E9-18348. Methyl Poly(Oxyethylene)C8-

AGENCY:

Environmental Protection Agency (EPA).

ACTION:

Final rule.

SUMMARY:

This regulation establishes an exemption from the requirement of a tolerance for residues of methyl poly(oxyethylene)C₈-C₁₈ alkylammonium chlorides where the poly(oxyethylene) content is n=2-15 and where C₈-C₁₈ alkyl is linear and may be saturated or unsaturated, herein referred to in this document as methyl poly(oxyethylene)C₈-C₁₈ alkylammonium chlorides (MPOACs), when used as an inert ingredient in pesticide formulations for pre-harvest uses under 40 CFR 180.920 at a maximum of 10% by weight in herbicide formulations and 5% by weight in all other formulations. The Joint Inerts Task Force (JITF), Cluster Support Team (CST No. 7), submitted a petition to EPA under the Federal Food, Drug, and Cosmetic Act (FFDCA), requesting an exemption from the requirement of a tolerance. This regulation eliminates the need to establish a maximum permissible level for residues of MPOACs.

DATES:

This regulation is effective August 5, 2009. Objections and requests for hearings must be received on or before October 5, 2009, 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:

EPA has established a docket for this action under docket identification (ID) number EPA-HQ-OPP-2009-0042. All documents in the docket are listed in the docket index available at http://www.regulations.gov. 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 Bldg.), 2777 S. Crystal Dr., Arlington, VA. The Docket Facility is open from 8:30 a.m. to 4 p.m., Monday through Friday, excluding legal holidays. The Docket Facility telephone number is [phone].

FOR FURTHER INFORMATION CONTACT:

Kerry Leifer, Registration Division (7505P), Office of Pesticide Programs, Environmental Protection Agency, 1200 Pennsylvania Ave., NW., Washington, DC 20460-0001; telephone number: [phone]; e-mail address: [e-mail].

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. Potentially affected entities may include, but are not limited to those engaged in the following activities:

• Crop production (NAICS code 111).
• Animal production (NAICS code 112).
• Food manufacturing (NAICS code 311).
• Pesticide manufacturing (NAICS code 32532).

This listing is not intended to be exhaustive, but rather to provide 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 electronically available documents 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 EPA's tolerance regulations at 40 CFR part 180 through the Government Printing Office's e-CFR cite at http://www.gpoaccess.gov/​ecfr. To access the OPPTS Hamonized Guidlines referenced in this document, go directly to the guidelines at http://www.epa.gpo/​opptsfrs/​home/​suidelin.htm.

C. Can I File an Objection or Hearing Request?

Under section 408(g) of FFDCA, 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-2009-0042 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 as required by 40 CFR part 178 on or before October 5, 2009.

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 this copy, identified by docket ID number EPA-HQ-OPP-2009-0042, 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 Bldg.), 2777 S. Crystal Dr., Arlington, VA. Deliveries are only accepted during the Docket Facility'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 Facility telephone number is [phone].

II. Background

In the Federal Register of March 4, 2009 (74 FR 9397) (FRL-8401-8), EPA issued a notice pursuant to section 408(d)(3) of FFDCA, 21 U.S.C. 346a(d)(3), announcing the filing of a pesticide petition (PP 9E7518) by The JITF, CST No. 7, c/o CropLife America, 1156 15^th St., NW., Suite 400, Washington, DC 20005. The petition requested that 40 CFR 180.920 be amended by establishing exemptions from the requirement of a tolerance for residues of the inert ingredient methyl poly(oxyethylene)C₈-C₁₈ alkylammonium chlorides where the poly(oxyethylene) content is n=2-15 and where C₈-C₁₈ alkyl is linear and may be saturated or unsaturated (MPOACs) for pre-harvest uses at a maximum of 10% by weight in herbicide formulations and 5% by weight in all other formulations. That notice referenced a summary of the petition prepared by The JITF, CST No. 7, the petitioner, which is available to the public in the docket, http://www.regulations.gov.

The Agency received two comments in response to the notice of filing. Both comments was received from private citizens who opposed the authorization to sell any pesticide that leaves a residue on food. The Agency understands the commenters' concerns and recognizes that some individuals believe that no residue of pesticides should be allowed. However, under the existing legal framework provided by section 408 of FFDCA, EPA is authorized to establish pesticide tolerances or exemptions where persons seeking such tolerances or exemptions have demonstrated that the pesticide meets the safety standard imposed by that statute.

This petition was submitted in response to a final rule of August 9, 2006, (71 FR 45415) (FRL-8084-1) in which the Agency revoked, under section 408(e)(1) of the FFDCA, the existing exemptions from the requirement of a tolerance for residues of certain inert ingredients because of insufficient data to make the determination of safety required by section 408(b)(2) of FFDCA. The expiration date for the tolerance exemptions subject to revocation was August 9, 2008, which was later extended August 9, 2009 by a final rule published in the Federal Register of August 4, 2008. (73 FR 45312) (FRL-8372-7) to allow for data to be submitted to support the establishment of tolerance exemptions for these inert ingredients prior to the effective date of the tolerance exemption revocation.

III. Inert Ingredient Definition

Inert ingredients are all ingredients that are not active ingredients as defined in 40 CFR 153.125 and include, but are not limited to, the following types of ingredients (except when they have a pesticidal efficacy of their own): Solvents such as alcohols and hydrocarbons; surfactants such as polyoxyethylene polymers and fatty acids; carriers such as clay and diatomaceous earth; thickeners such as carrageenan and modified cellulose; wetting, spreading, and dispersing agents; propellants in aerosol dispensers; microencapsulating agents; and emulsifiers. The term “inert” is not intended to imply nontoxicity; the ingredient may or may not be chemically active. Generally, EPA has exempted inert ingredients from the requirement of a tolerance based on the low toxicity of the individual inert ingredients.

IV. Aggregate Risk Assessment and Determination of Safety

Section 408(b)(2)(A)(i) of FFDCA allows EPA to establish an exemption from the requirement of 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. . . .

EPA performs a number of analyses to determine the risks from aggregate exposure to pesticide residues. First, EPA determines the toxicity of pesticides. Second, EPA examines exposure to the pesticide through food, drinking water, and through other exposures that occur as a result of pesticide use in residential settings.

Consistent with section 408(b)(2)(D) of FFDCA, and the factors specified in 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 for the petitioned-for exemption from the requirement of a tolerance for residues of MPOACs when used as inert ingredients in pesticide formulations for pre-harvest uses at a maximum of 10% by weight in herbicide formulations and 5% by weight in all other formulations. EPA's assessment of exposures and risks associated with establishing tolerances 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 toxicity data available on the MPOACs consists of acute toxicity studies, mutagenicity studies, and an OPPTS Harmonized Guideline 870.3650 combined repeated dose toxicity study with the reproduction/developmental toxicity screening test. The majority of the MPOAC compounds are reported as “not acutely toxic” for lethality by the oral and dermal routes of exposure (Toxicity Category III). However, CAS Reg. No. 70750-47-9, the representative test compound, is more toxic by the oral and dermal routes (Toxicity Category II). All MPOACs are severely irritating to the eye (Toxicity Category I), and the MPOAC identified by CAS Reg. No.70750-47-9 (quatenary ammonium compounds, coco alkylbis(hydroxyethyl)methy1, chlorides) is severely irritating to the skin. Inhalation data on two of the MPOACs indicate irritation at high doses.

The OPPTS Harmonized Guideline 870.3650 study on the representative surfactant, (CAS Reg. No. 70750-47-9) demonstrated severe toxicity in rats, as evidenced by deaths of all test subjects at 100 milligrams/kilogram/day (mg/kg/day) after 5 days, and deaths of 5 out of 10 females at 50 mg/kg/day after 6-8 days of exposure. Given the extremely corrosive nature of the test material, the Agency believes that the high mortality rate is secondary to the forestomach lesions seen in the rats. Further, the Agency notes that the severity of the effects may be related to the unique anatomy of the rats. Humans do not have a forestomach which serves as a storage reservoir in rodents; therefore, effects seen in the rat forestomach are likely to be significantly more severe than what would be expected from the compound in the glandular stomachs in humans and therefore, have less relevance to humans.

The no observed adverse effect level (NOAEL) for developmental and reproductive toxicity is 25 mg/kg/day, the lowest dose tested (LDT). Although no reproductive or developmental effects were observed at the next higher dose of 50 mg/kg/day, the evaluation at this dose level included only 5 surviving female animals. While the actual lowest observed adverse effect level (LOAEL) for reproductive developmental effects may be higher, or reproductive developmental effects may not occur at all as a result of exposure to this chemical, in the absence of a sufficient number of animals to assess, the Agency has conservatively assumed that if more animals had been available at the mid-dose, developmental or reproductive toxicity might have been observed. There are no concerns for sensitivity of offspring.

There was no evidence of neurotoxicity in this study; functional- observational battery and motor-activity data were similar in all the treatment groups. Liver enzymes were elevated but were not accompanied by microscopic lesions or increased organ weight and were not considered adverse. No carcinogenicity studies are available for the MPOACs. A qualitative structure activity relationship database, DEREK Version 11, identified no structural alerts suggestive of carcinogenicity.

Specific information on the studies received and the nature of the adverse effects caused by MPOACs as well as the NOAEL and the LOAEL from the toxicity studies can be found at http://www.regulations.gov in document MPOACs-JITF CST No. 7 Inert Ingredients). Human Health Risk Assessment to Support Proposed Exemption from the Requirement of a Tolerance When Used as Inert Ingredients in Pesticide Formulations pages 9-13 and pages 25-26 in docket ID number EPA-HQ-OPP-2009-0042.

B. Toxicological Endpoints

For hazards that have a threshold below which there is no appreciable risk, a toxicological point of departure (POD) is identified as the basis for derivation of reference values for risk assessment. The POD may be defined as the highest dose tested (HDT) at which the NOAEL in the toxicology study identified as appropriate for use in risk assessment. However, if a NOAEL cannot be determined, the lowest dose at which adverse effects of concern are identified (the LOAEL) or a benchmark dose (BMD) approach is sometimes used for risk assessment. Uncertainty/safety factors (UFs) are used in conjunction with the POD to take into account 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. Safety is assessed for acute and chronic dietary risks by comparing aggregate food and water exposure to the pesticide to the acute population adjusted dose (aPAD) and chronic population adjusted dose (cPAD). The aPAD and cPAD are calculated by dividing the POD by all applicable UFs. Aggregate short-term, intermediate-term, and chronic-term risks are evaluated by comparing food, water, and residential exposure to the POD to ensure that the margin of exposure (MOE) called for by the product of all applicable UFs is not exceeded. This latter value is referred to as the level of concern (LOC).

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 greater than that 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 MPOACs used for human health risk assessment is shown in Table 1 of this unit.

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

Exposure/Scenario	Point of Departure and Uncertainty/Safety Factors	RfD, PAD, LOC for Risk Assessment	Study and Toxicological Effects
Acute dietary (all populations)	Acute toxicity was not identified.
Chronic dietary (all populations)	NOAEL = 25 mg/kg/day UFA = 10x UFH = 10x Food quality protection act (FQPA) SF = 1x	Chronic RfD = 0.25 mg/kg/day cPAD = 0.25 mg/kg/day	LOAEL = 50 mg/kg/day based on stomach inflammation and mortality associated with the forestomach inflammation
Incidental oral (short-term and intermediate-term)	NOAEL= 25 mg/kg/day UFA = 10x UFH = 10x FQPA SF = 1x	Residential LOC for MOE = 100	LOAEL = 50 mg/kg/day based on stomach inflammation and mortality associated with the forestomach inflammation.
Dermal and inhalation (all durations)	Quantitative assessment not required: Cluster is corrosive irritating and exposure will be self limiting; expected low-dermal and inhalation absorptions; product is used in low percentages in household products (i.e., low exposure).
Cancer (oral, dermal, inhalation)	Classification: No animal toxicity data available for an assessment. Based on SAR analysis, MPOACs is not expected to be carcinogenic.
POD = A data point or an estimated point that is derived from observed dose-response data and used to mark the beginning of extrapolation to determine risk associated with lower environmentally relevant human exposures. NOAEL = no observed adverse effect level. LOAEL = lowest observed adverse effect level. UF = uncertainty factor. UFA = extrapolation from animal to human (interspecies). UFH = potential variation in sensitivity among members of the human population (intraspecies). PAD = population adjusted dose (a=acute, c=chronic). FQPA SF = FQPA Safety Factor. RfD = reference dose. MOE = margin of exposure. LOC = level of concern. N/A = not applicable.

C. Exposure Assessment

Sufficient data were provided on the chemical identity of the MPOACs; however, limited data are available on the metabolism and environmental degradation of these compounds. The Agency relied collectively on information provided on the representative chemical structures, the generic cluster structures, the submitted physicochemical data, structure-activity relationship information, as well as information on other surfactants and chemicals of similar size and functionality to determine the residues of concern for these inert ingredients. The residues of concern for risk assessment purposes are the parent compounds only.

The registrant selected CAS Reg. No. 70750-47-9, as the test compound because the coco alkyl encompasses the broad range of C₈-C₁₈ alkyl chain included in the descriptor. The Agency concluded that the cluster grouping was appropriate. Further, the Agency also concluded that it is unlikely that any potential environmental degradates that would be found in food and water will be more toxic than the parent compound. Residue estimates used in the dietary risk assessment were chosen to represent an upper bound on the combined residues of parent and any potential metabolite or degradate of concern.

Quantitative dermal or inhalation risk assessments were not be performed for residential exposures because the MPOACs are highly corrosive irritating, and therefore, exposure will be self-limiting and will be regulated based on labeling of the formulations. There is not a significant concern for dermal or inhalation exposures due to expected low dermal and inhalation absorptions and the fact that the product is used in low percentages in household products (i.e., low exposure). An aggregate assessment need only be conducted for food, water, and incidental oral exposures.

1. Dietary exposure from food and feed uses. In evaluating dietary exposure to MPOACs, EPA considered exposure under the petitioned-for exemptions from the requirement of a tolerance. EPA assessed dietary exposures from MPOACs in food as follows:

i. Acute exposure. No adverse effects attributable to a single exposure of MPOACs was seen in the toxicity databases. Therefore, acute dietary risk assessments for MPOACs is not necessary.

ii. Chronic exposure. In conducting the chronic dietary exposure assessment, EPA used food consumption information from the United States Department of Agriculture (USDA) 1994-1996 and 1998 Nationwide Continuing Surveys of Food Intake by Individuals (CSFII). As to residue levels in food, no residue data were submitted for MPOACs. In the absence of specific residue data, EPA has developed an approach which uses surrogate information to derive upper bound exposure estimates for the subject inert ingredient. Upper bound exposure estimates are based on the highest tolerance for a given commodity from a list of high-use insecticides, herbicides, and fungicides. A complete description of the general approach taken to assess inert ingredient risks in the absence of residue data is contained in the memorandum entitled Alkyl Amines Polyalkoxylates (Cluster 4): Acute and Chronic Aggregate (Food and Drinking Water) Dietary Exposure and Risk Assessments for the Inerts. (D361707, S. Piper, 2/25/09) and can be found at http://www.regulations.gov in docket ID number EPA-HQ-OPP-2008-0738.

In the dietary exposure assessment, the Agency assumed that the residue level of the inert ingredient would be no higher than the highest tolerance for a given commodity. Implicit in this assumption is that there would be similar rates of degradation (if any) between the active and inert ingredient and that the concentration of inert ingredient in the scenarios leading to these highest of tolerances would be no higher than the concentration of the active ingredient.

The Agency believes the assumptions used to estimate dietary exposures lead to an extremely conservative assessment of dietary risk due to a series of compounded conservatisms. First, assuming that the level of residue for an inert ingredient is equal to the level of residue for the active ingredient will overstate exposure. The concentrations of active ingredient in agricultural products is generally at least 50% of the product and often can be much higher. Further, pesticide products rarely have a single inert ingredient; rather there is generally a combination of different inert ingredients used which additionally reduces the concentration of any single inert ingredient in the pesticide product in relation to that of the active ingredient. In the case of MPOACs, EPA made a specific adjustment to the dietary exposure assessment to account for the use limitations of the amount of MPOACs that may be in formulations (no more than 10% by weight in herbicide formulations) and assumed that the MPOACs are present at the maximum limitations rather than at equal quantities with the active ingredient. This remains a very conservative assumption because surfactants are generally used at levels far below this percentage.

Second, the conservatism of this methodology is compounded by EPA's decision to assume that, for each commodity, the active ingredient which will serve as a guide to the potential level of inert ingredient residues is the active ingredient with the highest tolerance level. This assumption overstates residue values because it would be highly unlikely, given the high number of inert ingredients, that a single inert ingredient or class of ingredients would be present at the level of the active ingredient in the highest tolerance for every commodity. Finally, a third compounding conservatism is EPA's assumption that all foods contain the inert ingredient at the highest tolerance level. In other words, EPA assumed 100% of all foods are treated with the inert ingredient at the rate and manner necessary to produce the highest residue legally possible for an active ingredient. In summary, EPA chose a very conservative method for estimating what level of inert residue could be on food, then used this methodology to choose the highest possible residue that could be found on food and assumed that all food contained this residue. No consideration was given to potential degradation between harvest and consumption even though monitoring data shows that tolerance level residues are typically one to two orders of magnitude higher than actual residues in food when distributed in commerce.

Accordingly, although sufficient information to quantify actual residue levels in food is not available, the compounding of these conservative assumptions will lead to a significant exaggeration of actual exposures. EPA does not believe that this approach underestimates exposure in the absence of residue data.

iii. Cancer. The Agency used a qualitative SAR database, DEREK11, to determine if there were structural alerts suggestive of carcinogenicity. No structural alerts for carcinogenicity were identified. MPOACs are not expected to be carcinogenic. Therefore, a cancer dietary exposure assessment is not necessary to assess cancer risk.

iv. Anticipated residue and percent crop treated (PCT) information. EPA did not use anticipated residue and PCT information in the dietary assessment for MPOACs. Tolerance level residues and 100 PCT 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 MPOACs in drinking water. These simulation models take into account data on the physical, chemical, and fate transport characteristics of MPOACs. Further information regarding EPA drinking water models used in the pesticide exposure assessment can be found at http://www.epa.gov/​oppefed1/​models/​water/​index.htm.

A screening level drinking water analysis, based on the Pesticide Root Zone Model /Exposure Analysis Modeling System (PRZM/EXAMS) was performed to calculate the estimated drinking water concentrations (EDWCs) of MPOACs. Modeling runs on four surrogate inert ingredients using a range of physical chemical properties that would bracket those of MPOACs were conducted. Modeled acute drinking water values ranged from 0.001 parts per billion (ppb) to 41 ppb. Modeled chronic drinking water values ranged from 0.0002 ppb to 19 ppb. Further details of this drinking water analysis can be found at http://www.regulations.gov in the document MPOACs- JITF, (CST No. 7 Inert Ingredients). Human Health Risk Assessment to Support Proposed Exemption from the Requirement of a Tolerance When Used as Inert Ingredients in Pesticide Formulations, pages 13-14 and 28-46 in docket ID number EPA-HQ-OPP-2009-0042.

For the purpose of the screening level dietary risk assessment to support this request for an exemption from the requirement of a tolerance for MPOACs, a conservative drinking water concentration value of 100 ppb based on screening level modeling was used to assess the contribution to drinking water for chronic dietary risk assessments for the parent compounds and for the metabolites of concern. These values were directly entered into the dietary exposure model.

3. From non-dietary exposure. The term “residential exposure” is used in this document to refer to non-occupational, non-dietary exposure (e.g., for lawn and garden pest control, indoor pest control, termiticides, and flea and tick control on pets). MPOACs may be used in inert ingredients in pesticide products that are registered for specific uses that may result in both indoor and outdoor residential exposures. A screening level residential exposure and risk assessment was completed for products containing MPOACs as inert ingredients. In this assessment, representative scenarios, based on end-use product application methods and labeled application rates, were selected. The MPOACs may be used as inert ingredients in pesticide formulations that are used in and around the home. Additionally, uses are possible in household cleaning products and in personal care products. The Agency has not selected endpoints for dermal or inhalation risk assessmenst; therefore, only exposure scenarios which will result in oral exposures have been assessed for the MPOACs. The Agency conducted an assessment to represent worst-case residential exposure by assessing postapplication exposures and risks from MPOACs in pesticide formulations (outdoor scenarios) and MPOACs in disinfectant-type uses (indoor scenarios). Further details of this residential exposure and risk analysis can be found at http://www.regulations.gov in the memorandum 9entitled JITF Inert Ingredients. Residential and Occupational Exposure Assessment Algorithms and Assumptions Appendix for the Human Health Risk Assessments to Support Proposed Exemption from the Requirement of a Tolerance When Used as Inert Ingredients in Pesticide Formulations; (D364751, 5/7/09, Lloyd/LaMay in docket ID number EPA-HQ-OPP-2008-0710.

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 MPOACs to share a common mechanism of toxicity with any other substances, and the MPOACs do not appear to produce a toxic metabolite produced by other substances. For the purposes of this tolerance action, therefore, EPA has assumed that the MPOACs do 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 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 FQPA SF. In applying this provision, EPA either retains the default value of 10X, or uses a different additional SF when reliable data available to EPA support the choice of a different factor.

2. Prenatal and postnatal sensitivity. The toxicity data available on the MPOACs consists of acute toxicity studies, mutagenicity studies, and an OPPTS Harmonized Guideline 870.3650 combined repeated dose toxicity study with the reproduction developmental toxicity screening test.

There was no evidence of increased sensitivity in young animals because no developmental or reproductive toxicity occurred in the lowest dose group (doses of 25 mg/kg/day) in the reproductive developmental toxicity screening test. Additionally, no developmental or reproductive toxicity was noted in the mid-dose group (doses of 50 mg/kg/day); however, since there were only five surviving female animals in this group, which is considered an insufficient number of animals, the study LOAEL was set at the mid-dose level. The mortality in rats that occurred in the study was associated with forestomach inflammation. Given the extremely corrosive nature of the test material, the Agency believes that the high mortality rate is secondary to the forestomach lesions seen in the rats. Further, the Agency notes that the severity of the effects may be related to the unique anatomy of the rats. Humans do not have a forestomach which serves as a storage reservoir in rodents; therefore effects seen in the rat forestomach are likely to be significantly more severe than what would be expected from the compound in the glandular stomachs in humans, and therefore, have less relevance to humans.

There was no evidence of neurotoxicity in the OPPTS Harmonized Guideline 870.3650 study; functional-observational battery and motor-activity data were similar in all the treatment groups.

There are no residual uncertainties identified in the exposure databases. The dietary (food and water) exposure assessment is not likely to underestimate exposure to any subpopulation, including those comprised of infants and children.

3. Conclusion. EPA has determined that reliable data show that 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 MPOACs is considered adequate for assessing the risks to infants and children (the available studies are described in Unit IV.D.2).

ii. No quantitative or qualitative increased susceptibility was demonstrated in the offspring in the OPPTS Harmonized Guideline 870.3650 combined repeated dose toxicity study with the reproduction developmental toxicity screening test in rats following in utero and post-natal exposure.

iii. Although mortality occurred in the OPPTS Harmonized Guideline 870.3650 study that was associated with forestomach inflammation, the Agency believes that, given the extremely corrosive nature of the test material, the high mortality rate is secondary to the forestomach lesions seen in the rats. Further, the Agency notes that the severity of the effects may be related to the unique anatomy of the rats. Humans do not have a forestomach which serves as a storage reservoir in rodents; therefore effects seen in the rat forestomach are likely to be significantly more severe than what would be expected from the compound in the glandular stomachs in humans and therefore, have less relevance to humans.

iv. There was no evidence of neurotoxicity in the OPPTS Harmonized Guideline 870.3650 study. Functional-observational battery and motor-activity data were similar in all the treatment groups. Thus, no additional neurotoxicity data are required.

v. While there is no chronic toxicity study, the Agency has concluded that since endpoint risk assessment is based on the forestomach lesions in rats, a very conservative hazard endpoint, coupled with the highly conservative exposure assessment and an absence of evidence of increased sensitivity, or neurotoxicity, the use of the standard 100X inter-species and intra-species UF are adequate to protect infants and children, and no additional UF is needed for extrapolating from subchronic to chronic exposure.

vi. There are no residual uncertainties identified in the exposure databases. The food and drinking water assessment is not likely to underestimate exposure to any subpopulation, including those comprised of infants and children. The food exposure assessments are considered to be highly conservative as they are based on the use of the highest tolerance level from the surrogate pesticides for every food and 100 PCT is assumed for all crops. EPA also made conservative (protective) assumptions in the ground and surface water modeling used to assess exposure to MPOACs in drinking water. EPA used similarly conservative assumptions to assess post-application exposure of children as well as incidental oral exposure of toddlers. These assessments will not underestimate the exposure and risks posed by MPOACs.

E. Aggregate Risks and Determination of Safety

EPA determines whether acute and chronic pesticide exposures are safe by comparing aggregate exposure estimates to the aPAD and cPAD. The aPAD and cPAD represent the highest safe exposures, taking into account all appropriate SFs. EPA calculates the aPAD and cPAD by dividing the POD by all applicable UFs. For linear cancer risks, EPA calculates the probability of additional cancer cases given the estimated aggregate exposure. Short-term, intermediate-term, and chronic-term risks are evaluated by comparing the estimated aggregate food, water, and residential exposure to the POD to ensure that the MOE called for by the product of all applicable UFs is not exceeded.

1. Acute risk. There was no hazard attributable to a single exposure seen in the toxicity database for MPOACs. Therefore, the MPOACs are not expected to pose an acute risk.

2. Chronic risk. A chronic aggregate risk assessment takes into account exposure estimates from chronic dietary consumption of food and drinking water. Using the exposure assumptions discussed in this unit for chronic exposure, the chronic dietary exposure from food and water to MPOACs is 16% of the cPAD for the U.S. population and 51% of the cPAD for children 1-2 yrs old, the most highly exposed population subgroup.

3. Short-term risk. Short-term aggregate exposure takes into account short-term residential exposure plus chronic exposure to food and water (considered to be a background exposure level).

MPOACs are used as an inert ingredients in pesticide products that are currently registered for uses that could result in short-term residential exposure and the Agency has determined that it is appropriate to aggregate chronic exposure through food and water with short-term residential exposures to MPOACs. Using the exposure assumptions described in this unit, EPA has concluded the combined short-term aggregated food, water, and residential exposures result in an aggregate MOE of 190 for children. Children's residential exposure includes hand-to-mouth exposures. As the LOC is for MOEs that are lower than 100, this MOE is not of concern.

4. Intermediate-term risk. Intermediate-term aggregate exposure takes into account intermediate-term residential exposure plus chronic exposure to food and water (considered to be a background exposure level).

MPOACs are currently registered for uses that could result in intermediate-term residential exposure and the Agency has determined that it is appropriate to aggregate chronic exposure through food and water with intermediate-term residential exposures to MPOACs. Using the exposure assumptions described in this unit, EPA has concluded the combined intermediate-term aggregated food, water, and residential exposures result in an aggregate MOE of 190 for children. Children's residential exposure includes hand-to-mouth exposures. As the LOC is for MOEs that are lower than 100, this MOE is not of concern.

5. Aggregate cancer risk for U.S. population. The Agency has not identified any concerns for carcinogenicity relating to MPOACs.

6. Determination of safety. Based on these risk assessments, EPA concludes that there is a reasonable certainty that no harm will result to the general population, or to infants and children from aggregate exposure to residues of MPOACs.

V. Other Considerations

A. Analytical Enforcement Methodology

An analytical method is not required for enforcement purposes since the Agency is establishing an exemption from the requirement of a tolerance without any numerical limitation.

B. International Residue Limits

The Agency is not aware of any country requiring a tolerance for MPOACs nor have any CODEX Maximum Residue Levels been established for any food crops at this time.

VI. Conclusion

Therefore, an exemption from the requirement of a tolerance is established for residues methyl poly(oxyethylene)C₈-C₁₈ alkylammonium chlorides where the poly(oxyethylene) content is n=2-15 and where C₈-C₁₈ alkyl is linear and may be saturated or unsaturated (MPOACs) for pre-harvest uses at a maximum of 10% by weight in herbicide formulations and 5% by weight in all other formulations.

VII. Statutory and Executive Order Reviews

This final rule establishes tolerances 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 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 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 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.

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 section 408(n)(4) of FFDCA. 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) (Public Law 104-4).

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).

VIII. Congressional Review Act

The Congressional Review Act, 5 U.S.C. 801 et seq., generally provides that before a rule may take effect, the agency promulgating the rule must submit a rule report 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).

List of Subjects in 40 CFR Part 180

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

Dated: July 21, 2009.

G. Jeffrey Herndon,

Acting Director, Registration Division, Office of Pesticide Programs.

Therefore, 40 CFR chapter I is amended as follows:

PART 180—[AMENDED]

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

Authority: 21 U.S.C. 321(q), 346a and 371.

2. In §180.920, the table is amended by adding alphabetically the following inert ingredients to read as follows:

§ 180.920

Inert ingredients used pre-harvest; exemptions from the requirement of a tolerance.

* * * * *

Inert Ingredients	Limits	Uses
*   *   *   *   *   *   *
Methyl poly(oxyethylene)C8-C18 alkylammonium chlorides where the poly(oxyethylene) content is n=2-15 and where C8-C18 alkyl is linear and may be saturated or unsaturated (CAS Reg. Nos. 3010-24-0, 18448-65-2, 70750-47-9, 22340-01-8, 67784-77-4, 64755-05-1, 61791-10-4, 28724-32-5, 28880-55-9, 68187-69-9, 68607-27-2, 60687-90-3.	Concentration in formulated end use products not to exceed 10% by weight in herbicide products and 5% by weight in all other pesticide products.	Surfactants, related adjuvants of surfactants
*   *   *   *   *   *   *