Spinosad; Pesticide Tolerance, 68534-68541 [E7-23579]
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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.
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 6, 2000) do not apply
to this rule. In addition, This 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).
adding the following commodities to the
table in paragraph (a) to read as follows:
VII. Congressional Review Act
Spinosad; Pesticide Tolerance
A. Does this Action Apply to Me?
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).
AGENCY:
Environmental Protection
Agency (EPA).
ACTION: Final rule.
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), e.g., agricultural workers;
greenhouse, nursery, and floriculture
workers; farmers.
• Animal production (NAICS code
112), e.g., cattle ranchers and farmers,
dairy cattle farmers, livestock farmers.
• Food manufacturing (NAICS code
311), e.g., agricultural workers; farmers;
greenhouse, nursery, and floriculture
workers; ranchers; pesticide applicators.
• Pesticide manufacturing (NAICS
code 32532), e.g., agricultural workers;
commercial applicators; farmers;
greenhouse, nursery, and floriculture
workers; residential users.
This listing is not intended to be
exhaustive, but rather 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.
List of Subjects in 40 CFR Part 180
Environmental protection,
Administrative practice and procedure,
Agricultural commodities, Pesticides
and pests, Reporting and recordkeeping
requirements.
Dated: November 26, 2007.
Donald R. Stubbs,
Acting 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:
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I
Authority: 21 U.S.C. 321(q), 346a and 371.
2. Section 180.416 is amended by
removing the current tolerance on
‘‘Canola, seed’’ and alphabetically
I
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§180.416 Ethalfluralin; tolerances for
residues.
(a) * * *
Commodity
Parts per million
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Dill, dried leaves .............
Dill, fresh leaves .............
Mustard, seed .................
*
*
*
Potato .............................
Rapeseed, seed .............
*
*
*
*
*
*
*
*
*
0.05
0.05
0.05
*
0.05
0.05
*
*
*
*
[FR Doc. E7–23578 Filed 12–4–07; 8:45 am]
BILLING CODE 6560–50–S
ENVIRONMENTAL PROTECTION
AGENCY
40 CFR Part 180
SUPPLEMENTARY INFORMATION:
[EPA–HQ–OPP–2007–0310; FRL–8339–8]
SUMMARY: This regulation establishes
tolerances for residues of spinosad in or
on spice, subgroup 19B, except black
pepper; pineapple; and pineapple,
process residue. Interregional Research
Project Number 4 (IR-4) requested these
tolerances under the Federal Food,
Drug, and Cosmetic Act (FFDCA).
DATES: This regulation is effective
December 5, 2007. Objections and
requests for hearings must be received
on or before February 4, 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–2007–0310. 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.
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FOR FURTHER INFORMATION CONTACT:
Susan Stanton, Registration Division
(7505P), Office of Pesticide Programs,
Environmental Protection Agency, 1200
Pennsylvania Ave., NW., Washington,
DC 20460–0001; telephone number:
(703) 305–5218; e-mail address:
stanton.susan@epa.gov.
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I. General Information
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B. How Can I Access Electronic Copies
of this Document?
Docket Facility telephone number is
(703) 305–5805.
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.
II. Petition for Tolerance
In the Federal Register of May 9, 2007
(72 FR 26375) (FRL–8128–1), 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 6E7148) by
Interregional Research Project Number 4
(IR–4), 500 College Road East, Suite 201
W, Princeton, NJ 08540–6635. The
petition requested that 40 CFR 180.495
be amended by establishing a tolerance
for residues of the insecticide spinosad,
in or on Spice crop subgroup 19B,
except black pepper at 1.7 parts per
million (ppm); pineapple at 0.02 ppm;
and pineapple, process residue at 0.08
ppm. Spinosad is a fermentation
product of Saccharopolyspora spinosa,
consisting of two related active
ingredients: Spinosyn A (Factor A; CAS
# 131929–60–7) or 2-[(6-deoxy-2,3,4-triO-methyl-a-L-manno-pyranosyl)oxy]13-[[5-(dimethylamino)-tetrahydro-6methyl-2H-pyran-2-yl]oxy]-9-ethyl2,3,3a,5a,5b,6,9,10,11,12,13,14,16a,16btetradecahydro-14-methyl-1H-asIndaceno[3,2-d]oxacyclododecin-7,15dione; and Spinosyn D (Factor D; CAS
# 131929–63–0) or 2-[(6-deoxy-2,3,4-triO-methyl-a-L-manno-pyranosyl)oxy]13-[[5-(dimethyl-amino)-tetrahydro-6methyl-2H-pyran-2-yl]oxy]-9-ethyl2,3,3a,5a,5b,6,9,10,11,12,13,14,16a,16btetradecahydro-4,14-methyl-1H-asIndaceno[3,2-d]oxacyclododecin-7,15dione. That notice referenced a
summary of the petition prepared by
Dow AgroSciences LLC, the registrant,
which is available to the public in the
docket, https://www.regulations.gov.
Comments were received on the notice
of filing from a private citizen. EPA’s
response to these comments is
discussed in Unit IV.C. below.
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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–2007–0310 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 January 4, 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–2007–0310, 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
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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
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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....’’ These provisions
were added to FFDCA by the Food
Quality Protection Act (FQPA) of 1996.
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 spinosad on
spice, subgroup 19B, except black
pepper at 1.7 ppm; pineapple at 0.02
ppm; and Pineapple, process residue at
0.08 ppm. EPA’s assessment of
exposures and risks associated with
establishing the tolerance follows.
A. Toxicological Profile
EPA has evaluated the available
toxicity data and considered its validity,
completeness, and reliability as well as
the relationship of the results of the
studies to human risk. EPA has also
considered available information
concerning the variability of the
sensitivities of major identifiable
subgroups of consumers, including
infants and children. Specific
information on the studies received and
the nature of the adverse effects caused
by spinosad as well as the no-observedadverse-effect-level (NOAEL) and the
lowest-observed-adverse-effect-level
(LOAEL) from the toxicity studies are
discussed in the final rule published in
the Federal Register of September 27,
2002 (67 FR 60923) (FRL–7199–5),
available on-line at https://www.epa.gov/
fedrgstr/EPA-PEST/2002/September/
Day-27/p24484.htm.
B. Toxicological Endpoints
For hazards that have a threshold
below which there is no appreciable
risk, the toxicological level of concern
(LOC) is derived from the highest dose
at which no adverse effects are observed
(the 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 adverse effects of concern are
identified (the LOAEL) is sometimes
used for risk assessment. Uncertainty/
safety factors (UFs) are used in
conjunction with the LOC 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
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human population as well as other
unknowns. Safety is assessed for acute
and chronic risks by comparing
aggregate 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 LOC by all
applicable UFs. Short-term,
intermediate-term, and long-term risks
are evaluated by comparing aggregate
exposure to the LOC to ensure that the
margin of exposure (MOE) called for by
the product of all applicable UFs is not
exceeded.
For non-threshold risks, the Agency
assumes that any amount of exposure
will lead to some degree of risk and
estimates risk in terms of the probability
of occurrence of additional adverse
cases. Generally, cancer risks are
considered non-threshold. 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.
The Agency has concluded that
spinosad should be considered
toxicologically identical to another
pesticide, spinetoram. This conclusion
is based on the following: (1)
Spinetoram and spinosad are large
molecules with nearly identical
structures; and (2) the toxicological
profiles for each are similar (generalized
systemic toxicity) with similar doses
and endpoints chosen for human-health
risk assessment. Spinosad and
spinetoram should be considered
toxicologically identical in the same
manner that metabolites are generally
considered toxicologically identical to
the parent.
Although, as stated above, the doses
and endpoints for spinosad and
spinetoram are similar, they are not
identical due to variations in dosing
levels used in the spinetoram and
spinosad toxicological studies. EPA
compared the spinosad and spinetoram
doses and endpoints for each exposure
scenario and selected the lower of the
two doses for use in human risk
assessment. A summary of the
toxicological endpoints for spinosad
and spinetoram used for human risk
assessment can be found at https://
www.regulations.gov in the document
Spinosad and Spinetoram. HumanHealth Risk Assessment for Application
of Spinosad to Pineapple and the Spice
Subgroup (19B, except black pepper) at
page 11 in docket ID number EPA–HQ–
OPP–2007–0310.
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C. Exposure Assessment
1. Dietary exposure from food and
feed uses. In evaluating dietary
exposure to spinosad, EPA considered
exposure under the petitioned-for
tolerances as well as all existing
spinosad tolerances in 40 CFR 180.495.
Since spinosad and spinetoram are
toxicologically identical, EPA
considered exposure to both in
assessing aggregate risk. EPA assessed
dietary exposures from spinosad and
spinetoram 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. No such effects were
identified in the toxicological studies
for spinosad and spinetoram; therefore,
a quantitative acute dietary exposure
assessment is unnecessary.
ii. Chronic exposure. Spinosad and
spinetoram are registered for use on the
same crops; however, EPA has
concluded it would overstate exposure
to assume that residues of both spinosad
and spinetoram would appear on the
same crop. It is unlikely that both will
be applied to the same crop, since
spinosad and spinetoram control the
same pest species. Rather, EPA
aggregated exposure from residues of
spinosad and spinetoram by assuming
that spinosad residues would be present
in all commodities, because side-by-side
spinosad and spinetoram residue data
indicated that spinetoram residues were
less than or equal to spinosad residues.
EPA assumed that 100 percent of each
food crop commodity would be treated
with spinosad. For feed crop
commodities, EPA summed the
percentage of the crop that would be
treated with spinosad and the
percentage expected to be treated with
spinetoram and used this estimate in
conjunction with spinosad residue data
to develop anticipated residues for
livestock commodities.
The chronic dietary exposure
assessment was conducted using the
Dietary Exposure Evaluation Model Food Consumption Intake Database
(DEEMTM-FCID), Version 2.03, which
incorporates food consumption data
from the United States Department of
Agriculture (USDA) 1994–1996 and
1998 Continuing Surveys of Food
Intakes by Individuals (CSFII). In
addition to the Percent Crop Treated
(PCT) assumptions described above,
EPA, in estimating chronic exposure,
relied upon average field trial residues
for apple, leafy vegetables (except
Brassica), citrus and fruiting vegetables;
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tolerance level residues for the
remaining food crop commodities;
average feed crop residues for feed
commodities from the following crops:
Sweet corn forage, leaves of root and
tuber vegetables and aspirated grain
fractions; average residues from animal
feeding and dermal magnitude of
residue studies; and DEEMTM (Version
7.81) default processing factors for all
commodities, excluding field corn
(meal, starch, flour and oil), grape juice
and wheat (flour and germ), where
processing factors based on the results
of processing studies were assumed.
iii. Cancer. Based on the results of
carcinogenicity studies in rats and mice,
spinosad has been classified as ‘‘Not
likely to be carcinogenic to humans.’’
Preliminary results of a carcinogenicity
study in mice indicate that spinetoram
is not carcinogenic to mice at doses up
to 37.5 milligram/kilogram/day (mg/kg/
day). Based on these preliminary results
and spinetoram’s structural and
toxicological similarity to spinosad,
spinetoram is also considered to be ‘‘Not
likely to be carcinogenic to humans.’’
Consequently, a quantitative cancer
exposure and risk assessment is not
appropriate for spinosad or spinetoram.
iv. Anticipated residue and PCT
information. Section 408(b)(2)(E) of
FFDCA authorizes EPA to use available
data and information on the anticipated
residue levels of pesticide residues in
food and the actual levels of pesticide
residues that have been measured in
food. If EPA relies on such information,
EPA must pursuant to FFDCA section
408(f)(1) require that data be provided 5
years after the tolerance is established,
modified, or left in effect, demonstrating
that the levels in food are not above the
levels anticipated. For the present
action, EPA will issue such data call-ins
as are required by FFDCA section
408(b)(2)(E) and authorized under
FFDCA section 408(f)(1). Data will be
required to be submitted no later than
5 years from the date of issuance of this
tolerance.
Section 408(b)(2)(F) of FFDCA states
that the Agency may use data on the
actual percent of food treated for
assessing chronic dietary risk only if:
a. The data used are reliable and
provide a valid basis to show what
percentage of the food derived from
such crop is likely to contain such
pesticide residue.
b. The exposure estimate does not
underestimate exposure for any
significant subpopulation group.
c. Data are available on pesticide use
and food consumption in a particular
area, the exposure estimate does not
understate exposure for the population
in such area. In addition, the Agency
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must provide for periodic evaluation of
any estimates used. To provide for the
periodic evaluation of the estimate of
PCT as required by FFDCA section
408(b)(2)(F), EPA may require
registrants to submit data on PCT.
The Agency used PCT information as
follows:
One-hundred percent crop treated
was assumed for all food crop
commodities and some feed crop
commodities (aspirated grain fractions,
sugarbeet molasses and cottonseed). For
certain feed crop commodities, the
Agency summed the projected PCT for
spinosad and spinetoram and used the
combined estimates in conjunction with
average field trial residues to calculate
cattle dietary burdens and anticipated
residues of spinosad in meat and milk.
The following combined projected PCT
estimates were used: sweet corn forage
(39%), sorghum grain (5%), soybean
seed meal (5%) and leaves of root and
tuber vegetables (50%).
Spinetoram is a new, recently
registered pesticide. EPA estimates an
upper bound of projected percent crop
treated (PPCT) for a new pesticide use
by assuming that its actual PCT during
the initial 5 years of use on a specific
use site will not exceed the recent PCT
of the market leader (i.e., the one with
the greatest PCT) on that site. EPA calls
this the market leader PPCT estimate. In
this specific case, the new use to be
estimated is the combined use of
spinosad together with that of
spinetoram since the most new use of
spinetoram will likely replace previous
use of spinosad. An average market
leader PCT, based on three recent
surveys of pesticide usage, if available,
is used for chronic risk assessment. The
average market leader PCT may be based
on one or two survey years if three are
not available. Also, with limited
availability of data, the average market
leader PCT may be based on a crosssection of state PCTs. Comparisons are
only made among pesticides of the same
pesticide type (i.e., the leading
insecticide on the use site is selected for
comparison with the new insecticide),
or, for refined estimates, among
pesticides targeting the same pests. The
market leader PCTs used to determine
the average may be each for the same
pesticide or for different pesticides for
any year since the same or different
pesticides may dominate for each year.
Typically, EPA uses U.S. Department of
Agriculture/National Agricultural
Statistics Service (USDA/NASS) as the
source for raw PCT data because it is
publicly available. When a specific use
site is not surveyed by USDA/NASS,
EPA uses other sources including
proprietary data.
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An estimated PPCT, based on the
average PCT of the market leaders, is
appropriate for use in chronic dietary
risk assessment. This method of
estimating PPCT for a new use of a
registered pesticide or a new pesticide
produces a high-end estimate that is
unlikely, in most cases, to be exceeded
during the initial 5 years of actual use.
Predominant factors that bear on
whether the PPCT could be exceeded
may include PCTs of similar
chemistries, pests controlled by
alternatives, pest prevalence in the
market and other factors. All relevant
information currently available for
predominant factors has been
considered for the combined use of
spinetoram and spinosad on each of
these several crops. It is the Agency’s
opinion that it is unlikely that actual
combined PCTs for spinetoram and
spinosad will exceed the corresponding
estimated PPCTs during the next 5
years.
The PPCTs for the combined use of
spinosad and spinetoram for chronic
risk assessment were determined using
the market leader approach for the feed
commodities of sweet corn, grain
sorghum, soybeans and turnip greens.
For turnip greens, the PCTs of market
leaders were averaged over states rather
than years because only 1–year of data
was available.
The Agency believes that the three
conditions listed in this Unit have been
met. With respect to Condition 1, PCT
estimates are derived from Federal and
private market survey data, which are
reliable and have a valid basis. The
Agency is reasonably certain that the
percentage of the food treated is not
likely to be an underestimation. As to
Conditions 2 and 3, regional
consumption information and
consumption information for significant
subpopulations is taken into account
through EPA’s computer-based model
for evaluating the exposure of
significant subpopulations including
several regional groups. Use of this
consumption information in EPA’s risk
assessment process ensures that EPA’s
exposure estimate does not understate
exposure for any significant
subpopulation group and allows the
Agency to be reasonably certain that no
regional population is exposed to
residue levels higher than those
estimated by the Agency. Other than the
data available through national food
consumption surveys, EPA does not
have available information on the
regional consumption of food to which
spinosad may be applied in a particular
area.
2. Dietary exposure from drinking
water. The Agency lacks sufficient
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68537
monitoring data to complete a
comprehensive dietary exposure
analysis and risk assessment for
spinosad in drinking water. Because the
Agency does not have comprehensive
monitoring data, drinking water
concentration estimates are made by
reliance on simulation or modeling
taking into account data on the
environmental fate characteristics of
spinosad. Further information regarding
EPA drinking water models used in
pesticide exposure assessment can be
found at https://www.epa.gov/oppefed1/
models/water/index.htm.
Based on the First Index Reservoir
Screening Tool (FIRST) and Screening
Concentration in Ground Water (SCIGROW) models, the estimated
environmental concentrations (EECs) of
spinosad for acute exposures are
estimated to be 34.5 parts per billion
(ppb) for surface water and 1.1 ppb for
ground water. The EECs for chronic
exposures are estimated to be 10.5 ppb
for surface water and 1.1 ppb for ground
water.
Modeled estimates of drinking water
concentrations were directly entered
into the dietary exposure model. As
explained above, an acute dietary risk
assessment was not conducted for
spinosad and spinetoram. For chronic
dietary risk assessment, the water
concentration of value 10.5 ppb was
used to access the contribution to
drinking water.
3. From non-dietary exposure. The
term ‘‘residential exposure’’ is used in
this document to refer to nonoccupational, non-dietary exposure
(e.g., for lawn and garden pest control,
indoor pest control, termiticides, and
flea and tick control on pets).
The Agency has concluded that
spinosad and spinetoram are
toxicologically equivalent; therefore,
residential exposure to both spinosad
and spinetoram was evaluated.
Spinosad is currently registered for the
following residential non-dietary sites:
Homeowner application to turf grass
and ornamentals to control a variety of
worms, moths, flies, beetles, midges,
thrips, leafminers and fire ants (granular
formulation). Spinetoram is registered
for homeowner applications to gardens,
lawns/ornamentals and turf grass for
control of lepidopterous larvae (worms
or caterpillars), dipterous leafminers,
thrips, sawfly larvae, certain psyllids
and leaf-feeding beetles and red
imported fire ants.
There is potential for residential
handler and post-application exposures
to both spinosad and spinetoram. Since
spinosad and spinetoram control the
same pests, EPA concludes that these
products will not be used in
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sroberts on PROD1PC70 with RULES
combination with each other and
combining the residential exposures is
unnecessary. Short-term residential
inhalation risks were estimated for adult
residential handlers, as well as shortterm post-application incidental oral
risks for toddlers, based on applications
to home lawns, home gardens and
ornamentals. Dermal exposures were
not assessed, since no dermal endpoints
of concern were identified in the
toxicology studies for spinosad and
spinetoram.
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.’’
Unlike other pesticides for which EPA
has followed a cumulative risk approach
based on a common mechanism of
toxicity, EPA has not made a common
mechanism of toxicity finding as to
spinosad and any other substances and
spinosad does not appear to produce a
toxic metabolite produced by other
substances. For the purposes of this
tolerance action, therefore, EPA has not
assumed that spinosad has a common
mechanism of toxicity with other
substances. For information regarding
EPA’s efforts to determine which
chemicals have a common mechanism
of toxicity and to evaluate the
cumulative effects of such chemicals,
see EPA’s website at https://
www.epa.gov/pesticides/cumulative.
D. Safety Factor for Infants and
Children
1. In general. Section 408 of FFDCA
provides that EPA shall apply an
additional (‘‘10X’’) tenfold margin of
safety for infants and children in the
case of threshold effects to account for
prenatal and postnatal toxicity and the
completeness of the database on toxicity
and exposure unless EPA determines
based on reliable data that a different
margin of safety will be safe for infants
and children. This additional margin of
safety is commonly referred to as the
FQPA safety factor. In applying this
provision, EPA either retains the default
value of 10X when reliable data do not
support the choice of a different factor,
or, if reliable data are available, EPA
uses a different additional FQPA safety
factor value based on the use of
traditional UFs and/or special FQPA
safety factors, as appropriate.
2. Prenatal and postnatal sensitivity.
The following acceptable studies are
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Jkt 214001
available for both spinosad and
spinoteram: developmental toxicity
studies in rats and rabbits and a two–
generation reproduction study in rats.
There is no evidence of increased
susceptibility of rat or rabbit fetuses to
in utero exposure to spinosad or
spinetoram. In the spinosad and
spinetoram rat and rabbit
developmental toxicity studies, no
developmental toxicity was observed at
dose levels that induced maternal
toxicity. In the spinosad two–generation
reproduction study, maternal and
offspring toxicity were equally severe,
indicating no evidence of increased
susceptibility. In the spinetoram 2–
generation reproduction study, no
adverse effects were observed in the
offspring at dose levels that produced
parental toxicity. Therefore, there is no
evidence of increased susceptibility and
there are no concerns or residual
uncertainties for pre and/or post-natal
toxicity.
3. Conclusion. EPA has determined
that reliable data show that it would be
safe for infants and children to reduce
the FQPA safety factor to 1X. That
decision is based on the following
findings:
i. The toxicity database for spinosad
is complete. The toxicity database for
spinetoram is adequate for this risk
assessment despite the lack of a chronic
toxicity study in rats. The preliminary
review of a mouse carcinogenicity study
for spinetoram provides evidence that
the chronic toxicity of spinosad and
spinetoram are comparable, since
spinetoram produced similar toxicity at
doses similar to those seen previously
with spinosad. Therefore, it is expected
that the ongoing spinetoram chronic
carcinogenicity study in rats would
produce similar chronic toxicity at a
similar dose as was seen in the chronic
toxicity study in rats with spinosad.
ii. There is no indication that
spinosad or spinetoram are neurotoxic
chemicals and there is no need for a
developmental neurotoxicity study or
additional UFs to account for
neurotoxicity.
iii. There is no evidence that spinosad
or spinetoram results in increased
susceptibility in in utero rats or rabbits
in the prenatal developmental studies or
in young rats in the 2–generation
reproduction studies.
iv. There are no residual uncertainties
identified in the exposure databases.
The dietary food exposure assessments
were performed based on tolerance-level
residues or anticipated residues derived
from reliable field trial data. 100 PCT
was assumed for all commodities except
certain feed crop commodities. The
projected PCT estimates used for these
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Fmt 4700
Sfmt 4700
commodities are conservative, high-end
estimates developed using the market
leader approach that are unlikely to be
exceeded. Conservative ground and
surface water modeling estimates were
used. Similarly, conservative
Residential SOPs were used to assess
incidental oral exposure of toddlers.
These assessments will not
underestimate the exposure and risks
posed by spinosad and spinetoram.
E. Aggregate Risks and Determination of
Safety
Safety is assessed for acute and
chronic risks by comparing aggregate
exposure to the pesticide to the aPAD
and cPAD. The aPAD and cPAD are
calculated by dividing the LOC by all
applicable UFs. For linear cancer risks,
EPA calculates the probability of
additional cancer cases given aggregate
exposure. Short-term, intermediateterm, and long-term risks are evaluated
by comparing aggregate exposure to the
LOC to ensure that the MOE called for
by the product of all applicable UFs is
not exceeded.
1. Acute risk. None of the toxicology
studies available for spinosad or
spinetoram has indicated the possibility
of an effect of concern occurring as a
result of a 1–day or single exposure;
therefore, spinosad and spinetoram are
not expected to pose an acute risk.
2. Chronic risk. Using the exposure
assumptions described in this unit for
chronic exposure, EPA has concluded
that exposure to spinosad and
spinetoram from food and water will
utilize 81% of the cPAD for children, 1
to 2 years old, the population group
with the greatest estimated exposure.
Based on the use patterns, chronic
residential exposure to residues of
spinosad or spinetoram is not expected.
3. Short-term risk. Short-term
aggregate exposure takes into account
residential exposure plus chronic
exposure to food and water (considered
to be a background exposure level).
Spinosad and spinetoram are
currently registered for uses that could
result in short-term residential
exposure, and the Agency has
determined that it is appropriate to
aggregate chronic food and water and
short-term exposures for spinosad and
spinetoram. Using the exposure
assumptions described in this unit for
short-term exposures, EPA has
concluded that food, water, and
residential exposures aggregated result
in aggregate MOEs of 650 to 710 for
adults and 180 to 300 for infants and
children. The aggregate MOEs for adults
are based on the residential turf scenario
and include combined food, drinking
water and handler inhalation exposures
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to spinetoram. Inhalation exposures are
not expected for residential handlers of
spinosad, based on its granular
formulation and low vapor pressure.
The aggregate MOEs for infants and
children include food, drinking water
and incidental oral exposures on turf
areas previously treated with spinosad
or spinetoram. Dermal exposures were
not assessed for adults or children, since
a dermal endpoint of concern was not
identified in the toxicology studies for
spinosad or spinetoram.
4. Intermediate-term risk.
Intermediate-term aggregate exposure
takes into account residential exposure
plus chronic exposure to food and water
(considered to be a background
exposure level). Spinosad is not
registered for use on any sites that
would result in intermediate-term (1–6
months) residential exposure. Therefore,
the aggregate risk is the sum of the risk
from food and water, which does not
exceed the Agency’s level of concern.
5. Aggregate cancer risk for U.S.
population. Based on the results of
carcinogenicity studies with spinosad in
rats and mice and the preliminary
results of a carcinogenicity study with
spinetoram in mice, spinosad and
spinetoram are considered ‘‘Not likely
to be carcinogenic to humans.’’
Spinosad and spinetoram are not
expected to pose a cancer risk.
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 spinosad and
spinetoram residues.
IV. Other Considerations
A. Analytical Enforcement Methodology
DowElanco Method 97.05, an
immunoassay particle-based method,
and Dow AgroSciences Method GRM
03.15, a high performance liquid
chromatography method with
ultraviolet absorption detection (HPLC/
UV), have been adequately validated
and determined to be acceptable to
enforce the tolerance expression in
spices and pineapple, respectively. The
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; email address: residuemethods@epa.gov.
sroberts on PROD1PC70 with RULES
B. International Residue Limits
There are currently no established
Codex, Canadian, or Mexican maximum
residue levels (MRLs) for spinosad (i.e.,
the combined residues of spinosyn A
and D).
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17:07 Dec 04, 2007
Jkt 214001
C. Response to Comments
Several comments were received from
a private citizen, B. Sachau, objecting to
establishing these tolerances for a
variety of generalized and
unsubstantiated reasons, including the
lack of ‘‘combinant’’ testing and longterm testing, pesticide residues and
unacceptable risk to Americans. The
Agency has received these same or
similar comments from this commenter
on numerous previous occasions. Refer
to Federal Registers of June 30, 2005 (70
FR 37683) (FRL–7718–3), January 7,
2005 (70 FR 1349) (FRL–7691–4), and
October 29, 2004 (69 FR 63083) (FRL–
7681–9) for the Agency’s response to
these objections. The commenter also
objected to issuance of ‘‘exemptions’’ for
this pesticide, an irrelevant comment in
the context of this tolerance-setting
action. Finally, this same commenter
raised concerns about risk to insects and
other animals from spinosad. EPA
considers such environmental risks in
deciding whether to register pesticide
products under the Federal Insecticide,
Fungicide and Rodenticide Act (FIFRA);
however, the safety standard for
approving tolerances under section 408
of the FFDCA focuses on potential
harms to human health and does not
permit consideration of effects on the
environment. Therefore, the comment
regarding risk to insects and other
animals is not relevant to this tolerance
action.
V. Conclusion
Therefore, tolerances are established
for residues of spinosad, consisting of
two related active ingredients: Spinosyn
A (Factor A; CAS # 131929–60–7) or 2[(6-deoxy-2,3,4-tri-O -methyl-a-Lmanno-pyranosyl)oxy]-13-[[5(dimethylamino)-tetrahydro-6-methyl2H-pyran-2-yl]oxy]-9-ethyl2,3,3a,5a,5b,6,9,10,11,12,13,14,16a,16btetradecahydro-14-methyl-1H-asIndaceno[3,2-d]oxacyclododecin-7,15dione; and Spinosyn D (Factor D; CAS
# 131929–63–0) or 2-[(6-deoxy-2,3,4-triO-methyl-a-L-manno-pyranosyl)oxy]13-[[5-(dimethyl-amino)-tetrahydro-6methyl-2H-pyran-2-yl]oxy]-9-ethyl2,3,3a,5a,5b,6,9,10,11,12,13,14,16a,16btetradecahydro-4,14-methyl-1H-asIndaceno[3,2-d]oxacyclododecin-7,15dione, in or on Spice, subgroup 19B,
except black pepper at 1.7 ppm;
Pineapple at 0.02 ppm; and Pineapple,
process residue at 0.08 ppm.
The table of spinosad tolerances at 40
CFR 180.495(a) currently includes a
third column for expiration/revocation
dates. Since none of the existing
tolerances are time-limited and EPA is
not time-limiting the new tolerances for
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Frm 00069
Fmt 4700
Sfmt 4700
68539
spice and pineapple commodities, there
is no need for this column. Therefore,
the third column of the table is being
deleted.
Time-limited tolerances were
established at 40 CFR 180.495(b) for
residues of spinosad in or on livestock
commodities in connection with FIFRA
section 18 emergency exemptions
granted by EPA. All of these timelimited tolerances have expired and are
no longer necessary, because permanent
tolerances have been established on
these commodities at higher levels.
Therefore, these expired, time-limited
tolerances for residues of spinosad
(Factor A and Factor D) are revoked.
Finally, EPA is correcting the
commodity terminology for ‘‘Vegetable,
brassica, leafy, group 5’’ in 40 CFR
180.495(a) to read ‘‘Brassica, leafy
greens, subgroup 5B’’ at 10.0 ppm, to
undo a transcription error. In 1998, EPA
established spinosad tolerances for the
two subgroups in Crop Group 5 Brassica (Cole) Leafy Vegetables (40 CFR
180.41(c)(5). (63 FR 18329, April 15,
1998). The two subgroups in Group 5
are Crop Subgroup 5A - Head and Stem
Brassica and Crop Subgroup 5B - Leafy
Brassica Greens. Tolerances were
established for the subgroups at levels of
2 ppm and 10 ppm respectively. No
tolerance applying across the whole
brassica crop group was established.
Subsequently, in a rulemaking
establishing spinosad tolerances for
various non-brassica commodities the
tolerance for the ‘‘greens’’ subgroup was
incorrectly transcribed as a tolerance for
the entire brassica group (70 FR 1349,
January 7, 2005). This transcription
error occurred when the tolerance table,
as revised by the addition of the new
non-brassica tolerances, was printed in
the Federal Register. The changing of
the subgroup tolerance to a group
tolerance was clearly nothing more than
a transcription error, because it was not
mentioned in the notice of filing for the
rulemaking or the preamble to the final
rule. Moreover, it is inconsistent with
the generic crop group regulation to
establish both a crop group and
subgroup of that crop group for the same
pesticide because the former would
displace the latter. This change merely
corrects the tolerance regulation to
specify the crop subgroup tolerance that
was actually promulgated, since this
tolerance is intended to cover only those
commodities in the ‘‘greens’’ subgroup.
A separate, lower tolerance of 2.0 ppm
has been established to cover head and
stem Brassica in subgroup 5A. The
tolerance for the ‘‘greens’’ subgroup was
incorrectly modified in connection with
the establishment of new spinosad
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sroberts on PROD1PC70 with RULES
tolerances in the Federal Register of
January 7, 2005 (70 FR 1349).
EPA finds there is good cause to make
these latter three changes without prior
notice and comment because they are
technical corrections which either
eliminate obsolete or unused portions of
the regulation or correct a transcription
error. EPA concludes notice and
comment are unnecessary on such
changes.
VI. Statutory and Executive Order
Reviews
This final rule establishes a tolerance
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 rule has
been exempted from review under
Executive Order 12866, this rule is not
subject to Executive Order 13211,
Actions Concerning Regulations That
Significantly Affect Energy Supply,
Distribution, or Use (66 FR 28355, May
22, 2001) 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
VerDate Aug<31>2005
17:07 Dec 04, 2007
Jkt 214001
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 6, 2000) do not apply
to this rule. In addition, This 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).
The product consists of two related
active ingredients: Spinosyn A (Factor
A: CAS # 131929–60–7) or 2-[(6-deoxy2,3,4-tri-O -methyl-a-L-mannopyranosyl)oxy]-13-[[5-(dimethylamino)tetrahydro-6-methyl-2H-pyran-2-yl]oxy]9-ethyl2,3,3a,5a,5b,6,9,10,11,12,13,14,16a,16btetradecahydro-14-methyl-1H-asIndaceno[3,2-d]oxacyclododecin-7,15dione; and Spinosyn D (Factor D; CAS
# 131929–63–0) or 2-[(6-deoxy-2,3,4-triO-methyl-a-L-manno-pyranosyl)oxy]13-[[5-(dimethyl-amino)-tetrahydro-6methyl-2H-pyran-2-yl]oxy]-9-ethyl2,3,3a,5a,5b,6,9,10,11,12,13,14,16a,16btetradecahydro-4,14-methyl-1H-asIndaceno[3,2-d]oxacyclododecin-7,15dione.
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).
Acerola ............................
Alfalfa, seed ....................
Alfalfa, seed screenings
Almond, hulls ..................
Amaranth, grain, grain ....
Amaranth, grain, stover ..
Animal feed, nongrass,
group, 18 .....................
Animal feed, nongrass,
group, 18, forage ........
Animal feed, nongrass,
group, 18, hay .............
Apple pomace .................
Artichoke, globe ..............
Asparagus .......................
Atemoya ..........................
Avocado ..........................
Banana ...........................
Beet, sugar, molasses ....
Biriba ...............................
Brassica, head and stem,
subgroup 5A ................
Brassica, leafy greens,
subgroup 5B ................
Bushberry subgroup 13B
Caneberry subgroup 13A
Canistel ...........................
Cattle, fat ........................
Cattle, liver ......................
Cattle, meat ....................
Cattle, meat byproducts,
except liver ..................
Cherimoya ......................
Citrus, oil .........................
Citrus, dried pulp ............
Coriander, leaves ...........
Corn, sweet, kernel plus
cob with husks removed .........................
Cotton, gin byproducts ...
Cotton, undelinted seed
Cranberry ........................
Custard apple .................
Egg .................................
Feijoa ..............................
Fig ...................................
Fish .................................
Fish-shellfish, crustacean
Fish-shellfish, mollusc ....
Food commodities ..........
Fruit, citrus, group 10 .....
Fruit, pome, group 11 .....
List of Subjects in 40 CFR Part 180
Environmental protection,
Administrative practice and procedure,
Agricultural commodities, Pesticides
and pests, Reporting and recordkeeping
requirements.
Dated: November 27, 2007.
Donald R. Stubbs,
Acting 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 180.495 is revised to read
as follows:
I
§ 180.495 Spinosad; tolerances for
residues.
(a) General. Tolerances are
established for residues of the
insecticide spinosad in or on the food
commodities in the table to this
paragraph. Spinosad is a fermentation
product of Saccharopolyspora spinosa.
PO 00000
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Fmt 4700
Sfmt 4700
Commodity
E:\FR\FM\05DER1.SGM
05DER1
Parts per million
1.5
0.15
2.0
2.0
1.0
10
0.02
35.0
30.0
0.5
0.3
0.2
0.3
0.3
0.25
0.75
0.3
2.0
10.0
0.250
0.7
0.3
50
10
2.0
5.0
0.3
3.0
0.5
8.0
0.02
1.5
0.02
0.01
0.3
0.30
.05
0.10
4.0
4.0
4.0
0.02
0.3
0.20
Federal Register / Vol. 72, No. 233 / Wednesday, December 5, 2007 / Rules and Regulations
Commodity
Parts per million
sroberts on PROD1PC70 with RULES
Fruit, stone, group 12 .....
Goat, fat ..........................
Goat, liver .......................
Goat, meat ......................
Goat, meat byproducts,
except liver ..................
Grain, aspirated fractions
Grain, cereal, group 15 ..
Grain, cereal, group 16,
forage, except rice ......
Grain, cereal, group 16,
hay, except rice ...........
Grain, cereal, group, 16,
stover, except rice .......
Grain, cereal, group, 16,
straw, except rice ........
Grape ..............................
Grape, raisin ...................
Grass, forage, fodder
and hay, group 17, forage ..............................
Grass, forage, fodder
and hay, group 17, hay
Guava .............................
Herb subgroup 19A,
dried ............................
Herb subgroup 19A,
fresh ............................
Hog, fat ...........................
Hog, meat byproducts ....
Hog, meat .......................
Hop, dried cones ............
Horse, fat ........................
Horse, liver .....................
Horse, meat ....................
Horse, meat byproducts,
except liver ..................
Ilama ...............................
Jaboticaba ......................
Juneberry ........................
VerDate Aug<31>2005
17:07 Dec 04, 2007
0.20
50
10
2.0
5.0
200
1.5
2.5
10.0
10.0
1.0
0.50
0.70
10.0
5.0
0.3
22
3.0
33
8.0
1.5
22
50
10
2.0
5.0
0.3
0.3
0.25
Jkt 214001
Commodity
Parts per million
Lingonberry .....................
Longan ............................
Lychee ............................
Mango .............................
Milk .................................
Milk, fat ...........................
Nut, tree, group 14 .........
Okra ................................
Onion, green ...................
Papaya ............................
Passionfruit .....................
Pea and bean, dried
shelled, except soybean, subgroup 6C .....
Pea and bean, succulent
shelled, subgroup 6B ..
Peanut ............................
Peanut, hay ....................
Peppermint, tops ............
Pineapple ........................
Pineapple, process residue .............................
Pistachio .........................
Poultry, fat ......................
Poultry, meat ..................
Poultry, meat byproducts
Pulasan ...........................
Rambutan .......................
Rice, hulls .......................
Salal ................................
Sapodilla .........................
Sapote, black ..................
Sapote, mamey ..............
Sapote, white ..................
Sheep, fat .......................
Sheep, liver .....................
Sheep, meat ...................
Sheep, meat byproducts,
except liver ..................
Soursop ..........................
PO 00000
Frm 00071
Fmt 4700
Sfmt 4700
0.250
0.3
0.3
0.3
7.0
85
0.02
0.40
2.0
0.3
0.3
0.02
0.02
0.02
11.0
3.5
0.02
0.08
0.020
1.3
0.10
0.10
0.3
0.3
4.0
0.250
0.3
0.3
0.3
0.3
50
10
2.0
5.0
0.3
Commodity
Soybean ..........................
Spanish lime ...................
Spearmint, tops ..............
Spice, subgroup 19B, except black pepper .......
Star apple .......................
Starfruit ...........................
Strawberry ......................
Sugar apple ....................
Ti, leaves ........................
Vegetable, bulb, group 3,
except green onion .....
Vegetable, cucurbit,
group 9 ........................
Vegetable, foliage of legume, group 7 ...............
Vegetable, fruiting, group
8 ..................................
Vegetable, leafy, except
brassica, group 4 ........
Vegetable, leaves of root
and tuber, group 2 ......
Vegetable, legume, edible podded, subgroup
6A ................................
Vegetable, root and
tuber, group 1 .............
Watercress ......................
Wax jambu ......................
68541
Parts per million
0.02
0.3
3.5
1.7
0.3
0.3
1.0
0.3
10.0
0.10
0.3
8.0
0.4
8.0
10.0
0.30
0.10
8.0
0.3
(b) Section 18 emergency exemptions.
[Reserved]
(c) Tolerances with regional
registrations. [Reserved]
(d) Indirect or inadvertant residues.
[Reserved]
[FR Doc. E7–23579 Filed 12–4–07; 8:45 am]
BILLING CODE 6560–50–S
E:\FR\FM\05DER1.SGM
05DER1
Agencies
[Federal Register Volume 72, Number 233 (Wednesday, December 5, 2007)]
[Rules and Regulations]
[Pages 68534-68541]
From the Federal Register Online via the Government Printing Office [www.gpo.gov]
[FR Doc No: E7-23579]
-----------------------------------------------------------------------
ENVIRONMENTAL PROTECTION AGENCY
40 CFR Part 180
[EPA-HQ-OPP-2007-0310; FRL-8339-8]
Spinosad; Pesticide Tolerance
AGENCY: Environmental Protection Agency (EPA).
ACTION: Final rule.
-----------------------------------------------------------------------
SUMMARY: This regulation establishes tolerances for residues of
spinosad in or on spice, subgroup 19B, except black pepper; pineapple;
and pineapple, process residue. Interregional Research Project Number 4
(IR-4) requested these tolerances under the Federal Food, Drug, and
Cosmetic Act (FFDCA).
DATES: This regulation is effective December 5, 2007. Objections and
requests for hearings must be received on or before February 4, 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-2007-0310. 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: Susan Stanton, Registration Division
(7505P), Office of Pesticide Programs, Environmental Protection Agency,
1200 Pennsylvania Ave., NW., Washington, DC 20460-0001; telephone
number: (703) 305-5218; e-mail address: stanton.susan@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), e.g., agricultural
workers; greenhouse, nursery, and floriculture workers; farmers.
Animal production (NAICS code 112), e.g., cattle ranchers
and farmers, dairy cattle farmers, livestock farmers.
Food manufacturing (NAICS code 311), e.g., agricultural
workers; farmers; greenhouse, nursery, and floriculture workers;
ranchers; pesticide applicators.
Pesticide manufacturing (NAICS code 32532), e.g.,
agricultural workers; commercial applicators; farmers; greenhouse,
nursery, and floriculture workers; residential users.
This listing is not intended to be exhaustive, but rather 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.
[[Page 68535]]
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-2007-0310 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 January 4, 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-2007-0310, 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 May 9, 2007 (72 FR 26375) (FRL-8128-1),
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 6E7148)
by Interregional Research Project Number 4 (IR-4), 500 College Road
East, Suite 201 W, Princeton, NJ 08540-6635. The petition requested
that 40 CFR 180.495 be amended by establishing a tolerance for residues
of the insecticide spinosad, in or on Spice crop subgroup 19B, except
black pepper at 1.7 parts per million (ppm); pineapple at 0.02 ppm; and
pineapple, process residue at 0.08 ppm. Spinosad is a fermentation
product of Saccharopolyspora spinosa, consisting of two related active
ingredients: Spinosyn A (Factor A; CAS 131929-60-7) or 2-[(6-
deoxy-2,3,4-tri-O-methyl-[alpha]-L-manno-pyranosyl)oxy]-13-[[5-
(dimethylamino)-tetrahydro-6-methyl-2H-pyran-2-yl]oxy]-9-ethyl-
2,3,3a,5a,5b,6,9,10,11,12,13,14,16a,16b-tetradecahydro-14-methyl-1H-as-
Indaceno[3,2-d]oxacyclododecin-7,15-dione; and Spinosyn D (Factor D;
CAS 131929-63-0) or 2-[(6-deoxy-2,3,4-tri-O-methyl-[alpha]-L-
manno-pyranosyl)oxy]-13-[[5-(dimethyl-amino)-tetrahydro-6-methyl-2H-
pyran-2-yl]oxy]-9-ethyl-2,3,3a,5a,5b,6,9,10,11,12,13,14,16a,16b-
tetradecahydro-4,14-methyl-1H-as-Indaceno[3,2-d]oxacyclododecin-7,15-
dione. That notice referenced a summary of the petition prepared by Dow
AgroSciences LLC, the registrant, which is available to the public in
the docket, https://www.regulations.gov. Comments were received on the
notice of filing from a private citizen. EPA's response to these
comments is discussed in Unit IV.C. below.
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....'' These provisions were added to FFDCA by the Food Quality
Protection Act (FQPA) of 1996.
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 spinosad on spice, subgroup 19B, except
black pepper at 1.7 ppm; pineapple at 0.02 ppm; and Pineapple, process
residue at 0.08 ppm. EPA's assessment of exposures and risks associated
with establishing the tolerance follows.
A. Toxicological Profile
EPA has evaluated the available toxicity data and considered its
validity, completeness, and reliability as well as the relationship of
the results of the studies to human risk. EPA has also considered
available information concerning the variability of the sensitivities
of major identifiable subgroups of consumers, including infants and
children. Specific information on the studies received and the nature
of the adverse effects caused by spinosad as well as the no-observed-
adverse-effect-level (NOAEL) and the lowest-observed-adverse-effect-
level (LOAEL) from the toxicity studies are discussed in the final rule
published in the Federal Register of September 27, 2002 (67 FR 60923)
(FRL-7199-5), available on-line at https://www.epa.gov/fedrgstr/EPA-
PEST/2002/September/Day-27/p24484.htm.
B. Toxicological Endpoints
For hazards that have a threshold below which there is no
appreciable risk, the toxicological level of concern (LOC) is derived
from the highest dose at which no adverse effects are observed (the
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 adverse effects of concern are identified (the LOAEL) is
sometimes used for risk assessment. Uncertainty/safety factors (UFs)
are used in conjunction with the LOC 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
[[Page 68536]]
human population as well as other unknowns. Safety is assessed for
acute and chronic risks by comparing aggregate 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 LOC by all applicable UFs. Short-term, intermediate-term,
and long-term risks are evaluated by comparing aggregate exposure to
the LOC to ensure that the margin of exposure (MOE) called for by the
product of all applicable UFs is not exceeded.
For non-threshold risks, the Agency assumes that any amount of
exposure will lead to some degree of risk and estimates risk in terms
of the probability of occurrence of additional adverse cases.
Generally, cancer risks are considered non-threshold. 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.
The Agency has concluded that spinosad should be considered
toxicologically identical to another pesticide, spinetoram. This
conclusion is based on the following: (1) Spinetoram and spinosad are
large molecules with nearly identical structures; and (2) the
toxicological profiles for each are similar (generalized systemic
toxicity) with similar doses and endpoints chosen for human-health risk
assessment. Spinosad and spinetoram should be considered
toxicologically identical in the same manner that metabolites are
generally considered toxicologically identical to the parent.
Although, as stated above, the doses and endpoints for spinosad and
spinetoram are similar, they are not identical due to variations in
dosing levels used in the spinetoram and spinosad toxicological
studies. EPA compared the spinosad and spinetoram doses and endpoints
for each exposure scenario and selected the lower of the two doses for
use in human risk assessment. A summary of the toxicological endpoints
for spinosad and spinetoram used for human risk assessment can be found
at https://www.regulations.gov in the document Spinosad and Spinetoram.
Human-Health Risk Assessment for Application of Spinosad to Pineapple
and the Spice Subgroup (19B, except black pepper) at page 11 in docket
ID number EPA-HQ-OPP-2007-0310.
C. Exposure Assessment
1. Dietary exposure from food and feed uses. In evaluating dietary
exposure to spinosad, EPA considered exposure under the petitioned-for
tolerances as well as all existing spinosad tolerances in 40 CFR
180.495. Since spinosad and spinetoram are toxicologically identical,
EPA considered exposure to both in assessing aggregate risk. EPA
assessed dietary exposures from spinosad and spinetoram 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. No such effects were
identified in the toxicological studies for spinosad and spinetoram;
therefore, a quantitative acute dietary exposure assessment is
unnecessary.
ii. Chronic exposure. Spinosad and spinetoram are registered for
use on the same crops; however, EPA has concluded it would overstate
exposure to assume that residues of both spinosad and spinetoram would
appear on the same crop. It is unlikely that both will be applied to
the same crop, since spinosad and spinetoram control the same pest
species. Rather, EPA aggregated exposure from residues of spinosad and
spinetoram by assuming that spinosad residues would be present in all
commodities, because side-by-side spinosad and spinetoram residue data
indicated that spinetoram residues were less than or equal to spinosad
residues. EPA assumed that 100 percent of each food crop commodity
would be treated with spinosad. For feed crop commodities, EPA summed
the percentage of the crop that would be treated with spinosad and the
percentage expected to be treated with spinetoram and used this
estimate in conjunction with spinosad residue data to develop
anticipated residues for livestock commodities.
The chronic dietary exposure assessment was conducted using the
Dietary Exposure Evaluation Model - Food Consumption Intake Database
(DEEM\TM\-FCID), Version 2.03, which incorporates food consumption data
from the United States Department of Agriculture (USDA) 1994-1996 and
1998 Continuing Surveys of Food Intakes by Individuals (CSFII). In
addition to the Percent Crop Treated (PCT) assumptions described above,
EPA, in estimating chronic exposure, relied upon average field trial
residues for apple, leafy vegetables (except Brassica), citrus and
fruiting vegetables; tolerance level residues for the remaining food
crop commodities; average feed crop residues for feed commodities from
the following crops: Sweet corn forage, leaves of root and tuber
vegetables and aspirated grain fractions; average residues from animal
feeding and dermal magnitude of residue studies; and DEEM\TM\ (Version
7.81) default processing factors for all commodities, excluding field
corn (meal, starch, flour and oil), grape juice and wheat (flour and
germ), where processing factors based on the results of processing
studies were assumed.
iii. Cancer. Based on the results of carcinogenicity studies in
rats and mice, spinosad has been classified as ``Not likely to be
carcinogenic to humans.'' Preliminary results of a carcinogenicity
study in mice indicate that spinetoram is not carcinogenic to mice at
doses up to 37.5 milligram/kilogram/day (mg/kg/day). Based on these
preliminary results and spinetoram's structural and toxicological
similarity to spinosad, spinetoram is also considered to be ``Not
likely to be carcinogenic to humans.'' Consequently, a quantitative
cancer exposure and risk assessment is not appropriate for spinosad or
spinetoram.
iv. Anticipated residue and PCT information. Section 408(b)(2)(E)
of FFDCA authorizes EPA to use available data and information on the
anticipated residue levels of pesticide residues in food and the actual
levels of pesticide residues that have been measured in food. If EPA
relies on such information, EPA must pursuant to FFDCA section
408(f)(1) require that data be provided 5 years after the tolerance is
established, modified, or left in effect, demonstrating that the levels
in food are not above the levels anticipated. For the present action,
EPA will issue such data call-ins as are required by FFDCA section
408(b)(2)(E) and authorized under FFDCA section 408(f)(1). Data will be
required to be submitted no later than 5 years from the date of
issuance of this tolerance.
Section 408(b)(2)(F) of FFDCA states that the Agency may use data
on the actual percent of food treated for assessing chronic dietary
risk only if:
a. The data used are reliable and provide a valid basis to show
what percentage of the food derived from such crop is likely to contain
such pesticide residue.
b. The exposure estimate does not underestimate exposure for any
significant subpopulation group.
c. Data are available on pesticide use and food consumption in a
particular area, the exposure estimate does not understate exposure for
the population in such area. In addition, the Agency
[[Page 68537]]
must provide for periodic evaluation of any estimates used. To provide
for the periodic evaluation of the estimate of PCT as required by FFDCA
section 408(b)(2)(F), EPA may require registrants to submit data on
PCT.
The Agency used PCT information as follows:
One-hundred percent crop treated was assumed for all food crop
commodities and some feed crop commodities (aspirated grain fractions,
sugarbeet molasses and cottonseed). For certain feed crop commodities,
the Agency summed the projected PCT for spinosad and spinetoram and
used the combined estimates in conjunction with average field trial
residues to calculate cattle dietary burdens and anticipated residues
of spinosad in meat and milk. The following combined projected PCT
estimates were used: sweet corn forage (39%), sorghum grain (5%),
soybean seed meal (5%) and leaves of root and tuber vegetables (50%).
Spinetoram is a new, recently registered pesticide. EPA estimates
an upper bound of projected percent crop treated (PPCT) for a new
pesticide use by assuming that its actual PCT during the initial 5
years of use on a specific use site will not exceed the recent PCT of
the market leader (i.e., the one with the greatest PCT) on that site.
EPA calls this the market leader PPCT estimate. In this specific case,
the new use to be estimated is the combined use of spinosad together
with that of spinetoram since the most new use of spinetoram will
likely replace previous use of spinosad. An average market leader PCT,
based on three recent surveys of pesticide usage, if available, is used
for chronic risk assessment. The average market leader PCT may be based
on one or two survey years if three are not available. Also, with
limited availability of data, the average market leader PCT may be
based on a cross-section of state PCTs. Comparisons are only made among
pesticides of the same pesticide type (i.e., the leading insecticide on
the use site is selected for comparison with the new insecticide), or,
for refined estimates, among pesticides targeting the same pests. The
market leader PCTs used to determine the average may be each for the
same pesticide or for different pesticides for any year since the same
or different pesticides may dominate for each year. Typically, EPA uses
U.S. Department of Agriculture/National Agricultural Statistics Service
(USDA/NASS) as the source for raw PCT data because it is publicly
available. When a specific use site is not surveyed by USDA/NASS, EPA
uses other sources including proprietary data.
An estimated PPCT, based on the average PCT of the market leaders,
is appropriate for use in chronic dietary risk assessment. This method
of estimating PPCT for a new use of a registered pesticide or a new
pesticide produces a high-end estimate that is unlikely, in most cases,
to be exceeded during the initial 5 years of actual use. Predominant
factors that bear on whether the PPCT could be exceeded may include
PCTs of similar chemistries, pests controlled by alternatives, pest
prevalence in the market and other factors. All relevant information
currently available for predominant factors has been considered for the
combined use of spinetoram and spinosad on each of these several crops.
It is the Agency's opinion that it is unlikely that actual combined
PCTs for spinetoram and spinosad will exceed the corresponding
estimated PPCTs during the next 5 years.
The PPCTs for the combined use of spinosad and spinetoram for
chronic risk assessment were determined using the market leader
approach for the feed commodities of sweet corn, grain sorghum,
soybeans and turnip greens. For turnip greens, the PCTs of market
leaders were averaged over states rather than years because only 1-year
of data was available.
The Agency believes that the three conditions listed in this Unit
have been met. With respect to Condition 1, PCT estimates are derived
from Federal and private market survey data, which are reliable and
have a valid basis. The Agency is reasonably certain that the
percentage of the food treated is not likely to be an underestimation.
As to Conditions 2 and 3, regional consumption information and
consumption information for significant subpopulations is taken into
account through EPA's computer-based model for evaluating the exposure
of significant subpopulations including several regional groups. Use of
this consumption information in EPA's risk assessment process ensures
that EPA's exposure estimate does not understate exposure for any
significant subpopulation group and allows the Agency to be reasonably
certain that no regional population is exposed to residue levels higher
than those estimated by the Agency. Other than the data available
through national food consumption surveys, EPA does not have available
information on the regional consumption of food to which spinosad may
be applied in a particular area.
2. Dietary exposure from drinking water. The Agency lacks
sufficient monitoring data to complete a comprehensive dietary exposure
analysis and risk assessment for spinosad in drinking water. Because
the Agency does not have comprehensive monitoring data, drinking water
concentration estimates are made by reliance on simulation or modeling
taking into account data on the environmental fate characteristics of
spinosad. Further information regarding EPA drinking water models used
in pesticide exposure assessment can be found at https://www.epa.gov/
oppefed1/models/water/index.htm.
Based on the First Index Reservoir Screening Tool (FIRST) and
Screening Concentration in Ground Water (SCI-GROW) models, the
estimated environmental concentrations (EECs) of spinosad for acute
exposures are estimated to be 34.5 parts per billion (ppb) for surface
water and 1.1 ppb for ground water. The EECs for chronic exposures are
estimated to be 10.5 ppb for surface water and 1.1 ppb for ground
water.
Modeled estimates of drinking water concentrations were directly
entered into the dietary exposure model. As explained above, an acute
dietary risk assessment was not conducted for spinosad and spinetoram.
For chronic dietary risk assessment, the water concentration of value
10.5 ppb was used to access 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).
The Agency has concluded that spinosad and spinetoram are
toxicologically equivalent; therefore, residential exposure to both
spinosad and spinetoram was evaluated. Spinosad is currently registered
for the following residential non-dietary sites: Homeowner application
to turf grass and ornamentals to control a variety of worms, moths,
flies, beetles, midges, thrips, leafminers and fire ants (granular
formulation). Spinetoram is registered for homeowner applications to
gardens, lawns/ornamentals and turf grass for control of lepidopterous
larvae (worms or caterpillars), dipterous leafminers, thrips, sawfly
larvae, certain psyllids and leaf-feeding beetles and red imported fire
ants.
There is potential for residential handler and post-application
exposures to both spinosad and spinetoram. Since spinosad and
spinetoram control the same pests, EPA concludes that these products
will not be used in
[[Page 68538]]
combination with each other and combining the residential exposures is
unnecessary. Short-term residential inhalation risks were estimated for
adult residential handlers, as well as short-term post-application
incidental oral risks for toddlers, based on applications to home
lawns, home gardens and ornamentals. Dermal exposures were not
assessed, since no dermal endpoints of concern were identified in the
toxicology studies for spinosad and spinetoram.
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.''
Unlike other pesticides for which EPA has followed a cumulative
risk approach based on a common mechanism of toxicity, EPA has not made
a common mechanism of toxicity finding as to spinosad and any other
substances and spinosad does not appear to produce a toxic metabolite
produced by other substances. For the purposes of this tolerance
action, therefore, EPA has not assumed that spinosad has a common
mechanism of toxicity with other substances. For information regarding
EPA's efforts to determine which chemicals have a common mechanism of
toxicity and to evaluate the cumulative effects of such chemicals, see
EPA's website at https://www.epa.gov/pesticides/cumulative.
D. Safety Factor for Infants and Children
1. In general. Section 408 of FFDCA provides that EPA shall apply
an additional (``10X'') tenfold margin of safety for infants and
children in the case of threshold effects to account for prenatal and
postnatal toxicity and the completeness of the database on toxicity and
exposure unless EPA determines based on reliable data that a different
margin of safety will be safe for infants and children. This additional
margin of safety is commonly referred to as the FQPA safety factor. In
applying this provision, EPA either retains the default value of 10X
when reliable data do not support the choice of a different factor, or,
if reliable data are available, EPA uses a different additional FQPA
safety factor value based on the use of traditional UFs and/or special
FQPA safety factors, as appropriate.
2. Prenatal and postnatal sensitivity. The following acceptable
studies are available for both spinosad and spinoteram: developmental
toxicity studies in rats and rabbits and a two-generation reproduction
study in rats. There is no evidence of increased susceptibility of rat
or rabbit fetuses to in utero exposure to spinosad or spinetoram. In
the spinosad and spinetoram rat and rabbit developmental toxicity
studies, no developmental toxicity was observed at dose levels that
induced maternal toxicity. In the spinosad two-generation reproduction
study, maternal and offspring toxicity were equally severe, indicating
no evidence of increased susceptibility. In the spinetoram 2-generation
reproduction study, no adverse effects were observed in the offspring
at dose levels that produced parental toxicity. Therefore, there is no
evidence of increased susceptibility and there are no concerns or
residual uncertainties for pre and/or post-natal toxicity.
3. Conclusion. EPA has determined that reliable data show that it
would be safe for infants and children to reduce the FQPA safety factor
to 1X. That decision is based on the following findings:
i. The toxicity database for spinosad is complete. The toxicity
database for spinetoram is adequate for this risk assessment despite
the lack of a chronic toxicity study in rats. The preliminary review of
a mouse carcinogenicity study for spinetoram provides evidence that the
chronic toxicity of spinosad and spinetoram are comparable, since
spinetoram produced similar toxicity at doses similar to those seen
previously with spinosad. Therefore, it is expected that the ongoing
spinetoram chronic carcinogenicity study in rats would produce similar
chronic toxicity at a similar dose as was seen in the chronic toxicity
study in rats with spinosad.
ii. There is no indication that spinosad or spinetoram are
neurotoxic chemicals and there is no need for a developmental
neurotoxicity study or additional UFs to account for neurotoxicity.
iii. There is no evidence that spinosad or spinetoram results in
increased susceptibility in in utero rats or rabbits in the prenatal
developmental studies or in young rats in the 2-generation reproduction
studies.
iv. There are no residual uncertainties identified in the exposure
databases. The dietary food exposure assessments were performed based
on tolerance-level residues or anticipated residues derived from
reliable field trial data. 100 PCT was assumed for all commodities
except certain feed crop commodities. The projected PCT estimates used
for these commodities are conservative, high-end estimates developed
using the market leader approach that are unlikely to be exceeded.
Conservative ground and surface water modeling estimates were used.
Similarly, conservative Residential SOPs were used to assess incidental
oral exposure of toddlers. These assessments will not underestimate the
exposure and risks posed by spinosad and spinetoram.
E. Aggregate Risks and Determination of Safety
Safety is assessed for acute and chronic risks by comparing
aggregate exposure to the pesticide to the aPAD and cPAD. The aPAD and
cPAD are calculated by dividing the LOC by all applicable UFs. For
linear cancer risks, EPA calculates the probability of additional
cancer cases given aggregate exposure. Short-term, intermediate-term,
and long-term risks are evaluated by comparing aggregate exposure to
the LOC to ensure that the MOE called for by the product of all
applicable UFs is not exceeded.
1. Acute risk. None of the toxicology studies available for
spinosad or spinetoram has indicated the possibility of an effect of
concern occurring as a result of a 1-day or single exposure; therefore,
spinosad and spinetoram are not expected to pose an acute risk.
2. Chronic risk. Using the exposure assumptions described in this
unit for chronic exposure, EPA has concluded that exposure to spinosad
and spinetoram from food and water will utilize 81% of the cPAD for
children, 1 to 2 years old, the population group with the greatest
estimated exposure. Based on the use patterns, chronic residential
exposure to residues of spinosad or spinetoram is not expected.
3. Short-term risk. Short-term aggregate exposure takes into
account residential exposure plus chronic exposure to food and water
(considered to be a background exposure level).
Spinosad and spinetoram are currently registered for uses that
could result in short-term residential exposure, and the Agency has
determined that it is appropriate to aggregate chronic food and water
and short-term exposures for spinosad and spinetoram. Using the
exposure assumptions described in this unit for short-term exposures,
EPA has concluded that food, water, and residential exposures
aggregated result in aggregate MOEs of 650 to 710 for adults and 180 to
300 for infants and children. The aggregate MOEs for adults are based
on the residential turf scenario and include combined food, drinking
water and handler inhalation exposures
[[Page 68539]]
to spinetoram. Inhalation exposures are not expected for residential
handlers of spinosad, based on its granular formulation and low vapor
pressure. The aggregate MOEs for infants and children include food,
drinking water and incidental oral exposures on turf areas previously
treated with spinosad or spinetoram. Dermal exposures were not assessed
for adults or children, since a dermal endpoint of concern was not
identified in the toxicology studies for spinosad or spinetoram.
4. Intermediate-term risk. Intermediate-term aggregate exposure
takes into account residential exposure plus chronic exposure to food
and water (considered to be a background exposure level). Spinosad is
not registered for use on any sites that would result in intermediate-
term (1-6 months) residential exposure. Therefore, the aggregate risk
is the sum of the risk from food and water, which does not exceed the
Agency's level of concern.
5. Aggregate cancer risk for U.S. population. Based on the results
of carcinogenicity studies with spinosad in rats and mice and the
preliminary results of a carcinogenicity study with spinetoram in mice,
spinosad and spinetoram are considered ``Not likely to be carcinogenic
to humans.'' Spinosad and spinetoram are not expected to pose a cancer
risk.
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 spinosad and spinetoram residues.
IV. Other Considerations
A. Analytical Enforcement Methodology
DowElanco Method 97.05, an immunoassay particle-based method, and
Dow AgroSciences Method GRM 03.15, a high performance liquid
chromatography method with ultraviolet absorption detection (HPLC/UV),
have been adequately validated and determined to be acceptable to
enforce the tolerance expression in spices and pineapple, respectively.
The 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 currently no established Codex, Canadian, or Mexican
maximum residue levels (MRLs) for spinosad (i.e., the combined residues
of spinosyn A and D).
C. Response to Comments
Several comments were received from a private citizen, B. Sachau,
objecting to establishing these tolerances for a variety of generalized
and unsubstantiated reasons, including the lack of ``combinant''
testing and long-term testing, pesticide residues and unacceptable risk
to Americans. The Agency has received these same or similar comments
from this commenter on numerous previous occasions. Refer to Federal
Registers of June 30, 2005 (70 FR 37683) (FRL-7718-3), January 7, 2005
(70 FR 1349) (FRL-7691-4), and October 29, 2004 (69 FR 63083) (FRL-
7681-9) for the Agency's response to these objections. The commenter
also objected to issuance of ``exemptions'' for this pesticide, an
irrelevant comment in the context of this tolerance-setting action.
Finally, this same commenter raised concerns about risk to insects and
other animals from spinosad. EPA considers such environmental risks in
deciding whether to register pesticide products under the Federal
Insecticide, Fungicide and Rodenticide Act (FIFRA); however, the safety
standard for approving tolerances under section 408 of the FFDCA
focuses on potential harms to human health and does not permit
consideration of effects on the environment. Therefore, the comment
regarding risk to insects and other animals is not relevant to this
tolerance action.
V. Conclusion
Therefore, tolerances are established for residues of spinosad,
consisting of two related active ingredients: Spinosyn A (Factor A; CAS
131929-60-7) or 2-[(6-deoxy-2,3,4-tri-O -methyl-[alpha]-L-
manno-pyranosyl)oxy]-13-[[5-(dimethylamino)-tetrahydro-6-methyl-2H-
pyran-2-yl]oxy]-9-ethyl-2,3,3a,5a,5b,6,9,10,11,12,13,14,16a,16b-
tetradecahydro-14-methyl-1H-as-Indaceno[3,2-d]oxacyclododecin-7,15-
dione; and Spinosyn D (Factor D; CAS 131929-63-0) or 2-[(6-
deoxy-2,3,4-tri-O-methyl-[alpha]-L-manno-pyranosyl)oxy]-13-[[5-
(dimethyl-amino)-tetrahydro-6-methyl-2H-pyran-2-yl]oxy]-9-ethyl-
2,3,3a,5a,5b,6,9,10,11,12,13,14,16a,16b-tetradecahydro-4,14-methyl-1H-
as-Indaceno[3,2-d]oxacyclododecin-7,15-dione, in or on Spice, subgroup
19B, except black pepper at 1.7 ppm; Pineapple at 0.02 ppm; and
Pineapple, process residue at 0.08 ppm.
The table of spinosad tolerances at 40 CFR 180.495(a) currently
includes a third column for expiration/revocation dates. Since none of
the existing tolerances are time-limited and EPA is not time-limiting
the new tolerances for spice and pineapple commodities, there is no
need for this column. Therefore, the third column of the table is being
deleted.
Time-limited tolerances were established at 40 CFR 180.495(b) for
residues of spinosad in or on livestock commodities in connection with
FIFRA section 18 emergency exemptions granted by EPA. All of these
time-limited tolerances have expired and are no longer necessary,
because permanent tolerances have been established on these commodities
at higher levels. Therefore, these expired, time-limited tolerances for
residues of spinosad (Factor A and Factor D) are revoked.
Finally, EPA is correcting the commodity terminology for
``Vegetable, brassica, leafy, group 5'' in 40 CFR 180.495(a) to read
``Brassica, leafy greens, subgroup 5B'' at 10.0 ppm, to undo a
transcription error. In 1998, EPA established spinosad tolerances for
the two subgroups in Crop Group 5 - Brassica (Cole) Leafy Vegetables
(40 CFR 180.41(c)(5). (63 FR 18329, April 15, 1998). The two subgroups
in Group 5 are Crop Subgroup 5A - Head and Stem Brassica and Crop
Subgroup 5B - Leafy Brassica Greens. Tolerances were established for
the subgroups at levels of 2 ppm and 10 ppm respectively. No tolerance
applying across the whole brassica crop group was established.
Subsequently, in a rulemaking establishing spinosad tolerances for
various non-brassica commodities the tolerance for the ``greens''
subgroup was incorrectly transcribed as a tolerance for the entire
brassica group (70 FR 1349, January 7, 2005). This transcription error
occurred when the tolerance table, as revised by the addition of the
new non-brassica tolerances, was printed in the Federal Register. The
changing of the subgroup tolerance to a group tolerance was clearly
nothing more than a transcription error, because it was not mentioned
in the notice of filing for the rulemaking or the preamble to the final
rule. Moreover, it is inconsistent with the generic crop group
regulation to establish both a crop group and subgroup of that crop
group for the same pesticide because the former would displace the
latter. This change merely corrects the tolerance regulation to specify
the crop subgroup tolerance that was actually promulgated, since this
tolerance is intended to cover only those commodities in the ``greens''
subgroup. A separate, lower tolerance of 2.0 ppm has been established
to cover head and stem Brassica in subgroup 5A. The tolerance for the
``greens'' subgroup was incorrectly modified in connection with the
establishment of new spinosad
[[Page 68540]]
tolerances in the Federal Register of January 7, 2005 (70 FR 1349).
EPA finds there is good cause to make these latter three changes
without prior notice and comment because they are technical corrections
which either eliminate obsolete or unused portions of the regulation or
correct a transcription error. EPA concludes notice and comment are
unnecessary on such changes.
VI. Statutory and Executive Order Reviews
This final rule establishes a tolerance 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 rule has been
exempted from review under Executive Order 12866, this rule is not
subject to Executive Order 13211, Actions Concerning Regulations That
Significantly Affect Energy Supply, Distribution, or Use (66 FR 28355,
May 22, 2001) 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 6, 2000) do not apply to this rule. In addition, This
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: November 27, 2007.
Donald R. Stubbs,
Acting 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 180.495 is revised to read as follows:
Sec. 180.495 Spinosad; tolerances for residues.
(a) General. Tolerances are established for residues of the
insecticide spinosad in or on the food commodities in the table to this
paragraph. Spinosad is a fermentation product of Saccharopolyspora
spinosa. The product consists of two related active ingredients:
Spinosyn A (Factor A: CAS 131929-60-7) or 2-[(6-deoxy-2,3,4-
tri-O -methyl-[alpha]-L-manno-pyranosyl)oxy]-13-[[5-(dimethylamino)-
tetrahydro-6-methyl-2H-pyran-2-yl]oxy]-9-ethyl-
2,3,3a,5a,5b,6,9,10,11,12,13,14,16a,16b-tetradecahydro-14-methyl-1H-as-
Indaceno[3,2-d]oxacyclododecin-7,15-dione; and Spinosyn D (Factor D;
CAS 131929-63-0) or 2-[(6-deoxy-2,3,4-tri-O-methyl-[alpha]-L-
manno-pyranosyl)oxy]-13-[[5-(dimethyl-amino)-tetrahydro-6-methyl-2H-
pyran-2-yl]oxy]-9-ethyl-2,3,3a,5a,5b,6,9,10,11,12,13,14,16a,16b-
tetradecahydro-4,14-methyl-1H-as-Indaceno[3,2-d]oxacyclododecin-7,15-
dione.
------------------------------------------------------------------------
Commodity Parts per million
------------------------------------------------------------------------
Acerola.............................................. 1.5
Alfalfa, seed........................................ 0.15
Alfalfa, seed screenings............................. 2.0
Almond, hulls........................................ 2.0
Amaranth, grain, grain............................... 1.0
Amaranth, grain, stover.............................. 10
Animal feed, nongrass, group, 18..................... 0.02
Animal feed, nongrass, group, 18, forage............. 35.0
Animal feed, nongrass, group, 18, hay................ 30.0
Apple pomace......................................... 0.5
Artichoke, globe..................................... 0.3
Asparagus............................................ 0.2
Atemoya.............................................. 0.3
Avocado.............................................. 0.3
Banana............................................... 0.25
Beet, sugar, molasses................................ 0.75
Biriba............................................... 0.3
Brassica, head and stem, subgroup 5A................. 2.0
Brassica, leafy greens, subgroup 5B.................. 10.0
Bushberry subgroup 13B............................... 0.250
Caneberry subgroup 13A............................... 0.7
Canistel............................................. 0.3
Cattle, fat.......................................... 50
Cattle, liver........................................ 10
Cattle, meat......................................... 2.0
Cattle, meat byproducts, except liver................ 5.0
Cherimoya............................................ 0.3
Citrus, oil.......................................... 3.0
Citrus, dried pulp................................... 0.5
Coriander, leaves.................................... 8.0
Corn, sweet, kernel plus cob with husks removed...... 0.02
Cotton, gin byproducts............................... 1.5
Cotton, undelinted seed.............................. 0.02
Cranberry............................................ 0.01
Custard apple........................................ 0.3
Egg.................................................. 0.30
Feijoa............................................... .05
Fig.................................................. 0.10
Fish................................................. 4.0
Fish-shellfish, crustacean........................... 4.0
Fish-shellfish, mollusc.............................. 4.0
Food commodities..................................... 0.02
Fruit, citrus, group 10.............................. 0.3
Fruit, pome, group 11................................ 0.20
[[Page 68541]]
Fruit, stone, group 12............................... 0.20
Goat, fat............................................ 50
Goat, liver.......................................... 10
Goat, meat........................................... 2.0
Goat, meat byproducts, except liver.................. 5.0
Grain, aspirated fractions........................... 200
Grain, cereal, group 15.............................. 1.5
Grain, cereal, group 16, forage, except rice......... 2.5
Grain, cereal, group 16, hay, except rice............ 10.0
Grain, cereal, group, 16, stover, except rice........ 10.0
Grain, cereal, group, 16, straw, except rice......... 1.0
Grape................................................ 0.50
Grape, raisin........................................ 0.70
Grass, forage, fodder and hay, group 17, forage...... 10.0
Grass, forage, fodder and hay, group 17, hay......... 5.0
Guava................................................ 0.3
Herb subgroup 19A, dried............................. 22
Herb subgroup 19A, fresh............................. 3.0
Hog, fat............................................. 33
Hog, meat byproducts................................. 8.0
Hog, meat............................................ 1.5
Hop, dried cones..................................... 22
Horse, fat........................................... 50
Horse, liver......................................... 10
Horse, meat.......................................... 2.0
Horse, meat byproducts, except liver................. 5.0
Ilama................................................ 0.3
Jaboticaba........................................... 0.3
Juneberry............................................ 0.25
Lingonberry.......................................... 0.250
Longan............................................... 0.3
Lychee............................................... 0.3
Mango................................................ 0.3
Milk................................................. 7.0
Milk, fat............................................ 85
Nut, tree, group 14.................................. 0.02
Okra................................................. 0.40
Onion, green......................................... 2.0
Papaya............................................... 0.3
Passionfruit......................................... 0.3
Pea and bean, dried shelled, except soybean, subgroup 0.02
6C..................................................
Pea and bean, succulent shelled, subgroup 6B......... 0.02
Peanut............................................... 0.02
Peanut, hay.......................................... 11.0
Peppermint, tops..................................... 3.5
Pineapple............................................ 0.02
Pineapple, process residue........................... 0.08
Pistachio............................................ 0.020
Poultry, fat......................................... 1.3
Poultry, meat........................................ 0.10
Poultry, meat byproducts............................. 0.10
Pulasan.............................................. 0.3
Rambutan............................................. 0.3
Rice, hulls.......................................... 4.0
Salal................................................ 0.250
Sapodilla............................................ 0.3
Sapote, black........................................ 0.3
Sapote, mamey........................................ 0.3
Sapote, white........................................ 0.3
Sheep, fat........................................... 50
Sheep, liver......................................... 10
Sheep, meat.......................................... 2.0
Sheep, meat byproducts, except liver................. 5.0
Soursop.............................................. 0.3
Soybean.............................................. 0.02
Spanish lime......................................... 0.3
Spearmint, tops...................................... 3.5
Spice, subgroup 19B, except black pepper............. 1.7
Star apple........................................... 0.3
Starfruit............................................ 0.3
Strawberry........................................... 1.0
Sugar apple.......................................... 0.3
Ti, leaves........................................... 10.0
Vegetable, bulb, group 3, except green onion......... 0.10
Vegetable, cucurbit, group 9......................... 0.3
Vegetable, foliage of legume, group 7................ 8.0
Vegetable, fruiting, group 8......................... 0.4
Vegetable, leafy, except brassica, group 4........... 8.0
Vegetable, leaves of root and tuber, group 2......... 10.0
Vegetable, legume, edible podded, subgroup 6A........ 0.30
Vegetable, root and tuber, group 1................... 0.10
Watercress........................................... 8.0
Wax jambu............................................ 0.3
------------------------------------------------------------------------
(b) Section 18 emergency exemptions. [Reserved]
(c) Tolerances with regional registrations. [Reserved]
(d) Indirect or inadvertant residues. [Reserved]
[FR Doc. E7-23579 Filed 12-4-07; 8:45 am]
BILLING CODE 6560-50-S