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Notice of Filing a Pesticide Petition to Establish a Tolerance for a Certain Pesticide Chemical in or on Food

Note: EPA no longer updates this information, but it may be useful as a reference or resource.


 [Federal Register: December 6, 2000 (Volume 65, Number 235)]
[Notices]
[Page 76249-76253]
From the Federal Register Online via GPO Access [wais.access.gpo.gov]
[DOCID:fr06de00-67]

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 ENVIRONMENTAL PROTECTION AGENCY

[PF-984; FRL-6755-4]


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 control number PF-984, must be
received on or before January 5, 2001.

ADDRESSES:  Comments may be submitted by mail, electronically, or in
person. Please follow the detailed

[[Page 76250]]

instructions for each method as provided in Unit I.C. of the
SUPPLEMENTARY INFORMATION. To ensure proper receipt by EPA, it is
imperative that you identify docket control number PF-984 in the
subject line on the first page of your response.

FOR FURTHER INFORMATION CONTACT:  By mail: Shaja R. Brothers,
Registration Support Branch, Registration Division (7505C), Office of
Pesticide Programs, Environmental Protection Agency, 1200 Pennsylvania
Ave., NW., Washington, DC 20460; telephone number: (703) 308-3194; e-
mail address: brothers.shaja@epa.gov.

SUPPLEMENTARY INFORMATION:

I. General Information

A. Does this Action Apply to Me?

    You may be affected by this action if you are an agricultural
producer, food manufacturer or pesticide manufacturer. Potentially
affected categories and entities may include, but are not limited to:

------------------------------------------------------------------------
                                                          Examples of
           Categories                    NAICS            potentially
                                                      affected  entities
------------------------------------------------------------------------
Industry                          111                 Crop production
                                  112                 Animal production
                                  311                 Food manufacturing
                                  32532               Pesticide
                                                       manufacturing
------------------------------------------------------------------------

    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 the table could also be
affected. The North American Industrial Classification System (NAICS)
codes have been provided to assist you and others in determining
whether or not this action might apply to certain entities. If you have
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 Additional Information, Including Copies of this
Document and Other Related Documents?

    1. Electronically. You may obtain electronic copies of this
document, and certain other related documents that might be available
electronically, from the EPA Internet Home Page at http://www.epa.gov/.
To access this document, on the Home Page select ``Laws and
Regulations'' and then look up the entry for this document under the
``Federal Register--Environmental Documents.'' You can also go directly
to the Federal Register listings at http://www.epa.gov/fedrgstr/.
    2. In person. The Agency has established an official record for
this action under docket control number PF-984. The official record
consists of the documents specifically referenced in this action, any
public comments received during an applicable comment period, and other
information related to this action, including any information claimed
as confidential business information (CBI). This official record
includes the documents that are physically located in the docket, as
well as the documents that are referenced in those documents. The
public version of the official record does not include any information
claimed as CBI. The public version of the official record, which
includes printed, paper versions of any electronic comments submitted
during an applicable comment period, is available for inspection in the
Public Information and Records Integrity Branch (PIRIB), Rm. 119,
Crystal Mall #2, 1921 Jefferson Davis Highway, Arlington, VA, from 8:30
a.m. to 4 p.m., Monday through Friday, excluding legal holidays. The
PIRIB telephone number is (703) 305-5805.

C. How and to Whom Do I Submit Comments?

    You may submit comments through the mail, in person, or
electronically. To ensure proper receipt by EPA, it is imperative that
you identify docket control number PF-984 in the subject line on the
first page of your response.
    1. By mail. Submit your comments to: Public Information and Records
Integrity Branch (PIRIB), Information Resources and Services Division
(7502C), Office of Pesticide Programs (OPP), Environmental Protection
Agency, 1200 Pennsylvania Ave., NW., Washington, DC 20460.
    2. In person or by courier. Deliver your comments to: Public
Information and Records Integrity Branch (PIRIB), Information Resources
and Services Division (7502C), Office of Pesticide Programs (OPP),
Environmental Protection Agency, Rm. 119, Crystal Mall #2, 1921
Jefferson Davis Highway, Arlington, VA. The PIRIB is open from 8:30
a.m. to 4 p.m., Monday through Friday, excluding legal holidays. The
PIRIB telephone number is (703) 305-5805.
    3. Electronically. You may submit your comments electronically by
e-mail to: opp-docket@epa.gov, or you can submit a computer disk as
described above. Do not submit any information electronically that you
consider to be CBI. Avoid the use of special characters and any form of
encryption. Electronic submissions will be accepted in Wordperfect 6.1/
8.0 or ASCII file format. All comments in electronic form must be
identified by docket control number PF-984. Electronic comments may
also be filed online at many Federal Depository Libraries.

D. How Should I Handle CBI That I Want to Submit to the Agency?

    Do not submit any information electronically that you consider to
be CBI. You may claim information that you submit to EPA in response to
this document as CBI by marking any part or all of that information as
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 version of the
official record. Information not marked confidential will be included
in the public version of the official record without prior notice. If
you have any questions about CBI or the procedures for claiming CBI,
please consult the person identified 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
control 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

[[Page 76251]]

under section 408 of the Federal Food, Drug, and Comestic Act (FFDCA),
21 U.S.C. 346a. EPA has determined that this petition contains data or
information regarding the elements set forth in section 408(d)(2);
however, EPA has not fully evaluated the sufficiency of the submitted
data at this time or whether the data support 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 22, 2000.
James Jones,

Director, Registration Division, Office of Pesticide Programs.

 Summary of Petitions

    The petitioner summary of the pesticide petition is printed below
as required by section 408(d)(3) of the FFDCA. The summary of the
petition was prepared by the petitioner and represents the view of the
petitioners. EPA is publishing the petition summary verbatim without
editing it in any way. 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.

 Interregional Research Project Number 4

 9E6063 and 7E4865

     EPA has received pesticide petitions (9E6063 and 7E4865) from
Interregional Research Project Number 4, Technology Centre of New
Jersey, 681 U.S. Highway # 1 South, North Brunswick, NJ, 08902-3390
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 tolerances for residues of clomazone in or on the raw
agricultural commodities (RAC) tuberous and corm vegetable (except
potato) crop subgroup and cucurbit vegetable crop group at 0.05 parts
per million (ppm). EPA has determined that the petitions contain data
or information regarding the elements set forth in section 408(d)(2) of
the FFDCA; however, EPA has not fully evaluated the sufficiency of the
submitted data at this time or whether the data supports granting of
the petitions. Additional data may be needed before EPA rules on the
petitions.

A. Residue Chemistry

    1. Plant metabolism. The metabolism of clomazone in plants is
adequately understood.
    2.  Analytical method. There is a practical analytical method for
detecting and measuring levels of clomazone in or on tuberous and corm
vegetable (except potato) crop subgroup and cucurbit vegetable crop
group, with a limit of detection that allows monitoring of food for
residues at or above the levels proposed in this tolerance. Samples are
analyzed using an analytical method consisting of an acid reflux, a
C18 solid phase extraction (SPE), a Florisil SPE clean-up
followed by gas chromatography (GC)-mass selective detection (MSD). The
method limit of quantitation (LOQ) is 0.05 ppm. The method limit of
detection (LOD) is 0.01 ppm.
    3. Magnitude of residues. The representative commodity for the
tuberous and corm vegetable (except potato) subgroup, is sweet potato.
IR-4 has previously submitted residue data for clomazone use on sweet
potato (MRID # 40572701). Four field trials, with two different
applications timings were conducted. No clomazone residues were found
above the LOQ (0.05 ppm) in any of the treated samples. FMC Corporation
submitted additional data for clomazone on sweet potatoes (MRID #
44441405).

B. Toxicological Profile

    1. Acute toxicity. The following mammalian toxicity studies have
been conducted with clomazone technical (unless noted otherwise) to
support registrations and/or tolerances of clomazone:
    i. A rat acute oral study with an lethal dose (LD)50 of
2,077 mg/kg (male) and 1,369 mg/kg (female).
    ii. A rabbit acute dermal lethal concentration (LC)50 of
> 2,000 mg/kg.
    iii. A rat acute inhalation LC50 of 6.25 mg/L/4 hrs.
(male), 4.23 mg/L/hrs. (female) and 4.85 mg/L/4 hrs. (combined sexes).
    iv. A primary eye irritation study in the rabbit which showed
practically no irritation.
    v. A primary dermal irritation study in the rabbit which showed
minimal irritation.
    vi. A primary dermal sensitization study in the guinea pig which
showed no sensitization.
    vii. Acute delayed neurotoxicity - clomazone, and its known
metabolites, are not structurally related to known neurotoxic
substances.
    2. Genotoxicity. The following genotoxicity tests were all
negative: Ames Assay; CHO/HGPRT Mutation Assay; and Structural
Chromosomal Aberration. The Unscheduled DNA Synthesis genotoxicity was
negative with activation; weakly positive without activation.
    3. Reproductive and developmental toxicity. A 2-generation
reproduction study was conducted in the rat with a parental systemic no
observed adverse effect level (NOAEL) of 1,000 ppm (50 mg/kg/day) based
on decreased body weight and food consumption at 2,000 ppm; and a
progeny systemic NOAEL of 1,000 ppm (50 mg/kg/day) based on decreased
pup body weight at 2,000 ppm. The reproductive performance NOAEL was >
4,000 ppm which was the highest dose tested (HDT). There was an
unexplained decrease in the fertility index during mating of the F1b
generation at 4,000 ppm which was not observed in the F1a litter or
repeated in the F2 generation. Additionally, there was one F2a pup at
1,000 ppm which had non-functional hindlimbs and one F2b pup at 4,000
ppm which had extended hindlimbs with no flexion at the ankle. These
limb abnormalities were not considered treatment-related for the
following reasons (i) there was no dose response observed, (ii) the
findings were not statistically significant, (iii) the findings were
not repeated at the 1,000 ppm dose level in the F2b litter or found in
the F1a or F1b litters, and (iv) these findings or related hindlimb
abnormalities were not observed in developmental studies at gavage dose
levels up to 100 mg/kg/day in the rat or 240 mg/kg/day in the rabbit.
     A developmental toxicity study in rats given gavage doses of 100,
300 and 600 mg/kg/day and with maternal and fetal NOAELs of 100 mg/kg/
day. The maternal NOAEL is based on decreased locomotion, genital
staining and runny eyes and the developmental NOAEL is based on
increased incidence of delayed ossification at 300 mg/kg/day. This
study was negative for developmental at all doses tested.
     A developmental toxicity study in rabbits given gavage doses of
30, 240 and 700 mg/kg/day with maternal and fetal NOAELs of 240 mg/kg/
day. The maternal NOAEL is based on a decrease in body weight and the
developmental NOAEL is based on an increase in the number of fetal
resorptions at 700 mg/kg/day. This study was negative for
teratogenicity at all doses tested.
     In all cases, the reproductive and developmental NOAELs were equal
to the parental NOAELs, thus indicating that clomazone does not pose
any increased risk to infants or children.
    4. Subchronic toxicity. In a 90-day feeding subchronic study in
mice the

[[Page 76252]]

NOAEL was 20 ppm (< 2.9 mg/kg/day)based on liver cytomegaly at 20 ppm.
    5. Chronic toxicity. A 12-month feeding study in the dog with a
NOAEL of 500 ppm (14.0 mg/kg/day for males; 14.9 mg/kg/day for females)
based on increased blood cholesterol and liver weights at 2,500 ppm.
     A 24-month chronic feeding/carcinogenicity study in the rat with a
NOAEL of 100 ppm (4.3 mg/kg/day for males; 5.5 mg/kg/day for females)
based on increased liver weights and increased liver cytomegaly at 500
ppm. There were no carcinogenic effects observed under the conditions
of the study.
     A 24-month chronic feeding/carcinogenicity study in the mouse with
a NOAEL of 100 ppm (15 mg/kg/day) based on an increase in the white
blood cell count. There were no carcinogenic effects observed under the
conditions of the study.
     Using the Guidelines for Carcinogen Risk Assessment, it is
proposed that clomazone be classified as Group E for carcinogenicity
(no evidence of carcinogenicity) based on the results of
carcinogenicity studies in rats and mice.
     The reference dose (RfD) for clomazone has been established at
0.043 mg/kg/day. The RfD for clomazone is based on the 24-Month
Feeding/Carcinogenicity Study in the Rat with a NOAEL of 4.3 mg/kg/day
and an uncertainty factor of 100.
    6. Animal metabolism. The metabolism of clomazone in animals is
adequately understood. Clomazone degrades rapidly and extensively in
rats, goats and poultry to a variety of metabolites which were readily
excreted from the body via excreta.
    7. Metabolite toxicology. No clomazone related metabolite residues
have been identified as being of toxicological concern. The residue of
significance is parent.
    8. Endocrine disruption. No specific tests have been conducted with
clomazone to determine whether the herbicide may have an effect in
humans that is similar to an effect produced by a naturally occurring
estrogen or other endocrine effects. It should be noted, however, that
the chemistry of clomazone is unrelated to that of any compound
previously identified as having estrogen or other endocrine effects.
Additionally, a standard battery of required studies has been
completed. These studies include an evaluation of the potential effects
on reproduction and development, and an evaluation of the pathology of
the endocrine organs following repeated or long-term exposure. No
endocrine effects were noted in any of these studies with clomazone.

C. Aggregate Exposure

    1. Dietary exposure--i. Food For purposes of assessing the
potential dietary exposure, EPA has estimated aggregate exposure based
on the Theoretical Maximum Residue Contribution (TMRC) from the
established tolerances for clomazone. The TMRC is a ``worst case''
estimate of dietary exposure since it is assumed that 100 percent of
all crops for which tolerances are established are treated and that
pesticide residues are present at the tolerance levels. Dietary
exposure to residues of clomazone in or on food will be limited to
residues on cabbage (0.1 ppm), cottonseed (0.05 ppm), cucurbit
vegetables (0.05 ppm), succulent peas (0.05 ppm), peppers (0.05 ppm),
soybeans (0.05 ppm), sweet potato (0.05 ppm), snap beans (0.05 ppm)
rice (0.05 ppm), sugar (from cane) (0.05 ppm) and residues on tuberous
and corm vegetable (except potato) (0.05 ppm each). As noted above,
this exposure assessment is based on very conservative assumptions,
i.e., 100% of crops treated will contain clomazone residues and those
residues would be at the level of the tolerance. It is FMC's opinion
that these assumptions result in an overestimate of human exposure.
    ii. Drinking water. It is unlikely that there will be exposure to
residues of clomazone through drinking water supplies. A field mobility
study was conducted at a loamy sand location. Clomazone was found only
in the top 0-1 ft. soil samples during the 61 day study period. No
clomazone residue
(< 0.02 ppm) was detected in the deeper soil levels (1-2, 2-3 and 3-4
ft.). Detectable residues of clomazone were found only in the 0-6
horizon. Should movement into surface water occur, potential for
clomazone residues to be detected in drinking water supplies at
significant levels is minimal. Accordingly, there is no reasonable
expectation that there would be an additional incremental aggregate
dietary contribution of clomazone through groundwater or surface water.
    2. Non-dietary exposure. Clomazone is only registered for use on
food crops. Since the proposed use on the tuberous and corm vegetable
(except potato) crop subgoup and cucurbit vegetable crop group is
consistent with existing registrations, there will be no non-dietary,
non-occupational exposure.

D. Cumulative Effects

     Clomazone is an isoxazolidinone herbicide. No other registered
chemical exists in this class of chemistry. Therefore, given
clomazone's unique chemistry low acute toxicity, the absence of
genotoxic, oncogenic, developmental or reproductive effects, and low
exposure potential (see Sections A and C), the expression of cumulative
human health effects with clomazone and other natural or synthetic
pesticides is not anticipated.

E. Safety Determination

    1. U.S. population. Using the conservative exposure assumptions
described above, based on the completeness and reliability of the
toxicology data, it is concluded that aggregate exposure due to
existing registered uses, and pending uses, of clomazone will utilize
less than 1% of the RfD for the U.S. population. Additionally, an
analysis concluded that aggregate exposure to clomazone adding use on
cucurbit vegetable crop group and tuberous and corm vegetable (except
potato) crop subgroup at a 0.05 ppm will utilize a negligible (i.e.,
0.011% or less for cucurbits and 0.002% or less for these root crops)
percent of the RfD for the U.S. population. EPA generally has no
concern for exposures below 100% of the RfD because the RfD represents
the level at or below which daily aggregate dietary exposure over a
lifetime will not pose appreciable risks to human health. It is
concluded that there is a reasonable certainty that no harm will result
from aggregate exposure to residues of clomazone, including all
anticipated dietary exposure.
    2. Infants and children. Based on the current toxicological data
requirements, the data base relative to prenata and postnatal effects
for children is complete (See Section B.3). Further, for clomazone, the
NOAEL in the two year feeding study which was used to calculate the RfD
(0.043 mg/kg/day) is already lower than the NOAELs from the
reproductive and developmental studies by a factor of more than 10-
fold. Therefore, it can be concluded that no additional uncertainty
factors are warranted and that the RfD at 0.043 mg/kg/day is
appropriate for assessing aggregate risk to infants and children as
well as adults.
     Using the conservative exposure assumptions described above, FMC
has concluded that < 1% of the RfD will be utilized by aggregate
exposure to residues of clomazone in/on tuberous and corm vegetable
(except potato) crop subgroup and cucurbit vegetable crop group for
non-nursing infants (< 1 year old), the population subgroup most
sensitive.
     Based on the above information, FMC has concluded that there is a
reasonable

[[Page 76253]]

certainty that no harm will result to infants, children or adults from
dietary food consumption exposure to clomazone residues from tuberous
and corm vegetable (except potato) crop subgroup and cucurbit vegetable
crop group plus all other clomazone treated human dietary food sources.

F. International Tolerances

     There are Codex residue limits for residues of clomazone in or on
oilseed rape, potatoes, tobacco, soybeans, rice, cottonseed, sugarcane
and peas.
[FR Doc. 00-31058 Filed 12-5-00; 8:45 am]
BILLING CODE 6560-50-S 

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