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, 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. 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-2007-0010 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 April 30, 2007.
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 your copies, identified by docket ID
number EPA-HQ-OPP-2007-0010, 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 telephone number is (703) 305-5805.
II. Background and Statutory Findings
In the Federal Register of July 27, 2005 (70 FR 43421) (FRL-7727-
8), 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 petition (PP 5F
6957) by ISAGRO S.p.A., Centro Uffici S. Siro -- Fabbricato D -- ALA 3,
Via Caldera, 21, 20153 Milano, Italy. The petition requested that 40
CFR part 180 be amended by establishing a tolerance for residues of the
herbicide orthosulfamuron in or on rice, grain and rice, straw at 0.05
ppm. That notice referenced a summary of the petition prepared by
ISAGRO S.p.A., Centro
[[Page 8929]]
Uffici S. Siro -- Fabbricato D -- ALA 3, Via Caldera, 21, 20153 Milano,
Italy, the registrant, that is included in the public docket. There
were no comments received in response to the notice of filing.
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 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 a tolerance for residues of orthosulfamuron in
or on rice, grain and rice, straw at 0.05 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 orthosulfamuron as well as the no-
observed-adverse-effect-level (NOAEL) and the lowest-observed-adverse-
effect-level (LOAEL) from the toxicity studies can be found at https://
www.regulations.gov in document 0002 (pages 38-44) in docket ID number
EPA-HQ-OPP-2007-0010.
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://docket.epa.gov/edkpub/index.jsp.
A summary of the toxicological endpoints for orthosulfamuron used
for human risk assessment can be found at https://www.regulations.gov in
document 2 (pages 19-20) in docket ID number EPA-HQ-OPP-2007-0010.
C. Exposure Assessment
1. Dietary exposure from food and feed uses. Risk assessments were
conducted by EPA to assess dietary exposures from orthosulfamuron 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 effects were
identified in the toxicological studies for orthosulfamuron; therefore,
a quantitative acute dietary exposure assessment was not performed.
ii. Chronic exposure. In conducting the chronic dietary exposure
assessment EPA used the Dietary Exposure Evaluation Model software with
the Food Commodity Intake Database (DEEM-FCID\TM\), which incorporates
food consumption data as reported by respondents in the U.S. 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 chronic analysis is based on tolerance
level residues and 100% of the crop treated.
iii. Cancer. Orthosulfamuron is classified as demonstrating
``suggestive evidence of carcinogenicity'' based on thyroid follicular
cell adenomas observed in male rats. The Agency has concluded that
quantification of human cancer risk is not warranted and the NOAEL
selected for the chronic reference dose (cRfD) is protective of cancer
effects.
iv. Anticipated residue and percent crop treated (PCT) information.
The chronic dietary exposure analysis was based on tolerance level
residues and 100 PCT assumptions.
2. Dietary exposure from drinking water. The Agency lacks
sufficient monitoring exposure data to complete a comprehensive dietary
exposure analysis and risk assessment for orthosulfamuron 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 orthosulfamuron. Further information regarding EPA
drinking water models used in pesticide exposure assessment can be
found at https://docket.epa.gov/edkpub/index.jsp
Based on the interim rice model and screening concentration in
groundwater (SCI-GROW) models, the estimated environmental
concentration (EECs) of orthosulfamuron in drinking water for chronic
exposures is estimated to be 40.5 parts per billion (ppb) for surface
water and 0.611 ppb for groundwater.
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).
Orthosulfamuron 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
[[Page 8930]]
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 orthosulfamuron and any
other substances and orthosulfamuron 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 orthosulfamuron
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 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 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 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. 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 UFs and/or special FQPA
safety factors, as appropriate.
2. Prenatal and postnatal sensitivity. There is no concern for
increased quantitative and/or qualitative susceptibility after exposure
to orthosulfamuron in developmental toxicity studies in rats and
rabbits, or a reproduction study in rats. In the developmental studies,
there was no treatment-related maternal or developmental toxicity
observed. In the reproduction study, decreased motor activity was seen
in 6-week old males (F1) at 354.5 milligrams/kilograms/day (mg/kg/day).
However, the offspring effects were observed in the presence of
maternal toxicity (kidney lesions), seen in adult females of both
generations (F0 and F1). The NOAEL (5 mg/kg/day) selected for the cRfD
is lower (70X) than the dose at which the motor activity was observed
and; thus, considered protective of the 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 orthosulfamuron is complete.
ii. There is no indication that orthosulfamuron is a neurotoxic
chemical and there is no need for a developmental neurotoxicity study
or additional UFs to account for neurotoxicity.
iii. There is no evidence that orthosulfamuron results in increased
susceptibility in in utero rats or rabbits in the prenatal
developmental studies or in young rats in the 2-generation reproduction
study.
iv. There are no residual uncertainties identified in the exposure
databases. The dietary food exposure assessments were performed based
on 100 PCT and tolerance-level residues. Conservative groundwater and
surface water modeling estimates were used. Similarly conservative.
These assessments will not underestimate the exposure and risks posed
by orthosulfamuron.
E. Aggregate Risks and Determination of Safety
1. Acute risk. Review of applicable toxicity studies indicated that
orthosulfamuron is not expected to pose an acute risk.
2. Short-term risk. Orthosulfamuron 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.
3. Intermediate-term risk. Intermediate-term aggregate exposure
takes into account residential exposure plus chronic exposure to food
and water (considered to be background exposure level).
Orthosulfamuron 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. Chronic risk. EPA considers chronic aggregate risk to consist of
risks resulting from exposure to residues in food, drinking water, and
residues resulting from residential applications. As there are no
residential uses for orthosulfamuron, chronic aggregate risk consists
of risks resulting from exposure to residues in food and drinking water
alone, which do not exceed the Agency's LOC.
5. Aggregate cancer risk for U.S. population. The long-term chronic
risk assessment outlined in this unit is considered to be protective of
cancer effects.
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 orthosulfamuron residues.
IV. Other Considerations
A. Analytical Enforcement Methodology
An adequate high performance liquid chromatography-mass
spectrometry analytical method for enforcement purposes is available.
The method may be requested from: Chief, Analytical Chemistry Branch,
Environmental Science Center, 701 Mapes Rd., Ft Meade, Maryland 20755-
5350. Telephone number: (410) 305-2905; e-mail address:
residuemethods@epa.gov.
B. International Residue Limits
No Codex maximum residue limits (MRLs) have been established for
residues of orthosulfamuron on any crops at this time.
V. Conclusion
Therefore, the tolerance is established for residues of
orthosulfamuron, in or on rice, grain and rice, straw at 0.05 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 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
[[Page 8931]]
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.
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 16, 2007.
James Jones,
Director, 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 180.625 is added to read as follows:
Sec. 180.625 Orthosulfamuron; tolerances for residues.
(a) General. Tolerances are established for residues of
orthosulfamuron 1-(4,6-dimethoxypyrimidin-2-yl)-3-[2-
(dimethylcarbamoyl)- phenylsulfamoyl] urea) per se in or on the
following commodities:
------------------------------------------------------------------------
Commodity Parts per million
------------------------------------------------------------------------
Rice, grain.......................................... 0.05
Rice, straw.......................................... 0.05
------------------------------------------------------------------------
(b) Section 18 emergency exemptions. [Reserved]
(c) Tolerances with regional registrations. [Reserved]
(d) Indirect and inadvertant residues. [Reserved]
[FR Doc. 07-898 Filed 2-23-07; 2:13 pm]
BILLING CODE 6560-50-S