Environmental Protection Agency (EPA).
This regulation establishes tolerances for residues of glyphosate in or on sunflower; safflower; noni; pea, dry; and vegetable, legume, group 6 except soybean, and pea, dry. The Start Printed Page 76181Interregional Research Project Number 4 (IR-4) requested these tolerances under the Federal Food, Drug, and Cosmetic Act (FFDCA), as amended by the Food Quality Protection Act of 1996 (FQPA).
This regulation is effective December 20, 2006. Objections and requests for hearings must be received on or before February 20, 2007, and must be filed in accordance with the instructions provided in 40 CFR part 178 (see also Unit I.C. of the SUPPLEMENTARY INFORMATION).
EPA has established a docket for this action under docket identification (ID) number EPA-HQ-OPP-2006-0177. All documents in the docket are listed in the index for the docket. Although listed in the index, some information is not publicly available, e.g., Confidential Business Information (CBI) or other information whose disclosure is restricted by statute. Certain other material, such as copyrighted material, is not placed on the Internet and will be publicly available only in hard copy form. Publicly available docket materials are available in the electronic docket at http://www.regulations.gov, or, if only available in hard copy, at the OPP Regulatory Public Docket in Rm. S-4400, One Potomac Yard (South Building), 2777 S. Crystal Drive, Arlington, VA. The Docket Facility is open from 8:30 a.m. to 4 p.m., Monday through Friday, excluding legal holidays. The Docket telephone number is (703) 305-5805.Start Further Info
FOR FURTHER INFORMATION CONTACT:
Shaja R. Brothers, Registration Division (7505P), Office of Pesticide Programs, Environmental Protection Agency, 1200 Pennsylvania Ave., NW., Washington, DC 20460-0001; telephone number: (703) 308-3194; e-mail address: firstname.lastname@example.org.End Further Info End Preamble Start Supplemental 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. Potentially affected entities may include, but are not limited to:
- Crop production (NAICS 111), e.g., agricultural workers; greenhouse, nursery, and floriculture workers; farmers.
- Animal production (NAICS 112), e.g., cattle ranchers and farmers, dairy cattle farmers, livestock farmers.
- Food manufacturing (NAICS 311), e.g., agricultural workers; farmers; greenhouse, nursery, and floriculture workers; ranchers; pesticide applicators.
- Pesticide manufacturing (NAICS 32532), e.g., agricultural workers; commercial applicators; farmers; greenhouse, nursery, and floriculture workers; residential users.
This listing is not intended to be exhaustive, but rather provides a guide for readers regarding entities likely to be affected by this action. Other types of entities not listed in this unit could also be affected. The North American Industrial Classification System (NAICS) codes have been provided to assist you and others in determining whether this action might apply to certain entities. If you have any questions regarding the applicability of this action to a particular entity, consult the person listed under FOR FURTHER INFORMATION CONTACT.
B. How Can I Access Electronic Copies of this Document?
In addition to accessing an electronic copy of this Federal Register document through the electronic docket at http://www.regulations.gov, you may access this Federal Register document electronically through the EPA Internet under the “Federal Register” listings at http://www.epa.gov/fedrgstr. You may also access a frequently updated electronic version of 40 CFR part 180 through the Government Printing Office's pilot e-CFR site at http://www.gpoaccess.gov/ecfr. To access the OPPTS Harmonized Guidelines referenced in this document, go directly to the guidelines at http://www.epa.gpo/opptsfrs/home/guidelin.htm.
C. Can I File an Objection or Hearing Request?
Under section 408(g) of the FFDCA, as amended by the FQPA, any person may file an objection to any aspect of this regulation and may also request a hearing on those objections. The EPA procedural regulations which govern the submission of objections and requests for hearings appear in 40 CFR part 178. 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-2006-0177 in the subject line on the first page of your submission. All requests must be in writing, and must be mailed or delivered to the Hearing Clerk on or before February 20, 2007.
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 that does not contain any CBI for inclusion in the public docket that is described in ADDRESSES. Information not marked confidential pursuant to 40 CFR part 2 may be disclosed publicly by EPA without prior notice. Submit your copies, identified by docket ID number EPA-HQ-OPP-2006-0177, by one of the following methods:
- Federal eRulemaking Portal: http://www.regulations.gov. Follow the on-line instructions for submitting comments.
- Mail: Office of Pesticide Programs (OPP) Regulatory Public Docket (7502P), Environmental Protection Agency, 1200 Pennsylvania Ave., NW., Washington, DC 20460-0001.
- Delivery: OPP Regulatory Public Docket (7502P), Environmental Protection Agency, Rm. S-4400, One Potomac Yard (South Building), 2777 S. Crystal Drive, Arlington, VA. Deliveries are only accepted during the Docket's normal hours of operation (8:30 a.m. to 4 p.m., Monday through Friday, excluding legal holidays). Special arrangements should be made for deliveries of boxed information. The Docket telephone number is (703) 305-5805.
II. Background and Statutory Findings
In the Federal Register of March 29, 2006 (71 FR 15734) (FRL-7766-9), EPA issued a notice pursuant to section 408(d)(3) of FFDCA, 21 U.S.C. 346a(d)(3), announcing the filing of pesticide petitions (PP 4E6878 and 5E6987) by IR-4, 500 College Road East, Suite 201 W, Princeton, NJ 08540. The petitions requested that 40 CFR 180.364 be amended by establishing tolerances for residues of the herbicide glyphosate, (N-phosphonomethyl)glycine, in or on sunflower and safflower at 25 parts per million (ppm) (PP 4E6878); vegetable, legume, group 6, except soybean at 8.0 ppm (5E6987); and mulberry, Indian at 0.2 ppm (5E6987). Following review of the residue chemistry data, EPA determined that the commodities term and tolerance levels should be revised to the following: Sunflower at 85 ppm; safflower at 85 ppm; pea, dry at 8.0 ppm; vegetable, legume, group 6 except soybean and pea, dry at 5.0 ppm; and noni at 0.20 ppm. This notice included a summary of the petitions prepared by Monsanto, the registrant. There were no comments received in response to the notice of filing.
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 Start Printed Page 76182all 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. . . .”
EPA performs a number of analyses to determine the risks from aggregate exposure to pesticide residues. For further discussion of the regulatory requirements of section 408 of the FFDCA and a complete description of the risk assessment process, see http://www.epa.gov/fedrgstr/EPA-PEST/1997/November/Day-26/p30948.htm.
III. Aggregate Risk Assessment and Determination of Safety
Consistent with section 408(b)(2)(D) of FFDCA, 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, consistent with section 408(b)(2) of FFDCA, for tolerances for residues of glyphosate on sunflower at 85 ppm; safflower at 85 ppm; noni at 0.20 ppm; pea, dry at 8.0 ppm; and vegetable, legume, group 6 except soybean and pea, dry at 5.0 ppm. EPA's assessment of exposures and risks associated with establishing these tolerances follow.
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. Specific information on the studies received and the nature of the toxic effects caused by glyphosate 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 www.regulations.gov. Docket ID EPA-HQ-OPP-2006-0177, Glyphosate Indian Mulberry and Dry Pea Human Health Risk Assessment, pages 10-11, and Glyphosate Safflower and Sunflower Human Health Risk Assessment, pages 12-14.
To locate this information on the Regulations.gov website follow these steps:
1. Select “Advanced Search,” then “Docket Search”
2. In the “Keyword” field type the chemical name or insert the applicable “Docket ID number.” (example: EPA-HQ-OPP-2006-0177).
3 Click the “Submit” button.
Follow the instructions on the regulations.gov website to view the index for the docket and access available documents.
B. Toxicological Endpoints
For hazards that have a threshold below which there is no appreciable risk, the dose at which the NOAEL from the toxicology study identified as appropriate for use in risk assessment is used to estimate the toxicological level of concern (LOC). However, the lowest dose at which the LOAEL is sometimes used for risk assessment if no NOAEL was achieved in the toxicology study selected. An uncertainty factor (UF) is applied to reflect uncertainties inherent in the extrapolation from laboratory animal data to humans and in the variations in sensitivity among members of the human population as well as other unknowns.
The linear default risk methodology (Q*) is the primary method currently used by the Agency to quantify non-threshold hazards such as cancer. The Q* approach assumes that any amount of exposure will lead to some degree of cancer risk, estimates risk in terms of the probability of occurrence of additional cancer cases. More information can be found on the general principles EPA uses in risk characterization at http://www.epa.gov/pesticides/health/human.htm.
A summary of the toxicological endpoints for glyphosate used for human risk assessment can be found at www.regulations.gov, Docket ID EPA-HQ-OPP-2006-0177, Glyphosate Indian Mulberry and Dry Pea Human Health Risk Assessment, pages 16-17, and Glyphosate Safflower and Sunflower Human Health Risk Assessment, pages 18-19.
C. Exposure Assessment
1. Dietary exposure from food and feed uses. Tolerances have been established 40 CFR 180.364 for the residues of glyphosate, in or on a variety of raw agricultural commodities. Additionally tolerances are established for meat, milk, poultry and egg. Risk assessments were conducted by EPA to assess dietary exposures from glyphosate in food as follows:
i. Acute exposure. No acute effects were identified in the toxicological studies for glyphosate, therefore a quantitative acute dietary exposure assessment is not necessary.
ii. Chronic exposure. In conducting the chronic dietary exposure assessment EPA used the Dietary Exposure Evaluation Model software with the Food Commodity Intake Database (DEEM-FCIDTM), which incorporates food consumption data as reported by respondents in the United States Department of Agriculture (USDA) 1994-1996 and 1998 Nationwide Continuing Surveys of Food Intake by Individuals (CSFII), and accumulated exposure to the chemical for each commodity. The following assumptions were made for the chronic exposure assessment: The Tier 1 chronic dietary analysis for glyphosate is a conservative estimate of dietary exposure that used tolerance level residues and 100% percent crop treated (PCT).
iii. Cancer. Glyphosate is classified as a not likely human carcinogen, so a cancer dietary exposure analysis is not necessary.
2. Dietary exposure from drinking water.The Agency lacks sufficient monitoring exposure data to complete a comprehensive dietary exposure analysis and risk assessment for glyphosate in drinking water. Because the Agency does not have comprehensive monitoring data, drinking water concentration estimates are made by reliance on simulation or modeling taking into account data on the physical characteristics of glyphosate. Further information regarding EPA drinking water models used in pesticide exposure assessment can be found at http://www.epa.gov/oppefed1/models/index.htm.
Glyphosate is registered for aquatic use to control weeds in water bodies. Therefore, the Agency estimated the concentration in surface water resulting from direct application to a water body 6 feet deep. This estimate is based on a dilution model that does not take into account degradation in the water body and partitioning into the water column-sediment phases. The estimate considered a single broadcast application at the maximum application rate of 3.75 lb of glyphosate free acid per acre. Based on a maximum total application rate of 3.75 pounds of glyphosate free acid per acre, the estimated concentration for use in the drinking water assessment is 230 g/L parts per billion (ppb).
Based on the generic expected environmental concentration (GENEEC) and screening concentration in groundwater (SCI-GROW) models, the Start Printed Page 76183estimated environmental concentrations (EECs) of glyphosate for acute exposures are estimated to be 21 ppb for surface water and 0.0038 ppb for ground water. The EECs for chronic exposures are estimated to be 0.83 ppb for surface water and 0.0038 ppb for ground water, based on glyphosate treatment in crops.
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).
Glyphosate is currently registered for use on broadcast and spot treatments on home lawns and gardens. Glyphosate, isopropylamine salt is registered for broadcast and spot treatments on home lawns and gardens. Glyphosate products for homeowner use are packaged as ready-to-mix formulations and ready-to-use sprayers and are very common in home and garden stores in the U.S. Glyphosate products are also used by lawn care operators for broadcast and spot treatment weed control programs on homeowner lawns. Glyphosate products are also labeled for turf renovation.
The risk assessment was conducted using the following residential exposure assumptions: Based on the registered residential use patterns, there is a potential for short-term dermal and inhalation exposures to homeowners who apply products containing glyphosate (residential handlers). Additionally, based on the results of environmental fate studies, there is a potential for short and intermediate-term post-application dermal exposures by adults and toddlers and incidental ingestion exposures by toddlers. However, since short or intermediate-term dermal or inhalation endpoints were not identified, no residential handler or post-application dermal assessment is necessary; only a post-application toddler assessment for incidental ingestion exposures was performed.
4. Cumulative effects from substances with a common mechanism of toxicity. Section 408(b)(2)(D)(v) of the 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.”
Unlike other pesticides for which EPA has followed a cumulative risk approach based on a common mechanism of toxicity, EPA has not made a common mechanism of toxicity finding as to glyphosate and any other substances and glyphosate does not appear to produce a toxic metabolite produced by other substances. For the purposes of this tolerance action, therefore, EPA has not assumed that glyphosate has 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 the policy statements released by EPA's Office of Pesticide Programs concerning common mechanism determinations and procedures for cumulating effects from substances found to have a common mechanism on EPA's website at http://www.epa.gov/pesticides/cumulative.
D. Safety Factor for Infants and Children
1. In general. Section 408 of FFDCA provides that EPA shall apply an additional tenfold 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 data base on toxicity and exposure unless EPA determines based on reliable data that a different margin of safety will be safe for infants and children. Margins of safety are incorporated into EPA risk assessments either directly through use of a MOE analysis or through using uncertainty (safety) factors in calculating a dose level that poses no appreciable risk to humans. In applying this provision, EPA either retains the default value of 10X when reliable data do not support the choice of a different factor, or, if reliable data are available, EPA uses a different additional safety factor value based on the use of traditional UFs and/or special FQPA safety factors, as appropriate.
2. Prenatal and postnatal sensitivity. Based on the available data, there was no evidence of quantitative or qualitative increased susceptibility following in utero glyphosate exposure to rats and rabbits, or following prenatal/postnatal exposure in the 2-generation reproduction study in rats. A developmental neurotoxicity study was not required.
3. Conclusion. EPA has determined that reliable data show that it would be safe for infants and children to reduce the FQPA safety factor to 1X. That decision is based on the following findings:
There is no evidence of quantitative or qualitative increased susceptibility of the young demonstrated in the prenatal developmental studies in rats and rabbits and prenatal/postnatal reproduction study in rats ii. the toxicology data base is complete iii. a developmental neurotoxicity study is not required; and iv. the dietary (food, drinking water, and residential) exposure assessments will not underestimate the potential exposures for infants and children.
E. Aggregate Risks and Determination of Safety
1. Acute risk. There were no toxic effects attributable to a single dose. An endpoint of concern was not identified to quantitate an acute-dietary risk to the U.S. general population or to the subpopulation females 13-50 years old. Therefore, glyphosate is not expected to pose an acute risk.
2. Chronic risk. Using the exposure assumptions described in this unit for chronic exposure, EPA has concluded that exposure to glyphosate from food and water will utilize 2% of the chronic population adjusted dose (cPAD) for the U.S. population, 7% of the cPAD for all infants <1 year old, and 5% of the cPAD for children 1-2 years old. Based on the use pattern, chronic residential exposure to residues of glyphosate is not expected.
3. Short-term and Intermediate-term risk. Short term and Intermediate term aggregate exposures take into account residential exposure plus chronic exposure to food and water (considered to be a background exposure level). Glyphosate is currently registered for uses that could result in short and intermediate term residential exposures. Since the incidental oral ingestion exposure estimates for toddlers from residential turf exposures exceeded the incidental oral exposure estimates from post-application swimmer exposures, the Agency conducted this risk assessment using exposure estimates from the worst-case situation. No attempt was made to combine exposures from the swimmer and residential turf scenarios due to the low probability of both occurring concurrently.
Using the exposure assumptions described in this unit for short-term exposures, EPA has concluded that food and residential exposures aggregated result in aggregate MOEs of 1,400 for children 1-2 years old (the most highly exposed population subgroup), and 4,610 for adults 20-49 years old.
4. Aggregate cancer risk for U.S. population. Glyphosate has been classified by the Cancer Peer Review Committee as “a Group E” chemical- negative as a human carcinogen - based on the absence of carcinogenicity in mice and rats. Therefore, a cancer risk assessment was not conducted.Start Printed Page 76184
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, and to infants and children from aggregate exposure to glyphosate residues.
IV. Other Considerations
A. Analytical Enforcement Methodology
Adequate enforcement methods are available for analysis of residues of glyphosate in or on plant and livestock commodities. These methods include Gas Liquid Chromatography (GLC) (Method I in Pesticides Analytical Manual II; the limit of detection is 0.05 ppm) and high-performance liquid chromatography (HPLC) with fluorometric detection. These analytical methods are adequate for residue data collection and enforcement of the proposed tolerances of glyphosate in/on noni and dry peas. The method may be requested from: Chief, Analytical Chemistry Branch, Environmental Science Center, 701 Mapes Rd., Ft. Meade, MD 20755-5350; telephone number: (410) 305-905; e-mail address: email@example.com.
B. International Residue Limits
The Codex Alimentarius Commission has established several maximum residue limits (MRLs) for glyphosate residues in various commodities. The Codex and U.S. tolerances are in harmony with respect to MRL/tolerance expression; both regulate the parent glyphosate only. The proposed tolerance of 8.0 ppm in dry peas exceeds the existing Codex MRL of 5.0 ppm. This discrepancy is not expected to result in a trade barrier, however, because the United States accounts for only about 5% of world dry production and is not expected to be a significant exporter of this commodity. There are currently no Codex Maximum Residue Limits for residues of glyphosate on safflower, sunflower, or noni; therefore, there are no international harmonization issues associated with these commodities.
Therefore, the tolerances are established for residues of glyphosate, (N-phosphonomethyl)glycine, in or on sunflower at 85 ppm; safflower at 85 ppm; noni at 0.20 ppm; pea, dry at 8.0 ppm; and vegetable, legume, group 6 except soybean and pea,dry at 5.0 ppm.
VI. Statutory and Executive Order Reviews
This final rule establishes a tolerance under section 408(d) of FFDCA 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 rule has been exempted from review under Executive Order 12866 due to its lack of significance, this rule is not subject to Executive Order 13211, Actions Concerning Regulations That Significantly Affect Energy Supply, Distribution, or Use (66 FR 28355, May 22, 2001). This final rule does not contain any information collections subject to OMB approval under the Paperwork Reduction Act (PRA), 44 U.S.C. 3501 et seq., or impose any enforceable duty or contain any unfunded mandate as described under Title II of the Unfunded Mandates Reform Act of 1995 (UMRA) (Public Law 104-4). 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); or OMB review or any Agency action under Executive Order 13045, entitled Protection of Children from Environmental Health Risks and Safety Risks (62 FR 19885, April 23, 1997). 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), Public Law 104-113, section 12(d) (15 U.S.C. 272 note). Since tolerances and exemptions that are established on the basis of a petition under section 408(d) of FFDCA, 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. In addition, the Agency has determined that this action will not have a substantial direct effect on States, on the relationship between the national government and the States, or on the distribution of power and responsibilities among the various levels of government, as specified in Executive Order 13132, entitled Federalism (64 FR 43255, August 10, 1999). Executive Order 13132 requires EPA to develop an accountable process to ensure “meaningful and timely input by State and local officials in the development of regulatory policies that have federalism implications.” “Policies that have federalism implications” is defined in the Executive Order to include regulations that have “substantial direct effects on the States, on the relationship between the national government and the States, or on the distribution of power and responsibilities among the various levels of government.” This final rule directly regulates growers, food processors, food handlers and food retailers, not States. This action does not alter the relationships or distribution of power and responsibilities established by Congress in the preemption provisions of section 408(n)(4) of FFDCA. For these same reasons, the Agency has determined that this rule does not have any “tribal implications” as described in Executive Order 13175, entitled Consultation and Coordination with Indian Tribal Governments (65 FR 67249, November 6, 2000). Executive Order 13175, requires EPA to develop an accountable process to ensure “meaningful and timely input by tribal officials in the development of regulatory policies that have tribal implications.” “Policies that have tribal implications” is defined in the Executive Order to include regulations that have “substantial direct effects on one or more Indian tribes, on the relationship between the Federal Government and the Indian tribes, or on the distribution of power and responsibilities between the Federal Government and Indian tribes.” This rule will not have substantial direct effects on tribal governments, on the relationship between the Federal Government and Indian tribes, or on the distribution of power and responsibilities between the Federal Government and Indian tribes, as specified in Executive Order 13175. Thus, Executive Order 13175 does not apply to this rule.
VII. Congressional Review Act
The Congressional Review Act, 5 U.S.C. 801 et seq., as added by the Small Business Regulatory Enforcement Fairness Act of 1996, generally provides that before a rule may take effect, the agency promulgating the rule must submit a rule report, which includes a copy of the rule, to each House of the Congress and to the Comptroller General of the United States. 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 this final rule in the Federal Register. This final rule is not a “major rule” as defined by 5 U.S.C. 804(2).Start List of Subjects
List of Subjects in 40 CFR Part 180End List of Subjects Start Signature
Dated: December 6, 2006.
Donald R. Stubbs,
Acting Director, Registration Division, Office of Pesticide Programs.
Therefore, 40 CFR chapter I is amended as follows:End Amendment Part Start Part
PART 180—[AMENDED]End Part Start Amendment Part
1. The authority citation for part 180 continues to read as follows:End Amendment Part Start Amendment Part
2. Section 180.364 is amended by alphabetically adding commodities to the table in paragraph (a) to read as follows:End Amendment Part
(a) * * *
|Commodity||Parts per million|
|* * * * *|
|* * * * *|
|* * * * *|
|* * * * *|
|* * * * *|
|Vegetable, legume, group 6 except soybean and pea,dry||5.0|
|* * * * *|
(b) Section 18 emergency exemptions. [Reserved]
(c) Tolerances with regional registrations. [Reserved]
(d) Indirect or inadvertent residues. [Reserved]
[FR Doc. E6-21490 Filed 12-19-06; 8:45 am]
BILLING CODE 6560-50-S