Final Rule.

　　SUMMARY

　　This regulation establishes tolerances for residues of saflufenacil in or on pomegranate. BASF Corporation requested these tolerances under the Federal Food, Drug, and Cosmetic Act (FFDCA).

　　TABLE OF CONTENTS

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　　DATES:

　　ADDRESSES:

　　FOR FURTHER INFORMATION CONTACT:

　　SUPPLEMENTARY INFORMATION:

　　I. General Information

　　A. Does this action apply to me?

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

　　C. How can I file an objection or hearing request?

　　II. Summary of Petitioned-For Tolerance

　　III. Aggregate Risk Assessment and Determination of Safety

　　A. Toxicological Profile

　　B. Toxicological Points of Departure/Levels of Concern

　　C. Exposure Assessment

　　D. Safety Factor for Infants and Children

　　E. Aggregate Risks and Determination of Safety

　　IV. Other Considerations

　　A. Analytical Enforcement Methodology

　　B. Internatio nal Residue Limits

　　C. Respo nse to Comments

　　V. Conclusion

　　VI. Statutory and Executive Order Reviews

　　VII. Co ngressional Review Act

　　List of Subjects in 40 CFR Part 180

　　PART 180—[AMENDED]

　　TABLES

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　　Table 1—Summary of Toxicological Doses and Endpoints for Saflufenacil for Use in Human Health Risk Assessment

　　DATES:

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　　This regulation is effective November 25, 2015. Objections and requests for hearings must be received on or before January 25, 2016, 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:

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　　The docket for this action, identified by docket identification (ID) number EPA-HQ-OPP-2014-0640, is available at http://www.regulations.gov or at the Office of Pesticide Programs Regulatory Public Docket (OPP Docket) in the Enviro nmental Protection Agency Docket Center (EPA/DC), West William Jefferson Clinton Bldg., Rm. 3334, 1301 Co nstitution Ave. NW., Washington, DC 20460-0001. The Public Reading Room is open from 8:30 a.m. to 4:30 p.m., Mo nday 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 additio nal information a bout the docket available at http://www.epa.gov/dockets.

　　FOR FURTHER INFORMATION CONTACT:

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

　　SUPPLEMENTARY INFORMATION:

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　　I. General Information

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　　A. Does this action apply to me?

　　You may be potentially affected by this action if you are an agricultural producer, food manufacturer, or pesticide manufacturer. The following list of North American Industrial Classification System (NAICS) codes is not intended to be exhaustive, but rather provides a guide to help readers determine whether this docu ment 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 electro nic access to other related information?

　　You may access a frequently updat ed electro nic 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-2014-0640 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 January 25, 2016. 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 Co nfidential Business Information (CBI)) for inclusion in the public docket. Information not marked co nfidential 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-2014-0640, by one of the following methods:

　　Federal eRulemaking Portal: http://www.regulations.gov. Follow the o nline instructions for submitting comments. Do not submit electro nically any information you co nsider to be CBI or other information whose disclosure is restricted by statute.

　　Mail: OPP Docket, Enviro nmental 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. Additio nal instructions on commenting or visiting the docket, along with more information a bout dockets generally, is available at http://www.epa.gov/dockets.

　　II. Summary of Petitioned-For Tolerance

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　　In the Federal Register of February 11, 2015, (80 FR 7559) (FRL-9921-94), EPA issued a docu ment pursuant to FFDCA section 408(d)(3), 21 U.S.C. 346a(d)(3), announcing the filing of a pesticide petition (PP) 4F8305 by BASF Corporation, 26 Davis Drive, P.O. Box 13528, Research Triangle Park, NC 27709-3528. The petition requested that 40 CFR 180.649 be amended by establishing tolerances for residues of the herbicide, saflufenacil (2-chloro-5-[3,6-dihydro-3-methyl-2,6-dioxo-4-(trifluoromethyl)-1(2 H)-pyrimidinyl]-4-fluoro-N-[[methyl(1-methylethyl) amino]sulfonyl]benzamide) and its me tabolites, in or on pomegranate at 0.03 parts per million (ppm). That docu ment referenced a summary of the petition prepared by BASF Corporation, the registrant, which is available in the docket, http://www.regulations.gov. Comments were received on the notice of filing. EPA's respo nse to these comments is discussed in Unit IV.C.

　　III. Aggregate Risk Assessment and Determination of Safety

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　　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) o nly if EPA determines that the tolerance is “safe.” Section 408(b)(2)(A)(ii) of FFDCA defines “safe” to mean that “there is a reaso nable 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 occupatio nal exposure. Section 408(b)(2)(C) of FFDCA requires EPA to give special co nsideration to exposure of infants and children to the pesticide chemical residue in establishing a tolerance and to “ensure that there is a reaso nable certainty that no harm will result to infants and children from aggregate exposure to the pesticide chemical residue. . . .”

　　Co nsistent 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 hassufficient data to assess the hazards of and to make a determination on aggregate exposure for saflufenacil, including exposure resulting from the tolerances established by this action. EPA's assessment of exposures and risks associated with saflufenacil follows.

　　A. Toxicological Profile

　　EPA has e valuated the available toxicity data and co nsidered its validity, completeness, and reliability as well as the relatio nship of the results of the studies to human risk. EPA has also co nsidered available information co ncerning the variability of the sensitivities of major identifiable subgroups of consumers, including infants and children.

　　The effects observed following repeated oral exposures to saflufenacil are co nsistent with the proposed mode of toxicity involving inhibition of protoporphyrinogen oxidase (PPO) in mammals, resulting in disruption of heme biosynthesis. Toxicological effects from subchro nic and chro nic toxicity studies in rats, mice and dogs co nsisted of decreased hematological parameters (RBC, Ht, MCV, MCH, and MCHC) at approximately the same dose level (13-39 mg/kg/day), except in the case of the dog, wher e the effects were seen at a slightly higher dose (50-100 mg/kg/day). In line with the absorption, distribution, me tabolism, and excretion (ADME) findings suggesting that male rats achieve a greater systemic exposure than females, males were the most sensitive sex in mice and rats, with LOAELs approximately 3-4X lower than their female counterparts. The hematological effects resulting from oral exposures to saflufenacil occurred around the same dose level from short- through long-term exposures without increasing in severity. Toxic effects were also seen in the liver (increased organ weight, centrilobular fatty change, lymphoid infiltrate) in mice, the spleen (increased organ weight and extramedullary hematopoiesis) in rats, and in both of these organs (increased iron storage in the liver and extramedullary hematopoiesis in the spleen) in dogs. These effects also occurred around the same dose level from short- through long-term exposures without a progression in severity.

　　Evidence for increased pre- and/or postnatal susceptibility was noted from the developmental toxicity studies in the rat and rabbit and in the 2-generation reproduction study in the rat. Decreased fetal body weights and increased skeletal variations occurred at doses (20 mg/kg/day) that were not maternally toxic in the developmental study in rats. Similarly, in rabbits, increased liver porphyrins in fetuses were observed at doses (200 mg/kg/day) that were not maternally toxic. In the 2-generation reproductive toxicity study in rats, there was evidence of increased qualitative susceptibility ba sed on an increased number of stillborn pups, decreased pup viability and lactation indices, decreased pre-weaning body-weight and/or body-weight gain, and changes in hematological parameters at the same dose level as less severe maternal effects co nsisting of decrements in food intake, body-weight, body-weight gain, and changes in organ weights and hematological parameters indicative of anemia.

　　In an acute neurotoxicity (ACN) study in rats, a decrease in motor activity was observed on the day of dosing at the limit dose (2,000 mg/kg/day) in males only. However, the finding was not accompanied by any neuropathological changes and was co nsidered a reflection of a mild and transient general systemic toxicity and not a substance-specific neurotoxic effect. In the subchro nic neurotoxicity (SCN) study, systemic toxicity (anemia) was seen at 1,000 ppm (66.2 mg/kg/day) and 1,350 ppm (101 mg/kg/day) in males and females, respectively. There was no evidence of neurotoxicity or neuropathology in either the acute or subchro nic neurotoxicity study.

　　In a 28-day dermal toxicity study in rats, saflufenacil did not induce any type of dermal or systemic toxicity up to the limit dose of 1,000 mg/kg bw/day.

　　ba sed on the results of acute toxicity studies, saflufenacil was ranked low for acute toxicity via the oral, dermal, and inhalation route of exposure. It was not classified as a dermal irritant or dermal sensitizer.

　　In a 28-day immunotoxicity study in mice, saflufenacil failed to induce toxicity specific to the immune system at the highest dose tested (i.e., 52 mg/kg bw/day).

　　Saflufenacil was weakly clastogenic in the in vitro chromosomal aberration assay in V79 cells in the presence of S9 activation; however, the respo nse was not evident in the absence of S9 activation. It was neither mutagenic in bacterial cells nor clastogenic in rodents in vivo. Carcinogenicity studies in rats and mice showed no evidence of increased incidence of tumors at the tested doses. Saflufenacil is classified as “not likely carcinogenic to humans.”

　　Specific information on the studies received and the nature of the adverse effects caused by saflufenacil as well as the no-observed-adverse-effect-level (NOAEL) and the lowest-observed-adverse-effect-level (LOAEL) from the toxicity studies can be found at http://www.regulations.gov in docu ment Saflufenacil. “Human Health Risk Assessment in Support of Tolerances for Residues in/on Pomegranate” pgs. 26-30 in docket ID number EPA-HQ-OPP-2014-0640.

　　B. Toxicological Points of Departure/Levels of Concern

　　o nce a pesticide's toxicological profile is determined, EPA identifies toxicological points of departure (POD) and levels of co ncern to use in e valuating 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 ba sed 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 co ncern are identified (the LOAEL). Uncertainty/safety factors are used in co njunction 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 des cription of the risk assessment process, see http://www2.epa.gov/pesticide-science-and-assessing-pesticide-risks/assessing-human-health-risk-pesticides.

　　A summary of the toxicological endpoints for saflufenacil used for human risk assessment is shown in Table 1 of this unit.

　　Table 1—Summary of Toxicological Doses and Endpoints for Saflufenacil for Use in Human Health Risk Assessment Back to Top

　　Exposure/scenarioPoint of departure and uncertainty/safety factorsRfD, PAD, LOC for risk assessmentStudy and toxicological effects

　　FQPA SF = Food Quality Protection Act Safety Factor. LOAEL = lowest-observed-adverse-effect-level. LOC = level of concern. mg/kg/day = milligram/kilogram/day. NOAEL = no-observed-adverse-effect-level. PAD = population adjusted dose (a = acute, c = chronic). RfD = reference dose. UF = uncertainty factor. UF A= extrapolation from animal to human (interspecies). UF H= potential variation in sensitivity among members of the human population (intraspecies).

　　Acute dietary (General population including infants and children)NOAEL = 500 mg/kg bw UF A= 10x UF H= 10x FQPA SF = 1xAcute RfD = 5 mg/kg aPAD = 5 mg/kgAcute Neurotoxicity Study (rat). LOAEL = 2,000 mg/kg bw ba sed on decreased motor activity representing mild and transient systemic toxicity in males.

　　Chro nic dietary (All populations)NOAEL = 4.6 mg/kg/day UF A=10x UF H= 10x FQPA SF = 1xChro nic RfD = 0.046mg/kg/day cPAD = 0.046 mg/kg/dayChronic/Carcinogenicity (mouse). LOAEL = 13.8 mg/kg bw/day ba sed on decreased red blood cells, hemoglobin, hematocrit, and porphyria observed in the satellite group.

　　C. Exposure Assessment

　　1. Dietary exposure from food and feed uses. In e valuating dietary exposure to saflufenacil, EPA co nsidered exposure under the petitioned-for tolerances as well as all existing saflufenacil tolerances in 40 CFR 180.649. EPA assessed dietary exposures from saflufenacil in food as follows:

　　i. Acute exposure. Quantitative acute dietary exposure and risk assessments are performed for a food-use pesticide, if a toxicological study has indicated the possibility of an effect of co ncern occurring as a result of a 1-day or single exposure.

　　Such effects were identified for saflufenacil. In estimating acute dietary exposure, EPA used food co nsumption information from the United States Department of Agriculture (USDA) Natio nal Health and Nutrition Examination Survey, What We Eat in America, (NHANES/WWEIA; 2003-2008). As to residue levels in food, EPA used an unrefined approach by assuming that 100% of the crop is treated and that residues are present at the tolerance-level or at tolerance-levels adjusted to account for the residues of co ncern for risk assessment for all foods. EPA also used default processing factors using the Dietary Exposure e valuation Model (DEEM) 7.8.

　　ii. Chro nic exposure. In co nducting the chro nic dietary exposure assessment EPA used the same co nservative assumptions that were used for the acute dietary assessment noted above.

　　iii. Cancer. ba sed on the data summarized in Unit III.A., EPA has co ncluded that saflufenacil does not pose a cancer risk to humans. Therefore, a dietary exposure assessment for the purpose of assessing cancer risk is unnecessary.

　　iv. Anticipated residue and percent crop treated (PCT) information. EPA did not use anticipated residue and/or PCT information in the dietary assessment for saflufenacil. Tolerance-level residues and/or 100% CT were assumed for all food commodities.

　　2. Dietary exposure from drinking water. The Agency used screening-level water exposure models in the dietary exposure analysis and risk assessment for saflufenacil in drinking water. These simulation models take into account data on the physical, chemical, and fate/transport characteristics of saflufenacil. Further information regarding EPA drinking water models used in pesticide exposure assessment can be found at http://www2.epa.gov/pesticide-science-and-assessing-pesticide-risks/a bout-water-exposure-models-used-pesticide.

　　ba sed on the Tier 1 Rice Model and Pesticide Root Zone Model Ground Water (PRZM GW), the estimated drinking water co ncentrations (EDWCs) of saflufenacil for acute exposures are estimated to be 133 parts per billion (ppb) for surface water and 69.2 ppb for ground water.

　　The EDWCs for chro nic exposures for non-cancer assessments are estimated to be 120 ppb for surface water and 51.5 ppb for ground water.

　　Modeled estimates of drinking water co ncentrations were directly entered into the dietary exposure model. For acute dietary risk assessment, the water co ncentration value of 133 ppb was used to assess the co ntribution to drinking water. For chro nic dietary risk assessment, the water co ncentration of value 120 ppb was used to assess the co ntribution to drinking water.

　　3. From non-dietary exposure. The term “residential exposure” is used in this docu ment to refer to non-occupational, non-dietary exposure (e.g., for lawn and garden pest control, indoor pest control, termiticides, and flea and tick co ntrol on pets).

　　Saflufenacil is not registered for any specific use patterns that would result in residential exposure.

　　4. Cumulative effects from substances with a common mechanism of toxicity. Section 408(b)(2)(D)(v) of FFDCA requires that, when co nsidering whether to establish, modify, or revoke a tolerance, the Agency co nsider “available information” co ncerning the cumulative effects of a particular pesticide's residues and “other substances that have a common mechanism of toxicity.”

　　EPA has not found saflufenacil to share a common mechanism of toxicity with any other substances, and saflufenacil does not appear to produce a toxic me tabolite produced by other substances. For the purposes of this tolerance action, therefore, EPA has assumed that saflufenacil does not have a common mechanism of toxicity with other substances. For information regarding EPA's efforts to determine which chemicals have a common mechanism of toxicity and to e valuate the cumulative effects of such chemicals, see EPA's Web site at http://www2.epa.gov/pesticide-science-and-assessing-pesticide-risks/cumulative-assessment-risk-pesticides.

　　D. Safety Factor for Infants and Children

　　1. In general. Section 408(b)(2)(C) of FFDCA provides that EPA shall apply an additio nal 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 databa se on toxicity and exposure unless EPA determines ba sed on reliable data that a different margin of safety will be safe for infants and children. This additio nal margin ofsafety is commo nly referred to as the FQPA Safety Factor (SF). In applying this provision, EPA either retains the default value of 10X, or uses a different additio nal safety factor when reliable data available to EPA support the choice of a different factor.

　　2. Prenatal and postnatal sensitivity. As discussed in III.A., there is evidence of increased pre- and/or postnatal susceptibility in the developmental toxicity studies in the rat and rabbit and in the 2-generation reproduction study in the rat. The co ncern for increased susceptibility following prenatal or postnatal exposure is low because clear NOAELs/LOAELs were established for the developmental effects seen in rats and rabbits as well as for the offspring effects seen in the 2-generation reproductive toxicity study. Further, the dose-respo nse relatio nship for the effects of co ncern are also well characterized and being used for assessing risks. The point of departure for risk assessments would be protective of the developmental and offspring effects.

　　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 ba sed on the following findings:

　　i. The toxicity databa se for saflufenacil is complete.

　　ii. There was no evidence of neurotoxicity or neuropathology in the acute and subchro nic neurotoxicity study. The decrease in motor activity observed in the acute neurotoxicity study on the day of dosing at the limit dose (2,000 mg/kg/day) in males is co nsidered a reflection of a mild and transient general systemic toxicity and not a substance-specific neurotoxic effect. No neurotoxic effects were seen in the sub-chro nic neurotoxicity study.

　　iii. The co ncern for increased susceptibility following prenatal or postnatal exposure is low because clear NOAELs/LOAELs were established for the developmental effects seen in rats and rabbits as well as for the offspring effects seen in the 2-generation reproductive toxicity study. Further, the dose-respo nse relatio nship for the effects of co ncern are also well characterized and being used for assessing risks. The POD for risk assessments would be protective of the developmental and offspring effects.

　　iv. There are no residual uncertainties identified in the exposure databa ses. The dietary food exposure assessments were performed ba sed on 100% CT and tolerance-level residues. EPA made co nservative (protective) assumptions in the ground and surface water modeling used to assess exposure to saflufenacil in drinking water. These assessments will not underestimate the exposure and risks posed by saflufenacil.

　　E. Aggregate Risks and Determination of Safety

　　EPA determines whether acute and chro nic dietary pesticide exposures are safe by comparing aggregate exposure estimates to the acute PAD (aPAD) and chro nic 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 e valuated by comparing the estimated aggregate food, water, and residential exposure to the appropriate PODs to ensure that an adequate MOE exists.

　　1. Acute risk. Using the exposure assumptions discussed in this unit for acute exposure, the acute dietary exposure from food and water to saflufenacil will occupy less than 1% of the aPAD for all infants (<1-year old), the population group receiving the greatest exposure.

　　2. Chro nic risk. Using the exposure assumptions described in this unit for chro nic exposure, EPA has co ncluded that chro nic exposure to saflufenacil from food and water will utilize 20% of the cPAD for all infants (<1-year old) the population group receiving the greatest exposure. There are no residential uses for saflufenacil.

　　3. Short-term and intermediate-term risk. Short-term aggregate exposure takes into account short-term residential exposure plus chro nic exposure to food and water (co nsidered to be a background exposure level). Intermediate-term aggregate exposure takes into account intermediate-term residential exposure plus chro nic exposure to food and water. Since there are no registered or proposed residential uses for saflufenacil that would result in short or intermediate-term residential exposures, and chro nic dietary exposure has already been assessed under the appropriately protective cPAD (which is at least as protective as the POD used to assess short-term risk), no further assessment of short or intermediate-term risk is necessary, and EPA relies on the chro nic dietary risk assessment for e valuating short and intermediate-term risk for saflufenacil.

　　4. Aggregate cancer risk for U.S. population. ba sed on the lack of evidence of carcinogenicity in two adequate rodent carcinogenicity studies, saflufenacil is not expected to pose a cancer risk to humans.

　　5. Determination of safety. ba sed on these risk assessments, EPA co ncludes that there is a reaso nable certainty that no harm will result to the general population, or to infants and children from aggregate exposure to saflufenacil residues.

　　IV. Other Considerations

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　　A. Analytical Enforcement Methodology

　　Adequate enforcement methodology (liquid chromatography/mass spectroscopy/mass spectroscopy (LC/MS/MS) Method D0603/02) is available to enforce the tolerance ex pression. The method may be requested from: Chief, Analytical Chemistry Branch, Enviro nmental Science Center, 701 Mapes Rd., Ft. Meade, MD 20755-5350; telephone number: (410) 305-2905; email address: residuemethods@epa.gov.

　　B. Internatio nal Residue Limits

　　In making its tolerance decisions, EPA seeks to harmo nize U.S. tolerances with internatio nal standards whenever possible, co nsistent with U.S. food safety standards and agricultural practices. EPA co nsiders the internatio nal 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 internatio nal 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 not established a MRL for saflufenacil on pomegranate. Therefore, harmo nization of MRLs and U.S. tolerances is not an issue at this time.

　　C. Respo nse to Comments

　　EPA received two comments to the docket, EPA-HQ-OPP-2014-0640; however, o nly one of these public submissions was in respo nse to the Notice of Filing for PP# 4F8305, while the remaining comment pertained to an unrelated petition in the Federal Register notice. For PP# 4F8305, the commenter stated that they are in support of actions to set tolerance levels for pesticides on the food we eat and that we are taking a step in the right direction by making it safer for human co nsumption by placing more regulations on pesticide chemicals.

　　EPA agrees with the commenter and will co ntinue to regulate pesticidesunder the legal f ramework provided by the Federal Insecticide, Fungicide, Rodenticide Act (FIFRA) and Section 408 of the Federal Food, Drug and Cosmetic Act (FFDCA), which allows EPA to assess the risk of pesticides and set tolerance levels for those pesticides on food commodities as deemed necessary to protect human health while still providing tools for growers so that they can meet the ever-growing food demands of this country and others.

　　V. Conclusion

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　　Therefore, tolerances are established for residues of saflufenacil, (2-chloro-5-[3,6-dihydro-3-methyl-2,6-dioxo-4-(trifluoromethyl)-1(2H)-pyrimidinyl]-4-fluoro-N-[[methyl(1-methylethyl)amino]sulfonyl]benzamide) and its me tabolites, in or on pomegranate at 0.03 ppm.

　　VI. Statutory and Executive Order Reviews

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　　This action establishes a tolerance under FFDCA section 408(d) in respo nse 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 Co ncerning Regulations That Significantly Affect Energy Supply, Distribution, or Use” (66 FR 28355, May 22, 2001) or Executive Order 13045, entitled “Protection of Children from Enviro nmental Health Risks and Safety Risks” (62 FR 19885, April 23, 1997). This action does not co ntain 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 co nsiderations under Executive Order 12898, entitled “Federal Actions to Address Enviro nmental 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 relatio nships or distribution of power and respo nsibilities established by Co ngress 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 relatio nship between the natio nal government and the States or tribal governments, or on the distribution of power and respo nsibilities 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 “Co nsultation 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 co ntain 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 co nsideration of voluntary co nsensus standards pursuant to section 12(d) of the Natio nal Technology Transfer and Advancement Act (NTTAA) (15 U.S.C. 272 note).

　　VII. Co ngressional Review Act

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　　Pursuant to the Co ngressional Review Act (5 U.S.C. 801 et seq.), EPA will submit a report co ntaining 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

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　　Enviro nmental protection

　　Administrative practice and procedure

　　Agricultural commodities

　　Pesticides and pests

　　Reporting and recordkeeping requirements

　　Dated: November 17, 2015.

　　Susan Lewis,

　　Director, Registration Division, Office of Pesticide Programs.

　　Therefore, 40 CFR chapter I is amended as follows:

1.The authority citation for part 180 continues to read as follows:

2.In § 180.649, add alphabetically the entry to the table in paragraph (a)(1) to read as follows:

§ 180.649 Saflufenacil; tolerances for residues.