
[Federal Register Volume 79, Number 209 (Wednesday, October 29, 2014)]
[Rules and Regulations]
[Pages 64317-64322]
From the Federal Register Online via the Government Printing Office [www.gpo.gov]
[FR Doc No: 2014-25592]


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ENVIRONMENTAL PROTECTION AGENCY

40 CFR Part 180

[EPA-HQ-OPP-2013-0729; FRL-9917-15]


Paraquat Dichloride; Pesticide Tolerance

AGENCY: Environmental Protection Agency (EPA).

ACTION: Final rule.

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SUMMARY: This regulation establishes a tolerance for residues of 
paraquat dichloride in or on the tuberous and corm vegetables subgroup 
1C. Interregional Research Project Number 4 (IR-4) requested this 
tolerance under the Federal Food, Drug, and Cosmetic Act (FFDCA).

DATES: This regulation is effective October 29, 2014. Objections and 
requests for hearings must be received on or before December 29, 2014, 
and must be filed in accordance with the instructions provided in 40 
CFR part 178 (see also Unit I.C. of the SUPPLEMENTARY INFORMATION).

ADDRESSES: The docket for this action, identified by docket 
identification (ID) number EPA-HQ-OPP-2013-0729, is available at http://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 http://www.epa.gov/dockets.

FOR FURTHER INFORMATION CONTACT: Susan Lewis, Registration Division 
(7505P), Office of Pesticide Programs, Environmental Protection Agency, 
1200 Pennsylvania Ave. NW., Washington, DC 20460-0001; main telephone 
number: (703) 305-7090; email address: RDFRNotices@epa.gov.

SUPPLEMENTARY INFORMATION:

I. General Information

A. Does this action apply to me?

    You may be potentially affected by this action if you are an 
agricultural producer, food manufacturer, or pesticide manufacturer. 
The following list of North American Industrial Classification System 
(NAICS) codes is not intended to be exhaustive, but rather

[[Page 64318]]

provides a guide to help readers determine whether this document 
applies to them. Potentially affected entities may include:
     Crop production (NAICS code 111).
     Animal production (NAICS code 112).
     Food manufacturing (NAICS code 311).
     Pesticide manufacturing (NAICS code 32532).

B. How can I get electronic access to other related information?

    You may access a frequently updated electronic version of EPA's 
tolerance regulations at 40 CFR part 180 through the Government 
Printing Office's e-CFR site at http://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-2013-0729 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 
December 29, 2014. Addresses for mail and hand delivery of objections 
and hearing requests are provided in 40 CFR 178.25(b).
    In addition to filing an objection or hearing request with the 
Hearing Clerk as described in 40 CFR part 178, please submit a copy of 
the filing (excluding any Confidential Business Information (CBI)) for 
inclusion in the public docket. Information not marked confidential 
pursuant to 40 CFR part 2 may be disclosed publicly by EPA without 
prior notice. Submit the non-CBI copy of your objection or hearing 
request, identified by docket ID number EPA-HQ-OPP-2013-0729, by one of 
the following methods:
     Federal eRulemaking Portal: http://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 http://www.epa.gov/dockets/contacts.html.
Additional instructions on commenting or visiting the docket, along 
with more information about dockets generally, is available at http://www.epa.gov/dockets.

II. Summary of Petitioned-For Tolerance

    In the Federal Register of December 30, 2013 (78 FR 79359) (FRL-
9903-69), EPA issued a document pursuant to FFDCA section 408(d)(3), 21 
U.S.C. 346a(d)(3), announcing the filing of a pesticide petition (PP 
3E8201) by IR-4, 500 College Road East, Suite 201 W., Princeton, NJ 
08540. The petition requested that 40 CFR 180.205 be amended by 
establishing tolerances for residues of the desiccant, defoliant, and 
herbicide paraquat dichloride (1,1'-dimethyl-4,4'-bipyridinium-ion) 
(hereafter in this document referred to solely as paraquat) derived 
from application of the dichloride salt (calculated as the cation) in 
or on tuberous and corm vegetables subgroup (Crop subgroup 1C) at 0.5 
parts per million (ppm). That document referenced a summary of the 
petition prepared by Syngenta Crop Protection, the registrant, which is 
available in the docket, http://www.regulations.gov. There were no 
comments received in response to the notice of filing.

III. Aggregate Risk Assessment and Determination of Safety

    Section 408(b)(2)(A)(i) of FFDCA allows EPA to establish a 
tolerance (the legal limit for a pesticide chemical residue in or on a 
food) only if EPA determines that the tolerance is ``safe.'' Section 
408(b)(2)(A)(ii) of FFDCA defines ``safe'' to mean that ``there is a 
reasonable certainty that no harm will result from aggregate exposure 
to the pesticide chemical residue, including all anticipated dietary 
exposures and all other exposures for which there is reliable 
information.'' This includes exposure through drinking water and in 
residential settings, but does not include occupational exposure. 
Section 408(b)(2)(C) of FFDCA requires EPA to give special 
consideration to exposure of infants and children to the pesticide 
chemical residue in establishing a tolerance and to ``ensure that there 
is a reasonable certainty that no harm will result to infants and 
children from aggregate exposure to the pesticide chemical residue . . 
. .''
    Consistent with FFDCA section 408(b)(2)(D), and the factors 
specified in FFDCA section 408(b)(2)(D), EPA has reviewed the available 
scientific data and other relevant information in support of this 
action. EPA has sufficient data to assess the hazards of and to make a 
determination on aggregate exposure for paraquat including exposure 
resulting from the tolerances established by this action. EPA's 
assessment of exposures and risks associated with paraquat follows.

A. Toxicological Profile

    EPA has evaluated the available toxicity data and considered its 
validity, completeness, and reliability as well as the relationship of 
the results of the studies to human risk. EPA has also considered 
available information concerning the variability of the sensitivities 
of major identifiable subgroups of consumers, including infants and 
children.
    The primary target organ of paraquat is the lung. Evidence of lung 
inflammation, scarring, and compromised lung function in response to 
paraquat are observed throughout the toxicity database (independent of 
route of exposure (oral, dermal, inhalation)) in different species 
(rats, mice, and dogs). Effects in the respiratory tract are observed 
after acute, subchronic, and chronic exposures regardless of the route 
of exposure (oral or inhalation). However, inhalation was a more 
sensitive route of exposure than the oral route. With increasing 
durations of exposure, effects of paraquat in other organ systems are 
observed. These effects include liver inflammation and necrosis in rats 
and inflammation and necrosis of the kidneys in rats and mice. 
Lenticular changes in the eyes of rats were also observed with 
increasing durations of exposure. Importantly, the lung effects occur 
at doses lower than effects in these other organs systems, and so 
protecting for lung effects protects for all other adverse effects of 
paraquat.
    The effects of paraquat in lungs are considered systemic effects. 
There are no dermal toxicity studies suitable for evaluation of 
systemic lung effects in the toxicity database for paraquat. Therefore, 
the Agency is using a dermal absorption factor of 0.3%, which was 
derived from dermal absorption studies conducted in humans and monkeys 
and an oral endpoint for dermal risk assessments.
    Paraquat does not cause reproductive toxicity. Developmental 
toxicity in response to paraquat, when observed, always occurred in the 
presence of maternal toxicity. Four developmental toxicity studies (two 
in rats and two in mice) are available. Since effects in the

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offspring (e.g., reduced body weight/gain and delayed skeletal 
ossification), when present, were lesser in severity than those 
observed in maternal animals (e.g. respiratory distress, reduced body 
weight, lesions in the lungs and kidneys) and were also consistent with 
those commonly observed as secondary to maternal toxicity, the Agency 
has concluded that there was no evidence of qualitative susceptibility 
in the young.
    No evidence of neurotoxicity was observed in acute and subchronic 
neurotoxicity studies conducted with paraquat up to the doses at which 
respiratory effects were observed (e.g. the maximum tolerated dose). 
There was also no evidence of immunotoxicity in response to paraquat.
    Based on the lack of evidence of carcinogenicity in mice and rats, 
the Agency has concluded that there is no concern for the carcinogenic 
potential of paraquat. Paraquat was not mutagenic in the Salmonella 
typhimurium assay, was not genotoxic in the unscheduled DNA synthesis 
assay in vitro or in vivo, was negative for chromosomal aberration in 
the bone marrow test, and no evidence was found for suppressed 
fertility or dominant lethal mutagenicity in mice. Conversely, paraquat 
was found to be weakly positive in the mouse lymphoma assay and human 
lymphocyte cytogenetic assay, and was positive in the sister chromatid 
exchange assay.
    Specific information on the studies received and the nature of the 
adverse effects caused by paraquat as well as the no-observed-adverse-
effect-level (NOAEL) and the lowest-observed-adverse-effect-level 
(LOAEL) from the toxicity studies can be found at http://www.regulations.gov in document ``Paraquat Dichloride. HED Human Health 
Risk Assessment for the Expansion of Representative Commodity Use on 
Potato to Tuberous and Corm Vegetables Subgroup 1C'' on pages 28-32 in 
docket ID number EPA-HQ-OPP-2013-0729.

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 http://www.epa.gov/pesticides/factsheets/riskassess.htm.
    A summary of the toxicological endpoints for paraquat used for 
human risk assessment is discussed in Unit B. of the final rule 
published in the Federal Register of August 9, 2012 (77 FR 47539) (FRL-
9357-1).

C. Exposure Assessment

    1. Dietary exposure from food and feed uses. In evaluating dietary 
exposure to paraquat, EPA considered exposure under the petitioned-for 
tolerances as well as all existing paraquat tolerances in 40 CFR 
180.205. EPA assessed dietary exposures from paraquat in food as 
follows:
    i. Acute exposure. Quantitative acute dietary exposure and risk 
assessments are performed for a food-use pesticide, if a toxicological 
study has indicated the possibility of an effect of concern occurring 
as a result of a 1-day or single exposure.
    Such effects were identified for paraquat. In estimating acute 
dietary exposure, EPA used food consumption information from the U.S. 
Department of Agriculture's (USDA's) National Health and Nutrition 
Examination Survey, What We Eat in America, (NHANES/WWEIA). As to 
residue levels in food, the acute analysis assumed a distribution of 
residues based on tolerance level residues. Empirical and Dietary 
Exposure Evaluation Model (DEEM) default processing factors were used 
to modify the field trial data. Maximum screening-level percent crop 
treated (PCT) estimates were used for commodities for which data were 
available. If no percent crop treated data were available, 100 PCT was 
assumed.
    ii. Chronic exposure. In conducting the chronic dietary exposure 
assessment EPA used the food consumption data from the USDA's NHANES/
WWEIA. As to residue levels in food, EPA assumed tolerance level 
residues and average estimates of PCT.
    iii. Cancer. Based on the data summarized in Unit III.A., EPA has 
concluded that paraquat does not pose a cancer risk to humans. 
Therefore, a dietary exposure assessment for the purpose of assessing 
cancer risk is unnecessary.
    iv. Anticipated residue and percent crop treated (PCT) information. 
Section 408(b)(2)(F) of FFDCA states that the Agency may use data on 
the actual percent of food treated for assessing chronic dietary risk 
only if:
     Condition a: The data used are reliable and provide a 
valid basis to show what percentage of the food derived from such crop 
is likely to contain the pesticide residue.
     Condition b: The exposure estimate does not underestimate 
exposure for any significant subpopulation group.
     Condition c: Data are available on pesticide use and food 
consumption in a particular area, the exposure estimate does not 
understate exposure for the population in such area. In addition, the 
Agency must provide for periodic evaluation of any estimates used. To 
provide for the periodic evaluation of the estimate of PCT as required 
by FFDCA section 408(b)(2)(F), EPA may require registrants to submit 
data on PCT.
    The Agency estimated the PCT in the acute dietary risk assessment 
for existing uses as follows:
    Almond, 35%; apple, 30%; apricot, 30%; artichoke, 70%; asparagus, 
20%; avocado, 5%; barley, 2.5%; green beans, 2.5%; blueberries, 20%; 
broccoli, 2.5%; cabbage, 10%; caneberries, 70%; cantaloupe, 10%; 
carrots, 2.5%; cauliflower, 2.5%; celery, 2.5%; cherry, 30%; corn, 
2.5%; cotton, 40%; cucumber, 10%; dry beans/peas, 5%; figs, 5%; garlic, 
2.5%; grapefruit, 15%; grapes, 30%; hazelnut, 70%; kiwifruit, 30%; 
lemon, 5%; lettuce, 2.5%; nectarine, 20%; olive, 2.5%; onion, 10%; 
orange, 15%; peach, 45%; peanut, 45%; pear, 20%; green peas, 2.5%; 
pecan, 10%; peppers, 15%; pistachio, 35%; plum/prune, 20%; potato, 10%; 
pumpkin, 10%; rice, 2.5%; sorghum, 2.5%; soybean, 2.5%; spinach, 5%; 
squash, 20%; strawberry, 20%; sugar beet, 2.5%; sugarcane, 10%; 
sunflower, 2.5%; sweet corn, 2.5%; tangelos, 10%; tangerine, 5%; 
tomato, 30%; walnut, 20%; watermelon, 15%; and wheat, 2.5%.
    The Agency estimated the PCT in the chronic dietary risk assessment 
for existing uses as follows:
    Almond, 25%; apple, 20%; apricot, 10%; artichoke, 30%; asparagus, 
10%; avocado, 5%; barley, 1%; green beans, 1%; blueberries, 15%; 
broccoli, 1%; cabbage, 2.5%; caneberries, 45%;

[[Page 64320]]

cantaloupe, 5%; carrots, 1%; cauliflower, 1%; celery, 1%; cherry, 20%; 
corn, 2.5%; cotton, 20%; cucumber, 5%; dry beans/peas, 2.5%; figs, 5%; 
garlic, 1%; grapefruit, 5%; grapes, 15%; hazelnut, 55%; kiwifruit, 30%; 
lemon, 2.5%; lettuce, 1%; nectarine, 10%; olive, 2.5%; onion, 5%; 
orange, 5%; peach, 30%; peanut, 25%; pear, 10%; green peas, 1%; pecan, 
5%; peppers, 10%; pistachio, 25%; plum/prune, 10%; potato, 5%; pumpkin, 
5%; rice, 1%; sorghum, 1%; soybean, 1%; spinach, 2.5%; squash, 5%; 
strawberry, 5%; sugar beet, 1%; sugarcane, 5%; sunflower, 1%; sweet 
corn, 1%; tangelo, 10%; tangerine, 5%; tomato, 10%; walnut, 15%; 
watermelon, 5%; and wheat, 1%.
    In most cases, EPA uses available data from United States 
Department of Agriculture/National Agricultural Statistics Service 
(USDA/NASS), proprietary market surveys, and the National Pesticide Use 
Database for the chemical/crop combination for the most recent 6-7 
years. EPA uses an average PCT for chronic dietary risk analysis. The 
average PCT figure for each existing use is derived by combining 
available public and private market survey data for that use, averaging 
across all observations, and rounding to the nearest 5%, except for 
those situations in which the average PCT is less than one. In those 
cases, 1% is used as the average PCT and 2.5% is used as the maximum 
PCT. EPA uses a maximum PCT for acute dietary risk analysis. The 
maximum PCT figure is the highest observed maximum value reported 
within the recent 6 years of available public and private market survey 
data for the existing use and rounded up to the nearest multiple of 5%.
    The Agency believes that the three conditions discussed in Unit 
III.C.1.iv. have been met. With respect to Condition a, PCT estimates 
are derived from Federal and private market survey data, which are 
reliable and have a valid basis. The Agency is reasonably certain that 
the percentage of the food treated is not likely to be an 
underestimation. As to Conditions b and c, regional consumption 
information and consumption information for significant subpopulations 
is taken into account through EPA's computer-based model for evaluating 
the exposure of significant subpopulations including several regional 
groups. Use of this consumption information in EPA's risk assessment 
process ensures that EPA's exposure estimate does not understate 
exposure for any significant subpopulation group and allows the Agency 
to be reasonably certain that no regional population is exposed to 
residue levels higher than those estimated by the Agency. Other than 
the data available through national food consumption surveys, EPA does 
not have available reliable information on the regional consumption of 
food to which paraquat may be applied in a particular area.
    2. Dietary exposure from drinking water. In the past the EPA has 
concluded that though paraquat undergoes minimal degradation in the 
environment, and thus is very persistent (as parent), paraquat residues 
are not expected in surface or ground water. Paraquat has a very high 
propensity to bind to solids, particularly clay, which makes it very 
immobile. In addition, paraquat does not readily appear to desorb from 
clay. The greatest cause for concern is likely to be erosion of 
contaminated sediments off-site and subsequent redeposition onto non-
target areas (especially surface water bodies). Because of its very low 
mobility and strong tendency to bind tightly to soils, paraquat 
contamination of drinking water supplies derived from groundwater is 
expected to be highly unlikely. In addition, the strong binding 
characteristics of paraquat dichloride are likely to render most 
residues in raw drinking water sources removable through sedimentation 
processes, which are typically included as part of standard drinking 
water treatments.
    Because of its strong cation-exchange sorption to soils, modeling 
is not appropriate for paraquat. In most circumstances, the levels of 
paraquat residues in surface or ground water are expected to be 
insignificant. Because it should sorb to suspended sediment, 
coagulation and flocculation processes in drinking water treatment 
plants are likely to remove any paraquat dichloride residues present in 
the raw water. Residues of paraquat dichloride in drinking water 
derived from surface supplies can therefore be assumed to be 
negligible.
    In order to determine the most appropriate and realistic drinking 
water numbers to use in the human health risk assessment, the Agency 
reviewed a non-guideline supplemental mobility study that was conducted 
to evaluate the effects of traditional water treatment processes on 
paraquat and to determine the mobility of paraquat through soil 
filtration column. \14\C-paraquat, spiked at around 30 parts per 
billion (ppb) into the raw surface water samples from five 
representative U.S community water supply facilities, was effectively 
removed by a combination of typical water treatment processes conducted 
on a laboratory-scale: The ``laboratory jar test'' (coagulation using 
alum with either lime or soda ash, flocculation and sedimentation), 
followed by duel media filtration (anthracite atop of filtering sand). 
The combination process was able to reduce the level of \14\C-paraquat 
to approximate or below the limit of detection of approximately 0.15 
[micro]g/L (ppb). The level of paraquat in the finished water of 0.15 
ppb was used in both the acute and chronic assessments.
    3. From non-dietary exposure. The term ``residential exposure'' is 
used in this document to refer to non-occupational, non-dietary 
exposure (e.g., for lawn and garden pest control, indoor pest control, 
termiticides, and flea and tick control on pets).
    Paraquat is not registered for any specific use patterns that would 
result in residential exposure.
    4. Cumulative effects from substances with a common mechanism of 
toxicity. Section 408(b)(2)(D)(v) of FFDCA requires that, when 
considering whether to establish, modify, or revoke a tolerance, the 
Agency consider ``available information'' concerning the cumulative 
effects of a particular pesticide's residues and ``other substances 
that have a common mechanism of toxicity.''
    EPA has not found paraquat to share a common mechanism of toxicity 
with any other substances, and paraquat does not appear to produce a 
toxic metabolite produced by other substances. For the purposes of this 
tolerance action, therefore, EPA has assumed that paraquat does not 
have a common mechanism of toxicity with other substances. For 
information regarding EPA's efforts to determine which chemicals have a 
common mechanism of toxicity and to evaluate the cumulative effects of 
such chemicals, see EPA's Web site at http://www.epa.gov/pesticides/cumulative.

D. Safety Factor for Infants and Children

    1. In general. Section 408(b)(2)(C) of FFDCA provides that EPA 
shall apply an additional tenfold (10X) margin of safety for infants 
and children in the case of threshold effects to account for prenatal 
and postnatal toxicity and the completeness of the database on toxicity 
and exposure unless EPA determines based on reliable data that a 
different margin of safety will be safe for infants and children. This 
additional margin of safety is commonly referred to as the Food Quality 
Protection Act Safety Factor (FQPA SF). In applying this provision, EPA 
either retains the default value of 10X, or uses a different additional 
safety factor when reliable data available to EPA support the choice of 
a different factor.

[[Page 64321]]

    2. Prenatal and postnatal sensitivity. Prenatal developmental 
studies in rats and mice show that developmental effects only occur in 
the presence of maternal toxicity. No effect on reproduction was 
observed. Fetal effects were limited to delayed ossification and 
decreased body weights, which are considered lesser in severity than 
the effects observed in maternal animals. There was no indication from 
these studies that paraquat dichloride is involved in endocrine 
disruption.
    3. Conclusion. EPA has determined that reliable data show the 
safety of infants and children would be adequately protected if the 
FQPA SF were reduced to 1X. That decision is based on the following 
findings:
    i. The toxicity database for paraquat is complete.
    ii. There is no indication that paraquat is a neurotoxic chemical 
and there is no need for a developmental neurotoxicity study or 
additional UFs to account for neurotoxicity.
    iii. There is no evidence that paraquat results in increased 
susceptibility in in utero rats or rabbits in the prenatal 
developmental studies or in young rats in the 2-generation reproduction 
study.
    iv. There are no residual uncertainties identified in the exposure 
databases. The acute dietary exposure analysis is based on tolerance 
level residues and maximum estimates of percent crop treated. The 
chronic analysis is based on tolerance level residues and average 
estimates of PCT. For estimating levels of paraquat in drinking water, 
the Agency relied on a study that evaluated the effects of traditional 
water treatment processes on paraquat. These assessments will not 
underestimate the exposure and risks posed by paraquat.

E. Aggregate Risks and Determination of Safety

    EPA determines whether acute and chronic dietary pesticide 
exposures are safe by comparing aggregate exposure estimates to the 
acute PAD (aPAD) and chronic PAD (cPAD). For linear cancer risks, EPA 
calculates the lifetime probability of acquiring cancer given the 
estimated aggregate exposure. Short-, intermediate-, and chronic-term 
risks are evaluated by comparing the estimated aggregate food, water, 
and residential exposure to the appropriate PODs to ensure that an 
adequate MOE exists.
    1. Acute risk. Using the exposure assumptions discussed in this 
unit for acute exposure, the acute dietary exposure from food and water 
to paraquat will occupy 75% of the aPAD for children 1-2 years old, the 
population group receiving the greatest exposure.
    2. Chronic risk. Using the exposure assumptions described in this 
unit for chronic exposure, EPA has concluded that chronic exposure to 
paraquat from food and water will utilize 27% of the cPAD for children 
1-2 years old, the population group receiving the greatest exposure. 
There are no residential uses for paraquat.
    3. Short- and Intermediate-term risk. Short- and intermediate-term 
aggregate exposure takes into account short- and intermediate-term 
residential exposure plus chronic exposure to food and water 
(considered to be a background exposure level). A short- and 
intermediate-term adverse effect was identified; however, paraquat is 
not registered for any use patterns that would result in short- and/or 
intermediate-term residential exposure. Short- and intermediate-term 
risk is assessed based on short- and intermediate-term residential 
exposure plus chronic dietary exposure. Because there is no short- and 
intermediate-term residential exposure and chronic dietary exposure has 
already been assessed under the appropriately protective cPAD (which is 
at least as protective as the POD used to assess short- and 
intermediate-term risk), no further assessment of short- and 
intermediate-term risk is necessary, and EPA relies on the chronic 
dietary risk assessment for evaluating short- and intermediate-term 
risk for paraquat.
    4. Aggregate cancer risk for U.S. population. Based on the lack of 
evidence of carcinogenicity in two adequate rodent carcinogenicity 
studies, paraquat is not expected to pose a cancer risk to humans.
    5. Determination of safety. Based on these risk assessments, EPA 
concludes that there is a reasonable certainty that no harm will result 
to the general population, or to infants and children from aggregate 
exposure to paraquat residues.

IV. Other Considerations

A. Analytical Enforcement Methodology

    An adequate spectrophotometric method, Method I of the Pesticide 
Analytical Manual (PAM) Vol. II, is available for enforcing tolerances 
for residues of paraquat in/on plant commodities.

B. International Residue Limits

    In making its tolerance decisions, EPA seeks to harmonize U.S. 
tolerances with international standards whenever possible, consistent 
with U.S. food safety standards and agricultural practices. EPA 
considers the international maximum residue limits (MRLs) established 
by the Codex Alimentarius Commission (Codex), as required by FFDCA 
section 408(b)(4). The Codex Alimentarius is a joint United Nations 
Food and Agriculture Organization/World Health Organization food 
standards program, and it is recognized as an international food safety 
standards-setting organization in trade agreements to which the United 
States is a party. EPA may establish a tolerance that is different from 
a Codex MRL; however, FFDCA section 408(b)(4) requires that EPA explain 
the reasons for departing from the Codex level.
    The Codex has established MRLs for paraquat in or on root and tuber 
vegetables at 0.05 ppm. These MRLs are different than the tolerance of 
5.0 ppm that will be established for the tuberous and corm vegetables 
subgroup 1C for residues of paraquat in the United States. The Agency 
cannot harmonize with the Codex MRL because available residue data 
demonstrates that application of paraquat in accordance with approved 
label directions could result in residues that exceed 0.05 ppm.

V. Conclusion

    Therefore, a tolerance is established for residues of paraquat, 
including its metabolites and degradates, in or on the tuberous and 
corm vegetables subgroup 1C at 0.50 ppm.
    In addition, EPA is removing the separate tolerances for cassava, 
ginger, potato, tanier, and true yam tuber because those are subsumed 
within the new tolerance for subgroup 1C.

VI. Statutory and Executive Order Reviews

    This final rule establishes tolerances under FFDCA section 408(d) 
in response to a petition submitted to the Agency. The Office of 
Management and Budget (OMB) has exempted these types of actions from 
review under Executive Order 12866, entitled ``Regulatory Planning and 
Review'' (58 FR 51735, October 4, 1993). Because this final rule has 
been exempted from review under Executive Order 12866, this final rule 
is not subject to Executive Order 13211, entitled ``Actions Concerning 
Regulations That Significantly Affect Energy Supply, Distribution, or 
Use'' (66 FR 28355, May 22, 2001) or Executive Order 13045, entitled 
``Protection of Children from Environmental Health Risks and Safety 
Risks'' (62 FR 19885, April 23, 1997). This final rule does not contain 
any information collections subject to OMB approval under the Paperwork 
Reduction Act (PRA) (44

[[Page 64322]]

U.S.C. 3501 et seq.), nor does it require any special considerations 
under Executive Order 12898, entitled ``Federal Actions to Address 
Environmental Justice in Minority Populations and Low-Income 
Populations'' (59 FR 7629, February 16, 1994).
    Since tolerances and exemptions that are established on the basis 
of a petition under FFDCA section 408(d), such as the tolerance in this 
final rule, do not require the issuance of a proposed rule, the 
requirements of the Regulatory Flexibility Act (RFA) (5 U.S.C. 601 et 
seq.), do not apply.
    This final rule directly regulates growers, food processors, food 
handlers, and food retailers, not States or tribes, nor does this 
action alter the relationships or distribution of power and 
responsibilities established by Congress in the preemption provisions 
of FFDCA section 408(n)(4). As such, the Agency has determined that 
this action will not have a substantial direct effect on States or 
tribal governments, on the relationship between the national government 
and the States or tribal governments, or on the distribution of power 
and responsibilities among the various levels of government or between 
the Federal Government and Indian tribes. Thus, the Agency has 
determined that Executive Order 13132, entitled ``Federalism'' (64 FR 
43255, August 10, 1999) and Executive Order 13175, entitled 
``Consultation and Coordination with Indian Tribal Governments'' (65 FR 
67249, November 9, 2000) do not apply to this final rule. In addition, 
this final rule does not impose any enforceable duty or contain any 
unfunded mandate as described under Title II of the Unfunded Mandates 
Reform Act of 1995 (UMRA) (2 U.S.C. 1501 et seq.).
    This action does not involve any technical standards that would 
require Agency consideration of voluntary consensus standards pursuant 
to section 12(d) of the National Technology Transfer and Advancement 
Act of 1995 (NTTAA) (15 U.S.C. 272 note).

VII. Congressional Review Act

    Pursuant to the Congressional Review Act (5 U.S.C. 801 et seq.), 
EPA will submit a report containing this rule and other required 
information to the U.S. Senate, the U.S. House of Representatives, and 
the Comptroller General of the United States prior to publication of 
the rule in the Federal Register. This action is not a ``major rule'' 
as defined by 5 U.S.C. 804(2).

List of Subjects in 40 CFR Part 180

    Environmental protection, Administrative practice and procedure, 
Agricultural commodities, Pesticides and pests, Reporting and 
recordkeeping requirements.

    Dated: October 16, 2014.
Daniel J. Rosenblatt,
Acting 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.  180.205:
0
a. In the table for paragraph (a), remove the entries for ``Ginger'' 
and ``Potato'' and add alphabetically the entry ``Vegetable, tuberous 
and corm, subgroup 1C'';
0
b. In the table for paragraph (c), remove the entries for and 
``Cassava,'' ``Tanier,'' and ``Yam, true, tuber''.
    The addition reads as follows:


Sec.  180.205  Paraquat; tolerances for residues.

    (a) * * *

------------------------------------------------------------------------
                                                            Parts  per
                        Commodity                             million
------------------------------------------------------------------------
 
                                * * * * *
Vegetable, tuberous and corn, subgroup 1C...............            0.50
 
                                * * * * *
------------------------------------------------------------------------

* * * * *
[FR Doc. 2014-25592 Filed 10-28-14; 8:45 am]
BILLING CODE 6560-50-P


