Source: https://www.federalregister.gov/documents/2018/11/13/2018-24379/cyantraniliprole-pesticide-tolerances
Timestamp: 2019-01-15 23:21:08
Document Index: 778972490

Matched Legal Cases: ['art 178', 'art 180', 'art 178', 'art 178', 'art 2', 'art 180', '§\u2009180']

This regulation is effective November 13, 2018. Objections and requests for hearings must be received on or before January 14, 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).
56262-56269 (8 pages)
FRL-9985-32
https://www.federalregister.gov/d/2018-24379 https://www.federalregister.gov/d/2018-24379
This regulation establishes tolerances for residues of cyantraniliprole in or on multiple commodities which are identified and discussed later in this document. The Interregional Research Project No. 4 (IR-4) and DuPont Crop Protection requested these tolerances under the Federal Food, Drug, and Cosmetic Act (FFDCA).
The docket for this action, identified by docket identification (ID) number EPA-HQ-OPP-2017-0694, 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.
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. To access the OCSPP test guidelines referenced in this document electronically, please go to https://www.epa.gov/​aboutepa/​about-office-chemical-safety-and-pollution-prevention-ocspp and select “Test Methods and Guidelines.”
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-2017-0694 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 14, 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-2017-0694, by one of the following methods:
In the Federal Register of March 21, 2018 (83 FR 12311) (FRL-9974-76), 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 7E8631) by The Interregional Research Project No. 4 (IR-4), Rutgers, The State University of New Jersey, 500 College Road East, Suite 201 W, Princeton, NJ 08540. The petition requested that 40 CFR 180.672 be amended by establishing tolerances for residues of the insecticide, cyantraniliprole, 3-bromo-1-(3-chloro-2-pyridinyl)-N-[4-cyano-2-methyl-6-[((methylamino)carbonyl]phenyl]-1H-pyrazole-5-carboxamide, in or on Berry, low growing, except strawberry, subgroup 13-07H, except blueberry, lowbush and lingonberry at 0.08 parts per million (ppm) (proposal to replace an existing tolerance at the same level that is only for imported Berry, low growing, except strawberry, subgroup 13-07H, with a tolerance supporting both domestic production and imported low growing berries, except strawberries); Brassica, leafy greens, subgroup 4-16B at 30 ppm; Caneberry subgroup 13-07A at 4.0 ppm; Celtuce at 20 ppm; Coffee, green bean at 0.05 ppm (proposal to replace an existing tolerance at the same level that is only for imported Coffee, green bean with a tolerance supporting both domestic production and imported coffee); Florence fennel at 20 ppm; Kohlrabi at 3.0 ppm; Leafy greens subgroup 4-16A at 20 ppm; Leaf petiole vegetable subgroup 22B at 20 ppm; and Vegetable, Start Printed Page 56263 Brassica, head and stem, group 5-16 at 3.0 ppm. Upon the establishment of the above tolerances, IR-4 proposed to remove existing tolerances in 40 CFR part 180.672 in or on the following commodities: Brassica head and stem, subgroup 5A at 3.0 ppm; Brassica leafy vegetables, subgroup 5B at 30 ppm; and Vegetable, leafy, except Brassica, group 4 at 20 ppm.
In the Federal Register of April 11, 2018 (83 FR 15528) (FRL-9975-57), 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 7F8622) by DuPont Crop Protection, Stine-Haskell Research Center, P.O. Box 30, Newark, DE 19714-0030. The petition requested that 40 CFR 180.672 be amended by establishing tolerances for residues of the insecticide cyantraniliprole, 3-bromo-1-(3-chloro-2-pyridinyl)-N-[4-cyano-2-methyl-6-[((methylamino)carbonyl]phenyl]-1H-pyrazole-5-carboxamide, in or on Rice, hulls at 0.05 ppm; Rice, straw at 0.015 ppm; Soybean, forage at 15 ppm; Soybean, hay at 50 ppm; Soybean, hulls at 1 ppm; Soybean, seed at 0.4 ppm; and Aspirated grain fractions at 200 ppm. Upon the approval of the proposed tolerances in soybean forage and hay, it is proposed that the existing tolerances for indirect or inadvertent residues in soybean forage and hay be cancelled. In addition, DuPont Crop Protection requests to amend the tolerances in 40 CFR 180.672, in or on rice, grain at 0.02 ppm by replacing an existing tolerance at the same level that is only for imported grain with a tolerance supporting both domestic production and imported grain.
These documents referenced summaries of the petitions prepared by DuPont Crop Protection, the registrant, which are available in the docket, http://www.regulations.gov. Three comments were received on the notices of filing. EPA's response to these comments is discussed in Unit IV.C.
Based upon review of the data supporting the petition, EPA modified some of the tolerance levels to conform to EPA's rounding classes and revised the commodity terminology for two tolerances. These changes are explained in Unit IV.D.
In general, cyantraniliprole administration in mammalian test species produces both adverse and adaptive changes in the liver, thyroid gland, and adrenal cortex. With repeated dosing, consistent findings of mild to moderate increases in liver weights across multiple species (rats, mice and dogs) are observed. Dogs appear to be more sensitive than rats and mice; cyantraniliprole produces adverse liver effects (increases in alkaline phosphatase, decreases in cholesterol, and decreases in albumin) in dogs at lower dose levels than in rats. In addition, the liver effects in the dog show progressive severity with increased duration of exposure. The available data also show thyroid hormone homeostasis is altered in rats following exposure to cyantraniliprole after 28 or 90 days; however, cyantraniliprole is not a direct thyroid toxicant.
Cyantraniliprole is classified as “not likely to be carcinogenic to humans” based on the absence of increased tumor incidence in acceptable/guideline carcinogenicity studies in rats and mice, and there are no mutagenicity concerns. There are also no developmental or reproductive toxicity concerns and no offspring susceptibility concerns. Cyantraniliprole does not produce developmental toxicity in either rats or rabbits. The 2-generation reproduction study in rats shows that cyantraniliprole has no adverse effect on any reproductive parameters.
Acute and subchronic neurotoxicity studies reveal no evidence of neurotoxicity. Similarly, cyantraniliprole does not adversely impact the immune system in rats and mice. Based on the results of a 28-day dermal study in rats (as well as the dermal LD50 study), cyantraniliprole does not demonstrate any appreciable toxicity via dermal exposure. The 28-day inhalation toxicity study in rats does not show any adverse systemic or portal of entry effect at the highest concentration tested (100 mg/m3, equivalent to 18 mg/kg/day).
Cyantraniliprole has no significant acute toxicity via the oral, dermal, and inhalation routes of exposure. Cyantraniliprole is not an eye or skin irritant and does not cause skin sensitization.
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 Start Printed Page 56264is 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/​pesticide-science-and-assessing-pesticide-risks.
A summary of the toxicological endpoints for cyantraniliprole used for human risk assessment is discussed in Unit III.B of the final rule published in the Federal Register of February 5, 2014 (79 FR 6826) (FRL-9388-7).
ii. Chronic exposure. In conducting the chronic dietary exposure assessment EPA used the food consumption data from the 2003-2008 United States 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, a refined chronic (food and drinking water) dietary assessment was conducted assuming average field trial residues for all crops (except crop subgroup 1A, for which tolerance level residues were assumed); percent crop treated (PCT) data; empirical processing factors; and default processing factors were used as appropriate.
Condition c: If 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 areas.
The Agency estimated the average PCT for existing uses as follows: Citrus: oranges 62%, grapefruit 87%, and lemons 46%; pome fruit: apples 61% and pears 76%; stone fruits: apricots 53%, cherries 48%, peaches 41%, and plums/prunes 59%; tree nuts: almonds 72%, hazelnuts 65%, pecans 22%, pistachios 49%, and walnuts 53%; bushberries (subgroup 13-07B): blueberries 45%; fruiting vegetables: peppers 45% and tomatoes 54%; cucurbits: cantaloupes 50%, cucumbers 23%, pumpkins 18%, squash 24%, and watermelons 29%; leafy vegetables: celery 70%, lettuce 78%, and spinach 53%; Brassica (cole) leafy vegetables: broccoli 81%, cabbage 50%, and cauliflower 83%; onion 58%; potato 50%; oilseeds: canola 15% and sunflower 35%; corn 56%, cotton 41%; peanuts 41%; carrots 23%; soybeans 21%; strawberries 59%; vegetable crop group 7: dry beans/peas 6%, soybeans 21%, beans (snap, bush, etc.) 49%, and peas fresh/green/sweet) 38%; vegetable crop group 2: sugar beets 40%; vegetable crop group 6A: soybeans 21%, beans (snap, bush, etc., string) 49%; peas fresh/green/sweet) 38%; and vegetable crop group 6C: dried bean and peas 6%. 100 PCT was assumed for all other crops, including all proposed new use crops. For imported grapes (wine grapes), a 50% import estimate was used in the chronic dietary risk assessment.
In most cases, EPA uses available data from United States Department of Agriculture/National Agricultural Statistics Service (USDA/NASS), proprietary market surveys, and California Department of Pesticide Regulation (CDPR) Pesticide Use Reporting (PUR) for the chemical/crop combination for the most recent 10 years. EPA uses an average PCT for chronic dietary risk analysis and a maximum PCT for acute dietary risk analysis. The average PCT figures for each existing use are derived by combining available public and private market survey data for that use, averaging across all observations, and rounding up to the nearest 5%, except for those situations in which the average PCT is less than 1% or less than 2.5%. In those cases, the Agency would use less than 1% or less than 2.5% as the average PCT value, respectively. The maximum PCT figure is the highest observed maximum value reported within the most recent 10 years of available public and private market survey data for the existing use and rounded up to the nearest multiple of 5%, except where the maximum PCT is less than 2.5%, in which case, the Agency uses less than 2.5% as the maximum PCT.
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 Start Printed Page 56265which cyantraniliprole may be applied in a particular area.
2. Dietary exposure from drinking water. The Agency used screening level water exposure models in the dietary exposure analysis and risk assessment for cyantraniliprole in drinking water. These simulation models take into account data on the physical, chemical, and fate/transport characteristics of cyantraniliprole. Further information regarding EPA drinking water models used in pesticide exposure assessment can be found at https://www.epa.gov/​pesticide-science-and-assessing-pesticide-risks/​about-water-exposure-models-used-pesticide.
Based on the Pesticides in Water Calculator (PWC; version 1.52) and Pesticide Root Zone Model Ground Water (PRZM GW) for ground water and FQPA Index Reservoir Screening Tool (FIRST) for surface water, the estimated drinking water concentrations (EDWCs) of cyantraniliprole for chronic exposures for non-cancer assessments are estimated to be 24 ppb for surface water and 64 ppb for ground water.
Modeled estimates of drinking water concentrations were directly entered into the dietary exposure model. For chronic dietary risk assessment, the water concentration value of 64 ppb was used to assess the contribution to drinking water.
Cyantraniliprole is currently registered for the following uses that could result in residential exposures: Turf grass (including residential, recreational, and golf course turf), ornamentals, and structural buildings (including indoor crack/crevice and outdoor broadcast). EPA assessed residential exposure using the following assumptions: EPA determined that residential exposures may occur by the dermal, oral, and inhalation routes of exposures. However, since dermal hazard has not been identified for cyantraniliprole, the only exposures of concern are handler inhalation (for adults), and post-application incidental oral (for children). Residential handler exposure is expected to be short-term in duration. The turf and ornamental labels indicate that a maximum of two applications are allowed per season. Thus, intermediate-term handler exposures are not likely because of the intermittent nature of applications by homeowners. Post-application incidental oral exposures for children may occur for short- and intermediate-term durations due to the persistence of cyantraniliprole. Further information regarding EPA standard assumptions and generic inputs for residential exposures may be found at https://www.epa.gov/​pesticide-science-and-assessing-pesticide-risks/​standard-operating-procedures-residential-pesticide.
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 cyantraniliprole to share a common mechanism of toxicity with any other substances, and cyantraniliprole does not appear to produce a toxic metabolite produced by other substances. For the purposes of this tolerance action, therefore, EPA has assumed that cyantraniliprole 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/​pesticide-science-and-assessing-pesticide-risks/​cumulative-assessment-risk-pesticides.
2. Prenatal and postnatal sensitivity. There is no evidence of susceptibility in developmental toxicity studies in rats and rabbits. The developmental toxicity study in rats is tested up to the limit dose (1,000 mg/kg/day). In the rabbit developmental toxicity study, decreases in fetal body weight are seen at a dose higher than that resulting in maternal effects. In the reproductive toxicity study, increased incidence of thyroid follicular epithelium hypertrophy/hyperplasia occurs in F1 parental animals at a dose lower than that for the parental (P) generation. A clear NOAEL (1.4 mg/kg/day) is established for F1 parental animals, and the PODs selected for risk assessment from the dog studies (1 or 3 mg/kg/day) are protective of the effect (thyroid effect) seen in the F1 parental animals. In addition, the submitted data support the conclusion that the effects on the thyroid are secondary to effects on the liver. As such, a comparative thyroid study is not required at this time.
iii. There is no evidence that cyantraniliprole 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 exposure databases are complete or are estimated based on data that reasonably account for potential exposures. The chronic dietary food exposure assessment was a refined assessment which assumed average field trial residues for all crops (except crop subgroup 1A); PCT when available; empirical processing factors, if available, or default processing factors, as appropriate. The 2012 Residential standard operating procedures (SOPs) were previously used to assess post-application exposure to children including incidental oral exposure, and the residential post-application assessment assumed that maximum application rates are applied and that hand-to-mouth activities occur on the day of application. All of the exposure estimates are based on conservative, health-protective assumptions and are not likely to underestimate risk. EPA made conservative (protective) assumptions in the ground and surface water modeling used to assess exposure to cyantraniliprole in drinking water. EPA used similarly conservative assumptions to assess post application exposure of children as well as Start Printed Page 56266incidental oral exposure of toddlers. These assessments will not underestimate the exposure and risks posed by cyantraniliprole.
2. Chronic risk. Using the exposure assumptions described in this unit for chronic exposure, EPA has concluded that chronic exposure to cyantraniliprole from food and water will utilize 99% of the cPAD for children 1 to 2 years old, the population group receiving the greatest exposure. Based on the explanation in Unit III.C.3., regarding residential use patterns, chronic residential exposure to residues of cyantraniliprole is not expected.
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 an aggregate MOE of 149 for children 1 to 2 years old. For adults, the oral and inhalation routes of exposure are not appropriate to be aggregated since the endpoints of concern are not common. Because EPA's level of concern for cyantraniliprole is a MOE of 100 or below, this MOE is not of concern.
There are no established Codex MRLs on the caneberry subgroup 13-07A, soybean, aspirated grain fractions, celtuce, Florence fennel and rice. The U.S. tolerances being established for coffee and Brassica, leafy greens subgroup 4-16A are harmonized with Codex. The U.S. tolerances being established for the low growing berry subgroup 13-07H; leaf petiole vegetable subgroup 22B; Brassica head and stem vegetable group 5-16; leafy greens subgroup 4-16B; and kohlrabi are not harmonized with Codex MRLs. The Codex MRLs established for residues of cyantraniliprole on these commodities are lower than the recommended U.S. tolerances. The U.S. tolerances cannot be harmonized because following the label use directions could result in residues above the established Codex MRLs.
EPA received three comments in response to the Notices of Filing. The first comment indicated IR-4 and Rutgers University are profiteering by registering pesticides. The content of this comment is not material to the safety of the tolerances that are the subject of this action; pesticide registration occurs under the provisions of the Federal Insecticide, Fungicide, and Rodenticide Act. The FFDCA allows any person to file a petition proposing the establishment of a tolerance, and financial benefit from associated registration of pesticides is not a factor EPA considers when determining whether a tolerance is safe.
The second comment stated, in part, that no residues should be allowed. The Agency recognizes that some individuals believe that pesticides should be banned on agricultural crops. However, the existing legal framework provided by section 408 of the Federal Food, Drug and Cosmetic Act (FFDCA) states that tolerances may be set when persons seeking such tolerances or exemptions have demonstrated that the pesticide meets the safety standard imposed by that statute. This citizen's comment appears to be directed at the underlying statute and not EPA's implementation of it; the citizen has made no contention that EPA has acted in violation of the statutory framework.
The last comment expressed concern about pollutant loadings and relatively high costs of regulations. The commenter also mentioned the Shelby Amendment, the Freedom of Information Act and the Intergovernmental Panel on Climate Change. The comment did not raise any issue related to the Agency's safety determination for cyantraniliprole tolerances. The receipt of this comment Start Printed Page 56267is acknowledged; however, this comment is not relevant to this action.
EPA modified the proposed tolerance levels for soybean, hulls and soybean, seed to conform to the Agency's rounding classes. The Agency also revised the commodity terminology to use the correct commodity definitions for Florence fennel (Fennel, Florence, fresh leaves and stalk) and Aspirated grain fractions (Grain, aspirated grain fractions).
Therefore, tolerances are established for residues of cyantraniliprole, 3-bromo-1-(3-chloro-2-pyridinyl)-N-[4-cyano-2-methyl-6-[((methylamino)carbonyl]phenyl]-1H-pyrazole-5-carboxamide, in or on Berry, low growing, except strawberry, subgroup 13-07H, except blueberry, lowbush and lingonberry at 0.08 parts per million (ppm); Brassica, leafy greens, subgroup 4-16B at 30 ppm; Caneberry subgroup 13-07A at 4.0 ppm; Celtuce at 20 ppm; Fennel, Florence, fresh leaves and stalk at 20 ppm; Grain, aspirated grain fractions at 200 ppm; Kohlrabi at 3.0 ppm; Leaf petiole vegetable subgroup 22B at 20 ppm; Leafy greens subgroup 4-16A at 20 ppm; Rice hulls at 0.05 ppm; Rice, straw at 0.015 ppm; Soybean, forage at 15 ppm; Soybean, hay at 50 ppm; Soybean, hulls at 1.0 ppm; Soybean, seed at 0.40 ppm; and Vegetable, Brassica, head and stem, group 5-16 at 3.0 ppm. In addition, EPA is removing the following tolerances as they are superseded by the new tolerances being established in this rulemaking: from paragraph (a) (Berry, low growing, except strawberry, subgroup 13-07H at 0.08 ppm; Brassica head and stem, subgroup 5A at 3.0 ppm; Brassica leafy vegetables, subgroup 5B at 30 ppm; and Vegetable, leafy, except Brassica, group 4 at 20 ppm) and from paragraph (d) (soybean, forage at 0.70 ppm and soybean, hay at 0.70 ppm). Finally, EPA is removing the footnote noting the lack of US registrations for the tolerances for coffee, green bean and rice, grain.
2. In § 180.672:
i. Remove the entry “Berry, low growing, except strawberry, subgroup 13-07H 1”.
ii. Add alphabetically the entry “Berry, low growing, except strawberry, subgroup 13-07H, except blueberry, lowbush and lingonberry”.
iii. Remove the entry “Brassica head and stem, subgroup 5A”.
iv. Add alphabetically the entry “Brassica, leafy greens, subgroup 4-16B.
v. Remove the entry “ Brassica leafy vegetables, subgroup 5B”.
vi. Add alphabetically the entries: “Caneberry subgroup 13-07A” and “Celtuce”.
vii. Revise the entry “Coffee, green bean”.
viii. Add alphabetically the entries: “Fennel, Florence, fresh leaves and stalk”; “Grain, aspirated grain fractions”; “Kohlrabi”; “Leaf petiole vegetable subgroup 22B”; “Leafy greens subgroup 4-16A”;
ix. Revise the entry “Rice, grain”.
x. Add alphabetically the entries: “Rice hulls”; “Rice, straw”; “Soybean, forage”; “Soybean, hay”; “Soybean, hulls”; “Soybean, seed”; and “Vegetable, Brassica, head and stem, group 5-16”.
xi. Remove the entry “Vegetable, leafy, except Brassica, group 4”.Start Printed Page 56268
b. Remove from the table in paragraph (d) the entries: “Soybean, forage”; and “Soybean, hay”.
Berry, low growing, except strawberry, subgroup 13-07H, except blueberry, lowbush and lingonberry 0.08
Brassica, leafy greens, subgroup 4-16B 30
Coffee, green bean 0.05
Grain, aspirated grain fractions 200
Leafy greens subgroup 4-16A 20
Rice, hulls 0.05
Rice, straw 0.015
Soybean, forage 15
[FR Doc. 2018-24379 Filed 11-9-18; 8:45 am]