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Environmental Protection Agency (EPA).
This regulation establishes tolerances for residues of the ovicide/miticide hexythiazox (trans-5-(4-chlorophenyl)-N-cyclohexyl-4-methyl-2-oxothiazolidine-3-carboxamide) and its metabolites containing the (4-chlorophenyl)-4-methyl-2-oxo-3-thiazolidine moiety (expressed as parent) in or on tree nuts (nutmeat), plums, fresh prunes, dried prunes, pistachios, peppermint (tops), spearmint (tops), and caneberries. Gowan Company and the Interregional Research Project No. 4 (IR-4) requested this tolerance under the Federal Food, Drug, and Cosmetic Act (FFDCA), as amended by the Food Quality Protection Act (FQPA) of 1996.
This regulation is effective April 18, 2001. Objections and requests for hearings, identified by docket control number OPP-301117, must be received by EPA on or before June 18, 2001.
Written objections and hearing requests may be submitted by mail, in person, or by courier. Please follow the detailed instructions for each method as provided in Unit VI. of the SUPPLEMENTARY INFORMATION. To ensure proper receipt by EPA, your objections and hearing requests must identify docket control number OPP-301117 in the subject line on the first page of your response.Start Further Info
FOR FURTHER INFORMATION CONTACT:
By mail: William G. Sproat, Jr., Registration Division (7505C), Office of Pesticide Programs, Environmental Protection Agency, 1200 Pennsylvania Ave., NW., Washington, DC 20460; telephone number: (703)-308-8587; and 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 affected by this action if you are an agricultural producer, food manufacturer, or pesticide manufacturer. Potentially affected categories and entities may include, but are not limited to:
|Categories||NAICS codes||Examples of potentially affected entities|
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 the table could also be affected. The North American Industrial Classification System (NAICS) codes have been provided to assist you and others in determining whether or not this action might apply to certain entities. If you have questions regarding the applicability of this action to a particular entity, consult the person listed under FOR FURTHER INFORMATION CONTACT.
B. How Can I Get Additional Information, Including Copies of this Document and Other Related Documents?
1. Electronically. You may obtain electronic copies of this document, and certain other related documents that might be available electronically, from the EPA Internet Home Page at http://www.epa.gov/. To access this document, on the Home Page select “Laws and Regulations,” “Regulations and Proposed Rules,” and then look up the entry for this document under the “Federal Register—Environmental Documents.” You can also go directly to the Federal Register listings at http://www.epa.gov/fedrgstr/. A frequently updated electronic version of 40 CFR part 180 is available at http://www.access.gpo/nara/cfr/cfrhtml_00/Title_40/40cfr180_00.html, a beta site currently under development. To access the OPPTS Harmonized Guidelines referenced in this document, go directly to the guidelines at http://www.epa.gov/opptsfrs/home/guidelin.htm.
2. In person. The Agency has established an official record for this action under docket control number OPP-301117. The official record consists of the documents specifically referenced in this action, and other information related to this action, including any information claimed as Confidential Business Information (CBI). This official record includes the documents that are physically located in the docket, as well as the documents that are referenced in those documents. The public version of the official record does not include any information claimed as CBI. The public version of the official record, which includes printed, paper versions of any electronic comments submitted during an applicable comment period is available for inspection in the Public Information and Records Integrity Branch (PIRIB), Rm. 119, Crystal Mall #2, 1921 Jefferson Davis Hwy., Arlington, VA, from 8:30 a.m. to 4 p.m., Monday through Friday, excluding legal holidays. The PIRIB telephone number is (703) 305-5805.
II. Background and Statutory Findings
Hexythiazox is the active ingredient in Savey Ovicide/Miticide 50 WP (EPA Reg. No. 10163-208). Permanent tolerances are established under 40 CFR 180.448(a) for residues of hexythiazox and its metabolites containing the (4-chlorophenyl)-4-methyl-2-oxo-3-thiazolidine moiety (expressed as parent) in/on apples at 0.50 parts per million (ppm), wet apple pommace at 0.80 ppm; hops at 2.0 ppm, and pears at 0.3 ppm; milk, fat, and meat by-products of cattle, goats, horses, sheep, and swine at 0.02 ppm; almonds at 0.30 ppm and almond hulls at 10 ppm; and strawberries at 3.0 ppm. Tolerances with regional registrations are established for cotton gin by-products (California only) at 3.0 ppm and undelinted cotton seed (California only) at 0.20 ppm.
In the Federal Register of July 31, 1996 (61 FR 39971) (FRL-5384-6); April 30, 1997 (62 FR 23455) (FRL-5600-8); January 28, 1998 (63 FR 4252) (FRL-5763-6); and December 28, 2000 (65 FR 82349) (FRL-6761-6), EPA issued notices pursuant to section 408 of the FFDCA, 21 U.S.C. 346a as amended by the FQPA of 1996 (Public Law 104-170) announcing the filing of pesticide petitions for tolerances by Gowan Company, P.O. Box 5569, Yuma, AZ 85366-5569, and the Interregional Research Project Number 4 (IR-4), Technology Centre of New Jersey, 681 U.S. Highway #1 South, North Brunswick, NJ, 08902-3390. These notices included summaries of the petitions prepared by Gowan Company, the registrant. There were no comments received in response to the notice of filings.
The petition(s) requested that 40 CFR 180.448 be amended by establishing tolerances for residues of the insecticide Start Printed Page 19880hexythiazox, in or on various food commodities as follows:
1. IR-4 petition 0E6198 proposes the establishment of tolerances for mint -at 2.0 ppm.
2. IR-4 petition 0E6215 proposes the establishment of tolerances for the --caneberry subgroup at 1.0 ppm.
3. Gowan Company petition PP 6F4738 proposes the establishment of ---------tolerances for stone fruits including plums at 1 ppm; prunes at 5 ppm; -and all tree nuts at 0.2 ppm.
The existing tolerance for almonds is being deleted since it is covered under the tree nut group tolerance.
Hexythiazox is currently proposed for use on mint to control Twospotted spider mites; stone fruits (including plums) to control European red mites, Twospotted spider mites, McDaniel spider mite, Strawberry spider mites, Pacific spider mites, Pecan leaf scorch mites, and Willamette mites; Tree nuts and pistachios to control European red mites, Twospotted spider mites, McDaniel spider mites, Strawberry spider mites, Pacific spider mites, Pecan leaf scorch mites, and Willamette mites; and on caneberries to control Twospotted spider mites, McDaniel spider mite, Yellow spider mite and Pacific spider mites.
Section 408(b)(2)(A)(i) of the 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) 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) 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 and a complete description of the risk assessment process, see the final rule on Bifenthrin Pesticide Tolerances (62 FR 62961, November 26, 1997) (FRL-5754-7).
III. Aggregate Risk Assessment and Determination of Safety
Consistent with 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, consistent with section 408(b)(2), for a tolerance for residues of hexythiazox on tree nut group at 0.30 ppm; plums at 0.10 ppm; fresh prunes at 0.10 ppm; dried prunes at 0.40 ppm; pistachio at 0.30 ppm; peppermint (tops) at 2.0 ppm; spearmint (tops) at 2.0 ppm; and caneberry crop group subgroup at 1.0 ppm. EPA's assessment of exposures and risks associated with establishing the tolerance 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 nature of the toxic effects caused by hexythiazox are discussed in the following Table 1 as well as the no observed adverse effect level (NOAEL) and the lowest observed adverse effect level (LOAEL) from the toxicity studies reviewed.
|Guideline No.||Study type||Results|
|870.3100||90-Day oral toxicity rodents||NOAEL = 8.1/5.4 milligram/kilogram/day (mg/kg/day) males/females LOAEL = 58.6/38.1 mg/kg/day, males/females, based on increased absolute and relative liver weights in both sexes, increased relative ovarian and kidney weights, and fatty degeneration of the adrenal zona fasciculata|
|870.3700a||Prenatal developmental in rodents||Maternal NOAEL = 240 mg/kg/day LOAEL = 720 mg/kg/day based on decreased maternal body weight gain, and decreased food consumption Developmental NOAEL = 240 mg/kg/day LOAEL = 720 mg/kg/day based on delayed ossification|
|870.3700b||Prenatal developmental in nonrodents||Maternal NOAEL >1080 mg/kg/day LOAEL > 1,080 mg/kg/day Developmental NOAEL > 1.080 mg/kg/day LOAEL > 1,080 mg/kg/day|
|870.3800||Reproduction and fertility effects||Parental/Systemic NOAEL = 29.73/34.77 mg/kg/day, males/females LOAEL = 180.67/207.67 mg/kg/day, males/females, based on decreased body weight gain and increased absolute and relative liver, kidney, and adrenal weights Reproductive NOAEL > 180.67/207.67 mg/kg/day, males/females LOAEL > 180.67/207.67 mg/kg/day, males/females Offspring NOAEL = 29.73/34.77 mg/kg/day, males/females LOAEL = 180.67/207.67 mg/kg/day, males/females, based on decreased pup weight during lactation, and delayed hair growth and/or eye opening|
|870.4100b||Chronic toxicity dogs||NOAEL = 2.5 mg/kg/day LOAEL = 12.5 mg/kg/day based on increased absolute and relative adrenal weights and associated adrenal histopathology|
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|870.4300||Chronic toxicity/ Carcinogenicity rats||NOAEL = 23/29 mg/kg/day, males/females LOAEL =163/207 mg/kg/day, males/females based on decreased body weight and body weight gain and increased absolute and relative liver weights in both sexes No evidence of carcinogenicity|
|870.4300||Carcinogenicity mice||NOAEL = 41.6/51.2 mg/kg/day, males/females LOAEL = 267/318 mg/kg/day, males/females based on decreased male body weight and body weight gain, and increased absolute and relative liver weights in both sexes. Evidence of carcinogenicity (causes liver tumors in females)|
|870.5100||Gene mutation||The test was negative up to the highest dose tested (HDT) (6,400 μg/plate +/-S9)|
|870.5300||Gene mutation||Independently performed trials were negative up to precipitating doses (≥60 μg/mL) and severely cytotoxic concentrations (200 μg/mL -S9; 400 μg/mL +S9)|
|870.5375||Cytogenetics||The test was negative up to precipitating doses accompanied by severe cytotoxicity (≥ 167 μg/mL +/-S9)|
|870.5395||Cytogenetics||The results were inconclusive because a positive response, which was within the wide range of historical background data, was recorded for female mice at the mid-and high-doses (500 and 1,000 mg/kg). The assay should be repeated to confirm or refute the equivocal results.|
|870.5550||Other effects||The test was negative up to a lethal dose (250 μg/mL)|
|870.7485||Metabolism and pharmacokinetics||Absorption and distribution of dosed radioactivity were rapid. The radioactive material was rapidly eliminated in the urine and feces; the majority of the radioactivity was eliminated within 24 hours. There were no observable differences in the total elimination of NA-73 between male and female rats. The major route of elimination in both the male and female rats was by fecal excretion. The major metabolite found, PT-1-8 (cis), accounted for 8-12% of the administered radioactivity in the low dose groups. Approximately 11-20% and 65-69% of the dosed radioactivity was identified as unchanged NA-73 in the low-dose and high-dose groups, respectively. All other metabolites were present at low concentrations (< 2%). There was no apparent sex difference in metabolite formation. Significant levels of NA-73 equivalent14 C-residues were detected in the fat, liver, and adrenals. A sex-related difference in the residue levels of all tissues was observed, with residues in female tissues being two-fold higher than those found in male tissues.|
|870.7485||Metabolism and pharmacokinetics||Total recovery of radioactivity 72 hours after treatment accounted for 101.9-103% of the dose. The distribution of radioactivity 72 hours after dosing was as follows: (1) 30% (male and female) was excreted in the urine, (2) 60% (female) to 67% (male) was excreted in the feces, and (3) about 4% (male) to 10% (female) of the administered radioactivity remained in the tissues, with the highest concentration in the fat (2.3 ppm, males; 5.4 ppm, females). Significant sex differences existed for the pharmacokinetics of NA-73 in these rats, with females exhibiting slower elimination rats and higher tissue residues (about double) than males. NA-73 was metabolized to a large number of metabolites that were excreted both in the urine and feces. Seven metabolites were structurally identified in addition to the parent compound in both excreta of both sexes, with the major fecal metabolite, PT-1-8 (cis) accounting for 10% of the dosed radioactivity. The others were all minor metabolites accounting for less than 1.4%. About 20% of the dose was excreted as unchanged NA-73 (97% of which was in the feces). No significant sex difference was apparent with respect to metabolite formation.|
|870.7600||Dermal penetration||The total percent of dose absorbed averaged 2%, 1%, and 1.1% for cannulated rats (10-hour sacrifice) and 0.8%, 0.2%, and 0.2% for non-cannulated rats (1-hour sacrifice) at the low, medium, and high dose levels, respectively. The amount of radioactivity in the blood, carcass, urine and other organs totaled < 2% of the applied dose. The results of this study (2% dermal absorption) can be used for risk assessment purposes.|
B. Toxicological Endpoints
The dose at which 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 adverse effects of concern are identified (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. An UF of 100 is routinely used, 10X to account for interspecies differences and 10X for intra species differences. Discuss any additional UF (other than the FQPA SF) used in the assessment.
For dietary risk assessment (other than cancer) the Agency uses the UF to calculate an acute or chronic reference dose (acute RfD or chronic RfD) where the RfD is equal to the NOAEL divided by the appropriate UF (RfD = NOAEL/UF). Where an additional safety factor is retained due to concerns unique to the FQPA, this additional factor is applied to the RfD by dividing the RfD by such additional factor. The acute or chronic Population Adjusted Dose (aPAD or cPAD) is a modification of the RfD to accommodate this type of FQPA Safety Factor.
For non-dietary risk assessments (other than cancer) the UF is used to determine the LOC. For example, when 100 is the appropriate UF (10X to account for interspecies differences and 10X for intraspecies differences) the LOC is 100. To estimate risk, a ratio of the NOAEL to exposures (margin of exposure (MOE) = NOAEL/exposure) is calculated and compared to the LOC.
The linear default risk methodology (Q*) is the primary method currently used by the Agency to quantify carcinogenic risk. The Q* approach assumes that any amount of exposure will lead to some degree of cancer risk. A Q* is calculated and used to estimate risk which represents a probability of occurrence of additional cancer cases (e.g., risk is expressed as 1 x 10-6 or one in a million). Under certain specific circumstances, MOE calculations will be used for the carcinogenic risk assessment. In this non-linear approach, a “point of departure” is identified below in which carcinogenic effects are not expected. The point of departure is typically a NOAEL based on an endpoint related to cancer effects though it may be a different value derived from the dose response curve. To estimate risk, a ratio of the point of departure to exposure (MOEcancer= point of departure/exposures) is calculated. A summary of the toxicological endpoints for hexythiazox used for human risk assessment is shown in the following Table 2:
|Exposure scenario||Dose used in risk assessment, UF||FQPA SF* and level of concern for risk assessment||Study and toxicological effects|
|Acute dietary females 13-50 years of age||NOAEL = 240 mg/kg/day UF = 100 Acute RfD = 2.4 mg/kg/day||FQPA SF = 1X aPAD = acute RfD FQPA SF = 2.4 mg/kg/day||Developmental toxicity Study - Rat Developmental LOAEL = 720 mg/kg/day based on delayed ossification.|
|Acute dietary general population including infants and children||A dose and endpoint attributable to a single exposure were not identified from the available oral toxicity studies, including maternal toxicity in the developmental toxicity studies.|
|Chronic dietary all populations||NOAEL= 2.5 mg/kg/day UF = 100 Chronic RfD = 0.025 mg/kg/day||FQPA SF = 1X cPAD = chronic RfD FQPA SF = 0.025 mg/kg/day||One year toxicity feeding Study - Dog LOAEL = 12.5 mg/kg/day based on increased absolute and relative adrenal weights and associated adrenal histopathology.|
|Short-term dermal (1 to 7 days) (Occupational)||Oral maternal NOAEL= 240 mg/kg/day (dermal absorption rate = 2 %)||LOC for MOE = 100 (Occupational)||Developmental toxicity Study - Rat LOAEL = 720 mg/kg/day based on decreased maternal body weight gain during gestation days 7-17 and decreased food consumption on gestation days 9-12|
|Intermediate-term dermal (1 week -several months) (Occupational)||Oral NOAEL= 5.4 mg/kg/day (dermal absorption rate = 2%)||LOC for MOE = 100 (Occupational)||13-Week feeding Study - Rat LOAEL = 38.1 mg/kg/day based on increased absolute and relative liver weights in both sexes, increased relative ovarian and kidney weights, and fatty degeneration of the adrenal zone fasciculata.|
|Short-term inhalation (1-7 days) (Occupational)||Oral NOAEL= 240 mg/kg/day (inhalation absorption rate = 100%)||LOC for MOE = 100 (Occupational)||Developmental Toxicity Study - Rat LOAEL = 720 mg/kg/day based on decreased maternal body weight gain during gestation days 7-17 and decreased food consumption on gestation days 9-12.|
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|Intermediate-term inhalation (1 week - several months) (Occupational)||Oral NOAEL= 5.4 mg/kg/day (inhalation absorption rate = 100%)||LOC for MOE = 100 (Occupational)||13-Week Feeding Study - Rat LOAEL = 38.1 mg/kg/day based on increased absolute and relative liver weights in both sexes, increased relative ovarian and kidney weights, and fatty degeneration of the adrenal zone fasciculata.|
|Cancer (oral, dermal, inhalation)||Category C (possible human carcinogen)||Q1* =2.22 x 10-2||Increases in incidence of malignant and combined benign/malignant liver tumors in mice.|
|*The reference to the FQPA Safety Factor refers to any additional safety factor retained due to concerns unique to the FQPA.|
C. Exposure Assessment
1. Dietary exposure from food and feed uses. Tolerances have been established (40 CFR 180.448) for the residues of hexythiazox, in or on a variety of raw agricultural commodities (RAC). Tolerances are established on plant commodities ranging from 0.02 ppm on apples to 3.0 ppm on strawberries. Hexythiazox is the common name for the active ingredient in Savey Ovicide/Miticide. When formulated as the product Savey 50 WP, the product is registered for agricultural use on outdoor terrestrial food crops. When sold under an alternate brand name, Hexygon, the product is also registered for commercial non-food use on ornamental and nursery stock. Savey 50 WP contains 50% hexythiazox by weight. For these petitions, SaveyTM will be applied to caneberries, pistachios, tree nuts and stone fruits at a maximum of 0.188 pounds a.i./acre and to mint at a maximum of 0.156 pounds a.i./acre. SaveyTM is formulated as a wettable powder (packaged in open bags or water soluble paks) and is applied once per season or crop. Savey provides control against tetranychid mite species by direct or indirect contact with treated plant surfaces. According to label specifications the use of this product may include alternation of active classes of insecticides on succeeding generations and targeting the most susceptible life stage. Risk assessments were conducted by EPA to assess dietary exposures from hexythiazox in food as follows:
i. Acute exposure. Acute dietary risk assessments are performed for a food-use pesticide if a toxicological study has indicated the possibility of an effect of concern occurring as a result of 1-day or single exposure. The Dietary Exposure Evaluation Model (DEEMTM) analysis evaluated the individual food consumption as reported by respondents in the USDA 1989-1992 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 acute exposure assessments: For acute dietary risk assessments, the entire distribution of single day food consumption events is combined with a single residue level (deterministic analysis) to obtain a distribution of exposure in mg/kg.
A conservative analysis was performed using existing and EPA-recommended tolerance level residues, DEEMTM default processing factors, and 100% crop treated information for all commodities. For acute dietary risk, EPA's level of concern is < 100% aPAD. The acute dietary exposure estimate for the females 13-50 years old subgroup is presented in Table 3 at the 95th percentile. The results of the acute analysis indicate that the estimated acute dietary risk for females 13-50 years old associated with the existing and EPA-recommended uses of hexythiazox is below EPA's level of concern.
|Subgroup||Exposure (mg/kg/day)||% aPAD|
|Females 13-50 years old||0.002619||< 1-|
EPA notes that there is a degree of uncertainty in extrapolating exposures for certain population subgroups which may not be sufficiently represented in the consumption surveys, (e.g., nursing infants). Therefore, risks estimated for these subpopulations were included in representative populations having sufficient numbers of survey respondents (e.g., all infants or females, 13-50 years old). Thus, the population subgroups listed in Tables 5 and 6 include those subgroups having sufficient numbers of survey respondents in the CSFII food consumption survey to be considered statistically reliable.
ii. Chronic exposure. In conducting this chronic dietary risk assessment the DEEMTM analysis evaluated the individual food consumption as reported by respondents in the USDA 1989-1992 nationwide CSFII and accumulated exposure to the chemical for each commodity. The following assumptions were made for the chronic exposure assessments: For chronic dietary risk assessments for residues in food, the 3-day average of consumption for each sub-population is combined with residues in commodities to determine average exposure in mg/kg/day. A partially refined chronic analysis was performed using anticipated residue (AR) levels, processing factors (where applicable), and percent crop treated (PCT) information. For chronic dietary risk, EPA's level of concern is > 100% cPAD. Dietary exposure estimates for the U.S. population and other representative subgroups are presented in Table 4. The results of the chronic analysis indicate that the estimated chronic dietary risk associated with the existing and EPA-recommended uses of hexythiazox is below EPA's level of concern for the U.S. population and all population subgroups.
|Subgroups||Exposure (mg/kg/day)||% cPAD|
|U.S. population||0.000011||< 1|
|All infants (< 1 year old)||0.000034||< 1|
|Start Printed Page 19884|
|Children (1-6 years old)||0.000029||< 1|
|Children (7-12 years old)||0.000016||< 1|
|Females (13-50 years old)||0.000008||< 1|
|Males (13-19 years old)||0.000004||< 1|
|Males (20+ years old)||0.000008||< 1|
|Seniors (55+ years old)||0.000010||< 1|
iii. Cancer. A partially refined carcinogenic risk estimate analysis was performed using AR levels, processing factors (where applicable), and PCT information. The dietary exposure estimate from residues in food for the U.S. population is presented in Table 5. The result of the carcinogenicity analysis indicates that the estimated dietary risk from residues in food associated with the existing recommended uses is below the level the Agency generally considers negligible for excess lifetime cancer risk (the range of 10-6).
|Subgroup||Exposure (mg/kg/day)||Lifetime Risk|
|U.S. population||0.000011||2.54 x 10-7|
For the chronic and cancer analyses, ARs from field trial data, the weighted average of PCT Quantitative Usage Analyses (QUA), and processing factors (where applicable) were used (see Table 6). DEEM processing factors were used unless otherwise noted in Table 6.
|Commoditya||Established or recommended tolerances (ppm)||Processing factorb||AR (ppm)||CT/anticipated market share (%)c|
|Caneberry crop subgroup||1.0||NA||0.34||15|
|Hog fat||0.02||NA||6.3 x 10-10 e|
|Hog liver||0.02||NA||4.8 x 10-9e|
|Hog meat by-products (except liver)||0.02||NA||2.0 x 10-9e|
|Meat by-products (except liver)d||0.02||NA||0.000024|
|Start Printed Page 19885|
|Plum, prune, dried||0.40||4.9 x||0.050||<1|
|Plum, prune, fresh||0.10||NA||0.050||<1|
|Refined cottonseed oil||0.20||0.13x||0.059||1|
|Wet apple pomace||0.80||2.4 x||0.12||4|
|a ARs were not calculated for commodities not included in the current petitions.|
|b DEEMTM default value used unless otherwise stated; DEEMTM default ratio kept constant for “apple-juice/cider” and “apple-juice-concentrate”.|
|c Electronic correspondence.|
|d These ARs were used for fat and meat byproducts of cattle, goats, horses, and sheep in the chronic and cancer analyses.|
|e These ARs were rounded up to 0.000001 ppm because DEEMTM cannot accommodate more than 6 place holders.|
iv. Anticipated residue and PCT information. Section 408(b)(2)(E) authorizes EPA to use available data and information on the anticipated residue levels of pesticide residues in food and the actual levels of pesticide chemicals that have been measured in food. If EPA relies on such information, EPA must require that data be provided 5 years after the tolerance is established, modified, or left in effect, demonstrating that the levels in food are not above the levels anticipated. Following the initial data submission, EPA is authorized to require similar data on a time frame it deems appropriate. As required by section 408(b)(2)(E), EPA will issue a Data Call-In for information relating to anticipated residues to be submitted no later than 5 years from the date of issuance of this tolerance.
Section 408(b)(2)(F) states that the Agency may use data on the actual percent of food treated for assessing chronic dietary risk only if the Agency can make the following findings: Condition 1, that the data used are reliable and provide a valid basis to show what percentage of the food derived from such crop is likely to contain such pesticide residue; Condition 2, that the exposure estimate does not underestimate exposure for any significant subpopulation group; and Condition 3, if data are available on pesticide use and food consumption in a particular area, the exposure estimate does not understate exposure for the population in such area. In addition, the Agency must provide for periodic evaluation of any estimates used. To provide for the periodic evaluation of the estimate of PCT as required by section 408(b)(2)(F), EPA may require registrants to submit data on PCT.
The Agency used PCT information specified above. The Agency believes that the three conditions listed above have been met. With respect to Condition 1, PCT estimates are derived from Federal and private market survey data, which are reliable and have a valid basis. EPA uses a weighted average PCT for chronic dietary exposure estimates. This weighted average PCT figure is derived by averaging State-level data for a period of up to 10 years, and weighting for the more robust and recent data. A weighted average of the PCT reasonably represents a person's dietary exposure over a lifetime, and is unlikely to underestimate exposure to an individual because of the fact that pesticide use patterns (both regionally and nationally) tend to change continuously over time, such that an individual is unlikely to be exposed to more than the average PCT over a lifetime. The Agency is reasonably certain that the percentage of the food treated is not likely to be an underestimation. As to Conditions 2 and 3, regional consumption information and consumption information for significant subpopulations is taken into account through EPA's computer-based model for evaluating the exposure of significant subpopulations including several regional groups. Use of this consumption information in EPA's risk assessment process ensures that EPA's exposure estimate does not understate exposure for any significant subpopulation group and allows the Agency to be reasonably certain that no regional population is exposed to residue levels higher than those estimated by the Agency. Other than the data available through national food consumption surveys, EPA does not have available information on the regional consumption of food to which hexythiazox may be applied in a particular area.
2. Dietary exposure from drinking water. The Agency lacks sufficient monitoring exposure data to complete a comprehensive dietary exposure analysis and risk assessment for hexythiazox in drinking water. Because the Agency does not have comprehensive monitoring data, Start Printed Page 19886drinking water concentration estimates are made by reliance on simulation or modeling taking into account data on the physical characteristics of hexythiazox.
The Agency uses the Generic Estimated Environmental Concentration (GENEEC) or the Pesticide Root Zone/Exposure Analysis Modeling System (PRZM/EXAMS) to estimate pesticide concentrations in surface water and SCI-GROW, which predicts pesticide concentrations in ground water. In general, EPA will use GENEEC (a tier 1 model) before using PRZM/EXAMS (a tier 2 model) for a screening-level assessment for surface water. The GENEEC model is a subset of the PRZM/EXAMS model that uses a specific high-end runoff scenario for pesticides. GENEEC incorporates a farm pond scenario, while PRZM/EXAMS incorporate an index reservoir environment in place of the previous pond scenario. The PRZM/EXAMS model includes a percent crop area factor as an adjustment to account for the maximum percent crop coverage within a watershed or drainage basin.
None of these models include consideration of the impact processing (mixing, dilution, or treatment) of raw water for distribution as drinking water would likely have on the removal of pesticides from the source water. The primary use of these models by the Agency at this stage is to provide a coarse screen for sorting out pesticides for which it is highly unlikely that drinking water concentrations would ever exceed human health levels of concern.
Since the models used are considered to be screening tools in the risk assessment process, the Agency does not use estimated environmental concentrations (EECs) from these models to quantify drinking water exposure and risk as a %RfD or %PAD. Instead, drinking water levels of comparison (DWLOCs) are calculated and used as a point of comparison against the model estimates of a pesticide's concentration in water. DWLOCs are theoretical upper limits on a pesticide's concentration in drinking water in light of total aggregate exposure to a pesticide in food, and from residential uses. Since DWLOCs address total aggregate exposure to hexythiazox they are further discussed in the aggregate risk sections below.
Based on the GENEEC and SCI-GROW models the EECs of hexythiazox for acute exposures are estimated to be 1.81 parts per billion (ppb) for surface water and 0.009 ppb for ground water. The EECs for chronic exposures are estimated to be 0.91 ppb for surface water and 0.009 ppb for ground water.
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). Hexythiazox is not registered for use on any sites that would result in residential exposure.
4. Cumulative exposure to substances with a common mechanism of toxicity. Section 408(b)(2)(D)(v) 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 does not have, at this time, available data to determine whether hexythiazox has a common mechanism of toxicity with other substances or how to include this pesticide in a cumulative risk assessment. Unlike other pesticides for which EPA has followed a cumulative risk approach based on a common mechanism of toxicity, hexythiazox 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 hexythiazox 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 final rule for Bifenthrin Pesticide Tolerances (62 FR 62961, November 26, 1997).
D. Safety Factor for Infants and Children
1. Safety factor for infants and children—i. In general. FFDCA section 408 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 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 margin of exposure (MOE) analysis or through using an UF (safety) in calculating a dose level that poses no appreciable risk to humans.
ii. Prenatal and postnatal sensitivity. The prenatal and postnatal toxicology data base for hexythiazox is complete with respect to FQPA considerations. The results of these studies indicated no increased susceptibility of rats or rabbits to in utero and/or postnatal exposure to hexythiazox. In the developmental toxicity study in rabbits, no developmental effects were seen at doses up to the limit dose. In the developmental toxicity study in rats, the developmental effects (delayed ossification) occurred at the same dose level (720 mg/kg/day) as the maternal effects (decreased maternal body weight gain and decreased food consumption). In the two generation reproduction study, the effects in the offspring (decreased pup body weight during lactation and delayed hair growth and/or eye opening) were observed only at treatment levels which resulted in evidence of parental toxicity (decreased body weight gain and increased absolute and relative liver, kidney, and adrenal weights).
A developmental neurotoxicity (DNT) study is not required at this time. However, EPA has requested an evaluation to determine the relationship between the adrenal effects (increased adrenal weights and/or adrenal pathology) seen in four studies (90-day feeding study in rats, chronic/carcinogenicity rat, chronic dog, and 2-generation reproduction study in rats) and the need for a DNT. It appears that the effects are more endocrine-related (not developmental). The possibility of the effects being endocrine-related is also supported by reports of ovarian weight increases in several studies in rats. In addition, the results of the developmental toxicity studies in rats and rabbits and the 2-generation reproduction study do not support a DNT. No neuropathology or central nervous system (CNS) malformations were seen in the developmental toxicity studies. In the 2-generation reproduction study in rats, there were no findings in pups that were suggestive of changes in neurological development, although no functional assessment was performed. Additionally, there was no evidence of neurotoxicity in other studies.
2. Conclusion. There is a complete toxicity data base for hexythiazox and exposure data are complete or are estimated based on data that reasonably accounts for potential exposures. EPA determined that the 10X safety factor to protect infants and children should be removed and reduced to 1X. The FQPA factor is removed because an additional safety factor is not needed to protect the safety of infants and children. Start Printed Page 19887
E. Aggregate Risks and Determination of Safety
To estimate total aggregate exposure to a pesticide from food, drinking water, and residential uses, the Agency calculates DWLOCs which are used as a point of comparison against the model estimates of a pesticide's concentration in water (EECs). DWLOC values are not regulatory standards for drinking water. DWLOCs are theoretical upper limits on a pesticide's concentration in drinking water in light of total aggregate exposure to a pesticide in food and residential uses. In calculating a DWLOC, the Agency determines how much of the acceptable exposure (i.e., the PAD) is available for exposure through drinking water e.g., allowable chronic water exposure (mg/kg/day) = cPAD - (average food + residential exposure). This allowable exposure through drinking water is used to calculate a DWLOC.
A DWLOC will vary depending on the toxic endpoint, drinking water consumption, and body weights. Default body weights and consumption values as used by EPA to calculate DWLOCs: 2L/70 killogram (kg) (adult male), 2L/60 kg (adult female), and 1L/10 kg (child). Default body weights and drinking water consumption values vary on an individual basis. This variation will be taken into account in more refined screening-level and quantitative drinking water exposure assessments. Different populations will have different DWLOCs. Generally, a DWLOC is calculated for each type of risk assessment used: acute, short-term, intermediate-term, chronic, and cancer.
When EECs for surface water and ground water are less than the calculated DWLOCs, EPA concludes with reasonable certainty that exposures to the pesticide in drinking water (when considered along with other sources of exposure for which EPA has reliable data) would not result in unacceptable levels of aggregate human health risk at this time. Because EPA considers the aggregate risk resulting from multiple exposure pathways associated with a pesticide's uses, levels of comparison in drinking water may vary as those uses change. If new uses are added in the future, EPA will reassess the potential impacts of residues of the pesticide in drinking water as a part of the aggregate risk assessment process.
1. Acute risk. Acute aggregate risk estimates are below EPA's level of concern. An acute conservative dietary exposure analysis for hexythiazox was performed using tolerance level residues, DEEMTM default processing factors, and assuming 100% CT for all commodities. The acute analysis applied to females 13-50 years old. The acute dietary exposure estimates (food only) for this population subgroup was <1% of the aPAD. Thus, the acute dietary risk associated with the proposed uses of hexythiazox does not exceed EPA's level of concern (>100% aPAD). The surface and ground water EECs were used to compare against back-calculated DWLOCs for aggregate risk assessments. For the acute scenario, the DWLOCs are 72,000 ppb for females 13-50 years old. For ground and surface water, the EECs for hexythiazox are less than EPA's DWLOCs for hexythiazox in drinking water as a contribution to acute aggregate exposure (Table 7). Therefore, EPA concludes with reasonable certainty that residues of hexythiazox in drinking water do not contribute significantly to the acute aggregate human health risk at the present time, as shown in Table 7:
|Scenario/population subgroup||aPAD, mg/kg/day||Dietary exposure, mg/kg/day||Allowable drinking water exposure1, mg/kg/day||DWLOC, ppb||Surface water, ppb||Ground water, ppb|
|Females (13-50 years old)||2.4||0.002619||2.4||72,000||1.8||0.009|
|1 Allowable Drinking Water Exposure (mg/kg/day) = aPAD (mg/kg/day) - Dietary Exposure from DEEM (mg/kg/day)|
2. Chronic risk. Chronic (non-cancer) aggregate risk estimates are below EPA's level of concern. A partially refined, chronic dietary exposure analysis for residues in food was performed using AR levels for most crops, processing factors where applicable and PCT or anticipated market share information for all crops. The chronic analysis applied to the U.S. population and all population subgroups. The chronic (non-cancer) dietary exposure estimates (food only) for the general U.S. population and all population subgroups were < 1% of the cPAD. Thus, the chronic (non-cancer) dietary risk associated with the proposed uses of hexythiazox does not exceed EPA's level of concern (>100% cPAD). The surface and ground water EECs were used to compare against back-calculated DWLOCs for aggregate risk assessments. For the chronic (non-cancer) scenario, the DWLOCs are 870 ppb for the U.S. population, 870 ppb for females 13-50 years old, and 250 ppb for all infants (< 1 year old). For ground and surface water, the EECs for hexythiazox are less than EPA's DWLOCs for hexythiazox in drinking water as a contribution to chronic (non-cancer) aggregate exposure (Table 8). Therefore, EPA concludes with reasonable certainty that residues of hexythiazox in drinking water do not contribute significantly to the chronic (non-cancer) aggregate human health risk at the present time, as shown in the following Table 8:
|Scenario/population subgroup||cPAD, mg/kg/day||Dietary exposure, mg/kg/day||Allowable drinking water exposure,1 mg/kg/day||DWLOC, ppb||Surface water EEC, ppb||Ground water EEC, ppb|
|All infants (< 1 year old)||0.025||0.000034||0.025||250||0.910||0.009|
|Children (1-6 years old)||0.025||0.000029||0.025||250||0.910||0.009|
|Start Printed Page 19888|
|Children (7-12 years old)||0.025||0.000016||0.025||250||0.910||0.009|
|Females (13-50 years old)||0.025||0.000008||0.025||870||0.910||0.009|
|Males (13-19 years old)||0.025||0.000004||0.025||870||0.910||0.009|
|Males (20+ years old)||0.025||0.000008||0.025||870||0.910||0.009|
|Seniors (55+ years old)||0.025||0.000010||0.025||870||0.910||0.009|
|1 Allowable Drinking Water Exposure (mg/kg/day) = cPAD (mg/kg/day) - Chronic Dietary Exposure from DEEM (mg/kg/day).|
3. Short-term risk. Short-term aggregate exposure takes into account residential exposure plus chronic exposure to food and water (considered to be a background exposure level). Hexythiazox 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 do not exceed the Agency's level of concern.
4. Intermediate-term risk. Intermediate-term aggregate exposure takes into account residential exposure plus chronic exposure to food and water considered to be a background exposure level. Hexythiazox 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 do not exceed the Agency's level of concern.
5. Aggregate cancer risk for U.S. population. Chronic (cancer) aggregate risk estimates are below EPA's level of concern. A partially refined analysis was performed using AR levels for most crops, processing factors where applicable, and PCT or anticipated market share information for all crops. The chronic cancer analysis applied to the U.S. population. The carcinogenic risk estimate (food only) for the general U.S. population was 2.5 x 10-7. Thus, the estimated dietary cancer risk to the U.S. population associated with the existing and recommended uses is below the level the Agency generally considers negligible for excess lifetime cancer risk (in the range of 10-7). The surface and ground water EECs were used to compare against back-calculated DWLOCs for aggregate risk assessments. For the carcinogenic risk scenario, the DWLOCs are 1.2 ppb for the U.S. population. For ground and surface water, the EECs for hexythiazox are less than EPA's DWLOCs for hexythiazox in drinking water as a contribution to carcinogenic aggregate exposure (Table 9). Therefore, EPA concludes with reasonable certainty that residues of hexythiazox in drinking water do not contribute significantly to the carcinogenic aggregate human health risk at the present time.
|Scenario/population subgroup||Q1*||Dietary exposure, mg/kg/day||Allowable drinking water exposure1, mg/kg/day||DWLOC, ppb2||Surface water EEC, ppb||Ground water EEC, ppb|
|U.S. population||2.2 2 x 10-2||0.000011||0.000034||1.2||0.91||0.009|
|1 Allowable Drinking Water Exposure (mg/kg/day)= negligible risk(1x10-6)/Q1* - (average food + residential exposure (ADD) (mg/kg/day)|
|2 DWLOC cancer= chronic water exposure (mg/kg/day) x body weight (kg)/water consumption (L) x 10-3 (mg/μg)|
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 hexythiazox residues.
IV. Other Considerations
A. Metabolism in Plants and Animals
1. Plants. Metabolism studies have been submitted and reviewed in conjunction with petitions for hexythiazox tolerances in/on apples, pears, grapes and citrus. The residues of concern in these crops are hexythiazox and its metabolites containing the (4-chlorophenyl)-4-methyl-2-oxo-3-thiazolidine moiety as specified in 40 CFR 180.448.
No further plant metabolism data are necessary to support the proposed uses on caneberries, mint, tree nuts, pistachios, and stone fruit. However, as metabolism data are only available for fruit, the nature of the residue is not understood in mint. Given the limited metabolism of hexythiazox observed in apple, pear, grape and citrus leaves and that mint is a minor use (with minimal dietary exposure), EPA concludes that the nature of the residue is understood in mint for the purposes of this petition only.
2. Livestock. The Agency has previously concluded that the nature of the residues of hexythiazox in cattle and goats is adequately understood. The residues of concern in ruminants are hexythiazox and its metabolites containing the (4-chlorophenyl)-4-methyl-2-oxo-3-thiazolidine moiety.
As there are no poultry feed items currently associated with caneberries, mint, tree nuts, pistachios, or stone Start Printed Page 19889fruit, issues pertaining to the nature of the residue in poultry are not germane to these petitions.
B. Analytical Enforcement Methodology
The HPLC/UV analytical methods used for determining the combined residues of hexythiazox and its metabolites in caneberries, mint, tree nuts, pistachios, and stone fruit are adequate for data collection purposes. Adequate method validation data were submitted. These methods are based on Method AMR-985-87, which has been deemed acceptable as a tolerance enforcement method in conjunction with a petition for use on apples. The method has been validated for use on various crop commodities, and has been forwarded to the Food and Drug Administration (FDA) for inclusion in PAM II. This earlier method is considered sufficient to enforce the proposed permanent tolerances for residues in/on caneberries, mint, tree nuts, pistachios, and stone fruit. The PAM-II analytical enforcement method for residues of hexythiazox and its metabolites (AMR-985-87) is available to measure residues in meat, milk, poultry and eggs.
The petitioner has submitted data describing the testing of hexythiazox through FDA Multiresidue Protocols C through E. This information has been forwarded to the FDA for inclusion in PAM I . In addition, hexythiazox and its metabolites have been tested according to the FDA Multiresidue Protocols C through E by BASF Corporation in conjunction with a petition for use on hops. The information pertaining to the testing of hexythiazox per se, which indicated that hexythiazox was not recovered from hops, has been forwarded to the FDA. Multiresidue method testing data for the major metabolites of hexythiazox were forwarded to FDA.
C. Magnitude of Residues
An adequate number of residue field trials reflecting the proposed use rules were submitted to EPA to demonstrate that tolerances for the tree nut group at 0.30 ppm; plums at 0.10 ppm; fresh prunes at 0.10 ppm; dried prunes at 0.40 ppm; pistachio at 0.30 ppm; peppermint (tops) at 2.0 ppm; spearmint (tops) at 2.0 ppm; and the caneberry group subgroup at 1.0 ppm will not be exceeded when hexythiazox products labeled for these uses are used as directed. For plums, EPA is requiring submission of additional crop field studies from three other plum growing areas of the United States as confirmatory data in support of the proposed tolerances. In addition, for mint, EPA is requiring submission of additional crop field studies from two other mint growing areas of the United States as confirmatory data in support of the proposed tolerances.
D. Rotational Crop Restrictions
As caneberries, mint, tree nuts, pistachios, and plums are perennial crops, confined and field rotational crop studies are not required to support the subject petitions.
E. International Residue Limits
The Codex Alimentarius Commission has established maximum residue limits (MRLs) for residues of hexythiazox per se in/on cherries and peaches at 1 mg/kg, and plums (including prunes) at 0.2 mg/kg; no codex MRLs are established for residues in/on caneberry and mint commodities. The Codex MRLs and U.S. tolerances are not compatible because the U.S. tolerance expression currently includes parent hexythiazox and its metabolites containing the (4-chlorophenyl)-4-methyl-2-oxo-3-thiazolidine moiety. Neither Canadian nor Mexican MRLs have been established for residues of hexythiazox in the subject crops.
Therefore, tolerances are established for residues of the ovicide/miticide hexythiazox (trans-5-(4-chlorophenyl)-N-cyclohexyl-4-methyl-2-oxothiazolidine-3-carboxamide) and its metabolites containing the (4-chlorophenyl)-4-methyl-2-oxo-3-thiazolidine moiety (expressed as parent) in or on the tree nut group at 0.30 ppm; plums at 0.10 ppm; fresh prunes at 0.10 ppm; dried prunes at 0.40 ppm; pistachio at 0.30 ppm; peppermint (tops) at 2.0 ppm; spearmint (tops) at 2.0 ppm; and the caneberry crop subgroup at 1.0 ppm.
Conditional registration for use of hexythiazox on these crops are being proposed to allow development and review of a 21-day dermal toxicity study (OPPTS Guideline No. 870.3200) (data gap); an acceptable in vivo mouse micronucleus assay (OPPTS Guideline No. 870.5375); three additional plum residue field trials; and two additional mint residue field trials. The registrant has agreed to submit the 21-day dermal toxicity study and the in vivo mouse micronucleus assay in their letter dated September 15, 2000.
VI. Objections and Hearing Requests
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. Although the procedures in those regulations require some modification to reflect the amendments made to the FFDCA by the FQPA of 1996, EPA will continue to use those procedures, with appropriate adjustments, until the necessary modifications can be made. The new section 408(g) provides essentially the same process for persons to “object” to a regulation for an exemption from the requirement of a tolerance issued by EPA under new section 408(d), as was provided in the old FFDCA sections 408 and 409. However, the period for filing objections is now 60 days, rather than 30 days.
A. What Do I Need to Do to File an Objection or Request a Hearing?
You must file your objection or request a hearing on this regulation in accordance with the instructions provided in this unit and in 40 CFR part 178. To ensure proper receipt by EPA, you must identify docket control number OPP-301117 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 June 18, 2001.
1. Filing the request. Your objection must specify the specific provisions in the regulation that you object to, and the grounds for the objections (40 CFR 178.25). If a hearing is requested, the objections must include a statement of the factual issues(s) on which a hearing is requested, the requestor's contentions on such issues, and a summary of any evidence relied upon by the objector (40 CFR 178.27). Information submitted in connection with an objection or hearing request may be claimed confidential by marking any part or all of that information as CBI. Information so marked will not be disclosed except in accordance with procedures set forth in 40 CFR part 2. A copy of the information that does not contain CBI must be submitted for inclusion in the public record. Information not marked confidential may be disclosed publicly by EPA without prior notice.
Mail your written request to: Office of the Hearing Clerk (1900), Environmental Protection Agency, 1200 Pennsylvania Ave., NW., Washington, DC 20460. You may also deliver your request to the Office of the Hearing Clerk in Rm. C400, Waterside Mall, 401 M St., SW., Washington, DC 20460. The Office of the Hearing Clerk is open from 8 a.m. to 4 p.m., Monday through Friday, excluding legal holidays. The telephone number for the Office of the Hearing Clerk is (202) 260-4865. Start Printed Page 19890
2. Tolerance fee payment. If you file an objection or request a hearing, you must also pay the fee prescribed by 40 CFR 180.33(i) or request a waiver of that fee pursuant to 40 CFR 180.33(m). You must mail the fee to: EPA Headquarters Accounting Operations Branch, Office of Pesticide Programs, P.O. Box 360277M, Pittsburgh, PA 15251. Please identify the fee submission by labeling it “Tolerance Petition Fees.”
EPA is authorized to waive any fee requirement “when in the judgement of the Administrator such a waiver or refund is equitable and not contrary to the purpose of this subsection.” For additional information regarding the waiver of these fees, you may contact James Tompkins by phone at (703) 305-5697, by e-mail at email@example.com, or by mailing a request for information to Mr. Tompkins at Registration Division (7505C), Office of Pesticide Programs, Environmental Protection Agency, 1200 Pennsylvania Ave., NW., Washington, DC 20460.
If you would like to request a waiver of the tolerance objection fees, you must mail your request for such a waiver to: James Hollins, Information Resources and Services Division (7502C), Office of Pesticide Programs, Environmental Protection Agency, 1200 Pennsylvania Ave., NW., Washington, DC 20460.
3. Copies for the docket. In addition to filing an objection or hearing request with the Hearing Clerk as described in Unit VI.A., you should also send a copy of your request to the PIRIB for its inclusion in the official record that is described in Unit I.B.2. Mail your copies, identified by docket control number OPP-301117, to: Public Information and Records Integrity Branch, Information Resources and Services Division (7502C), Office of Pesticide Programs, Environmental Protection Agency, 1200 Pennsylvania Ave., NW., Washington, DC 20460. In person or by courier, bring a copy to the location of the PIRIB described in Unit I.B.2. You may also send an electronic copy of your request via e-mail to: firstname.lastname@example.org. Please use an ASCII file format and avoid the use of special characters and any form of encryption. Copies of electronic objections and hearing requests will also be accepted on disks in WordPerfect 6.1/8.0 or ASCII file format. Do not include any CBI in your electronic copy. You may also submit an electronic copy of your request at many Federal Depository Libraries.
B. When Will the Agency Grant a Request for a Hearing?
A request for a hearing will be granted if the Administrator determines that the material submitted shows the following: There is a genuine and substantial issue of fact; there is a reasonable possibility that available evidence identified by the requestor would, if established resolve one or more of such issues in favor of the requestor, taking into account uncontested claims or facts to the contrary; and resolution of the factual issues(s) in the manner sought by the requestor would be adequate to justify the action requested (40 CFR 178.32).
VII. Regulatory Assessment Requirements
This final rule establishes a tolerance under FFDCA section 408(d) 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). 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 FFDCA section 408(d), such as the tolerance in this final rule, do not require the issuance of a proposed rule, the requirements of the Regulatory Flexibility Act (RFA) (5 U.S.C. 601 et seq.) do not apply. 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 FFDCA section 408(n)(4).
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 tribe 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.
VIII. Submission to Congress and the Comptroller General
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 Start Printed Page 19891the 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 180
- Environmental protection
- Administrative practice and procedure
- Agricultural commodities
- Pesticides and pests
- Reporting and recordkeeping requirements
Dated: April 9, 2001.
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 180.448 is amended by revising the table in paragraph (a) to read as follows:End Amendment Part
(a) General. * * *
|Commodity||Parts per million|
|Apple, wet pomace||0.80|
|Caneberry crop subgroup||1.0|
|Fruit, stone, group (except plums||1.0|
|Nut, tree, group||0.30|
|Plum, prune, dried||0.40|
|Plum, prune, fresh||0.10|
[FR Doc. 01-9596 Filed 4-17-01; 8:45 am]
BILLING CODE 6560-50-S