1
ILLINOIS POLLUTION CONTROL BOARD
August 21, 2008
IN THE MATTER OF:
ABBOTT LABORATORIES’ PROPOSED SITE SPECIFIC AMENDMENT TO APPLICABILITY SECTION OF ORGANIC MATERIAL EMISSION STANDARDS AND LIMITATIONS FOR THE CHICAGO AREA; SUBPART T: PHARMACEUTICAL MANUFACTURING (35 ILL. ADM. CODE 218.480(b))
|
)
)
)
)
)
)
)
)
)
)
|
R08-8
(Rulemaking - Air)
|
Adopted Rule. Final Order.
OPINION AND ORDER OF THE BOARD (by N.J. Melas):
On September 4, 2007, Abbott Laboratories (Abbott) filed a proposal for site-specific rulemaking pursuant to Section 28 of the Environmental Protection Act (Act) (415 ILCS 5/28 (2006), to allow it “additional operational flexibility” with regard to emissions from certain tunnel dryers and fluid bed dryers at its pharmaceutical manufacturing facility located in Libertyville Township, Lake County. At Abbott’s request, on October 4, 2008, the Board ordered immediate publication of the rules for first notice under the Illinois Administrative Procedure Act (APA), 5 ILCS 100/1-1 et seq (2006). See, respectively, 35 Ill. Adm. Code Sections 102.202(g) and 101.512.
The proposal was published at 31 Ill. Reg. 14581 (Oct. 26, 2007). The Board held a hearing on the proposal in Libertyville, Lake County on March 7, 2008. The sole participants were Abbott and the Illinois Environmental Protection Agency (IEPA); IEPA filed a post-hearing comment in support of the requested relief.
On June 19, 2008, the Board adopted a second-notice proposal for submission to the Joint Committee on Administrative Rules (JCAR) under the APA. The proposal incorporated changes requested by Abbott and discussed at hearing. JCAR voted a certificate of no objection at its August 19, 2008 meeting. As JCAR suggested no changes, the final rule the Board adopts is identical to the rule as proposed at second notice.
By today’s action, the Board adopts a final rule, to become effective upon its filing by the Clerk with the Secretary of State. This opinion will set out the proposal’s background, summarize the proposal, and discuss the evidence presented and public comments made concerning the economic reasonableness and technical feasibility of the rule.
BACKGROUND
Abbott owns a pharmaceutical manufacturing facility located in Libertyville Township, Lake County, Illinois (the Facility). Abbott’s operations are subject to the emissions standards for volatile organic materials (VOM) at 35 Ill. Adm. Code, Subpart T – Pharmaceutical Manufacturing (Subpart T rules). As currently written, Section 218.480(b) contains certain exemptions that are only applicable to Abbott’s air suspension coater/dryer, fluid bed dryers, tunnel dryers, and Accelacotas located at the Facility.
Abbott proposed to amend these site-specific exemptions by “capping” and lowering the overall emissions allowable under the exemptions from its tunnel dryers numbered #1, #2, #3 and #4, and fluid bed dryers numbered #1, #2 and #3, and calculating the amount of exempted emissions from the dryers based on the actual combined emissions from the dryers. Abbott believes that, if adopted, the proposed amendment would reduce the overall allowable emissions from these units while increasing Abbott’s operational flexibility, by allowing it to make preferential use of the more efficient fluid bed dryers.
Abbott’s proposal to amend 35 Ill. Adm. Code 218.480(b), as modified by Abbott’s February 29, 2008 filing, is as follows (proposed amendments are shown by underlining new language and striking through deleted language:
| b)
| Notwithstanding subsection (a) of this Section, the air suspension coater/dryer, fluid bed dryers, tunnel dryers, and Accelacotas located in Libertyville Township, Lake County, Illinois shall be exempt from the rules of this Subpart, except for Sections 218.483 through 218.485, if emissions of VOM not vented to air pollution control equipment do not exceed the following levels: |
| |
| 1)
| For the air suspension coater/dryer: 2,268 kg/year (2.5 tons/year); |
| |
| 2)
| Except as set forth in subsection 218.480(b)(4) of this Section, for For each fluid bed dryer: 4,535 kg/year (5.0 tons/year); |
| |
| 3)
| Except as set forth in subsection 218.480(b)(4) of this Section, for For each tunnel dryer: 6,803 kg/year (7.5 tons/year); and |
| |
| 4)
| For fluid bed dryers #1, #2, and #3 and for tunnel dryers #1, #2, #3, and #4, the combined total annual emissions from the dryers listed in this subsection 218.480(b)(4) shall not exceed 18,688 kg/year (20.6 tons/year). [BOARD NOTE: tunnel dryers are otherwise referred to as warm air dryers]; and |
| |
45)
| For each Accelacota: 6,803 kg/year (7.5 tons/year). |
| |
Back to top
PROCEDURAL HISTORY
As previously stated, Abbott filed this proposal on September 4, 2007. As well as the text of the proposed amendment to 35 Ill. Adm. Code 218.480(b), Abbott's original filing included a Statement of Reasons (S.R.) and three exhibits (Exh.): an Aerial Photograph of Abbott Park and Vicinity, Libertyville Township, Illinois (Exh. 1), a document entitled Improving Air Quality with Economic Incentive Programs [EIP], Doc. No.EPA-452/R01-001, United States Environmental Protection Agency (USEPA), Office of Air and
Radiation, Office of Air Quality Planning and Standards (Jan. 2001) (Exh. 2), and a table entitled "Historical VOM Air Emissions from Tunnel Dryers and Fluid Bed Dryers at the Abbott Park Facility." (Exh. 3). The proposal was accompanied by motions to waive the 200-signature requirement, and a request for expedited decision.
On October 4, 2008, the Board waived the 200 signatures, accepted the proposal for hearing, and ordered publication of the rules for first notice without comment on the merits. However, the Board denied Abbott’s motion for expedited decision, citing resource and time constraints. By letter of October 18, 2008, the Board requested the Director of the Department of Commerce and Economic Opportunity (DCEO) to request an economic impact study concerning this rulemaking as required by Section 27 (b) of the Act. 415 ILCS 5/27(b) (2006). To date, DCEO has not responded to the request.
The proposal was published at 31 Ill. Reg.14581 (Oct. 26, 2007). JCAR filed its technical comment on the first notice on October 18, 2007, and its Request for Economic and Budgetary Effects on October 22, 2008.
Pursuant to a January 31, 2008 hearing officer order setting a March 7, 2008 hearing date, and asking questions to be addressed at hearing, Abbott pre-filed testimony of two of its employees: Diane Beno and Robert C. Wells. On February 29, 2008, Abbott filed a motion to modify its original proposal to better take into account data on its historical VOM emissions. The March 4, 2008 hearing officer order granted the motion to modify, but reserved ruling on a motion to revise Exhibit 3, the table of historical VOM emissions to be presented at hearing. The order additionally specified questions the Board requested the participants to address at hearing.
The Board held a hearing on the proposal in Libertyville, Lake County on March 7, 2008 to receive testimony and comment concerning the merits and the economic impact of the proposed rule (including the absence of any DCEO study).
1
The sole participants were counsel for, and employees of, Abbott and IEPA; no members of the public attended the hearing.
Abbott presented the testimony of two witnesses in support of its proposal: Diane Beno, the plant manager at the Facility’s Building
AP16, and Robert C. Wells
Air Manager for Environmental Support in Abbott's Global Environmental Health & Safety Department. The three previously identified exhibits were entered at hearing, and the hearing officer granted the requested leave to file a revised exhibit i.e., the aerial photograph of the Abbott Facility (Exh. 1), USEPA EIP document (Exh. 2), and a revised table of historical VOM emissions (Exh. 3). Three additional exhibits were entered: a chart entitled "Granulation Process—Fluid Bed Drying" and "Granulation Process—Tunnel Drying" (Exh. 4), Ms. Well’s pre-filed testimony (Exh. 5), and the questions contained in the March 4, 2008 hearing officer order (Exh. 6).
The IEPA presented one witness, solely to answer questions posed by the Board: Yoginder Mahajan, an Engineer with the Air Quality Planning Section of the IEPA Bureau of Air. During the course of hearing, Abbott and the IEPA advised that USEPA had requested Abbott to provide IEPA with additional data. The hearing officer accordingly set May 1, 2008 as the filing date for the participants’ closing comments to the Board, to facilitate preparation and consideration of USEPS data requests. On May 1, 2008, the Board received timely post hearing comments from Abbott (PC 1) and IEPA (PC 2). In its comment, IEPA stated that:
Abbott proposed a source-specific cap on emissions of volatile organic material(“VOM”) from its combined fluid bed dryers and tunnel dyers in lieu of rate-based limits provided in Section 218.480(b). The net effect of the proposal will result in a reduction of 24.5 tons per year of VOM emissions.
| The Illinois EPA has determined that the proposal will not adversely affect the air quality in Illinois. The Illinois EPA further consulted the United States Environmental Protection Agency (“USEPA”) and concluded that the proposal is consistent with the guidelines of USEPA’s Economic Incentive Program. Accordingly, after reviewing Abbott’s petition, the Illinois EPA supports the requested site-specific relief. PC 2 at 1.
|
| | | |
On June 19, 2008, the Board adopted a second-notice proposal for submission to JCAR under the APA. The proposal incorporated changes requested by Abbott and discussed at hearing. JCAR voted a certificate of no objection at its August 19, 2008 meeting.
UNCONTESTED EVIDENCE CONCERNING ABBOTT’S PROCESS AND EMISSIONS
Abbotts’ Process
In Building AP16 at the Facility, Abbott produces intermediate and final pharmaceutical product formulation using batch production processes. Active and inactive ingredients are combined with a liquid in a process called “massing to form uniform granules. Wet granules are dried in tunnel dryers or fluid bed dryers and then further processed into tablets or capsules. Beno at 2. The massing fluid, which is typically either water or ethanol, is evaporated from the solid material in the drying step. Id. If an organic solvent is volatilized from the dryer, it is emitted to the ambient air as VOM. The quantity of VOM emissions varies for different products, and is calculated from the quantity of VOM added to the mixture and loss factors defined for the dryers and specified in the Clean Air Act Permit Program (CAAPP) Permit for the Facility. Id.
Abbott's proposed site-specific amendment covers four tunnel dryers and three fluid bed dryers. Beno at 3. The technologies are not interchangeable, although individual dryers of the same type can be used in combination or interchangeably. In the use of tunnel dryers, materials to be dried are spread on trays and placed in a warming chamber or "tunnel" that circulates warm air over and under the trays. Id.
A fluid bed dryer is a large vertical cylindrical shaped vessel with a diffuser that blows warm air up from the bottom of the vessel. Beno at 3. The wet intermediate granules are loaded into the dryer and flow upward, suspended in the warm air stream. Abbott has increased its use of fluid bed dryers for recently developed products because they are more efficient and produce a more uniform product than the tunnel dryers. Abbott anticipates increased use of water for the massing fluid in future products. Abbott expects that this preferential use of fluid bed dryers and water-based products will continue. Id.
“Process trains” are designed to accommodate the manufacture of batches in large or small scales. Beno at 4. The scale of a given batch plays an important role in determining which of the dryers will be most efficient. Also, given the amount of cleaning (up to three days) required between batches of different products, Abbott prefers to continue running batches of the same product consecutively in the process train to minimize this cleaning and lost production time. Id.
Abbott explains that, for practical purposes, Section 218.480(b) defines a 12-month total
VOM limit on each individual dryer. Beno at 4. To ensure compliance with each dryer’s limit, for a particular batch Abbott may need to utilize a dryer with low VOM emissions during the last 12 months, instead of using the most efficient dryer from a production scale viewpoint. This can result in inefficient use of a large-scale process train to dry a small batch of product to maintain the equipment-specific VOM limits. Beno at 4-5.
Total annual emissions from a dryer result from the quantity of organic solvent removed from the different products processed in a dryer over a rolling 12-month period. The assignment of a “campaign” of products to dryers involves operating factors. But, the VOM emission threshold acts as an overriding factor. Beno at 5. This increases the operational cost, but results in no environmental benefit, because the actual emissions will be the same as if the campaign would have used the original equipment. Id.
Back to top
Abbott’s Emissions
Subpart T requires VOM controls for tunnel dryers and fluid bed dryers if the actual emissions exceed 7.5 tons per year (tpy) for a tunnel dryer of 5 tpy for a fluid bed dryer. Tr. at 25. If uncontrolled, the four tunnel dryers and three fluid bed dryers involved here have a potential to emit 45 tpy. The seven dryers’ actual emissions vary; in recent years, tunnel dryer emissions have varied from 0.6 tpy to 5.6 tpy, while those of fluid bed dryers have ranged from 0.1 tpy to 3.9 tpy per year of operation. Tr. at 25-26.
At hearing, in response to a Board queries, Abbott verified that the economics presented in the R96-10 rulemaking had not changed. Tr. at 31-32. Similarly, since then there have been no fundamental changes in emission control technology. Abbott’s lower emissions since 2000 have been the result of variations in demand in the pharmaceutical industry, as well as Abbott’s use of water-based solvents where available. Tr. at 33. Abbott does not expect emissions to increase over time. Tr. at 35. The only organic solvent Abbott has used during the last 10 years is ethanol. Since 2002, Abbott has been using beverage grade ethanol (which does not contain methanol as the denaturant.) While it is impractical to change ethanol-based processes to water-based processes because of United States Food and Drug Administration (FDA) concerns, Abbott does expect to see an increased use of water in new products. Tr. at 40. While fluid bed dryers are, by their mode of operation, more efficient than tunnel dryers, Abbott does not expect to be able to phase out tunnel dryers entirely, as switching the technologies can have an impact on the drug product so as to raise FDA concerns.
USEPA Economic Incentive Program
As a result of discussions between Abbott, IEPA, and USEPA, a compliance alternative was developed called a Source Specific Emissions Cap (SSEC) under USEPA’s EIP. See USEPA EIP document (Exh. 2). The general principles of the EIP are integrity, equity, and environmental benefit. Tr. at 28-30. The SSEC would allow Abbott to combine its future emissions limits for all seven dryers, and establish a limit below the historical actual emissions, rather than the previously allowable emissions or emissions allowable without control. Tr. at 27.
Based on the highest two-year emission period (1999-2000) during the preceding ten-year period, Abbott calculated baseline emissions of 22.9 tpy
2
. Reducing that by 10% to guarantee a net environmental benefit, the new emission limt would be 20.6 tpy for the seven dryers. This is less than half the current 45 tpy effective limit for the dryers. Tr. at 27-28.
At hearing, the Agency answered questions from the Board concerning USEPA’s EIP. The Agency’s Mr. Mahajan clarified that the Board could properly consider Abbott’s request even though the state has not formally adopted an EIP policy, and has no current plans to do so. Tr. at 49. He also confirmed that IEPA and USEPA consider Abbott’s proposal as satisfying EIP principles. Mr. Mahajan confirmed that the SSEC elements are those described in the USEPS guidance, and that the proposed combined VOM limit was consistent with EIP guidelines. Tr. at 49-54.
Economic and Budgetary Information
At hearing, Abbott was reminded that JCAR had requested an Economic and Budgetary Effects analysis be submitted to it with any second notice rule. Abbott presented testimony that the proposed rule applies only to its units. The proposed rule will allow for increased operational flexibility at Abbott's facility, which, in turn will result in more efficient and cost effective production of pharmaceutical products. Moreover, the proposal will not impose
any new requirements on Abbott or the Agency. Tr. at 9-10.
Back to top
BOARD CONCLUSION
Based on the undisputed facts in this record, the Board finds that adoption of Abbott’s proposed rule will result in definite, if unquantifiable, economic savings to Abbott by allowing it to use its business judgment in determining the most efficient use of its process equipment. At the same time, adoption of the alternative compliance method suggested will result in net reductions of VOM emissions from Abbott’s facility. The Board accordingly finds that the adopted rule is economically reasonable, technically feasible, and will not impose a negative economic impact on the State of Illinois within the meaning of Section 27(b) of the Act. 415 ILCS 5/27(b) (2006).
ORDER
The Board directs the Clerk to file the following adopted rules with the Secretary of State, to become effective upon filing (amendments adopted in this rulemaking continue to be indicated in the order, but will not be so indicated in final filed rule text):
TITLE 35: ENVIRONMENTAL PROTECTION
SUBTITLE B: AIR POLLUTION
CHAPTER I: POLLUTION CONTROL BOARD
SUBCHAPTER c: EMISSIONS STANDARDS AND
LIMITATIONS FOR STATIONARY SOURCES
PART 218
ORGANIC MATERIAL EMISSION STANDARDS AND
LIMITATIONS FOR THE CHICAGO AREA
SUBPART A: GENERAL PROVISIONS
Section
| 218.100
| Introduction |
| 218.101
| Savings Clause |
| 218.102
| Abbreviations and Conversion Factors |
| 218.103
| Applicability |
| 218.104
| Definitions |
| 218.105
| Test Methods and Procedures |
| 218.106
| Compliance Dates |
| 218.107
| Operation of Afterburners |
| 218.108
| Exemptions, Variations, and Alternative Means of Control or Compliance Determinations |
| 218.109
| Vapor Pressure of Volatile Organic Liquids |
| 218.110
| Vapor Pressure of Organic Material or Solvent |
| 218.111
| Vapor Pressure of Volatile Organic Material |
| 218.112
| Incorporations by Reference |
| 218.113
| Monitoring for Negligibly-Reactive Compounds |
| 218.114
| Compliance with Permit Conditions |
| |
SUBPART B: ORGANIC EMISSIONS FROM STORAGE AND LOADING OPERATIONS
Section
| 218.119
| Applicability for VOL |
| 218.120
| Control Requirements for Storage Containers of VOL |
| 218.121
| Storage Containers of VPL |
| 218.122
| Loading Operations |
| 218.123
| Petroleum Liquid Storage Tanks |
| 218.124
| External Floating Roofs |
| 218.125
| Compliance Dates |
| 218.126
| Compliance Plan (Repealed) |
| 218.127
| Testing VOL Operations |
| 218.128
| Monitoring VOL Operations |
| 218.129
| Recordkeeping and Reporting for VOL Operations |
| |
SUBPART C: ORGANIC EMISSIONS FROM MISCELLANEOUS EQUIPMENT
Section
| 218.141
| Separation Operations |
| 218.142
| Pumps and Compressors |
| 218.143
| Vapor Blowdown |
| 218.144
| Safety Relief Valves |
| |
SUBPART E: SOLVENT CLEANING
Section
| 218.181
| Solvent Cleaning in General |
| 218.182
| Cold Cleaning |
| 218.183
| Open Top Vapor Degreasing |
| 218.184
| Conveyorized Degreasing |
| 218.185
| Compliance Schedule (Repealed) |
| 218.186
| Test Methods |
| |
SUBPART F: COATING OPERATIONS
Section
| 218.204
| Emission Limitations |
| 218.205
| Daily-Weighted Average Limitations |
| 218.206
| Solids Basis Calculation |
| 218.207
| Alternative Emission Limitations |
| 218.208
| Exemptions from Emission Limitations |
| 218.209
| Exemption from General Rule on Use of Organic Material |
| 218.210
| Compliance Schedule |
| 218.211
| Recordkeeping and Reporting |
| 218.212
| Cross-Line Averaging to Establish Compliance for Coating Lines |
| 218.213
| Recordkeeping and Reporting for Cross-Line Averaging Participating Coating Lines |
| 218.214
| Changing Compliance Methods |
218.215 Wood Furniture Coating Averaging Approach
218.216 Wood Furniture Coating Add-On Control Use
218.217 Wood Furniture Coating Work Practice Standards
SUBPART G: USE OF ORGANIC MATERIAL
Section
| 218.301
| Use of Organic Material |
| 218.302
| Alternative Standard |
| 218.303
| Fuel Combustion Emission Units |
| 218.304
| Operations with Compliance Program |
| |
SUBPART H: PRINTING AND PUBLISHING
Section
| 218.401
| Flexographic and Rotogravure Printing |
| 218.402
| Applicability |
| 218.403
| Compliance Schedule |
| 218.404
| Recordkeeping and Reporting |
| 218.405
| Lithographic Printing: Applicability |
| 218.406
| Provisions Applying to Heatset Web Offset Lithographic Printing Prior to March 15, 1996 |
| 218.407
| Emission Limitations and Control Requirements for Lithographic Printing Lines On and After March 15, 1996 |
| 218.408
| Compliance Schedule for Lithographic Printing On and After March 15, 1996 |
| 218.409
| Testing for Lithographic Printing On and After March 15, 1996 |
| 218.410
| Monitoring Requirements for Lithographic Printing |
| 218.411
| Recordkeeping and Reporting for Lithographic Printing |
| |
SUBPART Q: SYNTHETIC ORGANIC CHEMICAL AND POLYMER MANUFACTURING PLANT
Section
| 218.421
| General Requirements |
| 218.422
| Inspection Program Plan for Leaks |
| 218.423
| Inspection Program for Leaks |
| 218.424
| Repairing Leaks |
| 218.425
| Recordkeeping for Leaks |
| 218.426
| Report for Leaks |
| 218.427
| Alternative Program for Leaks |
| 218.428
| Open-Ended Valves |
| 218.429
| Standards for Control Devices |
| 218.430
| Compliance Date (Repealed) |
| 218.431
| Applicability |
| 218.432
| Control Requirements |
| 218.433
| Performance and Testing Requirements |
| 218.434
| Monitoring Requirements |
| 218.435
| Recordkeeping and Reporting Requirements |
| 218.436
| Compliance Date |
| |
SUBPART R: PETROLEUM REFINING AND RELATED INDUSTRIES; ASPHALT MATERIALS
Section
| 218.441
| Petroleum Refinery Waste Gas Disposal |
| 218.442
| Vacuum Producing Systems |
| 218.443
| Wastewater (Oil/Water) Separator |
| 218.444
| Process Unit Turnarounds |
| 218.445
| Leaks: General Requirements |
| 218.446
| Monitoring Program Plan for Leaks |
| 218.447
| Monitoring Program for Leaks |
| 218.448
| Recordkeeping for Leaks |
| 218.449
| Reporting for Leaks |
| 218.450
| Alternative Program for Leaks |
| 218.451
| Sealing Device Requirements |
| 218.452
| Compliance Schedule for Leaks |
| 218.453
| Compliance Dates (Repealed) |
| |
SUBPART S: RUBBER AND MISCELLANEOUS PLASTIC PRODUCTS
Section
| 218.461
| Manufacture of Pneumatic Rubber Tires |
| 218.462
| Green Tire Spraying Operations |
| 218.463
| Alternative Emission Reduction Systems |
| 218.464
| Emission Testing |
| 218.465
| Compliance Dates (Repealed) |
| 218.466
| Compliance Plan (Repealed) |
| |
SUBPART T: PHARMACEUTICAL MANUFACTURING
Section
| 218.480
| Applicability |
| 218.481
| Control of Reactors, Distillation Units, Crystallizers, Centrifuges and Vacuum Dryers |
| 218.482
| Control of Air Dryers, Production Equipment Exhaust Systems and Filters |
| 218.483
| Material Storage and Transfer |
| 218.484
| In-Process Tanks |
| 218.485
| Leaks |
| 218.486
| Other Emission Units |
| 218.487
| Testing |
| 218.488
| Monitoring for Air Pollution Control Equipment |
| 218.489
| Recordkeeping for Air Pollution Control Equipment |
| |
SUBPART V: BATCH OPERATIONS AND AIR OXIDATION PROCESSES
Section
| 218.500
| Applicability for Batch Operations |
| 218.501
| Control Requirements for Batch Operations |
| 218.502
| Determination of Uncontrolled Total Annual Mass Emissions and Average Flow Rate Values for Batch Operations |
| 218.503
| Performance and Testing Requirements for Batch Operations |
| 218.504
| Monitoring Requirements for Batch Operations |
| 218.505
| Reporting and Recordkeeping for Batch Operations |
| 218.506
| Compliance Date |
| 218.520
| Emission Limitations for Air Oxidation Processes |
| 218.521
| Definitions (Repealed) |
| 218.522
| Savings Clause |
| 218.523
| Compliance |
| 218.524
| Determination of Applicability |
| 218.525
| Emission Limitations for Air Oxidation Processes |
| 218.526
| Testing and Monitoring |
| 218.527
| Compliance Date (Repealed) |
| |
SUBPART W: AGRICULTURE
Section
| 218.541
| Pesticide Exception |
| |
SUBPART X: CONSTRUCTION
Section
| 218.561
| Architectural Coatings |
| 218.562
| Paving Operations |
| 218.563
| Cutback Asphalt |
| |
SUBPART Y: GASOLINE DISTRIBUTION
Section
| 218.581
| Bulk Gasoline Plants |
| 218.582
| Bulk Gasoline Terminals |
| 218.583
| Gasoline Dispensing Operations - Storage Tank Filling Operations |
| 218.584
| Gasoline Delivery Vessels |
| 218.585
| Gasoline Volatility Standards |
| 218.586
| Gasoline Dispensing Operations - Motor Vehicle Fueling Operations |
| |
SUBPART Z: DRY CLEANERS
Section
| 218.601
| Perchloroethylene Dry Cleaners (Repealed) |
| 218.602
| Applicability (Repealed) |
| 218.603
| Leaks (Repealed) |
| 218.604
| Compliance Dates (Repealed) |
| 218.605
| Compliance Plan (Repealed) |
| 218.606
| Exception to Compliance Plan (Repealed) |
| 218.607
| Standards for Petroleum Solvent Dry Cleaners |
| 218.608
| Operating Practices for Petroleum Solvent Dry Cleaners |
| 218.609
| Program for Inspection and Repair of Leaks |
| 218.610
| Testing and Monitoring |
| 218.611
| Applicability for Petroleum Solvent Dry Cleaners |
| 218.612
| Compliance Dates (Repealed) |
| 218.613
| Compliance Plan (Repealed) |
| |
SUBPART AA: PAINT AND INK MANUFACTURING
Section
| 218.620
| Applicability |
| 218.621
| Exemption for Waterbase Material and Heatset Offset Ink |
| 218.623
| Permit Conditions (Repealed) |
| 218.624
| Open Top Mills, Tanks, Vats or Vessels |
| 218.625
| Grinding Mills |
| 218.626
| Storage Tanks |
| 218.628
| Leaks |
| 218.630
| Clean Up |
| 218.636
| Compliance Schedule |
| 218.637
| Recordkeeping and Reporting |
| |
SUBPART BB: POLYSTYRENE PLANTS
Section
| 218.640
| Applicability |
| 218.642
| Emissions Limitation at Polystyrene Plants |
| 218.644
| Emissions Testing |
| |
SUBPART CC: POLYESTER RESIN PRODUCT MANUFACTURING PROCESS
Section
| 218.660
| Applicability |
| 218.666
| Control Requirements |
| 218.667
| Compliance Schedule |
| 218.668
| Testing |
| 218.670
| Recordkeeping and Reporting for Exempt Emission Units |
| 218.672
| Recordkeeping and Reporting for Subject Emission Units |
| |
SUBPART DD: AEROSOL CAN FILLING
Section
| 218.680
| Applicability |
| 218.686
| Control Requirements |
| 218.688
| Testing |
| 218.690
| Recordkeeping and Reporting for Exempt Emission Units |
| 218.692
| Recordkeeping and Reporting for Subject Emission Units |
| |
SUBPART FF: BAKERY OVENS (REPEALED)
Section
| 218.720
| Applicability (Repealed) |
| 218.722
| Control Requirements (Repealed) |
| 218.726
| Testing (Repealed) |
| 218.727
| Monitoring (Repealed) |
| 218.728
| Recordkeeping and Reporting (Repealed) |
| 218.729
| Compliance Date (Repealed) |
| 218.730
| Certification (Repealed) |
| |
SUBPART GG: MARINE TERMINALS
Section
| 218.760
| Applicability |
| 218.762
| Control Requirements |
| 218.764
| Compliance Certification |
| 218.766
| Leaks |
| 218.768
| Testing and Monitoring |
| 218.770
| Recordkeeping and Reporting |
| |
SUBPART HH: MOTOR VEHICLE REFINISHING
Section
| 218.780
| Emission Limitations |
| 218.782
| Alternative Control Requirements |
| 218.784
| Equipment Specifications |
| 218.786
| Surface Preparation Materials |
| 218.787
| Work Practices |
| 218.788
| Testing |
| 218.789
| Monitoring and Recordkeeping for Control Devices |
| 218.790
| General Recordkeeping and Reporting (Repealed) |
| 218.791
| Compliance Date |
| 218.792
| Registration |
| 218.875
| Applicability of Subpart BB (Renumbered) |
| 218.877
| Emissions Limitation at Polystyrene Plants (Renumbered) |
| 218.879
| Compliance Date (Repealed) |
| 218.881
| Compliance Plan (Repealed) |
| 218.883
| Special Requirements for Compliance Plan (Repealed) |
| 218.886
| Emissions Testing (Renumbered) |
| |
SUBPART PP: MISCELLANEOUS FABRICATED PRODUCT MANUFACTURING PROCESSES
Section
| 218.920
| Applicability |
| 218.923
| Permit Conditions (Repealed) |
| 218.926
| Control Requirements |
| 218.927
| Compliance Schedule |
| 218.928
| Testing |
218.929 Cementable and Dress or Performance Shoe Leather
SUBPART QQ: MISCELLANEOUS FORMULATION MANUFACTURING PROCESSES
Section
| 218.940
| Applicability |
| 218.943
| Permit Conditions (Repealed) |
| 218.946
| Control Requirements |
| 218.947
| Compliance Schedule |
| 218.948
| Testing |
| |
SUBPART RR: MISCELLANEOUS ORGANIC CHEMICAL MANUFACTURING PROCESSES
Section
| 218.960
| Applicability |
| 218.963
| Permit Conditions (Repealed) |
| 218.966
| Control Requirements |
| 218.967
| Compliance Schedule |
| 218.968
| Testing |
| |
SUBPART TT: OTHER EMISSION UNITS
Section
| 218.980
| Applicability |
| 218.983
| Permit Conditions (Repealed) |
| 218.986
| Control Requirements |
| 218.987
| Compliance Schedule |
| 218.988
| Testing |
| |
SUBPART UU: RECORDKEEPING AND REPORTING
Section
| 218.990
| Exempt Emission Units |
| 218.991
| Subject Emission Units |
| |
| 218.APPENDIX A:
| List of Chemicals Defining Synthetic Organic Chemical and Polymer Manufacturing |
| 218.APPENDIX B:
| VOM Measurement Techniques for Capture Efficiency (Repealed) |
| 218.APPENDIX C:
|
| Reference Methods and Procedures |
| 218.APPENDIX D:
| Coefficients for the Total Resource Effectiveness Index (TRE) Equation |
| 218.APPENDIX E:
|
| List of Affected Marine Terminals |
| 218.APPENDIX G:
| TRE Index Measurements for SOCMI Reactors and Distillation Units |
| 218.APPENDIX H:
| Baseline VOM Content Limitations for Subpart F, Section 218.212 Cross-Line Averaging |
| |
AUTHORITY: Implementing Section 10 and authorized by Sections 27, 28, 28.5 of the Environmental Protection Act [415 ILCS 5/10 and 28.5].
SOURCE: Adopted at R91-7 at 15 Ill. Reg. 12231, effective August 16, 1991; amended in R91-24 at 16 Ill. Reg. 13564, effective August 24, 1992; amended in R91-28 and R91-30 at 16 Ill. Reg. 13864, effective August 24, 1992; amended in R93-9 at 17 Ill. Reg. 16636, effective September 27, 1993; amended in R93-14 at 18 Ill. Reg. at 1945, effective January 24, 1994; amended in R94-12 at 18 Ill. Reg. 14973, effective September 21, 1994; amended in R94-15 at 18 Ill. Reg. 16392, effective October 25, 1994; amended in R94-16 at 18 Ill. Reg. 16950, effective November 15, 1994; amended in R94-21, R94-31 and R94-32 at 19 Ill. Reg. 6848, effective May 9, 1995; amended in R94-33 at 19 Ill. Reg. 7359, effective May 22, 1995; amended in R96-13 at 20 Ill. Reg. 14428, effective October 17, 1996; amended in R97-24 at 21 Ill. Reg. 7708, effective June 9, 1997; amended in R97-31 at 22 Ill. Reg. 3556, effective February 2, 1998; amended in R98-16 at 22 Ill. Reg. 14282, effective July 16, 1998; amended in R02-20 at 27 Ill. Reg. 7283, effective April 8, 2003; amended in R04-12/20 at 30 Ill. Reg. 9684, effective May 15, 2006; amended in R06-21 at 31 Ill. Reg. 7086, effective April 30, 2007; amended in R08-8 at 32 Ill. Reg. ___________, effective _______________.
SUBPART T: PHARMACEUTICAL MANUFACTURING
Section 218.480 Applicability
| a)
| The rules of this Subpart, except for Sections 218.483 through 218.485 of this Part, apply to all emission units of VOM, including but not limited to reactors, distillation units, dryers, storage tanks for VOL, equipment for the transfer of VOL, filters, crystallizers, washers, laboratory hoods, pharmaceutical coating operations, mixing operations and centrifuges used in manufacturing, including packaging, of pharmaceuticals, and emitting more than 6.8 kg/day (15 lbs/day) and more than 2,268 kg/year (2.5 tons/year) of VOM. If such an emission unit emits less than 2,268 kg/year (2.5 tons/year) of VOM, the requirements of this Subpart still apply to the emission unit if VOM emissions from the emission unit exceed 45.4 kg/day (100 lbs/day). |
| |
| b)
| Notwithstanding subsection (a) of this Section, the air suspension coater/dryer, fluid bed dryers, tunnel dryers, and Accelacotas located in Libertyville Township, Lake County, Illinois shall be exempt from the rules of this Subpart, except for Sections 218.483 through 218.485, if emissions of VOM not vented to air pollution control equipment do not exceed the following levels: |
| |
| 1)
| For the air suspension coater/dryer: 2,268 kg/year (2.5 tons/year); |
| |
| 2)
| Except as set forth in subsection 218.480(b)(4) of this Section, for For each fluid bed dryer: 4,535 kg/year (5.0 tons/year); |
| |
| 3)
| Except as set forth in subsection 218.480(b)(4) of this Section, for For each tunnel dryer: 6,803 kg/year (7.5 tons/year); and |
| |
| 4)
| For fluid bed dryers #1, #2, and #3 and for tunnel dryers #1, #2, #3, and #4, the combined total annual emissions from the dryers listed in this subsection 218.480(b)(4) shall not exceed 18,688 kg/year (20.6 tons/year). [BOARD NOTE: tunnel dryers are otherwise referred to as warm air dryers]; and |
| |
45)
| For each Accelacota: 6,803 kg/year (7.5 tons/year). |
| |
| c)
| Sections 218.483 through 218.485 of this Part apply to a source having one or more emission units that: |
| |
| 1)
| Are used to manufacture pharmaceuticals, and |
| |
| 2)
| Emit more than 6.8 kg/day (15 lbs/day) of VOM and more than 2,268 kg/year (2.5 tons/year) of VOM, or, if less than 2,268 kg/year (2.5 tons/year), these Sections still apply if emissions from one or more sources exceed 45.4 kg/day (100 lbs/day). |
| |
| d)
| No owner or operator shall violate any condition in a permit when the condition results in exclusion of an emission unit from this Subpart. |
| |
| e)
| Any pharmaceutical manufacturing source that becomes subject to the provisions of this Subpart at any time shall remain subject to the provisions of this Subpart at all times. |
| |
| f)
| Emissions subject to this Subpart shall be controlled at all times consistent with the requirements set forth in this Subpart. |
| |
| g)
| Any control device required pursuant to this Subpart shall be operated at all times when the source it is controlling is operated. |
| |
| h)
| Determinations of daily and annual emissions for purposes of this Section shall be made using both data on the hourly emission rate (or the emissions per unit of throughput) and appropriate daily and annual data from records of emission unit operation (or material throughput or material consumption data). In the absence of representative test data pursuant to Section 218.487 of this Part for the hourly emission rate (or the emissions per unit of throughput) such items shall be calculated using engineering calculations, including the methods described in Appendix B of "Control of Volatile Organic Emissions from Manufacturing of Synthesized Pharmaceutical Products" (EPA-450/2-78-029), incorporated by reference in Section 218.112 of this Part. (This subsection shall not affect the Agency's or the USEPA's authority to require emission tests to be performed pursuant to Section 218.487 of this Part.) |
| |
| i)
| Equipment and operations emitting VOM at a source subject to subsection (a) or (c) of this Section and used to produce pharmaceutical products or a pharmaceutical-like product such as a hormone, enzyme, or antibiotic, shall be deemed to be engaged in the manufacture of pharmaceuticals for the purposes of this Subpart. |
| |
(Source: Amended at 32 Ill. Reg. __________, effective ___________)
IT IS SO ORDERED.
Board Member Andrea S. Moore abstained.
Section 41(a) of the Environmental Protection Act provides that final Board orders may be appealed directly to the Illinois Appellate Court within 35 days after the Board serves the order. 415 ILCS 5/41(a) (2006); see also 35 Ill. Adm. Code 101.300(d)(2), 101.906, 102.706. Illinois Supreme Court Rule 335 establishes filing requirements that apply when the Illinois Appellate Court, by statute, directly reviews administrative orders. 172 Ill. 2d R. 335. The Board’s procedural rules provide that motions for the Board to reconsider or modify its final orders may be filed with the Board within 35 days after the order is received. 35 Ill. Adm. Code 101.520; see also 35 Ill. Adm. Code 101.902, 102.700, 102.702.
I, John T. Therriault, Assistant Clerk of the Illinois Pollution Control Board, certify that the Board adopted the above opinion and order on August 21, 2008, by a vote of. 3-0.
___________________________________
John T. Therriault, Assistant Clerk
Illinois Pollution Control Board
Back to top