[Federal Register: November 19, 2004 (Volume 69, Number 223)]
[Notices]
[Page 67731-67735]
From the Federal Register Online via GPO Access [wais.access.gpo.gov]
[DOCID:fr19no04-52]
[[Page 67731]]
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ENVIRONMENTAL PROTECTION AGENCY
[OPP-2004-0363; FRL-7686-5]
Pinoxaden; Notice of Filing a Pesticide Petition to Establish a
Tolerance for a Certain Pesticide Chemical in or on Food
AGENCY: Environmental Protection Agency (EPA).
ACTION: Notice.
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SUMMARY: This notice announces the initial filing of a pesticide
petition proposing the establishment of regulations for residues of a
certain pesticide chemical in or on various food commodities.
DATES: Comments, identified by docket identification (ID) number OPP-
2004-0363, must be received on or before December 20, 2004.
ADDRESSES: Comments may be submitted electronically, by mail, or
through hand delivery/courier. Follow the detailed instructions as
provided in Unit I. of the SUPPLEMENTARY INFORMATION.
FOR FURTHER INFORMATION CONTACT: Jim Tompkins, Registration Division
(7505C), 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)
Animal production (NAICS 112)
Food manufacturing (NAICS 311)
Pesticide manufacturing (NAICS 32532)
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 Get Copies of this Document and Other Related Information?
1. Docket. EPA has established an official public docket for this
action under docket ID number OPP-2004-0363. The official public docket
consists of the documents specifically referenced in this action, any
public comments received, and other information related to this action.
Although a part of the official docket, the public docket does not
include Confidential Business Information (CBI) or other information
whose disclosure is restricted by statute. The official public docket
is the collection of materials that is available for public viewing at
the Public Information and Records Integrity Branch (PIRIB), Rm. 119,
Crystal Mall 2, 1801 S. Bell St., Arlington, VA. This docket
facility is open from 8:30 a.m. to 4 p.m., Monday through Friday,
excluding legal holidays. The docket telephone number is (703) 305-
5805.
2. Electronic access. You may access this Federal Register document
electronically through the EPA Internet under the ``Federal Register''
listings at http://www.epa.gov/fedrgstr/.
An electronic version of the public docket is available through
EPA's electronic public docket and comment system, EPA Dockets. You may
use EPA Dockets at http://www.epa.gov/edocket/ to submit or view public
comments, access the index listing of the contents of the official
public docket, and to access those documents in the public docket that
are available electronically. Although not all docket materials may be
available electronically, you may still access any of the publicly
available docket materials through the docket facility identified in
Unit I.B.1. Once in the system, select ``search,'' then key in the
appropriate docket ID number.
Certain types of information will not be placed in the EPA Dockets.
Information claimed as CBI and other information whose disclosure is
restricted by statute, which is not included in the official public
docket, will not be available for public viewing in EPA's electronic
public docket. EPA's policy is that copyrighted material will not be
placed in EPA's electronic public docket but will be available only in
printed, paper form in the official public docket. To the extent
feasible, publicly available docket materials will be made available in
EPA's electronic public docket. When a document is selected from the
index list in EPA Dockets, the system will identify whether the
document is available for viewing in EPA's electronic public docket.
Although not all docket materials may be available electronically, you
may still access any of the publicly available docket materials through
the docket facility identified in Unit I.B. EPA intends to work towards
providing electronic access to all of the publicly available docket
materials through EPA's electronic public docket.
For public commenters, it is important to note that EPA's policy is
that public comments, whether submitted electronically or in paper,
will be made available for public viewing in EPA's electronic public
docket as EPA receives them and without change, unless the comment
contains copyrighted material, CBI, or other information whose
disclosure is restricted by statute. When EPA identifies a comment
containing copyrighted material, EPA will provide a reference to that
material in the version of the comment that is placed in EPA's
electronic public docket. The entire printed comment, including the
copyrighted material, will be available in the public docket.
Public comments submitted on computer disks that are mailed or
delivered to the docket will be transferred to EPA's electronic public
docket. Public comments that are mailed or delivered to the docket will
be scanned and placed in EPA's electronic public docket. Where
practical, physical objects will be photographed, and the photograph
will be placed in EPA's electronic public docket along with a brief
description written by the docket staff.
C. How and To Whom Do I Submit Comments?
You may submit comments electronically, by mail, or through
handdelivery/courier. To ensure proper receipt by EPA, identify the
appropriate docket ID number in the subject line on the first page of
your comment. Please ensure that your comments are submitted within the
specified comment period. Comments received after the close of the
comment period will be marked ``late.'' EPA is not required to consider
these late comments. If you wish to submit CBI or information that is
otherwise protected by statute, please follow the instructions in Unit
I.D. Do not use EPA Dockets or e-mail to submit CBI or information
protected by statute.
1. Electronically. If you submit an electronic comment as
prescribed in this unit, EPA recommends that you include your name,
mailing address, and an e-mail address or other contact information in
the body of your comment. Also include this contact information on the
outside of any disk or CD ROM you submit, and in any
[[Page 67732]]
cover letter accompanying the disk or CD ROM. This ensures that you can
be identified as the submitter of the comment and allows EPA to contact
you in case EPA cannot read your comment due totechnical difficulties
or needs further information on the substance of your comment. EPA's
policy is that EPA will not edit your comment, and any identifying or
contact information provided in the body of a comment will be included
as part of the comment that is placed in the official public docket,
and made available in EPA's electronic public docket. If EPA cannot
read your comment due to technical difficulties and cannot contact you
for clarification, EPA may not be able to consider your comment.
i. EPA Dockets. Your use of EPA's electronic public docket to
submit comments to EPA electronically is EPA's preferred method for
receiving comments. Go directly to EPA Dockets at http://www.epa.gov/edocket/
, and follow the online instructions for submitting comments.
Once in the system, select ``search,'' and then key in docket ID number
OPP-2004-0363. The system is an ``anonymous access'' system, which
means EPA will not know your identity, e-mail address, or other contact
information unless you provide it in the body of your comment.
ii. E-mail. Comments may be sent by e-mail to opp-docket@epa.gov,
Attention: Docket ID Number OPP-2004-0363. Incontrast to EPA's
electronic public docket, EPA's e-mail system is not an ``anonymous
access'' system. If you send an e-mail comment directly to the docket
without going through EPA's electronic public docket, EPA's e-mail
system automatically captures your e-mail address. E-mail addresses
that are automatically captured by EPA's e-mail system are included as
part of the comment that is placed in the official public docket, and
made available in EPA's electronic public docket.
iii. Disk or CD ROM. You may submit comments on a diskor CD ROM
that you mail to the mailing address identified in Unit I.C.2. These
electronic submissions will be accepted in WordPerfect or ASCII file
format. Avoid the use of special characters and any form of encryption.
2. By mail. Send your comments to: Public Information and Records
Integrity Branch (PIRIB) (7502C), Office of Pesticide Programs (OPP),
Environmental Protection Agency, 1200 Pennsylvania Ave., NW.,
Washington, DC 20460-0001, Attention: Docket ID Number OPP-2004-0363.
3. By hand delivery or courier. Deliver your comments to: Public
Information and Records Integrity Branch (PIRIB), Office of Pesticide
Programs (OPP), Environmental Protection Agency, Rm. 119, Crystal Mall
2, 1801 S. Bell St., Arlington, VA, Attention: Docket ID
Number OPP-2004-0363. Such deliveries are only accepted during the
docket's normal hours of operation as identified in Unit I.B.1.
D. How Should I Submit CBI to the Agency?
Do not submit information that you consider to be CBI
electronically through EPA's electronic public docket or by e-mail. You
may claim information that you submit to EPA as CBI by marking any part
or all of that information as CBI (if you submit CBI on disk or CD ROM,
mark the outside of the disk or CD ROM as CBI and then identify
electronically within the disk or CD ROM the specific information that
is CBI). Information so marked will not be disclosed except in
accordance with procedures set forth in 40 CFR part 2.
In addition to one complete version of the comment that includes
any information claimed as CBI, a copy of the comment that does not
contain the information claimed as CBI must be submitted for inclusion
in the public docket and EPA's electronic public docket. If you submit
the copy that does not contain CBI on disk or CD ROM, mark the outside
of the disk or CD ROM clearly that it does not contain CBI. Information
not marked as CBI will be included in the public docket and EPA's
electronic public docket without prior notice. If you have any
questions about CBI or the procedures for claiming CBI, please consult
the person listed under FOR FURTHER INFORMATION CONTACT.
E. What Should I Consider as I Prepare My Comments for EPA?
You may find the following suggestions helpful for preparing your
comments:
1. Explain your views as clearly as possible.
2. Describe any assumptions that you used.
3. Provide copies of any technical information and/or data you
used that support your views.
4. If you estimate potential burden or costs, explain how you
arrived at the estimate that you provide.
5. Provide specific examples to illustrate your concerns.
6. Make sure to submit your comments by the deadline in this
notice.
7. To ensure proper receipt by EPA, be sure to identify the docket
ID number assigned to this action in the subject line on the first page
of your response. You may also provide the name, date, and Federal
Register citation.
II. What Action is the Agency Taking?
EPA has received a pesticide petition as follows proposing the
establishment and/or amendment of regulations for residues of a certain
pesticide chemical in or on various food commodities under section 408
of the Federal Food, Drug, and Cosmetic Act (FFDCA), 21 U.S.C. 346a.
EPA has determined that this petition contains data or information
regarding theelements set forth in FFDCA section 408(d)(2); however,
EPA has not fully evaluated the sufficiency of the submitted data at
this time or whether the data supports granting of the petition.
Additional data may be needed before EPA rules on the petition.
List of Subjects
Environmental protection, Agricultural commodities, Feed additives,
Food additives, Pesticides and pests, Reporting and recordkeeping
requirements.
Dated: November 3, 2004
Lois Rossi,
Director, Registration Division, Office of PesticidePrograms.
Summary of Petition
The petitioner summary of the pesticide petition is printed below
as required by FFDCA section 408(d)(3). The summary of the petition was
prepared by the petitioner and represents the view of the petitioner.
The petition summary announces the availability of a description of the
analytical methods available to EPA for the detection and measurement
of the pesticide chemical residues or an explanation of why no such
method is needed.
Syngenta Crop Protection
EPA has received a pesticide petition 4F6817 from Syngenta Crop
Protection, Inc., P.O. Box 18300, Greensboro, North Carolina, 27419-
8300 proposing, pursuant to section 408(d) of the Federal Food, Drug,
and Cosmetic Act (FFDCA), 21 U.S.C. 346a(d), to amend 40 CFR part 180
by establishing a tolerance for residues of pinoxaden in or on the raw
agricultural commodities (RAC) wheat grain at 0.70 parts per million
(ppm), wheat, forage at 3.0 ppm, wheat, hay at 1.75 ppm, wheat, straw
at 1.5 ppm, barley, grain at 0.70 ppm, barley, hay at 1.25 ppm, and
barley, straw at 0.60 ppm. EPA has determined that the petition
contains data or information regarding the elements set forth in
section 408(d)(2) of the FFDCA;
[[Page 67733]]
however, EPA has not fully evaluated the sufficiency of the submitted
data at this time or whether the data supports granting of the
petition. Additional data may be needed before EPA rules on the
petition.
A. Residue Chemistry
1. Plant metabolism. Metabolism of pinoxaden was studied in wheat
using radiolabeled pinoxaden. The metabolism in plants is well
understood and the data is adequate for selection of residues of
concern for tolerance setting purposes. The metabolic profile in plants
supports the use of an analytical method that accounts for parent
pinoxaden and its major metabolites.
2. Analytical method. Syngenta Crop Protection, Inc., has submitted
practical analytical methodology for detecting and measuring levels of
pinoxaden and its three major metabolites. The method is based upon
commodity specific cleanup procedures and High Performance Liquid
Chromatography (HPLC) determination with triple stage quadruple mass
spectrometry (LC/MS/MS). The limit of quantitation (LOQ), as
demonstrated by the lowest acceptable recovery samples, is 0.01 ppm for
grain, and 0.02 ppm for forage, hay, and straw.
3. Magnitude of residues. A magnitude of the residueprogram was
performed with pinoxaden on full guideline geography to support uses on
all types of wheat, and barley crops.
B. Toxicological Profile
1. Acute toxicity. Pinoxaden technical and the end-use formulation
have very low acute toxicity by oral, dermal, and inhalation exposure
routes. For pinoxaden technical, the oral LD50 in rats is
>5,000 millgrams/kilogram (mg/kg). The rat dermal LD50 is
>2,000 mg/kg and the rat inhalation LC50 is 5.22 milligrams/
liter (mg/L) air. Pinoxaden technical is irritating to the eye and non-
irritating to the skin. The end-use formulation is mildly to moderately
irritating to the eye and skin, the oral LD50 in rats is
3,129 mg/kg, the rat dermal LD50 is >2,000 mg/kg and the rat
inhalation LC50 is >5 mg/L. Neither the technical nor the
formulation are skin sensitizers.
2. Genotoxicty. Pinoxaden has been tested for its potential to
induce gene mutation and chromosomal changes in six different test
systems. Pinoxaden technical was negative in a bacterial gene mutation
assay, a mouse lymphoma mammalian cell mutation assay and an
unscheduled DNA synthesis (UDS) assay in rat hepatocytes. In in vitro
tests for chromosome aberrations in Chinese hamster ovary cells, a
small dose related increase was observed at dose levels that produced
cytotoxicity. To assess the biological significance of this single
positive in vitro finding, two in vivo tests were performed. When
tested in a micronucleus test in bone marrow cells of the mouse at dose
levels up to a limit dose of 2,000 mg/kg, pinoxaden did not induce
micronuclei, and produced no significant toxicity in the animals. In an
in vivo UDS study in rats, pinoxaden was negative in this assay for DNA
repair. Based on the complete database, it is concluded that pinoxaden
is not genotoxic.
3. Reproductive and developmental toxicity. Pinoxadenproduced no
evidence of reproductive toxicity. In a rat multi-generation
reproduction study, pinoxaden technical was administered orally by
gavage to rats at dosages of 0, 10, 50, 250, and 500 mg/kg/day over two
generations. At 500 mg/kg, parental toxicity was observed as decreased
body weight gain (F0 males) and kidney pathology accompanied
by increased water consumption (F0 and F1 males
and females.) At 500 mg/kg/day, F1 and F2 pups
had lower body weight gain during lactation. Changes in organ weights
were seen in pups at this dose level, but no treatment-related adverse
findings were observed for pups ineither generation upon histologic
examination. At 10, 50 and 250 mg/kg/day, there was no indication of
any adverse effects of treatment. On the basis of the results obtained
in this study, the no observed adverse effect level (NOAEL) for both
sexes and generations was 250 mg/kg/day. There were no effects on the
reproductive parameters and the NOAEL for reproductive toxicity was
>500 mg/kg/day. Offspring effects were minor and were observed only at
dose levels that produced parental toxicity. There were no indications
of any differences in sensitivity to pinoxaden exposure between the
different generations or between parental animals andoffspring, and it
is concluded that pinoxaden does not cause reproductive toxicity.
In a rat teratogenicity study, pinoxaden technical was administered
by gavage to 24 pregnant rats per group at dose levels of 0, 3, 30, 300
or 800 mg/kg/day from days 6 through 20 of gestation. Maternal body
weight gain was significantly reduced at the top two dose levels
compared to controls. There was no effect of treatment on the number of
implantation sites, post-implantation loss, live litter size, and sex
ratios, and no significant findings were observed in the maternal
animals upon necropsy. Gravid uterus weights, carcass weights and net
weight change from day 6 post coitum were significantly reduced at the
top dose level. In the presence of the maternal toxicity, mean fetal
body weights were reduced at 800 mg/kg/day, and slightly reduced
ossification was observed at both 800 and 300 mg/kg bw/day. There were
no treatment-related external or visceral observations in the fetuses.
Pinoxaden, was not teratogenic in rats when tested under the conditions
of this study. The no observed effect level (NOEL) for both maternal
and developmental toxicity was 30 mg/kg/day.
Pinoxaden, was evaluated in rabbit developmental toxicity studies.
In an initial guideline rabbit study, pinoxaden technical was
administered by gavage to pregnant rabbits at dose levels of 0, 10, 30,
and 100 mg/kg/day from days 7 through 28 of gestation. Maternal body
weight gain was significantly reduced at 100 mg/kg/day. Fetal body
weight was reduced at the 100 mg/kg dose level. A second guideline
developmental toxicity study was conducted in the rabbit at 0, 10, 30,
and 100 mg/kg/day. Maternal toxicity was observed at 30 and at 100 mg/
kg/day in the form of reduced overall weight gain compared to control
animals. There was no effect of treatment on the number, growth or
survival of the fetuses in utero and no evidence for an adverse effect
on fetal development. There were no treatment-related fetal external,
visceral or skeletal findings. In conclusion, the full set of studies
indicated that pinoxaden is not teratogenic in rabbits. The maternal
NOEL was 10 mg/kg/day, and the NOEL for developmental toxicity was 30
mg/kg/day.
In conclusion, there is no evidence that developing offspring are
more sensitive than adults to the effects of pinoxaden, and it is
concluded, that pinoxaden does not cause primary developmental toxicity
or reproductive toxicity.
4. Subchronic toxicity. Pinoxaden technical was evaluated in a
number of subchronic studies. In a 3-month gavage study in rats the
NOAEL was 300 mg/kg, the highest dose tested. Higher doses in a 28-day
rat study caused kidney toxicity at 600 mg/kg, with a NOAEL of 300 mg/
kg. In a 3-month gavage study in mice, the NOAEL was 100 mg/kg. Effects
at higher dose levels involved reduced body weights at 1,000 mg/kg,
reduced hemoglobin at doses greater than or equal to 400 mg/kg (females
only) and renal tubule basophilia and increased water consumption in
males at 1,000 mg/kg. In a 3-month study in dogs the NOAEL was 100 mg/
kg, and inappetance, body weight loss and gastro-intestinal effects
were seen at 250 mg/kg. In a 28-day dermal (rat) study,
[[Page 67734]]
the NOAEL was 1,000 mg/kg, the highest dose tested, and only a mild,
low-grade inflammatory response at the treatment site was noted. In a
90-day subchronic neurotoxicity study in rats, pinoxaden was not
neurotoxic when administered by gavage at dose levels of 0, 10, 100 and
500 mg/kg/day. There were no treatment-related neurobehavioral or motor
activity effects, no macroscopic findings and no microscopic findings
in central or peripheral nervous tissue. In addition, pinoxaden was
devoid of any acute neurotoxic effects when administered to rats at a
single oral dose of up to 2,000 mg/kg.
5. Chronic toxicity. Pinoxaden was not oncogenic in rats or mice.
In a 2-year combined carcinogenicity/chronic toxicity study in rats,
pinoxaden technical was administered by daily gavage at dose levels of
0, 1, 10, 100, 250, and 500 mg/kg/day. Toxicity was observed in the
form of decreased body weight (500 and 250 mg/kg/day), depressed
survival (500 and 250 mg/kg/day males only), and kidney pathological
changes (500, 250, and 100 mg/kg/day). The kidney pathology was
associated with changes in blood chemistry parameters and other
associated effects. A minor and sporadic epithelial thickening of the
duodenum was observed mainly at 250 and 500 mg/kg. There was no
evidence of a carcinogenic effect in this study. In conclusion, chronic
treatment of pinoxaden to rats produced effects in only one major
target organ at high dose levels, involving chronic progressive
nephropathy and associated effects related to kidney toxicity. The NOEL
was 10 mg/kg for males and females based on kidney effects at 100 mg/kg
and above, and pinoxaden was not carcinogenic.
In an 18-month mouse oncogenicity study, pinoxaden technical was
administered by gavage at dose levels of 0, 5, 40, 300 and 750 mg/kg
body. Toxicity was observed in the form of decreased body weight gain
at 300 mg/kg/day (females only) and 750 mg/kg/day (males and females),
decreased survival rates (40, 300 and 750 mg/kg/day males), minor
hematology effects (300 and 750 mg/kg), increased liver weights (300
and 750 mg/kg, with increased glycogen deposition) and increased kidney
weights (750 mg/kg in females only). Increased epithelial thickening
occurred in the small intestine of males and females at 300 and 750 mg/
kg. The reduced survival at the higher dose levels in males was a
consequence of the gavage dosing procedure, as demonstrated by macro-
and micropathology evidence of lung involvement as the single major
factor contributing to death. Other than increased mortality in males,
there were no treatment-related effects at 40 mg/kg/day. The NOEL for
this study was 5 mg/kg for both males and females, and pinoxaden was
not carcinogenic.
In a 12-month chronic oral toxicity study in dogs, pinoxaden
technical was administered by capsule at dose levels of 0, 5, 25 or 125
mg/kg/day. At 25 and 125 mg/kg/day, treatment-related clinical
observations were limited to an increased incidence of salivation at
dosing and minor gastrointestinal effects, which were not considered
adverse. There were noadverse effects on body weights or food
consumption. Minor changes in hematology and blood clinical chemistry
parameters were observed at 25 and 125 mg/kg/day compared to control
animals. However, due to the small magnitude of the effects and the
absence of any treatment-related effects on organ weights or any
pathology findings, these clinical pathology changes are considered to
be of no toxicological significance. There were no treatment-related
micropathology changes seen at any dose level. The NOAEL in this study
was 125 mg/kg/day.
6. Animal metabolism. Animal metabolism of pinoxaden is well
understood. Pinoxaden is rapidly absorbed and excreted when
administered to rats, and tissue residues are extremely low, with no
accumulation upon repeated dosing. Similar rapid absorption and
excretion was seen in mice and rabbits. The metabolic pathway is
similar in rodents, rabbits, goats and hens.
7. Metabolite toxicology. Toxicity of pinoxaden metabolites has
been tested and is well understood. The toxicological profile of all
metabolites supports the proposed definition of residue.
8. Endocrine disruption. Pinoxaden does not belong to a class of
chemicals known or suspected of having adverse effects on the endocrine
system. There is no evidence that pinoxaden has any effect on endocrine
function in developmental or reproductive studies. Furthermore,
histological investigation of endocrine organs in chronic dog, mouse,
and rat studies did not indicate that the endocrine system is targeted
by pinoxaden.
C. Aggregate Exposure
1. Dietary exposure. The potential for chronic and acute dietary
exposure from pinoxaden through food and water sources is addressed
below.
i. Food. Dietary (food) risk evaluations for pinoxaden were
performed using field trial residues. A percent of crop treated value
of 20% was estimated for wheat and barley based upon Syngenta's
estimates of economic, pest, and competitive pressures. Wheat and
barley are the only RAC included in the assessment. For the chronic
assessments, the average wheat and barley field trial residue values
were utilized. For the acute assessment, the two highest field trial
residues were averaged and this highest average field trial residue
(HAFT) was used in the assessment for all non-blended and partially
blended commodities. All dietary exposure evaluations were made using
the Dietary Evaluation Model (DEEMTM, version 7.87) from
Exponent, Inc. and the USDA's Continuing Survey of Food Intake by
Individuals (1994-96) with the supplemental 1998 children's survey.
Chronic exposure was compared to a chronic reference dose of 0.10 mg/kg
bw/day is based upon a NOAEL of 10 mg/kg bw/day from the chronic rat
study. The acute reference dose of 0.3 mg/kg bw/day for the
subpopulation of women 13-49 years of age is based upon the
developmental NOAEL of 30 mg/kg/day in developmental toxicity studies
in rabbits. For all other subpopulations, the acute reference dose of
1.5 mg/kg bw/day is based upon a NOAEL for acute effects at 150 mg/kg/
day in a range finding rabbit developmental toxicity study. A 100x
uncertainty factor was assumed for both the chronic and acute
assessments. The chronic exposures were expressed as a percent of a
reference dose of 0.10 mg/kg bw/day. The acute exposures (at the 99.9th
percentile) were expressed as a percent of a reference dose of 0.3 mg/
kg bw/day for women 13-49 years of age and 1.5 mg/kg bw/day for all
other subpopulations. Secondary residues in animal commodities were
calculated by constructing diets for beef and dairy cattle, poultry and
swine in order to calculate anticipated residues in meat, fat, milk and
pork. The beef cattle diet was used to calculate meat, fat and organ
meats residues. The dairy cattle diet was used to estimate residues in
milk. The swine diet was used for secondary residues in pork
commodities and the poultry diet was used for residues in poultry
commodities. The chronic animal diet was calculated using averaged
field trial residues where as the acute animal diet used averaged field
trial residues on blended commodities such as grain and the HAFT on
non-blended commodities such as hay, straw and forage. Beef (cattle and
dairy) and swine transfer factors were derived from a lactating goat
metabolism study, where the
[[Page 67735]]
animals were dosed with 121 ppm pinoxaden. Poultry transfer factors
were derived from a hen metabolism study, where the animals were dosed
with 97 ppm pinoxaden.
The results were favorable in both acute and chronic assessment
scenarios. Acute exposures at the (99.9th percentile) were 0.11% of the
acute reference dose (0.3 mg/kg bw/day) for women 13-49 years of age,
and less than 0.05% for all other subpopulations. The chronic exposure
values were negligible (< 0.05% of the chronic reference dose of 0.10
mg/kg bw/day for all subpopulations).
ii. Drinking water. The acute estimated environmental
concentrations of pinoxaden (including the major degradates) in surface
and ground water are 1.366 ppb (PRZM/EXAMS) and 0.003234 ppb (SCI-
GROW), respectively. The acute Population Adjusted Dose (aPAD) for
pinoxaden (plus degradates) is 0.3 mg/kg bw/day for women 13-49 years
of age and 1.5 mg/kg bw/day for all other population subgroups. From
the acute dietary exposure analysis, the highest acute food exposure
from the uses of pinoxaden was 0.000509 mg/kg/day at the 99.9th
percentile for the 20-49 years old subpopulation. Using this
information, acute drinking water levels of comparison (DWLOC acute)
were calculated for pinoxaden and the major degradates, ranging from
8,990 to 52,487 ppb. Based on this analysis, pinoxaden (plus
degradates) estimated environmental concentrations (EECs) do not exceed
the calculated acute DWLOCs. The chronic estimated environmental
concentration of pinoxaden (including the major degradates) in surface
water is 0.21137 ppb (annual average value from PRZM/EXAMS). The
chronic PAD for pinoxaden (plus degradates) is 0.10 mg/kg bw/day. From
the chronic dietary exposure analysis, the highest exposure estimate of
0.000047 mg/kg bw/day was determined for the children 1-2 years old
subpopulation. Based on the EPA's ``Interim Guidance for Conducting
Drinking Water Exposure and Risk Assessments'' document (62 FR 63662,
December, 2, 1997), chronic DWLOC chronic were calculated for pinoxaden
(plus degradates), ranging from 999.5 to 2999.4 ppb. Based on this
analysis, pinoxaden (plus degradates) EECs do not exceed the calculated
chronic DWLOCs.
2. Non-dietary exposure. There are no sources ofnon-dietary
exposure, as pinoxaden will be registered for agricultural uses only
and will not be available for any residential or public uses.
D. Cumulative Effects
The potential for cumulative effects of pinoxaden and other
substances that have a common mechanism of toxicity has also been
considered. Pinoxaden, is a member of the new phenylpyrazolin class of
herbicides. There is no reliable information to indicate that toxic
effects produced by pinoxaden would be cumulative with those of any
other chemical including another pesticide. Therefore, Syngenta
believes it is appropriate toconsider only the potential risks of
pinoxaden in an aggregate risk assessment.
E. Safety Determination
1. Infants and children. In assessing the potential for additional
sensitivity of infants and children to residues of pinoxaden, data from
developmental toxicity studies in the rat and rabbit and a two-
generation reproduction study in the rat have been considered. In a
multi-generation reproductive study, there were no indications of any
differences in sensitivity to pinoxaden exposure between the different
generations or between animals and offspring. The parental NOAEL for
both sexes was considered to be 250 mg/kg/day. Offspring effects were
not observed at dose levels that did not produce parental toxicity.
Pinoxaden was not teratogenic and not directly toxic to the progeny in
a developmental toxicity study in rats. The NOEL for both maternal and
developmental toxicity was 30 mg/kg/day. Pinoxaden was not teratogenic
in rabbits, and the maternal NOEL was 10 mg/kg/day. The NOEL for
fetuses was 30 mg/kg/day. Since the NOEL for fetal effects was higher
than the NOEL for maternal effects, there was no indication of a
greater sensitivity of fetuses to pinoxaden administration. FFDCA
section 408 provides that EPA may apply an additional safety factor for
infants and children in the case of threshold effects to account for
prenatal and postnatal toxicity and the completeness of the database.
Based on the current toxicological requirements, the database for
pinoxaden relative to prenatal and postnatal effects for children is
complete. Further, the developmental studies showed no increased
sensitivity in fetuses as compared to maternal animals following in
utero exposures in rats and rabbits, and no increased sensitivity in
pups as compared to the adults in the multi-generation reproductive
toxicity study. Therefore, it is concluded that an additional
uncertainty factor is not warranted to protect the health of infants
and children and that RfDs of 0.3 mg/kg/day (acute exposures to women
13-50 yrs of age), 1.5 mg/kg/day (acute exposures to general
population) and 0.10 mg/kg/day (chronic expsoures) are appropriate for
assessing aggregate risk to infants and children of pinoxaden. Chronic
and acute aggregate exposures to all infants (< 1 year old) is less than
0.2% of the acute and chronic RfDs. Therefore, based on the
completeness and reliability of the toxicity database, Syngenta
concludes that there is reasonable certainty that no harm will result
to infants and children from aggregate exposure to pinoxaden residues.
F. International Tolerances
There are no tolerances or maximum residue limits set for pinoxaden
in any country at the time of this filing.
[FR Doc. 04-25714 Filed 11-18-04; 8:45 am]
BILLING CODE 6560-50-S