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OPP ID: [OPP-2005-0133; FRL-7738-7]
SUBJECT CATEGORY: Fenpropathrin; Pesticide Tolerance
DOCUMENT SUMMARY: This regulation establishes tolerances for residues of fenpropathrin in or on bushberry subgroup 13B; lingonberry; juneberry; salal; pea, succulent; and vegetable, fruiting, group 8. Interregional Research Project Number 4 (IR4) requested these tolerances under the Federal Food, Drug, and Cosmetic Act (FFDCA), as amended by the Food Quality Protection Act of 1996 (FQPA).
SUMMARY: Fenpropathrin,
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:
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 [[Page 55741]]
be affected. The North American Industrial Classification System
(NAICS) codes have been provided to assist you and others in
determining whether this action might apply to certain entities. If you
have any questions regarding the applicability of this action to a
particular entity, consult the person listed under FOR FURTHER INFORMATION CONTACT.
B. How Can I Access Electronic Copies of this Document and Other Related Information?
In addition to using EDOCKET(http://www.epa.gov/edocket/), you may access this Federal Register document electronically through the EPA Internet under the ``Federal Register'' listings at http://www.epa.gov/fedrgstr/. A frequently updated electronic version of 40 CFR part 180 is available at ECFR Beta Site Two at http://www.gpoaccess.gov/ecfr/. To access the OPPTS Harmonized Guidelines referenced in this document, go directly to the guidelines athttp://www.epa.gpo/opptsfrs/home/guidelin.htm/ .
In the Federal Register of March 24, 2004 (69 FR 13833) (FRL7347
2), 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
1E6261, PP 1E6331, PP 1E6336, and PP 3E6588 by IR4, 681 U.S. Highway
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 http://www.epa.gov/fedrgstr/EPAPEST/1997/November/Day26/p30948.htm .
Consistent with section 408(b)(2)(D) of FFDCA, EPA has reviewed the available scientific data and other relevant information in support of these actions. EPA has sufficient data to assess the hazards of and to make a determination on aggregate exposure, consistent with section 408(b)(2) ofFFDCA, for tolerances for residues of fenpropathrin on vegetable, fruiting, group 8 at 1.0 ppm; pea, succulent at 0.02 ppm; and bushberry subgroup 13B, lingonberry, juneberry, and salal at 3.0 ppm. EPA's assessment of exposures and risks associated with establishing these tolerances follows.
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. The nature of the toxic effects caused by fenpropathrin is
discussed in Table 1 of this unit as well as the noobservedadverse
effectlevel (NOAEL) and the lowestobservedadverseeffectlevel (LOAEL) from the toxicity studies reviewed.
Table 1.Subchronic, Chronic, and Other Toxicity
Guideline No. Study Type Results
870.3100 90Day oral NOAEL = 15 milligrams/
toxicity kilogram/day (mg/kg/ rodents (Rat) day)
LOAEL = 30 mg/kg/day
based on clinical
signs of tremors,
body weight
reductions,
decreased blood
clotting time in
females, and
possibly increased
alkaline phosphatase
levels (both sexes)
870.3150 90Day oral NOAEL = < 6.2 mg/kg/ toxicity day
nonrodents LOAEL = 6.2 mg/kg/day
(Beagle dog) based on effects on
the gastrointestinal
system, tremors, and
body weight changes
870.3200 21Day dermal NOAEL = >3,000 mg/kg/ toxicity (NZW day
rabbit) Only local irritation
was seen. There were
no systemic effects,
thus the LOAEL was
not determined [[Page 55742]]
870.3700 Prenatal Maternal NOAEL = 3 mg/ developmental kg/day
rodents(Fischer The maternal NOAEL
Rats) for the
developmental rat
study was 3.0 mg/kg/
day based on
decreased food
consumption and body
weight gains.
However, these
effects are not
characteristic of an
acute exposure and
are not a suitable
option for this
exposure scenario.
One of the factors
to consider in
selecting an acute
dietary endpoint is
when the toxic
effects occur. For
an acute effect, a
relevant endpoint
would occur as the
result of a single
dose. Since the
neurotoxic signs
observed in the dams
of the developmental
rat study were most
severe within two
hours after dosing,
the clinical effects
are resultant from a
single dose, and are
therefore
appropriate
endpoints for acute
exposure scenarios.
Maternal LOAEL = 6
mg/kg/day based on
decreased food
consumption and body
weight gains. At 10
mg/kg/day, 6 dams
died between days 7
and 13, and one dam
was sacrificed
moribund on day 8.
The remaining 23
dams survived
through the end of
gestation. Also in
the high dose group,
many clinical signs
were observed in the
dams including
ataxia, sensitivity
to external stimuli,
spastic jumping, and
tremors. These signs
were most severe 2
hours postdosing
and during the first
days of dosing.
Developmental NOAEL
= 6 mg/kg/day
Developmental LOAEL
= 10 mg/kg/day based
on increased
incidence of
asymmetrical
ossification of
sternabrae and
incomplete
ossification of the
5th and 6th
sternabrae.
870.3700 Prenatal Maternal NOAEL = 4 mg/ developmental kg/day
nonrodents (NZW Maternal LOAEL = 12
rabbit) mg/kg/day based on
flicking of the
forepaws
Developmental NOAEL =
>36 mg/kg/day
No dose related
effects were seen,
thus the LOAEL was
not determined
870.3800 Reproduction and Parental/Systemic
fertility NOAEL = M:3.0; F:
effects (Sprague 3.0 mg/kg/day
Dawley rats) LOAEL = M: 8.9; F:
10.1 mg/kg/day based
on death and
clinical signs of
neurotoxicity in
females.
Offspring NOAEL =
FOR FURTHER INFORMATION CONTACT Shaja R. Brothers, Registration
Division (7505C), Office of Pesticide Programs, Environmental
Protection Agency, 1200 Pennsylvania Ave., NW., Washington, DC 20460
0001; telephone number: (703) 3083194; email address:
brothers.shaja@epa.gov.
14 CFR Part 39 40 CFR Part 52 14 CFR Part 71 33 CFR Part 165 50 CFR Part 679 47 CFR Part 73 26 CFR Part 1 40 CFR Part 180 33 CFR Part 117 50 CFR Part 17 44 CFR Part 67 50 CFR Part 648 14 CFR Part 97 33 CFR Part 100 40 CFR Part 63 50 CFR Part 622 44 CFR Part 65 50 CFR Part 660 26 CFR Part 301 39 CFR Part 111 40 CFR Part 300 6 CFR Part 5 40 CFR Part 271 47 CFR Part 64 40 CFR Parts 52 and 81 50 CFR Part 665 44 CFR Part 64 10 CFR Part 50 49 CFR Part 571 47 CFR Part 76