[Federal Register Volume 59, Number 222 (Friday, November 18, 1994)] [Unknown Section] [Page 0] From the Federal Register Online via the Government Publishing Office [www.gpo.gov] [FR Doc No: 94-28548] [[Page Unknown]] [Federal Register: November 18, 1994] ----------------------------------------------------------------------- ENVIRONMENTAL PROTECTION AGENCY 40 CFR Part 52 [IL12-9-5167; FRL-5107-9] Approval and Promulgation of Implementation Plans; Illinois AGENCY: United States Environmental Protection Agency (USEPA). ACTION: Proposed rule. ----------------------------------------------------------------------- SUMMARY: On June 29, 1990, the USEPA promulgated Federal stationary source volatile organic compound (VOC) control measures representing reasonably available control technology (RACT) for emission sources located in six northeastern Illinois (Chicago area) counties: Cook, DuPage, Kane, Lake, McHenry and Will. The USEPA also took final rulemaking action on certain VOC RACT rules previously adopted and submitted by the State of Illinois for inclusion in its State Implementation Plan (SIP). Included in the USEPA's rules was a requirement that the Viskase Corporation's (Viskase) cellulose food casing facility in Bedford Park (Cook County) be subject to the ``generic'' rule for miscellaneous fabricated product manufacturing processes and the ``generic'' rule for miscellaneous formulation manufacturing processes. On July 19, 1990, Viskase requested that USEPA reconsider its rule as applicable to Viskase's food casing manufacturing operations and, as a result, the USEPA convened a proceeding for reconsideration. The USEPA has considered the issues raised by Viskase and is presenting in this proposed rule both a discussion of these issues and a newly proposed rulemaking applicable to Viskase's food casing manufacturing operations. The USEPA is also proposing rulemaking on a site-specific SIP revision for Viskase that has been submitted by Illinois. The USEPA solicits public comments on the USEPA's proposed rulemaking action. DATES: Comments on this proposal must be received by December 19, at the address below. A public hearing, if requested, will be held in Chicago, Illinois. Requests for a hearing should be submitted to J. Elmer Bortzer by December 19, 1994 at the address below. Interested persons may call Randolph O. Cano at (312) 886-6036 to see if a hearing will be held and the date and location of the hearing. Any hearing will be strictly limited to the subject matter of this proposal, the scope of which is discussed below. ADDRESSES: Written comments on this proposed action should be addressed to J. Elmer Bortzer, Chief, Regulation Development Section (AR-18J), U.S. Environmental Protection Agency, Region 5, 77 West Jackson Blvd., Chicago, Illinois 60604. Comments should be strictly limited to the subject matter of this proposal. DOCKET: Pursuant to section 307(d)(1)(B) and (N) of the Clean Air Act (Act), 42 U.S.C. 7607(d)(1)(B) and (N) (1991), this action is subject to the procedural requirements of section 307(d). Therefore, the USEPA has established a public docket for this action, A-93-37, which is available for public inspection and copying between 8:00 a.m. and 4:00 p.m., Monday through Friday, at the following addresses. We recommend that you contact Randolph O. Cano before visiting the Chicago location and Rachel Romine before visiting the Washington, DC location. A reasonable fee may be charged for copying. U.S. Environmental Protection Agency, Region 5, Regulation Development Branch, 18th Floor, Southwest, 77 West Jackson Blvd., Chicago, Illinois 60604. U.S. Environmental Protection Agency, Docket No. A-93-37, Air Docket (LE-131), room M1500, Waterside Mall, 401 M Street SW., Washington, DC 20460, (202) 245-3639. FOR FURTHER INFORMATION CONTACT: Steven Rosenthal, Regulation Development Branch, United States Environmental Protection Agency, Region 5, (312) 886-6052, at the Chicago address indicated above. SUPPLEMENTARY INFORMATION: I. Background In an effort to comply with certain requirements under Part D of the Act, as amended in 1977, 42 U.S.C. 7401 et seq. (1990),1 the Illinois Pollution Control Board (IPCB) adopted an organic emission ``generic'' rule on April 7, 1988. The purpose of the generic rule was to satisfy the USEPA's requirement that Illinois adopt rules for major (100 tons per year (TPY) and greater) non-CTG sources.2 This requirement is discussed in the April 4, 1979, General Preamble for Proposed Rulemaking (44 FR 20372). --------------------------------------------------------------------------- \1\The Clean Air Act was amended on November 15, 1990. Pub. L. 101-549, 104 Stat. 2399, codified at 42 U.S.C. 7401-7671q (1991). However, the USEPA's obligation to promulgate a Federal implementation plan for the Chicago nonattainment area arose under the pre-amended Act, as did Illinois' obligation to submit the SIP RACT rules that the state submitted in 1988. Therefore, while the USEPA is procedurally subject to the amended Act in this proposed rulemaking, the USEPA must refer to the pre-amended Act requirements. To clarify these references, the amended Act will be referred to as the ``Act'' and the pre-amended Act will be referred to as the ``1977 Act''. \2\Control techniques guideline (CTG) documents have been prepared by the USEPA to assist States in defining RACT for the control of VOC emissions from existing stationary sources. Each individual CTG recommends a presumptive norm of control considered reasonably available to a specific source category. Sources in categories for which no CTG exists are termed ``non-CTG sources.'' See 44 FR 53762 (September 14, 1979). --------------------------------------------------------------------------- The Illinois Environmental Protection Agency (IEPA) first proposed to the IPCB to control VOCs through a ``generic rule'' on May 12, 1986. The first hearings on this rule were held in October 1986. A revised and second revised generic rule were subsequently submitted by IEPA. Hearings on the generic rule were held February 10 and 11, 1987, and April 23 and 24, 1987. At the April 23, 1987, hearing, IEPA presented a fourth proposal (alternative generic proposal), and recommended that it be adopted rather than the original or either of its two revisions. On August 6, 1987, the IPCB adopted the IEPA's alternative generic proposal for First Notice of Adoption, which was published in the August 28, 1987, Illinois Register. On November 2, 1987, the Illinois Department of Energy and Natural Resources filed an Economic Impact Study (EcIS). Two hearings were held on the EcIS (December 14, 1987, and December 18, 1987). On February 4, 1988, the IPCB adopted the alternative rule for Second Notice, and on April 7, 1988, the IPCB adopted, as a final rule, the alternative proposal. Under the adopted generic rule, Subpart PP, ``Miscellaneous Fabricated Manufacturing Processes,'' regulates ``a manufacturing process involving * * * viscose solutions for food casings,'' and Subpart QQ, ``Miscellaneous Formulation Manufacturing Processes,'' regulates ``a manufacturing process which compounds * * * viscose solutions.'' These subparts require that sources either comply with an emission limit of 3.5 pounds volatile organic material (VOM) per gallon coating (which only applies to coating sources and therefore doesn't apply to Viskase because it isn't a coating source) or 81 percent reduction in VOM emissions from uncontrolled levels;3 or that they procure an Adjusted RACT emission limitation from the IPCB. --------------------------------------------------------------------------- \3\The State of Illinois uses the term ``VOM'' in its regulations. For the purposes of this RACT analysis, this term is considered equivalent to USEPA's term ``volatile organic compounds (VOC).'' --------------------------------------------------------------------------- On August 5, 1988, Viskase filed a Petition for Adjusted RACT Emissions Limitation with the IPCB. Under the generic rule's adjusted standards procedures, Viskase was required to show that an 81 percent reduction in uncontrolled VOM emissions is not RACT for Viskase, and that the emission levels proposed by Viskase are RACT and would not interfere with the State's plan for achieving ambient air quality standards. On January 5, 1989, the IPCB ruled that an 81 percent reduction of uncontrolled emissions would not constitute RACT for Viskase's Bedford Park facility. The IPCB determined that a 33 percent reduction in allowable VOM emissions (to a level of 994 tons per year) constitutes RACT for the Bedford Park facility and would not interfere with the State's progress toward achieving attainment of the ambient air quality standards. At that time, the IPCB adopted the following emission standards applicable to Viskase's Bedford Park plant. 1. The volatile organic material (VOM) emissions from Viskase's Bedford Park plant shall not exceed 994 tons per year. In addition, VOM emissions, computed on a monthly average basis, shall not exceed the following: 2.22 tons per day for each month during the period from June through August; and 3.30 tons per day for each month during the period from September through May. 32. Emissions of VOM, including carbon disulfide, from the Bedford Park plant shall be determined from raw material consumption and plant- specific emission factors. These factors shall be developed using the methods and procedures for testing contained in 40 CFR Part 60 (1988), including Appendix A, Methods 2, 2A, 2B, 15, 25, 25A and 25B, as appropriate. The methodology for computing a monthly average from daily emission values will be determined by the permit, issued to Viskase by the Illinois Environmental Protection Agency, which prescribes the emission standards set forth herein. 3. In accordance with the applicable methodologies, Viskase shall: (a) Maintain a monthly record of raw material consumption by each process or group of processes subject to a different emission factor; and (b) Calculate and record monthly VOM emissions, daily VOM emissions, average daily VOM emissions in tons/day, on a monthly basis. 4. (a) Records of testing shall be retained by Viskase at its Bedford Park facility for at least 5 years following the date last relied upon for calculating emissions; and (b) Raw material consumption records, VOM emission calculations, and VOM emission records shall be retained by Viskase at its Bedford Park facility for at least 2 years following the date prepared. The IEPA submitted this adjusted standard to USEPA as a proposed revision to the Illinois SIP4 on February 24, 1989. --------------------------------------------------------------------------- \4\Under Illinois' regulatory procedures, IEPA does not have the authority to adopt regulations, but must submit recommended proposals for adoption to the IPCB, an independent rulemaking body. IEPA is, however, responsible for submitting such regulations to USEPA as proposed SIP revisions. --------------------------------------------------------------------------- On April 1, 1987, the State of Wisconsin filed a complaint in the United States District Court for the Eastern District of Wisconsin against the USEPA and sought a judgment that the USEPA, among other requested actions, be required to promulgate revisions to the Illinois ozone SIP for northeastern Illinois. Wisconsin v. Reilly, No. 87-C- 0395, (E.D. Wis.). On January 18, 1989, the District Court ordered that USEPA promulgate an ozone implementation plan for northeastern Illinois within 14 months of the date of that order. On September 22, 1989, the USEPA and the States of Illinois and Wisconsin signed a settlement agreement in an attempt to substitute a more acceptable schedule for promulgation of a plan for the control of ozone in the Chicago area. On November 6, 1989, the District Court vacated its prior order and ordered all further proceedings stayed, pending the performance of the settlement agreement. The settlement agreement called for the use of a more sophisticated air quality model, allowed more time for the USEPA to promulgate a Federal implementation plan (FIP) using the model5, and requires interim emission reductions while the modeling study is being performed. The interim emission reductions consisted of Federal promulgation of required VOM RACT rules for Illinois to remedy deficiencies in its State regulations. --------------------------------------------------------------------------- \5\USEPA is no longer required to promulgate a FIP using the modeling results because the settlement agreement relieves USEPA of such responsibility in the event that amendments to the Act establish new deadlines for States to achieve attainment of the ozone standard. The primary responsibility for developing any remaining revisions to Illinois' State implementation plan belongs to Illinois because the Clean Air Act Amendments of 1990 establishes such new deadlines. --------------------------------------------------------------------------- On December 27, 1989, (54 FR 53080) USEPA proposed to disapprove the Illinois generic rules (Subparts AA, II, PP, QQ, RR of Part 215: Organic Material Emission Standards and Limitations) largely because the applicability criteria were not consistent with the USEPA RACT guidance for major non-CTG sources. On that date, the USEPA also proposed a number of RACT rules, including generic rules which covered all of Viskase's cellulose food casing manufacturing operations. On March 2, 1990, Viskase submitted comments to USEPA, raising a number of issues on the proposal. On June 29, 1990, (55 FR 26814), the USEPA took final action to disapprove the Illinois' generic rules and promulgate the proposed Federal rules, including the generic ``Miscellaneous Fabricated Manufacturing Processes'' and ``Miscellaneous Formulation Manufacturing Processes'' rules. However, the USEPA stated at that time that the need to promulgate Federal regulations, under the tight timeframe ordered by the District Court, had prevented the USEPA from being able to consider fully Viskase's comments, including the merits of the proposed, alternative site-specific limits for Viskase. Consequently, the USEPA deferred the effective date of the applicable rules with regard to Viskase for six months. 55 FR 26846. On July 19, 1990, Viskase filed a formal request that USEPA reconsider the Federal rules for Viskase, and stay the compliance date until at least one year after the USEPA has (1) fully considered the State's rules and Viskase's comments, and (2) has either promulgated a site-specific rule or formally refused to promulgate such a rule. As a result, the USEPA convened a proceeding for reconsideration pursuant to section 307(d)(7)(B) of the Act 42 U.S.C. 7607(d)(7)(B) (56 FR 463 and 56 FR 24722). And on August 22, 1990, Viskase filed a petition for review of the USEPA's June 29, 1990, rulemaking in the United States Court of Appeals for the Seventh Circuit. Nine other parties filed petitions for review, which were ultimately consolidated by the Court as Illinois Environmental Regulatory Group (``IERG'') et al. v. Reilly, No. 90-2778. On January 4, 1991 (56 FR 460), the USEPA announced a three-month partial stay pending reconsideration for Viskase and two other petitioners. Elsewhere in the January 4, 1991, Federal Register (56 FR 463), the USEPA proposed to extend the stay beyond the three-month period, only if and as necessary to complete reconsideration of the subject rules (including any appropriate regulatory action), pursuant to the USEPA's authority to revise the Federal rules by following rulemaking procedures in sections 110(c) and 301(a)(1) of the Act, 42 U.S.C. 7410(c) and 7601(a)(1). Two of the rules for which the stay was proposed were the ``Miscellaneous Fabricated Manufacturing Processes'' and ``Miscellaneous Formulation Manufacturing Processes'' rules only as applied to Viskase's cellulose food casing manufacturing operations, codified at 40 CFR 52.741(u) and (v), as well as the July 1, 1991, compliance date, codified at 40 CFR 52.741(u)(4) and (v)(4). On May 31, 1991, (56 FR 24722), the USEPA responded to public comments on the proposed extension of the partial stay, and took final action to extend the stay as long as necessary to complete reconsideration of the rules identified in the proposal. Today's notice, in effect, presents the results of the USEPA's reconsideration of the Federal generic rules as they apply to Viskase, and proposes rulemaking based on these results. II. Discussion of Viskase's Manufacturing Operations Viskase's Bedford Park facility manufactures sausage casings and related food packaging materials using the viscose process. The viscose process, which produces regenerated cellulose food casings, is also used to produce rayon and cellophane as well as cellulose food casings. Production of cellulose food casings by the viscose process begins with the reaction of a cellulose material, either cotton or wood pulp, with an aqueous sodium hydroxide solution to produce alkali cellulose. After aging, the alkali cellulose is reacted with carbon disulfide to form an intermediate compound, cellulose xanthate, which is subsequently dissolved in a dilute caustic solution to form a viscous fluid called ``viscose.'' After aging and filtering, the viscose is extruded into precision-sized tubes which are passed through a series of acid baths where the cellulose is regenerated. The extruded regenerated cellulose film is then purified, dried, and reeled and finished. Gaseous emissions from the viscose process consist primarily of carbon disulfide and hydrogen sulfide. These gases evolve during the xanthation, coagulation, regeneration and purification stages of the process. Smaller volumes of carbon disulfide are also emitted during carbon disulfide unloading and transfer operations. In 1972, the Bedford Park plant installed a wet scrubber system to remove hydrogen sulfide from the exhaust gas stream. III. Viskase RACT Analysis The IPCB's January 5, 1989, opinion on Viskase's adjusted RACT petition states that Viskase is currently permitted to emit 1,476 TPY of VOM and that its emission reduction proposal entails a reduction in allowable emissions down to 994 tons per year, or a reduction of 482 TPY. This proposed reduction in allowable emissions is to be accomplished by process changes and not add-on control. Viskase claims that it has obtained a 12.4 percent reduction in carbon disulfide emissions by switching from cotton to wood as a cellulose source. In extensive comments submitted to USEPA on March 2, 1990, Viskase contends that an 81 percent overall VOM reduction is not RACT due to a number of reasons, including: 1. The Occupational Safety and Health Administration has recently reduced the Permissible Exposure Level for carbon disulfide from 20 parts per million (PPM) to 4 PPM. Viskase anticipates increasing the plant exhaust rate from 220,000 cubic feet per minute (CFM) to 250,000 CFM. This will increase the cost of add-on control, which is primarily based on the flowrate. 2. No other viscose cellulose food casing manufacturer in the world is presently required to control carbon disulfide emissions. 3. Of the five different technologies which are generally considered to be applicable to VOC emission control, i.e., material substitution, condensation, carbon adsorption, chemical scrubbing and thermal incineration, only thermal incineration is potentially feasible to control the Bedford Park plant carbon disulfide emissions to the level required by the proposed Federal rule. An incineration control system to be utilized at the Bedford Park plant to control carbon disulfide emissions however would be enormously expensive according to Viskase, who estimates that the annual costs of control would be $7,890 per ton of carbon disulfide removed. 4. In addition to unreasonable economic costs, the cross-media environmental impact of an incinerator would also be substantial. Incineration would produce sulfur dioxide as an incineration product, in amounts more than twice the amount of carbon disulfide destroyed. Incineration of the Bedford Park plant's carbon disulfide emissions would also result in the incinerator being considered a new ``major source'' of sulfur dioxide under the Clean Air Act, and would require Viskase to install and operate sulfur dioxide control equipment. That equipment would, in turn, result in the discharge with the Bedford Park plant's wastewaters of 3.9 pounds of sodium sulfate for each pound of carbon disulfide incinerated, or more than 7,000,000 pounds per year of sodium sulfate, which would not otherwise be discharged to the waters of Illinois. In addition to sulfur dioxide, incineration would also produce approximately 17.4 pounds of carbon dioxide for each pound of carbon disulfide destroyed, or 28,000,000 new pounds of carbon dioxide, which would not otherwise be emitted. 5. The IPCB's January 5, 1989, opinion states that carbon disulfide has substantially less ozone producing capability than a typical VOM. After reviewing Viskase's comments, USEPA has determined that an 81 percent reduction of uncontrolled VOM emissions would not constitute RACT for Viskase's Bedford Park facility. The USEPA has also determined that a 33 percent reduction in Viskase's allowable emissions to 994 tons per year is RACT for Viskase. However, the control requirements established by the IPCB in its January 5, 1989, order are not approvable for the following reasons: 1. There are no short-term emission limitations. Viskase is limited to 994 TPY and 2.22 tons per day, on a monthly average, from June through August, and 3.30 tons per day, on a monthly average, for the remaining months of the year. The USEPA's January 20, 1984, policy memorandum, titled ``Averaging Times for Compliance with VOC Emission Limits--SIP Revision Policy'' clarifies USEPA's policy regarding emission time averaging for existing sources of VOC. The objective of USEPA's national VOC emissions control program is the timely attainment and maintenance of the national ambient air quality standard for ozone. Therefore, averaging times must be reasonably consistent with protecting the short-term ozone standard. Further, since SIPs and associated VOC control programs contemplate the actual application of RACT, regulatory actions that incorporate longer term averages to circumvent the installation of overall RACT level controls cannot be allowed. Therefore to protect the ozone standard and ensure RACT, this policy prohibits longer than daily averaging unless source operations are such that daily VOC emissions cannot be determined or where the application of RACT is not economically or technically feasible. In those cases in which daily emissions cannot be determined or in which daily averaging is not feasible, longer averaging times can be permitted if the conditions specified in this policy memorandum are followed. However, Viskase has neither demonstrated that daily VOC emissions cannot be determined, nor demonstrated the infeasibility of complying on a daily basis. In addition, Viskase has not satisfied the other conditions in this policy memorandum nor explained why such conditions should not be applicable. The general need for daily averaging is also stated on page 2-10 of ``Issues Relating to VOC Regulation Cutpoints, Deficiencies, and Deviations,'' a May 25, 1988, USEPA guidance document. 2. The IPCB's order states that emissions of VOM, including carbon disulfide, from the Bedford Park plant shall be determined from raw material consumption and plant-specific emission factors and these factors are to be developed using the test methods in 40 CFR Part 60, including Appendix A, Methods 2, 2A, 2B, 15, 25, 25A and 25B, as appropriate. While this is a generally reasonable approach, a specific method is required for review to ensure that the daily VOM emissions are determined in a consistent and accurate manner. 3. The recordkeeping requirements in the IPCB's order are too general to be enforceable. On February 9, 1994, representatives from Viskase met with representatives from USEPA to discuss daily emission levels and recordkeeping practices, and provided USEPA with technical information about its process operations and emissions. The USEPA has determined, based upon the previously discussed information, that RACT for Viskase consists of the following: 1. VOM emissions shall never exceed 3.30 tons per day. 2. VOM emissions shall not exceed 2.22 tons per day, on a monthly average, during June, July, and August. 3. VOM emissions shall not exceed 2.44 tons per day during June, July, and August. 4. Compliance with the emission limits in items 1-3 above, and the records in item 5 below, shall be determined using an emission factor of ``0.72 pounds of VOM emissions per pound of carbon disulfide consumed.'' 5. Viskase must keep the following daily records: (a) The pounds of carbon disulfide per charge for its fibrous process. If charges with different levels of carbon disulfide per charge are used the same day, a separate record must be kept for each level of carbon disulfide per charge. (b) The pounds of carbon disulfide per charge for its NOJAX process. If charges with different levels of carbon disulfide per charge are used the same day, a separate record must be kept for each level of carbon disulfide per charge. (c) The number of charges per day, for each level of carbon disulfide per charge, used in Viskase's Fibrous process. (d) The number of charges per day, for each level of carbon disulfide per charge, used in Viskase's NOJAX process. (e) The total quantity of carbon disulfide used per day in Viskase's Fibrous process, the total quantity of carbon disulfide used per day in Viskase's NOJAX process, and the daily VOM emissions resulting from use of the carbon disulfide. (f) The monthly use of carbon disulfide, and the monthly VOM emissions resulting from use of the carbon disulfide, during June, July, and August. 6. Any violation of the emission limits in items 1, 2, or 3 above must be reported to USEPA within 30 days of its occurrence. 7. In order to determine daily and monthly VOM emissions, the test methods in section 52.741(a)(4) may be used in addition to, and take precedence over, the emission factor cited in item 4 above. Method 15 is to be used instead of Methods 18, 25, and 25A when the test methods in section 52.741(a)(4) are used to determine VOM emissions from Viskase's cellulose food casing facility. Compliance with these requirements is required three months from the date this action becomes final. This will allow time for Viskase to develop its recordkeeping procedures. IV. SIP Revision Proposed by Illinois for Viskase On February 24, 1989, Illinois submitted a proposed revision to the Illinois SIP. This revision consists of an adjusted RACT Standard for Viskase, docketed as AS-88-1 by the IPCB. On January 5, 1989, the IPCB adopted an opinion and order for this proceeding. This IPCB Order limits VOM emissions to 994 TPY, 2.22 tons per day, on a monthly average, for June, July, and August, and 3.30 tons per day, on a monthly average, for the remaining months. The USEPA is proposing to disapprove this requested SIP revision for the following reasons: (1) monthly averaging is inconsistent with USEPA policy regarding RACT; (2) there are no specific procedures for calculating daily emissions; and (3) there are no specific recordkeeping requirements. V. Summary and Conclusions USEPA is proposing to disapprove the requested SIP revision submitted by IEPA because of the reasons provided in the above paragraph. USEPA is also proposing to promulgate RACT VOC emission limits generally consistent to what was adopted by the IPCB. However, USEPA has added daily emission limits and recordkeeping requirements which will make the RACT limits enforceable. Also, USEPA is proposing to withdraw the May 31, 1991, stay. USEPA is taking this action pursuant to its authority under section 110(k)(6) of the Act to correct through rulemaking any plan or plan revision.6 USEPA is interpreting this provision to authorize the USEPA to make corrections to a promulgated regulation when it is shown to USEPA's satisfaction that the information made available to the USEPA at the time of promulgation is subsequently demonstrated to have been clearly inadequate, and other information persuasively supports a change in the regulation. See 57 FR 6762 at 6763 (November 30, 1992). In this case, the information made available to USEPA during the rulemaking for Viskase was inadequate for the development of a site- specific RACT determination.7 --------------------------------------------------------------------------- \6\Since USEPA is taking this action pursuant to section 110(k)(6), USEPA believes that section 193 of the Act (the savings clause) is inapplicable. By its terms, section 110(k)(6) does not require any additional submission or evidence. Section 193 requires an assurance of equivalency for any revision and, in order to provide for equivalency, the State would need to provide for compensating reductions. USEPA believes that this conflict should be resolved concluding that section 110(k)(6) is not constrained by the savings clause requirement of equivalent reductions. USEPA believes that the State and the sources within the State should not have to bear the burden of additional reductions where USEPA lacked important site-specific information at the time of an initial promulgation. This is particularly true in the case of FIPs, where USEPA takes the lead in developing the regulations and is not merely acting on State-submitted regulations. \7\As discussed earlier, USEPA was required to promulgate the June 29, 1990, regulations under the tight timeframe ordered by the Court in Wisconsin v. Reilly. --------------------------------------------------------------------------- Public comment is solicited on this proposal for Viskase. Public comments received by the date shown above will be considered in the development of USEPA's final rule. Under the Regulatory Flexibility Act, 5 U.S.C. 600 et seq., the USEPA must prepare a regulatory flexibility analysis assessing the impact of any proposed or final rule on small entities. 5 U.S.C. 603 and 604. Alternatively, the USEPA may certify that the rule will not have a significant impact on a substantial number of small entities. Small entities include small businesses, small not-for-profit enterprises, and government entities with jurisdiction over populations of less than 50,000. This action involves only one source, Viskase Corporation. Viskase is not a small entity. Therefore, the USEPA certifies that this RACT promulgation does not have a significant impact on a substantial number of small entities. The Office of Management and Budget (OMB) has exempted this regulatory action from Executive Order 12866 review. List of Subjects in 40 CFR Part 52 Environmental protection, Air pollution control, Hydrocarbons, Intergovernmental relations, Ozone. Dated: November 10, 1994. Carol M. Browner, Administrator. For reasons set forth in the preamble, it is proposed that part 52, chapter I, title 40 of the Code of Federal Regulations be amended as follows: PART 52--[AMENDED] 1. The authority citation for part 52 continues to read as follows: Authority: 42 U.S.C. 7401-7671q. Subpart O--Illinois 2. Section 52.741 is amended by adding a new paragraph (u)(8) and removing and reserving paragraph (z)(1) to read as follows: Sec. 52.741 Control strategy: Ozone control measures for Cook, DuPage, Kane, Lake, McHenry, and Will Counties. * * * * * (u) * * * (8) The control, recordkeeping and reporting requirements in this paragraph apply to the cellulose food casing manufacturing operations at the Viskase Corporation plant in Bedford Park, Illinois (Cook County) instead of the requirements in paragraph (v) of this section, the other parts of paragraph (u) of this section, and the recordkeeping requirements in paragraph (y) of this section. Unless otherwise stated, the following requirements must be met by Viskase on and after three months after date of publication of the final rule in the Federal Register. (i) VOM emissions shall never exceed 3.30 tons per day. (ii) VOM emissions shall not exceed 2.22 tons per day, on a monthly average, during June, July, and August. (iii) VOM emissions shall not exceed 2.44 tons per day during June, July, and August. (iv) Compliance with the emission limits in paragraphs (u)(8)(i) through (iii) of this section, and the records in paragraph (u)(8)(v) of this section, shall be determined using an emission factor of ``0.72 pounds of VOM emissions per pound of carbon disulfide consumed.'' (v) Viskase must keep the following daily records: (A) The pounds of carbon disulfide per charge for its Fibrous process. If charges with different levels of carbon disulfide per charge are used the same day, a separate record must be kept for each level of carbon disulfide per charge. (B) The pounds of carbon disulfide per charge for its NOJAX process. If charges with different levels of carbon disulfide per charge are used the same day, a separate record must be kept for each level of carbon disulfide per charge. (C) The number of charges per day, for each level of carbon disulfide per charge, used in Viskase's Fibrous process. (D) The number of charges per day, for each level of carbon disulfide per charge, used in Viskase's NOJAX process. (E) The total quantity of carbon disulfide used per day in Viskase's Fibrous process, the total quantity of carbon disulfide used per day in Viskase's NOJAX process, and the daily VOM emissions resulting from use of the carbon disulfide. (F) The monthly use of carbon disulfide, and the monthly VOM emissions resulting from use of the carbon disulfide, during June, July, and August. (vi) Any violation of the emission limits in paragraphs (u)(8) (i) through (iii) of this section must be reported to USEPA within 30 days of its occurrence. (vii) In order to determine daily and monthly VOM emissions, the test methods in Sec. 52.741(a)(4) may be used in addition to, and take precedence over, the emission factor cited in paragraph iv above. Method 15 is to be used instead of Methods 18, 25, and 25A when the test methods in Sec. 52.741(a)(4) are used to determine VOM emissions from Viskase's cellulose food casing facility. * * * * * [FR Doc. 94-28548 Filed 11-17-94; 8:45 am] BILLING CODE 6360-50-P