96-30468. Metolachlor Pesticide Tolerance; Emergency Exemption For Use on Spinach  

  • [Federal Register Volume 61, Number 231 (Friday, November 29, 1996)]
    [Rules and Regulations]
    [Pages 60617-60622]
    From the Federal Register Online via the Government Publishing Office [www.gpo.gov]
    [FR Doc No: 96-30468]
    
    
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    ENVIRONMENTAL PROTECTION AGENCY
    40 CFR Part 180
    
    [OPP-300443; FRL-5574-7]
    RIN 2070-AB78
    
    
    Metolachlor Pesticide Tolerance; Emergency Exemption For Use on 
    Spinach
    
    AGENCY: Environmental Protection Agency (EPA).
    
    ACTION: Final rule.
    
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    SUMMARY: This regulation establishes a time-limited tolerance for 
    combined residues of the herbicide metolachlor in or on the raw 
    agricultural commodity spinach in connection with EPA's granting of 
    emergency exemptions under section 18 of the Federal Insecticide, 
    Fungicide, and Rodenticide Act authorizing use of metolachlor on 
    spinach in Arkansas, Oklahoma, Texas and Virginia. This regulation 
    establishes a maximum permissible level for residues of metolachlor in 
    this food pursuant to section 408(l)(6) of the Federal Food, Drug and 
    Cosmetic Act, as amended by the Food Quality Protection Act of 1996. 
    This tolerance will expire and be revoked automatically without further 
    action by EPA on November 15, 1998.
    DATES: This regulation becomes effective November 29, 1996. This 
    regulation expires and is revoked automatically without further action 
    by EPA on November 15, 1998. Objections and requests for hearings must 
    be received by EPA on January 28, 1997.
    
    ADDRESSES: Written objections and hearing requests, identified by the 
    docket number, [OPP-300443], must be submitted to: Hearing Clerk 
    (1900), Environmental Protection Agency, Rm. M3708, 401 M St., SW., 
    Washington, DC 20460. Fees accompanying objections and hearing requests 
    shall be labeled ``Tolerance Petition Fees'' and forwarded to: EPA 
    Headquarters Accounting Operations Branch, Office of Pesticide Programs 
    (Tolerance Fees), P.O. Box 360277M, Pittsburgh, PA 15251. A copy of any 
    objections and hearing requests filed with the Hearing Clerk identified 
    by the docket number, [OPP-300443], should be submitted to: Public 
    Response and Program Resources Branch, Field Operations Division 
    (7506C), Office of Pesticide Programs, Environmental Protection Agency, 
    401 M St., SW., Washington, DC 20460. In
    
    [[Page 60618]]
    
    person, bring a copy of objections and hearing requests to Rm. 1132, CM 
    #2, 1921 Jefferson Davis Hwy., Arlington, VA.
        A copy of objections and hearing requests filed with the Hearing 
    Clerk may also be submitted electronically by sending electronic mail 
    (e-mail) to: opp-docket@epamail.epa.gov. Copies of objections and 
    hearing requests must be submitted as an ASCII file avoiding the use of 
    special characters and any form of encryption. Copies of objections and 
    hearing requests will also be accepted on disks in WordPerfect 5.1 file 
    format or ASCII file format. All copies of objections and hearing 
    requests in electronic form must be identified by the docket number 
    [OPP-300443]. No Confidential Business Information (CBI) should be 
    submitted through e-mail. Electronic copies of objections and hearing 
    requests on this rule may be filed online at many Federal Depository 
    Libraries. Additional information on electronic submissions can be 
    found below in this document.
    
    FOR FURTHER INFORMATION CONTACT: By mail: Margarita Collantes, 
    Registration Division (7505W), Environmental Protection Agency, 401 M 
    St., SW., Washington, DC 20460. Office location, telephone number, and 
    e-mail: Sixth Floor, Crystal Station #1, 2800 Jefferson Davis Highway, 
    Arlington, VA 22202, (703) 308-8347, e-mail: 
    collantes.margarita@epamail.epa.gov.
    SUPPLEMENTARY INFORMATION: EPA, on its own initiative, pursuant to 
    section 408(e) and (l)(6) of the Federal Food, Drug, and Cosmetic Act 
    (FFDCA), 21 U.S.C. 346a(e) and (l)(6), is establishing a tolerance for 
    residues of the herbicide metolachlor, 2-chloro-N-(2-ethyl-6-
    methylphenyl)-N-(2-methoxy-1-methylethyl)acetamide in or on spinach at 
    0.3 part per million (ppm). This tolerance will expire and be revoked 
    automatically without further action by EPA on November 15, 1998.
    
    I. Background and Statutory Authority
    
        The Food Quality Protection Act of 1996 (FQPA) (Pub. L. 104-170) 
    was signed into law August 3, 1996. FQPA amends both the Federal Food, 
    Drug, and Cosmetic Act (FFDCA), 21 U.S.C. 301 et seq., and the Federal 
    Insecticide, Fungicide, and Rodenticide Act (FIFRA), 7 U.S.C. 136 et 
    seq. The FQPA amendments went into effect immediately. Among other 
    things, FQPA amends FFDCA to bring all EPA pesticide tolerance-setting 
    activities under a new section 408 with a new safety standard and new 
    procedures. These activities were discussed in detail in the final rule 
    establishing a tolerance for an emergency exemption for use of 
    propiconazole on sorghum (61 FR 58135, Nov. 13, 1996).
        New section 408(b)(2)(A)(i) 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, 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....''
        Section 18 of FIFRA authorizes EPA to exempt any Federal or State 
    agency from any provision of FIFRA, if EPA determines that ``emergency 
    conditions exist which require such exemption.'' This provision was not 
    amended by FQPA. EPA has established regulations governing such 
    emergency exemptions in 40 CFR part 166.
        Section 408(l)(6) requires EPA to establish a time-limited 
    tolerance or exemption from the requirement for a tolerance for 
    pesticide chemical residues in food that will result from the use of a 
    pesticide under an emergency exemption granted by EPA under section 18 
    of FIFRA. Section 408(l)(6) also requires EPA to promulgate regulations 
    by August 3, 1997, governing the establishment of tolerances and 
    exemptions under section 408(l)(6) and requires that the regulations be 
    consistent with section 408(b)(2) and (c)(2) and FIFRA section 18.
        Section 408(l)(6) allows EPA to establish tolerances or exemptions 
    from the requirement for a tolerance, in connection with EPA's granting 
    of FIFRA section 18 emergency exemptions, without providing notice or a 
    period for public comment. Thus, consistent with the need to act 
    expeditiously on requests for emergency exemptions under FIFRA, EPA can 
    establish such tolerances or exemptions under the authority of section 
    408(e) and (l)(6) without notice and comment rulemaking.
        In establishing section 18-related tolerances and exemptions during 
    this interim period before EPA issues the section 408(l)(6) procedural 
    regulation and before EPA makes its broad policy decisions concerning 
    the interpretation and implementation of the new section 408, EPA does 
    not intend to set precedents for the application of section 408 and the 
    new safety standard to other tolerances and exemptions. Rather, these 
    early section 18 tolerance and exemption decisions will be made on a 
    case-by-case basis and will not bind EPA as it proceeds with further 
    rulemaking and policy development. EPA intends to act on section 18-
    related tolerances and exemptions that clearly qualify under the new 
    law.
    
    II. Emergency Exemptions for Metolachlor on Spinach and FFDCA 
    Tolerances
    
        On September 13, 1996, the Texas Department of Agriculture availed 
    itself of the authority to declare the existence of a crisis situation 
    within the State, thereby authorizing use under FIFRA section 18 of 
    metolachlor on spinach for control of various weeds. The States of 
    Arkansas, Oklahoma, and Virginia have also requested specific 
    exemptions for use of metolachlor on spinach in those States to control 
    various weeds. Emergency conditions are determined to exist due to the 
    loss of Antor 4E, diethatyl ethyl, a herbicide used on spinach. NOR-AM 
    Chemical Company no longer manufactures Antor and stocks were exhausted 
    from 1993 production. Furthermore, at the present there is no 
    preemergence herbicide registered to control annual weeds in spinach. 
    Roneet E6 is the only herbicide registered for use on spinach at 
    planting; however, it has proven ineffective as a preemergence control 
    for weeds.
        As part of its assessment of these applications for crisis 
    declaration and emergency exemptions, EPA assessed the potential risks 
    presented by residues of metolachlor on spinach. In doing so, EPA 
    considered the new safety standard in FFDCA section 408(b)(2), and EPA 
    decided to grant the section 18 exemptions only after concluding that 
    the necessary tolerance under FFDCA section 408(l)(6) would be 
    consistent with the new safety standard and with FIFRA section 18. This 
    tolerance for metolachlor will permit the marketing of spinach treated 
    in accordance with the provisions of the section 18 emergency 
    exemptions. Consistent with the need to move quickly on the emergency 
    exemptions and to ensure that the resulting food is safe and lawful, 
    EPA is issuing this tolerance without notice and opportunity for public 
    comment under section 408(e) as provided in section 408(l)(6). Although 
    this tolerance will expire and be
    
    [[Page 60619]]
    
    revoked automatically without further action by EPA on November 5, 
    1998, under FFDCA section 408(l)(5), residues of metolachlor not in 
    excess of the amount specified in the tolerance remaining in or on 
    spinach after that date will not be unlawful, provided the pesticide is 
    applied during the term of, and in accordance with all the conditions 
    of, the emergency exemptions. EPA will take action to revoke this 
    tolerance earlier if any experience with, scientific data on, or other 
    relevant information on this pesticide indicate that the residues are 
    not safe.
        EPA has not made any decisions about whether metolachlor meets the 
    requirements for registration under FIFRA section 3 for use on spinach 
    or whether a permanent tolerance for metolachlor for spinach would be 
    appropriate. This action by EPA does not serve as a basis for 
    registration of metolachlor by a State for special local needs under 
    FIFRA section 24(c). Nor does this action serve as the basis for any 
    States other than those listed above to use this product on spinach 
    under section 18 of FIFRA without following all provisions of section 
    18 as identified in 40 CFR part 166. For additional information 
    regarding the emergency exemptions for metolachlor, contact the 
    Agency's Registration Division at the address provided above.
    
    III. Risk Assessment and Statutory Findings
    
        EPA performs a number of analyses to determine the risks from 
    aggregate exposure to pesticide residues. First, EPA determines the 
    toxicity of pesticides based primarily on toxicological studies using 
    laboratory animals. These studies address many adverse health effects, 
    including (but not limited to) reproductive effects, developmental 
    toxicity, toxicity to the nervous system, and carcinogenicity. For many 
    of these studies, a dose response relationship can be determined, which 
    provides a dose that causes adverse effects (threshold effects) and 
    doses causing no observed effects (the ``no-observed effect level'' or 
    ``NOEL'').
        Once a study has been evaluated and the observed effects have been 
    determined to be threshold effects, EPA generally divides the NOEL from 
    the study with the lowest NOEL by an uncertainty factor (usually 100 or 
    more) to determine the Reference Dose (RfD). The RfD is a level at or 
    below which daily aggregate exposure over a lifetime will not pose 
    appreciable risks to human health. An uncertainty factor (sometimes 
    called a ``safety factor'') of 100 is commonly used since it is assumed 
    that people may be up to 10 times more sensitive to pesticides than the 
    test animals, and that one person or subgroup of the population (such 
    as infants and children) could be up to 10 times more sensitive to a 
    pesticide than another. In addition, EPA assesses the potential risks 
    to infants and children based on the weight of the evidence of the 
    toxicology studies and determines whether an additional uncertainty 
    factor is warranted. Thus, an aggregate daily exposure to a pesticide 
    residue at or below the RfD (expressed as 100 percent or less of the 
    RfD) is generally considered acceptable by EPA.
        Lifetime feeding studies in two species of laboratory animals are 
    conducted to screen pesticides for cancer effects. When evidence of 
    increased cancer is noted in these studies, the Agency conducts a 
    weight of the evidence review of all relevant toxicological data 
    including short term and mutagenicity studies and structure activity 
    relationship. Once a pesticide has been classified as a potential human 
    carcinogen, different types of risk assessments (e.g., linear low dose 
    extrapolations or margin of exposure (MOE) calculation based on the 
    appropriate NOEL) will be carried out based on the nature of the 
    carcinogenic response and the Agency's knowledge of its mode of action.
        In examining aggregate exposure, FFDCA section 408 requires that 
    EPA take into account available and reliable information concerning 
    exposure from the pesticide residue in the food in question, residues 
    in other foods for which there are tolerances, and other non-
    occupational exposures, such as where residues leach into groundwater 
    or surface water that is consumed as drinking water. Dietary exposure 
    to residues of a pesticide in a food commodity are estimated by 
    multiplying the average daily consumption of the food forms of that 
    commodity by the tolerance level or the anticipated pesticide residue 
    level. The Theoretical Maximum Residue Contribution (TMRC) is an 
    estimate of the level of residues consumed daily if each food item 
    contained pesticide residues equal to the tolerance. The TMRC is a 
    ``worst case'' estimate since it is based on the assumptions that food 
    contains pesticide residues at the tolerance level and that 100 percent 
    of the crop is treated by pesticides that have established tolerances. 
    If the TMRC exceeds the RfD or poses a lifetime cancer risk that is 
    greater than approximately one in a million, EPA attempts to derive a 
    more accurate exposure estimate for the pesticide by evaluating 
    additional types of information (anticipated residue data and/or 
    percent of crop treated data) which show, generally, that pesticide 
    residues in most foods when they are eaten are well below established 
    tolerances.
    
    IV. 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. Metolachlor is already registered by EPA for numerous food 
    and feed uses, as well as use on outdoor residential lawn, numerous 
    ornamental plants and trees, highway rights-of-way and recreational 
    area use. EPA has also assessed the toxicology data base for 
    metolachlor in its evaluation of applications for registration on 
    spinach. Thus, EPA has sufficient data to assess the hazards of 
    metolachlor and to make a determination on aggregate exposure, 
    consistent with section 408(b)(2), for the time-limited tolerances for 
    residues of metolachlor on spinach at 0.3 ppm. EPA's assessment of the 
    dietary exposures and risks associated with establishing these 
    tolerances follows.
    
    A. Toxicological Profile
    
        1. Chronic toxicity. Based on the available chronic toxicity data, 
    the Office of Pesticide Programs (OPP) has established the RfD for 
    metolachlor at 0.10 milligrams(mg)/kilogram(kg)/day. The RfD for 
    metolachlor is based on a 1-year feeding study in dogs with a NOEL of 
    9.7 mg/kg/day and an uncertainty factor of 100. Decreased body weight 
    gain was the effect observed at the Lowest Effect Level (LEL) of 33 mg/
    kg/day.
        2. Acute toxicity. OPP has determined that data do not indicate the 
    potential for adverse effects after a single dietary exposure.
        3. Short-term toxicity. OPP has determined that an intermediate 
    term risk assessment is appropriate for occupational and residential 
    routes of exposure. OPP recommends that the NOEL of 100 mg/kg/day, 
    taken from the 21-day dermal toxicity study, be used for these MOE 
    calculations. Effects observed at the lowest observed effect level 
    (LOEL) of 1,000 mg/kg/day are dose-related increases in minor 
    histopathological alterations of the skin, total bilirubin (females), 
    absolute and relative liver weights (males), and relative kidney 
    weights (females). However, no acceptable reliable dermal exposure data 
    to assess these potential risks are available at this time. OPP did
    
    [[Page 60620]]
    
    not identify an inhalation exposure intermediate-term hazard.
        4. Carcinogenicity. Using its Guidelines for Carcinogen Risk 
    Assessment published September 24, 1986 (51 FR 33992), the 
    Carcinogenicity Peer Review Committee (CPRC) has classified metolachlor 
    as a Group C chemical, possible human carcinogen, based on (a) the 
    increased incidence of adenomas and combined adenomas/carcinomas in 
    female rats, both by pair-wise and trend analysis and the replication 
    of this finding in a second study, (b) negative mutagenicity studies, 
    and (c) comparative metabolism studies indicating that metolachlor has 
    a different metabolic profile than acetochlor and alachlor with regard 
    to the quinone imine metabolite. Based on these findings, the CPRC 
    recommended that the NOEL of 15.7 mg/kg/day, from the 2-year feeding 
    study [MRID#: 00129377] in rat, and the MOE approach be used for 
    quantification of risk.
    
    B. Aggregate Exposure
    
        Tolerances for residues of metolachlor in or on food/feed 
    commodities are currently expressed in terms of the combined residues 
    (free and bound) of the herbicide metolachlor [2-chloro-N-(2-ethyl-6-
    methylphenyl)-N-(2-methoxy-1-methylethyl)acetamide] and its 
    metabolites, determined as the derivatives, 2-[(2-ethyl-6-
    methylphenyl)amino]-1-propanol and 4-(2-ethyl-6-methylphenyl)-2-
    hydroxy-5-methyl-3-morpholinone, each expressed as the parent compound 
    (40 CFR 180.368(a), (b), and (c)).
        For the purpose of assessing chronic dietary exposure from 
    metolachlor, EPA assumed tolerance level residues and percent of crop 
    treated refinements to estimate the Anticipated Residue Contribution 
    (ARC) from the proposed and existing food uses of metolachlor. The use 
    of percent of crop treated data for most of the existing food uses in 
    this analysis results in a more refined estimate of exposure than the 
    TMRC.
        Other potential sources of exposure of the general population to 
    residues of pesticides are residues in drinking water and exposure from 
    non-occupational sources. Based on the available studies used in EPA's 
    assessment of environmental risk, metolachlor appears to be moderately 
    persistent and ranges from being mobile to highly mobile in different 
    soils. Data collected from around the United States provides evidence 
    that metolachlor leaches into ground water, occasionally at levels that 
    exceed the Lifetime Health Advisory (HA) Level of 100 parts per billion 
    (ppb). The ``Pesticides In Groundwater Database'' (EPA 734-122-92-001, 
    Sept. 1992), indicates that metolachlor residues were detected in wells 
    in 20 States. Levels exceeded the lifetime HA in three wells located in 
    Wisconsin, New York, and Montana. In eight other States concentrations 
    in some well waters exceeded 10 percent of the HA. Incident reports 
    submitted under 6(a)(2) of FIFRA describe 47 detections of metolachlor 
    in the groundwater of 7 States at concentrations ranging from 0.11 ppb 
    to 116 ppb. Metolachlor is not yet formally regulated under the Safe 
    Drinking Water Act; therefore, no enforcement Maximum Concentration 
    Level (MCL) has been established for it. Metolachlor also has 
    relatively high health advisory levels (1 to 10 day HA level of 2,000 
    ppb and lifetime HA level of 100 ppb).
        Although residue levels of metolachlor exceeding the lifetime HA of 
    100 ppb have been measured, the 1 to 10 day HA level of 2,000 is not 
    exceeded in any well measured and residues over time in these wells are 
    highly unlikely to exceed the lifetime HA of 100 ppb anywhere. As part 
    of the risk mitigation in the metolachlor Registration Eligibility 
    Document (RED), additional label restrictions designed to minimize 
    ground and surface water contamination are required. Groundwater 
    concerns may be mitigated by adhering to these label restrictions and 
    advisory statements.
        Previous experience with persistent and mobile pesticides for which 
    there have been available data to perform quantitative risk assessments 
    have demonstrated that drinking water exposure is typically a small 
    percentage of the total exposure when compared to the total dietary 
    exposure. This observation holds even for pesticides detected in wells 
    and drinking water at levels nearing or exceeding established MCLs. 
    Based on this experience and OPP's best scientific judgement, and 
    considering the low percent of the RfD occupied by dietary exposure 
    estimates including spinach (0.6 percent RfD for U.S. population), EPA 
    does not anticipate that combined exposure from drinking water and 
    dietary exposure would result in an ARC that exceeds 100 percent of the 
    RfD. Therefore, the EPA concludes that potential metolachlor residues 
    in drinking water are not likely to pose a human health concern.
        There are residential uses of metolachlor and EPA acknowledges that 
    there may be short-, intermediate-, and long-term non-occupational 
    exposure scenarios. OPP has identified a toxicity endpoint for an 
    intermediate-term residential risk assessment. However, no acceptable 
    reliable exposure data to assess these potential risks are available at 
    this time. Given the time-limited nature of this request, the need to 
    make emergency exemption decisions quickly, and the significant 
    scientific uncertainty at this time about how to aggregate non-
    occupational exposure with dietary exposure, the Agency will make its 
    safety determination for this tolerance based on those factors which it 
    can reasonably integrate into a risk assessment.
        At this time, the Agency has not made a determination that 
    metolachlor and other substances that may have a common mode of 
    toxicity would have cumulative effects. Given the time limited nature 
    of this request, the need to make emergency exemption decisions 
    quickly, and the significant scientific uncertainty at this time about 
    how to define common mode of toxicity, the Agency will make its safety 
    determination for this tolerance based on those factors which it can 
    reasonably integrate into a risk assessment. For purposes of this 
    tolerance only, the Agency is considering only the potential risks of 
    metolachlor in its aggregate exposure.
    
    C. Safety Determinations For U.S. Population
    
        Based on the completeness and reliability of the toxicity and 
    consumption data, EPA has concluded that dietary exposure to 
    metolachlor will utilize 0.6 percent of the RfD for the U.S. 
    population. As mentioned before, EPA does not expect that chronic 
    exposure from drinking water would result in an aggregate exposure 
    which would exceed 100 percent of the RfD. EPA concludes that there is 
    a reasonable certainty that no harm will result from aggregate exposure 
    to metolachlor residues.
        As discussed earlier, quantitation of cancer risk using the MOE 
    approach was recommended by the CPRC using the NOEL of 15.7 mg/kg/day 
    from the 2-year feeding study in rats. However, as noted in the 
    metolachlor RED, because the RfD is set on a NOEL of 9.7 mg/kg/day from 
    the 1 year feeding study in dogs, dietary cancer concerns are 
    adequately addressed by the chronic exposure analysis using the RfD.
    
    D. Determination of Safety for Infants and Children.
    
        In assessing the potential for additional sensitivity of infants 
    and children to residues of metolachlor, EPA considered pre- and post-
    natal toxicity data. EPA notes that the developmental toxicity NOELs of 
    300 mg/kg/day (in rats) and greater than or equal to 360 mg/kg/day (HDT 
    in rabbits) demonstrate
    
    [[Page 60621]]
    
    that there is no developmental (prenatal) toxicity present for 
    metolachlor in the absence of maternal toxicity. EPA notes that there 
    was developmental toxicity in rats at 1,000 mg/kg/day (but not in 
    rabbits). The developmental NOELs are more than 30- and 37-fold higher 
    in the rats and rabbits, respectively, than the NOEL of 9.7 mg/kg/day 
    from the 1-year feeding study in dogs, which is the basis of the RfD. 
    In the 2-generation reproductive toxicity study in the rat, the 
    reproductive/developmental toxicity NOEL of 15 mg/kg/day was less than 
    the parental (systemic) toxicity NOEL of greater than 50 mg/kg/day. The 
    reproductive/developmental NOEL was based on decreased pup body weight 
    during late lactation. The NOEL for post-natal pup effects occurred at 
    a level which is below the NOEL for maternal toxicity. This finding 
    suggests that post-natal development in pups is more sensitive and that 
    infants and children may have a greater sensitivity to metolachlor than 
    adult animals. EPA notes that the NOELs are 1.5-fold (reproductive) and 
    greater than 5-fold higher (parental) than the NOEL of 9.7 mg/kg/day 
    from the 1-year feeding study in dogs, which is the basis of the RfD. 
    The reproductive/developmental LEL of 50 mg/kg/day was based on reduced 
    pup body weight at postnatal days 14 and 21 for the first generation 
    (F1 pups) and at post natal days 4, 14, and 21 for the second 
    generation (F2 pups). Because the second generation (F2) pups are in 
    the offspring of adults that have been exposed throughout their 
    lifetime, including in utero exposure, there is the possibility that 
    body weight decreases observed in these second generation offspring are 
    an indication of increased susceptibility.
        EPA has concluded that the percent of the RfD that will be utilized 
    by chronic dietary exposure to residues of metolachlor ranges from 1.0 
    percent for children 7 to 12 years old, up to 2.1 percent for non-
    nursing infants (<1 year="" old).="" however,="" this="" calculation="" assumes="" tolerance="" level="" residues="" for="" all="" commodities="" and="" is="" therefore="" an="" over-="" estimate="" of="" dietary="" risk.="" refinement="" of="" the="" dietary="" risk="" assessment="" by="" using="" anticipated="" residue="" data="" would="" reduce="" dietary="" exposure.="" as="" mentioned="" before,="" the="" addition="" of="" potential="" exposure="" from="" metolachlor="" residues="" in="" drinking="" water="" is="" not="" expected="" to="" result="" in="" an="" exposure="" which="" would="" exceed="" the="" rfd.="" epa="" therefore="" concludes="" that="" there="" is="" a="" reasonable="" certainty="" that="" no="" harm="" will="" result="" to="" infants="" and="" children="" from="" aggregate="" exposure="" to="" metolachlor.="" as="" mentioned="" above,="" dietary="" cancer="" concerns="" for="" infants="" and="" children="" are="" adequately="" addressed="" by="" the="" chronic="" exposure="" analysis="" using="" the="" rfd.="" ffdca="" section="" 408="" provides="" that="" epa="" may="" apply="" an="" additional="" safety="" factor="" for="" infants="" and="" children="" in="" the="" case="" of="" threshold="" effects="" to="" account="" for="" pre-="" and="" post-natal="" toxicity="" and="" the="" completeness="" of="" the="" data="" base.="" should="" an="" additional="" uncertainty="" factor="" be="" deemed="" appropriate,="" when="" considered="" in="" conjunction="" with="" a="" refine="" exposure="" estimate,="" it="" is="" unlikely="" that="" the="" dietary="" risk="" will="" exceed="" 100="" percent="" of="" the="" rfd.="" therefore,="" epa="" concludes="" that="" this="" tolerance="" will="" not="" pose="" an="" unacceptable="" risk="" to="" infants="" and="" children.="" v.="" other="" considerations="" the="" metabolism="" of="" metolachlor="" in="" plants="" and="" animals="" is="" adequately="" understood="" for="" the="" purposes="" of="" this="" tolerance.="" there="" are="" no="" codex="" maximum="" residue="" levels="" established="" for="" residues="" of="" metolachlor="" on="" spinach.="" adequate="" methods="" for="" purposes="" of="" data="" collection="" and="" enforcement="" of="" tolerance="" for="" metolachlor="" residues="" are="" available.="" methods="" for="" determining="" the="" combined="" residues="" of="" metolachlor="" and="" its="" metabolites,="" as="" the="" derivatives="" cga-37913="" and="" cga-49751,="" are="" described="" in="" pam,="" vol.="" ii,="" as="" method="" i="" (plants;="" gc-npd)="" and="" method="" ii="" (animals;="" gc-ms).="" vi.="" conclusion="" therefore,="" a="" tolerance="" in="" connection="" with="" the="" fifra="" section="" 18="" emergency="" exemptions="" is="" established="" for="" residues="" of="" metolachlor="" in="" spinach="" at="" 0.3="" ppm.="" this="" tolerance="" will="" expire="" and="" be="" automatically="" revoked="" without="" further="" action="" by="" epa="" on="" november="" 15,="" 1997.="" vii.="" objections="" and="" hearing="" requests="" the="" new="" ffdca="" section="" 408(g)="" provides="" essentially="" the="" same="" process="" for="" persons="" to="" ``object''="" to="" a="" tolerance="" regulation="" issued="" by="" epa="" under="" new="" section="" 408(e)="" and="" (l)(6)="" as="" was="" provided="" in="" the="" old="" section="" 408="" and="" in="" section="" 409.="" however,="" the="" period="" for="" filing="" objections="" is="" 60="" days,="" rather="" than="" 30="" days.="" epa="" currently="" has="" procedural="" regulations="" which="" govern="" the="" submission="" of="" objections="" and="" hearing="" requests.="" these="" regulations="" will="" require="" some="" modification="" to="" reflect="" the="" new="" law.="" however,="" until="" those="" modifications="" can="" be="" made,="" epa="" will="" continue="" to="" use="" those="" procedural="" regulations="" with="" appropriate="" adjustments="" to="" reflect="" the="" new="" law.="" any="" person="" may,="" by="" january="" 28,="" 2996="" file="" written="" objections="" to="" any="" aspect="" of="" this="" regulation="" (including="" the="" automatic="" revocation="" provision)="" and="" may="" also="" request="" a="" hearing="" on="" those="" objections.="" objections="" and="" hearing="" requests="" must="" be="" filed="" with="" the="" hearing="" clerk,="" at="" the="" address="" given="" above="" (40="" cfr="" 178.20).="" a="" copy="" of="" the="" objections="" and/or="" hearing="" requests="" filed="" with="" the="" hearing="" clerk="" should="" be="" submitted="" to="" the="" opp="" docket="" for="" this="" rulemaking.="" the="" objections="" submitted="" must="" specify="" the="" provisions="" of="" the="" regulation="" deemed="" objectionable="" and="" the="" grounds="" for="" the="" objections="" (40="" cfr="" 178.25).="" each="" objection="" must="" be="" accompanied="" by="" the="" fee="" prescribed="" by="" 40="" cfr="" 180.33(i).="" if="" a="" hearing="" is="" requested,="" the="" objections="" must="" include="" a="" statement="" of="" the="" factual="" issues="" on="" which="" a="" hearing="" is="" requested,="" the="" requestor's="" contentions="" on="" such="" issues,="" and="" a="" summary="" of="" any="" evidence="" relied="" upon="" by="" the="" requestor="" (40="" cfr="" 178.27).="" a="" request="" for="" a="" hearing="" will="" be="" granted="" if="" the="" administrator="" determines="" that="" the="" material="" submitted="" shows="" the="" following:="" there="" is="" 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="" in="" the="" manner="" sought="" by="" the="" requestor="" would="" be="" adequate="" to="" justify="" the="" action="" requested="" (40="" cfr="" 178.32).="" information="" submitted="" in="" connection="" with="" an="" objection="" or="" hearing="" request="" may="" be="" claimed="" confidential="" by="" marking="" any="" part="" or="" all="" of="" that="" information="" as="" confidential="" business="" information="" (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.="" viii.="" public="" docket="" a="" record="" has="" been="" established="" for="" this="" rulemaking="" under="" docket="" number="" [opp-300443].="" a="" public="" version="" of="" this="" record,="" which="" does="" not="" include="" any="" information="" claimed="" as="" cbi,="" is="" available="" for="" inspection="" from="" 8="" a.m.="" to="" 4:30="" p.m.,="" monday="" through="" friday,="" excluding="" legal="" holidays.="" the="" public="" record="" is="" located="" in="" room="" 1132="" of="" the="" public="" response="" and="" program="" resources="" branch,="" field="" operations="" division="" (7506c),="" office="" of="" pesticide="" programs,="" environmental="" protection="" agency,="" crystal="" mall="" #2,="" 1921="" jefferson="" davis="" highway,="" arlington,="" va.="" the="" official="" record="" for="" this="" rulemaking,="" as="" well="" as="" the="" public="" version,="" as="" described="" above,="" is="" kept="" in="" paper="" form.="" accordingly,="" in="" the="" event="" there="" are="" objections="" and="" hearing="" [[page="" 60622]]="" requests,="" epa="" will="" transfer="" any="" copies="" of="" objections="" and="" hearing="" requests="" received="" electronically="" into="" printed,="" paper="" form="" as="" they="" are="" received="" and="" will="" place="" the="" paper="" copies="" in="" the="" official="" rulemaking="" record.="" the="" official="" rulemaking="" record="" is="" the="" paper="" record="" maintained="" at="" the="" address="" in="" ``addresses''="" at="" the="" beginning="" of="" this="" document.="" ix.="" regulatory="" assessment="" requirements="" under="" executive="" order="" 12866="" (58="" fr="" 51735,="" october="" 4,="" 1993),="" this="" action="" is="" not="" a="" ``significant="" regulatory="" action''="" and,="" since="" this="" action="" does="" not="" impose="" any="" information="" collection="" requirements="" as="" defined="" by="" the="" paperwork="" reduction="" act,="" 44="" u.s.c.="" 3501="" et="" seq.,="" it="" is="" not="" subject="" to="" review="" by="" the="" office="" of="" management="" and="" budget.="" in="" addition,="" this="" action="" does="" not="" impose="" any="" enforceable="" duty="" or="" contain="" any="" unfunded="" mandate="" as="" described="" in="" the="" unfunded="" mandates="" reform="" act="" of="" 1995="" (pub.="" l.="" 104-4),="" or="" require="" prior="" consultation="" with="" state="" officials="" as="" specified="" by="" executive="" order="" 12875="" (58="" fr="" 58093,="" october="" 28,="" 1993),="" or="" special="" considerations="" as="" required="" by="" executive="" order="" 12898="" (59="" fr="" 7629,="" february="" 16,="" 1994).="" under="" 5="" u.s.c.="" 801(a)(1)(a)="" of="" the="" administrative="" procedure="" act="" (apa)="" as="" amended="" by="" the="" small="" business="" regulatory="" enforcement="" fairness="" act="" of="" 1996="" (title="" ii="" of="" pub.="" l.="" 104-121,="" 110="" stat.="" 847),="" epa="" submitted="" 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="" general="" accounting="" office="" prior="" to="" publication="" of="" the="" rule="" in="" today's="" federal="" register.="" this="" rule="" is="" a="" ``major="" rule''="" as="" defined="" by="" 5="" u.s.c.="" 804(2)="" of="" the="" apa="" as="" amended.="" because="" ffdca="" section="" 408(l)(6)="" permits="" establishment="" of="" this="" regulation="" without="" a="" notice="" of="" proposed="" rulemaking,="" the="" regulatory="" flexibility="" analysis="" requirements="" of="" the="" regulatory="" flexibility="" act,="" 5="" u.s.c.="" 604(a),="" do="" not="" apply.="" list="" of="" subjects="" in="" 40="" cfr="" part="" 180="" environmental="" protection,="" administrative="" practice="" and="" procedure,="" agricultural="" commodities,="" pesticides="" and="" pests,="" reporting="" and="" recordkeeping="" requirements.="" dated:="" november="" 20,="" 1996.="" daniel="" m.="" barolo,="" 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.="" 346a="" and="" 371.="" 2.="" in="" sec.="" 180.368,="" by="" adding="" and="" reserving="" paragraph="" (d)="" and="" adding="" a="" new="" paragraph="" (e)="" to="" read="" as="" follows:="" sec.="" 180.368="" metolachlor;="" tolerances="" for="" residues="" *="" *="" *="" *="" *="" (d)="" [reserved]="" (e)="" a="" time-limited="" tolerance="" is="" established="" for="" the="" combined="" residues="" (free="" and="" bound)="" of="" the="" herbicide="" metolachlor="" [2-chloro-n-(2-="" ethyl-6-methylphenyl)-n-(2-methoxy-1-methylethyl)acetamide]="" and="" its="" metabolites,="" determined="" as="" the="" derivatives,="" 2-[(2-ethyl-6-="" methylphenyl)amino]-1-propanol="" and="" 4-(2-ethyl-6-methylphenyl)-2-="" hydroxy-5-methyl-3-morpholinone,="" each="" expressed="" as="" the="" parent="" compound="" in="" connection="" with="" use="" of="" the="" pesticide="" under="" section="" 18="" emergency="" exemptions="" granted="" by="" epa.="" the="" tolerance="" is="" specified="" in="" the="" following="" table.="" the="" tolerance="" expires="" and="" is="" automatically="" revoked="" on="" the="" date="" specified="" in="" the="" table="" without="" further="" action="" by="" epa.="" ------------------------------------------------------------------------="" parts="" per="" commodity="" million="" expiration/revocation="" date="" ------------------------------------------------------------------------="" spinach......................="" 0.3="" november="" 15,="" 1998="" ------------------------------------------------------------------------="" [fr="" doc.="" 96-30468="" filed="" 11-27-96;="" 8:45="" am]="" billing="" code="" 6560-50-f="">

Document Information

Effective Date:
11/29/1996
Published:
11/29/1996
Department:
Environmental Protection Agency
Entry Type:
Rule
Action:
Final rule.
Document Number:
96-30468
Dates:
This regulation becomes effective November 29, 1996. This regulation expires and is revoked automatically without further action by EPA on November 15, 1998. Objections and requests for hearings must be received by EPA on January 28, 1997.
Pages:
60617-60622 (6 pages)
Docket Numbers:
OPP-300443, FRL-5574-7
RINs:
2070-AB78
PDF File:
96-30468.pdf
CFR: (1)
40 CFR 180.368