Cyprodinil; Pesticide Tolerances, 50548-50553 [E8-19747]
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50548
Federal Register / Vol. 73, No. 167 / Wednesday, August 27, 2008 / Rules and Regulations
Dated: August 18, 2008.
Fred M. Rosa, Jr.,
Rear Admiral, U.S. Coast Guard Commander,
Fifth Coast Guard District.
[FR Doc. E8–19894 Filed 8–26–08; 8:45 am]
BILLING CODE 4910–15–P
ENVIRONMENTAL PROTECTION
AGENCY
40 CFR Part 180
[EPA–HQ–OPP–2007–1069; FRL–8377–8]
Cyprodinil; Pesticide Tolerances
Environmental Protection
Agency (EPA).
ACTION: Final rule.
sroberts on PROD1PC70 with RULES
AGENCY:
SUMMARY: This regulation establishes
tolerances for residues of cyprodinil, 4cyclopropyl-6-methyl-N-phenyl-2pyrimidinamine, in or on tomato;
tomatillo; tomato, paste; avocado;
sapote, black; canistel; sapote, mamey;
mango; papaya; sapodilla; star apple;
parsley, leaves; parsley, dried leaves;
vegetable, leaves of root and tuber,
group 2; vegetable, root, except
sugarbeet, subgroup 1B; lemon; lime;
citrus, dried pulp; citrus, oil; kiwifruit;
onion, bulb; onion, green; strawberries;
vegetable, cucurbit, group 9; and meat
byproducts of cattle, goats, horses and
sheep. Interregional Research Project
Number 4 (IR–4) requested these
tolerances under the Federal Food,
Drug, and Cosmetic Act (FFDCA).
DATES: This regulation is effective
August 27, 2008. Objections and
requests for hearings must be received
on or before October 27, 2008, and must
be filed in accordance with the
instructions provided in 40 CFR part
178 (see also Unit I.C. of the
SUPPLEMENTARY INFORMATION).
ADDRESSES: EPA has established a
docket for this action under docket
identification (ID) number EPA–HQ–
OPP–2007–1069. To access the
electronic docket, go to https://
www.regulations.gov, select ‘‘Advanced
Search,’’ then ‘‘Docket Search.’’ Insert
the docket ID number where indicated
and select the ‘‘Submit’’ button. Follow
the instructions on the regulations.gov
website to view the docket index or
access available documents. All
documents in the docket are listed in
the docket index available in
regulations.gov. Although listed in the
index, some information is not publicly
available, e.g., Confidential Business
Information (CBI) or other information
whose disclosure is restricted by statute.
Certain other material, such as
copyrighted material, is not placed on
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the Internet and will be publicly
available only in hard copy form.
Publicly available docket materials are
available in the electronic docket at
https://www.regulations.gov, or, if only
available in hard copy, at the OPP
Regulatory Public Docket in Rm. S–
4400, One Potomac Yard (South Bldg.),
2777 S. Crystal Dr., Arlington, VA. The
Docket Facility is open from 8:30 a.m.
to 4 p.m., Monday through Friday,
excluding legal holidays. The Docket
Facility telephone number is (703) 305–
5805.
FOR FURTHER INFORMATION CONTACT:
Barbara Madden, Registration Division
(7505P), Office of Pesticide Programs,
Environmental Protection Agency, 1200
Pennsylvania Ave., NW., Washington,
DC 20460–0001; telephone number:
(703) 305–6463; e-mail address:
madden.barbara@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 those engaged in the
following activities:
• Crop production (NAICS code 111).
• Animal production (NAICS code
112).
• Food manufacturing (NAICS code
311).
• Pesticide manufacturing (NAICS
code 32532).
This listing is not intended to be
exhaustive, but rather to provide 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 EPA’s tolerance
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regulations at 40 CFR part 180 through
the Government Printing Office’s pilot
e-CFR site at https://www.gpoaccess.gov/
ecfr.
C. Can I File an Objection or Hearing
Request?
Under section 408(g) of FFDCA, any
person may file an objection to any
aspect of this regulation and may also
request a hearing on those objections.
You must file your objection or request
a hearing on this regulation in
accordance with the instructions
provided in 40 CFR part 178. To ensure
proper receipt by EPA, you must
identify docket ID number EPA–HQ–
OPP–2007–1069 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
as required by 40 CFR part 178 on or
before October 27, 2008.
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 this copy,
identified by docket ID number EPA–
HQ–OPP–2007–1069, by one of the
following methods:
• Federal eRulemaking Portal: https://
www.regulations.gov. Follow the on-line
instructions for submitting comments.
• Mail: Office of Pesticide Programs
(OPP) Regulatory Public Docket (7502P),
Environmental Protection Agency, 1200
Pennsylvania Ave., NW., Washington,
DC 20460–0001.
• Delivery: OPP Regulatory Public
Docket (7502P), Environmental
Protection Agency, Rm. S–4400, One
Potomac Yard (South Bldg.), 2777 S.
Crystal Dr., Arlington, VA. Deliveries
are only accepted during the Docket’s
normal hours of operation (8:30 a.m. to
4 p.m., Monday through Friday,
excluding legal holidays). Special
arrangements should be made for
deliveries of boxed information. The
Docket Facility telephone number is
(703) 305–5805.
II. Petition for Tolerance
In the Federal Register of January 23,
2008 (73 FR 3964) (FRL–8345–7), EPA
issued a notice pursuant to section
408(d)(3) of FFDCA, 21 U.S.C.
346a(d)(3), announcing the filing of a
pesticide petition (PP 7E7235) by
Interregional, Research Project Number
4 (IR–4), 500 College Road East, Suite
201W, Princeton, NJ 08540. The petition
requested that 40 CFR 180.532 be
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amended by establishing tolerances for
residues of the fungicide cyprodinil, 4cyclopropyl-6-methyl-N-phenyl-2pyrimidinamine, in or on the food
commodities tomato at 0.40 parts per
million (ppm); tomatillo at 0.40 ppm;
tomato, paste at 1.0 ppm; avocado at 1.2
ppm; sapote, black at 1.2 ppm; canistel
at 1.2 ppm; sapote, mamey at 1.2 ppm;
mango at 1.2 ppm; papaya at 1.2 ppm;
sapodilla at 1.2 ppm; star apple at 1.2
ppm; herbs subgroup19A, fresh at 25
ppm; herbs subgroup 19A, dried at 170
ppm; vegetable, root and tuber, group,
leaves at 9.0 ppm; vegetable, root,
except sugarbeet subgroup at 0.60 ppm;
lemon at 0.6 ppm; lime at 0.6 ppm;
kiwifruit at 1.8 ppm; onion, dry bulb at
0.50 ppm; onion, green at 1.2 ppm;
strawberry at 7.0 ppm; and cucurbits at
0.40 ppm. That notice referenced a
summary of the petition prepared by IR4, the registrant, which is available to
the public in the docket, https://
www.regulations.gov. Comments were
received on the notice of filing. EPA’s
response to these comments is
discussed in Unit IV.C.
Based upon review of the data
supporting the petition, EPA is revising
some of the items as proposed in this
Unit. The reason for these changes is
explained in Unit IV.D.
III. Aggregate Risk Assessment and
Determination of Safety
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. . . .’’
Consistent with section 408(b)(2)(D)
of FFDCA, and the factors specified in
section 408(b)(2)(D) of FFDCA, EPA has
reviewed the available scientific data
and other relevant information in
support of this action. EPA has
sufficient data to assess the hazards of
and to make a determination on
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aggregate exposure for the petitioned-for
tolerances for residues of cyprodinil, 4cyclopropyl-6-methyl-N-phenyl-2pyrimidinamine on tomato; tomatillo;
tomato, paste; avocado; sapote, black;
canistel; sapote, mamey; mango; papaya;
sapodilla; star apple; parsley, leaves;
parsley, dried leaves; vegetable, leaves
of root and tuber, group 2; vegetable,
root, except sugarbeet, subgroup 1B;
lemon; lime; citrus, dried pulp; citrus,
oil; kiwifruit; onion, bulb; onion, green;
strawberries; vegetable, cucurbit, group
9; and meat byproducts of cattle, goats,
horses and sheep. EPA’s assessment of
exposures and risks associated with
establishing tolerances 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.
Cyprodinil has low acute toxicity via
the oral, dermal, and inhalation routes.
Cyprodinil is mildly irritating to the
eyes and negligibly irritating to the skin.
It is a dermal sensitizer. The major
target organs of cyprodinil are the liver
in both rats and mice and the kidney in
rats. Liver effects were consistent among
male and female rats and mice in both
subchronic and chronic studies and
typically included increased liver
weights along with increases in serum
clinical chemistry parameters associated
with adverse effects on liver function
(i.e., increased cholesterol and
phospholipid levels). Microscopic
lesions in rats and mice included
hepatocyte hypertrophy and
hepatocellular necrosis. In the kidneys,
adverse effects were manifested as
chronic tubular lesions and chronic
kidney inflamation following
subchronic exposure of male rats.
Chronically, cyprodinil caused
increased kidney weights and
progressive nephropathy in male rats.
Chronic effects in dogs were limited to
decreased body-weight gain, decreased
food consumption and decreased food
efficiency. Liver toxicity was not seen in
the dog. The hematopoietic system also
appeared to be a target of cyprodinil,
causing mild anemia in rats exposed
subchronically. There was no evidence
of carcinogenic potential in either the
rat chronic toxicity/carcinogenicity or
mouse carcinogenicity studies and no
concern for mutagenicity. There was no
evidence of increased susceptibility in
the developmental rat or rabbit study
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following in utero exposure or in the 2generation reproduction study following
prenatal or postnatal exposure. No
clinical signs of toxicity suggestive of
neurobehavioral alterations nor
evidence of neuropathological effects
were observed in the available oraltoxicity studies. There was also no
evidence of a neurodevelopmental effect
in the rat or rabbit developmental
toxicity studies or in the rat 2generation reproductive-toxicity study.
Specific information on the studies
received and the nature of the adverse
effects caused by cyprodinil as well as
the no-observed-adverse-effect-level
(NOAEL) and the lowest-observedadverse-effect-level (LOAEL) from the
toxicity studies can be found at https://
www.regulations.gov in document
Cyprodinil Human Health Risk
Assessment for the uses in/on tomato,
avocado, herbs, root vegetables, leaves
of root and tuber vegetables, lemon,
lime, cucurbits, kiwifruit, green and dry
bulb onions, and strawberries, page 16
in docket ID number EPA–HQ–OPP–
2007–1069.
B. Toxicological Endpoints
For hazards that have a threshold
below which there is no appreciable
risk, a toxicological point of departure
(POD) is identified as the basis for
derivation of reference values for risk
assessment. The POD may be defined as
the highest dose at which NOAEL in the
toxicology study identified as
appropriate for use in risk assessment.
However, if a NOAEL cannot be
determined, the lowest dose at which
the LOAEL of concern are identified or
a Benchmark Dose (BMD) approach is
sometimes used for risk assessment.
Uncertainty/safety factors (UFs) are
used in conjunction with the POD to
take into account 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. Safety is assessed for
acute and chronic dietary risks by
comparing aggregate food and water
exposure to the pesticide to the acute
population adjusted dose (aPAD) and
chronic population adjusted dose
(cPAD). The aPAD and cPAD are
calculated by dividing the POD by all
applicable UFs. Aggregate short-term,
intermediate-term, and chronic-term
risks are evaluated by comparing food,
water, and residential exposure to the
POD to ensure that the margin of
exposure (MOE) called for by the
product of all applicable UFs is not
exceeded. This latter value is referred to
as the Level of Concern (LOC).
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For non-threshold risks, the Agency
assumes that any amount of exposure
will lead to some degree of risk. Thus,
the Agency estimates risk in terms of the
probability of an occurrence of the
adverse effect greater than that expected
in a lifetime. For more information on
the general principles EPA uses in risk
characterization and a complete
description of the risk assessment
process, see https://www.epa.gov/
pesticides/factsheets/riskassess.htm.
A summary of the toxicological
endpoints for cyprodinil used for
human risk assessment can be found at
https://www.regulations.gov in document
Cyprodinil Human Health Risk
Assessment for the uses in/on tomato,
avocado, herbs, root vegetables, leaves
of root and tuber vegetables, lemon,
lime, cucurbits, kiwifruit, green and dry
bulb onions, and strawberries, page 22
in docket ID number EPA–HQ–OPP–
2007–1069.
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C. Exposure Assessment
1. Dietary exposure from food and
feed uses. In evaluating dietary
exposure to cyprodinil, EPA considered
exposure under the petitioned-for
tolerances as well as all existing
cyprodinil tolerances in (40 CFR
180.532). EPA assessed dietary
exposures from cyprodinil in food as
follows:
i. Acute exposure. Quantitative acute
dietary exposure and risk assessments
are performed for a food-use pesticide,
if a toxicological study has indicated the
possibility of an effect of concern
occurring as a result of a 1–day or single
exposure.
In estimating acute dietary exposure,
EPA used food consumption
information from the United States
Department of Agriculture (USDA)
1994–1996 and 1998 Nationwide
Continuing Surveys of Food Intake by
Individuals (CSFII). As to residue levels
in food, EPA used tolerance-level
residues, DEEM default processing
factors and assumed 100 percent crop
treated (PCT) for all existing and
proposed commodities.
ii. Chronic exposure. In conducting
the chronic dietary exposure assessment
EPA used the food consumption data
from the USDA 1994–1996 and 1998
CSFII. As to residue levels in food, EPA
used tolerance level residues, DEEM
default processing factors, and assumed
100 PCT for all existing and proposed
commodities.
iii. Cancer An aggregate exposure
assessment for the purpose of assessing
cancer risk was not performed because
cyprodinil has been classified as ‘‘not
likely to be carcinogenic to humans.’’
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iv. Anticipated residue and PCT
information. EPA did not use
anticipated residue and/or PCT
information in the dietary assessment
for cyprodinil. Tolerance level residues
and 100 PCT were assumed for all
existing and proposed food
commodities.
2. Dietary exposure from drinking
water. The Agency used screening level
water exposure models in the dietary
exposure analysis and risk assessment
for cyprodinil in drinking water. These
simulation models take into account
data on the physical, chemical, and fate/
transport characteristics of cyprodinil.
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.
For surface water the Pesticide Root
Zone Model/Exposure Analysis
Modeling System (PRZM/EXAMS) Tier
2 aquatic models were used, and for
ground water, the Tier 1 aquatic model
Screening Concentration in Ground
Water (SCI–GROW) was utilized. For
the assessment, maximum application
rates and minimum intervals between
applications were used. The Agency has
concluded that the transformation
product CGA–249287 of cyprodinil is of
potential concern for drinking water
sources. Therefore, estimated drinking
water concentrations (EDWCs) of CGA–
249287 were also simulated using the
PRZM/EXAMS and SCI–GROW models.
For surface water, this degradate was
modeled individually, as opposed to the
use of the total residue approach due to
the fact that only one degradate was
modeled and sufficient information was
available for the modeling.
Based on the Tier 2 PRZM/EXAMS
and the Tier 1 SCI–GROW models, the
EDWCs of cyprodinil and its
transformation product CGA–249287 for
acute exposures are estimated to be
34.56 parts per billion (ppb) for surface
water and 0.108 ppb for ground water.
For chronic exposures for non-cancer
assessments the concentrations are
estimated to be 20.05 ppb for surface
water and 0.108 ppb for ground water.
Modeled estimates of drinking water
concentrations were directly entered
into the dietary exposure model. For
acute dietary risk assessment, the water
concentration value of 34.56 ppb was
used to assess the contribution to
drinking water.
For chronic dietary risk assessment,
the water concentration of value 20.05
ppb was used to assess the contribution
to drinking water.
3. From non-dietary exposure. The
term ‘‘residential exposure’’ is used in
this document to refer to non-
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occupational, non-dietary exposure
(e.g., for lawn and garden pest control,
indoor pest control, termiticides, and
flea and tick control on pets).
Cyprodinil is not registered for any
specific use patterns that would result
in residential exposure.
4. Cumulative effects from substances
with a common mechanism of toxicity.
Section 408(b)(2)(D)(v) of FFDCA
requires that, when considering whether
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.’’
EPA has not found cyprodinil to share
a common mechanism of toxicity with
any other substances, and cyprodinil
does not appear to produce a toxic
metabolite produced by other
substances. For the purposes of this
tolerance action, therefore, EPA has
assumed that cyprodinil does not have
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 EPA’s website at https://
www.epa.gov/pesticides/cumulative.
D. Safety Factor for Infants and
Children
1. In general. Section 408(b)(2)(c) of
FFDCA provides that EPA shall apply
an additional tenfold (10X) margin of
safety (MOS) for infants and children in
the case of threshold effects to account
for prenatal and postnatal toxicity and
the completeness of the database on
toxicity and exposure unless EPA
determines based on reliable data that a
different MOS will be safe for infants
and children. This additional margin of
safety is commonly referred to as the
FQPA safety factor (SF). In applying this
provision, EPA either retains the default
value of 10X, or uses a different
additional SF when reliable data
available to EPA support the choice of
a different factor.
2. Prenatal and postnatal sensitivity.
There are no concerns or residual
uncertainties for prenatal and/or
postnatal exposure.
3. Conclusion. EPA has determined
that reliable data show the safety of
infants and children would be
adequately protected if the FQPA SF
were reduced to 1X. That decision is
based on the following findings:
i. The toxicity database for cyprodinil
is complete.
ii. There is no indication that
cyprodinil is a neurotoxic chemical and
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there is no need for a developmental
neurotoxicity study or additional UFs to
account for neurotoxicity.
iii. There is no evidence that
cyprodinil results in increased
susceptibility in in utero rats or rabbits
in the prenatal developmental studies or
in young rats in the 2-generation
reproduction study.
iv. There are no residual uncertainties
identified in the exposure databases.
EPA made conservative (protective)
assumptions in the ground water and
surface water modeling used to assess
exposure to cyprodinil in drinking
water. EPA used similarly conservative
assumptions to assess postapplication
exposure of children as well as
incidental oral exposure of toddlers.
These assessments will not
underestimate the exposure and risks
posed by cyprodinil.
E. Aggregate Risks and Determination of
Safety
EPA determines whether acute and
chronic pesticide exposures are safe by
comparing aggregate exposure estimates
to the aPAD and cPAD. The aPAD and
cPAD represent the highest safe
exposures, taking into account all
appropriate SFs. EPA calculates the
aPAD and cPAD by dividing the POD by
all applicable UFs. For linear cancer
risks, EPA calculates the probability of
additional cancer cases given the
estimated aggregate exposure. Shortterm, intermediate-term, and chronicterm risks are evaluated by comparing
the estimated aggregate food, water, and
residential exposure to the POD to
ensure that the MOE called for by the
product of all applicable UFs is not
exceeded.
1. Acute risk. Using the exposure
assumptions discussed in this unit for
acute exposure, the acute dietary
exposure from food and water to
cyprodinil will occupy 4% of the aPAD
for females 13–49 years old, the only
population group of concern.
2. Chronic risk. Using the exposure
assumptions described in this unit for
chronic exposure, EPA has concluded
that chronic exposure to cyprodinil
from food and water will utilize 67% of
the cPAD for children 1–2 years old, the
population group receiving the greatest
exposure. There are no residential uses
for cyprodinil.
3. Short-term risk. Short-term
aggregate exposure takes into account
short-term residential exposure plus
chronic exposure to food and water
(considered to be a background
exposure level).
Cyprodinil is not registered for any
use patterns that would result in
residential exposure. Therefore, the
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short-term aggregate risk is the sum of
the risk from exposure to cyprodinil
through food and water and will not be
greater than the chronic aggregate risk.
4. Intermediate-term risk.
Intermediate-term aggregate exposure
takes into account intermediate-term
residential exposure plus chronic
exposure to food and water (considered
to be a background exposure level).
Cyprodinil is not registered for any
use patterns that would result in
intermediate-term residential exposure.
Therefore, the intermediate-term
aggregate risk is the sum of the risk from
exposure to cyprodinil through food and
water, which has already been
addressed, and will not be greater than
the chronic aggregate risk.
5. Aggregate cancer risk for U.S.
population. Based on the lack of
evidence of carcinogenicity in mice and
rats at doses that were judged to be
adequate to assess the carcinogenic
potential, cyprodinil was classified as
‘‘not likely to be carcinogenic to
humans.’’ Therefore, cyprodinil is not
expected to pose a cancer risk to
humans.
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, or to infants and children
from aggregate exposure to cyprodinil
residues.
IV. Other Considerations
A. Analytical Enforcement Methodology
Adequate enforcement methodology
(high performance liquid
chromatography with ultraviolet
detector (HPLC/UV)) is available to
enforce the tolerance expression on
plant commodities. In addition, a high
performance liquid chromatography
with mass spectrometry (HPLC/MS)
method (Method No. GRM010.01A) is
available for determining residues of
cyprodinil and its metabolite CGA–
304075 (free+conjugated) in livestock
commodities. These methods 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
Canadian or Mexican MRLs for
cyprodinil on any of the plant
commodities of interest in these
petitions. There are Codex MRLs for
tomato, bulb onion, cucurbit, and
summer squash. Tomato has a proposed
tolerance of 0.45 ppm and a Codex MRL
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50551
of 0.5 ppm, therefore no change in the
tolerance is necessary for harmonization
purposes. The Codex MRLs for bulb
onion at 0.3 ppm (vs 4.0 ppm for green
onion and 0.60 ppm for dry bulb onion),
cucurbit at 0.2 ppm (vs 0.70 ppm for
cucurbit vegetables), and summer
squash at 0.2 ppm (vs 1.0 ppm for head
and stem Brassica, 5A) were established
based on application levels from 0.21 to
0.26x the domestic rate. Harmonization
of U.S. tolerances on these commodities
is not possible at this time.
Codex MRLs have been established
for livestock commodities, and these
MRLs are set at the method LOQ. For
both the Canadian and Codex MRLs, the
regulated residues include cyprodinil
per se. As the U.S. definition for
cyprodinil residues in livestock
commodities is different than those
established for Canada and Codex,
harmonization of U.S. tolerances on
livestock commodities is not possible at
this time.
C. Response to Comments
EPA received one comment to the
Notice of Filing that had a general
objection to ‘‘this product being allowed
on food.’’ The comment contained no
scientific data or other substantive
evidence to rebut this conclusion or the
Agency’s finding that there is a
reasonable certainty that no harm will
result from aggregate exposure to
cyprodinil from the establishment of
these tolerances. The Agency has
received these same or similar
comments from this commenter on
numerous previous occasions. Refer to
Federal Register 70 FR 37686 (June 30,
2005), 70 FR 1354 (January 7, 2005), and
69 FR 63096 (October 29, 2004) for the
Agency’s previous responses to these
objections.
D. Revisions to Petitioned-For
Tolerances
Based upon review of the data
supporting the petitions, EPA
determined that separate tolerances are
needed for fresh parsley at 35 ppm;
dried parsley at 170 ppm; citrus, dry
pulp at 8.0 ppm; citrus, oil at 340 ppm;
and meat byproducts of cattle, goats,
horses and sheep at 0.02 ppm. EPA is
establishing those tolerances in this
action. In addition, EPA revised the
tolerances for tomato from 0.40 ppm to
0.45 ppm; tomatillo from 0.40 ppm to
0.45 ppm; herb subgroup 19A fresh from
25 ppm to 3 ppm and re-naming herb
subgroup 19A fresh, except parsley;
herb subgroup 19A dried from 170 ppm
to 15 ppm and re-naming herb subgroup
19A, dried, except parsley; leaves of
root and tuber vegetables from 9.0 ppm
to 10 ppm; root vegetables, except sugar
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beet subgroup from 0.60 ppm to 0.75
ppm; cucurbits from 0.40 to 0.70 ppm.
EPA revised these tolerance levels based
on analyses of the residue field trial data
using the Agency’s Tolerance
Spreadsheet in accordance with the
Agency’s Guidance for Setting Pesticide
Tolerances Based on Field Trial Data.
V. Conclusion
Therefore, tolerances are established
for residues of cyprodinil, 4cyclopropyl-6-methyl-N-phenyl-2pyrimidinamine, in or on the food
commodities tomato at 0.45 ppm;
tomatillo at 0.45 ppm; tomato, paste at
1.0 ppm; avocado at 1.2 ppm; sapote,
black at 1.2 ppm; canistel at 1.2 ppm;
sapote, mamey at 1.2 ppm; mango at 1.2
ppm; papaya at 1.2 ppm; sapodilla at 1.2
ppm; star apple at 1.2 ppm; parsley,
leaves at 35 ppm; parsley, dried leaves
at 170 ppm; vegetable, leaves of root and
tuber, group 2 at 10 ppm; vegetable,
root, except sugarbeet, subgroup 1B at
0.75 ppm; lemon at 0.60 ppm; lime at
0.60 ppm; citrus, dried pulp at 8.0 ppm;
citrus, oil at 340 ppm; kiwifruit at 1.8
ppm; onion, bulb at 0.60 ppm; onion,
green at 4.0 ppm; strawberry at 5.0 ppm;
vegetable, cucurbit, group 9 at 0.70
ppm; and meat byproducts of cattle,
goats, horses and sheep at 0.02 ppm.
Also, the following entries in the table
in paragraph (a)(1) are changed to read
as follows: ‘‘herb subgroup 19A, fresh’’
is amended to ‘‘herb subgroup 19A,
fresh, except parsley’’; ‘‘herb subgroup
19A, dried’’ is amended to ‘‘herb
subgroup 19 A, dried, except parsley’’..
Further, the following entry is
removed from the table in paragraph
(a)(1): ‘‘Carrot’’ because of the
establishment of the vegetable, root
tolerance by this action.
And lastly, the following entries are
removed from the table in paragraph
(a)(2): ‘‘Onion, bulb’’ ‘‘onion, green’’,
and ‘‘strawberry’’ because permanent
tolerances are being established by this
action.
sroberts on PROD1PC70 with RULES
VI. Statutory and Executive Order
Reviews
This final rule establishes tolerances
under section 408(d) of FFDCA in
response to a petition submitted to the
Agency. The Office of Management and
Budget (OMB) has exempted these types
of actions from review under Executive
Order 12866, entitled Regulatory
Planning and Review (58 FR 51735,
October 4, 1993). Because this final rule
VerDate Aug<31>2005
16:50 Aug 26, 2008
Jkt 214001
has been exempted from review under
Executive Order 12866, this final 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) or Executive Order 13045,
entitled Protection of Children from
Environmental Health Risks and Safety
Risks (62 FR 19885, April 23, 1997).
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., 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).
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.
This final rule directly regulates
growers, food processors, food handlers,
and food retailers, not States or tribes,
nor does this action alter the
relationships or distribution of power
and responsibilities established by
Congress in the preemption provisions
of section 408(n)(4) of FFDCA. As such,
the Agency has determined that this
action will not have a substantial direct
effect on States or tribal governments,
on the relationship between the national
government and the States or tribal
governments, or on the distribution of
power and responsibilities among the
various levels of government or between
the Federal Government and Indian
tribes. Thus, the Agency has determined
that Executive Order 13132, entitled
Federalism (64 FR 43255, August 10,
1999) and Executive Order 13175,
entitled Consultation and Coordination
with Indian Tribal Governments (65 FR
67249, November 9, 2000) do not apply
to this final rule. In addition, this final
rule does not 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).
This action does not involve any
technical standards that would require
Agency consideration of voluntary
consensus standards pursuant to section
PO 00000
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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).
VII. Congressional Review Act
The Congressional Review Act, 5
U.S.C. 801 et seq., generally provides
that before a rule may take effect, the
agency promulgating the rule must
submit a rule report to each House of
the Congress and to the Comptroller
General of the United States. EPA will
submit a report containing this rule and
other required information to the U.S.
Senate, the U.S. House of
Representatives, and the Comptroller
General of the United States prior to
publication of this final rule in the
Federal Register. This final rule is not
a ‘‘major rule’’ as defined by 5 U.S.C.
804(2).
List of Subjects in 40 CFR Part 180
Environmental protection,
Administrative practice and procedure,
Agricultural commodities, Pesticides
and pests, Reporting and recordkeeping
requirements.
Dated: August 15, 2008.
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 180.532 is amended as
follows:
i. Paragraph (a)(2) is removed.
ii. Paragraph (a)(1) is redesignated as
paragraph (a).
iii. Newly designated paragraph (a) is
amended in the table by removing the
commodity ‘‘Carrot’’; by revising the
commodities ‘‘Herb subgroup 19A,
dried’’ and ‘‘Herb subgroup 19A, fresh’’
to read ‘‘Herb, subgroup 19A, dried,
except parsley’’ and ‘‘Herb, subgroup
19A, fresh, except parsley’’ respectively;
and by alphabetically adding
commodities.
The amendments read as follows:
I
§ 180.532 Cyprodinil; tolerances for
residues.
(a) General. * * *
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Commodity
Parts per million
*
*
*
*
*
Avocado ...............................................................................................................................................................................
*
*
*
*
*
Canistel ................................................................................................................................................................................
*
*
*
*
*
Cattle, meat byproducts .......................................................................................................................................................
Citrus, dried pulp .................................................................................................................................................................
Citrus, oil ..............................................................................................................................................................................
*
*
*
*
*
Goat, meat byproducts ........................................................................................................................................................
*
*
*
*
*
Horse, meat byproducts ......................................................................................................................................................
*
*
*
*
*
Kiwifruit ................................................................................................................................................................................
*
*
*
*
*
Lemon ..................................................................................................................................................................................
Lime .....................................................................................................................................................................................
*
*
*
*
*
Mango ..................................................................................................................................................................................
Onion, bulb ..........................................................................................................................................................................
Onion, green ........................................................................................................................................................................
Papaya .................................................................................................................................................................................
Parsley, dried leaves ...........................................................................................................................................................
Parsley, leaves ....................................................................................................................................................................
*
*
*
*
*
Sapodilla ..............................................................................................................................................................................
Sapote, black .......................................................................................................................................................................
Sapote, mamey ....................................................................................................................................................................
Sheep, meat byproducts ......................................................................................................................................................
*
*
*
*
*
Star apple ............................................................................................................................................................................
Strawberry ............................................................................................................................................................................
Tomatillo ..............................................................................................................................................................................
Tomato .................................................................................................................................................................................
Tomato, paste ......................................................................................................................................................................
*
*
*
*
*
Vegetable, cucurbit, group 9 ...............................................................................................................................................
Vegetable, leaves of root and tuber, group 2 .....................................................................................................................
Vegetable, root, except sugarbeet, subgroup 1B ................................................................................................................
*
*
*
*
*
*
*
*
*
*
[FR Doc. E8–19747 Filed 8–26–08; 8:45 am]
BILLING CODE 6560–50–S
ENVIRONMENTAL PROTECTION
AGENCY
40 CFR Part 180
[EPA–HQ–OPP–2007–1020; FRL–8378–5]
Bacillus subtilis GB03; Exemption
from the Requirement of a Tolerance
Environmental Protection
Agency (EPA).
ACTION: Final rule.
sroberts on PROD1PC70 with RULES
SUMMARY: This regulation establishes an
exemption from the requirement of a
tolerance for residues of the microbial
pesticide Bacillus subtilis GB03 in or on
all raw agricultural commodities when
applied in accordance with good
agricultural practices. Growth Products
Ltd. submitted a petition to EPA under
the Federal Food, Drug, and Cosmetic
Act (FFDCA), as amended by the Food
VerDate Aug<31>2005
16:50 Aug 26, 2008
Jkt 214001
Quality Protection Act of 1996 (FQPA),
requesting an amendment of the existing
exemption from the requirement of a
tolerance to cover use in or on all
agricultural commodities and remove
the regulatory text specifying ‘‘when
applied as a seed treatment.’’ This
regulation eliminates the need to
establish a maximum permissible level
for residues of Bacillus subtilis GB03 in
or on all raw agricultural commodities.
This regulation is effective
August 27, 2008. Objections and
requests for hearings must be received
on or before October 27, 2008, and must
be filed in accordance with the
instructions provided in 40 CFR part
178 (see also Unit I.C. of the
SUPPLEMENTARY INFORMATION).
DATES:
AGENCY:
EPA has established a
docket for this action under docket
identification (ID) number EPA–HQ–
OPP–2007–1020. To access the
electronic docket, go to https://
www.regulations.gov, select ‘‘Advanced
Search,’’ then ‘‘Docket Search.’’ Insert
the docket identification (ID) number
ADDRESSES:
PO 00000
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1.2
1.2
0.02
8.0
340
0.02
0.02
1.8
0.60
0.60
1.2
0.60
4.0
1.2
170
35
1.2
1.2
1.2
0.02
1.2
5.0
0.45
0.45
1.0
0.70
10
0.75
where indicated and select the
‘‘Submit’’ button. Follow the
instructions on the regulations.gov
website to view the docket index or
access available documents. All
documents in the docket are listed in
the docket index available in
regulations.gov. Although listed in the
index, some information is not publicly
available, e.g., Confidential Business
Information (CBI) or other information
whose disclosure is restricted by statute.
Certain other material, such as
copyrighted material, is not placed on
the Internet and will be publicly
available only in hard copy form.
Publicly available docket materials are
available in the electronic docket at
https://www.regulations.gov, or, if only
available in hard copy, at the OPP
Regulatory Public Docket in Rm. S–
4400, One Potomac Yard (South Bldg.),
2777 S. Crystal Dr., Arlington, VA. The
Docket Facility is open from 8:30 a.m.
to 4 p.m., Monday through Friday,
excluding legal holidays. The Docket
Facility telephone number is (703) 305–
5805.
E:\FR\FM\27AUR1.SGM
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Agencies
[Federal Register Volume 73, Number 167 (Wednesday, August 27, 2008)]
[Rules and Regulations]
[Pages 50548-50553]
From the Federal Register Online via the Government Printing Office [www.gpo.gov]
[FR Doc No: E8-19747]
=======================================================================
-----------------------------------------------------------------------
ENVIRONMENTAL PROTECTION AGENCY
40 CFR Part 180
[EPA-HQ-OPP-2007-1069; FRL-8377-8]
Cyprodinil; Pesticide Tolerances
AGENCY: Environmental Protection Agency (EPA).
ACTION: Final rule.
-----------------------------------------------------------------------
SUMMARY: This regulation establishes tolerances for residues of
cyprodinil, 4-cyclopropyl-6-methyl-N-phenyl-2-pyrimidinamine, in or on
tomato; tomatillo; tomato, paste; avocado; sapote, black; canistel;
sapote, mamey; mango; papaya; sapodilla; star apple; parsley, leaves;
parsley, dried leaves; vegetable, leaves of root and tuber, group 2;
vegetable, root, except sugarbeet, subgroup 1B; lemon; lime; citrus,
dried pulp; citrus, oil; kiwifruit; onion, bulb; onion, green;
strawberries; vegetable, cucurbit, group 9; and meat byproducts of
cattle, goats, horses and sheep. Interregional Research Project Number
4 (IR-4) requested these tolerances under the Federal Food, Drug, and
Cosmetic Act (FFDCA).
DATES: This regulation is effective August 27, 2008. Objections and
requests for hearings must be received on or before October 27, 2008,
and must be filed in accordance with the instructions provided in 40
CFR part 178 (see also Unit I.C. of the SUPPLEMENTARY INFORMATION).
ADDRESSES: EPA has established a docket for this action under docket
identification (ID) number EPA-HQ-OPP-2007-1069. To access the
electronic docket, go to https://www.regulations.gov, select ``Advanced
Search,'' then ``Docket Search.'' Insert the docket ID number where
indicated and select the ``Submit'' button. Follow the instructions on
the regulations.gov website to view the docket index or access
available documents. All documents in the docket are listed in the
docket index available in regulations.gov. Although listed in the
index, some information is not publicly available, e.g., Confidential
Business Information (CBI) or other information whose disclosure is
restricted by statute. Certain other material, such as copyrighted
material, is not placed on the Internet and will be publicly available
only in hard copy form. Publicly available docket materials are
available in the electronic docket at https://www.regulations.gov, or,
if only available in hard copy, at the OPP Regulatory Public Docket in
Rm. S-4400, One Potomac Yard (South Bldg.), 2777 S. Crystal Dr.,
Arlington, VA. The Docket Facility is open from 8:30 a.m. to 4 p.m.,
Monday through Friday, excluding legal holidays. The Docket Facility
telephone number is (703) 305-5805.
FOR FURTHER INFORMATION CONTACT: Barbara Madden, Registration Division
(7505P), Office of Pesticide Programs, Environmental Protection Agency,
1200 Pennsylvania Ave., NW., Washington, DC 20460-0001; telephone
number: (703) 305-6463; e-mail address: madden.barbara@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 those
engaged in the following activities:
Crop production (NAICS code 111).
Animal production (NAICS code 112).
Food manufacturing (NAICS code 311).
Pesticide manufacturing (NAICS code 32532).
This listing is not intended to be exhaustive, but rather to
provide 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 EPA's tolerance regulations at
40 CFR part 180 through the Government Printing Office's pilot e-CFR
site at https://www.gpoaccess.gov/ecfr.
C. Can I File an Objection or Hearing Request?
Under section 408(g) of FFDCA, any person may file an objection to
any aspect of this regulation and may also request a hearing on those
objections. You must file your objection or request a hearing on this
regulation in accordance with the instructions provided in 40 CFR part
178. To ensure proper receipt by EPA, you must identify docket ID
number EPA-HQ-OPP-2007-1069 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 as required by 40 CFR part 178 on or
before October 27, 2008.
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 this copy, identified by docket ID number
EPA-HQ-OPP-2007-1069, by one of the following methods:
Federal eRulemaking Portal: https://www.regulations.gov.
Follow the on-line instructions for submitting comments.
Mail: Office of Pesticide Programs (OPP) Regulatory Public
Docket (7502P), Environmental Protection Agency, 1200 Pennsylvania
Ave., NW., Washington, DC 20460-0001.
Delivery: OPP Regulatory Public Docket (7502P),
Environmental Protection Agency, Rm. S-4400, One Potomac Yard (South
Bldg.), 2777 S. Crystal Dr., Arlington, VA. Deliveries are only
accepted during the Docket's normal hours of operation (8:30 a.m. to 4
p.m., Monday through Friday, excluding legal holidays). Special
arrangements should be made for deliveries of boxed information. The
Docket Facility telephone number is (703) 305-5805.
II. Petition for Tolerance
In the Federal Register of January 23, 2008 (73 FR 3964) (FRL-8345-
7), EPA issued a notice pursuant to section 408(d)(3) of FFDCA, 21
U.S.C. 346a(d)(3), announcing the filing of a pesticide petition (PP
7E7235) by Interregional, Research Project Number 4 (IR-4), 500 College
Road East, Suite 201W, Princeton, NJ 08540. The petition requested that
40 CFR 180.532 be
[[Page 50549]]
amended by establishing tolerances for residues of the fungicide
cyprodinil, 4-cyclopropyl-6-methyl-N-phenyl-2-pyrimidinamine, in or on
the food commodities tomato at 0.40 parts per million (ppm); tomatillo
at 0.40 ppm; tomato, paste at 1.0 ppm; avocado at 1.2 ppm; sapote,
black at 1.2 ppm; canistel at 1.2 ppm; sapote, mamey at 1.2 ppm; mango
at 1.2 ppm; papaya at 1.2 ppm; sapodilla at 1.2 ppm; star apple at 1.2
ppm; herbs subgroup19A, fresh at 25 ppm; herbs subgroup 19A, dried at
170 ppm; vegetable, root and tuber, group, leaves at 9.0 ppm;
vegetable, root, except sugarbeet subgroup at 0.60 ppm; lemon at 0.6
ppm; lime at 0.6 ppm; kiwifruit at 1.8 ppm; onion, dry bulb at 0.50
ppm; onion, green at 1.2 ppm; strawberry at 7.0 ppm; and cucurbits at
0.40 ppm. That notice referenced a summary of the petition prepared by
IR-4, the registrant, which is available to the public in the docket,
https://www.regulations.gov. Comments were received on the notice of
filing. EPA's response to these comments is discussed in Unit IV.C.
Based upon review of the data supporting the petition, EPA is
revising some of the items as proposed in this Unit. The reason for
these changes is explained in Unit IV.D.
III. Aggregate Risk Assessment and Determination of Safety
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. . .
.''
Consistent with section 408(b)(2)(D) of FFDCA, and the factors
specified in section 408(b)(2)(D) of FFDCA, EPA has reviewed the
available scientific data and other relevant information in support of
this action. EPA has sufficient data to assess the hazards of and to
make a determination on aggregate exposure for the petitioned-for
tolerances for residues of cyprodinil, 4-cyclopropyl-6-methyl-N-phenyl-
2-pyrimidinamine on tomato; tomatillo; tomato, paste; avocado; sapote,
black; canistel; sapote, mamey; mango; papaya; sapodilla; star apple;
parsley, leaves; parsley, dried leaves; vegetable, leaves of root and
tuber, group 2; vegetable, root, except sugarbeet, subgroup 1B; lemon;
lime; citrus, dried pulp; citrus, oil; kiwifruit; onion, bulb; onion,
green; strawberries; vegetable, cucurbit, group 9; and meat byproducts
of cattle, goats, horses and sheep. EPA's assessment of exposures and
risks associated with establishing tolerances 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.
Cyprodinil has low acute toxicity via the oral, dermal, and
inhalation routes. Cyprodinil is mildly irritating to the eyes and
negligibly irritating to the skin. It is a dermal sensitizer. The major
target organs of cyprodinil are the liver in both rats and mice and the
kidney in rats. Liver effects were consistent among male and female
rats and mice in both subchronic and chronic studies and typically
included increased liver weights along with increases in serum clinical
chemistry parameters associated with adverse effects on liver function
(i.e., increased cholesterol and phospholipid levels). Microscopic
lesions in rats and mice included hepatocyte hypertrophy and
hepatocellular necrosis. In the kidneys, adverse effects were
manifested as chronic tubular lesions and chronic kidney inflamation
following subchronic exposure of male rats. Chronically, cyprodinil
caused increased kidney weights and progressive nephropathy in male
rats. Chronic effects in dogs were limited to decreased body-weight
gain, decreased food consumption and decreased food efficiency. Liver
toxicity was not seen in the dog. The hematopoietic system also
appeared to be a target of cyprodinil, causing mild anemia in rats
exposed subchronically. There was no evidence of carcinogenic potential
in either the rat chronic toxicity/carcinogenicity or mouse
carcinogenicity studies and no concern for mutagenicity. There was no
evidence of increased susceptibility in the developmental rat or rabbit
study following in utero exposure or in the 2-generation reproduction
study following prenatal or postnatal exposure. No clinical signs of
toxicity suggestive of neurobehavioral alterations nor evidence of
neuropathological effects were observed in the available oral-toxicity
studies. There was also no evidence of a neurodevelopmental effect in
the rat or rabbit developmental toxicity studies or in the rat 2-
generation reproductive-toxicity study.
Specific information on the studies received and the nature of the
adverse effects caused by cyprodinil as well as the no-observed-
adverse-effect-level (NOAEL) and the lowest-observed-adverse-effect-
level (LOAEL) from the toxicity studies can be found at https://
www.regulations.gov in document Cyprodinil Human Health Risk Assessment
for the uses in/on tomato, avocado, herbs, root vegetables, leaves of
root and tuber vegetables, lemon, lime, cucurbits, kiwifruit, green and
dry bulb onions, and strawberries, page 16 in docket ID number EPA-HQ-
OPP-2007-1069.
B. Toxicological Endpoints
For hazards that have a threshold below which there is no
appreciable risk, a toxicological point of departure (POD) is
identified as the basis for derivation of reference values for risk
assessment. The POD may be defined as the highest dose at which NOAEL
in the toxicology study identified as appropriate for use in risk
assessment. However, if a NOAEL cannot be determined, the lowest dose
at which the LOAEL of concern are identified or a Benchmark Dose (BMD)
approach is sometimes used for risk assessment. Uncertainty/safety
factors (UFs) are used in conjunction with the POD to take into account
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. Safety is assessed for
acute and chronic dietary risks by comparing aggregate food and water
exposure to the pesticide to the acute population adjusted dose (aPAD)
and chronic population adjusted dose (cPAD). The aPAD and cPAD are
calculated by dividing the POD by all applicable UFs. Aggregate short-
term, intermediate-term, and chronic-term risks are evaluated by
comparing food, water, and residential exposure to the POD to ensure
that the margin of exposure (MOE) called for by the product of all
applicable UFs is not exceeded. This latter value is referred to as the
Level of Concern (LOC).
[[Page 50550]]
For non-threshold risks, the Agency assumes that any amount of
exposure will lead to some degree of risk. Thus, the Agency estimates
risk in terms of the probability of an occurrence of the adverse effect
greater than that expected in a lifetime. For more information on the
general principles EPA uses in risk characterization and a complete
description of the risk assessment process, see https://www.epa.gov/
pesticides/factsheets/riskassess.htm.
A summary of the toxicological endpoints for cyprodinil used for
human risk assessment can be found at https://www.regulations.gov in
document Cyprodinil Human Health Risk Assessment for the uses in/on
tomato, avocado, herbs, root vegetables, leaves of root and tuber
vegetables, lemon, lime, cucurbits, kiwifruit, green and dry bulb
onions, and strawberries, page 22 in docket ID number EPA-HQ-OPP-2007-
1069.
C. Exposure Assessment
1. Dietary exposure from food and feed uses. In evaluating dietary
exposure to cyprodinil, EPA considered exposure under the petitioned-
for tolerances as well as all existing cyprodinil tolerances in (40 CFR
180.532). EPA assessed dietary exposures from cyprodinil in food as
follows:
i. Acute exposure. Quantitative acute dietary exposure and risk
assessments are performed for a food-use pesticide, if a toxicological
study has indicated the possibility of an effect of concern occurring
as a result of a 1-day or single exposure.
In estimating acute dietary exposure, EPA used food consumption
information from the United States Department of Agriculture (USDA)
1994-1996 and 1998 Nationwide Continuing Surveys of Food Intake by
Individuals (CSFII). As to residue levels in food, EPA used tolerance-
level residues, DEEM default processing factors and assumed 100 percent
crop treated (PCT) for all existing and proposed commodities.
ii. Chronic exposure. In conducting the chronic dietary exposure
assessment EPA used the food consumption data from the USDA 1994-1996
and 1998 CSFII. As to residue levels in food, EPA used tolerance level
residues, DEEM default processing factors, and assumed 100 PCT for all
existing and proposed commodities.
iii. Cancer An aggregate exposure assessment for the purpose of
assessing cancer risk was not performed because cyprodinil has been
classified as ``not likely to be carcinogenic to humans.''
iv. Anticipated residue and PCT information. EPA did not use
anticipated residue and/or PCT information in the dietary assessment
for cyprodinil. Tolerance level residues and 100 PCT were assumed for
all existing and proposed food commodities.
2. Dietary exposure from drinking water. The Agency used screening
level water exposure models in the dietary exposure analysis and risk
assessment for cyprodinil in drinking water. These simulation models
take into account data on the physical, chemical, and fate/transport
characteristics of cyprodinil. 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.
For surface water the Pesticide Root Zone Model/Exposure Analysis
Modeling System (PRZM/EXAMS) Tier 2 aquatic models were used, and for
ground water, the Tier 1 aquatic model Screening Concentration in
Ground Water (SCI-GROW) was utilized. For the assessment, maximum
application rates and minimum intervals between applications were used.
The Agency has concluded that the transformation product CGA-249287 of
cyprodinil is of potential concern for drinking water sources.
Therefore, estimated drinking water concentrations (EDWCs) of CGA-
249287 were also simulated using the PRZM/EXAMS and SCI-GROW models.
For surface water, this degradate was modeled individually, as opposed
to the use of the total residue approach due to the fact that only one
degradate was modeled and sufficient information was available for the
modeling.
Based on the Tier 2 PRZM/EXAMS and the Tier 1 SCI-GROW models, the
EDWCs of cyprodinil and its transformation product CGA-249287 for acute
exposures are estimated to be 34.56 parts per billion (ppb) for surface
water and 0.108 ppb for ground water. For chronic exposures for non-
cancer assessments the concentrations are estimated to be 20.05 ppb for
surface water and 0.108 ppb for ground water.
Modeled estimates of drinking water concentrations were directly
entered into the dietary exposure model. For acute dietary risk
assessment, the water concentration value of 34.56 ppb was used to
assess the contribution to drinking water.
For chronic dietary risk assessment, the water concentration of
value 20.05 ppb was used to assess the contribution to drinking water.
3. From non-dietary exposure. The term ``residential exposure'' is
used in this document to refer to non-occupational, non-dietary
exposure (e.g., for lawn and garden pest control, indoor pest control,
termiticides, and flea and tick control on pets).
Cyprodinil is not registered for any specific use patterns that
would result in residential exposure.
4. Cumulative effects from substances with a common mechanism of
toxicity. Section 408(b)(2)(D)(v) of FFDCA requires that, when
considering whether 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.''
EPA has not found cyprodinil to share a common mechanism of
toxicity with any other substances, and cyprodinil does not appear to
produce a toxic metabolite produced by other substances. For the
purposes of this tolerance action, therefore, EPA has assumed that
cyprodinil does not have 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 EPA's website at https://
www.epa.gov/pesticides/cumulative.
D. Safety Factor for Infants and Children
1. In general. Section 408(b)(2)(c) of FFDCA provides that EPA
shall apply an additional tenfold (10X) margin of safety (MOS) for
infants and children in the case of threshold effects to account for
prenatal and postnatal toxicity and the completeness of the database on
toxicity and exposure unless EPA determines based on reliable data that
a different MOS will be safe for infants and children. This additional
margin of safety is commonly referred to as the FQPA safety factor
(SF). In applying this provision, EPA either retains the default value
of 10X, or uses a different additional SF when reliable data available
to EPA support the choice of a different factor.
2. Prenatal and postnatal sensitivity. There are no concerns or
residual uncertainties for prenatal and/or postnatal exposure.
3. Conclusion. EPA has determined that reliable data show the
safety of infants and children would be adequately protected if the
FQPA SF were reduced to 1X. That decision is based on the following
findings:
i. The toxicity database for cyprodinil is complete.
ii. There is no indication that cyprodinil is a neurotoxic chemical
and
[[Page 50551]]
there is no need for a developmental neurotoxicity study or additional
UFs to account for neurotoxicity.
iii. There is no evidence that cyprodinil results in increased
susceptibility in in utero rats or rabbits in the prenatal
developmental studies or in young rats in the 2-generation reproduction
study.
iv. There are no residual uncertainties identified in the exposure
databases. EPA made conservative (protective) assumptions in the ground
water and surface water modeling used to assess exposure to cyprodinil
in drinking water. EPA used similarly conservative assumptions to
assess postapplication exposure of children as well as incidental oral
exposure of toddlers. These assessments will not underestimate the
exposure and risks posed by cyprodinil.
E. Aggregate Risks and Determination of Safety
EPA determines whether acute and chronic pesticide exposures are
safe by comparing aggregate exposure estimates to the aPAD and cPAD.
The aPAD and cPAD represent the highest safe exposures, taking into
account all appropriate SFs. EPA calculates the aPAD and cPAD by
dividing the POD by all applicable UFs. For linear cancer risks, EPA
calculates the probability of additional cancer cases given the
estimated aggregate exposure. Short-term, intermediate-term, and
chronic-term risks are evaluated by comparing the estimated aggregate
food, water, and residential exposure to the POD to ensure that the MOE
called for by the product of all applicable UFs is not exceeded.
1. Acute risk. Using the exposure assumptions discussed in this
unit for acute exposure, the acute dietary exposure from food and water
to cyprodinil will occupy 4% of the aPAD for females 13-49 years old,
the only population group of concern.
2. Chronic risk. Using the exposure assumptions described in this
unit for chronic exposure, EPA has concluded that chronic exposure to
cyprodinil from food and water will utilize 67% of the cPAD for
children 1-2 years old, the population group receiving the greatest
exposure. There are no residential uses for cyprodinil.
3. Short-term risk. Short-term aggregate exposure takes into
account short-term residential exposure plus chronic exposure to food
and water (considered to be a background exposure level).
Cyprodinil is not registered for any use patterns that would result
in residential exposure. Therefore, the short-term aggregate risk is
the sum of the risk from exposure to cyprodinil through food and water
and will not be greater than the chronic aggregate risk.
4. Intermediate-term risk. Intermediate-term aggregate exposure
takes into account intermediate-term residential exposure plus chronic
exposure to food and water (considered to be a background exposure
level).
Cyprodinil is not registered for any use patterns that would result
in intermediate-term residential exposure. Therefore, the intermediate-
term aggregate risk is the sum of the risk from exposure to cyprodinil
through food and water, which has already been addressed, and will not
be greater than the chronic aggregate risk.
5. Aggregate cancer risk for U.S. population. Based on the lack of
evidence of carcinogenicity in mice and rats at doses that were judged
to be adequate to assess the carcinogenic potential, cyprodinil was
classified as ``not likely to be carcinogenic to humans.'' Therefore,
cyprodinil is not expected to pose a cancer risk to humans.
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, or to infants and children from aggregate
exposure to cyprodinil residues.
IV. Other Considerations
A. Analytical Enforcement Methodology
Adequate enforcement methodology (high performance liquid
chromatography with ultraviolet detector (HPLC/UV)) is available to
enforce the tolerance expression on plant commodities. In addition, a
high performance liquid chromatography with mass spectrometry (HPLC/MS)
method (Method No. GRM010.01A) is available for determining residues of
cyprodinil and its metabolite CGA-304075 (free+conjugated) in livestock
commodities. These methods 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 Canadian or Mexican MRLs for
cyprodinil on any of the plant commodities of interest in these
petitions. There are Codex MRLs for tomato, bulb onion, cucurbit, and
summer squash. Tomato has a proposed tolerance of 0.45 ppm and a Codex
MRL of 0.5 ppm, therefore no change in the tolerance is necessary for
harmonization purposes. The Codex MRLs for bulb onion at 0.3 ppm (vs
4.0 ppm for green onion and 0.60 ppm for dry bulb onion), cucurbit at
0.2 ppm (vs 0.70 ppm for cucurbit vegetables), and summer squash at 0.2
ppm (vs 1.0 ppm for head and stem Brassica, 5A) were established based
on application levels from 0.21 to 0.26x the domestic rate.
Harmonization of U.S. tolerances on these commodities is not possible
at this time.
Codex MRLs have been established for livestock commodities, and
these MRLs are set at the method LOQ. For both the Canadian and Codex
MRLs, the regulated residues include cyprodinil per se. As the U.S.
definition for cyprodinil residues in livestock commodities is
different than those established for Canada and Codex, harmonization of
U.S. tolerances on livestock commodities is not possible at this time.
C. Response to Comments
EPA received one comment to the Notice of Filing that had a general
objection to ``this product being allowed on food.'' The comment
contained no scientific data or other substantive evidence to rebut
this conclusion or the Agency's finding that there is a reasonable
certainty that no harm will result from aggregate exposure to
cyprodinil from the establishment of these tolerances. The Agency has
received these same or similar comments from this commenter on numerous
previous occasions. Refer to Federal Register 70 FR 37686 (June 30,
2005), 70 FR 1354 (January 7, 2005), and 69 FR 63096 (October 29, 2004)
for the Agency's previous responses to these objections.
D. Revisions to Petitioned-For Tolerances
Based upon review of the data supporting the petitions, EPA
determined that separate tolerances are needed for fresh parsley at 35
ppm; dried parsley at 170 ppm; citrus, dry pulp at 8.0 ppm; citrus, oil
at 340 ppm; and meat byproducts of cattle, goats, horses and sheep at
0.02 ppm. EPA is establishing those tolerances in this action. In
addition, EPA revised the tolerances for tomato from 0.40 ppm to 0.45
ppm; tomatillo from 0.40 ppm to 0.45 ppm; herb subgroup 19A fresh from
25 ppm to 3 ppm and re-naming herb subgroup 19A fresh, except parsley;
herb subgroup 19A dried from 170 ppm to 15 ppm and re-naming herb
subgroup 19A, dried, except parsley; leaves of root and tuber
vegetables from 9.0 ppm to 10 ppm; root vegetables, except sugar
[[Page 50552]]
beet subgroup from 0.60 ppm to 0.75 ppm; cucurbits from 0.40 to 0.70
ppm. EPA revised these tolerance levels based on analyses of the
residue field trial data using the Agency's Tolerance Spreadsheet in
accordance with the Agency's Guidance for Setting Pesticide Tolerances
Based on Field Trial Data.
V. Conclusion
Therefore, tolerances are established for residues of cyprodinil,
4-cyclopropyl-6-methyl-N-phenyl-2-pyrimidinamine, in or on the food
commodities tomato at 0.45 ppm; tomatillo at 0.45 ppm; tomato, paste at
1.0 ppm; avocado at 1.2 ppm; sapote, black at 1.2 ppm; canistel at 1.2
ppm; sapote, mamey at 1.2 ppm; mango at 1.2 ppm; papaya at 1.2 ppm;
sapodilla at 1.2 ppm; star apple at 1.2 ppm; parsley, leaves at 35 ppm;
parsley, dried leaves at 170 ppm; vegetable, leaves of root and tuber,
group 2 at 10 ppm; vegetable, root, except sugarbeet, subgroup 1B at
0.75 ppm; lemon at 0.60 ppm; lime at 0.60 ppm; citrus, dried pulp at
8.0 ppm; citrus, oil at 340 ppm; kiwifruit at 1.8 ppm; onion, bulb at
0.60 ppm; onion, green at 4.0 ppm; strawberry at 5.0 ppm; vegetable,
cucurbit, group 9 at 0.70 ppm; and meat byproducts of cattle, goats,
horses and sheep at 0.02 ppm.
Also, the following entries in the table in paragraph (a)(1) are
changed to read as follows: ``herb subgroup 19A, fresh'' is amended to
``herb subgroup 19A, fresh, except parsley''; ``herb subgroup 19A,
dried'' is amended to ``herb subgroup 19 A, dried, except parsley''..
Further, the following entry is removed from the table in paragraph
(a)(1): ``Carrot'' because of the establishment of the vegetable, root
tolerance by this action.
And lastly, the following entries are removed from the table in
paragraph (a)(2): ``Onion, bulb'' ``onion, green'', and ``strawberry''
because permanent tolerances are being established by this action.
VI. Statutory and Executive Order Reviews
This final rule establishes tolerances under section 408(d) of
FFDCA in response to a petition submitted to the Agency. The Office of
Management and Budget (OMB) has exempted these types of actions from
review under Executive Order 12866, entitled Regulatory Planning and
Review (58 FR 51735, October 4, 1993). Because this final rule has been
exempted from review under Executive Order 12866, this final 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) or Executive Order 13045, entitled Protection of
Children from Environmental Health Risks and Safety Risks (62 FR 19885,
April 23, 1997). 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., 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).
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.
This final rule directly regulates growers, food processors, food
handlers, and food retailers, not States or tribes, nor does this
action alter the relationships or distribution of power and
responsibilities established by Congress in the preemption provisions
of section 408(n)(4) of FFDCA. As such, the Agency has determined that
this action will not have a substantial direct effect on States or
tribal governments, on the relationship between the national government
and the States or tribal governments, or on the distribution of power
and responsibilities among the various levels of government or between
the Federal Government and Indian tribes. Thus, the Agency has
determined that Executive Order 13132, entitled Federalism (64 FR
43255, August 10, 1999) and Executive Order 13175, entitled
Consultation and Coordination with Indian Tribal Governments (65 FR
67249, November 9, 2000) do not apply to this final rule. In addition,
this final rule does not 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).
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).
VII. Congressional Review Act
The Congressional Review Act, 5 U.S.C. 801 et seq., generally
provides that before a rule may take effect, the agency promulgating
the rule must submit a rule report to each House of the Congress and to
the Comptroller General of the United States. EPA will submit a report
containing this rule and other required information to the U.S. Senate,
the U.S. House of Representatives, and the Comptroller General of the
United States prior to publication of this final rule in the Federal
Register. This final rule is not a ``major rule'' as defined by 5
U.S.C. 804(2).
List of Subjects in 40 CFR Part 180
Environmental protection, Administrative practice and procedure,
Agricultural commodities, Pesticides and pests, Reporting and
recordkeeping requirements.
Dated: August 15, 2008.
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 180.532 is amended as follows:
i. Paragraph (a)(2) is removed.
ii. Paragraph (a)(1) is redesignated as paragraph (a).
iii. Newly designated paragraph (a) is amended in the table by
removing the commodity ``Carrot''; by revising the commodities ``Herb
subgroup 19A, dried'' and ``Herb subgroup 19A, fresh'' to read ``Herb,
subgroup 19A, dried, except parsley'' and ``Herb, subgroup 19A, fresh,
except parsley'' respectively; and by alphabetically adding
commodities.
The amendments read as follows:
Sec. 180.532 Cyprodinil; tolerances for residues.
(a) General. * * *
[[Page 50553]]
------------------------------------------------------------------------
Commodity Parts per million
------------------------------------------------------------------------
* * * * *
Avocado........................................ 1.2
* * * * *
Canistel....................................... 1.2
* * * * *
Cattle, meat byproducts........................ 0.02
Citrus, dried pulp............................. 8.0
Citrus, oil.................................... 340
* * * * *
Goat, meat byproducts.......................... 0.02
* * * * *
Horse, meat byproducts......................... 0.02
* * * * *
Kiwifruit...................................... 1.8
* * * * *
Lemon.......................................... 0.60
Lime........................................... 0.60
* * * * *
Mango.......................................... 1.2
Onion, bulb.................................... 0.60
Onion, green................................... 4.0
Papaya......................................... 1.2
Parsley, dried leaves.......................... 170
Parsley, leaves................................ 35
* * * * *
Sapodilla...................................... 1.2
Sapote, black.................................. 1.2
Sapote, mamey.................................. 1.2
Sheep, meat byproducts......................... 0.02
* * * * *
Star apple..................................... 1.2
Strawberry..................................... 5.0
Tomatillo...................................... 0.45
Tomato......................................... 0.45
Tomato, paste.................................. 1.0
* * * * *
Vegetable, cucurbit, group 9................... 0.70
Vegetable, leaves of root and tuber, group 2... 10
Vegetable, root, except sugarbeet, subgroup 1B. 0.75
* * * * *
------------------------------------------------------------------------
* * * * *
[FR Doc. E8-19747 Filed 8-26-08; 8:45 am]
BILLING CODE 6560-50-S