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 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 EPA's tolerance regulations at 40 CFR part 180 through the Government Printing Office's pilot eCFR site at http://www.gpoaccess.gov/ecfr. C. Can I File an Objection or Hearing Request?

Under section 408(g) of FFDCA, 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 EPAHQOPP20060785 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 April 28, 2008.

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 EPAHQOPP20060785, by one of the following methods:

II. Petition for Tolerance

In the Federal Register of September 29, 2006 (71 FR 57507) (FRL 80941), 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 6F7101) by Dow AgroSciences LLC, 9330 Zionsville Road, Indianapolis, IN 462681054. The petition requested that 40 CFR part 180 be amended by establishing tolerances for residues of the herbicide pyroxsulam, N (5,7dimethoxy[1,2,4]triazolo[1,5a]pyrimidin2yl)2methoxy4
(trifluoromethyl)3pyridinesulfonamide, in or on wheat, forage at 0.04 parts per million (ppm); wheat, grain at 0.01 ppm; wheat, hay at 0.01 ppm; and wheat, straw at 0.01 ppm. That notice referenced a summary of the petition prepared by Dow AgroSciences LLC, the registrant, which is available to the public in the docket, http://www.regulations.gov. Comments were received on the notice of filing. EPA's response to these comments is discussed in Unit IV.C.

Based upon review of the field residue data supporting the petition, EPA has modified the tolerance levels for wheat, forage from 0.04 to 0.06 ppm and for wheat, straw from 0.01 ppm to 0.03 ppm. III. Aggregate Risk Assessment and Determination of Safety

Section 408(b)(2)(A)(i) of FFDCA allows EPA to establish a tolerance (the legal limit for a pesticide chemical residue in or on a food) only if EPA determines that the tolerance is ``safe.'' Section 408(b)(2)(A)(ii) of FFDCA defines ``safe'' to mean that ``there is a reasonable certainty that no harm will result from aggregate exposure to the pesticide chemical residue, including all anticipated dietary exposures and all other exposures for which there is reliable information.'' This includes exposure through drinking water and in residential settings, but does not include occupational exposure. Section 408(b)(2)(C) of FFDCA requires EPA to give special consideration to exposure of infants and children to the pesticide chemical residue in establishing a tolerance and to ``ensure that there is a reasonable certainty that no harm will result to infants and children from aggregate exposure to the pesticide chemical residue....'' These provisions were added to FFDCA by the Food Quality Protection Act (FQPA) of 1996.

Consistent with FFDCA section 408(b)(2)(D), and the factors specified in FFDCA section 408(b)(2)(D), EPA has reviewed the available scientific data and other relevant information in support of this action. EPA has sufficient data to assess the hazards of and to make a determination on aggregate exposure for the petitionedfor tolerances for residues of pyroxsulam on wheat, forage at 0.06 ppm; wheat, grain at 0.01 ppm; wheat, hay at 0.01 ppm and wheat, straw at 0.03 ppm. EPA's assessment of exposures and risks associated with establishing the 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.

Pyroxsulam has low or minimal acute toxicity via the oral (Acute Toxicity Category III), dermal and inhalation (Acute Toxicity Category IV) routes of exposure. It is nonirritating to the eyes and skin. It is a dermal sensitizer.

Little toxicity was observed in the repeatdose toxicology studies via the oral and dermal routes of exposure. No treatmentrelated adverse effects were observed in the subchronic studies (mice, rats, or dogs). There was evidence of increased serum cholesterol levels in the subchronic exposures, but in light of a 28day satellite recovery group in the subchronic rat study, where the cholesterol levels returned to normal after cessation of treatment, these effects were considered to be adaptive and nonadverse. Increased liver weights were observed in several of the subchronic and chronic studies; however, in the absence of corroborating changes in histopathology, the increased liver weights were not considered adverse. No adverse effects were observed in the chronic dog study or chronic/carcinogenicity study in rats. In the carcinogenicity study in mice, the lowestobservedadverseeffectlevel (LOAEL) was 1,000 milligrams/kilogram/day (mg/kg/day), based on increased liver weights with corroborating evidence of increased incidence of clear cell foci of alteration in hepatocytes in males. The noobservedadverseeffectlevel (NOAEL) was 100 mg/kg/day.

There was no evidence of maternal or offspring toxicity in the developmental or 2generation reproduction studies in rats up to 1,000 mg/kg/day. Considered in conjunction with the rangefinding study, the developmental study in rabbits showed no signs of maternal or offspring toxicity up to 600 mg/kg/day. None of these studies showed signs of increased quantitative or qualitative susceptibility. Pyroxsulam is not mutagenic; it is classified as ``not likely to be carcinogenic to humans.''

Specific information on the studies received and the nature of the adverse effects caused by pyroxsulam as well as the NOAEL and the LOAEL from the toxicity studies can be found at http://www.regulations.gov. The referenced document is available in the docket established by this action, which is described under ADDRESSES, and is identified as ``Pyroxsulam Human Health Risk Assessment for Proposed Uses on Wheat.'' PC Code: 108702, Petition No: 6F7101, DP Barcode: D335496 in that docket.

B. Toxicological Endpoints

For hazards that have a threshold below which there is no appreciable risk, the toxicological level of concern (LOC) is derived from the highest dose at which no adverse effects are observed (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) is sometimes used for risk assessment. Uncertainty/safety factors (UFs) are used in conjunction with the LOC 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 risks by comparing aggregate 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 LOC by all applicable UFs. Shortterm, intermediateterm, and longterm risks are evaluated by comparing aggregate exposure to the LOC to ensure that the margin of exposure (MOE) called for by the product of all applicable UFs is not exceeded.

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For nonthreshold risks, the Agency assumes that any amount of exposure will lead to some degree of risk and estimates risk in terms of the probability of occurrence of additional adverse cases. Generally, cancer risks are considered nonthreshold. 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/fedrgstr/EPAPEST/1997/November/Day26/p30948.htm.

A summary of the toxicological endpoints for pyroxsulam used for human risk assessment can be found at http://www.regulations.gov in document ``Pyroxsulam Human Health Risk Assessment for Proposed Uses on Wheat.'' PC Code: 108702, Petition No: 6F7101, DP Barcode: D335496 at page 23 in docket ID number EPAHQOPP20060785.

C. Exposure Assessment

1. Dietary exposure from food and feed uses. In evaluating dietary exposure to pyroxsulam, EPA considered exposure under the petitioned for tolerances. EPA assessed dietary exposures from pyroxsulam in food as follows:

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

No such effects were identified in the toxicological studies for pyroxsulam; therefore, a quantitative acute dietary exposure assessment is unnecessary.

ii. Chronic exposure. In conducting the chronic dietary exposure assessment EPA used the food consumption data from the United States Department of Agriculture (USDA) 19941996, and 1998; Nationwide Continuing Surveys of Food Intakes by Individuals (CSFII). As to residue levels in food, EPA assumed all foods for which there are tolerances were treated and contain tolerancelevel residues.

iii. Cancer. Pyroxsulam was negative for carcinogenicity in feeding studies in rats and mice and was classified as ``not likely to be a human carcinogen.'' Therefore, a quantitative exposure assessment to evaluate cancer risk is unnecessary.

2. Dietary exposure from drinking water. The Agency lacks sufficient monitoring data to complete a comprehensive dietary exposure analysis and risk assessment for pyroxsulam 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 environmental fate characteristics of pyroxsulam. Further information regarding EPA drinking water models used in pesticide exposure assessment can be found at http:// www.epa.gov/oppefed1/models/water/index.htm.

Based on the Pesticide Root Zone Model /Exposure Analysis Modeling System (PRZM/EXAMS) and Screening Concentration in Ground Water (SCI GROW) models, the estimated environmental concentrations (EECs) of pyroxsulam for chronic exposures are estimated to be 0.102 parts per billion (ppb) for surface water and 0.465 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 of value 0.465 ppb was used to assess the contribution of the estimated drinking water concentration to the dietary risk assessment.

3. From nondietary exposure. The term ``residential exposure'' is used in this document to refer to nonoccupational, nondietary exposure (e.g., for lawn and garden pest control, indoor pest control, termiticides, and flea and tick control on pets).

Pyroxsulam is not registered for use on any sites that would result in residential exposure.

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

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 pyroxsulam and any other substances and pyroxsulam 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 pyroxsulam 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 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 (``10X'') 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 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 safety factor. 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 FQPA safety factor value based on the use of traditional UFs and/or special FQPA safety factors, as appropriate.

2. Prenatal and postnatal sensitivity. There is no evidence of quantitative and/or qualitative susceptibility and there are no residual uncertainties with regard to prenatal toxicity following in utero exposure to rats or rabbits.

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:

i. The toxicity database for pyroxsulam is complete.

ii. There is no indication that pyroxsulam is a neurotoxic chemical and there is no need for a developmental neurotoxicity study or additional UFs to account for neurotoxicity.

iii. There is no evidence that pyroxsulam results in increased susceptibility to rats or rabbits in utero in the prenatal developmental studies or in young rats in the 2generation reproduction study.

iv. There are no residual uncertainties identified in the exposure databases. The dietary (food and drinking water) exposure assessment will not underestimate the potential exposure for infants, children, and/or women of childbearing age. There is no potential for residential exposure.

E. Aggregate Risks and Determination of Safety

Safety is assessed for acute and chronic risks by comparing aggregate exposure to the pesticide to the aPAD and cPAD. The aPAD and cPAD are calculated by dividing the LOC by all applicable UFs. For linear cancer risks, EPA calculates the probability of additional cancer cases given aggregate
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exposure. Shortterm, intermediateterm, and longterm risks are evaluated by comparing aggregate exposure to the LOC to ensure that the MOE called for by the product of all applicable UFs is not exceeded.

1. Acute risk. There were no effects observed in oral toxicity studies including developmental toxicity studies in rats and rabbits that could be attributable to a single dose (exposure). Therefore, pyroxsulam 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 pyroxsulam from food and water will utilize <1 % of the cPAD for all population groups. There are no residential uses for pyroxsulam that result in chronic residential exposure to pyroxsulam.

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

Pyroxsulam is not registered for use on any sites that would result in residential exposure. Therefore, the aggregate risk is the sum of the risk from food and water.

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

Pyroxsulam is not registered for use on any sites that would result in residential exposure. Therefore, the aggregate risk is the sum of the risk from food and water, which does not exceed the Agency's LOC for any population subgroup.

5. Aggregate cancer risk for U.S. population. Pyroxsulam is classified as ``not likely to be carcinogenic in humans'' based on the results of a carcinogenicity study in mice and the combined chronic toxicity and carcinogenicity study in the rat. Therefore, pyroxsulam is not expected to pose a cancer risk to humans.

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 pyroxsulam residues.
IV. Other Considerations

A. Analytical Enforcement Methodology

Adequate enforcement methodology (liquid chromatography with positiveion electrospray ionization (ESI) tandem mass spectrometry (LC/MS/MS) is available to enforce the tolerance expression. The method may be requested from: Chief, Analytical Chemistry Branch, Environmental Science Center, 701 Mapes Rd., Ft. Meade, MD 207555350; telephone number: (410) 3052905; email address:
residuemethods@epa.gov. B. International Residue Limits

No Codex, Canadian, or Mexican maximum residue limits (MRLs) have been established for pyroxsulam. However, tolerances for pyroxsulam on wheat are pending in Canada and Australia. These Canadian and Australian tolerances are not expected to result in any harmonization issues.

C. Response to Comments

Public comments were received from B. Sachau who objected to the proposed tolerances because of the amounts of pesticides already consumed and carried by the American population. She further indicated that testing conducted on animals have absolutely no validity and are cruel to the test animals. B. Sachau's comments contained no scientific data or evidence to rebut the Agency's conclusion that there is a reasonable certainty that no harm will result from aggregate exposure to pyroxsulam, including all anticipated dietary exposures and all other exposures for which there is reliable information. EPA has responded to B. Sachau's generalized comments on numerous previous occasions. 70 FR 1349, 1354 (January 7, 2005); 69 FR 63083, 63096 (October 29, 2004).

V. Conclusion

Therefore, tolerances are established for residues of pyroxsulam, N(5,7dimethoxy[1,2,4]triazolo[1,5a]pyrimidin2yl)2methoxy4
(trifluoromethyl)3pyridinesulfonamide, in or on wheat, forage at 0.06 ppm; wheat, grain at 0.01 ppm; wheat, hay at 0.01 ppm and wheat, straw at 0.03 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, 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) 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 LowIncome 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 6, 2000) do not apply to this rule. In addition, This 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 1044).

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 104113, section 12(d) (15 U.S.C. 272 note).

VII. 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
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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: February 10, 2008.
Debra Edwards,
Director, 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. Section 180.638 is added to read as follows:
Sec. 180.638 Pyroxsulam; tolerances for residues.
(a) General. Tolerances are established for residues of the herbicide pyroxsulam, N(5,7dimethoxy[1,2,4]triazolo[1,5a]pyrimidin 2yl)2methoxy4(trifluoromethyl)3pyridinesulfonamide in or on the raw agricultural commodities:
Commodity Parts per million Wheat, forage........................................ 0.06 Wheat, grain......................................... 0.01 Wheat, hay........................................... 0.01 Wheat, straw......................................... 0.03 (b) Section 18 emergency exemptions. [Reserved]
(c) Tolerances with regional registrations. [Reserved]
(d) Indirect or inadvertent residues. [Reserved]
[FR Doc. E83490 Filed 22608; 8:45 am]
BILLING CODE 656050S

FOR FURTHER INFORMATION CONTACT Erik Kraft, Registration Division (7505P), Office of Pesticide Programs, Environmental Protection Agency, 1200 Pennsylvania Ave., NW., Washington, DC 204600001; telephone number: (703) 3089358; email address: Kraft.Erik@epa.gov.