Saflufenacil; Pesticide Tolerances, 52215-52220 [2014-20947]
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Federal Register / Vol. 79, No. 170 / Wednesday, September 3, 2014 / Rules and Regulations
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Office of Pesticide Programs,
Environmental Protection Agency, 1200
Pennsylvania Ave. NW., Washington,
DC 20460–0001; main telephone
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number: (703) 305–7090; email address:
0.06 RDFRNotices@epa.gov.
15 SUPPLEMENTARY INFORMATION:
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million
Commodity
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Pea, field, hay .......................
Pea, field, vines ....................
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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. The following
list of North American Industrial
Classification System (NAICS) codes is
not intended to be exhaustive, but rather
provides a guide to help readers
determine whether this document
applies to them. Potentially affected
entities may include:
• Crop production (NAICS code 111).
• Animal production (NAICS code
112).
• Food manufacturing (NAICS code
311).
• Pesticide manufacturing (NAICS
code 32532).
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[FR Doc. 2014–20928 Filed 9–2–14; 8:45 am]
BILLING CODE 6560–50–P
ENVIRONMENTAL PROTECTION
AGENCY
40 CFR Part 180
[EPA–HQ–OPP–2013–0622 and EPA–HQ–
OPP–2014–0124; FRL–9912–91]
Saflufenacil; Pesticide Tolerances
Environmental Protection
Agency (EPA).
ACTION: Final rule.
AGENCY:
This regulation establishes
and revises tolerances for residues of
saflufenacil in or on multiple
commodities which are identified and
discussed later in this document. BASF
Corporation requested these tolerances
under the Federal Food, Drug, and
Cosmetic Act (FFDCA).
DATES: This regulation is effective
September 3, 2014. Objections and
requests for hearings must be received
on or before November 3, 2014, 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: The dockets for this action,
identified by docket identification (ID)
numbers EPA–HQ–OPP–2013–0622 and
EPA–HQ–OPP–2014–0124, are available
at https://www.regulations.gov or at the
Office of Pesticide Programs Regulatory
Public Docket (OPP Docket) in the
Environmental Protection Agency
Docket Center (EPA/DC), West William
Jefferson Clinton Bldg., Rm. 3334, 1301
Constitution Ave. NW., Washington, DC
20460–0001. The Public Reading Room
is open from 8:30 a.m. to 4:30 p.m.,
Monday through Friday, excluding legal
holidays. The telephone number for the
Public Reading Room is (202) 566–1744,
and the telephone number for the OPP
Docket is (703) 305–5805. Please review
the visitor instructions and additional
information about the docket available
at https://www.epa.gov/dockets.
FOR FURTHER INFORMATION CONTACT: Lois
Rossi, Registration Division (7505P),
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SUMMARY:
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I. General Information
B. How can I get electronic access to
other related information?
You may access a frequently updated
electronic version of EPA’s tolerance
regulations at 40 CFR part 180 through
the Government Printing Office’s e-CFR
site at https://www.ecfr.gov/cgi-bin/textidx?&c=ecfr&tpl=/ecfrbrowse/Title40/
40tab_02.tpl.
C. How can I file an objection or hearing
request?
Under FFDCA section 408(g), 21
U.S.C. 346a, 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 numbers EPA–HQ–
OPP–2013–0622 and EPA–HQ–OPP–
2014–0124 in the subject line on the
first page of your submission. All
objections and requests for a hearing
must be in writing, and must be
received by the Hearing Clerk on or
before November 3, 2014. Addresses for
mail and hand delivery of objections
and hearing requests are provided in 40
CFR 178.25(b).
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 (excluding
any Confidential Business Information
(CBI)) for inclusion in the public docket.
Information not marked confidential
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52215
pursuant to 40 CFR part 2 may be
disclosed publicly by EPA without prior
notice. Submit the non-CBI copy of your
objection or hearing request, identified
by docket ID number EPA–HQ–OPP–
2013–0622 and EPA–HQ–OPP–2014–
0124, by one of the following methods:
• Federal eRulemaking Portal: https://
www.regulations.gov. Follow the online
instructions for submitting comments.
Do not submit electronically any
information you consider to be CBI or
other information whose disclosure is
restricted by statute.
• Mail: OPP Docket, Environmental
Protection Agency Docket Center
(EPA/DC), (28221T), 1200 Pennsylvania
Ave. NW., Washington, DC 20460–0001.
• Hand Delivery: To make special
arrangements for hand delivery or
delivery of boxed information, please
follow the instructions at https://
www.epa.gov/dockets/contacts.html.
Additional instructions on
commenting or visiting the docket,
along with more information about
dockets generally, is available at
https://www.epa.gov/dockets.
II. Summary of Petitioned-for Tolerance
In the Federal Register of October 25,
2013 (78 FR 63938) (FRL–9901–96),
EPA issued a document pursuant to
FFDCA section 408(d)(3), 21 U.S.C.
346a(d)(3), announcing the filing of a
pesticide petition (PP 3F8192) by BASF
Corporation, 26 Davis Dr., P.O. Box
13528, Research Triangle Park, NC
27709–3528. The petition requested that
40 CFR 180.649 be amended by
establishing tolerances for residues of
the herbicide saflufenacil, 2-chloro-5[3,6-dihydro-3-methyl-2,6-dioxo-4(trifluoromethyl)-1(2H)-pyrimidinyl]-4fluoro-N-[[methyl(1-methylethyl)amino]
sulfonyl]benzamide, and its metabolites,
N-[2-chloro-5-(2,6-dioxo-4(trifluoromethyl)-3,6-dihydro-1(2H)pyrimidinyl)-4-fluorobenzoyl]-N′isopropylsulfamide and N-[4-chloro-2fluoro-5-({[(isopropylamino)sulfonyl
]amino}carbonyl)phenyl]urea,
calculated as the stoichiometric
equivalent of saflufenacil, in or on grass,
forage at 15 parts per million (ppm);
grass, hay at 20 ppm; grass, seed
screenings at 0.9 ppm; and grass, straw
at 1.5 ppm and revising the livestock
commodity tolerances for (cattle, goat,
horse, and sheep): Fat from 0.01 ppm to
0.05 ppm; liver from 2.5 ppm to 45
ppm; and meat byproducts, except liver
from 0.05 ppm to 0.5 ppm; hog, fat from
0.01 ppm to 0.05 ppm; hog, liver from
0.80 ppm to 45 ppm; and hog, meat
byproducts, except liver from 0.02 ppm
to 0.5 ppm.
The same Federal Register document
of October 25, 2013, also announced
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BASF Corporation’s filing of a pesticide
petition (PP 3F8185) that requested 40
CFR 180.649 be amended by revising
tolerances for saflufenacil and its
metabolites in or on barley, grain from
0.10 ppm to 1.0 ppm; barley, straw from
0.10 ppm to 15.0 ppm; barley, bran from
0.10 ppm to 1.53 ppm; wheat, grain
from 0.10 ppm to 0.6 ppm; and wheat,
straw from 0.10 ppm to 6.0 ppm,
included under the existing tolerances
for ‘‘Grain, cereal, group 15’’ and
‘‘Grain, cereal, forage, fodder and straw
group 16.’’ In addition, BASF
Corporation requested to amend the
existing commodity definition, ‘‘Grain,
cereal, forage, fodder and straw group
16’’ to ‘‘Grain, cereal, forage, fodder and
straw, group 16, except barley, rice and
wheat straw’’ as well as amend the
commodity definition, ‘‘Grain, cereal,
group 15’’ to ‘‘Grain, cereal, group 15,
except barley and wheat.’’
Finally, in the Federal Register of
February 25, 2014 (79 FR 10458) (FRL–
9906–77), EPA issued a document
pursuant to FFDCA section 408(d)(3), 21
U.S.C. 346a(d)(3), announcing the filing
of a pesticide petition (PP 4F8229) by
BASF Corporation. The petition
requested that 40 CFR 180.649 be
amended by establishing tolerances for
residues of the herbicide saflufenacil, 2chloro-5-[3,6-dihydro-3-methyl-2,6dioxo-4-(trifluoromethyl)-1(2H)pyrimidinyl]-4-fluoro-N-[[methyl(1methylethyl)amino]sulfonyl]benzamide,
and its metabolites, N-[2-chloro-5-(2,6dioxo-4-(trifluoromethyl)-3,6-dihydro1(2H)-pyrimidinyl)-4-fluorobenzoyl]-N′isopropylsulfamide and N-[4-chloro-2fluoro-5-({[(isopropylamino)sulfonyl]
amino}carbonyl)phenyl]urea, calculated
as the stoichiometric equivalent of
saflufenacil in or on olive at 0.03 ppm.
These documents referenced summaries
of the petitions prepared by BASF
Corporation, the petitioner, which are
available in the dockets, https://
www.regulations.gov. There were no
comments received in response to these
notices of filings.
Based upon review of the supporting
data, EPA has made modifications to the
proposed tolerances which include:
1. Rounding the proposed tolerance
for barley, bran.
2. Revising the commodity definition
for crop group 16.
3. Decreasing the proposed tolerances
for grass, seed screenings and grass,
straw.
4. Increasing the existing tolerance for
residues in or on grain, aspirated
fractions.
5. Making several changes to the
proposed livestock tolerances.
The reasons for these changes are
explained in Unit IV.C.
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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
of infants and children to the pesticide
chemical residue in establishing a
tolerance and to ‘‘ensure that there is a
reasonable certainty that no harm will
result to infants and children from
aggregate exposure to the pesticide
chemical residue. . . .’’
Consistent with FFDCA section
408(b)(2)(D), and the factors specified in
FFDCA section 408(b)(2)(D), 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 saflufenacil,
including exposure resulting from the
tolerances established by this action.
EPA’s assessment of exposures and risks
associated with saflufenacil 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. In the Federal
Register of February 21, 2014 (79 FR
9861) (FRL–9905–87), EPA published a
final rule establishing tolerances for
residues of the herbicide saflufenacil
and its metabolites in or on sugarcane,
fish, and shellfish commodities based
on EPA’s conclusion that aggregate
exposure to saflufenacil is safe for the
general population, including infants
and children. Since that rulemaking,
there have been no additional tolerance
actions for saflufenacil, nor has the
toxicity profile for saflufenacil changed.
Specific information on the studies
received and the nature of the adverse
effects caused by saflufenacil, as well as
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the no-observed-adverse-effect-level
(NOAEL) and the lowest-observedadverse-effect-level (LOAEL) from the
toxicity studies are discussed in that
rulemaking which can be found in the
docket under docket ID numbers EPA–
HQ–OPP–2012–0775 and EPA–HQ–
OPP–2013–0008.
B. Toxicological Points of Departure/
Levels of Concern
Once a pesticide’s toxicological
profile is determined, EPA identifies
toxicological points of departure (POD)
and levels of concern to use in
evaluating the risk posed by human
exposure to the pesticide. For hazards
that have a threshold below which there
is no appreciable risk, the toxicological
POD is used as the basis for derivation
of reference values for risk assessment.
PODs are developed based on a careful
analysis of the doses in each
toxicological study to determine the
dose at which the NOAEL and the
lowest dose at which the LOAEL are
identified. Uncertainty/safety factors
(UFs) are used in conjunction with the
POD to calculate a safe exposure level—
generally referred to as a populationadjusted dose (PAD) or a reference dose
(RfD)—and a safe margin of exposure
(MOE). For non-threshold risks, the
Agency assumes that any amount of
exposure will lead to some degree of
risk. Thus, the Agency estimates risk in
terms of the probability of an occurrence
of the adverse effect expected in a
lifetime. For more information on the
general principles EPA uses in risk
characterization and a complete
description of the risk assessment
process, see https://www.epa.gov/
pesticides/factsheets/riskassess.htm. A
summary of the toxicological endpoints
for saflufenacil used for human risk
assessment is discussed in Unit III.B. of
the February 21, 2014 Federal Register
final rule.
C. Exposure Assessment
1. Dietary exposure from food and
feed uses. In evaluating dietary
exposure to saflufenacil, EPA
considered exposure under the
petitioned-for tolerances as well as all
existing saflufenacil tolerances in 40
CFR 180.649. EPA assessed dietary
exposures from saflufenacil 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. Such effects were identified
for saflufenacil. In estimating acute
dietary exposure, EPA used food
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consumption information from the
United States Department of Agriculture
National Health and Nutrition
Examination Survey, What We Eat in
America, (USDA NHANES/WWEIA,
2003–2008). As to residue levels in
food, EPA assumed 100 percent crop
treated (PCT), Dietary Exposure
Evaluation Model (DEEM) 7.81 default
processing factors, and tolerance-level
or higher (i.e., tolerance levels adjusted
to take into account metabolite levels)
residues for all foods.
ii. Chronic exposure. In conducting
the chronic dietary exposure assessment
EPA used the food consumption data
from the USDA NHANES/WWEIA,
2003–2008. As to residue levels in food,
EPA made the same assumptions
(adjusted tolerance-level residues and
100 PCT) as in the acute dietary
exposure assessment.
iii. Cancer. As indicated in the
February 21, 2014 Federal Register final
rule preamble for saflufenacil, EPA has
concluded that saflufenacil does not
pose a cancer risk to humans. Therefore,
a dietary exposure assessment for the
purpose of assessing cancer risk is
unnecessary.
iv. Anticipated residue and PCT
information. EPA did not use
anticipated residue and/or PCT
information in the dietary assessment
for saflufenacil. Tolerance-level residues
(or higher) and 100 PCT were assumed
for all food commodities.
2. Dietary exposure from drinking
water. The Agency used screening level
water exposure models in the dietary
exposure analysis and risk assessment
for saflufenacil in drinking water. These
simulation models take into account
data on the physical, chemical, and fate/
transport characteristics of saflufenacil.
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 Tier 1 Rice Model and
Tier II Pesticide Root Zone Model
Ground Water (PRZM GW), the
estimated drinking water concentrations
(EDWCs) of saflufenacil for acute
exposures are estimated to be 133 parts
per billion (ppb) for surface water and
69.2 ppb for ground water. Chronic
exposures for non-cancer assessments
are estimated to be 120 ppb for surface
water and 51.5 ppb for ground water.
Modeled estimates of drinking water
concentrations were directly entered
into the dietary exposure model. For
acute dietary risk assessment, the water
concentration value of 133 ppb was
used to assess the contribution to
drinking water. For chronic dietary risk
assessment, the water concentration of
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value 120 ppb was used to assess the
contribution to drinking water.
3. From non-dietary exposure. The
term ‘‘residential exposure’’ is used in
this document to refer to nonoccupational, non-dietary exposure
(e.g., for lawn and garden pest control,
indoor pest control, termiticides, and
flea and tick control on pets).
Saflufenacil is not registered for any
specific use patterns that would result
in residential exposure.
4. Cumulative effects from substances
with a common mechanism of toxicity.
Section 408(b)(2)(D)(v) of FFDCA
requires that, when considering whether
to establish, modify, or revoke a
tolerance, the Agency consider
‘‘available information’’ concerning the
cumulative effects of a particular
pesticide’s residues and ‘‘other
substances that have a common
mechanism of toxicity.’’ EPA has not
found saflufenacil to share a common
mechanism of toxicity with any other
substances, and saflufenacil does not
appear to produce a toxic metabolite
produced by other substances. For the
purposes of this tolerance action,
therefore, EPA has assumed that
saflufenacil does not have a common
mechanism of toxicity with other
substances. For information regarding
EPA’s efforts to determine which
chemicals have a common mechanism
of toxicity and to evaluate the
cumulative effects of such chemicals,
see EPA’s Web site at https://
www.epa.gov/pesticides/cumulative.
D. Safety Factor for Infants and
Children
1. In general. Section 408(b)(2)(C) of
FFDCA provides that EPA shall apply
an additional tenfold (10X) margin of
safety 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
Food Quality Protection Act Safety
Factor (FQPA SF). In applying this
provision, EPA either retains the default
value of 10X, or uses a different
additional safety factor when reliable
data available to EPA support the choice
of a different factor.
2. Prenatal and postnatal sensitivity.
Increased fetal susceptibility was
observed in the developmental toxicity
studies in the rat and rabbit and in the
2-generation reproduction study in the
rat. Developmental effects (decreased
fetal body weights and increased
skeletal variations in rats and increased
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liver porphyrins in rabbits) occurred at
doses that were not maternally toxic in
the developmental studies, indicating
increased quantitative susceptibility. In
the 2-generation reproductive toxicity
study in rats, the reported offspring
effects were more severe than the
maternal effects at the same dose level,
indicating evidence for increased
qualitative susceptibility. An increased
number of stillborn pups, decreased
viability and lactation indices,
decreased pre-weaning body weight
and/or body-weight gain, and changes
in hematological parameters occurred at
the same dose level as maternal
decrements in food intake, body weight,
body-weight gain, and changes in
hematological parameters and organ
weights indicative of anemia.
3. Conclusion. EPA has determined
that reliable data show the safety of
infants and children would be
adequately protected if the FQPA SF
were reduced to 1X. That decision is
based on the following findings:
i. The toxicity database for
saflufenacil is complete.
ii. There is no indication that
saflufenacil is a neurotoxic chemical
and there is no need for a
developmental neurotoxicity study or
additional UFs to account for
neurotoxicity.
iii. The concern for increased
susceptibility following prenatal or
postnatal exposure is low because clear
NOAELs/LOAELs were established for
the developmental effects seen in rats
and rabbits as well as for the offspring
effects seen in the 2-generation
reproductive toxicity study. Further, the
dose-response relationship for the
effects of concern is also well
characterized and being used for
assessing risks. None of the effects in
the developmental or reproduction
studies were attributable to a single
exposure and, therefore, are not of
concern for acute risk assessment. The
chronic point of departure used for risk
assessment is protective of any
developmental and offspring effects
observed in these studies.
iv. There are no residual uncertainties
identified in the exposure databases.
The dietary food exposure assessments
were performed based on 100 PCT and
tolerance-level residues. EPA made
conservative (protective) assumptions in
the ground and surface water modeling
used to assess exposure to saflufenacil
in drinking water. These assessments
will not underestimate the exposure and
risks posed by saflufenacil.
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E. Aggregate Risks and Determination of
Safety
EPA determines whether acute and
chronic dietary pesticide exposures are
safe by comparing aggregate exposure
estimates to the acute PAD (aPAD) and
chronic PAD (cPAD). For linear cancer
risks, EPA calculates the lifetime
probability of acquiring cancer given the
estimated aggregate exposure. Short-,
intermediate-, and chronic-term risks
are evaluated by comparing the
estimated aggregate food, water, and
residential exposure to the appropriate
PODs to ensure that an adequate MOE
exists.
1. Acute risk. Using the exposure
assumptions discussed in this unit for
acute exposure, the acute dietary
exposure from food and water to
saflufenacil will occupy <1% of the
aPAD for infants less than 1-year old,
the population group receiving the
greatest exposure.
2. Chronic risk. Using the exposure
assumptions described in this unit for
chronic exposure, EPA has concluded
that chronic exposure to saflufenacil
from food and water will utilize 20% of
the cPAD for infants less than 1-year
old, the population group receiving the
greatest exposure. There are no
residential uses for saflufenacil.
3. Short and intermediate-term risk.
Short and intermediate-term aggregate
exposure takes into account short and
intermediate-term residential exposures
plus chronic exposure to food and water
(considered to be a background
exposure level). Because there is no
short or intermediate-term residential
exposure and chronic dietary exposure
has already been assessed under the
appropriately protective cPAD (which is
at least as protective as the POD used to
assess short-term risk), no further
assessment of short or intermediate-term
risk is necessary, and EPA relies on the
chronic dietary risk assessment for
evaluating short-term risk for
saflufenacil.
4. Aggregate cancer risk for U.S.
population. Based on the lack of
evidence of carcinogenicity in two
adequate rodent carcinogenicity studies,
saflufenacil is not expected to pose a
cancer risk to humans.
5. 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 saflufenacil
residues.
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IV. Other Considerations
A. Analytical Enforcement Methodology
Adequate enforcement methods
‘‘D0603/02’’ and ‘‘L0073/01’’ (liquid
chromatography/mass spectroscopy/
mass spectroscopy (LC–MS/MS)) are
available to enforce the tolerance
expression. These methods may be
requested from: Chief, Analytical
Chemistry Branch, Environmental
Science Center, 701 Mapes Rd., Ft.
Meade, MD 20755–5350; telephone
number: (410) 305–2905; email address:
residuemethods@epa.gov.
B. International Residue Limits
In making its tolerance decisions, EPA
seeks to harmonize U.S. tolerances with
international standards whenever
possible, consistent with U.S. food
safety standards and agricultural
practices. EPA considers the
international maximum residue limits
(MRLs) established by the Codex
Alimentarius Commission (Codex), as
required by FFDCA section 408(b)(4).
The Codex Alimentarius is a joint
United Nations Food and Agriculture
Organization/World Health
Organization food standards program,
and it is recognized as an international
food safety standards-setting
organization in trade agreements to
which the United States is a party. EPA
may establish a tolerance that is
different from a Codex MRL; however,
FFDCA section 408(b)(4) requires that
EPA explain the reasons for departing
from the Codex level.
There are MRLs established for
residues of saflufenacil, measuring the
levels of the parent only and not
residues of the metabolites, as follows:
0.01 ppm in or on cereal grains, which
includes barley, corn, and wheat; 0.05
ppm for maize fodder (dry), sorghum
straw and fodder, dry; 0.05 ppm for
barley straw and fodder, dry; 0.05 ppm
for wheat straw and fodder, dry; 0.01
mammalian fats (except milk fats),
which includes cattle, goat, hog, horse,
and sheep; and 0.3 edible offal
mammalian, which includes cattle, goat,
hog, horse, and sheep.
Harmonization between the Codex
MRLs for cereal grains and the U.S.
tolerances for barley, grain and wheat,
grain and between the Codex MRL for
barley straw and fodder, dry and the
U.S. tolerance for barley, straw and
between the Codex MRL for wheat straw
and fodder, dry and the U.S. tolerance
for wheat, straw is not possible as the
U.S. use pattern (harvest-aide/
burndown application) results in
significantly higher residues than the
Codex use pattern (pre-emergence
application). The higher residues
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translate into higher residues of
saflufenacil in animal byproducts than
are covered by the corresponding Codex
MRLs for livestock commodities under
the Codex use pattern; therefore, U.S.
tolerances for livestock commodities
cannot be harmonized with Codex
MRLs for corresponding livestock
commodities.
The U.S. tolerances for crop groups 15
and 16 are not harmonized with the
Codex MRLs for cereal grains and straw
and fodder because the compliance with
the Codex MRLs involve measurement
of residues of the parent only and not
the metabolites, whereas the U.S.
tolerance requires measurement of both,
in order to be harmonized with
Canadian tolerances.
C. Revisions to Petitioned-for Tolerances
EPA is making several revisions to the
petitioned-for tolerances. These include
the following. First, the petitioned value
for barley bran is being rounded from
1.53 ppm to 1.5 ppm to be consistent
with the current Organization for
Economic Cooperation and
Development (OECD) tolerancecalculation procedure. Second, the
commodity definition ‘‘Grain, cereal,
forage, fodder, and straw group 16
(except barley, wheat and rice straw)’’ is
being revised to ‘‘Grain, cereal, forage,
fodder and straw group 16 (except
barley and wheat straw)’’ as the new use
pattern (harvest aid/desiccant) was not
proposed for rice. Third, the petitioner
requested tolerance values for grass
straw and seed screenings were based
on data from trials in which the samples
were harvested at a significantly shorter
preharvest interval (PHI) than that listed
on the label. Additional residue data
reflecting the actual PHI listed on the
label showed lower residue levels;
therefore, the tolerance values for grass
straw and seed screenings are being
decreased. Fourth, the existing tolerance
of 10 ppm for residues in or on grain,
aspirated fractions is being increased to
50 ppm as a result of the new tolerances
for cereal grains and based on available
residues data. Finally, EPA is making
several revisions to the proposed
livestock tolerances which include:
1. Decreasing the proposed tolerances
for cattle, goat, sheep, hog and horse fat
from 0.05 ppm to 0.04 ppm and meat
byproducts (except liver) from 0.05 ppm
to 0.03 ppm.
2. Increasing the tolerances proposed
for cattle, goat, sheep and horse liver
from 45 ppm to 50 ppm.
3. Decreasing the tolerance proposed
for hog liver from 45 ppm to 2.0 ppm.
4. Establishing tolerances for cattle,
goat, sheep and horse meat at 0.02 ppm.
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5. Retaining the currently established
tolerances for hog, fat or hog, meat
byproducts (except liver), instead of
increasing them as requested.
The tolerances being set for residues
in livestock differ from the petitionedfor tolerances due to differences in
calculation methods of the maximum
reasonably balanced diets (MRBDs) with
the results of the ruminant feeding
study. It also appears that the petitioner
over-estimated residues in hog
commodities as a result of using the
cattle MRDB.
wreier-aviles on DSK5TPTVN1PROD with RULES
V. Conclusion
Therefore, tolerances are established
for residues of saflufenacil, including its
metabolites and degradates, as set forth
in the regulatory text. Compliance with
the plant tolerances is to be determined
by measuring the sum of saflufenacil, 2chloro-5-[3,6-dihydro-3-methyl-2,6dioxo-4-(trifluoromethyl)-1(2H)pyrimidinyl]-4-fluoro-N-[[methyl(1methylethyl)amino]sulfonyl]benzamide,
and its metabolites N-[2-chloro-5-(2,6dioxo-4-(trifluoromethyl)-3,6-dihydro1(2H)-pyrimidinyl)-4-fluorobenzoyl]-N’isopropylsulfamide and N-[4-chloro-2fluoro-5-({[(isopropylamino)
sulfonyl]amino}carbonyl)phenyl]urea,
calculated as the stoichiometric
equivalent of saflufenacil. Compliance
with the livestock tolerances is to be
determined by measuring only
saflufenacil, 2-chloro-5-[3,6-dioxo-4(trifluoromethyl)-3,6-dihydro-1(2H)pyrimidinyl)-4-fluoro-N-[[methyl(1methylethyl)amino]sulfonyl]benzamide.
VI. Statutory and Executive Order
Reviews
This final rule establishes tolerances
under FFDCA section 408(d) in
response to a petition submitted to the
Agency. The Office of Management and
Budget (OMB) has exempted these types
of actions from review under Executive
Order 12866, entitled ‘‘Regulatory
Planning and Review’’ (58 FR 51735,
October 4, 1993). Because this final rule
has been exempted from review under
Executive Order 12866, this final rule is
not subject to Executive Order 13211,
entitled ‘‘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
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14:42 Sep 02, 2014
Jkt 232001
‘‘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 FFDCA section 408(d), 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 FFDCA section 408(n)(4). As such,
the Agency has determined that this
action will not have a substantial direct
effect on States or tribal governments,
on the relationship between the national
government and the States or tribal
governments, or on the distribution of
power and responsibilities among the
various levels of government or between
the Federal Government and Indian
Tribes. Thus, the Agency has
determined that Executive Order 13132,
entitled ‘‘Federalism’’ (64 FR 43255,
August 10, 1999) and Executive Order
13175, entitled ‘‘Consultation and
Coordination with Indian Tribal
Governments’’ (65 FR 67249, November
9, 2000) do not apply to this final rule.
In addition, this final rule does not
impose any enforceable duty or contain
any unfunded mandate as described
under Title II of the Unfunded Mandates
Reform Act of 1995 (UMRA) (2 U.S.C.
1501 et seq.).
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) (15 U.S.C. 272 note).
VII. Congressional Review Act
Pursuant to the Congressional Review
Act (5 U.S.C. 801 et seq.), 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 the rule in the Federal
Register. This action is not a ‘‘major
rule’’ as defined by 5 U.S.C. 804(2).
and pests, Reporting and recordkeeping
requirements.
Dated: August 25, 2014.
Lois Rossi,
Director, Registration Division, Office of
Pesticide Programs.
Therefore, 40 CFR chapter I is
amended as follows:
PART 180—[AMENDED]
1. The authority citation for part 180
continues to read as follows:
■
Authority: 21 U.S.C. 321(q), 346a and 371.
2. In § 180.649:
a. Remove the commodities ‘‘Grain,
aspirated fractions,’’ ‘‘Grain, cereal,
forage, fodder and straw group 16,’’ and
‘‘Grain, cereal, group 15’’ in the table in
paragraph (a)(1).
■ b. Add alphabetically the following
commodities to the table in paragraph
(a)(1).
■ c. Revise the following commodities
in the table in paragraph (a)(2).
The amendments read as follows:
■
■
§ 180.649 Saflufenacil; tolerances for
residues.
(a) * * *
(1) * * *
Parts per
million
Commodity
*
*
*
Barley, bran ........................
Barley, grain .......................
Barley, straw .......................
*
*
1.5
1.0
15
*
*
*
Grain, aspirated grain fractions .................................
Grain, cereal, forage, fodder
and straw group 16 (except barley and wheat
straw) ..............................
Grain, cereal, group 15 (except barley and wheat
grain) ...............................
*
*
*
Grass,
Grass,
Grass,
Grass,
*
*
forage ......................
hay ..........................
seed screenings ......
straw .......................
*
*
15
20
0.15
0.15
*
*
*
Olive ....................................
*
*
0.03
*
*
*
Wheat, grain .......................
Wheat, straw .......................
*
*
0.60
6.0
*
*
*
(2) * * *
*
50
0.10
0.03
*
List of Subjects in 40 CFR Part 180
Environmental protection,
Administrative practice and procedure,
Agricultural commodities, Pesticides
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Fmt 4700
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Commodity
Cattle, fat ............................
E:\FR\FM\03SER1.SGM
03SER1
Parts per
million
0.04
52220
Federal Register / Vol. 79, No. 170 / Wednesday, September 3, 2014 / Rules and Regulations
Parts per
million
Commodity
Cattle,
Cattle,
Cattle,
cept
liver ..........................
meat ........................
meat byproducts, exliver ..........................
50
0.02
0.30
*
*
*
Goat, fat ..............................
Goat, liver ...........................
Goat, meat ..........................
Goat, meat byproducts, except liver ..........................
*
*
*
*
Hog, liver ............................
*
*
2.0
*
*
*
Horse, fat ............................
Horse, liver .........................
Horse, meat ........................
Horse, meat byproducts,
except liver ......................
*
*
0.04
50
0.02
*
*
*
Sheep, fat ...........................
Sheep, liver .........................
Sheep, meat .......................
Sheep, meat byproducts,
except liver ......................
*
*
*
*
*
*
0.04
50
0.02
0.30
0.30
*
0.04
50
0.02
0.30
*
[FR Doc. 2014–20947 Filed 9–2–14; 8:45 am]
BILLING CODE 6560–50–P
ENVIRONMENTAL PROTECTION
AGENCY
40 CFR Part 271
[EPA–R06–RCRA–2013–0624 FRL 9915–99–
Region 6]
Texas: Final Authorization of State
Hazardous Waste Management
Program Revision
Environmental Protection
Agency (EPA).
ACTION: Direct final rule.
AGENCY:
The State of Texas has
applied to the Environmental Protection
Agency (EPA) for Final authorization of
the changes to its hazardous waste
program under the Resource
Conservation and Recovery Act (RCRA).
EPA has determined that these changes
satisfy all requirements needed to
qualify for Final authorization, and is
authorizing the State’s changes through
this direct final action. The EPA is
publishing this rule to authorize the
changes without a prior proposal
because we believe this action is not
controversial and do not expect
comments that oppose it. Unless we
receive written comments which oppose
this authorization during the comment
period, the decision to authorize Texas’
changes to its hazardous waste program
wreier-aviles on DSK5TPTVN1PROD with RULES
SUMMARY:
VerDate Mar<15>2010
14:42 Sep 02, 2014
Jkt 232001
will take effect. If we receive comments
that oppose this action, we will publish
a document in the Federal Register
withdrawing this rule before it takes
effect, and a separate document in the
proposed rules section of this Federal
Register will serve as a proposal to
authorize the changes.
DATES: This final authorization will
become effective on November 3, 2014
unless the EPA receives adverse written
comment by October 3, 2014. If the EPA
receives such comment, it will publish
a timely withdrawal of this direct final
rule in the Federal Register and inform
the public that this authorization will
not take effect.
ADDRESSES: Submit your comments by
one of the following methods:
1. Federal eRulemaking Portal:
https://www.regulations.gov. Follow the
on-line instructions for submitting
comments.
2. Email: patterson.alima@epa.gov.
3. Mail: Alima Patterson, Region 6,
Regional Authorization Coordinator,
State/Tribal Oversight Section (6PD–O),
Multimedia Planning and Permitting
Division, EPA Region 6, 1445 Ross
Avenue, Dallas, Texas 75202–2733.
4. Hand Delivery or Courier. Deliver
your comments to Alima Patterson,
Region 6, Regional Authorization
Coordinator, State/Tribal Oversight
Section (6PD–O), Multimedia Planning
and Permitting Division, EPA Region 6,
1445 Ross Avenue, Dallas, Texas 75202–
2733.
Instructions: Do not submit
information that you consider to be CBI
or otherwise protected through
regulations.gov, or email. The Federal
regulations.gov Web site is an
‘‘anonymous access’’ system, which
means the EPA will not know your
identity or contact information unless
you provide it in the body of your
comment. If you send an email
comment directly to the EPA without
going through regulations.gov, your
email address will be automatically
captured and included as part of the
comment that is placed in the public
docket and made available on the
Internet. If you submit an electronic
comment, the EPA recommends that
you include your name and other
contact information in the body of your
comment and with any disk or CD–ROM
you submit. If the EPA cannot read your
comment due to technical difficulties
and cannot contact you for clarification,
the EPA may not be able to consider
your comment. Electronic files should
avoid the use of special characters, any
form of encryption, and be free of any
defects or viruses. You can view and
copy Texas’ application and associated
PO 00000
Frm 00056
Fmt 4700
Sfmt 4700
publicly available materials from 8:30
a.m. to 4 p.m. Monday through Friday
at the following locations: Texas
Commission on Environmental Quality,
(TCEQ) 12100 Park S. Circle, Austin
Texas 78753–3087, (512) 239–6079 and
EPA, Region 6, 1445 Ross Avenue,
Dallas, Texas 75202–2733, phone
number (214) 665–8533. Interested
persons wanting to examine these
documents should make an
appointment with the office at least two
weeks in advance.
FOR FURTHER INFORMATION CONTACT:
Alima Patterson, Region 6 Regional
Authorization Coordinator, State/Tribal
Oversight Section (6PD–O), Multimedia
Planning and Permitting Division, (214)
665–8533, EPA Region 1445 Ross
Avenue, Dallas, Texas 75202–2733, and
Email address patterson.alima@epa.gov.
SUPPLEMENTARY INFORMATION:
A. Why are revisions to State programs
necessary?
States which have received final
authorization from the EPA under RCRA
section 3006(b), 42 U.S.C. 6926(b), must
maintain a hazardous waste program
that is equivalent to, consistent with,
and no less stringent than the Federal
program. As the Federal program
changes, States must change their
programs and ask the EPA to authorize
the changes. Changes to State programs
may be necessary when Federal or State
statutory or regulatory authority is
modified or when certain other changes
occur. Most commonly, States must
change their programs because of
changes to the EPA’s regulations in 40
Code of Federal Regulations (CFR) parts
124, 260 through 268, 270, 273, and 279.
B. What decisions have we made in this
rule?
We conclude that the State of Texas’
application to revise its authorized
program meets all of the statutory and
regulatory requirements established by
RCRA. Therefore, we grant the State of
Texas Final Authorization to operate its
hazardous waste program with the
changes described in the authorization
application. The State of Texas has
responsibility for permitting treatment,
storage, and disposal facilities within its
borders (except in Indian Country) and
for carrying out the aspects of the RCRA
program described in its revised
program application, subject to the
limitations of the Hazardous and Solid
Waste Amendments of 1984 (HSWA).
New Federal requirements and
prohibitions imposed by Federal
regulations that the EPA promulgates
under the authority of HSWA take effect
in authorized States before they are
E:\FR\FM\03SER1.SGM
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Agencies
[Federal Register Volume 79, Number 170 (Wednesday, September 3, 2014)]
[Rules and Regulations]
[Pages 52215-52220]
From the Federal Register Online via the Government Printing Office [www.gpo.gov]
[FR Doc No: 2014-20947]
-----------------------------------------------------------------------
ENVIRONMENTAL PROTECTION AGENCY
40 CFR Part 180
[EPA-HQ-OPP-2013-0622 and EPA-HQ-OPP-2014-0124; FRL-9912-91]
Saflufenacil; Pesticide Tolerances
AGENCY: Environmental Protection Agency (EPA).
ACTION: Final rule.
-----------------------------------------------------------------------
SUMMARY: This regulation establishes and revises tolerances for
residues of saflufenacil in or on multiple commodities which are
identified and discussed later in this document. BASF Corporation
requested these tolerances under the Federal Food, Drug, and Cosmetic
Act (FFDCA).
DATES: This regulation is effective September 3, 2014. Objections and
requests for hearings must be received on or before November 3, 2014,
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: The dockets for this action, identified by docket
identification (ID) numbers EPA-HQ-OPP-2013-0622 and EPA-HQ-OPP-2014-
0124, are available at https://www.regulations.gov or at the Office of
Pesticide Programs Regulatory Public Docket (OPP Docket) in the
Environmental Protection Agency Docket Center (EPA/DC), West William
Jefferson Clinton Bldg., Rm. 3334, 1301 Constitution Ave. NW.,
Washington, DC 20460-0001. The Public Reading Room is open from 8:30
a.m. to 4:30 p.m., Monday through Friday, excluding legal holidays. The
telephone number for the Public Reading Room is (202) 566-1744, and the
telephone number for the OPP Docket is (703) 305-5805. Please review
the visitor instructions and additional information about the docket
available at https://www.epa.gov/dockets.
FOR FURTHER INFORMATION CONTACT: Lois Rossi, Registration Division
(7505P), Office of Pesticide Programs, Environmental Protection Agency,
1200 Pennsylvania Ave. NW., Washington, DC 20460-0001; main telephone
number: (703) 305-7090; email address: RDFRNotices@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.
The following list of North American Industrial Classification System
(NAICS) codes is not intended to be exhaustive, but rather provides a
guide to help readers determine whether this document applies to them.
Potentially affected entities may include:
Crop production (NAICS code 111).
Animal production (NAICS code 112).
Food manufacturing (NAICS code 311).
Pesticide manufacturing (NAICS code 32532).
B. How can I get electronic access to other related information?
You may access a frequently updated electronic version of EPA's
tolerance regulations at 40 CFR part 180 through the Government
Printing Office's e-CFR site at https://www.ecfr.gov/cgi-bin/text-
idx?&c=ecfr&tpl=/ecfrbrowse/Title40/40tab02.tpl.
C. How can I file an objection or hearing request?
Under FFDCA section 408(g), 21 U.S.C. 346a, 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 numbers EPA-HQ-OPP-2013-0622 and EPA-HQ-OPP-2014-0124 in the
subject line on the first page of your submission. All objections and
requests for a hearing must be in writing, and must be received by the
Hearing Clerk on or before November 3, 2014. Addresses for mail and
hand delivery of objections and hearing requests are provided in 40 CFR
178.25(b).
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 (excluding any Confidential Business Information (CBI)) for
inclusion in the public docket. Information not marked confidential
pursuant to 40 CFR part 2 may be disclosed publicly by EPA without
prior notice. Submit the non-CBI copy of your objection or hearing
request, identified by docket ID number EPA-HQ-OPP-2013-0622 and EPA-
HQ-OPP-2014-0124, by one of the following methods:
Federal eRulemaking Portal: https://www.regulations.gov.
Follow the online instructions for submitting comments. Do not submit
electronically any information you consider to be CBI or other
information whose disclosure is restricted by statute.
Mail: OPP Docket, Environmental Protection Agency Docket
Center (EPA/DC), (28221T), 1200 Pennsylvania Ave. NW., Washington, DC
20460-0001.
Hand Delivery: To make special arrangements for hand
delivery or delivery of boxed information, please follow the
instructions at https://www.epa.gov/dockets/contacts.html.
Additional instructions on commenting or visiting the docket, along
with more information about dockets generally, is available at https://www.epa.gov/dockets.
II. Summary of Petitioned-for Tolerance
In the Federal Register of October 25, 2013 (78 FR 63938) (FRL-
9901-96), EPA issued a document pursuant to FFDCA section 408(d)(3), 21
U.S.C. 346a(d)(3), announcing the filing of a pesticide petition (PP
3F8192) by BASF Corporation, 26 Davis Dr., P.O. Box 13528, Research
Triangle Park, NC 27709-3528. The petition requested that 40 CFR
180.649 be amended by establishing tolerances for residues of the
herbicide saflufenacil, 2-chloro-5-[3,6-dihydro-3-methyl-2,6-dioxo-4-
(trifluoromethyl)-1(2H)-pyrimidinyl]-4-fluoro-N-[[methyl(1-
methylethyl)amino]sulfonyl]benzamide, and its metabolites, N-[2-chloro-
5-(2,6-dioxo-4-(trifluoromethyl)-3,6-dihydro-1(2H)-pyrimidinyl)-4-
fluorobenzoyl]-N'-isopropylsulfamide and N-[4-chloro-2-fluoro-5-
({[(isopropylamino)sulfonyl]amino{time} carbonyl)phenyl]urea,
calculated as the stoichiometric equivalent of saflufenacil, in or on
grass, forage at 15 parts per million (ppm); grass, hay at 20 ppm;
grass, seed screenings at 0.9 ppm; and grass, straw at 1.5 ppm and
revising the livestock commodity tolerances for (cattle, goat, horse,
and sheep): Fat from 0.01 ppm to 0.05 ppm; liver from 2.5 ppm to 45
ppm; and meat byproducts, except liver from 0.05 ppm to 0.5 ppm; hog,
fat from 0.01 ppm to 0.05 ppm; hog, liver from 0.80 ppm to 45 ppm; and
hog, meat byproducts, except liver from 0.02 ppm to 0.5 ppm.
The same Federal Register document of October 25, 2013, also
announced
[[Page 52216]]
BASF Corporation's filing of a pesticide petition (PP 3F8185) that
requested 40 CFR 180.649 be amended by revising tolerances for
saflufenacil and its metabolites in or on barley, grain from 0.10 ppm
to 1.0 ppm; barley, straw from 0.10 ppm to 15.0 ppm; barley, bran from
0.10 ppm to 1.53 ppm; wheat, grain from 0.10 ppm to 0.6 ppm; and wheat,
straw from 0.10 ppm to 6.0 ppm, included under the existing tolerances
for ``Grain, cereal, group 15'' and ``Grain, cereal, forage, fodder and
straw group 16.'' In addition, BASF Corporation requested to amend the
existing commodity definition, ``Grain, cereal, forage, fodder and
straw group 16'' to ``Grain, cereal, forage, fodder and straw, group
16, except barley, rice and wheat straw'' as well as amend the
commodity definition, ``Grain, cereal, group 15'' to ``Grain, cereal,
group 15, except barley and wheat.''
Finally, in the Federal Register of February 25, 2014 (79 FR 10458)
(FRL-9906-77), EPA issued a document pursuant to FFDCA section
408(d)(3), 21 U.S.C. 346a(d)(3), announcing the filing of a pesticide
petition (PP 4F8229) by BASF Corporation. The petition requested that
40 CFR 180.649 be amended by establishing tolerances for residues of
the herbicide saflufenacil, 2-chloro-5-[3,6-dihydro-3-methyl-2,6-dioxo-
4-(trifluoromethyl)-1(2H)-pyrimidinyl]-4-fluoro-N-[[methyl(1-
methylethyl)amino]sulfonyl]benzamide, and its metabolites, N-[2-chloro-
5-(2,6-dioxo-4-(trifluoromethyl)-3,6-dihydro-1(2H)-pyrimidinyl)-4-
fluorobenzoyl]-N'-isopropylsulfamide and N-[4-chloro-2-fluoro-5-
({[(isopropylamino)sulfonyl]amino{time} carbonyl)phenyl]urea,
calculated as the stoichiometric equivalent of saflufenacil in or on
olive at 0.03 ppm. These documents referenced summaries of the
petitions prepared by BASF Corporation, the petitioner, which are
available in the dockets, https://www.regulations.gov. There were no
comments received in response to these notices of filings.
Based upon review of the supporting data, EPA has made
modifications to the proposed tolerances which include:
1. Rounding the proposed tolerance for barley, bran.
2. Revising the commodity definition for crop group 16.
3. Decreasing the proposed tolerances for grass, seed screenings
and grass, straw.
4. Increasing the existing tolerance for residues in or on grain,
aspirated fractions.
5. Making several changes to the proposed livestock tolerances.
The reasons for these changes are explained in Unit IV.C.
III. Aggregate Risk Assessment and Determination of Safety
Section 408(b)(2)(A)(i) of FFDCA allows EPA to establish a
tolerance (the legal limit for a pesticide chemical residue in or on a
food) only if EPA determines that the tolerance is ``safe.'' Section
408(b)(2)(A)(ii) of FFDCA defines ``safe'' to mean that ``there is a
reasonable certainty that no harm will result from aggregate exposure
to the pesticide chemical residue, including all anticipated dietary
exposures and all other exposures for which there is reliable
information.'' This includes exposure through drinking water and in
residential settings, but does not include occupational exposure.
Section 408(b)(2)(C) of FFDCA requires EPA to give special
consideration to exposure of infants and children to the pesticide
chemical residue in establishing a tolerance and to ``ensure that there
is a reasonable certainty that no harm will result to infants and
children from aggregate exposure to the pesticide chemical residue. . .
.''
Consistent with FFDCA section 408(b)(2)(D), and the factors
specified in FFDCA section 408(b)(2)(D), 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 saflufenacil, including
exposure resulting from the tolerances established by this action.
EPA's assessment of exposures and risks associated with saflufenacil
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. In the Federal Register of February 21, 2014 (79 FR 9861)
(FRL-9905-87), EPA published a final rule establishing tolerances for
residues of the herbicide saflufenacil and its metabolites in or on
sugarcane, fish, and shellfish commodities based on EPA's conclusion
that aggregate exposure to saflufenacil is safe for the general
population, including infants and children. Since that rulemaking,
there have been no additional tolerance actions for saflufenacil, nor
has the toxicity profile for saflufenacil changed. Specific information
on the studies received and the nature of the adverse effects caused by
saflufenacil, 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 that rulemaking which can be found in the
docket under docket ID numbers EPA-HQ-OPP-2012-0775 and EPA-HQ-OPP-
2013-0008.
B. Toxicological Points of Departure/Levels of Concern
Once a pesticide's toxicological profile is determined, EPA
identifies toxicological points of departure (POD) and levels of
concern to use in evaluating the risk posed by human exposure to the
pesticide. For hazards that have a threshold below which there is no
appreciable risk, the toxicological POD is used as the basis for
derivation of reference values for risk assessment. PODs are developed
based on a careful analysis of the doses in each toxicological study to
determine the dose at which the NOAEL and the lowest dose at which the
LOAEL are identified. Uncertainty/safety factors (UFs) are used in
conjunction with the POD to calculate a safe exposure level--generally
referred to as a population-adjusted dose (PAD) or a reference dose
(RfD)--and a safe margin of exposure (MOE). For non-threshold risks,
the Agency assumes that any amount of exposure will lead to some degree
of risk. Thus, the Agency estimates risk in terms of the probability of
an occurrence of the adverse effect expected in a lifetime. For more
information on the general principles EPA uses in risk characterization
and a complete description of the risk assessment process, see https://www.epa.gov/pesticides/factsheets/riskassess.htm. A summary of the
toxicological endpoints for saflufenacil used for human risk assessment
is discussed in Unit III.B. of the February 21, 2014 Federal Register
final rule.
C. Exposure Assessment
1. Dietary exposure from food and feed uses. In evaluating dietary
exposure to saflufenacil, EPA considered exposure under the petitioned-
for tolerances as well as all existing saflufenacil tolerances in 40
CFR 180.649. EPA assessed dietary exposures from saflufenacil 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. Such effects were identified
for saflufenacil. In estimating acute dietary exposure, EPA used food
[[Page 52217]]
consumption information from the United States Department of
Agriculture National Health and Nutrition Examination Survey, What We
Eat in America, (USDA NHANES/WWEIA, 2003-2008). As to residue levels in
food, EPA assumed 100 percent crop treated (PCT), Dietary Exposure
Evaluation Model (DEEM) 7.81 default processing factors, and tolerance-
level or higher (i.e., tolerance levels adjusted to take into account
metabolite levels) residues for all foods.
ii. Chronic exposure. In conducting the chronic dietary exposure
assessment EPA used the food consumption data from the USDA NHANES/
WWEIA, 2003-2008. As to residue levels in food, EPA made the same
assumptions (adjusted tolerance-level residues and 100 PCT) as in the
acute dietary exposure assessment.
iii. Cancer. As indicated in the February 21, 2014 Federal Register
final rule preamble for saflufenacil, EPA has concluded that
saflufenacil does not pose a cancer risk to humans. Therefore, a
dietary exposure assessment for the purpose of assessing cancer risk is
unnecessary.
iv. Anticipated residue and PCT information. EPA did not use
anticipated residue and/or PCT information in the dietary assessment
for saflufenacil. Tolerance-level residues (or higher) and 100 PCT were
assumed for all food commodities.
2. Dietary exposure from drinking water. The Agency used screening
level water exposure models in the dietary exposure analysis and risk
assessment for saflufenacil in drinking water. These simulation models
take into account data on the physical, chemical, and fate/transport
characteristics of saflufenacil. 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 Tier 1 Rice Model and Tier II Pesticide Root Zone
Model Ground Water (PRZM GW), the estimated drinking water
concentrations (EDWCs) of saflufenacil for acute exposures are
estimated to be 133 parts per billion (ppb) for surface water and 69.2
ppb for ground water. Chronic exposures for non-cancer assessments are
estimated to be 120 ppb for surface water and 51.5 ppb for ground
water.
Modeled estimates of drinking water concentrations were directly
entered into the dietary exposure model. For acute dietary risk
assessment, the water concentration value of 133 ppb was used to assess
the contribution to drinking water. For chronic dietary risk
assessment, the water concentration of value 120 ppb was used to assess
the contribution to drinking water.
3. From non-dietary exposure. The term ``residential exposure'' is
used in this document to refer to non-occupational, non-dietary
exposure (e.g., for lawn and garden pest control, indoor pest control,
termiticides, and flea and tick control on pets).
Saflufenacil is not registered for any specific use patterns that
would result in residential exposure.
4. Cumulative effects from substances with a common mechanism of
toxicity. Section 408(b)(2)(D)(v) of FFDCA requires that, when
considering whether to establish, modify, or revoke a tolerance, the
Agency consider ``available information'' concerning the cumulative
effects of a particular pesticide's residues and ``other substances
that have a common mechanism of toxicity.'' EPA has not found
saflufenacil to share a common mechanism of toxicity with any other
substances, and saflufenacil does not appear to produce a toxic
metabolite produced by other substances. For the purposes of this
tolerance action, therefore, EPA has assumed that saflufenacil does not
have a common mechanism of toxicity with other substances. For
information regarding EPA's efforts to determine which chemicals have a
common mechanism of toxicity and to evaluate the cumulative effects of
such chemicals, see EPA's Web site at https://www.epa.gov/pesticides/cumulative.
D. Safety Factor for Infants and Children
1. In general. Section 408(b)(2)(C) of FFDCA provides that EPA
shall apply an additional tenfold (10X) margin of safety 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 Food Quality
Protection Act Safety Factor (FQPA SF). In applying this provision, EPA
either retains the default value of 10X, or uses a different additional
safety factor when reliable data available to EPA support the choice of
a different factor.
2. Prenatal and postnatal sensitivity. Increased fetal
susceptibility was observed in the developmental toxicity studies in
the rat and rabbit and in the 2-generation reproduction study in the
rat. Developmental effects (decreased fetal body weights and increased
skeletal variations in rats and increased liver porphyrins in rabbits)
occurred at doses that were not maternally toxic in the developmental
studies, indicating increased quantitative susceptibility. In the 2-
generation reproductive toxicity study in rats, the reported offspring
effects were more severe than the maternal effects at the same dose
level, indicating evidence for increased qualitative susceptibility. An
increased number of stillborn pups, decreased viability and lactation
indices, decreased pre-weaning body weight and/or body-weight gain, and
changes in hematological parameters occurred at the same dose level as
maternal decrements in food intake, body weight, body-weight gain, and
changes in hematological parameters and organ weights indicative of
anemia.
3. Conclusion. EPA has determined that reliable data show the
safety of infants and children would be adequately protected if the
FQPA SF were reduced to 1X. That decision is based on the following
findings:
i. The toxicity database for saflufenacil is complete.
ii. There is no indication that saflufenacil is a neurotoxic
chemical and there is no need for a developmental neurotoxicity study
or additional UFs to account for neurotoxicity.
iii. The concern for increased susceptibility following prenatal or
postnatal exposure is low because clear NOAELs/LOAELs were established
for the developmental effects seen in rats and rabbits as well as for
the offspring effects seen in the 2-generation reproductive toxicity
study. Further, the dose-response relationship for the effects of
concern is also well characterized and being used for assessing risks.
None of the effects in the developmental or reproduction studies were
attributable to a single exposure and, therefore, are not of concern
for acute risk assessment. The chronic point of departure used for risk
assessment is protective of any developmental and offspring effects
observed in these studies.
iv. There are no residual uncertainties identified in the exposure
databases. The dietary food exposure assessments were performed based
on 100 PCT and tolerance-level residues. EPA made conservative
(protective) assumptions in the ground and surface water modeling used
to assess exposure to saflufenacil in drinking water. These assessments
will not underestimate the exposure and risks posed by saflufenacil.
[[Page 52218]]
E. Aggregate Risks and Determination of Safety
EPA determines whether acute and chronic dietary pesticide
exposures are safe by comparing aggregate exposure estimates to the
acute PAD (aPAD) and chronic PAD (cPAD). For linear cancer risks, EPA
calculates the lifetime probability of acquiring cancer given the
estimated aggregate exposure. Short-, intermediate-, and chronic-term
risks are evaluated by comparing the estimated aggregate food, water,
and residential exposure to the appropriate PODs to ensure that an
adequate MOE exists.
1. Acute risk. Using the exposure assumptions discussed in this
unit for acute exposure, the acute dietary exposure from food and water
to saflufenacil will occupy <1% of the aPAD for infants less than 1-
year old, the population group receiving the greatest exposure.
2. Chronic risk. Using the exposure assumptions described in this
unit for chronic exposure, EPA has concluded that chronic exposure to
saflufenacil from food and water will utilize 20% of the cPAD for
infants less than 1-year old, the population group receiving the
greatest exposure. There are no residential uses for saflufenacil.
3. Short and intermediate-term risk. Short and intermediate-term
aggregate exposure takes into account short and intermediate-term
residential exposures plus chronic exposure to food and water
(considered to be a background exposure level). Because there is no
short or intermediate-term residential exposure and chronic dietary
exposure has already been assessed under the appropriately protective
cPAD (which is at least as protective as the POD used to assess short-
term risk), no further assessment of short or intermediate-term risk is
necessary, and EPA relies on the chronic dietary risk assessment for
evaluating short-term risk for saflufenacil.
4. Aggregate cancer risk for U.S. population. Based on the lack of
evidence of carcinogenicity in two adequate rodent carcinogenicity
studies, saflufenacil is not expected to pose a cancer risk to humans.
5. 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 saflufenacil residues.
IV. Other Considerations
A. Analytical Enforcement Methodology
Adequate enforcement methods ``D0603/02'' and ``L0073/01'' (liquid
chromatography/mass spectroscopy/mass spectroscopy (LC-MS/MS)) are
available to enforce the tolerance expression. These methods may be
requested from: Chief, Analytical Chemistry Branch, Environmental
Science Center, 701 Mapes Rd., Ft. Meade, MD 20755-5350; telephone
number: (410) 305-2905; email address: residuemethods@epa.gov.
B. International Residue Limits
In making its tolerance decisions, EPA seeks to harmonize U.S.
tolerances with international standards whenever possible, consistent
with U.S. food safety standards and agricultural practices. EPA
considers the international maximum residue limits (MRLs) established
by the Codex Alimentarius Commission (Codex), as required by FFDCA
section 408(b)(4). The Codex Alimentarius is a joint United Nations
Food and Agriculture Organization/World Health Organization food
standards program, and it is recognized as an international food safety
standards-setting organization in trade agreements to which the United
States is a party. EPA may establish a tolerance that is different from
a Codex MRL; however, FFDCA section 408(b)(4) requires that EPA explain
the reasons for departing from the Codex level.
There are MRLs established for residues of saflufenacil, measuring
the levels of the parent only and not residues of the metabolites, as
follows: 0.01 ppm in or on cereal grains, which includes barley, corn,
and wheat; 0.05 ppm for maize fodder (dry), sorghum straw and fodder,
dry; 0.05 ppm for barley straw and fodder, dry; 0.05 ppm for wheat
straw and fodder, dry; 0.01 mammalian fats (except milk fats), which
includes cattle, goat, hog, horse, and sheep; and 0.3 edible offal
mammalian, which includes cattle, goat, hog, horse, and sheep.
Harmonization between the Codex MRLs for cereal grains and the U.S.
tolerances for barley, grain and wheat, grain and between the Codex MRL
for barley straw and fodder, dry and the U.S. tolerance for barley,
straw and between the Codex MRL for wheat straw and fodder, dry and the
U.S. tolerance for wheat, straw is not possible as the U.S. use pattern
(harvest-aide/burndown application) results in significantly higher
residues than the Codex use pattern (pre-emergence application). The
higher residues translate into higher residues of saflufenacil in
animal byproducts than are covered by the corresponding Codex MRLs for
livestock commodities under the Codex use pattern; therefore, U.S.
tolerances for livestock commodities cannot be harmonized with Codex
MRLs for corresponding livestock commodities.
The U.S. tolerances for crop groups 15 and 16 are not harmonized
with the Codex MRLs for cereal grains and straw and fodder because the
compliance with the Codex MRLs involve measurement of residues of the
parent only and not the metabolites, whereas the U.S. tolerance
requires measurement of both, in order to be harmonized with Canadian
tolerances.
C. Revisions to Petitioned-for Tolerances
EPA is making several revisions to the petitioned-for tolerances.
These include the following. First, the petitioned value for barley
bran is being rounded from 1.53 ppm to 1.5 ppm to be consistent with
the current Organization for Economic Cooperation and Development
(OECD) tolerance-calculation procedure. Second, the commodity
definition ``Grain, cereal, forage, fodder, and straw group 16 (except
barley, wheat and rice straw)'' is being revised to ``Grain, cereal,
forage, fodder and straw group 16 (except barley and wheat straw)'' as
the new use pattern (harvest aid/desiccant) was not proposed for rice.
Third, the petitioner requested tolerance values for grass straw and
seed screenings were based on data from trials in which the samples
were harvested at a significantly shorter preharvest interval (PHI)
than that listed on the label. Additional residue data reflecting the
actual PHI listed on the label showed lower residue levels; therefore,
the tolerance values for grass straw and seed screenings are being
decreased. Fourth, the existing tolerance of 10 ppm for residues in or
on grain, aspirated fractions is being increased to 50 ppm as a result
of the new tolerances for cereal grains and based on available residues
data. Finally, EPA is making several revisions to the proposed
livestock tolerances which include:
1. Decreasing the proposed tolerances for cattle, goat, sheep, hog
and horse fat from 0.05 ppm to 0.04 ppm and meat byproducts (except
liver) from 0.05 ppm to 0.03 ppm.
2. Increasing the tolerances proposed for cattle, goat, sheep and
horse liver from 45 ppm to 50 ppm.
3. Decreasing the tolerance proposed for hog liver from 45 ppm to
2.0 ppm.
4. Establishing tolerances for cattle, goat, sheep and horse meat
at 0.02 ppm.
[[Page 52219]]
5. Retaining the currently established tolerances for hog, fat or
hog, meat byproducts (except liver), instead of increasing them as
requested.
The tolerances being set for residues in livestock differ from the
petitioned-for tolerances due to differences in calculation methods of
the maximum reasonably balanced diets (MRBDs) with the results of the
ruminant feeding study. It also appears that the petitioner over-
estimated residues in hog commodities as a result of using the cattle
MRDB.
V. Conclusion
Therefore, tolerances are established for residues of saflufenacil,
including its metabolites and degradates, as set forth in the
regulatory text. Compliance with the plant tolerances is to be
determined by measuring the sum of saflufenacil, 2-chloro-5-[3,6-
dihydro-3-methyl-2,6-dioxo-4-(trifluoromethyl)-1(2H)-pyrimidinyl]-4-
fluoro-N-[[methyl(1-methylethyl)amino]sulfonyl]benzamide, and its
metabolites N-[2-chloro-5-(2,6-dioxo-4-(trifluoromethyl)-3,6-dihydro-
1(2H)-pyrimidinyl)-4-fluorobenzoyl]-N'-isopropylsulfamide and N-[4-
chloro-2-fluoro-5-
({[(isopropylamino)sulfonyl]amino{time} carbonyl)phenyl]urea,
calculated as the stoichiometric equivalent of saflufenacil. Compliance
with the livestock tolerances is to be determined by measuring only
saflufenacil, 2-chloro-5-[3,6-dioxo-4-(trifluoromethyl)-3,6-dihydro-
1(2H)-pyrimidinyl)-4-fluoro-N-[[methyl(1-
methylethyl)amino]sulfonyl]benzamide.
VI. Statutory and Executive Order Reviews
This final rule establishes tolerances under FFDCA section 408(d)
in response to a petition submitted to the Agency. The Office of
Management and Budget (OMB) has exempted these types of actions from
review under Executive Order 12866, entitled ``Regulatory Planning and
Review'' (58 FR 51735, October 4, 1993). Because this final rule has
been exempted from review under Executive Order 12866, this final rule
is not subject to Executive Order 13211, entitled ``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 FFDCA section 408(d), 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 FFDCA section 408(n)(4). As such, the Agency has determined that
this action will not have a substantial direct effect on States or
tribal governments, on the relationship between the national government
and the States or tribal governments, or on the distribution of power
and responsibilities among the various levels of government or between
the Federal Government and Indian Tribes. Thus, the Agency has
determined that Executive Order 13132, entitled ``Federalism'' (64 FR
43255, August 10, 1999) and Executive Order 13175, entitled
``Consultation and Coordination with Indian Tribal Governments'' (65 FR
67249, November 9, 2000) do not apply to this final rule. In addition,
this final rule does not impose any enforceable duty or contain any
unfunded mandate as described under Title II of the Unfunded Mandates
Reform Act of 1995 (UMRA) (2 U.S.C. 1501 et seq.).
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) (15 U.S.C. 272 note).
VII. Congressional Review Act
Pursuant to the Congressional Review Act (5 U.S.C. 801 et seq.),
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
the rule in the Federal Register. This action is not a ``major rule''
as defined by 5 U.S.C. 804(2).
List of Subjects in 40 CFR Part 180
Environmental protection, Administrative practice and procedure,
Agricultural commodities, Pesticides and pests, Reporting and
recordkeeping requirements.
Dated: August 25, 2014.
Lois Rossi,
Director, Registration Division, Office of Pesticide Programs.
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. In Sec. 180.649:
0
a. Remove the commodities ``Grain, aspirated fractions,'' ``Grain,
cereal, forage, fodder and straw group 16,'' and ``Grain, cereal, group
15'' in the table in paragraph (a)(1).
0
b. Add alphabetically the following commodities to the table in
paragraph (a)(1).
0
c. Revise the following commodities in the table in paragraph (a)(2).
The amendments read as follows:
Sec. 180.649 Saflufenacil; tolerances for residues.
(a) * * *
(1) * * *
------------------------------------------------------------------------
Parts per
Commodity million
------------------------------------------------------------------------
* * * * *
Barley, bran............................................ 1.5
Barley, grain........................................... 1.0
Barley, straw........................................... 15
* * * * *
Grain, aspirated grain fractions........................ 50
Grain, cereal, forage, fodder and straw group 16 (except 0.10
barley and wheat straw)................................
Grain, cereal, group 15 (except barley and wheat grain). 0.03
* * * * *
Grass, forage........................................... 15
Grass, hay.............................................. 20
Grass, seed screenings.................................. 0.15
Grass, straw............................................ 0.15
* * * * *
Olive................................................... 0.03
* * * * *
Wheat, grain............................................ 0.60
Wheat, straw............................................ 6.0
------------------------------------------------------------------------
* * * * *
(2) * * *
------------------------------------------------------------------------
Parts per
Commodity million
------------------------------------------------------------------------
Cattle, fat............................................. 0.04
[[Page 52220]]
Cattle, liver........................................... 50
Cattle, meat............................................ 0.02
Cattle, meat byproducts, except liver................... 0.30
* * * * *
Goat, fat............................................... 0.04
Goat, liver............................................. 50
Goat, meat.............................................. 0.02
Goat, meat byproducts, except liver..................... 0.30
* * * * *
Hog, liver.............................................. 2.0
* * * * *
Horse, fat.............................................. 0.04
Horse, liver............................................ 50
Horse, meat............................................. 0.02
Horse, meat byproducts, except liver.................... 0.30
* * * * *
Sheep, fat.............................................. 0.04
Sheep, liver............................................ 50
Sheep, meat............................................. 0.02
Sheep, meat byproducts, except liver.................... 0.30
------------------------------------------------------------------------
* * * * *
[FR Doc. 2014-20947 Filed 9-2-14; 8:45 am]
BILLING CODE 6560-50-P