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EPA-APPROVED OHIO NONREGULATORY AND QUASI-REGULATORY PROVISIONS—Continued
Applicable geographical or
non-attainment area
Title
*
Ozone (8-Hour,
2015).
State date
*
*
Columbus
(Delaware,
Fairfield,
Franklin, and Licking Counties.
*
*
EPA approval
*
4/23/2019
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8/21/2019, [insert Federal
Register citation].
*
*
Authority: 42 U.S.C. 7401, et seq.
PART 81—DESIGNATION OF AREAS
FOR AIR QUALITY PLANNING
PURPOSES
4. Section 81.336 is amended by
revising the entry for Columbus, OH in
the table entitled ‘‘Ohio-2015 8-Hour
■
3. The authority citation for part 81
continues to read as follows:
■
Comments
*
*
*
*
Ozone NAAQS [Primary and
Secondary]’’ to read as follows:
§ 81.336
*
Ohio.
*
*
*
*
OHIO—2015 8-HOUR OZONE NAAQS
[Primary and secondary]
Designation
Classification
Designated area 1
Date 2
*
*
*
Columbus, OH: .....................................................
Delaware County
Fairfield County
Franklin County
Licking County
*
*
8/21/2019
*
Date 2
Type
*
Attainment.
*
Type
*
*
*
*
*
*
1 Includes
any Indian country in each county or area, unless otherwise specified. EPA is not determining the boundaries of any area of Indian
country in this table, including any area of Indian country located in the larger designation area. The inclusion of any Indian country in the designation area is not a determination that the state has regulatory authority under the Clean Air Act for such Indian country.
2 This date is August 3, 2018, unless otherwise noted.
*
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[FR Doc. 2019–17795 Filed 8–20–19; 8:45 am]
BILLING CODE 6560–50–P
ENVIRONMENTAL PROTECTION
AGENCY
40 CFR Part 180
[EPA–HQ–OPP–2018–0201; FRL–9997–14]
C1-C4 Linear and Branched Chain Alkyl
D-Glucitol Dianhydro Alkyl Ethers;
Exemption From the Requirement of a
Tolerance
Environmental Protection
Agency (EPA).
ACTION: Final rule.
AGENCY:
This regulation establishes
exemptions from the requirement of a
tolerance for residues of pesticide inert
ingredients within the C1-C4 linear and
branched chain alkyl d-glucitol
dianhydro alkyl ethers (AD–GDAE)
cluster. These exemptions are being
established with the following terms:
When used as an inert ingredient
(solvent, co-solvent, viscosity modifier
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SUMMARY:
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and adjuvant) in pesticide formulations
applied to growing crops and raw
agricultural commodities after harvest,
on animals, and in antimicrobial
formulations applied to food-contact
surfaces in public-eating places, dairyprocessing equipment, and foodprocessing equipment, and utensils, and
in antimicrobial formulations used for
dairy processing equipment, and foodprocessing equipment and utensils.
Exponent, Inc., on behalf of Croda, Inc.,
submitted a petition to EPA under the
Federal Food, Drug, and Cosmetic Act
(FFDCA), requesting establishment of an
exemption from the requirement of a
tolerance. This regulation eliminates the
need to establish a maximum
permissible level for residues of C1-C4
linear and branched chain alkyl dglucitol dianhydro alkyl ethers cluster
when used in accordance with the terms
of these exemptions.
This regulation is effective
August 21, 2019. Objections and
requests for hearings must be received
on or before October 21, 2019, and must
be filed in accordance with the
instructions provided in 40 CFR part
DATES:
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178 (see also Unit I.C. of the
SUPPLEMENTARY INFORMATION).
The docket for this action,
identified by docket identification (ID)
number EPA–HQ–OPP–2018–0201, is
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.
ADDRESSES:
FOR FURTHER INFORMATION CONTACT:
Michael L. Goodis, Registration Division
(7505P), Office of Pesticide Programs,
Environmental Protection Agency, 1200
Pennsylvania Ave. NW, Washington, DC
20460–0001; main telephone number:
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(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 40 CFR part 180
through the Government Publishing
Office’s e-CFR site at https://
www.ecfr.gov/cgi-bin/textidx?&c=ecfr&tpl=/ecfrbrowse/Title40/
40tab_02.tpl.
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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 number EPA–HQ–
OPP–2018–0201 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 October 21, 2019. 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–
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2018–0201, 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. Petition for Exemption
In the Federal Register of October 18,
2018 (83 FR 52787) (FRL–9984–21),
EPA issued a document pursuant to
FFDCA section 408, 21 U.S.C. 346a,
announcing the filing of a pesticide
petition (PP IN–11109) by Exponent,
Inc. (1150 Connecticut Ave, Suite 1100,
NW, Washington, DC 20036), on behalf
of Croda, Inc. (315 Cherry Lane New
Castle, DE 19720). The petition
requested that 40 CFR be amended by
establishing exemptions from the
requirement of a tolerance for residues
of C1–C4 linear and branched chain
alkyl d-glucitol dianhydro alkyl ethers
(C1–C4 Linear and Branched Chain AD–
GDAE) cluster—d-glucitol, 1,4:3,6dianhydro-2,5-di-O-methyl-(CAS Reg.
No. 5306–85–4); d-glucitol, 1,4:3,6dianhydro-2,5-di-O-ethyl- (CAS Reg. No.
30915–81–2); d-glucitol, 1,4:3,6dianhydro-2,5-di-O-propyl) (CAS Reg.
No. 107644–13–3); d-glucitol, 1,4:3,6dianhydro-2,5-bis-O-(1-methylethyl),(iso-propyl diether) (CAS Reg. No.
103594–41–8); d-glucitol, 1,4:3,6dianhydro-2,5-di-O-butyl- (CAS Reg.
No. 103594–42–9); d-glucitol, 1,4:3,6dianhydro-2,5-di-O-(1-methylpropyl)-,
(CAS Reg. No. not assigned); and dglucitol, 1,4:3,6-dianhydro-2,5-di-O-(2methylpropyl)-, (CAS Reg. No. not
assigned) when used as an inert
ingredient (solvent, co-solvent, viscosity
modifier and adjuvant) in pesticide
formulations applied to growing crops
and raw agricultural commodities after
harvest under 40 CFR 180.910, applied
in or on animals under 40 CFR 180.930,
in antimicrobial formulations used in
food-contact surfaces in public-eating
places, dairy-processing equipment, and
food-processing equipment and utensils
under 40 CFR 180.940(a) and in
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antimicrobial formulations used for
dairy-processing equipment, and foodprocessing equipment and utensils
under 40 CFR 180.940(b). That
document referenced a summary of the
petition prepared by Exponent, Inc. on
behalf of Croda, Inc., the petitioner,
which is available in the docket, https://
www.regulations.gov. Although one
comment was submitted in response to
the relating to notice of filing regarding
the use of pesticides generally, it was
not specific to tolerances or this
rulemaking.
III. Inert Ingredient Definition
Inert ingredients are all ingredients
that are not active ingredients as defined
in 40 CFR 153.125 and include, but are
not limited to, the following types of
ingredients (except when they have a
pesticidal efficacy of their own):
Solvents such as alcohols and
hydrocarbons; surfactants such as
polyoxyethylene polymers and fatty
acids; carriers such as clay and
diatomaceous earth; thickeners such as
carrageenan and modified cellulose;
wetting, spreading, and dispersing
agents; propellants in aerosol
dispensers; microencapsulating agents;
and emulsifiers. The term ‘‘inert’’ is not
intended to imply nontoxicity; the
ingredient may or may not be
chemically active. Generally, EPA has
exempted inert ingredients from the
requirement of a tolerance based on the
low toxicity of the individual inert
ingredients.
IV. Aggregate Risk Assessment and
Determination of Safety
Section 408(c)(2)(A)(i) of FFDCA
allows EPA to establish an exemption
from the requirement for 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. . . .’’
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EPA establishes exemptions from the
requirement of a tolerance only in those
cases where it can be clearly
demonstrated that the risks from
aggregate exposure to pesticide
chemical residues under reasonably
foreseeable circumstances will pose no
appreciable risks to human health. In
order to determine the risks from
aggregate exposure to pesticide inert
ingredients, the Agency considers the
toxicity of the inert in conjunction with
possible exposure to residues of the
inert ingredient through food, drinking
water, and through other exposures that
occur as a result of pesticide use in
residential settings. If EPA is able to
determine that a finite tolerance is not
necessary to ensure that there is a
reasonable certainty that no harm will
result from aggregate exposure to the
inert ingredient, an exemption from the
requirement of a tolerance may be
established.
Consistent with FFDCA section
408(c)(2)(A), and the factors specified in
FFDCA section 408(c)(2)(B), 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 C1-C4 linear and
branched chain alkyl d-glucitol
dianhydro alkyl ethers cluster including
exposure resulting from the exemption
established by this action. EPA’s
assessment of exposures and risks
associated with C1-C4 linear and
branched chain alkyl d-glucitol
dianhydro alkyl ethers cluster follows.
A. Toxicological Profile
EPA has evaluated the available
toxicity data and considered their
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 C1-C4 linear and branched chain
alkyl d-glucitol dianhydro alkyl ethers
cluster as well as the no-observedadverse-effect-level (NOAEL) and the
lowest-observed-adverse-effect-level
(LOAEL) from the toxicity studies are
discussed in this unit.
The seven compounds included in the
cluster are C1-C4 linear and branched
chain glucitol, 1,4:3,6-dianhydro ether
congeners of isosorbide, which is
described as a fused ring furo[3,2b]furan, d-glucitol heterocycle. These
chemicals are similar in structure and
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are expected to be similar in regard to
toxicity profile. Therefore, d-glucitol,
1,4:3,6-dianhydro-2,5-di-O-methyl- was
selected as a suitable analogue to
represent toxicity due to exposure to the
seven compounds included in the
cluster and all toxicological studies
were conducted with d-glucitol, 1,4:3,6dianhydro-2,5-di-O-methyl-.
The acute oral and dermal toxicities
are low in rats and rabbits, respectively.
C1-C4 linear and branched chain alkyl dglucitol dianhydro alkyl ethers are not
irritating to the skin or eyes in the
rabbit. Acute inhalation and
sensitization studies are not available
for review.
New Zealand white rabbits exposed
for 8 days via gavage to doses as high
as 300 mg/kg/day of d-glucitol, 1,4:3,6dianhydro-2,5-di-O-methyl- do not
exhibit adverse effects. No adverse
effects are observed up to 375 mg/kg/
day in rats following 13 weeks of
exposure via gavage to d-glucitol,
1,4:3,6-dianhydro-2,5-di-O-methyl-.
Conversely, adverse effects are observed
in the dog following 13 weeks of
exposure via capsule to d-glucitol,
1,4:3,6-dianhydro-2,5-di-O-methyl-.
Decreased mean body weight, body
weight gain, food consumption, changes
in clinical biochemistry, lower levels of
red blood cells (RBCs), hemoglobin and
hematocrit and decreased relative liver
weights are observed in dogs at 700 mg/
kg/day. The no-observed-adverse-effect
level (NOAEL) is 100 mg/kg/day.
No fetal susceptibility is observed in
the developmental toxicity studies in
rats and rabbits. Developmental studies
with d-glucitol, 1,4:3,6-dianhydro-2,5di-O-methyl-in the rat and rabbit show
no maternal or developmental adverse
effects up to 375 and 300 mg/kg/day,
respectively, the highest doses tested.
No reproduction toxicity studies are
available for review, however, no
evidence of toxicity to reproductive
organs is observed in the 13-week oral
toxicity studies in the rat or dog up to
375 and 700 mg/kg/day, respectively.
The Ames test and chromosomal
aberrations assay in human
lymphocytes are negative. Therefore, dglucitol, 1,4:3,6-dianhydro-2,5-di-Omethyl- is not considered mutagenic.
D-glucitol, 1,4:3,6-dianhydro-2,5-diO-methyl- is not expected to be
carcinogenic based on a Derek Nexus
structural alert analysis. No structural
alerts for carcinogenicity or
mutagenicity are indicated in the
analysis.
Neurotoxicity and immunotoxicity
studies are not available for review.
However, no evidence of neurotoxicity
and immunotoxicity is observed in the
submitted studies.
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Metabolism studies are not available
for the C1-C4 linear and branched chain
alkyl d-glucitol dianhydro alkyl ethers
cluster. However, based on the classical
metabolic pathways for the alkyl and
aryl etherases, it is expected that the C1C4 linear and branched chain alkyl dglucitol dianhydro alkyl ethers cluster
would be metabolized to monoethers,
isosorbide (the common and major
metabolite), and sorbitol.
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 no adverse effects are
observed (the NOAEL) and the lowest
dose at which adverse effects of concern
are identified (the LOAEL). Uncertainty/
safety factors 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.
The 13-week oral toxicity study in
dogs is selected for the chronic dietary
exposure scenario as well as
intermediate-term incidental oral,
dermal and inhalation exposure
scenarios. The NOAEL is 100 mg/kg/
day, and the LOAEL is 700 mg/kg/day
based on decreased mean body weight,
body weight gain and food
consumption, changes in clinical
biochemistry, lower levels of RBCs,
hemoglobin and hematocrit and
decreased relative liver weights. This
represents the lowest NOAEL in the
database in the most sensitive species.
The developmental studies in rats and
rabbits are selected for short-term
exposure scenarios. These studies are
considered co-critical, the NOAEL is
300 mg/kg/day, the highest dose tested.
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The standard inter- and intra-species
uncertainty factors of 10x are applied; as
discussed below in Unit IV.D., the
Agency applied a 1x Food Quality
Protection Act (FQPA) Safety Factor
(SF). The default factor of 100% is
applied for the dermal absorption rate
and the inhalation absorption rate.
C. Exposure Assessment
1. Dietary exposure from food and
feed uses. In evaluating dietary
exposure to C1-C4 linear and branched
chain alkyl d-glucitol dianhydro alkyl
ethers cluster, EPA considered exposure
under the proposed exemption from the
requirement of a tolerance. EPA
assessed dietary exposures from C1-C4
linear and branched chain alkyl dglucitol dianhydro alkyl ethers cluster
in food as follows:
No adverse effects attributable to a
single exposure of endpoint was
identified for d-glucitol, 1,4:3,6dianhydro-2,5-di-O-methyl-; therefore,
an acute dietary exposure assessment
was not conducted.
In conducting the chronic dietary
exposure assessment using the Dietary
Exposure Evaluation Model DEEM–
FCIDTM, Version 3.16, EPA used food
consumption information from the U.S.
Department of Agriculture’s (USDA’s)
2003–2008 National Health and
Nutrition Examination Survey, What We
Eat in America (NHANES/WWEIA). As
to residue levels in food, no residue data
were submitted for d-glucitol, 1,4:3,6dianhydro-2,5-di-O-methyl-. In the
absence of specific residue data, EPA
has developed an approach which uses
surrogate information to derive upper
bound exposure estimates for the
subject inert ingredient. Upper bound
exposure estimates are based on the
highest tolerance for a given commodity
from a list of high use insecticides,
herbicides, and fungicides. A complete
description of the general approach
taken to assess inert ingredient risks in
the absence of residue data is contained
in the memorandum entitled ‘‘Alkyl
Amines Polyalkoxylates (Cluster 4):
Acute and Chronic Aggregate (Food and
Drinking Water) Dietary Exposure and
Risk Assessments for the Inerts,’’
(D361707, S. Piper, 2/25/09) and can be
found at https://www.regulations.gov in
docket ID number EPA–HQ–OPP–2008–
0738.
In the dietary exposure assessment,
the Agency assumed that the residue
level of the inert ingredient would be no
higher than the highest tolerance for a
given commodity. Implicit in this
assumption is that there would be
similar rates of degradation (if any)
between the active and inert ingredient
and that the concentration of inert
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ingredient in the scenarios leading to
these highest levels of tolerances would
be no higher than the concentration of
the active ingredient.
The Agency believes the assumptions
used to estimate dietary exposures lead
to an extremely conservative assessment
of dietary risk due to a series of
compounded conservatisms. First,
assuming that the level of residue for an
inert ingredient is equal to the level of
residue for the active ingredient will
overstate exposure. The concentrations
of active ingredient in agricultural
products are generally at least 50
percent of the product and often can be
much higher. Further, pesticide
products rarely have a single inert
ingredient; rather there is generally a
combination of different inert
ingredients used which additionally
reduces the concentration of any single
inert ingredient in the pesticide product
in relation to that of the active
ingredient.
Second, the conservatism of this
methodology is compounded by EPA’s
decision to assume that, for each
commodity, the active ingredient which
will serve as a guide to the potential
level of inert ingredient residues is the
active ingredient with the highest
tolerance level. This assumption
overstates residue values because it
would be highly unlikely, given the
high number of inert ingredients, that a
single inert ingredient or class of
ingredients would be present at the
level of the active ingredient in the
highest tolerance for every commodity.
Finally, a third compounding
conservatism is EPA’s assumption that
all foods contain residues of the inert
ingredient at the highest tolerance level.
In other words, EPA assumed 100
percent of all foods are treated with the
inert ingredient at the rate and manner
necessary to produce the highest residue
legally possible for an active ingredient.
In summary, EPA chose a very
conservative method for estimating
what level of inert residue could be on
food, then used this methodology to
choose the highest possible residue that
could be found on food and assumed
that all food contained this residue. No
consideration was given to potential
degradation between harvest and
consumption even though monitoring
data shows that tolerance level residues
are typically one to two orders of
magnitude higher than actual residues
in food when distributed in commerce.
Accordingly, although sufficient
information to quantify actual residue
levels in food is not available, the
compounding of these conservative
assumptions will lead to a significant
exaggeration of actual exposures. EPA
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does not believe that this approach
underestimates exposure in the absence
of residue data.
To assess dietary exposure due to its
use in antimicrobial products, EPA
calculated the daily dietary dose (DDD)
and the estimated daily intake (EDI) as
described in the Food Drug
Administration (FDA) model. The
assessment considered: Application
rates, residual solution or quantity of
solution remaining on the treated
surface without rinsing with potable
water, surface area of the treated surface
which comes into contact with food,
pesticide migration fraction, and body
weight. These assumptions are based on
FDA guidelines (2003). Dietary
exposures due to antimicrobial uses are
aggregated with the aforementioned
dietary exposures.
2. Dietary exposure from drinking
water. For the purpose of the screeninglevel dietary risk assessment to support
this request for an exemption from the
requirement of a tolerance for C1-C4
linear and branched chain alkyl dglucitol dianhydro alkyl ethers, a
conservative drinking water
concentration value of 100 ppb based on
screening-level modeling was used to
assess the contribution to drinking
water for the chronic dietary risk
assessments for parent compound.
These values were directly entered into
the dietary exposure model.
3. From non-dietary exposure. The
term ‘‘residential exposure’’ is used in
this document to refer to nonoccupational, non-dietary exposure
(e.g., textiles (clothing and diapers),
carpets, swimming pools, and hard
surface disinfection on walls, floors,
tables).
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). D-glucitol,
1,4:3,6-dianhydro-2,5-di-O-methyl- may
be used as an inert ingredient in
pesticide products that are registered for
specific uses that may result in
residential exposure. A conservative
residential exposure and risk
assessments were completed for
pesticide products containing d-glucitol,
1,4:3,6-dianhydro-2,5-di-O-methyl- as
inert ingredients. The Agency assessed
pesticide products containing d-glucitol,
1,4:3,6-dianhydro-2,5-di-O-methylusing exposure scenarios (treated lawns,
mopping, wiping and aerosol spray) to
represent conservative residential
handler exposure. Further details of this
residential exposure and risk analysis
can be found at https://
www.regulations.gov in the
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memorandum entitled: ‘‘JITF Inert
Ingredients. Residential and
Occupational Exposure Assessment
Algorithms and Assumptions Appendix
for the Human Health Risk Assessments
to Support Proposed Exemption from
the Requirement of a Tolerance When
Used as Inert Ingredients in Pesticide
Formulations,’’ (D364751, 5/7/09,
Lloyd/LaMay in docket ID number
EPA–HQ–OPP–2008–0710. D-glucitol,
1,4:3,6-dianhydro-2,5-di-O-methyl- is
also present in some anti-acne and antiaging topically applied pharmaceuticals
products. The typical use levels of dglucitol, 1,4:3,6-dianhydro-2,5-di-Omethyl- in these products are limited to
less than 5.44% to 15% weight/weight
(w/w). These products are used
sparingly and applied selectively to
limited areas of the skin.
The Agency does not have sufficient
data to quantitatively assess exposures
to d-glucitol, 1,4:3,6-dianhydro-2,5-diO-methyl- that result from these nonpesticidal uses. However, the Agency
believes the assessments of exposures
due to pesticide uses are protective of
these non-pesticidal uses. Based on the
available data on the typical reported
concentration ranges of d-glucitol,
1,4:3,6-dianhydro-2,5-di-O-methyltopically applied pharmaceuticals as
well as the specific use and limited
exposures resulting from such uses, the
Agency anticipates that exposures to dglucitol, 1,4:3,6-dianhydro-2,5-di-Omethyl- that might result from anti-acne
and anti-aging topically applied
pharmaceutical products uses are likely
to be markedly less than the
conservatively-estimated exposures
resulting from pesticide use. Therefore,
the Agency believes that any
contribution to the estimated pesticide
exposure resulting from topically
applied pharmaceuticals products is
likely to be insignificant in comparison
to the estimates for exposure from
pesticide use and these exposures have
not been aggregated with other nonresidential exposures.
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 C1-C4 linear and
branched chain alkyl d-glucitol
dianhydro alkyl ethers cluster to share
a common mechanism of toxicity with
any other substances, and C1-C4 linear
and branched chain alkyl d-glucitol
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dianhydro alkyl ethers cluster does not
appear to produce a toxic metabolite
produced by other substances. For the
purposes of this tolerance action,
therefore, EPA has assumed that C1-C4
linear and branched chain alkyl dglucitol dianhydro alkyl ethers cluster
does not have a common mechanism of
toxicity with other substances. For
information regarding EPA’s efforts to
determine which chemicals have a
common mechanism of toxicity and to
evaluate the cumulative effects of such
chemicals, see EPA’s website at https://
www.epa.gov/pesticides/cumulative.
D. Safety Factor for Infants and
Children
1. In general. Section 408(b)(2)(C) of
FFDCA provides that EPA shall apply
an additional tenfold (10X) margin of
safety 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 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.
The Agency has concluded that there
is reliable data to determine that infants
and children will be safe if the FQPA SF
of 10x is reduced to 1x for the chronic
dietary assessment for the following
reasons. The toxicity database for C1–C4
linear and branched chain alkyl dglucitol dianhydro alkyl ethers cluster
contains subchronic, developmental and
mutagenicity studies. There is no
indication of immunotoxicity or
neurotoxicity in the available studies;
therefore, there is no need to require an
immunotoxicity or neurotoxicity study.
Fetal susceptibility is not observed in
developmental toxicity studies in the rat
and rabbit. No maternal or
developmental toxicity is observed in
either study up to 300 mg/kg/day. A
reproduction toxicity is not available;
however, reproduction parameters were
not affected in the submitted studies at
doses as high as 375 and 700 mg/kg/day
in the rat and dog, respectively. Based
on the adequacy of the toxicity database,
the conservative nature of the exposure
assessment and the lack of concern for
prenatal and postnatal sensitivity, the
Agency has concluded that there is
reliable data to determine that infants
and children will be safe if the FQPA SF
of 10x is reduced to 1x.
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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. An acute aggregate risk
assessment takes into account acute
exposure estimates from dietary
consumption of food and drinking
water. No adverse effect resulting from
a single oral exposure was identified
and no acute dietary endpoint was
selected. Therefore, C1-C4 linear and
branched chain alkyl d-glucitol
dianhydro alkyl ethers cluster is 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 chronic exposure to C1-C4 linear
and branched chain alkyl d-glucitol
dianhydro alkyl ethers cluster from food
and water will utilize 70.6% of the
cPAD for children 1 to 2 years old, the
population group receiving the greatest
exposure.
3. Short-term risk. Short-term
aggregate exposure takes into account
short-term residential exposure plus
chronic exposure to food and water
(considered to be a background
exposure level).
C1-C4 linear and branched chain alkyl
d-glucitol dianhydro alkyl ethers cluster
is currently used as an inert ingredient
in pesticide products that are registered
for uses that could result in short-term
residential exposure, and the Agency
has determined that it is appropriate to
aggregate chronic exposure through food
and water with short-term residential
exposures to C1-C4 linear and branched
chain alkyl d-glucitol dianhydro alkyl
ethers cluster.
Using the exposure assumptions
described in this unit for short-term
exposures, EPA has concluded the
combined short-term food, water, and
residential exposures result in aggregate
MOEs of 148 for adult males and
females. Adult residential exposure
combines high-end dermal and
inhalation handler exposure from
indoor hard surface, aerosol spray with
a high-end post application dermal
exposure from contact with treated
lawns. The combined short-term
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Federal Register / Vol. 84, No. 162 / Wednesday, August 21, 2019 / Rules and Regulations
aggregated food, water, and residential
pesticide exposures result in an
aggregate MOE of 122 for children.
Children’s residential exposure includes
total exposures associated with contact
with treated surfaces (dermal and handto-mouth exposures). Because EPA’s
level of concern for C1-C4 linear and
branched chain alkyl d-glucitol
dianhydro alkyl ethers cluster is an
MOE of less than 100, these MOEs are
not of concern.
4. Intermediate-term risk.
Intermediate-term aggregate exposure
takes into account intermediate-term
residential exposure plus chronic
exposure to food and water (considered
to be a background exposure level).
C1-C4 linear and branched chain alkyl
d-glucitol dianhydro alkyl ethers cluster
is currently used as an inert ingredient
in pesticide products that are registered
for uses that could result in
intermediate-term residential exposure,
and the Agency has determined that it
is appropriate to aggregate chronic
exposure through food and water with
intermediate-term residential exposures
to C1-C4 linear and branched chain alkyl
d-glucitol dianhydro alkyl ethers
cluster.
Using the exposure assumptions
described in this unit for intermediateterm exposures, EPA has concluded that
the combined intermediate-term food,
water, and residential exposures result
in aggregate MOEs of 434 for adult
males and females. Adult residential
exposure includes high end post
application dermal exposure from
contact with treated lawns. The
combined intermediate-term aggregated
food, water, and residential exposures
result in an aggregate MOE of 125 for
children. Children’s residential
exposure includes total exposures
associated with contact with treated
surfaces (dermal and hand-to-mouth
exposures). Because EPA’s level of
concern for C1-C4 linear and branched
chain alkyl d-glucitol dianhydro alkyl
ethers cluster is an MOE of less than
100, these MOEs are not of concern.
5. Aggregate cancer risk for U.S.
population. Based on a DEREK
structural alert analysis, the lack of
mutagenicity, and the lack of specific
organ toxicity in the chronic toxicity
study, C1-C4 linear and branched chain
alkyl d-glucitol dianhydro alkyl ethers
cluster is not expected to pose a cancer
risk to humans.
6. Determination of safety. Based on
these risk assessments, EPA concludes
that there is a reasonable certainty that
no harm will result to the general
population, or to infants and children
from aggregate exposure to C1-C4 linear
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16:52 Aug 20, 2019
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and branched chain alkyl d-glucitol
dianhydro alkyl ethers cluster residues.
V. Other Considerations
Analytical Enforcement Methodology
An analytical method is not required
for enforcement purposes since the
Agency is establishing an exemption
from the requirement of a tolerance
without any numerical limitation.
VI. Conclusions
Therefore, exemptions from the
requirement of a tolerance are
established for residues of the following
seven compounds within the C1-C4
linear and branched chain alkyl dglucitol dianhydro alkyl ethers (AD–
GDAE) cluster: (1) d-glucitol, 1,4:3,6dianhydro-2,5-di-O-methyl- (CAS Reg.
No. 5306–85–4); (2) d-glucitol, 1,4:3,6dianhydro-2,5-di-O-ethyl- (CAS Reg. No.
30915–81–2); (3) d-glucitol, 1,4:3,6dianhydro-2,5-di-O-propyl) (CAS Reg.
No.107644–13–3); (4) d-glucitol, 1,4:3,6dianhydro-2,5-bis-O-(1-methylethyl),(iso-propyl diether) (CAS Reg. No.
103594–41–8); (5) d-glucitol, 1,4:3,6dianhydro-2,5-di-O-butyl- (CAS Reg.
No. 103594–42–9); (6) d-glucitol,
1,4:3,6-dianhydro-2,5-di-O-(1methylpropyl)-, (CAS Reg. No. not
assigned); and (7) d-glucitol, 1,4:3,6dianhydro-2,5-di-O-(2-methylpropyl)-,
(CAS Reg. No. not assigned) when used
as an inert ingredient (solvent, cosolvent, viscosity modifier and
adjuvant) in pesticide formulations
applied to growing crops and raw
agricultural commodities after harvest
under 40 CFR 180.910; applied in or on
animals under 40 CFR 180.930; when
used in antimicrobial formulations
applied to food-contact surfaces in
public-eating places, dairy-processing
equipment, and food-processing
equipment and utensils under 40 CFR
180.940(a) limited to 500 ppm; and in
antimicrobial formulations used for
dairy-processing equipment, and foodprocessing equipment and utensils
under 40 CFR 180.940(b) limited to
1,000 ppm.
VII. Statutory and Executive Order
Reviews
This action establishes a tolerance
exemption 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 action has been exempted from
review under Executive Order 12866,
this action is not subject to Executive
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43515
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),
nor is it considered a regulatory action
under Executive Order 13771, entitled
‘‘Reducing Regulations and Controlling
Regulatory Costs’’ (82 FR 9339, February
3, 2017). This action 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 action 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 action. In addition, this action
does not impose any enforceable duty or
contain any unfunded mandate as
described under Title II of the Unfunded
Mandates Reform Act (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
(NTTAA) (15 U.S.C. 272 note).
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Federal Register / Vol. 84, No. 162 / Wednesday, August 21, 2019 / Rules and Regulations
VIII. Congressional Review Act
List of Subjects in 40 CFR Part 180
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).
Environmental protection,
Administrative practice and procedure,
Agricultural commodities, Pesticides
and pests, Reporting and recordkeeping
requirements.
PART 180—[AMENDED]
Dated: August 8, 2019.
Michael Goodis,
Director, Registration Division, Office of
Pesticide Programs.
Therefore, 40 CFR chapter I is
amended as follows:
*
3. In § 180.930, add alphabetically the
following inert ingredients to the table
to read as follows:
■
*
*
4. In § 180.940, add alphabetically the
following inert ingredients to the tables
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*
Uses
*
*
*
*
*
*
*
Limits
*
*
in paragraphs (a) and (b) to read as
follows:
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Uses
*
*
*
........................................ solvent, co-solvent, viscosity
modifier, and adjuvant.
*
Sfmt 4700
*
§ 180. 940 Tolerance exemptions for active
and inert ingredients for use in
antimicrobial formulations (Food-contact
surface sanitizing solutions).
*
VerDate Sep<11>2014
*
§ 180.930 Inert ingredients applied to
animals; exemptions from the requirement
of a tolerance.
*
■
*
*
*
*
*
*
D-glucitol, 1,4:3,6-dianhydro-2,5-di-O-methyl-(CAS Reg. No. 5306–85–4); D-glucitol,
1,4:3,6-dianhydro-2,5-di-O-ethyl- (CAS Reg. No. 30915–81–2); D-glucitol, 1,4:3,6dianhydro-2,5-di-O-propyl) (CAS Reg. No.107644–13–3); D-glucitol, 1,4:3,6dianhydro-2,5-bis-O-(1-methylethyl)-,(iso-propyl diether) (CAS Reg. No. 103594–41–
8); D-glucitol, 1,4:3,6-dianhydro-2,5-di-O-butyl- (CAS Reg. No. 103594–42–9); D-glucitol, 1,4:3,6-dianhydro-2,5-di-O-(1-methylpropyl)-, (CAS Reg. No. not assigned);
and D-glucitol, 1,4:3,6-dianhydro-2,5-di-O-(2-methylpropyl)-, (CAS Reg. No. not assigned).
*
*
*
*
*
........................................ solvent, co-solvent, viscosity
modifier, and adjuvant.
Inert ingredients
*
2. In § 180.910, add alphabetically the
following inert ingredients to the table
to read as follows:
■
Limits
*
*
*
*
D-glucitol, 1,4:3,6-dianhydro-2,5-di-O-methyl- (CAS Reg. No. 5306–85–4); D-glucitol,
1,4:3,6-dianhydro-2,5-di-O-ethyl- (CAS Reg. No. 30915–81–2); D-glucitol, 1,4:3,6dianhydro-2,5-di-O-propyl) (CAS Reg. No.107644–13–3); D-glucitol, 1,4:3,6dianhydro-2,5-bis-O-(1-methylethyl)-,(iso-propyl diether) (CAS Reg. No. 103594–41–
8); D-glucitol, 1,4:3,6-dianhydro-2,5-di-O-butyl- (CAS Reg. No. 103594–42–9); D-glucitol, 1,4:3,6-dianhydro-2,5-di-O-(1-methylpropyl)-, (CAS Reg. No. not assigned);
and D-glucitol, 1,4:3,6-dianhydro-2,5-di-O-(2-methylpropyl)-, (CAS Reg. No. not assigned).
*
Authority: 21 U.S.C. 321(q), 346a and 371.
§ 180.910 Inert ingredients used pre- and
post-harvest; exemptions from the
requirement of a tolerance.
Inert ingredients
*
1. The authority citation for part 180
continues to read as follows:
■
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*
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Federal Register / Vol. 84, No. 162 / Wednesday, August 21, 2019 / Rules and Regulations
(a) * * *
Pesticide chemical
CAS Reg. No.
*
*
*
*
C1-C4 linear and branched chain alkyl d-glucitol dianhydro alkyl ethers cluster ..........
*
*
5306–85–4; 30915–81–2;
107644–13–3; 103594–
41–8; 103594–42–9.
None ...................................
None ...................................
D-glucitol, 1,4:3,6-dianhydro-2,5-di-O-(1-methylpropyl)-, ..............................................
D-glucitol, 1,4:3,6-dianhydro-2,5-di-O-(2-methylpropyl)-, (CAS Reg. No. not assigned).
*
*
*
*
*
Limits
*
When ready for use, the
end-use concentration is
not to exceed 500 ppm.
*
*
(b) * * *
Pesticide chemical
CAS Reg. No.
*
*
*
*
C1-C4 linear and branched chain alkyl d-glucitol dianhydro alkyl ethers cluster ..............
D-glucitol, 1,4:3,6-dianhydro-2,5-di-O-(1-methylpropyl)-, ..................................................
D-glucitol, 1,4:3,6-dianhydro-2,5-di-O-(2-methylpropyl)-, (CAS Reg. No. not assigned)
*
*
*
*
*
*
*
*
BILLING CODE 6560–50–P
ENVIRONMENTAL PROTECTION
AGENCY
40 CFR Part 770
[EPA–HQ–OPPT–2018–0174; FRL–9994–47]
RIN 2070–AK47
Technical Issues; Formaldehyde
Emission Standards for Composite
Wood Products
Environmental Protection
Agency (EPA).
ACTION: Final rule.
AGENCY:
EPA is publishing this final
rule to amend the formaldehyde
standards for composite wood products
regulation. EPA is publishing these
amendments to address certain
technical issues and to further align the
final rule requirements with the
California Air Resources Board (CARB)
Airborne Toxic Control Measures
(ATCM) Phase II program. Addressing
these technical issues will add clarity
for regulated entities. These revisions to
the existing rule will also streamline
compliance programs and help to
ensure continued smooth transitions for
supply chains to comply with the
requirements associated with regulated
composite wood products.
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SUMMARY:
17:40 Aug 20, 2019
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*
*
*
5306–85–4; 30915–81–
When ready for use, the
2; 107644–13–3;
end-use concentration is
103594–41–8;
not to exceed 1,000 ppm.
103594–42–9.
None ..............................
None ..............................
*
This final rule is effective on
August 21, 2019. The incorporation by
reference of certain material is approved
by the Director of the Federal Register
as of August 21, 2019. The
incorporation by reference of other
material was approved by the Director
of the Federal Register as of February
10, 2017.
ADDRESSES: The docket for this action,
identified by docket identification (ID)
number EPA–HQ–OPPT–2018–0174, is
available at https://www.regulations.gov
or at the Office of Pollution Prevention
and Toxics Docket (OPPT Docket),
Environmental Protection Agency
Docket Center (EPA/DC), West William
Jefferson Clinton Bldg., Rm. 3334, 1301
Constitution Ave. NW, Washington, DC.
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 OPPT
Docket is (202) 566–0280. Please review
the visitor instructions and additional
information about the docket available
at https://www.epa.gov/dockets.
FOR FURTHER INFORMATION CONTACT:
For technical information contact:
Todd Coleman, National Program
Chemicals Division, Office of Pollution
Prevention and Toxics, Environmental
Protection Agency, 1200 Pennsylvania
Ave. NW, Washington, DC 20460–0001;
telephone number: (202) 564–1208;
email address: coleman.todd@epa.gov.
DATES:
[FR Doc. 2019–17993 Filed 8–20–19; 8:45 am]
VerDate Sep<11>2014
*
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Limits
*
*
For general information contact: The
TSCA-Hotline, ABVI-Goodwill, 422
South Clinton Ave., Rochester, NY
14620; telephone number: (202) 554–
1404; email address: TSCA-Hotline@
epa.gov.
SUPPLEMENTARY INFORMATION:
I. Does this action apply to me?
You may be affected by this final rule
if you manufacture (including import),
sell, supply, offer for sale, test, or work
with certification firms that certify
hardwood plywood, medium-density
fiberboard, particleboard, and/or
products containing these composite
wood materials in the United States.
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:
• Veneer, plywood, and engineered
wood product manufacturing (NAICS
code 3212).
• Manufactured home (mobile home)
manufacturing (NAICS code 321991).
• Prefabricated wood building
manufacturing (NAICS code 321992).
• Furniture and related product
manufacturing (NAICS code 337).
• Furniture merchant wholesalers
(NAICS code 42321).
• Lumber, plywood, millwork, and
wood panel merchant wholesalers
(NAICS code 42331).
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Agencies
[Federal Register Volume 84, Number 162 (Wednesday, August 21, 2019)]
[Rules and Regulations]
[Pages 43510-43517]
From the Federal Register Online via the Government Publishing Office [www.gpo.gov]
[FR Doc No: 2019-17993]
-----------------------------------------------------------------------
ENVIRONMENTAL PROTECTION AGENCY
40 CFR Part 180
[EPA-HQ-OPP-2018-0201; FRL-9997-14]
C1-C4 Linear and Branched Chain Alkyl D-
Glucitol Dianhydro Alkyl Ethers; Exemption From the Requirement of a
Tolerance
AGENCY: Environmental Protection Agency (EPA).
ACTION: Final rule.
-----------------------------------------------------------------------
SUMMARY: This regulation establishes exemptions from the requirement of
a tolerance for residues of pesticide inert ingredients within the
C1-C4 linear and branched chain alkyl d-glucitol
dianhydro alkyl ethers (AD-GDAE) cluster. These exemptions are being
established with the following terms: When used as an inert ingredient
(solvent, co-solvent, viscosity modifier and adjuvant) in pesticide
formulations applied to growing crops and raw agricultural commodities
after harvest, on animals, and in antimicrobial formulations applied to
food-contact surfaces in public-eating places, dairy-processing
equipment, and food-processing equipment, and utensils, and in
antimicrobial formulations used for dairy processing equipment, and
food-processing equipment and utensils. Exponent, Inc., on behalf of
Croda, Inc., submitted a petition to EPA under the Federal Food, Drug,
and Cosmetic Act (FFDCA), requesting establishment of an exemption from
the requirement of a tolerance. This regulation eliminates the need to
establish a maximum permissible level for residues of C1-
C4 linear and branched chain alkyl d-glucitol dianhydro
alkyl ethers cluster when used in accordance with the terms of these
exemptions.
DATES: This regulation is effective August 21, 2019. Objections and
requests for hearings must be received on or before October 21, 2019,
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 docket for this action, identified by docket
identification (ID) number EPA-HQ-OPP-2018-0201, is 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: Michael L. Goodis, Registration
Division (7505P), Office of Pesticide Programs, Environmental
Protection Agency, 1200 Pennsylvania Ave. NW, Washington, DC 20460-
0001; main telephone number:
[[Page 43511]]
(703) 305-7090; email address: [email protected].
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 40 CFR
part 180 through the Government Publishing Office's e-CFR site at
https://www.ecfr.gov/cgi-bin/text-idx?&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 number EPA-HQ-OPP-2018-0201 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
October 21, 2019. 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-2018-0201, 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. Petition for Exemption
In the Federal Register of October 18, 2018 (83 FR 52787) (FRL-
9984-21), EPA issued a document pursuant to FFDCA section 408, 21
U.S.C. 346a, announcing the filing of a pesticide petition (PP IN-
11109) by Exponent, Inc. (1150 Connecticut Ave, Suite 1100, NW,
Washington, DC 20036), on behalf of Croda, Inc. (315 Cherry Lane New
Castle, DE 19720). The petition requested that 40 CFR be amended by
establishing exemptions from the requirement of a tolerance for
residues of C1-C4 linear and branched chain alkyl d-glucitol dianhydro
alkyl ethers (C1-C4 Linear and Branched Chain AD-GDAE) cluster--d-
glucitol, 1,4:3,6-dianhydro-2,5-di-O-methyl-(CAS Reg. No. 5306-85-4);
d-glucitol, 1,4:3,6-dianhydro-2,5-di-O-ethyl- (CAS Reg. No. 30915-81-
2); d-glucitol, 1,4:3,6-dianhydro-2,5-di-O-propyl) (CAS Reg. No.
107644-13-3); d-glucitol, 1,4:3,6-dianhydro-2,5-bis-O-(1-methylethyl)-
,(iso-propyl diether) (CAS Reg. No. 103594-41-8); d-glucitol, 1,4:3,6-
dianhydro-2,5-di-O-butyl- (CAS Reg. No. 103594-42-9); d-glucitol,
1,4:3,6-dianhydro-2,5-di-O-(1-methylpropyl)-, (CAS Reg. No. not
assigned); and d-glucitol, 1,4:3,6-dianhydro-2,5-di-O-(2-methylpropyl)-
, (CAS Reg. No. not assigned) when used as an inert ingredient
(solvent, co-solvent, viscosity modifier and adjuvant) in pesticide
formulations applied to growing crops and raw agricultural commodities
after harvest under 40 CFR 180.910, applied in or on animals under 40
CFR 180.930, in antimicrobial formulations used in food-contact
surfaces in public-eating places, dairy-processing equipment, and food-
processing equipment and utensils under 40 CFR 180.940(a) and in
antimicrobial formulations used for dairy-processing equipment, and
food-processing equipment and utensils under 40 CFR 180.940(b). That
document referenced a summary of the petition prepared by Exponent,
Inc. on behalf of Croda, Inc., the petitioner, which is available in
the docket, https://www.regulations.gov. Although one comment was
submitted in response to the relating to notice of filing regarding the
use of pesticides generally, it was not specific to tolerances or this
rulemaking.
III. Inert Ingredient Definition
Inert ingredients are all ingredients that are not active
ingredients as defined in 40 CFR 153.125 and include, but are not
limited to, the following types of ingredients (except when they have a
pesticidal efficacy of their own): Solvents such as alcohols and
hydrocarbons; surfactants such as polyoxyethylene polymers and fatty
acids; carriers such as clay and diatomaceous earth; thickeners such as
carrageenan and modified cellulose; wetting, spreading, and dispersing
agents; propellants in aerosol dispensers; microencapsulating agents;
and emulsifiers. The term ``inert'' is not intended to imply
nontoxicity; the ingredient may or may not be chemically active.
Generally, EPA has exempted inert ingredients from the requirement of a
tolerance based on the low toxicity of the individual inert
ingredients.
IV. Aggregate Risk Assessment and Determination of Safety
Section 408(c)(2)(A)(i) of FFDCA allows EPA to establish an
exemption from the requirement for 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. . . .''
[[Page 43512]]
EPA establishes exemptions from the requirement of a tolerance only
in those cases where it can be clearly demonstrated that the risks from
aggregate exposure to pesticide chemical residues under reasonably
foreseeable circumstances will pose no appreciable risks to human
health. In order to determine the risks from aggregate exposure to
pesticide inert ingredients, the Agency considers the toxicity of the
inert in conjunction with possible exposure to residues of the inert
ingredient through food, drinking water, and through other exposures
that occur as a result of pesticide use in residential settings. If EPA
is able to determine that a finite tolerance is not necessary to ensure
that there is a reasonable certainty that no harm will result from
aggregate exposure to the inert ingredient, an exemption from the
requirement of a tolerance may be established.
Consistent with FFDCA section 408(c)(2)(A), and the factors
specified in FFDCA section 408(c)(2)(B), 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 C1-C4
linear and branched chain alkyl d-glucitol dianhydro alkyl ethers
cluster including exposure resulting from the exemption established by
this action. EPA's assessment of exposures and risks associated with
C1-C4 linear and branched chain alkyl d-glucitol
dianhydro alkyl ethers cluster follows.
A. Toxicological Profile
EPA has evaluated the available toxicity data and considered their
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 C1-C4 linear and
branched chain alkyl d-glucitol dianhydro alkyl ethers cluster 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 this unit.
The seven compounds included in the cluster are C1-
C4 linear and branched chain glucitol, 1,4:3,6-dianhydro
ether congeners of isosorbide, which is described as a fused ring
furo[3,2-b]furan, d-glucitol heterocycle. These chemicals are similar
in structure and are expected to be similar in regard to toxicity
profile. Therefore, d-glucitol, 1,4:3,6-dianhydro-2,5-di-O-methyl- was
selected as a suitable analogue to represent toxicity due to exposure
to the seven compounds included in the cluster and all toxicological
studies were conducted with d-glucitol, 1,4:3,6-dianhydro-2,5-di-O-
methyl-.
The acute oral and dermal toxicities are low in rats and rabbits,
respectively. C1-C4 linear and branched chain
alkyl d-glucitol dianhydro alkyl ethers are not irritating to the skin
or eyes in the rabbit. Acute inhalation and sensitization studies are
not available for review.
New Zealand white rabbits exposed for 8 days via gavage to doses as
high as 300 mg/kg/day of d-glucitol, 1,4:3,6-dianhydro-2,5-di-O-methyl-
do not exhibit adverse effects. No adverse effects are observed up to
375 mg/kg/day in rats following 13 weeks of exposure via gavage to d-
glucitol, 1,4:3,6-dianhydro-2,5-di-O-methyl-. Conversely, adverse
effects are observed in the dog following 13 weeks of exposure via
capsule to d-glucitol, 1,4:3,6-dianhydro-2,5-di-O-methyl-. Decreased
mean body weight, body weight gain, food consumption, changes in
clinical biochemistry, lower levels of red blood cells (RBCs),
hemoglobin and hematocrit and decreased relative liver weights are
observed in dogs at 700 mg/kg/day. The no-observed-adverse-effect level
(NOAEL) is 100 mg/kg/day.
No fetal susceptibility is observed in the developmental toxicity
studies in rats and rabbits. Developmental studies with d-glucitol,
1,4:3,6-dianhydro-2,5-di-O-methyl-in the rat and rabbit show no
maternal or developmental adverse effects up to 375 and 300 mg/kg/day,
respectively, the highest doses tested. No reproduction toxicity
studies are available for review, however, no evidence of toxicity to
reproductive organs is observed in the 13-week oral toxicity studies in
the rat or dog up to 375 and 700 mg/kg/day, respectively.
The Ames test and chromosomal aberrations assay in human
lymphocytes are negative. Therefore, d-glucitol, 1,4:3,6-dianhydro-2,5-
di-O-methyl- is not considered mutagenic.
D-glucitol, 1,4:3,6-dianhydro-2,5-di-O-methyl- is not expected to
be carcinogenic based on a Derek Nexus structural alert analysis. No
structural alerts for carcinogenicity or mutagenicity are indicated in
the analysis.
Neurotoxicity and immunotoxicity studies are not available for
review. However, no evidence of neurotoxicity and immunotoxicity is
observed in the submitted studies.
Metabolism studies are not available for the C1-
C4 linear and branched chain alkyl d-glucitol dianhydro
alkyl ethers cluster. However, based on the classical metabolic
pathways for the alkyl and aryl etherases, it is expected that the
C1-C4 linear and branched chain alkyl d-glucitol
dianhydro alkyl ethers cluster would be metabolized to monoethers,
isosorbide (the common and major metabolite), and sorbitol.
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 no adverse effects are observed (the NOAEL)
and the lowest dose at which adverse effects of concern are identified
(the LOAEL). Uncertainty/safety factors 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.
The 13-week oral toxicity study in dogs is selected for the chronic
dietary exposure scenario as well as intermediate-term incidental oral,
dermal and inhalation exposure scenarios. The NOAEL is 100 mg/kg/day,
and the LOAEL is 700 mg/kg/day based on decreased mean body weight,
body weight gain and food consumption, changes in clinical
biochemistry, lower levels of RBCs, hemoglobin and hematocrit and
decreased relative liver weights. This represents the lowest NOAEL in
the database in the most sensitive species. The developmental studies
in rats and rabbits are selected for short-term exposure scenarios.
These studies are considered co-critical, the NOAEL is 300 mg/kg/day,
the highest dose tested.
[[Page 43513]]
The standard inter- and intra-species uncertainty factors of 10x are
applied; as discussed below in Unit IV.D., the Agency applied a 1x Food
Quality Protection Act (FQPA) Safety Factor (SF). The default factor of
100% is applied for the dermal absorption rate and the inhalation
absorption rate.
C. Exposure Assessment
1. Dietary exposure from food and feed uses. In evaluating dietary
exposure to C1-C4 linear and branched chain alkyl
d-glucitol dianhydro alkyl ethers cluster, EPA considered exposure
under the proposed exemption from the requirement of a tolerance. EPA
assessed dietary exposures from C1-C4 linear and
branched chain alkyl d-glucitol dianhydro alkyl ethers cluster in food
as follows:
No adverse effects attributable to a single exposure of endpoint
was identified for d-glucitol, 1,4:3,6-dianhydro-2,5-di-O-methyl-;
therefore, an acute dietary exposure assessment was not conducted.
In conducting the chronic dietary exposure assessment using the
Dietary Exposure Evaluation Model DEEM-FCIDTM, Version 3.16, EPA used
food consumption information from the U.S. Department of Agriculture's
(USDA's) 2003-2008 National Health and Nutrition Examination Survey,
What We Eat in America (NHANES/WWEIA). As to residue levels in food, no
residue data were submitted for d-glucitol, 1,4:3,6-dianhydro-2,5-di-O-
methyl-. In the absence of specific residue data, EPA has developed an
approach which uses surrogate information to derive upper bound
exposure estimates for the subject inert ingredient. Upper bound
exposure estimates are based on the highest tolerance for a given
commodity from a list of high use insecticides, herbicides, and
fungicides. A complete description of the general approach taken to
assess inert ingredient risks in the absence of residue data is
contained in the memorandum entitled ``Alkyl Amines Polyalkoxylates
(Cluster 4): Acute and Chronic Aggregate (Food and Drinking Water)
Dietary Exposure and Risk Assessments for the Inerts,'' (D361707, S.
Piper, 2/25/09) and can be found at https://www.regulations.gov in
docket ID number EPA-HQ-OPP-2008-0738.
In the dietary exposure assessment, the Agency assumed that the
residue level of the inert ingredient would be no higher than the
highest tolerance for a given commodity. Implicit in this assumption is
that there would be similar rates of degradation (if any) between the
active and inert ingredient and that the concentration of inert
ingredient in the scenarios leading to these highest levels of
tolerances would be no higher than the concentration of the active
ingredient.
The Agency believes the assumptions used to estimate dietary
exposures lead to an extremely conservative assessment of dietary risk
due to a series of compounded conservatisms. First, assuming that the
level of residue for an inert ingredient is equal to the level of
residue for the active ingredient will overstate exposure. The
concentrations of active ingredient in agricultural products are
generally at least 50 percent of the product and often can be much
higher. Further, pesticide products rarely have a single inert
ingredient; rather there is generally a combination of different inert
ingredients used which additionally reduces the concentration of any
single inert ingredient in the pesticide product in relation to that of
the active ingredient.
Second, the conservatism of this methodology is compounded by EPA's
decision to assume that, for each commodity, the active ingredient
which will serve as a guide to the potential level of inert ingredient
residues is the active ingredient with the highest tolerance level.
This assumption overstates residue values because it would be highly
unlikely, given the high number of inert ingredients, that a single
inert ingredient or class of ingredients would be present at the level
of the active ingredient in the highest tolerance for every commodity.
Finally, a third compounding conservatism is EPA's assumption that all
foods contain residues of the inert ingredient at the highest tolerance
level. In other words, EPA assumed 100 percent of all foods are treated
with the inert ingredient at the rate and manner necessary to produce
the highest residue legally possible for an active ingredient. In
summary, EPA chose a very conservative method for estimating what level
of inert residue could be on food, then used this methodology to choose
the highest possible residue that could be found on food and assumed
that all food contained this residue. No consideration was given to
potential degradation between harvest and consumption even though
monitoring data shows that tolerance level residues are typically one
to two orders of magnitude higher than actual residues in food when
distributed in commerce.
Accordingly, although sufficient information to quantify actual
residue levels in food is not available, the compounding of these
conservative assumptions will lead to a significant exaggeration of
actual exposures. EPA does not believe that this approach
underestimates exposure in the absence of residue data.
To assess dietary exposure due to its use in antimicrobial
products, EPA calculated the daily dietary dose (DDD) and the estimated
daily intake (EDI) as described in the Food Drug Administration (FDA)
model. The assessment considered: Application rates, residual solution
or quantity of solution remaining on the treated surface without
rinsing with potable water, surface area of the treated surface which
comes into contact with food, pesticide migration fraction, and body
weight. These assumptions are based on FDA guidelines (2003). Dietary
exposures due to antimicrobial uses are aggregated with the
aforementioned dietary exposures.
2. Dietary exposure from drinking water. For the purpose of the
screening-level dietary risk assessment to support this request for an
exemption from the requirement of a tolerance for C1-
C4 linear and branched chain alkyl d-glucitol dianhydro
alkyl ethers, a conservative drinking water concentration value of 100
ppb based on screening-level modeling was used to assess the
contribution to drinking water for the chronic dietary risk assessments
for parent compound. These values were directly entered into the
dietary exposure model.
3. From non-dietary exposure. The term ``residential exposure'' is
used in this document to refer to non-occupational, non-dietary
exposure (e.g., textiles (clothing and diapers), carpets, swimming
pools, and hard surface disinfection on walls, floors, tables).
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). D-glucitol, 1,4:3,6-dianhydro-2,5-di-O-methyl- may be
used as an inert ingredient in pesticide products that are registered
for specific uses that may result in residential exposure. A
conservative residential exposure and risk assessments were completed
for pesticide products containing d-glucitol, 1,4:3,6-dianhydro-2,5-di-
O-methyl- as inert ingredients. The Agency assessed pesticide products
containing d-glucitol, 1,4:3,6-dianhydro-2,5-di-O-methyl- using
exposure scenarios (treated lawns, mopping, wiping and aerosol spray)
to represent conservative residential handler exposure. Further details
of this residential exposure and risk analysis can be found at https://www.regulations.gov in the
[[Page 43514]]
memorandum entitled: ``JITF Inert Ingredients. Residential and
Occupational Exposure Assessment Algorithms and Assumptions Appendix
for the Human Health Risk Assessments to Support Proposed Exemption
from the Requirement of a Tolerance When Used as Inert Ingredients in
Pesticide Formulations,'' (D364751, 5/7/09, Lloyd/LaMay in docket ID
number EPA-HQ-OPP-2008-0710. D-glucitol, 1,4:3,6-dianhydro-2,5-di-O-
methyl- is also present in some anti-acne and anti-aging topically
applied pharmaceuticals products. The typical use levels of d-glucitol,
1,4:3,6-dianhydro-2,5-di-O-methyl- in these products are limited to
less than 5.44% to 15% weight/weight (w/w). These products are used
sparingly and applied selectively to limited areas of the skin.
The Agency does not have sufficient data to quantitatively assess
exposures to d-glucitol, 1,4:3,6-dianhydro-2,5-di-O-methyl- that result
from these non-pesticidal uses. However, the Agency believes the
assessments of exposures due to pesticide uses are protective of these
non-pesticidal uses. Based on the available data on the typical
reported concentration ranges of d-glucitol, 1,4:3,6-dianhydro-2,5-di-
O-methyl- topically applied pharmaceuticals as well as the specific use
and limited exposures resulting from such uses, the Agency anticipates
that exposures to d-glucitol, 1,4:3,6-dianhydro-2,5-di-O-methyl- that
might result from anti-acne and anti-aging topically applied
pharmaceutical products uses are likely to be markedly less than the
conservatively-estimated exposures resulting from pesticide use.
Therefore, the Agency believes that any contribution to the estimated
pesticide exposure resulting from topically applied pharmaceuticals
products is likely to be insignificant in comparison to the estimates
for exposure from pesticide use and these exposures have not been
aggregated with other non-residential exposures.
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 C1-C4 linear and branched
chain alkyl d-glucitol dianhydro alkyl ethers cluster to share a common
mechanism of toxicity with any other substances, and C1-
C4 linear and branched chain alkyl d-glucitol dianhydro
alkyl ethers cluster does not appear to produce a toxic metabolite
produced by other substances. For the purposes of this tolerance
action, therefore, EPA has assumed that C1-C4
linear and branched chain alkyl d-glucitol dianhydro alkyl ethers
cluster does not have a common mechanism of toxicity with other
substances. For information regarding EPA's efforts to determine which
chemicals have a common mechanism of toxicity and to evaluate the
cumulative effects of such chemicals, see EPA's website at https://www.epa.gov/pesticides/cumulative.
D. Safety Factor for Infants and Children
1. In general. Section 408(b)(2)(C) of FFDCA provides that EPA
shall apply an additional tenfold (10X) margin of safety 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 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.
The Agency has concluded that there is reliable data to determine
that infants and children will be safe if the FQPA SF of 10x is reduced
to 1x for the chronic dietary assessment for the following reasons. The
toxicity database for C1-C4 linear and branched chain alkyl d-glucitol
dianhydro alkyl ethers cluster contains subchronic, developmental and
mutagenicity studies. There is no indication of immunotoxicity or
neurotoxicity in the available studies; therefore, there is no need to
require an immunotoxicity or neurotoxicity study. Fetal susceptibility
is not observed in developmental toxicity studies in the rat and
rabbit. No maternal or developmental toxicity is observed in either
study up to 300 mg/kg/day. A reproduction toxicity is not available;
however, reproduction parameters were not affected in the submitted
studies at doses as high as 375 and 700 mg/kg/day in the rat and dog,
respectively. Based on the adequacy of the toxicity database, the
conservative nature of the exposure assessment and the lack of concern
for prenatal and postnatal sensitivity, the Agency has concluded that
there is reliable data to determine that infants and children will be
safe if the FQPA SF of 10x is reduced to 1x.
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. An acute aggregate risk assessment takes into
account acute exposure estimates from dietary consumption of food and
drinking water. No adverse effect resulting from a single oral exposure
was identified and no acute dietary endpoint was selected. Therefore,
C1-C4 linear and branched chain alkyl d-glucitol
dianhydro alkyl ethers cluster is 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 chronic exposure to
C1-C4 linear and branched chain alkyl d-glucitol
dianhydro alkyl ethers cluster from food and water will utilize 70.6%
of the cPAD for children 1 to 2 years old, the population group
receiving the greatest exposure.
3. Short-term risk. Short-term aggregate exposure takes into
account short-term residential exposure plus chronic exposure to food
and water (considered to be a background exposure level).
C1-C4 linear and branched chain alkyl d-
glucitol dianhydro alkyl ethers cluster is currently used as an inert
ingredient in pesticide products that are registered for uses that
could result in short-term residential exposure, and the Agency has
determined that it is appropriate to aggregate chronic exposure through
food and water with short-term residential exposures to C1-
C4 linear and branched chain alkyl d-glucitol dianhydro
alkyl ethers cluster.
Using the exposure assumptions described in this unit for short-
term exposures, EPA has concluded the combined short-term food, water,
and residential exposures result in aggregate MOEs of 148 for adult
males and females. Adult residential exposure combines high-end dermal
and inhalation handler exposure from indoor hard surface, aerosol spray
with a high-end post application dermal exposure from contact with
treated lawns. The combined short-term
[[Page 43515]]
aggregated food, water, and residential pesticide exposures result in
an aggregate MOE of 122 for children. Children's residential exposure
includes total exposures associated with contact with treated surfaces
(dermal and hand-to-mouth exposures). Because EPA's level of concern
for C1-C4 linear and branched chain alkyl d-
glucitol dianhydro alkyl ethers cluster is an MOE of less than 100,
these MOEs are not of concern.
4. Intermediate-term risk. Intermediate-term aggregate exposure
takes into account intermediate-term residential exposure plus chronic
exposure to food and water (considered to be a background exposure
level).
C1-C4 linear and branched chain alkyl d-
glucitol dianhydro alkyl ethers cluster is currently used as an inert
ingredient in pesticide products that are registered for uses that
could result in intermediate-term residential exposure, and the Agency
has determined that it is appropriate to aggregate chronic exposure
through food and water with intermediate-term residential exposures to
C1-C4 linear and branched chain alkyl d-glucitol
dianhydro alkyl ethers cluster.
Using the exposure assumptions described in this unit for
intermediate-term exposures, EPA has concluded that the combined
intermediate-term food, water, and residential exposures result in
aggregate MOEs of 434 for adult males and females. Adult residential
exposure includes high end post application dermal exposure from
contact with treated lawns. The combined intermediate-term aggregated
food, water, and residential exposures result in an aggregate MOE of
125 for children. Children's residential exposure includes total
exposures associated with contact with treated surfaces (dermal and
hand-to-mouth exposures). Because EPA's level of concern for
C1-C4 linear and branched chain alkyl d-glucitol
dianhydro alkyl ethers cluster is an MOE of less than 100, these MOEs
are not of concern.
5. Aggregate cancer risk for U.S. population. Based on a DEREK
structural alert analysis, the lack of mutagenicity, and the lack of
specific organ toxicity in the chronic toxicity study, C1-C4 linear and
branched chain alkyl d-glucitol dianhydro alkyl ethers cluster is not
expected to pose a cancer risk to humans.
6. Determination of safety. Based on these risk assessments, EPA
concludes that there is a reasonable certainty that no harm will result
to the general population, or to infants and children from aggregate
exposure to C1-C4 linear and branched chain alkyl
d-glucitol dianhydro alkyl ethers cluster residues.
V. Other Considerations
Analytical Enforcement Methodology
An analytical method is not required for enforcement purposes since
the Agency is establishing an exemption from the requirement of a
tolerance without any numerical limitation.
VI. Conclusions
Therefore, exemptions from the requirement of a tolerance are
established for residues of the following seven compounds within the
C1-C4 linear and branched chain alkyl d-glucitol dianhydro alkyl ethers
(AD-GDAE) cluster: (1) d-glucitol, 1,4:3,6-dianhydro-2,5-di-O-methyl-
(CAS Reg. No. 5306-85-4); (2) d-glucitol, 1,4:3,6-dianhydro-2,5-di-O-
ethyl- (CAS Reg. No. 30915-81-2); (3) d-glucitol, 1,4:3,6-dianhydro-
2,5-di-O-propyl) (CAS Reg. No.107644-13-3); (4) d-glucitol, 1,4:3,6-
dianhydro-2,5-bis-O-(1-methylethyl)-,(iso-propyl diether) (CAS Reg. No.
103594-41-8); (5) d-glucitol, 1,4:3,6-dianhydro-2,5-di-O-butyl- (CAS
Reg. No. 103594-42-9); (6) d-glucitol, 1,4:3,6-dianhydro-2,5-di-O-(1-
methylpropyl)-, (CAS Reg. No. not assigned); and (7) d-glucitol,
1,4:3,6-dianhydro-2,5-di-O-(2-methylpropyl)-, (CAS Reg. No. not
assigned) when used as an inert ingredient (solvent, co-solvent,
viscosity modifier and adjuvant) in pesticide formulations applied to
growing crops and raw agricultural commodities after harvest under 40
CFR 180.910; applied in or on animals under 40 CFR 180.930; when used
in antimicrobial formulations applied to food-contact surfaces in
public-eating places, dairy-processing equipment, and food-processing
equipment and utensils under 40 CFR 180.940(a) limited to 500 ppm; and
in antimicrobial formulations used for dairy-processing equipment, and
food-processing equipment and utensils under 40 CFR 180.940(b) limited
to 1,000 ppm.
VII. Statutory and Executive Order Reviews
This action establishes a tolerance exemption 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 action has been
exempted from review under Executive Order 12866, this action 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), nor is it considered a
regulatory action under Executive Order 13771, entitled ``Reducing
Regulations and Controlling Regulatory Costs'' (82 FR 9339, February 3,
2017). This action 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 action 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 action. In addition, this
action does not impose any enforceable duty or contain any unfunded
mandate as described under Title II of the Unfunded Mandates Reform Act
(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 (NTTAA) (15 U.S.C. 272 note).
[[Page 43516]]
VIII. 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 8, 2019.
Michael Goodis,
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. 180.910, add alphabetically the following inert ingredients
to the table to read as follows:
Sec. 180.910 Inert ingredients used pre- and post-harvest; exemptions
from the requirement of a tolerance.
* * * * *
----------------------------------------------------------------------------------------------------------------
Inert ingredients Limits Uses
----------------------------------------------------------------------------------------------------------------
* * * * * * *
D-glucitol, 1,4:3,6-dianhydro-2,5-di-O- ......................................... solvent, co-solvent,
methyl- (CAS Reg. No. 5306-85-4); D- viscosity modifier, and
glucitol, 1,4:3,6-dianhydro-2,5-di-O- adjuvant.
ethyl- (CAS Reg. No. 30915-81-2); D-
glucitol, 1,4:3,6-dianhydro-2,5-di-O-
propyl) (CAS Reg. No.107644-13-3); D-
glucitol, 1,4:3,6-dianhydro-2,5-bis-O-(1-
methylethyl)-,(iso-propyl diether) (CAS
Reg. No. 103594-41-8); D-glucitol,
1,4:3,6-dianhydro-2,5-di-O-butyl- (CAS
Reg. No. 103594-42-9); D-glucitol,
1,4:3,6-dianhydro-2,5-di-O-(1-
methylpropyl)-, (CAS Reg. No. not
assigned); and D-glucitol, 1,4:3,6-
dianhydro-2,5-di-O-(2-methylpropyl)-,
(CAS Reg. No. not assigned).
* * * * * * *
----------------------------------------------------------------------------------------------------------------
0
3. In Sec. 180.930, add alphabetically the following inert ingredients
to the table to read as follows:
Sec. 180.930 Inert ingredients applied to animals; exemptions from
the requirement of a tolerance.
* * * * *
----------------------------------------------------------------------------------------------------------------
Inert ingredients Limits Uses
----------------------------------------------------------------------------------------------------------------
* * * * * * *
D-glucitol, 1,4:3,6-dianhydro-2,5-di-O- ......................................... solvent, co-solvent,
methyl-(CAS Reg. No. 5306-85-4); D- viscosity modifier, and
glucitol, 1,4:3,6-dianhydro-2,5-di-O- adjuvant.
ethyl- (CAS Reg. No. 30915-81-2); D-
glucitol, 1,4:3,6-dianhydro-2,5-di-O-
propyl) (CAS Reg. No.107644-13-3); D-
glucitol, 1,4:3,6-dianhydro-2,5-bis-O-(1-
methylethyl)-,(iso-propyl diether) (CAS
Reg. No. 103594-41-8); D-glucitol,
1,4:3,6-dianhydro-2,5-di-O-butyl- (CAS
Reg. No. 103594-42-9); D-glucitol,
1,4:3,6-dianhydro-2,5-di-O-(1-
methylpropyl)-, (CAS Reg. No. not
assigned); and D-glucitol, 1,4:3,6-
dianhydro-2,5-di-O-(2-methylpropyl)-,
(CAS Reg. No. not assigned).
* * * * * * *
----------------------------------------------------------------------------------------------------------------
0
4. In Sec. 180.940, add alphabetically the following inert
ingredients to the tables in paragraphs (a) and (b) to read as follows:
Sec. 180. 940 Tolerance exemptions for active and inert ingredients
for use in antimicrobial formulations (Food-contact surface sanitizing
solutions).
* * * * *
[[Page 43517]]
(a) * * *
----------------------------------------------------------------------------------------------------------------
Pesticide chemical CAS Reg. No. Limits
----------------------------------------------------------------------------------------------------------------
* * * * * * *
C1-C4 linear and branched chain alkyl d- 5306-85-4; 30915-81-2; 107644-13-3; 103594- When ready for use, the
glucitol dianhydro alkyl ethers cluster. 41-8; 103594-42-9. end-use concentration is
not to exceed 500 ppm.
D-glucitol, 1,4:3,6-dianhydro-2,5-di-O- None....................................... .........................
(1-methylpropyl)-,.
D-glucitol, 1,4:3,6-dianhydro-2,5-di-O- None....................................... .........................
(2-methylpropyl)-, (CAS Reg. No. not
assigned).
* * * * * * *
----------------------------------------------------------------------------------------------------------------
(b) * * *
----------------------------------------------------------------------------------------------------------------
Pesticide chemical CAS Reg. No. Limits
----------------------------------------------------------------------------------------------------------------
* * * * * * *
C1-C4 linear and branched chain alkyl d- 5306-85-4; 30915-81-2; 107644-13-3; When ready for use, the
glucitol dianhydro alkyl ethers cluster. 103594-41-8; 103594-42-9. end-use concentration is
not to exceed 1,000 ppm.
D-glucitol, 1,4:3,6-dianhydro-2,5-di-O-(1- None..................................... ..........................
methylpropyl)-,.
D-glucitol, 1,4:3,6-dianhydro-2,5-di-O-(2- None..................................... ..........................
methylpropyl)-, (CAS Reg. No. not
assigned).
* * * * * * *
----------------------------------------------------------------------------------------------------------------
* * * * *
[FR Doc. 2019-17993 Filed 8-20-19; 8:45 am]
BILLING CODE 6560-50-P