APPENDIX J

REASONABLY AVAILABLE CONTROL TECHNOLOGY ANALYSISJ-2 REASONABLY AVAILABLE CONTROL TECHNOLOGY (RACT) ANALYSIS

Introduction Under the one-hour ozone National Ambient Air Quality Standard (NAAQS), the four-county DFW area, consisting of Collin, Dallas, Denton, and Tarrant Counties, was classified as a serious nonattainment area. The eight-hour ozone NAAQS classifies the nine-county DFW area, consisting of Collin, Dallas, Denton, Ellis, J ohnson, Kaufman, Parker, Rockwall, and Tarrant Counties, as a moderate nonattainment area. U nder the eight-hour ozone standard, the ninecounty DFW area is required to meet the RACT mandates of the Federal Clean Air Act (FCAA) under §172(c)(1), §182(b)(2) and §182(f). A ccording to the United States Environmental Protection Agency’s (EPA’s) Final Rule to Im plement the Eight-Hour Ozone NAAQS – Phase 2 (40 Code of Federal Regulations (CFR) §51. 912, November 29, 2005), areas classified as moderate nonattainment or higher must demonstrate, by revision to their SIP, that their current rules fulfill eight-hour RACT for all Control T echnique Guidelines (CTG) categories and all nonCTG major sources of NO Xand VOC emissions.

RACT is defined as the lowest emissions limitation that a particular source is capable of meeting by the application of control technology that is reasonably available considering technological and economic feasibility (44 Federal Register (FR) 53762; September 17, 1979). RACT requirements for moderate nonattainment areas are included in the FCAA to assure that significant source categories at major sources of ozone precursor emissions are controlled to a reasonable extent, but not necessarily to best available control technology (BACT) levels expected of new sources or maximum achievable control technology (MACT) required for major sources of hazardous air pollutants.

RACT Demonstration The TCEQ demonstrates that the RACT require ments are being fulfilled in the DFW eight-hour ozone nonattainment area by (1) identifying all CTG source categories of VOC and NO X emissions and submitting negative declarations fo r categories where there are no major emission sources within the DFW area; (2) identifyi ng all non-CTG major sources of VOC and NO X emissions; (3) identifying the state regulati on that implements or exceeds RACT for each applicable CTG source category or non-CTG majo r emission source; and (4) describing the basis for concluding that these regulations fulfill RACT.

Identification of CTG and Non-CTG Emission Sources The EPA has issued CTG documents defining RACT for existing facilities that emit large amounts of air pollutants and Alternative Control Technology (ACT) documents that describe available control technologies but do not define presumptive RACT levels. The TCEQ reviewed EPA CTG and ACT documents to identify all source categories of NO X and VOC emissions that require RACT. RACT determinations are not re quired if there are no facilities in the DFW eighthour ozone nonattainment area that are subject to a CTG or ACT document. A negative declaration is provided for source categories descr ibed within the EPA guidance documents that do not exist in the DFW area.

To identify all non-CTG major source categories, the TCEQ reviewed its emission inventory database for all major sources of NO X or VOC emissions not covered by a CTG. Under the EPA’s eight-hour ozone regulations for moderate ozone nonattainment areas, the threshold for major stationary sources is 100 tons per year (tpy) of either VOC or NO Xemissions. Since the emission inventory database reports actual emissions rather than potential to emit, the TCEQlooked at sources that reported as few as 50 tpy or more of actual emissions to identify all nonCTG major source categories of NO X and VOC emissions.

Determining if State Regulations Fulfill RACT Requirements The TCEQ examined the rules in Title 30 of th e Texas Administrative Code (TAC) Chapters 115 and 117 to verify that the current state rules satisfy the corresponding RACT requirements for allJ-3 applicable CTG source categories and non-CTG major emission sources. To determine if the control technologies associated with the exis ting state emission specifications fulfill RACT requirements for the relevant unit types, the TCEQ compared the existing state regulations to the controls contained in the CTG and ACT guidance documents. State regulations that implement the controls suggested in CTG and ACT documen ts or that implement equivalent emission control strategies were determined to fulfill RACT requirements.

The TCEQ also reviewed new technologies thatare now considered RACT by the EPA and current control technologies and methodologies implemented as RACT in other moderate nonattainment areas. Current technologies and methodologies were examined to identify nonCTG emission source categories that are regulat ed by other moderate nonattainment areas, to ensure there are no new economically or tec hnologically feasible controls that could be implemented in the DFW area, and to verify that the state rules fulfill RACT requirements. The TCEQ also evaluated control technologies suggest ed during the public comment period for recent rule projects. State rules that were consistent with or more stringent than the current control technologies and methodologies implemented in other moderate nonattainment areas were also determined to fulfill RACT requirements.

The EPA must evaluate SIP-related rules prior to approval to determine if those rules fulfill all applicable EPA guidelines and policies and th erefore, any EPA SIP-approved rules were determined to meet RACT requirements at the time of federal approval. Federally approved state rules, especially those rules that were approved ma ny years ago, were evaluated to determine if the existing rules still fulfill RACT requirements. Federally approved state rules and rule approval dates can be found in 40 CFR §52.2270(c) EPA Approved Regulations in the Texas SIP

. BACT is an emission limitation based on the maximum degree of emission reduction (considering energy, environmental, and economic impacts) achievable through application of production processes and available methods, systems, and techniques. BACT does not permit emissions in excess of those allowed under any applicable FCAA provisions. MACT is the emission standard for sources of air pollution requiring the maximum reduction of hazardous emissions, taking cost and feasibility into account . Under the FCAA Amendments of 1990, the MACT must not be less than the average emis sion level achieved by controls on the best performing 12 percent of existing sources, by category of industrial and utility sources. Therefore, emission sources subject to the more stringent BACT or MACT requirements were determined to also fulfill RACT requirements.

Conclusion Table J-1: State Rules Addressing RACT Requirements in CTG and ACT Reference Documents provides the emission source categories, the CTG and ACT reference documents, and the state rules addressing the RACT requirements for sources in the CTG and ACT documents. Table J-1 also includes non-CTG NO Xemission source categories, identified during the current technology and methodology evaluation, for which other nonattainment areas have adopted RACT regulations. A negative declaration is provided in the table for emission source categories that are described within the EPA guidance documents wh ich, based on information available to the TCEQ, either do not exist in the DFW eight-hou r area or exist but are not considered major sources and are therefore not required to demonstrate RACT compliance. All CTG source categories and non-CTG major emission sources in the DFW eight-hour ozone nonattainment area are controlled by source specific state rules th at fulfill RACT requirements or are controlled by standards that meet or exceed what would otherwise be considered RACT.

Table J-2: State Rules Addressing RACT Requirements for Major Emission Sources in the DFW Eight-Hour Ozone Nonattainment Area lists the major stationary emission sources in the DFW area with actual emissions, as reported in the TCEQ emissions inventory, equal to or greater than 50 tpy. Table J-2 provides the emission s ource account number, company name, standard industrial classification (SIC) code, a brief descr iption of the source, and the reported annualJ-4 emissions (in tpy). Table J-2 also includes either the state rules satisfying the RACT requirements, the permit requirements that limit emissions, or the reasoned justification for why controlling the emissions is not c onsidered RACT. Most major st ationary emission sources in the DFW eight-hour ozone nonattainment area are controlled by source specific state rules that fulfill RACT requirements or are controlled by standards th at meet or exceed what would otherwise be considered RACT. In some instances howeve r the TCEQ has determined that controlling emissions from some sources is not economically f easible and thus is not considered RACT for the state.

Basis for Concluding State Regulations Fulfill RACT Requirements The EPA proposed to approve RACT for all majo r sources of VOC emissions in the four-county DFW one-hour ozone nonattainment area on Nove mber 18, 2001, and received no comments (66 FR 4756). On August 22, 2006, the EPA proposed to approve the DFW 5 percent Increment of Progress (IOP) SIP and stated their intention to finalize approval of the DFW 5 percent IOP SIP and the one-hour RACT in the same rulemaking (71 FR 48870). The DFW 5 percent IOP SIP extended the applicability of certain RACT require ments to include all nine counties in the DFW eight-hour ozone nonattainment area . On November 15, 2006, the TCEQ adopted rules extending the applicability of the remaining control, mon itoring, testing, recordkeeping, and reporting requirements in 30 TAC Chapter 115 to include all nine counties in the DFW eight-hour ozone nonattainment area. With the adoption of these ru les the new five counties are subject to the same rules that EPA has proposed to approve as RA CT for the original four-county DFW area.

The only comment the TCEQ received regarding additional controls was a suggestion that thermal oxidizers be used to control VOC emissi ons from cement kilns. As discussed in the preamble to the adopted rule (rule project num ber 2006-011-115-EN) the use of thermal oxidizers does not represent RACT for control of VOC emissions from cement kilns because it is not economically reasonable. In addition, since mode ling discussed in Chapter 2 of this SIP revision indicates the reduction of VOC emissions has less benefit in reducing ozone levels than reduction in NO Xemissions, the level of control required by the rules in 30 TAC Chapter 115 represents RACT for the nine-county DFW area.

The emission specifications for attainment demonstration in 30 TAC §117.400 – §117.456 regulate all major sources of NO Xemissions in the DFW eight-hour ozone nonattainment area. Due to the significant NO X emissions reductions necessary to demonstrate ozone attainment in DFW, these emissions specifications are equal to or more stringent than the emission limits associated with the controls contained in th e CTG and ACT guidance documents and current control technologies and methodologies implemen ted as RACT in other moderate nonattainment areas. Additional discussion on the basis for determining these NO Xemission specifications for attainment demonstration can be found in th e preamble to the Chapter 117 rulemaking (rule project number 2006-034-117-EN).

The TCEQ received comments suggesting emission c ontrol strategies for cement kilns in Ellis County. Based on review of the 2006 cement kiln study and all other available information, the TCEQ has determined that all technologically or economically feasible controls are being implemented in the DFW eight-hour ozone nonattainment area. The 2006 cement kiln study can be found in Appendix I: Assessment of NOX Reduction Strategies for Cement Kiln - Ellis County, Final Report (July 14, 2006) . Additional discussion on the basis for this conclusion can be found in the response to comments sections of both the preamble to the Chapter 117 rules and the DFW Attainment Demonstration SIP (rule project numbers 2006-034-117-EN and 2006-013-SIP-EN respectively).

The TCEQ has compared the exis ting state rules in 30 TAC Chapters 115 and 117 to the current RACT standards and determined that these rules fulfill the RACT requirements for the eight-hour ozone NAAQS. The emission source categories in the DFW eight-hour ozone nonattainment area have been reviewed and evaluated to determine appropriate emission specifications, controlJ-5 requirements, and associated control technologies for those source categories. The TCEQ has determined that the controls adopted with th is rulemaking are available, reasonable, and necessary to help the DFW eight-hour ozone nona ttainment area achieve the eight-hour ozoneNAAQS. All CTG source categories and non-CTG major emission sources in the DFW eighthour ozone nonattainment area, for which RACT is technologically and economically feasible, are controlled by source specific state rules thatfulfill RACT requirements or are controlled by standards that meet or exceed what would otherwise be considered RACT.J-6 Table J-1: State Rules Addressing RACT Requirements in CTG and ACT Reference Documents

Emission Source Category CTG or ACT Reference Document State Regulations Fulfilling RACT Requirements VOC Emissions Aerospace Guideline Seri es: Control of Volatile Organic Compound Emissions from Coating Operations at Aerospace Manufacturing and Rework Operations (EPA-453/R-97-004, EPA-68/D1- 00115, EPA-453/D-96-016, December 1997) (see 59 FR 29216, June 6, 1994) §115.420 – §115.429

Agricultural Pesticides Control of Volatile Organic Compound Emissions from the Application of Agricultural Pesticides (EPA-450/R-92-011, March 1993) The TCEQ does not regulate the use of agricultural pesticides and this ACT document does not give presumptive control therefore, no RACT determination is required for this source category. Architectural and Industrial Maintenance Coatings Reduction of Volatile Organic Compound Emissions from Application of Traffic Markings (EPA-450/3-88-007, August 1988) Emissions from this source category are regulated by the AIM National Rule.

Automobile Coating The Reduction of Volatile Organic Compound Emissions from Automobile Refinishing (EPA-450/3-88-009, October 1988) §115.420 – §115.429

Automobile Refinishing Alternative Control Techniques Document: Automobile Body Refinishing (EPA-453/R-94-031, April 1994) §115.420 – §115.429

Batch Processes Alternative Control Techniques Document: Control of Volatile Organic Compound Emissions from Batch Processes (EPA-453/R-93-017 or EPA 453/R-93- 020, February 1994) No existing major sources in the DFW eight-hour ozone area (SIC 2821, 2833, 2834, 2861, 2865, 2869, and 2879).

Bulk Gasoline Plants Control of Volatile Organic Emissions from Bulk Gasoline Plants (EPA-450/2-77-035, December 1977) §115.211 – §115.219

Cleaning Solvents Alternative Control Techniques Document: Industrial Cleaning Solvents (EPA-453/R-94-015, February 1994) §115.412 – §115.419 §115.420 – §115.429

Commercial Bakeries Alternative Control Techniques Document: Bakery Ovens (EPA-453/R-92-017, December 1992) §115.120 – §115.129

Cutback Asphalt Control of Volatile Organic Compounds from Use of Cutback Asphalt (EPA-450/2-77-037, December 1977) §115.510 – §115.519

Ethylene Oxide Sterilization/ Fumigation Operations Alternative Control Technology Document: Ethylene Oxide Sterilization/Fumigation Operations (EPA-450/3-89-007, March 1989) Emissions from this source category are regulated by MACT per §113.200.J-7 Emission Source Category CTG or ACT Reference Document State Regulations Fulfilling RACT Requirements Fugitive Emissions Fugitive Emission Sources of Organic Compounds – Additional Information on Emissions, Emission Reductions, and Costs (EPA-450/3-82-010, April 1982) §115.352 – §115.359

Gasoline Service Stations Design Criteria for Stage I Vapor Control Systems - Gasoline Service Stations (November 1975) §115.221 – §115.229

Graphic Arts Control of Volatile Organic Emissions from Existing Stationary Sources, Volume VIII: Graphic Arts -Rotogravure and Flexography (EPA450/2-78-033, December 1978) §115.430 – §115.439

Graphic Arts Control of Volatile Organic Compound Emissions from Offset Lithographic Printing (September 1993) §115.440 – §115.449

Graphic Arts Alternativ e Control Technology Document: Offset Lithographic Printing (EPA-453/R-94-054, June 1994) §115.440 – §115.449

Industrial Wastewater Control Techniques for Industrial Wastewater (EPA-453/D-93-056, September 1992) (ACT: April 1994, consists of cover memo with option tables and CTG) §115.140 – §115.149

Ink and Paint Manufacturing Alternative Control Technology Document: Control of Volatile Organic Compounds from Ink and Paint Manufacturing (EPA-453/3-92-013) No existing major sources in the DFW eight-hour ozone area (SIC 2842 and 2851).

Leather Tanning and Finishing Operations Alternative Control Technology Document: Leather Tanning and Finishing Operations (EPA-453/R-93-025) No existing major sources in the DFW eight-hour ozone area (SIC 3111).

Metal Furniture Control of Volatile Organic Emissions from Existing Stationary Sources, Volume III: Surface Coating of Metal Furniture (EPA-450/2-77-032, December 1977) §115.420 – §115.429

Natural Gas/Gasoline Processing Control of Volatile Organic Compound Equipment Leaks from Natural Gas/Gasoline Processing Plants (EPA-450/2-83-007, December 1983) §115.352 – §115.359

Petroleum Dry Cleaners Control of Volatile Organic Compound Emissions from Large Petroleum Dry Cleaners (EPA-450/3-82-009, September 1982) Contingency Measures: §115.552 – §115.553 §115.555 – §115.557 §115.559 Petroleum Liquid Storage Control of Volatile Organic Emissions from Storage of Petroleum Liquids in Fixed Roof Tanks (EPA-450/2-77-036, December 1977) §115.112 – §115.119

Petroleum Liquid Control of Volatile Organic Emissions §115.112 – §115.119J-8 Emission Source Category CTG or ACT Reference Document State Regulations Fulfilling RACT Requirements Storage from Petroleum Liquid Storage in External Floating Roof Tanks (EPA-450/2-78-047, December 1978) Petroleum Liquid Storage Alternative Control Techniques Document: Volatile Organic Liquid Storage in Floating and Fixed Roof Tanks (EPA-453/R-94-001, January 1994) §115.112 – §115.119

Plywood Veneer Dryers Control Techniques for Organic Emissions from Plywood Veneer Dryers (EPA-450/3-83-012, May 1983) No existing major sources in the DFW eight-hour ozone area (SIC 2435 and 2436).

Process Vents Alternative Control Technology Document: Organic Waste Process Vents (EPA-450/3-91-007, December 1990) §115.120 – §115.129

Refineries Control of Refinery Vacuum Producing Systems, Wastewater Separators, and Process Unit Turnarounds (EPA-450/2-77-025, October 1977) §115.311 – §115.319 §115.131 – §115.139

Refineries Control of Volatile Organic Compound Leaks from Petroleum Refinery Equipment (EPA-450/2-78-036, June 1978) §115.352 – §115.359

Rubber Tires Control of Volatile Organic Emissions from Manufacture of Pneumatic Rubber Tires (EPA-450/2-78-030, December 1978) No existing major sources in the DFW eight-hour ozone area (SIC 3011).

Shipbuilding and Ship Repair Control Technique Guidelines for Shipbuilding and Ship Repair Operations (EPA-453/R-94-032, April 1994 ) No existing major sources in the DFW eight-hour ozone area (SIC 3731).

Shipbuilding and Ship Repair Control Technique Guidelines for Shipbuilding and Ship Repair Surface Coating Operations (61 FR 44050, August 27, 1996) No existing major sources in the DFW eight-hour ozone area (SIC 3731).

Solvent Cleaning Control of Volatile Organic Emissions from Solvent Metal Cleaning (EPA-450/2-77-022, November 1977) §115.412 – §115.419 §115.420 – §115.429

Solvent Cleaning Alterna tive Control Technology Document: Halogenated Solvent Cleaners (EPA-450/3-89-030, August 1989) §115.412 – §115.419

Surface Coating Control of Volatile Organic Emissions from Existing Stationary Sources, Volume I: Control Methods for Surface Coating Operations (EPA-450/2-76-028, November 1976) §115.420 – §115.429

Surface Coating Control of Volatile Organic Emissions from Existing Stationary Sources, Volume II: Surface Coating of Cans, Coils, Paper, Fabrics, Automobiles, and Light-Duty Trucks §115.420 – §115.429J-9 Emission Source Category CTG or ACT Reference Document State Regulations Fulfilling RACT Requirements (EPA-450/2-77-008, May 1977) Surface Coating Control of Volatile Organic Emissions from Existing Stationary Sources, Volume IV: Surface Coating for Insulation of Magnet Wire (EPA-450/2-77-033, December 1977) §115.420 – §115.429

Surface Coating Control of Volatile Organic Emissions from Existing Stationary Sources, Volume V: Surface Coating of Large Appliances (EPA-450/2-77-034, December 1977) §115.420 – §115.429

Surface Coating Control of Volatile Organic Emissions from Existing Stationary Sources, Volume VI: Surface Coating of Miscellaneous Metal Parts and Products (EPA-450/2-78-015, June 1978) §115.420 – §115.429

Surface Coating Control of Volatile Organic Emissions from Existing Stationary Sources, Volume VII: Factory Surface Coating of Flat Wood Paneling (EPA-450/2-78-032, June 1978) §115.420 – §115.429

Surface Coating Alternative Control Techniques Document: Surface Coating of Automotive/Transportation and Business Machine Plastic Parts (EPA-453/R-94-017, February 1994) §115.420 – §115.429

Synthetic Organic Chemical Manufacturing Industry Control of Volatile Organic Emissions from Manufacture of Synthesized Pharmaceutical Products (EPA-450/2-78-029, December 1978) §115.531 – §115.539

Synthetic Organic Chemical Manufacturing Industry Control of Volatile Organic CompoundEmissions from Manufacture of HighDensity Polyethylene, Polypropylene, and Polystyrene Resins (EPA-450/3-83-008, November 1983) §115.120 – §115.129

Synthetic Organic Chemical Manufacturing Industry Control of Volatile Organic Compound Fugitive Emissions from Synthetic Organic Chemical Polymer and Resin Manufacturing Equipment (EPA-450/3-83-006, March 1984) §115.352 – §115.359

Synthetic Organic Chemical Manufacturing Industry Control of Volatile Organic Compound Emissions from Air Oxidation Processes in Synthetic Organic Chemical Manufacturing Industry (EPA-450/3-84-015, December 1984) §115.120 – §115.129

Synthetic Organic Chemical Manufacturing Industry Polystyrene Foam Manufacturing (EPA-450/3-90-020, 1990) §115.120 – §115.129

Synthetic Organic Chemical Manufacturing Control of Volatile Organic Compound Emissions from Reactor Processes and Distillation Operations in Synthetic §115.120 – §115.129J-10 Emission Source Category CTG or ACT Reference Document State Regulations Fulfilling RACT Requirements Industry Organic Chemical Manufacturing Industry (EPA-450/4-91-031, August 1993) Tank Trucks Control of Hydrocarbons from Tank Truck Gasoline Loading Terminals (EPA-450/2-77-026, December 1977) §115.211 – §115.219 §115.221 – §115.229

Tank Trucks Control of Volatile Organic Compound Leaks from Gasoline Tank Trucks and Vapor Collection Systems (EPA-450/2-78-051, December 1978) §115.211 – §115.219 §115.234 – §115.239

Vegetable Oil Manufacturing Control of Volatile Organic Emissions from Manufacture of Vegetable Oils (EPA-450/2-78-035, June 1978) No existing major sources in the DFW eight-hour ozone area (SIC 2046 and 2076). Wood Furniture Manufacturing Guideline Series: Control of Volatile Organic Compound Emissions from Wood Furniture Manufacturing Operations (EPA-453/D-95-002) §115.420 – §115.429

Wood Furniture Manufacturing Guidelines Series: Control of Volatile Organic Compound Emissions from Wood Furniture Manufacturing Operations (EPA-453/R-96-007, April 1996) (see also 61 FR 25223, and, 61 FR 50823, September 27, 1996) §115.420 – §115.429

NO X Emissions Brick & Ceramic Manufacturing Non-CTG Major NO X Source §117.410(b)(7)(B)

Cement Manufacturing NO XEmissions from Cement Manufacturing (EPA-453/R-94-004, March 1994) (Updated September 2000) §117.3110(a) – (f) & §117.3123

Coke, Wood, Rice, and Other Biomass-Fired Boilers Non-CTG Major NO X Source No existing major sources in DFW eight-hour ozone area.

Fiberglass Manufacturing Non-CTG Major NO X Source §117.410(b)(10) & (11)

Fuel Switching Fuel Switching to Meet NO XRACT for NO X (EPA Memorandum, July 30, 1993) §117.400 – §117.456 §117.1300 – §117.1356

Glass Manufacturing NO XEmissions from Glass Manufacturing (EPA-453/R-94-037, June 1994) §117.410(b)(10) & (11)

Hot Mix Asphalt Plants Non-CTG Major NO X Source No existing major sources in DFW eight-hour ozone area. Incinerators Non-CTG Major NO X Source §117.410(b)(9) Industrial, Commercial, and Institutional Boilers NOx Emissions from Industrial, Commercial & Institutional Boilers (EPA-453/R-94-022, March 1994) §117.410(b)(1) & (2)

Iron and Steel NO XEmissions from Iron and Steel Mills §117.410(b)(8)J-11 Emission Source Category CTG or ACT Reference Document State Regulations Fulfilling RACT Requirements (EPA-453/R-94-065, September 1994) Lead Smelting Non-CTG Major NO X Source §117.410(b)(8) Lightweight Aggregate Kilns Non-CTG Major NO X Source No existing major sources in DFW eight-hour ozone area. Lime Manufacturing Non-CTG Major NO X Source §117.410(b)(7)(A)

Magnesium Chloride Fluidized Bed Dryers Non-CTG Major NO X Source No existing major sources in DFW eight-hour ozone area.

Natural Gas-Fired Dryers, Heaters, and Ovens at Major Sources Non-CTG Major NO X Source §117.410(b)(12) & (13)

Nitric and Adipic Acid Manufacturing NO XEmissions from Nitric and Adipic Acid Manufacturing Plants (EPA-453/3-91-026, December 1991) §117.4000 – §117.4050 §117.4100 – §117.4150 §117.4200 – §117.4210 Oilfield Drilling Operations Non-CTG Major NO X Source No existing major sources in DFW eight-hour ozone area. Other Minerals Processing Kilns Non-CTG Major NO X Source No existing major sources in DFW eight-hour ozone area. Petroleum Refining Operations Non-CTG Major NO X Source No existing major sources in DFW eight-hour ozone area.

Process Heaters NO XEmissions from Process Heaters (EPA-453/R-93-034, revised September 1993) §117.410(b)(3)

Pulping Liquor Recovery Furnaces Non-CTG Major NO X Source No existing major sources in DFW eight-hour ozone area.

Pyrolysis Reactors Non-CTG Major NO X Source No existing major sources in DFW eight-hour ozone area. Stationary Internal Combustion Engines NO XEmissions from Stationary Internal Combustion Engines (EPA-453/R-93-032, July 1993) (Updated September 2000) §117.410(a) & (b)(4)

Stationary Turbines NO XEmissions from Stationary Combustion Turbines (EPA-453/R-93-007, January 1993) §117.410(b)(5)

Utility Auxiliary Steam Boilers Non-CTG Major NO X Source §117.1310(a)(2)

Utility Boilers NO XEmissions from Utility Boilers (EPA-453/R-94-023, March 1994) §117.1310(a)(1)

Utility Stationary Gas Turbines Non-CTG Major NO X Source §117.1310(a)(3)J-12 Table J-2: State Rules Addressing RACT Requirements for Major Emission Sources in the DFW Eight-Hour Ozone Nonattainment Area

Source Account # Company Name SIC Code Source Description Emissions (tpy) RACT Determination

Major Sources of VOC Emissions (from the 2002 TCEQ Emissions Inventory) ED0099J Holcim Texas LP 3241 Cement kilns 626.67 Control of VOC emissions is not economically feasible. ED0168P Dartco of TX LP 3089 Foam containers 539.65 VOC emissions are controlled per BACT in NSR Permit No. 18505. Additional control for RACT is not economically feasible. ED0011D Chaparral Steel Midlothian LP 3312 Iron and Steel foundry electric arc furnaces 339.59 VOC emissions are controlled per BACT in NSR Permit No. 1635, 3026, 5983, 8097, 8099. Further control may be required by MACT. Additional control for RACT is not economically feasible. JH0025O Johns Manville International Inc. 3296 Fiberglass curing 219.30 VOC emissions are controlled per BACT in NSR Permit No. 946A, 1218. Additional control for RACT is not economically feasible. ED0051O Owens-Corning Waxahachie Plant 3296 Fiberglass forming and curing 137.50 VOC emissions are controlled per BACT in NSR Permit No. 6093. Additional control for RACT is not economically feasible. KB0015U Vistawall Architectural Products 3354 Aluminum coating 112.37 Surface coating operations are covered by RACT in §115.420 – §115.429. PC0001E ACME Brick Bennett Plant 3251 Brick kiln 90.59 VOC emissions are controlled per BACT in NSR Permit No. 25937. Additional control for RACT is not economically feasible. PC0013U Enbridge Gathering Springtown Gas Plant 1321 Gas plant, fugitives, storage tanks covered 91.90 VOC emissions from equipment leak fugitives are covered in §115.352 – §115.359 and from storage tanks by §115.112 – §115.119.J-13 Source Account # Company Name SIC Code Source Description Emissions (tpy) RACT Determination

ED0332D Midlothian Energy LP 4911 Gas-fired combustion turbines 77.39 VOC emissions arise from natural gas combustion; control is not economically feasible. KB0073G Madix Inc Skyline Manufacturing Facility 2542 Surface coating misc. metal parts 63.49 Surface coating operations are covered by RACT in §115.420 – §115.429. ED0018M Elk Corp. of TX 2952 Asphalt Roofing 59.66 VOC emissions are controlled per BACT in NSR Permits. Additional control for RACT is not economically feasible. ED0032S G.S. Roofing Products 2952 Asphalt Roofing 51.27 VOC emissions are controlled per BACT in NSR Permits. Additional control for RACT is not economically feasible. TA0157I General Motors Corporation 3711 Motor vehicle manufacture 555.77 Surface coating operations are covered by rules satisfying RACT in §115.420 – §115.429. DF0051J Peterbilt Motors Co. 3711 Motor vehicle manufacture 181.76 Surface coating operations are covered by rules satisfying RACT in §115.420 – §115.429. DB0802D Quebecor World 2754 Printing 159.24 Printing operations are covered by rules satisfying RACT in §115.430 – §115.439. TA0235N Miller Brewing Co. 2082 Beverage alcohol production 149.65 VOC emissions are controlled per BACT in NSR Permit No. 3113. Additional control for RACT is not economically feasible. CP0004W General Cable Texas Operations 3366 Copper foundries 121.49 Plant was shut down in 2004.

DB1172K Western Extrusions Corp 3354 Aluminum coating 106.63 Surface coating operations are covered by rules satisfying RACT in §115.420 – §115.429.J-14 Source Account # Company Name SIC Code Source Description Emissions (tpy) RACT Determination

TA0133W Styrochem US Ltd 2821 Plastics and resins 98.4 Vent emissions are covered by rules satisfying RACT in §115.120 – §115.129. Fugitive emissions are covered under §115.352 – §115.359. DB0838F Texwood Industries LP 2434 Wood kitchen cabinets 91.31 Surface coating operations are covered by rules satisfying RACT in §115.420 – §115.429. DB0482W Datron Inc. 3443 Metal coating 86.58 Surface coating operations are covered by rules satisfying RACT in §115.420 – §115.429. DB0179D Rock-Tenn Co. 2621 Paper mill 82.87 VOC emissions are controlled per BACT in NSR Permit No. 49039. Additional control for RACT is not economically feasible. TA0353G Ex-Tex LaPorte LP 4911 Electricity generation 77.46 Control of VOC emissions is not economically feasible. DB0976P Lasco Bathware Inc. 3088 Plastic plumbing fixtures 70.84 Installed control equipment; emissions reported in 2005 less than 50 tpy with a presumed PTE less than 100 tpy. TA0508B Valero Logistics Southlake Terminal 5171 Gasoline terminal 68.14 Gasoline terminal operations are covered by rules satisfying RACT for storage tanks in §115.112 – §115.119 and for loading in §115.211 – §115.219. DB0447B Hensley Industries Inc. 3325 Steel production 65.01 VOC emissions are controlled per BACT in NSR Permit No. 2489A. Additional control for RACT is not economically feasible. DB1040F Williamson Printing Corp. 2752 Lithographic printing 64.17 Printing operations are covered by rules satisfying RACT in §115.430 – §115.439.J-15 Source Account # Company Name SIC Code Source Description Emissions (tpy) RACT Determination

DB0566P SST Truck Co. 3711 Motor vehicle manufacture 59.71 Surface coating operations are covered by rules satisfying RACT in §115.420 – §115.429. DB0386T General Aluminum Company of TX 3442 Aluminum windows 57.04 Surface coating operations are covered by rules satisfying RACT in §115.420 – §115.429. TA0102K Conoco Phillips 5171 Gasoline terminal 56.25 Gasoline terminal operations are covered by rules satisfying RACT for storage tanks in §115.112 – §115.119 and for loading in §115.211 – §115.219. DB0259E Dallas Woodcraft Company LP 2499 Wooden picture frames 56.19 Surface coating operations are covered by rules satisfying RACT in §115.420 – §115.429. DB0914O Vought Aircraft Industries 3721 Aircraft 54.76 Surface coating operations are covered by rules satisfying RACT in §115.420 – §115.429. DB0249H TXU Generation Co. 4911 Electricity generation 54.69 Control of VOC emissions is not economically feasible. CP0029G Exide Corp. 3341 Battery recycling 53.11 VOC emissions are controlled per BACT in NSR Permit No. 1147A. Additional control for RACT is not economically feasible DB0344M ExxonMobil Corp. 5171 Gasoline terminal 52.51 Gasoline terminal operations are covered by rules satisfying RACT for storage tanks in §115.112 – §115.119 and for loading in §115.211 – §115.219. DB0795V Motiva Enterprises LLP 5171 Gasoline terminal 52.37 Gasoline terminal operations are covered by rules satisfying RACT for storage tanks in §115.112 – §115.119 and for loading in §115.211 – §115.219. Major Sources of NO X Emissions (from the 2000 TCEQ Emissions Inventory)J-16 Source Account # Company Name SIC Code Source Description Emissions (tpy) RACT Determination

ED0066B TXI Operations LP 3241 Cement Manufacturing 4515.42 NO X emissions from cement kilns are covered by rules satisfying RACT in §117.3100 – §117.3145. TA0353G ExTex LaPorte LP 4911 Industrial Dist. Oil/Diesel Reciprocating 3690.54 NO X emissions from engines are covered by rules satisfying RACT in §117.410(b)(4). ED0099J Holcim Texas LP 3241 Cement Manufacturing 3474.71 NO X emissions from cement kilns are covered by rules satisfying RACT in §117.3100 – §117.3145. DB0252S ExTex LaPorte LP 4911 Electric Generation, Natural Gas >100 MMBtu/hr 2905.36 NO X emissions from utility electric generation are covered by rules satisfying RACT in §117.1300 – §117.1356. ED0034O Ash Grove Texas LP 3241 Cement Manufacturing 2904.90 NO X emissions from cement kilns are covered by rules satisfying RACT in §117.3100 – §117.3145. DB0251U TXU Electric Company 4911 Electric Generation Dist. Oil/Diesel Turbine 2676.48 NO X emissions from utility electric generation are covered by rules satisfying RACT in §117.1300 – §117.1356. DB0249H TXU Generation Company LP 4911 Electric Generation Dist. Oil/Diesel Reciprocating 2339.15 NO X emissions from utility electric generation are covered by rules satisfying RACT in §117.1300 – §117.1356. TA0352I TXU Generation Company LP 4911 Electric Generation Dist. Oil/Diesel Reciprocating 1336.45 NO X emissions from utility electric generation are covered by rules satisfying RACT in §117.1300 – §117.1356. CP0026M Garland Municipal Power and Light 4911 Electric Generation, Natural Gas, Tan Fired Boilers 1092.85 NO X emissions from utility electric generation are covered by rules satisfying RACT in §117.1300 – §117.1356.J-17 Source Account # Company Name SIC Code Source Description Emissions (tpy) RACT Determination

JH0045I Texas Lime Company 3274 Lime Manufacturing, Calcining, Rotary Kiln 1028.60 NO X emissions from lime kilns are covered by rules satisfying RACT in §117.400 – §117.456. DB0253Q TXU Generation Company LP 4911 Electric Generation Dist. Oil/Diesel Reciprocating 1012.93 NO X emissions from utility electric generation are covered by rules satisfying RACT in §117.1300 – §117.1356. ED0051O Owens-Corning 3296 Industrial Natural Gas <10 MMBtu/hr 586.36 NO X emissions from fiberglass are covered by rules satisfying RACT in §117.410(b)(10). PC0013U Enbridge Gathering (North Texas) LP 1321 Industrial, Natural Gas, 4- Cycle Rich-Burn 551.20 NO X emissions from engines are covered by rules satisfying RACT in §117.410(b)(4). ED0011D Chaparral Steel Midlothian LP 3312 Steel Foundries 507.17 NO X emissions from furnaces used in steel production are covered by rules satisfying RACT in §117.410(b)(8). DF0012T Garland Municipal Power and Light 4911 Electric Generation, Natural Gas, >100 MMBtu/hr 485.58 NO X emissions from electric generation are covered by rules satisfying RACT in §117.1310. TA0512K Village Creek Wastewater Treatment 4952 Industrial, Large Bore Engine, Dual-Fuel (Oil/Gas) 450.90 NO X emissions from engines are covered by rules satisfying RACT in §117.410(b)(4). ED0044L Saint Gobain Containers 3221 Glass Manufacturing, Container Glass Melting Furnace 310.10 NO X emissions from glass melting furnaces are covered by rules satisfying RACT in §117.410(b)(10). TA0354E TXU Generation Company LP 4911 Electric Generation, Natural Gas, >100 MMBtu/hr 305.72 NO X emissions from utility electric generation are covered by rules satisfying RACT in §117.1310. DB2459D The University of Texas Southwestern 8221 Industrial, Large Bore Engine, Dual-Fuel (Oil/Gas) 267.64 NO X emissions from engines are covered by rules satisfying RACT in §117.410(b)(4). TA4004G Tyson Foods Inc 2099 Industrial, Natural Gas, 4-Cycle LeanBurn 242.27 NO X emissions from engines are covered by rules satisfying RACT in §117.410(b)(4).J-18 Source Account # Company Name SIC Code Source Description Emissions (tpy) RACT Determination

JH0230L Ponderosa Pine Energy Partners Ltd 4911 Electric Generation, Natural Gas, >100 MMBtu/hr 169.00 NO X emissions from utility electric generation are covered by rules satisfying RACT in §117.1310. DB3357F Tyson Foods Inc 2013 Industrial, Natural Gas, 4-Cycle LeanBurn 155.73 NO X emissions from engines are covered by rules satisfying RACT in §117.410(b)(4). CP0065C TXU Generation Company LP 4911 Electric Generation Dist. Oil/Diesel Reciprocating 148.39 NO X emissions from utility electric generation are covered by rules satisfying RACT in §117.1310. KB0050S Energy Transfer Fuel LP 1311 Industrial, Natural Gas, 2-Cycle LeanBurn 137.82 NO X emissions from engines are covered by rules satisfying RACT in §117.410(b)(4). DB0179D Rock-Tenn Company 2621 Fuel Fired Equipment Process Heaters Natural Gas 136.68 NO X emissions from process heaters are covered by rules satisfying RACT in §117.410(b)(4). PC0140M Cantera Resources Inc 1321 Industrial, Natural Gas Reciprocating 127.35 NO X emissions from engines are covered by rules satisfying RACT in §117.410(b)(4). JH0025O Johns Manville International Inc 3296 Fiberglass Wool-Type Fiber, Regenerative Furnace 122.23 NO X emissions from fiberglass furnaces are covered by rules satisfying RACT in §117.410(b)(10). DB0820B Texas Instruments Inc 3674 CommercialInstitutional Natural Gas 10- 100 MMBtu/hr 79.17 NO X emissions from ICI boilers are covered by rules satisfying RACT in §117.410(b)(1). DB1073N American Marazzi Tile Inc 3253 CommercialInstitutional Natural Gas <10 MMBtu/hr 68.13 NO X emissions from brick and ceramic kilns are covered by rules satisfying RACT in §117.410(b)(7). DB0384A Garland Municipal Power and Light 4911 Electric Generation, Natural Gas, >100 MMBtu/hr 67.87 NO X emissions from utility electric generation are covered by rules satisfying RACT in §117.1310. PC0005T Brazos Electric Power Cooperative Inc 4911 Electric Generation, Natural Gas, >100 MMBtu/hr 60.82 NO X emissions from utility electric generation are covered by rules satisfying RACT in §117.1310.J-19 Source Account # Company Name SIC Code Source Description Emissions (tpy) RACT Determination

DF0001B ACME Brick Company 3251 Brick Manufacturing 57.69 NO X emissions from brick kilns are covered by rules satisfying RACT in §117.410(b)(7). CP0029G Exide Corporation 3341 CommercialInstitutional Natural Gas <10 MMBtu/hr 57.35 NO X emissions from boilers are covered by rules satisfying RACT in §117.410(b)(1). TA0115B DFW International Airport 4581 Industrial Dist. Oil/Diesel Reciprocating 55.99 NO X emissions from engines are covered by rules satisfying RACT in §117.410(b)(4). TA0157I General Motors Corporation 3711 Engine Testing Reciprocating Gasoline 53.77 Control of NO X emissions is not economically feasible. DF0558Q Texas Aero Engine Service LLC 4581 Engine Testing, Aircraft, Jet A Fuel 53.44 Control of NO X emissions is not economically feasible.