Pendimethalin; Pesticide Tolerance, 56369-56374 [06-8254]
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Federal Register / Vol. 71, No. 187 / Wednesday, September 27, 2006 / Rules and Regulations
4. Subpart G of part 82 is amended by
adding Appendix P to read as follows:
I
56369
Appendix P to subpart G of part 82Substitutes listed in the September 27,
2006 Final Rule, effective November 27,
2006
FIRE SUPPRESSION AND EXPLOSION PROTECTION SECTOR—TOTAL FLOODING AGENTS—ACCEPTABLE SUBJECT TO
NARROWED USE LIMITS
End-use
Substitute
Decision
Conditions
Further information
Total flooding .........
Gelled Halocarbon/Dry Chemical Suspension with any agent other than
ammonium polyphosphate or sodium
bicarbonate
additive
(Envirogel with sodium bicarbonate
additive).
Acceptable subject
to narrowed use
limits.
For use only in
normally unoccupied areas.
Use of this agent should be in accordance with the safety guidelines in
the latest edition of the NFPA 2001
Standard for Clean Agent Fire Extinguishing Systems, for whichever
hydrofluorocarbon gas is employed.
Envirogel is listed as a streaming substitute under the generic name
Gelled Halocarbon/Dry Chemical
Suspension. Envirogel was also
previously listed as a total flooding
substitute under the same generic
name.
EPA has found Envirogel with the ammonium polyphosphate additive and
Envirogel with the sodium bicarbonate additive to be acceptable as
total flooding agents in both occupied and unoccupied areas.
See additional comments 1, 2, 3, 4, 5
Additional comments:
1—Should conform to relevant OSHA requirements, including 29 CFR 1910, subpart L, Sections 1910.160 and 1910.162.
2—Per OSHA requirements, protective gear (SCBA) should be available in the event personnel should reenter the area.
3—Discharge testing should be strictly limited to that which is essential to meet safety or performance requirements.
4—The agent should be recovered from the fire protection system in conjunction with testing or servicing, and recycled for later use or destroyed.
5—EPA has no intention of duplicating or displacing OSHA coverage related to the use of personal protective equipment (e.g., respiratory protection), fire protection, hazard communication, worker training or any other occupational safety and health standard with respect to halon
substitutes.
[FR Doc. E6–15831 Filed 9–26–06; 8:45 am]
BILLING CODE 6560–50–P
ENVIRONMENTAL PROTECTION
AGENCY
40 CFR Part 180
[EPA–HQ–OPP–2006–0645; FRL–8092–6]
Pendimethalin; Pesticide Tolerance
Environmental Protection
Agency (EPA).
ACTION: Final rule.
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AGENCY:
SUMMARY: This regulation establishes a
tolerance for combined residues of
pendimethalin, N-(1-ethylpropyl)-3,4dimethyl-2,6-dinitrobenzenamine, and
its metabolite 4-[(1-ethylpropyl)amino]2-methyl-3,5-dinitrobenyzl alcohol in or
on alfalfa, forage; alfalfa, hay; alfalfa,
seed; apple, wet pomace; fruit, pome,
group 11; fruit, stone, group 12;
juneberry; leek; onion, green; onion,
welsh; pomegranate; shallot; strawberry;
vegetable, fruiting, group 8; wheat,
grain; wheat, forage; wheat, hay; and
wheat, straw. BASF Corporation and
Interregional Research Project Number 4
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(IR-4) requested these tolerances under
the Federal Food, Drug, and Cosmetic
Act (FFDCA), as amended by the Food
Quality Protection Act of 1996 (FQPA).
DATES: This regulation is effective
September 27, 2006. Objections and
requests for hearings must be received
on or before November 27, 2006 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–2006–0645. All documents in the
docket are listed in the index for the
docket. 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–
PO 00000
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4400, One Potomac Yard (South
Building), 2777 S. Crystal Drive,
Arlington, VA. The Docket Facility is
open from 8:30 a.m. to 4 p.m., Monday
through Friday, excluding legal
holidays. The Docket telephone number
is (703) 305–5805.
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.
FOR FURTHER INFORMATION CONTACT:
SUPPLEMENTARY INFORMATION:
I. General Information
A. Does this Action Apply to Me?
You may be potentially affected by
this action if you are an agricultural
producer, food manufacturer, or
pesticide manufacturer. Potentially
affected entities may include, but are
not limited to:
• Crop production (NAICS 111), e.g.,
agricultural workers; greenhouse,
nursery, and floriculture workers;
farmers.
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• Animal production (NAICS 112),
e.g., cattle ranchers and farmers, dairy
cattle farmers, livestock farmers.
• Food manufacturing (NAICS 311),
e.g., agricultural workers; farmers;
greenhouse, nursery, and floriculture
workers; ranchers; pesticide applicators.
• Pesticide manufacturing (NAICS
32532), e.g., agricultural workers;
commercial applicators; farmers;
greenhouse, nursery, and floriculture
workers; residential users.
This listing is not intended to be
exhaustive, but rather provides a guide
for readers regarding entities likely to be
affected by this action. Other types of
entities not listed in this unit could also
be affected. The North American
Industrial Classification System
(NAICS) codes have been provided to
assist you and others in determining
whether this action might apply to
certain entities. If you have any
questions regarding the applicability of
this action to a particular entity, consult
the person listed under FOR FURTHER
INFORMATION CONTACT.
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B. How Can I Access Electronic Copies
of this Document?
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 the FFDCA, as
amended by the 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–2006–0645 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 November 27, 2006.
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
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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–2006–0645 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 Building), 2777 S.
Crystal Drive, 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 June 14,
2006 (71 FR 34341–34342) (FRL–8072–
1), EPA issued a notice pursuant to
section 408(d)(3) of FFDCA, 21 U.S.C.
346a(d)(3), announcing the filing of
pesticide petitions PP 0E6175
(vegetable, fruiting, group 8), PP 2E6450
(fruit, pome, group 11; apple, wet
pomace; and juneberry), PP 2E6464
(fruit, stone, group 12), PP 2E6449
(pomegranates), by Interregional
Research Project Number 4 (IR–4), 681
U.S. Highway #1 South, New
Brunswick, NJ 08902–390.
In the Federal Register of June 14,
2006 (71 FR 34344–34345) (FRL–8072–
7), EPA issued a notice pursuant to
section 408(d)(3) of FFDCA, 21 U.S.C.
346a(d)(3), announcing the filing of
pesticide petitions PP 5E6927 (onion,
green; onion, welsh; leek; and shallot),
PP 5E6928 (strawberry), by Interregional
Research Project Number 4 (IR–4), 681
U.S. Highway #1 South, New
Brunswick, NJ 08902–390.
In the Federal Register of August 18,
2006 (71 FR 47810–47811 (FRL–8084–
71), EPA issued a notice pursuant to
section 408(d)(3) of FFDCA, 21 U.S.C.
346a(d)(3), announcing the filing of
pesticide petitions PP 4F6870 (wheat,
grain; wheat, forage; wheat, hay; and
wheat, straw), and PP 5F6961 (alfalfa,
forage; alfalfa, hay; and alfalfa, seed) by
BASF Corporation Agricultural
Products, P.O. Box 13528, Research
Triangle Park, NC 27709–3528.
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These petitions requested that 40 CFR
180.361 be amended by establishing a
tolerance for combined residues of the
herbicide pendimethalin, N-(1ethylpropyl)-3,4-dimethyl-2,6dinitrobenzenamine, and its metabolite
4-[(1-ethylpropyl)amino]-2-methyl-3,5dinitrobenyzl alcohol in or on
vegetables, fruiting, group 8 at 0.10 ppm
(PP 0E6175), fruit, pome, group 11 at
0.10 ppm; apple, wet pomace at 0.20
ppm; and juneberry at 0.10 ppm (PP
2E6450), fruit, stone, group 12 at 0.10
ppm (PP 2E6464), pomergranate at 0.10
ppm (PP 2E6449), onion, green at 0.20
ppm; onion, welsh at 0.20 ppm, leek at
0.20 ppm; and shallot at 0.2 ppm (PP
5E6927), strawberry at 0.10 ppm (PP
5E6928), wheat, grain at 0.10 ppm;
wheat, forge at 3.0 ppm; wheat, hay at
0.60 ppm; and wheat, straw at 0.30
ppm; (PP 4F6870), alfalfa, forage at 3.0
ppm; alfalfa, hay at 4.0 ppm; and alfalfa,
seed at 0.10 ppm (PP 5F6961). These
notices included a summary of the
petition prepared by IR-4 and BASF
Corporation, the registrant. One
comment was received in response to
the notices of filing. EPA’s response to
this comment is discussed in Unit IV.C.
Section 408(b)(2)(A)(i) of FFDCA
allows EPA to establish a tolerance (the
legal limit for a pesticide chemical
residue in or on a food) only if EPA
determines that the tolerance is ‘‘safe.’’
Section 408(b)(2)(A)(ii) of FFDCA
defines ‘‘safe’’ to mean that ‘‘there is a
reasonable certainty that no harm will
result from aggregate exposure to the
pesticide chemical residue, including
all anticipated dietary exposures and all
other exposures for which there is
reliable information.’’ This includes
exposure through drinking water and in
residential settings, but does not include
occupational exposure. Section
408(b)(2)(C) of FFDCA requires EPA to
give special consideration to exposure
of infants and children to the pesticide
chemical residue in establishing a
tolerance and to ‘‘ensure that there is a
reasonable certainty that no harm will
result to infants and children from
aggregate exposure to the pesticide
chemical residue....’’
EPA performs a number of analyses to
determine the risks from aggregate
exposure to pesticide residues. For
further discussion of the regulatory
requirements of section 408 of the
FFDCA and a complete description of
the risk assessment process, see https://
www.epa.gov/fedrgstr/EPA-PEST/1997/
November/Day-26/p30948.htm.
III. Aggregate Risk Assessment and
Determination of Safety
Consistent with section 408(b)(2)(D)
of FFDCA, EPA has reviewed the
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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 combined
residues of pendimethalin, N-(1ethylpropyl)-3,4-dimethyl-2,6dinitrobenzenamine, and its metabolite
4-[(1-ethylpropyl)amino]-2-methyl-3,5dinitrobenyzl alcohol in or on
vegetables, fruiting, group 8 at 0.10
ppm; fruit, pome, group 11 at 0.10 ppm;
apple, wet pomace at 0.20 ppm;
juneberry at 0.10 ppm; fruit, stone,
group 12 at 0.10 ppm; pomergranate at
0.10 ppm; onion, green at 0.20 ppm;
onion, welsh at 0.20 ppm; leek at 0.20
ppm, shallot at 0.2 ppm; strawberry at
0.10 ppm; wheat, grain at 0.10 ppm;
wheat, forge at 3.0 ppm; wheat, hay at
0.60 ppm, wheat, straw at 0.30 ppm;
alfalfa, forage at 3.0 ppm; alfalfa, hay at
4.0 ppm; and alfalfa, seed at 0.10 ppm.
EPA’s assessment of exposures and risks
associated with establishing the
tolerance follows.
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A. Toxicological Profile
EPA has evaluated the available
toxicity data and considered its validity,
completeness, and reliability as well as
the relationship of the results of the
studies to human risk. EPA has also
considered available information
concerning the variability of the
sensitivities of major identifiable
subgroups of consumers, including
infants and children. Specific
information on the studies received and
the nature of the toxic effects caused by
pendimethalin as well as the noobserved-adverse-effect-level (NOAEL)
and the lowest-observed-adverse-effectlevel (LOAEL) from the toxicity studies
can be found at http:/
www.regulations.gov/fdmspublic/
component/main, see Docket OPP–
2005–0056–0002.
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
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of the human population as well as
other unknowns.
The linear default risk methodology
(Q*) is the primary method currently
used by the Agency to quantify nonthreshold hazards such as cancer. The
Q* approach assumes that any amount
of exposure will lead to some degree of
cancer risk, estimates risk in terms of
the probability of occurrence of
additional cancer cases. More
information can be found on the general
principles EPA uses in risk
characterization at https://www.epa.gov/
fedrgstr/EPA-PEST/1997/November/
Day-26/p30948.htm.
A summary of the toxicological
endpoints for pendimethalin used for
human risk assessment is discussed in
Unit III.B. of the final rule published in
the Federal Register of April 12, 2006,
70 FR 18628–18635 (FRL–7770–4)
C. Exposure Assessment
1. Dietary exposure from food and
feed uses. Tolerances have been
established (40 CFR 180.361) for the
combined residues of pendimethalin, N(1-ethylpropyl)-3,4-dimethyl-2,6dinitrobenzenamine, and its metabolite
4-[(1-ethylpropyl)amino]-2-methyl-3,5dinitrobenyzl alcohol, in or on a variety
of raw agricultural commodities. Risk
assessments were conducted by EPA to
assess dietary exposures from
pendimethalin 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 one-day or
single exposure. No such effects were
identified in the toxicological studies
for pendimethalin; therefore, a
quantitative acute dietary exposure
assessment is unnecessary.
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 USDA 1994–1996
and 1998 Nationwide Continuing
Surveys of Food Intake by Individuals
(CSFII), and accumulated exposure to
the chemical for each commodity.
Tolerance-level residues were assumed
for all food commodities with current
and proposed pendimethalin tolerances,
and it was assumed that all of the crops
included in the analysis were treated
(i.e., 100% crop treated). These
assumptions result in highly
conservative estimates of dietary
exposure and risk.
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iii. Cancer. Pendimethalin is
classified ‘‘Group C,’’ possible human
carcinogen, chemical based on a
statistically significant increased trend
and pair-wise comparison between the
high dose group and controls for thyroid
follicular cell adenomas in male and
female rats. The Agency used a nonlinear approach (i.e., reference dose
(RfD) approach) since mode of action
studies are available that demonstrate
that the thyroid tumors are due to a
thyroid-pituitary imbalance, and also
since pendimethalin was shown to be
non-mutagenic in mammalian somatic
cells and germ.
2. Dietary exposure from drinking
water. The Agency lacks sufficient
monitoring exposure data to complete a
comprehensive dietary exposure
analysis and risk assessment for
pendimethalin 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
pendimethalin. 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 Pesticide Root Zone
Model-Exposure Analysis Modeling
System (PRZM-EXAMS) and screening
concentration in ground water (SCIGROW) models, the estimated
environmental concentrations (EECs) of
pendimethalin for acute exposures are
estimated to be 39 parts per billion
(ppb) for surface water and 0.024 ppb
for ground water. The EECs for chronic
exposures are estimated to be 4.8 ppb
for surface water and 0.024 ppb for
ground water. Modeled estimates of
drinking water concentrations were
directly entered into the dietary
exposure model (DEEM-FCIDTM,
Version 2.03). An acute dietary risk
assessment for the peak water
concentration value was not done
because no such effects were identified
in the toxicological studies for
pendimethalin. For chronic dietary risk
assessment, an estimated drinking water
concentration (EDWC) of 0.039 ppm, the
1 in 10 year annual peak concentration
in surface water as calculated by PRZMEXAMS modeling, resulting from a
single application of pendimethalin to
apples at a rate of 4.0 lb of active
ingredient/acre, was entered into DEEM.
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
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flea and tick control on pets).
Pendimethalin is currently registered for
use on the following residential nondietary sites: Landscapes, grounds
plantings, ornamental crops, turf grass,
and lawns. The risk assessment for
residential non-dietary sites is discussed
in Unit III.C.3. of the final rule
published in the Federal Register of
April 12, 2006, FR Page 18628–18635
(FRL–7770–4)
4. Cumulative effects from substances
with a common mechanism of toxicity.
Section 408(b)(2)(D)(v) of the FFDCA
requires that, when considering whether
to establish, modify, or revoke a
tolerance, the Agency consider
‘‘available information’’ concerning the
cumulative effects of a particular
pesticide’s residues and ‘‘other
substances that have a common
mechanism of toxicity.’’
Unlike other pesticides for which EPA
has followed a cumulative risk approach
based on a common mechanism of
toxicity, EPA has not made a common
mechanism of toxicity finding as to
pendimethalin and any other substances
and pendimethalin 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 pendimethalin 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 data base on
toxicity and exposure unless EPA
determines based on reliable data that a
different margin of safety will be safe for
infants and children. Margins of safety
are incorporated into EPA risk
assessments either directly through use
of a margin of exposure (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
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reliable data do not support the choice
of a different factor, or, if reliable data
are available, EPA uses a different
additional safety factor value based on
the use of traditional uncertainty factors
and/or special FQPA safety factors, as
appropriate.
2. Prenatal and postnatal sensitivity.
The data base for pendimethalin does
not indicate a potential for increased
toxicological sensitivity from either
prenatal or postnatal exposures. No
developmental toxicity was observed in
either the rat or rabbit developmental
toxicity studies, nor was there evidence
in the two-generation reproduction
study of developmental or reproductive
toxicity at dose levels below those in
which parental toxicity was observed.
There was no neurotoxicity observed in
the submitted toxicity studies.
Therefore, a developmental
neurotoxicity (DNT) study is not
required.
Available data show the thyroid is a
target organ for pendimethalin. The
endpoints and doses selected for risk
assessment were based on the most
sensitive effect, thyroid toxicity, which
was well-characterized in both chronic
and subchronic toxicity studies on the
basis of clear NOAELs and LOAELs. In
addition, the exposure data used to
evaluate risks for the general U.S.
population and infants and children are
conservative, and therefore the
calculated risks are considered to be
protective.
3. Conclusion. There was no evidence
of qualitative or quantitative
susceptibility in the submitted data.
Additionally, exposure estimates are
based on very conservative data and
assumptions that will overstate
exposure to pendimethalin. There is,
however, a concern that perturbation of
thyroid homeostatis may lead to
hypothyroidism, and possibly result in
adverse effects on the developing
nervous system. Since thyroid toxicity
parameters were not measured in the
developmental toxicity studies, the
Agency has requested a developmental
thyroid assay be conducted to evaluate
the impact of pendimethalin on thyroid
hormones, structure, and/or thyroid
hormone homeostasis during
development. The Agency has retained
the additional 10X FQPA safety factor in
the form of a database uncertainty factor
(UFDB) for the lack of the study, to be
applied in determining pendimethalin
risks.
E. Aggregate Risks and Determination of
Safety
1. Acute risk. No toxic effects
attributed to a single dose were
identified for pendimethalin. Therefore
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an acute risk is not anticipated for this
chemical.
2. Chronic risk. Using the exposure
assumptions described in this unit for
chronic exposure, EPA has concluded
that exposure to pendimethalin from
food and drinking water will utilize
11% of the chronic population adjusted
dose (cPAD) for the U.S. population,
19% of the cPAD for infants, and 26%
of the cPAD for Children 1 to 2 years of
age. Based on the use pattern, chronic
residential exposure to residues of
pendimethalin is not expected.
3. Short-term risk. Short-term
aggregate exposure takes into account
residential exposure plus chronic
exposure to food and water (considered
to be a background exposure level).
Pendimethalin is currently registered
for use that could result in short-term
residential exposure and the Agency has
determined that it is appropriate to
aggregate chronic food and water and
short-term exposures for pendimethalin.
Using the exposure assumptions
described in this unit for short-term
exposures, EPA has concluded that
food, drinking water and residential
exposures aggregated result in aggregate
MOEs of 580 for adult males, 520 for
females 13 years or older, and 310 for
children 1 to 2 years old. These
aggregate MOEs do not exceed the
Agency’s level of concern (MOE 300) for
aggregate exposure to food, drinking
water and residential uses. See 71 FR
18628–18630, April 12, 2006.
4. Intermediate-term risk.
Intermediate-term aggregate exposure
takes into account residential exposure
plus chronic exposure to food and water
(considered to be a background
exposure level). Based on the currently
registered and requested uses, there are
no scenarios that are likely to result in
intermediate-term exposure (30 to 180
days, continuously). Therefore an
intermediate-term risk is not anticipated
for pendimethalin.
5. Aggregate cancer risk for U.S.
population. The Agency determined
that the 0.10 mg/kg/day RfD for chronic
risks, is protective of both the chronic,
non-carcinogenic effects as well as the
carcinogenic effect seen in the rat.
Accordingly, based on the risk estimates
for chronic risk above, EPA concludes
that aggregate chronic exposure to
pendimethalin is not expected to pose a
cancer risk of concern.
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
pendimethalin and its metabolite
residues.
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Federal Register / Vol. 71, No. 187 / Wednesday, September 27, 2006 / Rules and Regulations
IV. Other Considerations
A. Analytical Enforcement Methodology
Adequate methods are available for
data collection and tolerance
enforcement for existing and proposed
uses of pendimethalin. Methods I
through IV in PAM Vol. II are gas
chromatography/electron capture (GC/
ECD) methods. Methods used for data
collection are essentially the same as the
PAM Vol. II methods, and have been
adequately validated.
The FDA PESTDATA database (PAM
Volume I, Appendix I) indicates that
pendimethalin is completely recovered
(>80%) by Multiresidue Methods
Section 302 (Luke method; Protocol D)
and 303 (Mills, Onley, Gaither method;
Protocol E, nonfatty), and partially
recovered (50–80%) by Multiresidue
Method Section 304 (Mills fatty food
method; Protocol E, fatty). 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
Codex maximum residue limits (MRLs)
for pendimethalin residues. Therefore,
there are no questions of compatibility
with respect to Codex MRLs and U.S.
tolerances.
sroberts on PROD1PC70 with RULES
C. Response to Comments
One comment was received in
response to the notices of filing for this
action. The comment contained no
scientific data or other substantive
evidence to rebut the Agency’s
conclusion that there is a reasonable
certaintythat no harm will result from
aggregate exposure to pendimethalin
from the establishment of these
tolerances.
V. Conclusion
Therefore, tolerances are established
for combined residues of
pendimethalin, N-(1-ethylpropyl)-3,4dimethyl-2,6-dinitrobenzenamine, and
its metabolite 4-[(1-ethylpropyl)amino]2-methyl-3,5-dinitrobenyzl alcohol in or
on alfalfa, forage at 3.0 ppm; alfalfa, hay
at 4.0 ppm; and alfalfa, seed at 0.10
ppm; fruit, pome, group 11 at 0.10 ppm;
apple, wet pomace at 0.20 ppm and
juneberry at 0.10 ppm; fruit, stone,
group 12 at 0.10 ppm; pomergranate at
0.10 ppm; onion, green at 0.20 ppm;
onion, welsh at 0.20 ppm; leek at 0.20
ppm; and shallot at 0.2 ppm; strawberry
at 0.10 ppm; wheat, grain at 0.10 ppm;
wheat, forge at 3.0 ppm; wheat, hay at
0.60 ppm; wheat, straw at 0.30 ppm;
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16:20 Sep 26, 2006
Jkt 208001
and vegetables, fruiting, group 8 at 0.10
ppm.
VI. Statutory and Executive Order
Reviews
This final rule establishes tolerances
under section 408(d) of FFDCA in
response to petitions submitted to the
Agency. The Office of Management and
Budget (OMB) has exempted these types
of actions from review under Executive
Order 12866, entitled Regulatory
Planning and Review (58 FR 51735,
October 4, 1993). Because this rule has
been exempted from review under
Executive Order 12866 due to its lack of
significance, this rule is not subject to
Executive Order 13211, Actions
Concerning Regulations That
Significantly Affect Energy Supply,
Distribution, or Use (66 FR 28355, May
22, 2001). This final rule does not
contain any information collections
subject to OMB approval under the
Paperwork Reduction Act (PRA), 44
U.S.C. 3501 et seq., or impose any
enforceable duty or contain any
unfunded mandate as described under
Title II of the Unfunded Mandates
Reform Act of 1995 (UMRA) (Public
Law 104–4). Nor does it require any
special considerations under Executive
Order 12898, entitled Federal Actions to
Address Environmental Justice in
Minority Populations and Low-Income
Populations (59 FR 7629, February 16,
1994), or OMB review or any Agency
action under Executive Order 13045,
entitled Protection of Children from
Environmental Health Risks and Safety
Risks (62 FR 19885, April 23, 1997).
This action does not involve any
technical standards that would require
Agency consideration of voluntary
consensus standards pursuant to section
12(d) of the National Technology
Transfer and Advancement Act of 1995
(NTTAA), Public Law 104–113, section
12(d) (15 U.S.C. 272 note). Since
tolerances and exemptions that are
established on the basis of a petition
under section 408(d) of FFDCA, such as
the tolerance in this final rule, do not
require the issuance of a proposed rule,
the requirements of the Regulatory
Flexibility Act (RFA) (5 U.S.C. 601 et
seq.) do not apply. In addition, the
Agency has determined that this action
will not have a substantial direct effect
on States, on the relationship between
the national government and the States,
or on the distribution of power and
responsibilities among the various
levels of government, as specified in
Executive Order 13132, entitled
Federalism (64 FR 43255, August 10,
1999). Executive Order 13132 requires
EPA to develop an accountable process
to ensure ‘‘meaningful and timely input
PO 00000
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Fmt 4700
Sfmt 4700
56373
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., as added by the Small
Business Regulatory Enforcement
Fairness Act of 1996, generally provides
that before a rule may take effect, the
agency promulgating the rule must
submit a rule report, which includes a
copy of the rule, to each House of the
Congress and to the Comptroller General
of the United States. EPA will submit a
report containing this rule and other
required information to the U.S. Senate,
the U.S. House of Representatives, and
the Comptroller General of the United
States prior to publication of this final
rule in the Federal Register. This final
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27SER1
56374
Federal Register / Vol. 71, No. 187 / Wednesday, September 27, 2006 / Rules and Regulations
rule is not a ‘‘major rule’’ as defined by
5 U.S.C. 804(2).
ENVIRONMENTAL PROTECTION
AGENCY
List of Subjects 40 CFR Part 180
40 CFR Part 180
Environmental protection,
Administrative practice and procedure,
Agricultural commodities, Pesticides
and pests, Reporting and recordkeeping
requirements.
Dated: September 19, 2006.
Lois Rossi,
Director, Registration Division, Office of
Pesticide Programs.
Therefore, 40 CFR chapter I is
amended as follows:
I
PART 180—[AMENDED]
1. The authority citation for part 180
continues to read as follows:
I
Authority: 21 U.S.C. 321(q), 346a and 371.
2. Section 180.361 is amended by
adding entries to the table in paragraph
(a) to read as follows:
I
§ 180.361 Pendimethalin, Tolerances for
Residues.
(a) *
*
*
Parts
per
million
Commodity
Alfalfa, Forage .....................................
Alfalfa, Hay ..........................................
Alfalfa, Seed ........................................
Apple, wet pomace ..............................
*
*
*
*
*
Fruit, pome, group 11 ..........................
Fruit, stone, group 12 ..........................
*
*
*
*
*
Juneberry .............................................
Leek .....................................................
*
*
*
*
*
Onion, green ........................................
Onion, welsh ........................................
*
*
*
*
*
Pomegranate .......................................
*
*
*
*
*
Shallot ..................................................
*
*
*
*
*
Strawberry ...........................................
*
*
*
*
*
Vegetable, fruiting, group 8 .................
Wheat, grain ........................................
Wheat, forage ......................................
Wheat, hay ..........................................
Wheat, straw .......................................
3.0
4.0
0.10
0.20
0.10
0.10
0.10
0.20
0.20
0.20
0.10
0.2
0.10
0.10
0.10
3.0
0.60
0.30
sroberts on PROD1PC70 with RULES
[FR Doc. 06–8254 Filed 9–26–06; 8:45 am]
BILLING CODE 6560–50–S
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17:39 Sep 26, 2006
Jkt 208001
[EPA–HQ–OPP–2006–0204; FRL–8094–5]
Quizalofop ethyl; Pesticide Tolerance
Environmental Protection
Agency (EPA).
ACTION: Final rule.
AGENCY:
SUMMARY: This regulation establishes a
tolerance for combined residues of
quizalofop ethyl in or on the raw
agricultural commodities barley, grain;
barley, hay; barley, straw; flax, seed;
milk, fat; sunflower, seed; wheat, forage;
wheat, grain; wheat, hay; and wheat,
straw. Nissan Chemical Industries, Ltd
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
September 27, 2006. Objections and
requests for hearings must be received
on or before November 27, 2006, 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–2006–0204. All documents in the
docket are listed in the index for the
docket. 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
Building), 2777 S. Crystal Drive,
Arlington, VA. The Docket Facility is
open from 8:30 a.m. to 4 p.m., Monday
through Friday, excluding legal
holidays. The Docket telephone number
is (703) 305–5805.
FOR FURTHER INFORMATION CONTACT:
James A. 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:
PO 00000
Frm 00040
Fmt 4700
Sfmt 4700
I. General Information
A. Does this Action Apply to Me?
You may be potentially affected by
this action if you are an agricultural
producer, food manufacturer, or
pesticide manufacturer. Potentially
affected entities may include, but are
not limited to:
• Crop production (NAICS 111), e.g.,
agricultural workers; greenhouse,
nursery, and floriculture workers;
farmers.
• Animal production (NAICS 112),
e.g., cattle ranchers and farmers, dairy
cattle farmers, livestock farmers.
• Food manufacturing (NAICS 311),
e.g., agricultural workers; farmers;
greenhouse, nursery, and floriculture
workers; ranchers; pesticide applicators.
• Pesticide manufacturing (NAICS
32532), e.g., agricultural workers;
commercial applicators; farmers;
greenhouse, nursery, and floriculture
workers; residential users.
This listing is not intended to be
exhaustive, but rather provides a guide
for readers regarding entities likely to be
affected by this action. Other types of
entities not listed in this unit could also
be affected. The North American
Industrial Classification System
(NAICS) codes have been provided to
assist you and others in determining
whether this action might apply to
certain entities. If you have any
questions regarding the applicability of
this action to a particular entity, consult
the person listed under FOR FURTHER
INFORMATION CONTACT.
B. How Can I Access Electronic Copies
of this Document?
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 the FFDCA, as
amended by the 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
E:\FR\FM\27SER1.SGM
27SER1
Agencies
[Federal Register Volume 71, Number 187 (Wednesday, September 27, 2006)]
[Rules and Regulations]
[Pages 56369-56374]
From the Federal Register Online via the Government Printing Office [www.gpo.gov]
[FR Doc No: 06-8254]
=======================================================================
-----------------------------------------------------------------------
ENVIRONMENTAL PROTECTION AGENCY
40 CFR Part 180
[EPA-HQ-OPP-2006-0645; FRL-8092-6]
Pendimethalin; Pesticide Tolerance
AGENCY: Environmental Protection Agency (EPA).
ACTION: Final rule.
-----------------------------------------------------------------------
SUMMARY: This regulation establishes a tolerance for combined residues
of pendimethalin, N-(1-ethylpropyl)-3,4-dimethyl-2,6-
dinitrobenzenamine, and its metabolite 4-[(1-ethylpropyl)amino]-2-
methyl-3,5-dinitrobenyzl alcohol in or on alfalfa, forage; alfalfa,
hay; alfalfa, seed; apple, wet pomace; fruit, pome, group 11; fruit,
stone, group 12; juneberry; leek; onion, green; onion, welsh;
pomegranate; shallot; strawberry; vegetable, fruiting, group 8; wheat,
grain; wheat, forage; wheat, hay; and wheat, straw. BASF Corporation
and Interregional Research Project Number 4 (IR-4) requested these
tolerances under the Federal Food, Drug, and Cosmetic Act (FFDCA), as
amended by the Food Quality Protection Act of 1996 (FQPA).
DATES: This regulation is effective September 27, 2006. Objections and
requests for hearings must be received on or before November 27, 2006
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-2006-0645. All documents in the
docket are listed in the index for the docket. 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 Building), 2777 S. Crystal Drive,
Arlington, VA. The Docket Facility is open from 8:30 a.m. to 4 p.m.,
Monday through Friday, excluding legal holidays. The Docket telephone
number is (703) 305-5805.
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 111), e.g., agricultural workers;
greenhouse, nursery, and floriculture workers; farmers.
[[Page 56370]]
Animal production (NAICS 112), e.g., cattle ranchers and
farmers, dairy cattle farmers, livestock farmers.
Food manufacturing (NAICS 311), e.g., agricultural
workers; farmers; greenhouse, nursery, and floriculture workers;
ranchers; pesticide applicators.
Pesticide manufacturing (NAICS 32532), e.g., agricultural
workers; commercial applicators; farmers; greenhouse, nursery, and
floriculture workers; residential users.
This listing is not intended to be exhaustive, but rather provides
a guide for readers regarding entities likely to be affected by this
action. Other types of entities not listed in this unit could also be
affected. The North American Industrial Classification System (NAICS)
codes have been provided to assist you and others in determining
whether this action might apply to certain entities. If you have any
questions regarding the applicability of this action to a particular
entity, consult the person listed under FOR FURTHER INFORMATION
CONTACT.
B. How Can I Access Electronic Copies of this Document?
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 the FFDCA, as amended by the 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-2006-0645 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 November 27, 2006.
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-2006-0645 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
Building), 2777 S. Crystal Drive, 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 June 14, 2006 (71 FR 34341-34342) (FRL-
8072-1), EPA issued a notice pursuant to section 408(d)(3) of FFDCA, 21
U.S.C. 346a(d)(3), announcing the filing of pesticide petitions PP
0E6175 (vegetable, fruiting, group 8), PP 2E6450 (fruit, pome, group
11; apple, wet pomace; and juneberry), PP 2E6464 (fruit, stone, group
12), PP 2E6449 (pomegranates), by Interregional Research Project Number
4 (IR-4), 681 U.S. Highway 1 South, New Brunswick, NJ 08902-
390.
In the Federal Register of June 14, 2006 (71 FR 34344-34345) (FRL-
8072-7), EPA issued a notice pursuant to section 408(d)(3) of FFDCA, 21
U.S.C. 346a(d)(3), announcing the filing of pesticide petitions PP
5E6927 (onion, green; onion, welsh; leek; and shallot), PP 5E6928
(strawberry), by Interregional Research Project Number 4 (IR-4), 681
U.S. Highway 1 South, New Brunswick, NJ 08902-390.
In the Federal Register of August 18, 2006 (71 FR 47810-47811 (FRL-
8084-71), EPA issued a notice pursuant to section 408(d)(3) of FFDCA,
21 U.S.C. 346a(d)(3), announcing the filing of pesticide petitions PP
4F6870 (wheat, grain; wheat, forage; wheat, hay; and wheat, straw), and
PP 5F6961 (alfalfa, forage; alfalfa, hay; and alfalfa, seed) by BASF
Corporation Agricultural Products, P.O. Box 13528, Research Triangle
Park, NC 27709-3528.
These petitions requested that 40 CFR 180.361 be amended by
establishing a tolerance for combined residues of the herbicide
pendimethalin, N-(1-ethylpropyl)-3,4-dimethyl-2,6-dinitrobenzenamine,
and its metabolite 4-[(1-ethylpropyl)amino]-2-methyl-3,5-dinitrobenyzl
alcohol in or on vegetables, fruiting, group 8 at 0.10 ppm (PP 0E6175),
fruit, pome, group 11 at 0.10 ppm; apple, wet pomace at 0.20 ppm; and
juneberry at 0.10 ppm (PP 2E6450), fruit, stone, group 12 at 0.10 ppm
(PP 2E6464), pomergranate at 0.10 ppm (PP 2E6449), onion, green at 0.20
ppm; onion, welsh at 0.20 ppm, leek at 0.20 ppm; and shallot at 0.2 ppm
(PP 5E6927), strawberry at 0.10 ppm (PP 5E6928), wheat, grain at 0.10
ppm; wheat, forge at 3.0 ppm; wheat, hay at 0.60 ppm; and wheat, straw
at 0.30 ppm; (PP 4F6870), alfalfa, forage at 3.0 ppm; alfalfa, hay at
4.0 ppm; and alfalfa, seed at 0.10 ppm (PP 5F6961). These notices
included a summary of the petition prepared by IR-4 and BASF
Corporation, the registrant. One comment was received in response to
the notices of filing. EPA's response to this comment is discussed in
Unit IV.C.
Section 408(b)(2)(A)(i) of FFDCA allows EPA to establish a
tolerance (the legal limit for a pesticide chemical residue in or on a
food) only if EPA determines that the tolerance is ``safe.'' Section
408(b)(2)(A)(ii) of FFDCA defines ``safe'' to mean that ``there is a
reasonable certainty that no harm will result from aggregate exposure
to the pesticide chemical residue, including all anticipated dietary
exposures and all other exposures for which there is reliable
information.'' This includes exposure through drinking water and in
residential settings, but does not include occupational exposure.
Section 408(b)(2)(C) of FFDCA requires EPA to give special
consideration to exposure of infants and children to the pesticide
chemical residue in establishing a tolerance and to ``ensure that there
is a reasonable certainty that no harm will result to infants and
children from aggregate exposure to the pesticide chemical
residue....''
EPA performs a number of analyses to determine the risks from
aggregate exposure to pesticide residues. For further discussion of the
regulatory requirements of section 408 of the FFDCA and a complete
description of the risk assessment process, see https://www.epa.gov/
fedrgstr/EPA-PEST/1997/November/Day-26/p30948.htm.
III. Aggregate Risk Assessment and Determination of Safety
Consistent with section 408(b)(2)(D) of FFDCA, EPA has reviewed the
[[Page 56371]]
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 combined residues of
pendimethalin, N-(1-ethylpropyl)-3,4-dimethyl-2,6-dinitrobenzenamine,
and its metabolite 4-[(1-ethylpropyl)amino]-2-methyl-3,5-dinitrobenyzl
alcohol in or on vegetables, fruiting, group 8 at 0.10 ppm; fruit,
pome, group 11 at 0.10 ppm; apple, wet pomace at 0.20 ppm; juneberry at
0.10 ppm; fruit, stone, group 12 at 0.10 ppm; pomergranate at 0.10 ppm;
onion, green at 0.20 ppm; onion, welsh at 0.20 ppm; leek at 0.20 ppm,
shallot at 0.2 ppm; strawberry at 0.10 ppm; wheat, grain at 0.10 ppm;
wheat, forge at 3.0 ppm; wheat, hay at 0.60 ppm, wheat, straw at 0.30
ppm; alfalfa, forage at 3.0 ppm; alfalfa, hay at 4.0 ppm; and alfalfa,
seed at 0.10 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 pendimethalin 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 http:/
www.regulations.gov/fdmspublic/component/main, see Docket OPP-2005-
0056-0002.
B. Toxicological Endpoints
For hazards that have a threshold below which there is no
appreciable risk, the dose at which no adverse effects are observed
(the NOAEL) from the toxicology study identified as appropriate for use
in risk assessment is used to estimate the toxicological level of
concern (LOC). However, the lowest dose at which adverse effects of
concern are identified (the LOAEL) is sometimes used for risk
assessment if no NOAEL was achieved in the toxicology study selected.
An uncertainty factor (UF) is applied to reflect uncertainties inherent
in the extrapolation from laboratory animal data to humans and in the
variations in sensitivity among members of the human population as well
as other unknowns.
The linear default risk methodology (Q*) is the primary method
currently used by the Agency to quantify non-threshold hazards such as
cancer. The Q* approach assumes that any amount of exposure will lead
to some degree of cancer risk, estimates risk in terms of the
probability of occurrence of additional cancer cases. More information
can be found on the general principles EPA uses in risk
characterization at https://www.epa.gov/fedrgstr/EPA-PEST/1997/November/
Day-26/p30948.htm.
A summary of the toxicological endpoints for pendimethalin used for
human risk assessment is discussed in Unit III.B. of the final rule
published in the Federal Register of April 12, 2006, 70 FR 18628-18635
(FRL-7770-4)
C. Exposure Assessment
1. Dietary exposure from food and feed uses. Tolerances have been
established (40 CFR 180.361) for the combined residues of
pendimethalin, N-(1-ethylpropyl)-3,4-dimethyl-2,6-dinitrobenzenamine,
and its metabolite 4-[(1-ethylpropyl)amino]-2-methyl-3,5-dinitrobenyzl
alcohol, in or on a variety of raw agricultural commodities. Risk
assessments were conducted by EPA to assess dietary exposures from
pendimethalin 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 one-day or single exposure. No such effects were
identified in the toxicological studies for pendimethalin; therefore, a
quantitative acute dietary exposure assessment is unnecessary.
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 USDA 1994-1996
and 1998 Nationwide Continuing Surveys of Food Intake by Individuals
(CSFII), and accumulated exposure to the chemical for each commodity.
Tolerance-level residues were assumed for all food commodities with
current and proposed pendimethalin tolerances, and it was assumed that
all of the crops included in the analysis were treated (i.e., 100% crop
treated). These assumptions result in highly conservative estimates of
dietary exposure and risk.
iii. Cancer. Pendimethalin is classified ``Group C,'' possible
human carcinogen, chemical based on a statistically significant
increased trend and pair-wise comparison between the high dose group
and controls for thyroid follicular cell adenomas in male and female
rats. The Agency used a non-linear approach (i.e., reference dose (RfD)
approach) since mode of action studies are available that demonstrate
that the thyroid tumors are due to a thyroid-pituitary imbalance, and
also since pendimethalin was shown to be non-mutagenic in mammalian
somatic cells and germ.
2. Dietary exposure from drinking water. The Agency lacks
sufficient monitoring exposure data to complete a comprehensive dietary
exposure analysis and risk assessment for pendimethalin 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 pendimethalin. 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 Pesticide Root Zone Model-Exposure Analysis Modeling
System (PRZM-EXAMS) and screening concentration in ground water (SCI-
GROW) models, the estimated environmental concentrations (EECs) of
pendimethalin for acute exposures are estimated to be 39 parts per
billion (ppb) for surface water and 0.024 ppb for ground water. The
EECs for chronic exposures are estimated to be 4.8 ppb for surface
water and 0.024 ppb for ground water. Modeled estimates of drinking
water concentrations were directly entered into the dietary exposure
model (DEEM-FCID\TM\, Version 2.03). An acute dietary risk assessment
for the peak water concentration value was not done because no such
effects were identified in the toxicological studies for pendimethalin.
For chronic dietary risk assessment, an estimated drinking water
concentration (EDWC) of 0.039 ppm, the 1 in 10 year annual peak
concentration in surface water as calculated by PRZM-EXAMS modeling,
resulting from a single application of pendimethalin to apples at a
rate of 4.0 lb of active ingredient/acre, was entered into DEEM.
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
[[Page 56372]]
flea and tick control on pets). Pendimethalin is currently registered
for use on the following residential non-dietary sites: Landscapes,
grounds plantings, ornamental crops, turf grass, and lawns. The risk
assessment for residential non-dietary sites is discussed in Unit
III.C.3. of the final rule published in the Federal Register of April
12, 2006, FR Page 18628-18635 (FRL-7770-4)
4. Cumulative effects from substances with a common mechanism of
toxicity. Section 408(b)(2)(D)(v) of the FFDCA requires that, when
considering whether to establish, modify, or revoke a tolerance, the
Agency consider ``available information'' concerning the cumulative
effects of a particular pesticide's residues and ``other substances
that have a common mechanism of toxicity.''
Unlike other pesticides for which EPA has followed a cumulative
risk approach based on a common mechanism of toxicity, EPA has not made
a common mechanism of toxicity finding as to pendimethalin and any
other substances and pendimethalin 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 pendimethalin 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 data base on toxicity and exposure
unless EPA determines based on reliable data that a different margin of
safety will be safe for infants and children. Margins of safety are
incorporated into EPA risk assessments either directly through use of a
margin of exposure (MOE) analysis or through using uncertainty (safety)
factors in calculating a dose level that poses no appreciable risk to
humans. In applying this provision, EPA either retains the default
value of 10X when reliable data do not support the choice of a
different factor, or, if reliable data are available, EPA uses a
different additional safety factor value based on the use of
traditional uncertainty factors and/or special FQPA safety factors, as
appropriate.
2. Prenatal and postnatal sensitivity. The data base for
pendimethalin does not indicate a potential for increased toxicological
sensitivity from either prenatal or postnatal exposures. No
developmental toxicity was observed in either the rat or rabbit
developmental toxicity studies, nor was there evidence in the two-
generation reproduction study of developmental or reproductive toxicity
at dose levels below those in which parental toxicity was observed.
There was no neurotoxicity observed in the submitted toxicity studies.
Therefore, a developmental neurotoxicity (DNT) study is not required.
Available data show the thyroid is a target organ for
pendimethalin. The endpoints and doses selected for risk assessment
were based on the most sensitive effect, thyroid toxicity, which was
well-characterized in both chronic and subchronic toxicity studies on
the basis of clear NOAELs and LOAELs. In addition, the exposure data
used to evaluate risks for the general U.S. population and infants and
children are conservative, and therefore the calculated risks are
considered to be protective.
3. Conclusion. There was no evidence of qualitative or quantitative
susceptibility in the submitted data. Additionally, exposure estimates
are based on very conservative data and assumptions that will overstate
exposure to pendimethalin. There is, however, a concern that
perturbation of thyroid homeostatis may lead to hypothyroidism, and
possibly result in adverse effects on the developing nervous system.
Since thyroid toxicity parameters were not measured in the
developmental toxicity studies, the Agency has requested a
developmental thyroid assay be conducted to evaluate the impact of
pendimethalin on thyroid hormones, structure, and/or thyroid hormone
homeostasis during development. The Agency has retained the additional
10X FQPA safety factor in the form of a database uncertainty factor
(UFDB) for the lack of the study, to be applied in
determining pendimethalin risks.
E. Aggregate Risks and Determination of Safety
1. Acute risk. No toxic effects attributed to a single dose were
identified for pendimethalin. Therefore an acute risk is not
anticipated for this chemical.
2. Chronic risk. Using the exposure assumptions described in this
unit for chronic exposure, EPA has concluded that exposure to
pendimethalin from food and drinking water will utilize 11% of the
chronic population adjusted dose (cPAD) for the U.S. population, 19% of
the cPAD for infants, and 26% of the cPAD for Children 1 to 2 years of
age. Based on the use pattern, chronic residential exposure to residues
of pendimethalin is not expected.
3. Short-term risk. Short-term aggregate exposure takes into
account residential exposure plus chronic exposure to food and water
(considered to be a background exposure level).
Pendimethalin is currently registered for use that could result in
short-term residential exposure and the Agency has determined that it
is appropriate to aggregate chronic food and water and short-term
exposures for pendimethalin.
Using the exposure assumptions described in this unit for short-
term exposures, EPA has concluded that food, drinking water and
residential exposures aggregated result in aggregate MOEs of 580 for
adult males, 520 for females 13 years or older, and 310 for children 1
to 2 years old. These aggregate MOEs do not exceed the Agency's level
of concern (MOE 300) for aggregate exposure to food, drinking water and
residential uses. See 71 FR 18628-18630, April 12, 2006.
4. Intermediate-term risk. Intermediate-term aggregate exposure
takes into account residential exposure plus chronic exposure to food
and water (considered to be a background exposure level). Based on the
currently registered and requested uses, there are no scenarios that
are likely to result in intermediate-term exposure (30 to 180 days,
continuously). Therefore an intermediate-term risk is not anticipated
for pendimethalin.
5. Aggregate cancer risk for U.S. population. The Agency determined
that the 0.10 mg/kg/day RfD for chronic risks, is protective of both
the chronic, non-carcinogenic effects as well as the carcinogenic
effect seen in the rat. Accordingly, based on the risk estimates for
chronic risk above, EPA concludes that aggregate chronic exposure to
pendimethalin is not expected to pose a cancer risk of concern.
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 pendimethalin and its metabolite residues.
[[Page 56373]]
IV. Other Considerations
A. Analytical Enforcement Methodology
Adequate methods are available for data collection and tolerance
enforcement for existing and proposed uses of pendimethalin. Methods I
through IV in PAM Vol. II are gas chromatography/electron capture (GC/
ECD) methods. Methods used for data collection are essentially the same
as the PAM Vol. II methods, and have been adequately validated.
The FDA PESTDATA database (PAM Volume I, Appendix I) indicates that
pendimethalin is completely recovered (>80%) by Multiresidue Methods
Section 302 (Luke method; Protocol D) and 303 (Mills, Onley, Gaither
method; Protocol E, nonfatty), and partially recovered (50-80%) by
Multiresidue Method Section 304 (Mills fatty food method; Protocol E,
fatty). 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 Codex maximum residue limits
(MRLs) for pendimethalin residues. Therefore, there are no questions of
compatibility with respect to Codex MRLs and U.S. tolerances.
C. Response to Comments
One comment was received in response to the notices of filing for
this action. The comment contained no scientific data or other
substantive evidence to rebut the Agency's conclusion that there is a
reasonable certaintythat no harm will result from aggregate exposure to
pendimethalin from the establishment of these tolerances.
V. Conclusion
Therefore, tolerances are established for combined residues of
pendimethalin, N-(1-ethylpropyl)-3,4-dimethyl-2,6-dinitrobenzenamine,
and its metabolite 4-[(1-ethylpropyl)amino]-2-methyl-3,5-dinitrobenyzl
alcohol in or on alfalfa, forage at 3.0 ppm; alfalfa, hay at 4.0 ppm;
and alfalfa, seed at 0.10 ppm; fruit, pome, group 11 at 0.10 ppm;
apple, wet pomace at 0.20 ppm and juneberry at 0.10 ppm; fruit, stone,
group 12 at 0.10 ppm; pomergranate at 0.10 ppm; onion, green at 0.20
ppm; onion, welsh at 0.20 ppm; leek at 0.20 ppm; and shallot at 0.2
ppm; strawberry at 0.10 ppm; wheat, grain at 0.10 ppm; wheat, forge at
3.0 ppm; wheat, hay at 0.60 ppm; wheat, straw at 0.30 ppm; and
vegetables, fruiting, group 8 at 0.10 ppm.
VI. Statutory and Executive Order Reviews
This final rule establishes tolerances under section 408(d) of
FFDCA in response to petitions submitted to the Agency. The Office of
Management and Budget (OMB) has exempted these types of actions from
review under Executive Order 12866, entitled Regulatory Planning and
Review (58 FR 51735, October 4, 1993). Because this rule has been
exempted from review under Executive Order 12866 due to its lack of
significance, this rule is not subject to Executive Order 13211,
Actions Concerning Regulations That Significantly Affect Energy Supply,
Distribution, or Use (66 FR 28355, May 22, 2001). This final rule does
not contain any information collections subject to OMB approval under
the Paperwork Reduction Act (PRA), 44 U.S.C. 3501 et seq., or impose
any enforceable duty or contain any unfunded mandate as described under
Title II of the Unfunded Mandates Reform Act of 1995 (UMRA) (Public Law
104-4). Nor does it require any special considerations under Executive
Order 12898, entitled Federal Actions to Address Environmental Justice
in Minority Populations and Low-Income Populations (59 FR 7629,
February 16, 1994), or OMB review or any Agency action under Executive
Order 13045, entitled Protection of Children from Environmental Health
Risks and Safety Risks (62 FR 19885, April 23, 1997). This action does
not involve any technical standards that would require Agency
consideration of voluntary consensus standards pursuant to section
12(d) of the National Technology Transfer and Advancement Act of 1995
(NTTAA), Public Law 104-113, section 12(d) (15 U.S.C. 272 note). Since
tolerances and exemptions that are established on the basis of a
petition under section 408(d) of FFDCA, such as the tolerance in this
final rule, do not require the issuance of a proposed rule, the
requirements of the Regulatory Flexibility Act (RFA) (5 U.S.C. 601 et
seq.) do not apply. In addition, the Agency has determined that this
action will not have a substantial direct effect on States, on the
relationship between the national government and the States, or on the
distribution of power and responsibilities among the various levels of
government, as specified in Executive Order 13132, entitled Federalism
(64 FR 43255, August 10, 1999). Executive Order 13132 requires EPA to
develop an accountable process to ensure ``meaningful and timely input
by State and local officials in the development of regulatory policies
that have federalism implications.'' ``Policies that have federalism
implications'' is defined in the Executive order to include regulations
that have ``substantial direct effects on the States, on the
relationship between the national government and the States, or on the
distribution of power and responsibilities among the various levels of
government.'' This final rule directly regulates growers, food
processors, food handlers and food retailers, not States. This action
does not alter the relationships or distribution of power and
responsibilities established by Congress in the preemption provisions
of section 408(n)(4) of FFDCA. For these same reasons, the Agency has
determined that this rule does not have any ``tribal implications'' as
described in Executive Order 13175, entitled Consultation and
Coordination with Indian Tribal Governments (65 FR 67249, November 6,
2000). Executive Order 13175, requires EPA to develop an accountable
process to ensure ``meaningful and timely input by tribal officials in
the development of regulatory policies that have tribal implications.''
``Policies that have tribal implications'' is defined in the Executive
order to include regulations that have ``substantial direct effects on
one or more Indian tribes, on the relationship between the Federal
Government and the Indian tribes, or on the distribution of power and
responsibilities between the Federal Government and Indian tribes.''
This rule will not have substantial direct effects on tribal
governments, on the relationship between the Federal Government and
Indian tribes, or on the distribution of power and responsibilities
between the Federal Government and Indian tribes, as specified in
Executive Order 13175. Thus, Executive Order 13175 does not apply to
this rule.
VII. Congressional Review Act
The Congressional Review Act, 5 U.S.C. 801 et seq., as added by the
Small Business Regulatory Enforcement Fairness Act of 1996, generally
provides that before a rule may take effect, the agency promulgating
the rule must submit a rule report, which includes a copy of the rule,
to each House of the Congress and to the Comptroller General of the
United States. EPA will submit a report containing this rule and other
required information to the U.S. Senate, the U.S. House of
Representatives, and the Comptroller General of the United States prior
to publication of this final rule in the Federal Register. This final
[[Page 56374]]
rule is not a ``major rule'' as defined by 5 U.S.C. 804(2).
List of Subjects 40 CFR Part 180
Environmental protection, Administrative practice and procedure,
Agricultural commodities, Pesticides and pests, Reporting and
recordkeeping requirements.
Dated: September 19, 2006.
Lois Rossi,
Director, Registration Division, Office of Pesticide Programs.
0
Therefore, 40 CFR chapter I is amended as follows:
PART 180--[AMENDED]
0
1. The authority citation for part 180 continues to read as follows:
Authority: 21 U.S.C. 321(q), 346a and 371.
0
2. Section 180.361 is amended by adding entries to the table in
paragraph (a) to read as follows:
Sec. 180.361 Pendimethalin, Tolerances for Residues.
(a) * * *
------------------------------------------------------------------------
Commodity Parts per million
------------------------------------------------------------------------
Alfalfa, Forage........................... 3.0
Alfalfa, Hay.............................. 4.0
Alfalfa, Seed............................. 0.10
Apple, wet pomace......................... 0.20
* * * * *
Fruit, pome, group 11..................... 0.10
Fruit, stone, group 12.................... 0.10
* * * * *
Juneberry................................. 0.10
Leek...................................... 0.20
* * * * *
Onion, green.............................. 0.20
Onion, welsh.............................. 0.20
* * * * *
Pomegranate............................... 0.10
* * * * *
Shallot................................... 0.2
* * * * *
Strawberry................................ 0.10
* * * * *
Vegetable, fruiting, group 8.............. 0.10
Wheat, grain.............................. 0.10
Wheat, forage............................. 3.0
Wheat, hay................................ 0.60
Wheat, straw.............................. 0.30
------------------------------------------------------------------------
[FR Doc. 06-8254 Filed 9-26-06; 8:45 am]
BILLING CODE 6560-50-S