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I NDIANA DEPARTMENT OF ENVIRONMENTAL MANAGEMENT We Protect Hoosiers and Our Environment. 100 N. Senate Avenue • Indianapolis, IN 46204 (800) 451-6027 (317) 232-8603 www.idem.IN.gov Michael R. Pence Thomas W. Easterly Governor Commissioner To: Interested Parties Date: January 7, 2015 From: Matthew Stuckey, Chief Permits Branch Office of Air Quality Source Name: Superior Hardwoods Permit Level: MSOP - Administrative Amendment Permit Number: 121 - 35251 - 00020 Source Location: 6429 W. 100 N., Montezuma, Indiana Type of Action Taken: Changes that are administrative in nature Notice of Decision: Approval Please be advised that on behalf of the Commissioner of the Department of Environmental Management, I have issued a decision regarding the matter referenced above. Pursuant to 326 IAC 2, this approval was effective immediately upon submittal of the application. The final decision is available on the IDEM website at: http://www.in.gov/apps/idem/caats/ To view the document, select Search option 3, then enter permit 35251. If you would like to request a paper copy of the permit document, please contact IDEM’s central file room: Indiana Government Center North, Room 1201 100 North Senate Avenue, MC 50-07 Indianapolis, IN 46204 Phone: 1-800-451-6027 (ext. 4-0965) Fax (317) 232-8659 (continues on next page) An Equal Opportunity Employer Recycled Paper

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Page 1: Notice of Decision: Approvalpermits.air.idem.in.gov/35251f.pdf · 2015. 1. 7. · Permit Number: 121 - 35251 - 00020 . Source Location: 6429 W. 100 N., Montezuma, Indiana . Type of

INDIANA DEPARTMENT OF ENVIRONMENTAL MANAGEMENT We Protect Hoosiers and Our Environment.

100 N. Senate Avenue • Indianapolis, IN 46204

(800) 451-6027 • (317) 232-8603 • www.idem.IN.gov

Michael R. Pence Thomas W. Easterly Governor Commissioner

To: Interested Parties Date: January 7, 2015 From: Matthew Stuckey, Chief Permits Branch Office of Air Quality Source Name: Superior Hardwoods Permit Level: MSOP - Administrative Amendment Permit Number: 121 - 35251 - 00020 Source Location: 6429 W. 100 N., Montezuma, Indiana Type of Action Taken: Changes that are administrative in nature

Notice of Decision: Approval

Please be advised that on behalf of the Commissioner of the Department of Environmental Management, I have issued a decision regarding the matter referenced above. Pursuant to 326 IAC 2, this approval was effective immediately upon submittal of the application. The final decision is available on the IDEM website at: http://www.in.gov/apps/idem/caats/ To view the document, select Search option 3, then enter permit 35251. If you would like to request a paper copy of the permit document, please contact IDEM’s central file room:

Indiana Government Center North, Room 1201 100 North Senate Avenue, MC 50-07 Indianapolis, IN 46204 Phone: 1-800-451-6027 (ext. 4-0965) Fax (317) 232-8659

(continues on next page)

An Equal Opportunity Employer

Recycled Paper

Page 2: Notice of Decision: Approvalpermits.air.idem.in.gov/35251f.pdf · 2015. 1. 7. · Permit Number: 121 - 35251 - 00020 . Source Location: 6429 W. 100 N., Montezuma, Indiana . Type of

If you wish to challenge this decision, IC 4-21.5-3-7 requires that you file a petition for administrative review. This petition may include a request for stay of effectiveness and must be submitted to the Office of Environmental Adjudication, 100 North Senate Avenue, Government Center North, Suite N 501E, Indianapolis, IN 46204, within eighteen (18) calendar days from the mailing of this notice. The filing of a petition for administrative review is complete on the earliest of the following dates that apply to the filing: (1) the date the document is delivered to the Office of Environmental Adjudication (OEA); (2) the date of the postmark on the envelope containing the document, if the document is mailed to

OEA by U.S. mail; or (3) The date on which the document is deposited with a private carrier, as shown by receipt issued

by the carrier, if the document is sent to the OEA by private carrier. The petition must include facts demonstrating that you are either the applicant, a person aggrieved or adversely affected by the decision or otherwise entitled to review by law. Please identify the permit, decision, or other order for which you seek review by permit number, name of the applicant, location, date of this notice and all of the following: (1) the name and address of the person making the request; (2) the interest of the person making the request; (3) identification of any persons represented by the person making the request; (4) the reasons, with particularity, for the request; (5) the issues, with particularity, proposed for considerations at any hearing; and (6) identification of the terms and conditions which, in the judgment of the person making the

request, would be appropriate in the case in question to satisfy the requirements of the law governing documents of the type issued by the Commissioner.

If you have technical questions regarding the enclosed documents, please contact the Office of Air Quality, Permits Branch at (317) 233-0178. Callers from within Indiana may call toll-free at 1-800-451-6027, ext. 3-0178.

Enclosures Decision Permit Amdendment 4/8/14

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Superior Hardwoods Page 2 of 5 Montezuma, Indiana Administrative Amendment No. 121-35251-00020 Permit Reviewer: Brian Wright

(a) The uncontrolled/unlimited potential to emit of the entire source after the addition of the emission units will continue to be within the threshold levels specified in 326 IAC 2-6.1 (MSOP). (See Appendix A for emission calculations).

(b) The incorporation of the modification will not cause the source’s potential to emit to be

greater than the threshold levels specified in 326 IAC 2-2 (PSD), 326 IAC 2-3 (Emission Offset), or 326 IAC 2-7 (Part 70).

(c) The new Veneer Operations natural gas-fired boiler is subject to the requirements of the

New Source Performance Standards (NSPS) for Small Industrial-Commercial-Institutional Steam Generating Units, 40 CFR 60, Subpart Dc (326 IAC 12), because it has a heat input capacity of greater than ten (10) MMBtu per hour and less than one-hundred (100) MMBtu per hour and it commenced construction after June 9, 1989.

Applicable portions of the NSPS are the following:

(1) 40 CFR 60.40c(a), (b) and (c) (2) 40 CFR 60.41c (3) 40 CFR 60.48c(a), (g), and (i)

(d) The requirements of the National Emission Standards for Hazardous Air Pollutants for Industrial, Commercial, and Institutional Boilers and Process Heaters, 40 CFR 63, Subpart DDDDD (326 IAC 20-95), are not included in this revision for the Veneer Operations natural gas-fired boiler, because this source is not a major source of HAPs.

(e) The requirements of the National Emission Standards for Hazardous Air Pollutants

(NESHAPs) for Industrial, Commercial, and Institutional Boilers - Area Sources, 40 CFR 63, Subpart JJJJJJ, are not included in the permit for the new Veneer Operations natural gas-fired boiler because it is a gas-fired boiler as defined by 40 CFR 63.11237.

(f) 326 IAC 6-2 (Particulate Limitations for Sources of Indirect Heating)

Pursuant to 326 IAC 6-2-1(d), the new Veneer Operations natural gas-fired boiler, is subject to 326 IAC 6-2-4 since it is a source of indirect heat constructed after September 21, 1983. Pt = 1.09

Q0.26

Where: Pt = Pounds of particulate matter emitted per million Btu (lb/MMBtu) heat input; and

Q = Total source maximum operating capacity rating in million Btu per hour (MMBtu/hr) heat input.

Q = 10.043 MMBtu/hr (new veneer operations boiler) + 0.45 MMBtu/hr (existing wood stoves AA4, constructed in 2007) + 12.42 MMBtu/hr (existing wood-fired boiler AA2, constructed in 2000) + 8.28 MMBtu/hr (existing boiler AA3, constructed in 1999) Q = 31.19

Therefore, Pt = 0.44 lb/MMBtu Based on the AP-42, Chapter 1.4, uncontrolled natural gas combustion particulate emission factor of 1.9 pounds per million cubic foot (MMCF) of natural gas, the natural gas fired boiler has particulate emissions as follows: (1.9 pound PM/MMCF) * (1 MMCF / 1020 MMBtu) = 0.0019 lb PM per MMBtu Therefore, the new Veneer Operations natural gas-fired boiler is able to comply with the particulate emission limitation under 326 IAC 6-2-4 without the use of a control device.

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Superior Hardwoods Page 3 of 5 Montezuma, Indiana Administrative Amendment No. 121-35251-00020 Permit Reviewer: Brian Wright

PTE of the Entire Source After Issuance of the MSOP Administrative Amendment The table below summarizes the potential to emit of the entire source after issuance of this revision, reflecting all limits, of the emission units. Any control equipment is considered federally enforceable only after issuance of this MSOP permit revision, and only to the extent that the effect of the control equipment is made practically enforceable in the permit. (Note: the table below was generated from the above table, with bold text un-bolded and strikethrough text deleted)

Process/ Emission Unit

Potential To Emit of the Entire Source After Issuance of Amendment (tons/year) (After Consideration of Integral Woodworking Controls)

PM PM10* PM2.5* SO2 NOx VOC CO GHGs as CO2e**

Total HAPs

Worst Single HAP

Woodworking AA1 93.27 39.21 39.21 0.00 0.00 0.00 0.00 0 0.00 0.00

End Wax 1.91 1.91 1.91 0.00 0.00 2.15 0.00 0 2.15 2.15 (Methanol)

End Paint 0.39 0.39 0.39 0.00 0.00 0.00 0.00 0 0.00 0.00

Kilns 0.00 0.00 0.00 0.00 0.00 29.78 3.21 0 4.17 1.85 (Methanol)

Wood Waste Boiler 21.76 20.51 17.79 1.36 26.66 0.92 32.64 11,496 1.82 1.03 (HCl)

Nat Gas Boiler 0.07 0.27 0.27 0.02 3.56 0.20 2.99 4,292 0.07 0.07 (Hexane)

Wood Stoves 0.79 0.74 0.64 0.05 0.97 0.03 1.18 417 0.07 0.04 (HCl)

Welding 0.04 0.04 0.04 0.00 0.00 0.00 0.00 0 0.00 0.00 Gasoline Dispensing Operation 0.00 0.00 0.00 0.00 0.00 0.15 0.00 0 1.9E-3 6.1E-4

(Toulene)

Lumber Soaking Operations 0.00 0.00 0.00 0.00 0.00 0.37 0.00 0 0.37 0.04 (Methanol)

Veneer Slicing 0.00 0.00 0.00 0.00 0.00 0.36 0.00 0 0.06 0.04 (Methanol)

Veneer Drying 5.22 5.22 5.22 0.00 0.00 7.76 0.62 0 1.21 0.72 (Methanol)

Nat Gas Boiler (Veneer Operations) (a) 0.08 0.33 0.33 0.03 4.31 0.24 3.62 5,206 0.08 0.08

(Hexane) Unpaved Roads 499.40 127.28 12.73 0.00 0.00 0.00 0.00 0 0.00 0.00

Total PTE of Entire Source 622.93 195.90 78.53 1.46 35.49 41.96 44.27 21,410 9.69 4.79 (Methanol)

Title V Major Source Thresholds** NA 100 100 100 100 100 100 100,000 25 10

PSD Major Source Thresholds** 250 250 250 250 250 250 250 NA NA NA

Subject to Regulation NA NA NA NA NA NA NA 100,000 NA NA (a) New units with this Revision. *Under the Part 70 Permit program (40 CFR 70), PM10 and PM2.5, not particulate matter (PM), are each considered as a "regulated air pollutant".

Pursuant to the provisions of 326 IAC 2-6.1-6, the permit is hereby amended as follows with the

deleted language as strikeouts and new language bolded.

1. Section A.2 has been amended as follows in order to remove the existing boiler and add the new boiler to the permit:

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Superior Hardwoods Page 4 of 5 Montezuma, Indiana Administrative Amendment No. 121-35251-00020 Permit Reviewer: Brian Wright

(m) One (1) Veneer Operations natural gas-fired boiler, approved in 2014 for construction, with a maximum heat input capacity of 8.28 MMBtu/hr, using no control, and vented to a stack.

(m) One (1) Veneer Operations natural gas-fired boiler, approved in 2015 for construction, with a maximum heat input capacity of 10.043 MMBtu/hr, using no control, and vented to a stack.

The boiler is an affected unit under the provisions of 40 CFR 60, Subpart Dc.

2. Section D.2 has been amended as follows in order to incorporate the new unit: SECTION D.2 EMISSIONS UNIT OPERATION CONDITIONS

****** (m) One (1) Veneer Operations natural gas-fired boiler, approved in 2014 for construction, with a

maximum heat input capacity of 8.28 MMBtu/hr, using no control, and vented to a stack. (m) One (1) Veneer Operations natural gas-fired boiler, approved in 2015 for construction,

with a maximum heat input capacity of 10.043 MMBtu/hr, using no control, and vented to a stack.

The boiler is an affected unit under the provisions of 40 CFR 60, Subpart Dc.

****** ****** D.2.2 Particulate Emission Limitations for Sources of Indirect Heating [326 IAC 6-2-4]

****** (d) Pursuant to 326 IAC 6-2-4, particulate emissions from the Veneer Operations natural

gas-fired boiler shall not exceed 0.45 0.44 pounds per million Btu (lb/MMBtu) of heat input

These limits are calculated using the following equation:

Pt = 1.09

Q0.26

where: Pt = Pounds of particulate matter (PM) emitted per million British thermal

units (lb/MMBtu) heat input. Q = Total source maximum operating capacity rating in million Btu per hour

(MMBtu/hr) heat input. For Boiler AA3, Q = 8.28 MMBtu per hour For Boiler AA2, Q = 20.7 MMBtu per hour (8.28 + 12.42) For Boiler AA4, Q = 21.15 MMBtu per hour (20.7 + 0.45) For Veneer Operations Boiler, Q = 29.43 31.19 MMBtu per hour (21.15 + 8.28 10.043)

3. Section E.1 has been amended as follows in order to incorporate the new unit: SECTION E.1 EMISSIONS UNIT OPERATION CONDITIONS

****** (m) One (1) Veneer Operations natural gas-fired boiler, approved in 2015 for construction,

with a maximum heat input capacity of 10.043 MMBtu/hr, using no control, and vented to a stack.

The boiler is an affected unit under the provisions of 40 CFR 60, Subpart Dc.

******

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Superior Hardwoods Administrative Amendment No. 121-35251-00020 Page 2 of 30 Montezuma, Indiana Revised by: Brian Wright M121-33610-00020 Permit Reviewer: Heath Hartley

TABLE OF CONTENTS A. SOURCE SUMMARY ............................................................................................................................... 4

A.1 General Information [326 IAC 2-5.1-3(c)][326 IAC 2-6.1-4(a)] A.2 Emission Units and Pollution Control Equipment Summary

B. GENERAL CONDITIONS ........................................................................................................................ 8

B.1 Definitions [326 IAC 2-1.1-1] B.2 Reserved B.3 Affidavit of Construction [326 IAC 2-5.1-3(h)] [326 IAC 2-5.1-4] B.4 Permit Term [326 IAC 2-6.1-7(a)][326 IAC 2-1.1-9.5][IC 13-15-3-6(a)] B.5 Term of Conditions [326 IAC 2-1.1-9.5] B.6 Enforceability B.7 Severability B.8 Property Rights or Exclusive Privilege B.9 Duty to Provide Information B.10 Annual Notification [326 IAC 2-6.1-5(a)(5)] B.11 Preventive Maintenance Plan [326 IAC 1-6-3] B.12 Prior Permits Superseded [326 IAC 2-1.1-9.5] B.13 Termination of Right to Operate [326 IAC 2-6.1-7(a)] B.14 Permit Renewal [326 IAC 2-6.1-7] B.15 Permit Amendment or Revision [326 IAC 2-5.1-3(e)(3)][326 IAC 2-6.1-6] B.16 Source Modification Requirement B.17 Inspection and Entry [326 IAC 2-5.1-3(e)(4)(B)][326 IAC 2-6.1-5(a)(4)][IC 13-14-2-2] [IC 13-17-3-2][IC 13-30-3-1] B.18 Transfer of Ownership or Operational Control [326 IAC 2-6.1-6] B.19 Annual Fee Payment [326 IAC 2-1.1-7] B.20 Credible Evidence [326 IAC 1-1-6]

C. SOURCE OPERATION CONDITIONS .................................................................................................. 13

Emission Limitations and Standards [326 IAC 2-6.1-5(a)(1)]

C.1 Particulate Emission Limitations For Processes with Process Weight Rates Less Than One Hundred (100) Pounds per Hour [326 IAC 6-3-2] C.2 Permit Revocation [326 IAC 2-1.1-9] C.3 Opacity [326 IAC 5-1] C.4 Open Burning [326 IAC 4-1] [IC 13-17-9] C.5 Incineration [326 IAC 4-2] [326 IAC 9-1-2] C.6 Fugitive Dust Emissions [326 IAC 6-4] C.7 Fugitive Particulate Matter Emission Limitations [326 IAC 6-5] C.8 Stack Height [326 IAC 1-7] C.9 Asbestos Abatement Projects [326 IAC 14-10] [326 IAC 18] [40 CFR 61, Subpart M]

Testing Requirements [326 IAC 2-6.1-5(a)(2)]

C.10 Performance Testing [326 IAC 3-6] Compliance Requirements [326 IAC 2-1.1-11]

C.11 Compliance Requirements [326 IAC 2-1.1-11] Compliance Monitoring Requirements [326 IAC 2-6.1-5(a)(2)]

C.12 Compliance Monitoring [326 IAC 2-1.1-11] C.13 Instrument Specifications [326 IAC 2-1.1-11]

Corrective Actions and Response Steps

C.14 Response to Excursions or Exceedances C.15 Actions Related to Noncompliance Demonstrated by a Stack Test

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Superior Hardwoods Administrative Amendment No. 121-35251-00020 Page 3 of 30 Montezuma, Indiana Revised by: Brian Wright M121-33610-00020 Permit Reviewer: Heath Hartley

Record Keeping and Reporting Requirements [326 IAC 2-6.1-5(a)(2)]

C.16 Malfunctions Report [326 IAC 1-6-2] C.17 General Record Keeping Requirements [326 IAC 2-6.1-5] C.18 General Reporting Requirements [326 IAC 2-1.1-11][326 IAC 2-6.1-2][IC 13-14-1-13]

D.1. EMISSIONS UNIT OPERATION CONDITIONS ................................................................................. 19

Emission Limitations and Standards [326 IAC 2-6.1-5(a)(1)]

D.1.1 Particulate Emission Limitations [326 IAC 6-3-2] D.1.2 Preventive Maintenance Plan [326 IAC 1-6-3]

D.2. EMISSIONS UNIT OPERATION CONDITIONS ................................................................................. 22

Emission Limitations and Standards [326 IAC 2-6.1-5(a)(1)] D.2.1 Particulate Emission Limitations [326 IAC 6-3-2] D.2.2 Particulate Emission Limitations for Sources of Indirect Heating [326 IAC 6-2-4] D.2.3 Preventive Maintenance Plan [326 IAC 1-6-3]

Record Keeping and Reporting Requirements [326 IAC 2-6.1-5(a)(2)]

D.2.4 Record Keeping Requirement E.1. EMISSIONS UNIT OPERATION CONDITIONS.................................................................................24

Emission Limitations and Standards [326 IAC 2-6.1-5(a)(1)] E.1.1 General Provisions Relating to New Source Performance Standards (NSPS) [40 CFR 60,

Subpart A] [326 IAC 12-1] E.1.2 Standard of Performance for Small Industrial-Commercial Institutional Steam Generating

Units [326 IAC 12] [40 CFR 60, Subpart Dc] E.2. EMISSIONS UNIT OPERATION CONDITIONS.................................................................................25

Emission Limitations and Standards [326 IAC 2-6.1-5(a)(1)] E.2.1 General Provisions Relating to National Emission Standards for Hazardous Air Pollutants

(NESHAP) [40 CFR 63, Subpart A] [326 IAC 20-1] E.2.2 National Emission Standards for Hazardous Air Pollutants (NESHAP) for Industrial,

Commercial, and Institutional Boilers Area Sources [40 CFR 63, Subpart JJJJJJ] E.3. EMISSIONS UNIT OPERATION CONDITIONS.................................................................................26

Emission Limitations and Standards [326 IAC 2-6.1-5(a)(1)] E.3.1 General Provisions Relating to National Emission Standards for Hazardous Air Pollutants

(NESHAP) [40 CFR 63, Subpart A] [326 IAC 20-1] E.3.2 Gasoline Dispensing Facilities NESHAP [40 CFR Part 63, Subpart CCCCCC]

Annual Notification ...................................................................................................................................... 27 Malfunction Report ...................................................................................................................................... 28 Affidavit of Construction .............................................................................................................................. 30

Attachment A – Fugitive Dust Control Plan Attachment B – 40 CFR 60, Subpart Dc Attachment C – 40 CFR 63, Subpart JJJJJJ Attachment D – 40 CFR 63, Subpart CCCCCC

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Superior Hardwoods Administrative Amendment No. 121-35251-00020 Page 4 of 30 Montezuma, Indiana Revised by: Brian Wright M121-33610-00020 Permit Reviewer: Heath Hartley SECTION A SOURCE SUMMARY

This permit is based on information requested by the Indiana Department of Environmental Management (IDEM), Office of Air Quality (OAQ). The information describing the source contained in conditions A.1 and A.2 is descriptive information and does not constitute enforceable conditions. However, the Permittee should be aware that a physical change or a change in the method of operation that may render this descriptive information obsolete or inaccurate may trigger requirements for the Permittee to obtain additional permits or seek modification of this permit pursuant to 326 IAC 2, or change other applicable requirements presented in the permit application. A.1 General Information [326 IAC 2-5.1-3(c)][326 IAC 2-6.1-4(a)]

The Permittee owns and operates a stationary sawmill and planing mill.

Source Address: 6429 W. 100 N., Montezuma, Indiana 47862 General Source Phone Number: (765) 245-2634 SIC Code: 2421 (Sawmills & Planing Mills, General),

2435 (Hardwood Veneer and Plywood) County Location: Parke Source Location Status: Attainment for all criteria pollutants Source Status: Minor Source Operating Permit Program Minor Source, under PSD and Emission Offset Rules

Minor Source, Section 112 of the Clean Air Act Not 1 of 28 Source Categories

A.2 Emission Units and Pollution Control Equipment Summary

This stationary source consists of the following emission units and pollution control devices:

(a) One woodworking operation, identified as AA1, consisting of the following operations:

(1) One (1) Debarker, identified as AA1-DB1, constructed in 1981, located in the Old Mill, with a maximum capacity of 2,820 bd-ft/hr (4.32 ton/hr).

(2) One (1) Head Saw, identified as AA1-HS1, constructed in 1994, located in the

Old Mill, with a maximum capacity of 2,820 bd-ft/hr (4.32 ton/hr), controlled by Cyclone C1 (exhausting outdoors) with collected wood emptied into the Silo.

(3) One (1) Edger, identified as AA1-E1, constructed in 2012, located in the Old Mill,

with a maximum capacity of 2,820 bd-ft/hr (4.32 ton/hr), controlled by Cyclone C1 (exhausting outdoors) with collected wood emptied into the Silo.

(4) One (1) Chipper, identified as AA1-C1, constructed in 2002, located in the Old

Mill, with a maximum capacity of 2,820 bd-ft/hr (4.32 ton/hr), with wood chips collected in a pile on ground and then loaded into a trailer and taken offsite, controlled by Cyclone C1 (exhausting outdoors) with collected wood emptied into the Silo.

(5) One (1) Debarker, identified as AA1-DB2, constructed in 2007 and approved in

2014 for replacement, located in the New Mill, with a maximum capacity of 9,719 bd-ft/hr (13.43 ton/hr).

(6) One (1) Head Saw, identified as AA1-HS2, constructed in 2007, located in the

New Mill, with a maximum capacity of 7,531 bd-ft/hr (10.41 ton/hr), controlled by Cyclone C1 (exhausting outdoors) with collected wood emptied into the Silo.

(7) One (1) Edger, identified as AA1-E2, constructed in 2007, located in the New

Mill, with a maximum capacity of 9,719 bd-ft/hr (13.43 ton/hr), controlled by Cyclone C1 (exhausting outdoors) with collected wood emptied into the Silo.

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Superior Hardwoods Administrative Amendment No. 121-35251-00020 Page 5 of 30 Montezuma, Indiana Revised by: Brian Wright M121-33610-00020 Permit Reviewer: Heath Hartley

(8) Two (2) Resaws, identified as AA1-RS1, constructed in 2007 and approved in

2014 for replacement, located in the New Mill, with a maximum capacity of 9,719 bd-ft/hr (13.43 ton/hr), controlled by Cyclone C1 (exhausting outdoors) with collected wood emptied into the Silo.

(9) One (1) Chipper, identified as AA1-C2, constructed in 2007, located in the New

Mill, with a maximum capacity of 9,719 bd-ft/hr (13.43 ton/hr), with wood chips blown into a trailer and then taken offsite, controlled by Cyclone C1 (exhausting outdoors) with collected wood emptied into the Silo.

(10) One (1) Grade Sorter, Trimmer & Stacker, identified as AA1-ST, constructed in

2002, with a maximum capacity of (7.84 ton/hr), with wood chips collected in a pile on floor and then loaded into a trailer and taken offsite, controlled by Cyclone C2 (exhausting outdoors) with wood collected in a bin and taken offsite.

(11) One (1) Chop Saw, identified as AA1-CS1, constructed in 2010, located in the

Dryline Building, with a maximum capacity of (2.10 ton/hr), controlled by Cyclone C3 (exhausting outdoors) with wood collected in a bin and taken offsite.

(12) One (1) Rip Saw, identified as AA1-RS1, constructed in 2007, located in the

Dryline Building, with a maximum capacity of (2.10 ton/hr), controlled by Cyclone C3 (exhausting outdoors) with wood collected in a bin and taken offsite.

(13) One (1) Planer, identified as AA1-P, constructed in 1999, located in the Planer

Building, with a maximum capacity of (3.16 ton/hr), controlled by Cyclone C1 (exhausting outdoors) with collected wood emptied into the Silo.

(14) One (1) Chop Saw, identified as AA1-CS2, constructed in 2010, located in the

Planer Building, with a maximum capacity of (3.16 ton/hr), controlled by Cyclone C1 (exhausting outdoors) with collected wood emptied into the Silo.

(15) One (1) Rip Saw, identified as AA1-RS2, constructed in 1999, located in the

Planer Building, with a maximum capacity of (3.16 ton/hr), controlled by Cyclone C1 (exhausting outdoors) with collected wood emptied into the Silo.

(16) One (1) Head Saw, approved in 2014 for construction, located in the New Mill,

with a maximum capacity of 2,188 bd-ft/hr (3.02 ton/hr), controlled by Cyclone C1 (exhausting outdoors), with collected wood emptied into the Silo.

(b) One (1) Silo, constructed in 2004, identified as Silo, with storage capacity of 88 tons and

a filling rate of 7.33 tons per hour. The Silo transfers sawdust pneumatically to an auger system and then transferred to the wood-fired boiler.

(c) One (1) wood waste handling operation, identified as WWH1, located in the Old Mill, with

a maximum capacity of 1.38 ton/hr. (d) One (1) wood waste handling operation, identified as WWH2, located in the New Mill,

with a maximum capacity of 6.46 ton/hr. (e) Veneer Operations, consisting of the following:

(1) One (1) Lumber Soaking Operation, approved in 2014 for construction, with a

maximum capacity of 425.6 bd-ft/hr (0.42 ton/hr), using no control, and exhausting indoors.

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(2) One (1) Veneer Slicing Operation, approved in 2014 for construction, with a maximum capacity of 425.6 bd-ft/hr (0.42 ton/hr), using no control, and exhausting indoors.

(3) One (1) Veneer Drying Operation, approved in 2014 for construction, with a

maximum capacity of 425.6 bd-ft/hr (0.42 ton/hr), using no control, and vented to a stack.

(f) One (1) End Wax Operation, identified as AA6, constructed in 1977, with a maximum

capacity of 0.85 gallons of wax per hour, using one (1) high volume low pressure (HVLP) spray applicator application, using dry filters for particulate control and exhausting outdoors.

(g) Eleven (11) kilns, identified as AA5, constructed between 1978 and 2006, heated with

steam from the wood waste boiler AA2, each with a maximum capacity of 0.48 ton/hr, and exhausting to vents V1-V11.

(h) Four (4) kilns, approved in 2014 for construction, heated with steam from the wood waste

boiler AA2, each with a maximum capacity of 0.21 ton/hr, using no control, and exhausting to vents.

(i) One (1) End Paint Operation, identified as AA7, constructed in 1977, with a maximum

capacity of 0.205 gallons of coating per hour, using one (1) high volume low pressure (HVLP) spray applicator application, using no control and exhausting outdoors.

(j) One (1) wood-fired boiler, identified as AA2, constructed in 2000 and approved in 2014

for modification, with a maximum heat input capacity of 12.42 MMBtu per hour and a maximum capacity of 1,616 pounds of wood waste per hour, and exhausting to stack S1. The fly ash is re-injected back into the boiler. This boiler provides steam for the kilns.

This boiler is an affected unit under the provisions of 40 CFR 60, Subpart Dc, and 40 CFR 63, Subpart JJJJJJ. Note: The Permittee will only combust clean wood in the wood-fired boiler (AA2). Clean wood consists of uncoated, unpainted, and untreated wood scrap, sawdust, chips, millings or shavings, and natural growth wood materials. Clean wood does not include wood products that have been painted, pigment-stained, or pressure treated by compounds such as chromate copper arsenate, pentachlorophenol, and creosote, or manufactured wood products that contain adhesives or resins (e.g., plywood, particle board, flake board, and oriented strand board).

(k) One (1) natural gas-fired boiler, identified as AA3, constructed in 1999, with a maximum

heat input of 8.28 MMBtu per hour exhausting through stack S2.

(l) Three (3) wood-fired stoves, identified as AA4, constructed in 2007, each with a maximum heat input of 0.15 MMBtu per hour exhausting through stacks S3, S4 and S5, respectively.

(m) One (1) Veneer Operations natural gas-fired boiler, approved in 2015 for construction,

with a maximum heat input capacity of 10.043 MMBtu/hr, using no control, and vented to a stack.

The boiler is an affected unit under the provisions of 40 CFR 60, Subpart Dc.

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(n) Welding operations for maintenance as follows:

(1) Submerged Arc welders (2) Stick welders (3) Four (4) Oxyacetylene flame-cutting stations

(o) One (1) gasoline fuel transfer and dispensing operation, with a storage capacity of 500

gallons and an annual throughput of 6000 gallons.

Under 40 CFR 63, Subpart CCCCCC, the gasoline fuel transfer and dispensing operation is considered an affected facility.

(p) One (1) diesel fuel transfer and dispensing operation, with a storage capacity of 2,000

gallons and an annual throughput of 24,000 gallons. (q) Two (2) 1,000 gallon diesel storage tanks, installed in 1999 and 2005. (r) One (1) 500 gallon gasoline storage tank, installed in 2000. (s) One (1) 1,000 gallon hydraulic oil storage tank, installed in 2004. (t) Two (2) 350 gallon motor oil storage tanks installed in 2008. (u) Unpaved roads (v) Blowdown for the following: Boiler.

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Superior Hardwoods Administrative Amendment No. 121-35251-00020 Page 8 of 30 Montezuma, Indiana Revised by: Brian Wright M121-33610-00020 Permit Reviewer: Heath Hartley SECTION B GENERAL CONDITIONS

B.1 Definitions [326 IAC 2-1.1-1] Terms in this permit shall have the definition assigned to such terms in the referenced regulation. In the absence of definitions in the referenced regulation, the applicable definitions found in the statutes or regulations (IC 13-11, 326 IAC 1-2 and 326 IAC 2-1.1-1) shall prevail.

B.2 Reserved B.3 Affidavit of Construction [326 IAC 2-5.1-3(h)] [326 IAC 2-5.1-4]

This document shall also become the approval to operate pursuant to 326 IAC 2-5.1-4 when the following requirements are met: (a) The attached Affidavit of Construction shall be submitted to the Office of Air Quality

(OAQ), verifying that the emission units were constructed as described in the application or the permit. The emission units covered in this permit may continue operating on the date the Affidavit of Construction is postmarked or hand delivered to IDEM if constructed as described.

(b) If actual construction of the emission units differs from the construction described in the

application, the source may not continue operation until the permit has been revised pursuant to 326 IAC 2 and an Operation Permit Validation Letter is issued.

(c) The Permittee shall attach the Operation Permit Validation Letter received from the Office

of Air Quality (OAQ) to this permit. B.4 Permit Term [326 IAC 2-6.1-7(a)][326 IAC 2-1.1-9.5][IC 13-15-3-6(a)]

(a) This permit, M121-33610-00020, is issued for a fixed term of five (5) years from the issuance date of this permit, as determined in accordance with IC 4-21.5-3-5(f) and IC 13-15-5-3. Subsequent revisions, modifications, or amendments of this permit do not affect the expiration date of this permit.

(b) If IDEM, OAQ, upon receiving a timely and complete renewal permit application, fails to

issue or deny the permit renewal prior to the expiration date of this permit, this existing permit shall not expire and all terms and conditions shall continue in effect, until the renewal permit has been issued or denied.

B.5 Term of Conditions [326 IAC 2-1.1-9.5]

Notwithstanding the permit term of a permit to construct, a permit to operate, or a permit modification, any condition established in a permit issued pursuant to a permitting program approved in the state implementation plan shall remain in effect until:

(a) the condition is modified in a subsequent permit action pursuant to Title I of the Clean Air

Act; or (b) the emission unit to which the condition pertains permanently ceases operation.

B.6 Enforceability Unless otherwise stated, all terms and conditions in this permit, including any provisions designed to limit the source's potential to emit, are enforceable by IDEM, the United States Environmental Protection Agency (U.S. EPA) and by citizens in accordance with the Clean Air Act.

B.7 Severability The provisions of this permit are severable; a determination that any portion of this permit is invalid shall not affect the validity of the remainder of the permit.

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Superior Hardwoods Administrative Amendment No. 121-35251-00020 Page 9 of 30 Montezuma, Indiana Revised by: Brian Wright M121-33610-00020 Permit Reviewer: Heath Hartley B.8 Property Rights or Exclusive Privilege

This permit does not convey any property rights of any sort or any exclusive privilege. B.9 Duty to Provide Information

(a) The Permittee shall furnish to IDEM, OAQ, within a reasonable time, any information that IDEM, OAQ may request in writing to determine whether cause exists for modifying, revoking and reissuing, or terminating this permit, or to determine compliance with this permit. Upon request, the Permittee shall also furnish to IDEM, OAQ copies of records required to be kept by this permit.

(b) For information furnished by the Permittee to IDEM, OAQ, the Permittee may include a claim of confidentiality in accordance with 326 IAC 17.1. When furnishing copies of requested records directly to U. S. EPA, the Permittee may assert a claim of confidentiality in accordance with 40 CFR 2, Subpart B.

B.10 Annual Notification [326 IAC 2-6.1-5(a)(5)]

(a) An annual notification shall be submitted by an authorized individual to the Office of Air Quality stating whether or not the source is in operation and in compliance with the terms and conditions contained in this permit.

(b) The annual notice shall be submitted in the format attached no later than March 1 of each

year to: Indiana Department of Environmental Management Compliance and Enforcement Branch, Office of Air Quality 100 North Senate Avenue MC 61-53 IGCN 1003 Indianapolis, Indiana 46204-2251

(c) The notification shall be considered timely if the date postmarked on the envelope or certified mail receipt, or affixed by the shipper on the private shipping receipt, is on or before the date it is due. If the document is submitted by any other means, it shall be considered timely if received by IDEM, OAQ on or before the date it is due.

B.11 Preventive Maintenance Plan [326 IAC 1-6-3]

(a) If required by specific condition(s) in Section D of this permit, the Permittee shall prepare and maintain Preventive Maintenance Plans (PMPs) no later than ninety (90) days after issuance of this permit or ninety (90) days after initial start-up, whichever is later, including the following information on each facility:

(1) Identification of the individual(s) responsible for inspecting, maintaining, and

repairing emission control devices; (2) A description of the items or conditions that will be inspected and the inspection

schedule for said items or conditions; and (3) Identification and quantification of the replacement parts that will be maintained

in inventory for quick replacement. If, due to circumstances beyond the Permittee’s control, the PMPs cannot be prepared and maintained within the above time frame, the Permittee may extend the date an additional ninety (90) days provided the Permittee notifies:

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Indiana Department of Environmental Management Compliance and Enforcement Branch, Office of Air Quality 100 North Senate Avenue MC 61-53 IGCN 1003 Indianapolis, Indiana 46204-2251 The Permittee shall implement the PMPs.

(b) A copy of the PMPs shall be submitted to IDEM, OAQ upon request and within a reasonable time, and shall be subject to review and approval by IDEM, OAQ. IDEM, OAQ may require the Permittee to revise its PMPs whenever lack of proper maintenance causes or is the primary contributor to an exceedance of any limitation on emissions.

(c) To the extent the Permittee is required by 40 CFR Part 60/63 to have an Operation Maintenance, and Monitoring (OMM) Plan for a unit, such Plan is deemed to satisfy the PMP requirements of 326 IAC 1-6-3 for that unit.

B.12 Prior Permits Superseded [326 IAC 2-1.1-9.5]

(a) All terms and conditions of permits established prior to M121-33610-00020 and issued pursuant to permitting programs approved into the state implementation plan have been either: (1) incorporated as originally stated, (2) revised, or (3) deleted.

(b) All previous registrations and permits are superseded by this permit.

B.13 Termination of Right to Operate [326 IAC 2-6.1-7(a)] The Permittee's right to operate this source terminates with the expiration of this permit unless a timely and complete renewal application is submitted at least one hundred twenty (120) days prior to the date of expiration of the source’s existing permit, consistent with 326 IAC 2-6.1-7.

B.14 Permit Renewal [326 IAC 2-6.1-7]

(a) The application for renewal shall be submitted using the application form or forms prescribed by IDEM, OAQ and shall include the information specified in 326 IAC 2-6.1-7. Such information shall be included in the application for each emission unit at this source. The renewal application does require an affirmation that the statements in the application are true and complete by an "authorized individual" as defined by 326 IAC 2-1.1-1(1). Request for renewal shall be submitted to: Indiana Department of Environmental Management Permit Administration and Support Section, Office of Air Quality 100 North Senate Avenue MC 61-53 IGCN 1003 Indianapolis, Indiana 46204-2251

(b) A timely renewal application is one that is:

(1) Submitted at least one hundred twenty (120) days prior to the date of the expiration of this permit; and

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(2) If the date postmarked on the envelope or certified mail receipt, or affixed by the shipper on the private shipping receipt, is on or before the date it is due. If the document is submitted by any other means, it shall be considered timely if received by IDEM, OAQ on or before the date it is due.

(c) If the Permittee submits a timely and complete application for renewal of this permit, the

source’s failure to have a permit is not a violation of 326 IAC 2-6.1 until IDEM, OAQ takes final action on the renewal application, except that this protection shall cease to apply if, subsequent to the completeness determination, the Permittee fails to submit by the deadline specified, pursuant to 326 IAC 2-6.1-4(b), in writing by IDEM, OAQ any additional information identified as being needed to process the application.

B.15 Permit Amendment or Revision [326 IAC 2-5.1-3(e)(3)][326 IAC 2-6.1-6] (a) Permit amendments and revisions are governed by the requirements of 326 IAC 2-6.1-6

whenever the Permittee seeks to amend or modify this permit.

(b) Any application requesting an amendment or modification of this permit shall be submitted to: Indiana Department of Environmental Management Permit Administration and Support Section, Office of Air Quality 100 North Senate Avenue MC 61-53 IGCN 1003 Indianapolis, Indiana 46204-2251

(c) The Permittee shall notify the OAQ no later than thirty (30) calendar days of implementing a notice-only change. [326 IAC 2-6.1-6(d)]

B.16 Source Modification Requirement

A modification, construction, or reconstruction is governed by the requirements of 326 IAC 2.

B.17 Inspection and Entry [326 IAC 2-5.1-3(e)(4)(B)][326 IAC 2-6.1-5(a)(4)][IC 13-14-2-2][IC 13-17-3-2][IC 13-30-3-1] Upon presentation of proper identification cards, credentials, and other documents as may be required by law, and subject to the Permittee’s right under all applicable laws and regulations to assert that the information collected by the agency is confidential and entitled to be treated as such, the Permittee shall allow IDEM, OAQ, U.S. EPA, or an authorized representative to perform the following:

(a) Enter upon the Permittee's premises where a permitted source is located, or emissions

related activity is conducted, or where records must be kept under the conditions of this permit;

(b) As authorized by the Clean Air Act, IC 13-14-2-2, IC 13-17-3-2, and IC 13-30-3-1, have access to and copy, at reasonable times, any records that must be kept under the conditions of this permit;

(c) As authorized by the Clean Air Act, IC 13-14-2-2, IC 13-17-3-2, and IC 13-30-3-1, inspect, at reasonable times, any facilities, equipment (including monitoring and air pollution control equipment), practices, or operations regulated or required under this permit;

(d) As authorized by the Clean Air Act, IC 13-14-2-2, IC 13-17-3-2, and IC 13-30-3-1, sample or monitor, at reasonable times, substances or parameters for the purpose of assuring compliance with this permit or applicable requirements; and

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(e) As authorized by the Clean Air Act, IC 13-14-2-2, IC 13-17-3-2, and IC 13-30-3-1, utilize any photographic, recording, testing, monitoring, or other equipment for the purpose of assuring compliance with this permit or applicable requirements.

B.18 Transfer of Ownership or Operational Control [326 IAC 2-6.1-6]

(a) The Permittee must comply with the requirements of 326 IAC 2-6.1-6 whenever the Permittee seeks to change the ownership or operational control of the source and no other change in the permit is necessary.

(b) Any application requesting a change in the ownership or operational control of the source shall contain a written agreement containing a specific date for transfer of permit responsibility, coverage and liability between the current and new Permittee. The application shall be submitted to: Indiana Department of Environmental Management Permit Administration and Support Section, Office of Air Quality 100 North Senate Avenue MC 61-53 IGCN 1003 Indianapolis, Indiana 46204-2251 The application which shall be submitted by the Permittee does require an affirmation that the statements in the application are true and complete by an "authorized individual" as defined by 326 IAC 2-1.1-1(1).

(c) The Permittee may implement notice-only changes addressed in the request for a notice-only change immediately upon submittal of the request. [326 IAC 2-6.1-6(d)(3)]

B.19 Annual Fee Payment [326 IAC 2-1.1-7]

(a) The Permittee shall pay annual fees due no later than thirty (30) calendar days of receipt of a bill from IDEM, OAQ,.

(b) The Permittee may call the following telephone numbers: 1-800-451-6027 or

317-233-4230 (ask for OAQ, Billing, Licensing, and Training Section), to determine the appropriate permit fee.

B.20 Credible Evidence [326 IAC 1-1-6]

For the purpose of submitting compliance certifications or establishing whether or not the Permittee has violated or is in violation of any condition of this permit, nothing in this permit shall preclude the use, including the exclusive use, of any credible evidence or information relevant to whether the Permittee would have been in compliance with the condition of this permit if the appropriate performance or compliance test or procedure had been performed.

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Superior Hardwoods Administrative Amendment No. 121-35251-00020 Page 13 of 30 Montezuma, Indiana Revised by: Brian Wright M121-33610-00020 Permit Reviewer: Heath Hartley SECTION C SOURCE OPERATION CONDITIONS

Entire Source

Emission Limitations and Standards [326 IAC 2-6.1-5(a)(1)]

C.1 Particulate Emission Limitations For Processes with Process Weight Rates Less Than One Hundred (100) Pounds per Hour [326 IAC 6-3-2] Pursuant to 326 IAC 6-3-2(e)(2), particulate emissions from any process not exempt under 326 IAC 6-3-1(b) or (c) which has a maximum process weight rate less than 100 pounds per hour and the methods in 326 IAC 6-3-2(b) through (d) do not apply shall not exceed 0.551 pounds per hour.

C.2 Permit Revocation [326 IAC 2-1.1-9] Pursuant to 326 IAC 2-1.1-9 (Revocation of Permits), this permit to construct and operate may be revoked for any of the following causes:

(a) Violation of any conditions of this permit.

(b) Failure to disclose all the relevant facts, or misrepresentation in obtaining this permit.

(c) Changes in regulatory requirements that mandate either a temporary or permanent

reduction of discharge of contaminants. However, the amendment of appropriate sections of this permit shall not require revocation of this permit.

(d) Noncompliance with orders issued pursuant to 326 IAC 1-5 (Episode Alert Levels) to

reduce emissions during an air pollution episode.

(e) For any cause which establishes in the judgment of IDEM, the fact that continuance of this permit is not consistent with purposes of this article.

C.3 Opacity [326 IAC 5-1]

Pursuant to 326 IAC 5-1-2 (Opacity Limitations), except as provided in 326 IAC 5-1-1 (Applicability) and 326 IAC 5-1-3 (Temporary Alternative Opacity Limitations), opacity shall meet the following, unless otherwise stated in this permit:

(a) Opacity shall not exceed an average of forty percent (40%) in any one (1) six (6) minute

averaging period as determined in 326 IAC 5-1-4.

(b) Opacity shall not exceed sixty percent (60%) for more than a cumulative total of fifteen (15) minutes (sixty (60) readings as measured according to 40 CFR 60, Appendix A, Method 9 or fifteen (15) one (1) minute nonoverlapping integrated averages for a continuous opacity monitor) in a six (6) hour period.

C.4 Open Burning [326 IAC 4-1] [IC 13-17-9] The Permittee shall not open burn any material except as provided in 326 IAC 4-1-3, 326 IAC 4-1-4 or 326 IAC 4-1-6. The previous sentence notwithstanding, the Permittee may open burn in accordance with an open burning approval issued by the Commissioner under 326 IAC 4-1-4.1.

C.5 Incineration [326 IAC 4-2] [326 IAC 9-1-2]

The Permittee shall not operate an incinerator except as provided in 326 IAC 4-2 or in this permit. The Permittee shall not operate a refuse incinerator or refuse burning equipment except as provided in 326 IAC 9-1-2 or in this permit.

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Superior Hardwoods Administrative Amendment No. 121-35251-00020 Page 14 of 30 Montezuma, Indiana Revised by: Brian Wright M121-33610-00020 Permit Reviewer: Heath Hartley C.6 Fugitive Dust Emissions [326 IAC 6-4]

The Permittee shall not allow fugitive dust to escape beyond the property line or boundaries of the property, right-of-way, or easement on which the source is located, in a manner that would violate 326 IAC 6-4 (Fugitive Dust Emissions).

C.7 Fugitive Particulate Matter Emission Limitations [326 IAC 6-5]

Pursuant to 326 IAC 6-5 (Fugitive Particulate Matter Emission Limitations), fugitive particulate matter emissions shall be controlled according to the attached plan as in Attachment A.

C.8 Stack Height [326 IAC 1-7]

The Permittee shall comply with the applicable provisions of 326 IAC 1-7 (Stack Height Provisions), for all exhaust stacks through which a potential (before controls) of twenty-five (25) tons per year or more of particulate matter or sulfur dioxide is emitted.

C.9 Asbestos Abatement Projects [326 IAC 14-10] [326 IAC 18] [40 CFR 61, Subpart M]

(a) Notification requirements apply to each owner or operator. If the combined amount of regulated asbestos containing material (RACM) to be stripped, removed or disturbed is at least 260 linear feet on pipes or 160 square feet on other facility components, or at least thirty-five (35) cubic feet on all facility components, then the notification requirements of 326 IAC 14-10-3 are mandatory. All demolition projects require notification whether or not asbestos is present.

(b) The Permittee shall ensure that a written notification is sent on a form provided by the Commissioner at least ten (10) working days before asbestos stripping or removal work or before demolition begins, per 326 IAC 14-10-3, and shall update such notice as necessary, including, but not limited to the following: (1) When the amount of affected asbestos containing material increases or

decreases by at least twenty percent (20%); or (2) If there is a change in the following:

(A) Asbestos removal or demolition start date;

(B) Removal or demolition contractor; or

(C) Waste disposal site.

(c) The Permittee shall ensure that the notice is postmarked or delivered according to the guidelines set forth in 326 IAC 14-10-3(2).

(d) The notice to be submitted shall include the information enumerated in 326 IAC 14-10-3(3). All required notifications shall be submitted to: Indiana Department of Environmental Management Compliance and Enforcement Branch, Office of Air Quality 100 North Senate Avenue MC 61-53 IGCN 1003 Indianapolis, Indiana 46204-2251 The notice shall include a signed certification from the owner or operator that the information provided in this notification is correct and that only Indiana licensed workers and project supervisors will be used to implement the asbestos removal project.

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(e) Procedures for Asbestos Emission Control The Permittee shall comply with the applicable emission control procedures in 326 IAC 14-10-4 and 40 CFR 61.145(c). Per 326 IAC 14-10-1, emission control requirements are applicable for any removal or disturbance of RACM greater than three (3) linear feet on pipes or three (3) square feet on any other facility components or a total of at least 0.75 cubic feet on all facility components.

(f) Demolition and Renovation The Permittee shall thoroughly inspect the affected facility or part of the facility where the demolition or renovation will occur for the presence of asbestos pursuant to 40 CFR 61.145(a).

(g) Indiana Licensed Asbestos Inspector The Permittee shall comply with 326 IAC 14-10-1(a) that requires the owner or operator, prior to a renovation/demolition, to use an Indiana Licensed Asbestos Inspector to thoroughly inspect the affected portion of the facility for the presence of asbestos. The requirement to use an Indiana Licensed Asbestos inspector is not federally enforceable.

Testing Requirements [326 IAC 2-6.1-5(a)(2)]

C.10 Performance Testing [326 IAC 3-6] (a) For performance testing required by this permit, a test protocol, except as provided

elsewhere in this permit, shall be submitted to: Indiana Department of Environmental Management Compliance and Enforcement Branch, Office of Air Quality 100 North Senate Avenue MC 61-53 IGCN 1003 Indianapolis, Indiana 46204-2251 no later than thirty-five (35) days prior to the intended test date.

(b) The Permittee shall notify IDEM, OAQ of the actual test date at least fourteen (14) days prior to the actual test date.

(c) Pursuant to 326 IAC 3-6-4(b), all test reports must be received by IDEM, OAQ not later than forty-five (45) days after the completion of the testing. An extension may be granted by IDEM, OAQ if the Permittee submits to IDEM, OAQ a reasonable written explanation not later than five (5) days prior to the end of the initial forty-five (45) day period.

Compliance Requirements [326 IAC 2-1.1-11]

C.11 Compliance Requirements [326 IAC 2-1.1-11] The commissioner may require stack testing, monitoring, or reporting at any time to assure compliance with all applicable requirements by issuing an order under 326 IAC 2-1.1-11. Any monitoring or testing shall be performed in accordance with 326 IAC 3 or other methods approved by the commissioner or the U. S. EPA.

Compliance Monitoring Requirements [326 IAC 2-6.1-5(a)(2)]

C.12 Compliance Monitoring [326 IAC 2-1.1-11] Compliance with applicable requirements shall be documented as required by this permit. The Permittee shall be responsible for installing any necessary equipment and initiating any required monitoring related to that equipment. All monitoring and record keeping requirements not already legally required shall be implemented when operation begins.

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Superior Hardwoods Administrative Amendment No. 121-35251-00020 Page 16 of 30 Montezuma, Indiana Revised by: Brian Wright M121-33610-00020 Permit Reviewer: Heath Hartley C.13 Instrument Specifications [326 IAC 2-1.1-11]

(a) When required by any condition of this permit, an analog instrument used to measure a parameter related to the operation of an air pollution control device shall have a scale such that the expected maximum reading for the normal range shall be no less than twenty percent (20%) of full scale. The analog instrument shall be capable of measuring values outside of the normal range.

(b) The Permittee may request that the IDEM, OAQ approve the use of an instrument that

does not meet the above specifications provided the Permittee can demonstrate that an alternative instrument specification will adequately ensure compliance with permit conditions requiring the measurement of the parameters.

Corrective Actions and Response Steps

C.14 Response to Excursions or Exceedances Upon detecting an excursion where a response step is required by the D Section or an exceedance of a limitation in this permit: (a) The Permittee shall take reasonable response steps to restore operation of the emissions

unit (including any control device and associated capture system) to its normal or usual manner of operation as expeditiously as practicable in accordance with good air pollution control practices for minimizing excess emissions.

(b) The response shall include minimizing the period of any startup, shutdown or

malfunction. The response may include, but is not limited to, the following: (1) initial inspection and evaluation; (2) recording that operations returned or are returning to normal without operator

action (such as through response by a computerized distribution control system); or

(3) any necessary follow-up actions to return operation to normal or usual manner of

operation. (c) A determination of whether the Permittee has used acceptable procedures in response to

an excursion or exceedance will be based on information available, which may include, but is not limited to, the following: (1) monitoring results; (2) review of operation and maintenance procedures and records; and/or (3) inspection of the control device, associated capture system, and the process.

(d) Failure to take reasonable response steps shall be considered a deviation from the

permit. (e) The Permittee shall record the reasonable response steps taken.

C.15 Actions Related to Noncompliance Demonstrated by a Stack Test

(a) When the results of a stack test performed in conformance with Section C - Performance Testing, of this permit exceed the level specified in any condition of this permit, the Permittee shall submit a description of its response actions to IDEM, OAQ, no later than seventy-five (75) days after the date of the test.

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(b) A retest to demonstrate compliance shall be performed no later than one hundred eighty (180) days after the date of the test. Should the Permittee demonstrate to IDEM, OAQ that retesting in one hundred eighty (180) days is not practicable, IDEM, OAQ may extend the retesting deadline

(c) IDEM, OAQ reserves the authority to take any actions allowed under law in response to noncompliant stack tests.

Record Keeping and Reporting Requirements [326 IAC 2-6.1-5(a)(2)]

C.16 Malfunctions Report [326 IAC 1-6-2] Pursuant to 326 IAC 1-6-2 (Records; Notice of Malfunction):

(a) A record of all malfunctions, including startups or shutdowns of any facility or emission

control equipment, which result in violations of applicable air pollution control regulations or applicable emission limitations shall be kept and retained for a period of three (3) years and shall be made available to the Indiana Department of Environmental Management (IDEM), Office of Air Quality (OAQ) or appointed representative upon request.

(b) When a malfunction of any facility or emission control equipment occurs which lasts more

than one (1) hour, said condition shall be reported to OAQ, using the Malfunction Report Forms (2 pages). Notification shall be made by telephone or facsimile, as soon as practicable, but in no event later than four (4) daytime business hours after the beginning of said occurrence.

(c) Failure to report a malfunction of any emission control equipment shall constitute a

violation of 326 IAC 1-6, and any other applicable rules. Information of the scope and expected duration of the malfunction shall be provided, including the items specified in 326 IAC 1-6-2(a)(1) through (6).

(d) Malfunction is defined as any sudden, unavoidable failure of any air pollution control

equipment, process, or combustion or process equipment to operate in a normal and usual manner. [326 IAC 1-2-39]

C.17 General Record Keeping Requirements [326 IAC 2-6.1-5]

(a) Records of all required monitoring data, reports and support information required by this permit shall be retained for a period of at least five (5) years from the date of monitoring sample, measurement, report, or application. These records shall be physically present or electronically accessible at the source location for a minimum of three (3) years. The records may be stored elsewhere for the remaining two (2) years as long as they are available upon request. If the Commissioner makes a request for records to the Permittee, the Permittee shall furnish the records to the Commissioner within a reasonable time.

(b) Unless otherwise specified in this permit, for all record keeping requirements not already legally required, the Permittee shall be allowed up to ninety (90) days from the date of permit issuance or the date of initial start-up, whichever is later, to begin such record keeping.

C.18 General Reporting Requirements [326 IAC 2-1.1-11] [326 IAC 2-6.1-2] [IC 13-14-1-13] (a) Reports required by conditions in Section D of this permit shall be submitted to:

Indiana Department of Environmental Management Compliance and Enforcement Branch, Office of Air Quality 100 North Senate Avenue MC 61-53 IGCN 1003 Indianapolis, Indiana 46204-2251

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(b) Unless otherwise specified in this permit, any notice, report, or other submission required

by this permit shall be considered timely if the date postmarked on the envelope or certified mail receipt, or affixed by the shipper on the private shipping receipt, is on or before the date it is due. If the document is submitted by any other means, it shall be considered timely if received by IDEM, OAQ on or before the date it is due.

(c) The first report shall cover the period commencing on the date of issuance of this permit

or the date of initial start-up, whichever is later, and ending on the last day of the reporting period. Reporting periods are based on calendar years, unless otherwise specified in this permit. For the purpose of this permit, “calendar year” means the twelve (12) month period from January 1 to December 31 inclusive.

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Superior Hardwoods Administrative Amendment No. 121-35251-00020 Page 19 of 30 Montezuma, Indiana Revised by: Brian Wright M121-33610-00020 Permit Reviewer: Heath Hartley SECTION D.1 EMISSIONS UNIT OPERATION CONDITIONS

Emissions Unit Description: (a) One woodworking operation, identified as AA1, consisting of the following operations:

(1) One (1) Debarker, identified as AA1-DB1, constructed in 1981, located in the Old Mill, with a maximum capacity of 2,820 bd-ft/hr (4.32 ton/hr).

(2) One (1) Head Saw, identified as AA1-HS1, constructed in 1994, located in the Old Mill,

with a maximum capacity of 2,820 bd-ft/hr (4.32 ton/hr), controlled by Cyclone C1 (exhausting outdoors) with collected wood emptied into the Silo.

(3) One (1) Edger, identified as AA1-E1, constructed in 2012, located in the Old Mill, with a

maximum capacity of 2,820 bd-ft/hr (4.32 ton/hr), controlled by Cyclone C1 (exhausting outdoors) with collected wood emptied into the Silo.

(4) One (1) Chipper, identified as AA1-C1, constructed in 2002, located in the Old Mill,

with a maximum capacity of 2,820 bd-ft/hr (4.32 ton/hr), with wood chips collected in a pile on ground and then loaded into a trailer and taken offsite, controlled by Cyclone C1 (exhausting outdoors) with collected wood emptied into the Silo.

(5) One (1) Debarker, identified as AA1-DB2, constructed in 2007 and approved in 2014

for replacement, located in the New Mill, with a maximum capacity of 9,719 bd-ft/hr (13.43 ton/hr).

(6) One (1) Head Saw, identified as AA1-HS2, constructed in 2007, located in the New

Mill, with a maximum capacity of 7,531 bd-ft/hr (10.41 ton/hr), controlled by Cyclone C1 (exhausting outdoors) with collected wood emptied into the Silo.

(7) One (1) Edger, identified as AA1-E2, constructed in 2007, located in the New Mill, with

a maximum capacity of 9,719 bd-ft/hr (13.43 ton/hr), controlled by Cyclone C1 (exhausting outdoors) with collected wood emptied into the Silo.

(8) Two (2) Resaws, identified as AA1-RS1, constructed in 2007 and approved in 2014 for

replacement, located in the New Mill, with a maximum capacity of 9,719 bd-ft/hr (13.43 ton/hr), controlled by Cyclone C1 (exhausting outdoors) with collected wood emptied into the Silo.

(9) One (1) Chipper, identified as AA1-C2, constructed in 2007, located in the New Mill,

with a maximum capacity of 9,719 bd-ft/hr (13.43 ton/hr), with wood chips blown into a trailer and then taken offsite, controlled by Cyclone C1 (exhausting outdoors) with collected wood emptied into the Silo.

(10) One (1) Grade Sorter, Trimmer & Stacker, identified as AA1-ST, constructed in 2002,

with a maximum capacity of (7.84 ton/hr), with wood chips collected in a pile on floor and then loaded into a trailer and taken offsite, controlled by Cyclone C2 (exhausting outdoors) with wood collected in a bin and taken offsite.

(11) One (1) Chop Saw, identified as AA1-CS1, constructed in 2010, located in the Dryline

Building, with a maximum capacity of (2.10 ton/hr), controlled by Cyclone C3 (exhausting outdoors) with wood collected in a bin and taken offsite.

(12) One (1) Rip Saw, identified as AA1-RS1, constructed in 2007, located in the Dryline

Building, with a maximum capacity of (2.10 ton/hr), controlled by Cyclone C3 (exhausting outdoors) with wood collected in a bin and taken offsite.

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(13) One (1) Planer, identified as AA1-P, constructed in 1999, located in the Planer Building, with a maximum capacity of (3.16 ton/hr), controlled by Cyclone C1 (exhausting outdoors) with collected wood emptied into the Silo.

(14) One (1) Chop Saw, identified as AA1-CS2, constructed in 2010, located in the Planer

Building, with a maximum capacity of (3.16 ton/hr), controlled by Cyclone C1 (exhausting outdoors) with collected wood emptied into the Silo.

(15) One (1) Rip Saw, identified as AA1-RS2, constructed in 1999, located in the Planer

Building, with a maximum capacity of (3.16 ton/hr), controlled by Cyclone C1 (exhausting outdoors) with collected wood emptied into the Silo.

(16) One (1) Head Saw, approved in 2014 for construction, located in the New Mill, with a maximum capacity of 2,188 bd-ft/hr (3.02 ton/hr), controlled by Cyclone C1 (exhausting outdoors), with collected wood emptied into the Silo.

(b) One (1) Silo, constructed in 2004, identified as Silo, with storage capacity of 88 tons and a

filling rate of 7.33 tons per hour. The Silo transfers sawdust pneumatically to an auger system and then transferred to the wood-fired boiler.

(c) One (1) wood waste handling operation, identified as WWH1, located in the Old Mill, with a maximum capacity of 1.38 ton/hr.

(d) One (1) wood waste handling operation, identified as WWH2, located in the New Mill, with a maximum capacity of 6.46 ton/hr.

(e) Veneer Operations, consisting of the following:

(1) One (1) Lumber Soaking Operation, approved in 2014 for construction, with a maximum capacity of 425.6 bd-ft/hr (0.42 ton/hr), using no control, and exhausting indoors.

(2) One (1) Veneer Slicing Operation, approved in 2014 for construction, with a maximum

capacity of 425.6 bd-ft/hr (0.42 ton/hr), using no control, and exhausting indoors. (3) One (1) Veneer Drying Operation, approved in 2014 for construction, with a maximum

capacity of 425.6 bd-ft/hr (0.42 ton/hr), using no control, and vented to a stack. (The information describing the process contained in this emissions unit description box is descriptive information and does not constitute enforceable conditions.)

Emission Limitations and Standards [326 IAC 2-6.1-5(a)(1)] D.1.1 Particulate Emission Limitations [326 IAC 6-3-2]

Pursuant to 326 IAC 6-3-2, the particulate emissions from each of the following processes shall not exceed the pounds per hour limit listed in the table below:

Emission Unit

Maximum Process Weight

(tons/hour)

326 IAC 6-3-2 Allowable Particulate

Emission Rate for each unit (lbs/hr)

Wood Waste Handling WWH1 1.38 5.1 Head Saw AA1-HS2 10.41 19.7 Edger AA1-E2 13.43 23.36

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Emission Unit

Maximum Process Weight

(tons/hour)

326 IAC 6-3-2 Allowable Particulate

Emission Rate for each unit (lbs/hr)

Resaws AA1-RS1 13.43 23.36 Chipper AA1-C2 13.43 23.36 Wood Waste Handling WWH2 6.46 14.32 Silo 7.33 15.6 Veneer Drying Operation 0.42 2.29

Interpolation of the data for the process weight rate up to sixty thousand (60,000) pounds per hour shall be accomplished by use of the equation: E = 4.10 P 0.67 where E = rate of emission in pounds per hour and

P = process weight rate in tons per hour D.1.2 Preventive Maintenance Plan [326 IAC 1-6-3]

A Preventive Maintenance Plan is required for these facilities and their control devices. Section B - Preventive Maintenance Plan contains the Permittee's obligation with regard to the preventive maintenance plan required by this condition.

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Superior Hardwoods Administrative Amendment No. 121-35251-00020 Page 22 of 30 Montezuma, Indiana Revised by: Brian Wright M121-33610-00020 Permit Reviewer: Heath Hartley SECTION D.2 EMISSIONS UNIT OPERATION CONDITIONS

Emissions Unit Description: (f) One (1) End Wax Operation, identified as AA6, constructed in 1977, with a maximum capacity

of 0.85 gallons of wax per hour, using one (1) high volume low pressure (HVLP) spray applicator application, using dry filters for particulate control and exhausting outdoors.

(i) One (1) End Paint Operation, identified as AA7, constructed in 1977, with a maximum capacity of 0.205 gallons of coating per hour, using one (1) high volume low pressure (HVLP) spray applicator application, using no control and exhausting outdoors.

(j) One (1) wood-fired boiler, identified as AA2, constructed in 2000 and approved in 2014 for modification, with a maximum heat input capacity of 12.42 MMBtu per hour and a maximum capacity of 1,616 pounds of wood waste per hour, and exhausting to stack S1. The fly ash is re-injected back into the boiler. This boiler provides steam for the kilns. This boiler is an affected unit under the provisions of 40 CFR 60, Subpart Dc, and 40 CFR 63, Subpart JJJJJJ. Note: The Permittee will only combust clean wood in the wood-fired boiler (AA2). Clean wood consists of uncoated, unpainted, and untreated wood scrap, sawdust, chips, millings or shavings, and natural growth wood materials. Clean wood does not include wood products that have been painted, pigment-stained, or pressure treated by compounds such as chromate copper arsenate, pentachlorophenol, and creosote, or manufactured wood products that contain adhesives or resins (e.g., plywood, particle board, flake board, and oriented strand board).

(k) One (1) natural gas-fired boiler, identified as AA3, constructed in 1999, with a maximum heat input of 8.28 MMBtu per hour exhausting through stack S2.

(l) Three (3) wood-fired stoves, identified as AA4, constructed in 2007, each with a maximum heat input of 0.15 MMBtu per hour exhausting through stacks S3, S4 and S5, respectively.

(m) One (1) Veneer Operations natural gas-fired boiler, approved in 2015 for construction, with a

maximum heat input capacity of 10.043 MMBtu/hr, using no control, and vented to a stack.

The boiler is an affected unit under the provisions of 40 CFR 60, Subpart Dc. (The information describing the process contained in this emissions unit description box is descriptive information and does not constitute enforceable conditions.)

Emission Limitations and Standards [326 IAC 2-6.1-5(a)(1)] D.2.1 Particulate Emission Limitations [326 IAC 6-3-2]

Pursuant to 326 IAC 6-3-2(d), particulate from End Wax AA6 shall be controlled by dry particulate filter, waterwash, or an equivalent control device, subject to the following: (a) The Permittee shall operate the control device in accordance with manufacturer’s

specifications. (b) If overspray is visibly detected at the exhaust or accumulates on the ground, the source

shall inspect the control device and do either of the following no later than four (4) hours after such observation:

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(1) Repair control device so that no overspray is visibly detectable at the exhaust or accumulates on the ground.

(2) Operate equipment so that no overspray is visibly detectable at the exhaust or

accumulates on the ground.

If overspray is visibly detected, the source shall maintain a record of the action taken as a result of the inspection, any repairs of the control device, or change in operations, so that overspray is not visibly detected at the exhaust or accumulates on the ground. These records must be maintained for five (5) years.

D.2.2 Particulate Emission Limitations for Sources of Indirect Heating [326 IAC 6-2-4]

(a) Pursuant to 326 IAC 6-2-4, particulate emissions from the natural gas-fired boiler, AA3 shall not exceed 0.6 pounds per million Btu (lb/MMBtu) of heat input.

(b) Pursuant to 326 IAC 6-2-4, particulate emissions from the wood-fired boiler, AA2, shall

not exceed 0.50 pounds per million Btu (lb/MMBtu) of heat input. (c) Pursuant to 326 IAC 6-2-4, particulate emissions from the wood stoves, AA4, shall not

exceed 0.49 pounds per million Btu (lb/MMBtu) of heat input. (d) Pursuant to 326 IAC 6-2-4, particulate emissions from the Veneer Operations natural

gas-fired boiler shall not exceed 0.44 pounds per million Btu (lb/MMBtu) of heat input

These limits are calculated using the following equation:

Pt = 1.09 Q0.26

where: Pt = Pounds of particulate matter (PM) emitted per million British thermal

units (lb/MMBtu) heat input. Q = Total source maximum operating capacity rating in million Btu per hour

(MMBtu/hr) heat input. For Boiler AA3, Q = 8.28 MMBtu per hour For Boiler AA2, Q = 20.7 MMBtu per hour (8.28 + 12.42) For Boiler AA4, Q = 21.15 MMBtu per hour (20.7 + 0.45) For Veneer Operations Boiler, Q = 31.19 MMBtu per hour (21.15 + 10.043)

D.2.3 Preventive Maintenance Plan [326 IAC 1-6-3]

A Preventive Maintenance Plan is required for these facilities and their control devices. Section B - Preventive Maintenance Plan contains the Permittee's obligation with regard to the preventive maintenance plan required by this condition.

Record Keeping and Reporting Requirements [326 IAC 2-6.1-5(a)(2)] D.2.4 Record Keeping Requirements

(a) To document the compliance status with Condition D.2.1, the Permittee shall maintain a record of any actions taken if overspray is visibly detected.

(b) In order to demonstrate that the End Paint AA7 uses less than 5 gallons of paint per day and is exempt from the requirements of 326 IAC 6-3-2(d), the Permittee shall maintain daily records of paint usage for End Paint AA7.

(c) Section C - General Record Keeping Requirements of this permit contains the Permittee’s obligations with regard to the records required by this condition.

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Emissions Unit Description: (j) One (1) wood-fired boiler, identified as AA2, constructed in 2000 and approved in 2014 for

modification, with a maximum heat input capacity of 12.42 MMBtu per hour and a maximum capacity of 1,616 pounds of wood waste per hour, and exhausting to stack S1. The fly ash is re-injected back into the boiler. This boiler provides steam for the kilns. This boiler is an affected unit under the provisions of 40 CFR 60, Subpart Dc, and 40 CFR 63, Subpart JJJJJJ.

Note: The Permittee will only combust clean wood in the wood-fired boiler (AA2). Clean wood consists of uncoated, unpainted, and untreated wood scrap, sawdust, chips, millings or shavings, and natural growth wood materials. Clean wood does not include wood products that have been painted, pigment-stained, or pressure treated by compounds such as chromate copper arsenate, pentachlorophenol, and creosote, or manufactured wood products that contain adhesives or resins (e.g., plywood, particle board, flake board, and oriented strand board).

(m) One (1) Veneer Operations natural gas-fired boiler, approved in 2015 for construction, with a maximum heat input capacity of 10.043 MMBtu/hr, using no control, and vented to a stack. The boiler is an affected unit under the provisions of 40 CFR 60, Subpart Dc.

(The information describing the process contained in this facility description box is descriptive information and does not constitute enforceable conditions.)

Emission Limitations and Standards [326 IAC 2-6.1-5(a)(1)] E.1.1 General Provisions Relating to New Source Performance Standards (NSPS) [40 CFR 60, Subpart

A] [326 IAC 12-1] The provisions of 40 CFR 60, Subpart A - General Provisions, which are incorporated by reference in 326 IAC 12-1, apply to the wood-fired boiler, identified as AA2, and the Veneer Operations natural gas-fired boiler except when otherwise specified in 40 CFR 60, Subpart Dc.

E.1.2 Standard of Performance for Small Industrial-Commercial Institutional Steam Generating Units [326 IAC 12] [40 CFR 60, Subpart Dc] Pursuant to 40 CFR 60 Subpart Dc, the Permittee shall comply with the following provisions of 40 CFR 60, Subpart Dc (included as Attachment B to this permit), which are incorporated as 326 IAC 12, for wood-fired boiler, identified as AA2, and the Veneer Operations natural gas-fired boiler: (1) 40 CFR 60.40c(a), (b) and (c) (2) 40 CFR 60.41c (3) 40 CFR 60.48c(a), (g), and (i)

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Emissions Unit Description: (j) One (1) wood-fired boiler, identified as AA2, constructed in 2000 and approved in 2014 for

modification, with a maximum heat input capacity of 12.42 MMBtu per hour and a maximum capacity of 1,616 pounds of wood waste per hour, and exhausting to stack S1. The fly ash is re-injected back into the boiler. This boiler provides steam for the kilns. This boiler is an affected unit under the provisions of 40 CFR 60, Subpart Dc, and 40 CFR 63, Subpart JJJJJJ.

Note: The Permittee will only combust clean wood in the wood-fired boiler (AA2). Clean wood consists of uncoated, unpainted, and untreated wood scrap, sawdust, chips, millings or shavings, and natural growth wood materials. Clean wood does not include wood products that have been painted, pigment-stained, or pressure treated by compounds such as chromate copper arsenate, pentachlorophenol, and creosote, or manufactured wood products that contain adhesives or resins (e.g., plywood, particle board, flake board, and oriented strand board).

(The information describing the process contained in this facility description box is descriptive information and does not constitute enforceable conditions.)

Emission Limitations and Standards [326 IAC 2-6.1-5(a)(1)] E.2.1 General Provisions Relating to the National Emission Standards for Hazardous Air Pollutants

(NESHAP) [40 CFR Part 63, Subpart A] [326 IAC 20-1] The provisions of 40 CFR 63, Subpart A - General Provisions, which are incorporated by reference as 326 IAC 20-1, apply to the wood-fired boiler, identified as AA2, except when otherwise specified in 40 CFR 63, Subpart JJJJJJ.

E.2.2 National Emission Standards for Hazardous Air Pollutants (NESHAP) for Industrial, Commercial, and Institutional Boilers Area Sources [40 CFR 63, Subpart JJJJJJ] Pursuant to 40 CFR 63 Subpart JJJJJJ, the Permittee shall comply with the provisions of 40 CFR 63, Subpart JJJJJJ (included as Attachment C to this permit), for the wood-fired boiler, identified as AA2, as specified as follows: (1) 40 CFR 63.11193 (2) 40 CFR 63.11194(a),(b),(f) (3) 40 CFR 63.11196(a)(1),(3) (4) 40 CFR 63.11200 (5) 40 CFR 63.11201(b),(d) (6) 40 CFR 63.11205(a) (7) 40 CFR 63.11210(c) (8) 40 CFR 63.11214(b),(c) (9) 40 CFR 63.11223(a),(c)(b) (10) 40 CFR 63.11225(a)(1)(2),(a)(4)(i)-(ii)(iii),(vi) (11) 40 CFR 63.11225(b)(1),(2)(i),(iii),(3) (12) 40 CFR 63.11225(c)(1),(2)(i),(ii),(iii),(4)-(6),(d) (13) 40 CFR 63.11235 (14) 40 CFR 63.11236 (15) 40 CFR 63.11237 (16) Table 2

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Emissions Unit Description: (o) One (1) gasoline fuel transfer and dispensing operation, with a storage capacity of 500 gallons

and an annual throughput of 6000 gallons.

Under 40 CFR 63, Subpart CCCCCC, the gasoline fuel transfer and dispensing operation is considered an affected facility.

(The information describing the process contained in this emissions unit description box is descriptive information and does not constitute enforceable conditions.)

Emission Limitations and Standards [326 IAC 2-6.1-5(a)(1)] E.3.1 General Provisions Relating to the National Emission Standards for Hazardous Air Pollutants

(NESHAP) [40 CFR Part 63, Subpart A] [326 IAC 20-1] The provisions of 40 CFR 63, Subpart A - General Provisions, which are incorporated by reference as 326 IAC 20-1, apply to the gasoline fuel transfer and dispensing operation except when otherwise specified in 40 CFR 63, Subpart CCCCCC.

E.3.2 Gasoline Dispensing Facilities NESHAP [40 CFR Part 63, Subpart CCCCCC]

Pursuant to 40 CFR 63 Subpart CCCCCC, the Permittee shall comply with the provisions of 40 CFR 63, Subpart CCCCCC (included as Attachment D to this permit), for the gasoline dispensing facilities, as specified as follows: (1) 40 CFR 63.11110 (2) 40 CFR 63.11111(a), (b), (e), (f), (h), (i), (j), (k) (3) 40 CFR 63.11112(a), (d) (4) 40 CFR 63.11113(b), (c) (5) 40 CFR 63.11115 (6) 40 CFR 63.11116 (7) 40 CFR 63.11130 (8) 40 CFR 63.11131 (9) 40 CFR 63.11132

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INDIANA DEPARTMENT OF ENVIRONMENTAL MANAGEMENT OFFICE OF AIR QUALITY

COMPLIANCE AND ENFORCEMENT BRANCH

MINOR SOURCE OPERATING PERMIT ANNUAL NOTIFICATION

This form should be used to comply with the notification requirements under 326 IAC 2-6.1-5(a)(5).

Company Name: Superior Hardwoods

Address: 6429 W. 100 N.

City: Montezuma, Indiana 47862

Phone #: (765) 245-2634

MSOP #: M121-33610-00020

I hereby certify that Superior Hardwoods is : still in operation. no longer in operation. I hereby certify that Superior Hardwoods is : in compliance with the requirements of

MSOP M121-33610-00020. not in compliance with the requirements of

MSOP M121-33610-00020.

Authorized Individual (typed):

Title:

Signature:

Date:

If there are any conditions or requirements for which the source is not in compliance, provide a narrative description of how the source did or will achieve compliance and the date compliance was, or will be achieved.

Noncompliance:

Page 35: Notice of Decision: Approvalpermits.air.idem.in.gov/35251f.pdf · 2015. 1. 7. · Permit Number: 121 - 35251 - 00020 . Source Location: 6429 W. 100 N., Montezuma, Indiana . Type of

Superior Hardwoods Administrative Amendment No. 121-35251-00020 Page 28 of 30 Montezuma, Indiana Revised by: Brian Wright M121-33610-00020 Permit Reviewer: Heath Hartley

MALFUNCTION REPORT

INDIANA DEPARTMENT OF ENVIRONMENTAL MANAGEMENT OFFICE OF AIR QUALITY

COMPLIANCE AND ENFORCEMENT BRANCH FAX NUMBER: (317) 233-6865

This form should only be used to report malfunctions applicable to Rule 326 IAC 1-6 and to qualify for the exemption under 326 IAC 1-6-4.

THIS FACILITY MEETS THE APPLICABILITY REQUIREMENTS BECAUSE IT HAS POTENTIAL TO EMIT 25 TONS/YEAR PARTICULATE MATTER ?_____, 25 TONS/YEAR SULFUR DIOXIDE ?_____, 25 TONS/YEAR NITROGEN OXIDES?_____, 25 TONS/YEAR VOC ?_____, 25 TONS/YEAR HYDROGEN SULFIDE ?_____, 25 TONS/YEAR TOTAL REDUCED SULFUR ?_____, 25 TONS/YEAR REDUCED SULFUR COMPOUNDS ?_____, 25 TONS/YEAR FLUORIDES ?_____, 100 TONS/YEAR CARBON MONOXIDE ?_____, 10 TONS/YEAR ANY SINGLE HAZARDOUS AIR POLLUTANT ?_____, 25 TONS/YEAR ANY COMBINATION HAZARDOUS AIR POLLUTANT ?_____, 1 TON/YEAR LEAD OR LEAD COMPOUNDS MEASURED AS ELEMENTAL LEAD ?_____, OR IS A SOURCE LISTED UNDER 326 IAC 2-5.1-3(2) ?_____. EMISSIONS FROM MALFUNCTIONING CONTROL EQUIPMENT OR PROCESS EQUIPMENT CAUSED EMISSIONS IN EXCESS OF APPLICABLE LIMITATION ________. THIS MALFUNCTION RESULTED IN A VIOLATION OF: 326 IAC _______ OR, PERMIT CONDITION # _______ AND/OR PERMIT LIMIT OF _______________ THIS INCIDENT MEETS THE DEFINITION OF “MALFUNCTION” AS LISTED ON REVERSE SIDE ? Y N THIS MALFUNCTION IS OR WILL BE LONGER THAN THE ONE (1) HOUR REPORTING REQUIREMENT ? Y N

COMPANY:_________________________________________________________PHONE NO. ( )___________________ LOCATION: (CITY AND COUNTY)_________________________________________________________________________ PERMIT NO. ________________ AFS PLANT ID: ________________ AFS POINT ID: ________________ INSP:__________ CONTROL/PROCESS DEVICE WHICH MALFUNCTIONED AND REASON:________________________________________ _____________________________________________________________________________________________________ DATE/TIME MALFUNCTION STARTED: _____/_____/ 20____ _________________________________________ AM / PM ESTIMATED HOURS OF OPERATION WITH MALFUNCTION CONDITION: _______________________________________

DATE/TIME CONTROL EQUIPMENT BACK-IN SERVICE______/______/ 20____ _______________ AM/PM

TYPE OF POLLUTANTS EMITTED: TSP, PM-10, SO2, VOC, OTHER:________________________________________ ESTIMATED AMOUNT OF POLLUTANT EMITTED DURING MALFUNCTION: _______________________________________ ______________________________________________________________________________________________________ MEASURES TAKEN TO MINIMIZE EMISSIONS:______________________________________________________________ ___________________________________________________________________________________________________ REASONS WHY FACILITY CANNOT BE SHUTDOWN DURING REPAIRS: CONTINUED OPERATION REQUIRED TO PROVIDE ESSENTIAL* SERVICES:_____________________________________ CONTINUED OPERATION NECESSARY TO PREVENT INJURY TO PERSONS:_____________________________________ CONTINUED OPERATION NECESSARY TO PREVENT SEVERE DAMAGE TO EQUIPMENT:__________________________ INTERIM CONTROL MEASURES: (IF APPLICABLE)____________________________________________________________ _____________________________________________________________________________________________________ _____________________________________________________________________________________________________ MALFUNCTION REPORTED BY:__________________________________TITLE:___________________________ (SIGNATURE IF FAXED) MALFUNCTION RECORDED BY:_______________________DATE:__________________TIME:__________________ *SEE PAGE 2

PAGE 1 OF 2

Page 36: Notice of Decision: Approvalpermits.air.idem.in.gov/35251f.pdf · 2015. 1. 7. · Permit Number: 121 - 35251 - 00020 . Source Location: 6429 W. 100 N., Montezuma, Indiana . Type of

Superior Hardwoods Administrative Amendment No. 121-35251-00020 Page 29 of 30 Montezuma, Indiana Revised by: Brian Wright M121-33610-00020 Permit Reviewer: Heath Hartley

Please note - This form should only be used to report malfunctions applicable to Rule 326 IAC 1-6 and to qualify for

the exemption under 326 IAC 1-6-4.

326 IAC 1-6-1 Applicability of rule Sec. 1. This rule applies to the owner or operator of any facility required to obtain a permit under 326 IAC 2-5.1 or 326 IAC 2-6.1. 326 IAC 1-2-39 “Malfunction” definition Sec. 39. Any sudden, unavoidable failure of any air pollution control equipment, process, or combustion or process equipment to operate in a normal and usual manner. *Essential services are interpreted to mean those operations, such as, the providing of electricity by power plants. Continued operation solely for the economic benefit of the owner or operator shall not be sufficient reason why a facility cannot be shutdown during a control equipment shutdown. If this item is checked on the front, please explain rationale: ________________________________________________________________________ ________________________________________________________________________

PAGE 2 OF 2

Page 37: Notice of Decision: Approvalpermits.air.idem.in.gov/35251f.pdf · 2015. 1. 7. · Permit Number: 121 - 35251 - 00020 . Source Location: 6429 W. 100 N., Montezuma, Indiana . Type of

Superior Hardwoods Administrative Amendment No. 121-35251-00020 Page 30 of 30 Montezuma, Indiana Revised by: Brian Wright M121-33610-00020 Permit Reviewer: Heath Hartley

Mail to: Permit Administration and Support Section Office of Air Quality

100 North Senate Avenue MC 61-53 IGCN 1003

Indianapolis, Indiana 46204-2251

Superior Hardwoods 6429 W. 100 N. Montezuma, Indiana 47862

Affidavit of Construction

I, , being duly sworn upon my oath, depose and say: (Name of the Authorized Representative)

1. I live in County, Indiana and being of sound mind and over twenty-one (21) years of age, I am competent to give this affidavit.

2. I hold the position of for . (Title) (Company Name)

3. By virtue of my position with , I have personal

(Company Name) knowledge of the representations contained in this affidavit and am authorized to make

these representations on behalf of . (Company Name)

4. I hereby certify that Superior Hardwoods 6429 W. 100 N., Montezuma, Indiana 47862, has constructed and will

operate a Sawmill and Planing Mill on in conformity with the requirements and intent of the construction permit application received by the Office of Air Quality on September 4, and as permitted pursuant to New Source Construction Permit and Minor Source Operating Permit No. M121-33610-00020, Plant ID No. 121-00020 issued on .

5. Permittee, please cross out the following statement if it does not apply: Additional (operations/facilities) were constructed/substituted as described in the attachment to this document and were not made in accordance with the construction permit.

Further Affiant said not.

I affirm under penalties of perjury that the representations contained in this affidavit are true, to the best of my information and belief.

Signature Date

STATE OF INDIANA) )SS COUNTY OF )

Subscribed and sworn to me, a notary public in and for County and State of Indiana

on this day of , 20 . My Commission expires: .

Signature Name (typed or printed)

Page 38: Notice of Decision: Approvalpermits.air.idem.in.gov/35251f.pdf · 2015. 1. 7. · Permit Number: 121 - 35251 - 00020 . Source Location: 6429 W. 100 N., Montezuma, Indiana . Type of

App. A to TSD Page 1 of 15

Appendix A: Emission CalculationsEmissions Summary

PTE After Issuance of Revision

Company Name: Superior HardwoodsSource Address: 6429 W. 100 North, Montezuma, IN 47862Permit Number: 121-35251-00020

Reviewer: Brian Wright

Unlimited Potential To Emit (PTE) (tons/yr) (Before Integral Woodworking Controls)

Emission Source PM PM10 PM2.5 SO2 NOx VOC COGHG as

CO2e Total HAPsWoodworking 173.00 86.06 86.06 0.00 0.00 0.00 0.00 0 0.00 0.00End Wax 1.91 1.91 1.91 0.00 0.00 2.15 0.00 0 2.15 2.15 MethanolEnd Paint 0.39 0.39 0.39 0.00 0.00 0.00 0.00 0 0.00 0.00Kilns 0.00 0.00 0.00 0.00 0.00 29.78 3.21 0 4.17 1.85 MethanolWood Waste Boiler 21.76 20.51 17.79 1.36 26.66 0.92 32.64 11,496 1.82 1.03 HClNat Gas Boiler 0.07 0.27 0.27 0.02 3.56 0.20 2.99 4,292 0.07 0.07 HexaneWood Stoves 0.79 0.74 0.64 0.05 0.97 0.03 1.18 417 0.07 0.04 HClWelding 0.04 0.04 0.04 0.00 0.00 0.00 0.00 0 0.00 0.00Gasoline Dispensing Operation 0.00 0.00 0.00 0.00 0.00 0.15 0.00 0 1.86E-03 6.10E-04 TolueneLumber Soaking Operations 0.00 0.00 0.00 0.00 0.00 0.37 0.00 0 0.06 0.04 MethanolVeneer Slicing 0.00 0.00 0.00 0.00 0.00 0.36 0.00 0 0.06 0.04 MethanolVeneer Drying 5.22 5.22 5.22 0.00 0.00 7.76 0.62 0 1.21 0.72 Methanol

New Unit Nat Gas Boiler (Veneer Operations) 0.08 0.33 0.33 0.03 4.31 0.24 3.62 5,206 0.08 0.08 HexaneTotals (Non-Fugitive) 203.26 115.47 112.65 1.46 35.49 41.96 44.27 21,410 9.69 4.75 Methanol

Existing Units Unpaved Roads (fugitive) 499.40 127.28 12.73 0.00 0.00 0.00 0.00 0 0.00 0.00Totals (Fugitive) 499.40 127.28 12.73 0.00 0.00 0.00 0.00 0 0.00 0.00

Total PTE (Non-Fugitive and Fugitive) 702.66 242.75 125.38 1.46 35.49 41.96 44.27 21,410 9.69 4.75 Methanol

Unlimited Potential To Emit (PTE) (tons/yr) (After Integral Woodworking Controls)

Emission Source PM PM10 PM2.5 SO2 NOx VOC COGHG as

CO2e Total HAPsWoodworking 93.27 39.21 39.21 0.00 0.00 0.00 0.00 0 0.00 0.00End Wax 1.91 1.91 1.91 0.00 0.00 2.15 0.00 0 2.15 2.15 MethanolEnd Paint 0.39 0.39 0.39 0.00 0.00 0.00 0.00 0 0.00 0.00Kilns 0.00 0.00 0.00 0.00 0.00 29.78 3.21 0 4.17 1.85 MethanolWood Waste Boiler 21.76 20.51 17.79 1.36 26.66 0.92 32.64 11,496 1.82 1.03 HClNat Gas Boiler 0.07 0.27 0.27 0.02 3.56 0.20 2.99 4,292 0.07 0.07 HexaneWood Stoves 0.79 0.74 0.64 0.05 0.97 0.03 1.18 417 0.07 0.04 HClWelding 0.04 0.04 0.04 0.00 0.00 0.00 0.00 0 0.00 0.00Gasoline Dispensing Operation 0.00 0.00 0.00 0.00 0.00 0.15 0.00 0 1.86E-03 6.10E-04 TolueneLumber Soaking Operations 0.00 0.00 0.00 0.00 0.00 0.37 0.00 0 0.06 0.04 MethanolVeneer Slicing 0.00 0.00 0.00 0.00 0.00 0.36 0.00 0 0.06 0.04 MethanolVeneer Drying 5.22 5.22 5.22 0.00 0.00 7.76 0.62 0 1.21 0.72 Methanol

New Unit Nat Gas Boiler (Veneer Operations) 0.08 0.33 0.33 0.03 4.31 0.24 3.62 5,206 0.08 0.08 HexaneTotals (Non-Fugitive) 123.53 68.62 65.81 1.46 35.49 41.96 44.27 21,410 9.69 4.79 Methanol

Existing Units Unpaved Roads 499.40 127.28 12.73 0.00 0.00 0.00 0.00 0 0.00 0.00Totals (Fugitive) 499.40 127.28 12.73 0.00 0.00 0.00 0.00 0 0.00 0.00

Total PTE (Non-Fugitive and Fugitive) 622.93 195.90 78.53 1.46 35.49 41.96 44.27 21,410 9.69 4.79 Methanol

Single HAP

Single HAP

Existing Units

Existing Units

Page 39: Notice of Decision: Approvalpermits.air.idem.in.gov/35251f.pdf · 2015. 1. 7. · Permit Number: 121 - 35251 - 00020 . Source Location: 6429 W. 100 N., Montezuma, Indiana . Type of

App. A to TSD Page 2 of 15

Appendix A: Emission CalculationsFacility Throughput Calculations

Company Name: Superior HardwoodsSource Address: 6429 W. 100 North, Montezuma, IN 47862Permit Number: 121-35255-00020

Reviewer: Brian WrightActual Throughput

13,809,725 bd-ft Historical Records Old Mill Throughput (2012) 9,813,721 bd-ft Historical Records2,236 hr Historical Records Hours of Operation (2012) 4,242 hr Historical Records

Potential Throughput Calculations

24,000,000 Maximum Facility CapacitySafety Factor 1.2PTE Throughput 28,800,000 bd-ft/yrNew Mill Percentage Throughput 58.46% Historical RecordsNew Mill PTE Throughput 16,835,820 bd-ft/yr Previous ApplicationNew Mill Hours of Operation (2012) 2,236 hr Previous ApplicationNew Mill Capacity 7,531.1 bd-ft/hr Previous Application

Maximum Modification Throughput 700,000 bd-ft/mo Projected Modification CapacityProjected Hours of Operation (2 Shifts) 320 hrs/mo (16 hrs/day x 5 days/wk x 4 wks/yr)Modification Capacity 2,187.5 bd-ft/hr Maximum Modification CapacityConversion Factor 0.083 ft3/bd-ft (1' x 1' x (1/12)' = 0.083ft3

Maximum Facility Throughput 24,000,000 bd-ft/yr Maximum Facility CapacitySafety Factor 1.2PTE Throughput 28,800,000 bd-ft/yrOld Mill Percentage Throughput 41.54% Historical RecordsOld Mill PTE Throughput 11,964,180 bd-ft/yrOld Mill Hours of Operation (2012) 4,242 hr Historical RecordsOld Mill Capacity 2,820 bd-ft/hrConversion Factor 0.083 ft3/bd-ft (1' x 1' x (1/12)' = 0.083ft3

Maximum Veneer Operation Throughput 3,405 bd-ft/shift Projected Modification CapacityProjected Hours of Operation (1 Shift) 8 hrs/shift Hours per shiftModification Capacity @ 3mils 425.6 bd-ft/hr Maximum Modification CapacityConversion Factor 0.083 ft3/bd-ft (1' x 1' x (1/12)' = 0.083ft3

Species Density Densitylb/ft3 kg/m3

% bd-ft/hr ft3/hr ton/hr % bd-ft/hr ft3/hr ton/hrPoplar 26.66 426.56 52% 3,916.2 326.3 4.35 52% 1,137.5 94.8 1.26Ash 39.83 637.28 17% 1,280.3 106.7 2.12 17% 371.9 31.0 0.62Hard Maple 42.2 675.2 11% 828.4 69.0 1.46 11% 240.6 20.1 0.42Red Oak 41.02 656.32 9% 677.8 56.5 1.16 9% 196.9 16.4 0.34Walnut 35.09 561.44 5% 376.6 31.4 0.55 5% 109.4 9.1 0.16White Oak 44.33 709.28 4% 301.2 25.1 0.56 4% 87.5 7.3 0.16Cherry 33.34 533.44 2% 150.6 12.6 0.21 2% 43.8 3.6 0.06Hickory 51.21 819.36 0% 0.0 0.0 0.00 0% 0.0 0.0 0.00Basswood 24.85 397.6 0% 0.0 0.0 0.00 0% 0.0 0.0 0.00Average Density 37.61 601.83Total 7,531.1 627.6 10.41 2,188 182.3 3.02

Total Throughput from New Mill and Modification 13.43 ton/hr 9,719 bd-ft/hr

Species Density Densitylb/ft3 kg/m3

% bd-ft/hr ft3/hr ton/hr % bd-ft/hr ft3/hr ton/hrPoplar 26.66 426.56 0% 0.0 0.0 0.00 42% 1,184.5 98.7 1.32Ash 39.83 637.28 0% 0.0 0.0 0.00 1% 28.2 2.4 0.05Hard Maple 42.2 675.2 0% 0.0 0.0 0.00 4% 112.8 9.4 0.20Red Oak 41.02 656.32 0% 0.0 0.0 0.00 31% 874.3 72.9 1.49Walnut 35.09 561.44 20% 85.1 7.1 0.11 0% 0.0 0.0 0.00White Oak 44.33 709.28 70% 297.9 24.8 0.31 4% 112.8 9.4 0.21Cherry 33.34 533.44 0% 0.0 0.0 0.00 0% 0.0 0.0 0.00Hickory 51.21 819.36 10% 42.6 3.5 0.00 17% 479.4 40.0 1.02Basswood 24.85 397.6 0% 0.0 0.0 0.00 1% 28.2 2.4 0.03Average Density 37.61 601.83Total 425.6 35.5 0.42 2,820.2 235.0 4.3

Old Mill

ThroughputPotential Throughput

ThroughputPotential Throughput

Veneer Throughput

New Mill Modification ThroughputNew Mill

New Mill Throughput (2012)Potential Emissions from Lumber Soaking Operations

Maximum Facility Throughput

OLD MILL (EXISTING)

NEW MILL (EXISTING)

INCREASED THROUGHPUT TO NEW MILL FROM REVISION

VENEER OPERATIONS - NEW WITH REVISION

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App. A to TSD Page 3 of 15

Appendix A: Emission CalculationsWoodworking

Company Name: Superior HardwoodsSource Address: 6429 W. 100 North, Montezuma, IN 47862Permit Number: 121-35255-00020

Reviewer: Brian Wright

Emission Unit Modification Status

Capacity (ton/hr)

PM Emission

Factor (lbs/ton)

PM10/PM2.5 Emission

Factor (lbs/ton)

PM Uncontrolled PTE (lb/hr)

PM Uncontrolled PTE (tons/yr)*

PM10 / PM2.5 Uncontrolled PTE (tons/yr)

Control Device

Control Efficiency

(%)

PM Controlled PTE (lb/hr)

PM Controlled

PTE (tons/yr)

PM10 / PM2.5

Controlled PTE

(tons/yr)Old Mill

Debarker AA1-DB1 Existing 4.32 0.02 0.011 0.09 0.38 0.21 None 0% 0.09 0.38 0.21Head Saw AA1-HS1 Existing 4.32 0.35 0.20 1.51 6.62 3.78 Cyclone C1 81% 0.29 1.27 0.73Edger AA1-E1 Existing 4.32 0.35 0.20 1.51 6.62 3.78 Cyclone C1 81% 0.29 1.27 0.73Chipper AA1-C1 Existing 4.32 0.35 0.20 1.51 6.62 3.78 Cyclone C1 81% 0.29 1.27 0.73Wood Waste Handling WWH1 Existing 1.38 1.00 0.36 1.38 6.04 2.18 None 0% 1.38 6.04 2.18

New Mill (With Modification)Debarker AA1-DB2 To be replaced 13.43 0.02 0.011 0.27 1.18 0.65 None 0% 0.27 1.18 0.65Head Saw AA1-HS2 No physical change 10.41 0.35 0.20 3.64 15.95 9.12 Cyclone C1 81% 0.70 3.07 1.75Head Saw To be added 3.02 0.35 0.20 1.06 4.63 2.65 Cyclone C1 81% 0.20 0.88 0.50Edger AA1-E2 No physical change 13.43 0.35 0.20 4.70 20.59 11.76 Cyclone C1 81% 0.90 3.96 2.26Resaws AA1-RS1 To be replaced 13.43 0.35 0.20 4.70 20.59 11.76 Cyclone C1 81% 0.90 3.96 2.26Chipper AA1-C2 No physical change 13.43 0.35 0.20 4.70 20.59 11.76 Cyclone C1 81% 0.90 3.96 2.26Wood Waste Handling WWH2 No physical change 6.46 1.00 0.36 6.46 28.31 10.19 None 0% 6.46 28.31 10.19Veneer Slicer To be added 0.42 ND ND 0.00 0.00 0.00 None 0% 0.00 0.00 0.00Silo No physical change 7.33 1.00 0.36 7.33 32.11 11.56 None 0% 7.33 32.11 11.56Grade Sorter/Trimmer AA1-ST No physical change 6.96 0.35 0.20 2.44 10.68 6.10 Cyclone C2 81% 0.47 2.06 1.17Dryline chop saw AA1-CS1 No physical change 1.87 0.35 0.20 0.65 2.86 1.64 Cyclone C3 81% 0.13 0.55 0.31Dryline rip saw AA1-RS1 No physical change 1.87 0.35 0.20 0.65 2.86 1.64 Cyclone C3 81% 0.13 0.55 0.31Planer AA1-P No physical change 2.80 0.35 0.20 0.98 4.29 2.45 Cyclone C1 81% 0.19 0.83 0.47Planer chop saw AA1-CS2 No physical change 2.80 0.35 0.20 0.98 4.29 2.45 Cyclone C1 81% 0.19 0.83 0.47Planer rip saw AA1-RS2 No physical change 2.66 0.35 0.20 0.93 4.08 2.33 Cyclone C1 81% 0.18 0.78 0.45

173.00 86.06 93.27 39.21

*Cylcones C1, C2 and C3 have been determined by IDEM to be integral.Emission Factors are from Emission Factors are from FIRE Version 6.23 Uncontrolled Emission Factor Listing for Criteria Air Pollutants, July 2001, for Sawmill Ops.

After the Grade Sorter/Trimmer Stacker, approximately 40% of the product will go to the Dryline and the other 60% to the Planer.

MethodologyUncontrolled PTE = Capacity (ton/hr) x Emission Factor (lbs/ton) x 1 ton / 2000 lbs x 8760 hrs/yrControlled PTE = Capacity (ton/hr) x Emission Factor (lbs/ton) x 1 ton / 2000 lbs x 8760 hrs/yr x (1 - Control Efficiency)

12 truck load X X 50 wk = 600 truck loadweek 1 yr yr

600 truck load X X 41,000 lb = 24,600,000 lbyr 1 truck load yr

24,600,000 lb X X 1 yr = 11,004.25 lbyr 2,235.50 hr hr

11,004.25 lb X X 1 ton = 5.50 tonhr 2000 lb hr

3 truck load X 50 wk = 150 truck loadweek 1 yr yr

150 truck load X 41,000 lb = 6,150,000 lbyr 1 truck load yr

6150000 lb X 1 yr = 2,751.06 lbyr 2,235.50 hr hr

2751.062402 lb X 1 ton = 1.38 tonhr 2000 lb hr

1.38 ton X 3.02 ton/hr = 0.96 tonhr 4.32 ton/hr hr

The maximum throughput of wood (ton/hr) for the Grade Sorter/Trimmer AA1-ST, Dryline and Planer are based on a bottleneck of material processed from the operations in the New Mill.

Maximum Capacity CalculationsWood Waste Handling - New Mill

Wood Waste Handling - 2014 Modification

Page 41: Notice of Decision: Approvalpermits.air.idem.in.gov/35251f.pdf · 2015. 1. 7. · Permit Number: 121 - 35251 - 00020 . Source Location: 6429 W. 100 N., Montezuma, Indiana . Type of

App. A to TSD Page 4 of 15

Appendix A: Emission Calculations VOC and Particulate

From Surface Coating Operations

Company Name: Superior HardwoodsSource Address: 6429 W. 100 North, Montezuma, IN 47862Permit Number: 121-35255-00020

Reviewer: Brian Wright

Material Density (Lb/Gal)

Weight % Volatile (H20 &

Organics)

Weight % Water

Weight % Organics

Volume % Water

Volume % Non-

Volatiles (solids)

Gal of Mat. (gal/unit)

Maximum (unit/hour)

Maximum (gal/hr)

Maximum (gal/day)

Pounds VOC per gallon of coating less

water

Pounds VOC per gallon of coating

Potential VOC

pounds per hour

Potential VOC

pounds per day

Potential VOC

tons per year

Particulate

Potential (ton/yr)

lb VOC/ gal solids

Transfer Efficiency

End Wax AA6Anchorseal 8.01 57.2% 50.0% 7.2% 32.0% 50.0% 0.125 6.80 0.850 20.40 0.85 0.58 0.49 11.77 2.15 1.91 1.153 85%

End Paint AA7Gempaint 8.34 65.0% 65.0% 0.0% 42.0% 35.0% 0.50 0.41 0.205 4.92 0.00 0.00 0.00 0.00 0.00 0.39 0.00 85%

1.055 25.32 0.49 11.77 2.15 2.31

MethodologyPounds of VOC per Gallon Coating less Water = (Density (lb/gal) * Weight % Organics) / (1-Volume % water)Pounds of VOC per Gallon Coating = (Density (lb/gal) * Weight % Organics)Potential VOC Pounds per Hour = Pounds of VOC per Gallon coating (lb/gal) * Gal of Material (gal/unit) * Maximum (units/hr)Potential VOC Pounds per Day = Pounds of VOC per Gallon coating (lb/gal) * Gal of Material (gal/unit) * Maximum (units/hr) * (24 hr/day)Potential VOC Tons per Year = Pounds of VOC per Gallon coating (lb/gal) * Gal of Material (gal/unit) * Maximum (units/hr) * (8760 hr/yr) * (1 ton/2000 lbs)Particulate Potential Tons per Year = (units/hour) * (gal/unit) * Density (lbs/gal) * (1- Weight % Volatiles) * (1-Transfer efficiency) *(8760 hrs/yr) *(1 ton/2000 lbs)Pounds VOC per Gallon of Solids = (Density (lbs/gal) * Weight % organics) / (Volume % solids)Particulate Potential (ton/yr) (After Control) = Particulate Potential (ton/yr) * (1 - Control Efficiency)

HAPs

Material DensityGallons of Material Maximum Weight %

Methanol Emissions

(Lb/Gal) (gal/unit) (unit/hour) Methanol (ton/yr)End Wax AA6

Anchorseal 8.01 0.125 6.80 7.20% 2.15End Paint AA7

Gempaint 8.34 0.5 0.68 0.00% 0.00

HAPS emission rate (tons/yr) = Density (lb/gal) * Gal of Material (gal/unit) * Maximum (unit/hr) * Weight % HAP * 8760 hrs/yr * 1 ton/2000 lbs

Page 42: Notice of Decision: Approvalpermits.air.idem.in.gov/35251f.pdf · 2015. 1. 7. · Permit Number: 121 - 35251 - 00020 . Source Location: 6429 W. 100 N., Montezuma, Indiana . Type of

App. A to TSD Page 5 of 15

Appendix A: Emission CalculationsNew Kilns

Company Name: Superior HardwoodsSource Address: 6429 W. 100 North, Montezuma, IN 47862Permit Number: 121-35255-00020

Reviewer: Brian Wright

Max. Throughput Max Density Max. Throughputton/hr kg/m3 MSF 3/8" / hr

1 kiln 0.21 1 kiln 0.094 kilns 0.83 819.4 4 kilns 1.01

Pollutant PM PM10 PM2.5 SO2 NOx VOC COEmission Factor (lb/MSF 3/8") (heated zone) 0 0 0 0 0 0.28 0.0088Emission Factor (lb/MSF 3/8") (cooling zone) 0 0 0 0 0 0.72 0.099Potential To Emit - One kiln (tons/year) 0.00 0.00 0.00 0.00 0.00 0.40 0.04Potential To Emit - 4 kilns (tons/year) 0.00 0.00 0.00 0.00 0.00 1.61 0.17

Hazardous Air Pollutants (HAPs)Pollutant Acetaldehyde Formaldehyde Methanol MIBK PhenolEmission Factor (lb/MSF 3/8") (heated zone) 0.0043 0.0011 0.041 0.0022 0.003Emission Factor (lb/MSF 3/8") (cooling zone) 0.032 0.0065 0.021 0.029 0Potential To Emit - One kiln (tons/year) 0.01 0.00 0.03 0.01 0.00Potential To Emit - 4 kilns (tons/year) 0.06 0.01 0.10 0.05 0.00

Potential To Emit Total HAPs (tons/year) 0.23 (kilns)

Methodology:

Max. Density is based on the type of wood with the highest density (see 'Facility Throughput').One lb/MSF 3/8" = 0.5 kg/m3

Emission factors are from AP 42 Chapter 10.5 (1/02) for indirect heated, hardwood drying process.For VOC, CO and HAP emission factors, emission factors for the heated zone and cooling section of the kiln were combined. There are no emission factors for PM, PM10/PM2.5, or SO2 for indirect-fired hardwood drying processes. The NOx and CO2 emission factor is listed in AP 42 as ND (no data available).PTE (tons/yr) = Emission Factor (lb/MSF of 3/8 inch thick veneer) x Max. Throughput (MSF 3/8" thick veneer / hr) x 8760 hrs/yr x 1 ton/2000 lbs

The maximum throughput of wood (ton/hr) for the new kilns is based on a maximum rate of 70,000 boardfeet per month per kiln.

Page 43: Notice of Decision: Approvalpermits.air.idem.in.gov/35251f.pdf · 2015. 1. 7. · Permit Number: 121 - 35251 - 00020 . Source Location: 6429 W. 100 N., Montezuma, Indiana . Type of

App. A to TSD Page 6 of 15

Appendix A: Emission CalculationsKilns

Company Name: Superior HardwoodsSource Address: 6429 W. 100 North, Montezuma, IN 47862Permit Number: 121-35255-00020

Reviewer: Brian Wright

Max. Throughput Max Density Max. Throughputton/hr kg/m3 MSF 3/8" / hr

1 kiln 0.48 1 kiln 0.5811 kilns 5.27 819.4 11 kilns 6.43

Pollutant PM PM10 PM2.5 SO2 NOx VOC COEmission Factor (lb/MSF 3/8") (heated zone) 0 0 0 0 0 0.28 0.0088Emission Factor (lb/MSF 3/8") (cooling zone) 0 0 0 0 0 0.72 0.099Potential To Emit - One kiln (tons/year) 0.00 0.00 0.00 0.00 0.00 2.56 0.28Potential To Emit - 11 kilns (tons/year) 0.00 0.00 0.00 0.00 0.00 28.17 3.04

Hazardous Air Pollutants (HAPs)Pollutant Acetaldehyde Formaldehyde Methanol MIBK PhenolEmission Factor (lb/MSF 3/8") (heated zone) 0.0043 0.0011 0.041 0.0022 0.003Emission Factor (lb/MSF 3/8") (cooling zone) 0.032 0.0065 0.021 0.029 0Potential To Emit - One kiln (tons/year) 0.09 0.02 0.16 0.08 0.01Potential To Emit - 11 kilns (tons/year) 1.02 0.21 1.75 0.88 0.08

Potential To Emit Total HAPs (tons/year) 3.95 (11 kilns)

Methodology:

Max. Density is based on the type of wood with the highest density (see 'Facility Throughput').One lb/MSF 3/8" = 0.5 kg/m3

Emission factors are from AP 42 Chapter 10.5 (1/02) for indirect heated, hardwood drying process.For VOC, CO and HAP emission factors, emission factors for the heated zone and cooling section of the kiln were combined. There are no emission factors for PM, PM10/PM2.5, or SO2 for indirect-fired hardwood drying processes. The NOx and CO2 emission factor is listed in AP 42 as ND (no data available).PTE (tons/yr) = Emission Factor (lb/MSF of 3/8 inch thick veneer) x Max. Throughput (MSF 3/8" thick veneer / hr) x 8760 hrs/yr x 1 ton/2000 lbs

The maximum throughput of wood (ton/hr) for the kilns are based on a bottleneck of material processed from the operations in the Old Mill and New Mill.

Page 44: Notice of Decision: Approvalpermits.air.idem.in.gov/35251f.pdf · 2015. 1. 7. · Permit Number: 121 - 35251 - 00020 . Source Location: 6429 W. 100 N., Montezuma, Indiana . Type of

App. A to TSD Page 7 of 15

Appendix A: Emission CalculationsWood-Fired Boiler AA2

Modified Wood Waste Combustion (uncontrolled)Dry Wood

Company Name: Superior HardwoodsSource Address: 6429 W. 100 North, Montezuma, IN 47862Permit Number: 121-35255-00020

Reviewer: Brian Wright

Capacity (MMBtu/hr) 12.42

Pollutant PM* PM10* PM2.5* SO2 NOx VOC CO**Emission Factor in lb/MMBtu 0.4 0.377 0.327 0.025 0.49 0.017 0.6Potential Emissions in tons/yr 21.76 20.51 17.79 1.36 26.66 0.92 32.64

Wet wood is considered to be greater than or equal to 20% moisture content. Dry wood is considered to be less than 20% moisture content.

Selected Hazardous Air Pollutants

Acrolein Benzene FormaldehydeHydrogen Chloride Styrene Total

Emission Factor in lb/MMBtu 4.0E-03 4.2E-03 4.4E-03 1.9E-02 1.9E-03Potential Emissions in tons/yr 0.22 0.23 0.24 1.03 0.10 1.82

MethodologyEmission Factors are from AP-42 Chapter 1.6 (revised 3/02)Emissions (tons/yr) = Capacity (MMBtu/hr) x Emission Factor (lb/MMBtu) x 8760hrs/yr x 1 ton/2000 lbsThese factors include the five HAPs with the highest AP-42 emission factors.

CO2 CH4 N2OEmission Factor in kg/mmBtu from 40 CFR 98 93.8 0.032 0.0042Potential Emission in tons/yr 11249.5 3.8 0.5Summed Potential Emissions in tons/yr 11,254CO2e Total in tons/yr 11,496

To convert from tons/hr capacity to MMBtu/hr capacity:Heat Input Capacity (MMBtu/hr) = Capacity (tons/hr) x Higher Heating Value of wood fuel (Btu/lb) x (1 MMBtu/106 Btu/) x 2000 lbs/1 tonCO2 & CH4 Emission Factors from Tables C-1 & 2 of 40 CFR Part 98 Subpart C. N2O emission factor from AP-43 Chapter 1.6 (revised 3/02).Global Warming Potentials (GWP) from Table A-1 of 40 CFR Part 98 Subpart A.Potential Emission (tons/yr) = Heat Input Capacity mmBtu/hr x Emission Factor (kg/mmBtu) x 2.20462 lb/kg x 8760 hrs/yr /2,000 lb/tonPotential Emission (tons/yr) = Heat Input Capacity mmBtu/hr x Emission Factor (lb/mmBtu) x 8760 hrs/yr /2,000 lb/ton

Methodology

CO2e (tons/yr) = CO2 Potential Emission ton/yr x CO2 GWP (1) + CH4 Potential Emission ton/yr x CH4 GWP (25) + N2O Potential Emission ton/yr x N2O GWP (298).

Greenhouse Gases

*The PM10 and PM2.5 emission factors include the condensible PM emission factor of 0.017 lb/MMBtu, measured by EPA Method 202 (or equivalent) and the appropriate filterable PM emission factor, measured by EPA Method 5 (or equivalent). The PM emission factor is filterable PM measured by EPA Method 5 (or equivalent).

Page 45: Notice of Decision: Approvalpermits.air.idem.in.gov/35251f.pdf · 2015. 1. 7. · Permit Number: 121 - 35251 - 00020 . Source Location: 6429 W. 100 N., Montezuma, Indiana . Type of

App. A to TSD Page 8 of 15

Appendix A: Emission CalculationsNatural Gas Boiler AA3

MM BTU/HR <100

Company Name: Superior HardwoodsSource Address: 6429 W. 100 North, Montezuma, IN 47862Permit Number: 121-35255-00020

Reviewer: Brian Wright

HHVMMBtu/hr mmBtu MMCF/yr

mmscf8.28 1020 71.1

Pollutant PM* PM10* direct PM2.5* SO2 NOx VOC COEmission Factor in lb/MMCF 1.9 7.6 7.6 0.6 100 5.5 84

0.07 0.27 0.27 0.02 3.56 0.20 2.99

PM2.5 emission factor is filterable and condensable PM2.5 combined.

Methodology

HAPS Calculations

Benzene Dichlorobenzene Formaldehyde Hexane Toluene Total - Organics

2.1E-03 1.2E-03 7.5E-02 1.8E+00 3.4E-037.5E-05 4.3E-05 2.7E-03 0.06 1.2E-04 0.07

Lead Cadmium Chromium Manganese Nickel Total - Metals5.0E-04 1.1E-03 1.4E-03 3.8E-04 2.1E-031.8E-05 3.9E-05 5.0E-05 1.4E-05 7.5E-05 1.9E-04

Total HAPs 0.07Worst HAP 0.07

Greenhouse Gas Calculations

CO2 CH4 N2O120,000 2.3 2.2

4,267 0.1 0.1Summed Potential Emissions in tons/yr 4,267CO2e Total in tons/yr 4,292

The N2O Emission Factor for uncontrolled is 2.2. The N2O Emission Factor for low Nox burner is 0.64.

Global Warming Potentials (GWP) from Table A-1 of 40 CFR Part 98 Subpart A.

Emission Factors are from AP 42, Chapter 1.4, Tables 1.4-1, 1.4-2, 1.4-3, SCC #1-02-006-02, 1-01-006-02, 1-03-006-02, and 1-03-006-03Potential Throughput (MMCF) = Heat Input Capacity (MMBtu/hr) x 8,760 hrs/yr x 1 MMCF/1,020 MMBtu

The five highest organic and metal HAPs emission factors are provided above. Additional HAPs emission factors are available in AP-42, Chapter 1.4.

All emission factors are based on normal firing.MMBtu = 1,000,000 Btu

Emission (tons/yr) = Throughput (MMCF/yr) x Emission Factor (lb/MMCF)/2,000 lb/ton

MMCF = 1,000,000 Cubic Feet of Gas

Emission Factor in lb/MMcfPotential Emission in tons/yr

Methodology is the same as above.

HAPs - Organics

HAPs - Metals

Emission Factors are from AP 42, Table 1.4-2 SCC #1-02-006-02, 1-01-006-02, 1-03-006-02, and 1-03-006-03.

Emission Factor in lb/MMcfPotential Emission in tons/yr

Emission Factor in lb/MMcf

Methodology

Emission (tons/yr) = Throughput (MMCF/yr) x Emission Factor (lb/MMCF)/2,000 lb/tonCO2e (tons/yr) = CO2 Potential Emission ton/yr x CO2 GWP (1) + CH4 Potential Emission ton/yr x CH4 GWP (25) + N2O Potential Emission ton/yr x N2O GWP (298).

Potential Emission in tons/yr

Greenhouse Gas

Potential Throughput

Potential Emission in tons/yr*PM emission factor is filterable PM only. PM10 emission factor is filterable and condensable PM10 combined.

**Emission Factors for NOx: Uncontrolled = 100, Low NOx Burner = 50, Low NOx Burners/Flue gas recirculation = 32

Page 46: Notice of Decision: Approvalpermits.air.idem.in.gov/35251f.pdf · 2015. 1. 7. · Permit Number: 121 - 35251 - 00020 . Source Location: 6429 W. 100 N., Montezuma, Indiana . Type of

App. A to TSD Page 9 of 15

Appendix A: Emission CalculationsExternal Combustion Wood Stoves AA4Wood Waste Combustion (uncontrolled)

Dry Wood

Company Name: Superior HardwoodsSource Address: 6429 W. 100 North, Montezuma, IN 47862Permit Number: 121-35255-00020

Reviewer: Brian Wright

Capacity (MMBtu/hr) 0.45 (3 wood-fired stoves, each with a max heat input capacity of 0.15 MMBtu/hour)

Pollutant PM* PM10* PM2.5* SO2 NOx VOC CO**Emission Factor in lb/MMBtu 0.4 0.377 0.327 0.025 0.49 0.017 0.6Potential Emissions in tons/yr 0.79 0.74 0.64 0.05 0.97 0.03 1.18

Wet wood is considered to be greater than or equal to 20% moisture content. Dry wood is considered to be less than 20% moisture content.

MethodologyEmission Factors are from AP-42 Chapter 1.6 (revised 9/03)Emissions (tons/yr) = Capacity (MMBtu/hr) x Emission Factor (lb/MMBtu) x 8760 hrs/yr x 1 ton/2000 lbs

Selected Hazardous Air Pollutants

Acrolein Benzene FormaldehydeHydrogen Chloride Styrene Total

Emission Factor in lb/MMBtu 4.0E-03 4.2E-03 4.4E-03 1.9E-02 1.9E-03Potential Emissions in tons/yr 0.01 0.01 0.01 0.04 0.00 0.07

MethodologyEmission Factors are from AP-42 Chapter 1.6 (revised 3/02)Emissions (tons/yr) = Capacity (MMBtu/hr) x Emission Factor (lb/MMBtu) x 8760hrs/yr x 1ton/2000lbsThese factors include the five HAPs with the highest AP-42 emission factors.

CO2 CH4 N2OEmission Factor in kg/mmBtu from 40 CFR 98 93.8 0.032 0.0042

407.6 0.1 0.0Summed Potential Emissions in tons/yr 408CO2e Total in tons/yr 417

To convert from tons/hr capacity to MMBtu/hr capacity:Heat Input Capacity (MMBtu/hr) = Capacity (tons/hr) x Higher Heating Value of wood fuel (Btu/lb) x (1 MMBtu/106 Btu/) x 2000 lbs/1 tonCO2 & CH4 Emission Factors from Tables C-1 & 2 of 40 CFR Part 98 Subpart C. N2O emission factor from AP-43 Chapter 1.6 (revised 3/02).Global Warming Potentials (GWP) from Table A-1 of 40 CFR Part 98 Subpart A.Potential Emission (tons/yr) = Heat Input Capacity mmBtu/hr x Emission Factor (kg/mmBtu) x 2.20462 lb/kg x 8760 hrs/yr /2,000 lb/tonPotential Emission (tons/yr) = Heat Input Capacity mmBtu/hr x Emission Factor (lb/mmBtu) x 8760 hrs/yr /2,000 lb/tonCO2e (tons/yr) = CO2 Potential Emission ton/yr x CO2 GWP (1) + CH4 Potential Emission ton/yr x CH4 GWP (25) + N2O Potential Emission ton/yr x N2O GWP (298).

Methodology

Greenhouse Gases

Potential Emission in tons/yr

*The PM10 and PM2.5 emission factors include the condensible PM emission factor of 0.017 lb/MMBtu, measured by EPA Method 202 (or equivalent) and the appropriate filterable PM emission factor, measured by EPA Method 5 (or equivalent). The PM emission factor is filterable PM measured by EPA Method 5 (or equivalent).

Page 47: Notice of Decision: Approvalpermits.air.idem.in.gov/35251f.pdf · 2015. 1. 7. · Permit Number: 121 - 35251 - 00020 . Source Location: 6429 W. 100 N., Montezuma, Indiana . Type of

App. A to TSD Page 10 of 15

Appendix A: Emission CalculationsWelding and Thermal Cutting

Company Name: Superior HardwoodsSource Address: 6429 W. 100 North, Montezuma, IN 47862Permit Number: 121-35255-00020

Reviewer: Brian Wright

Lumber Soaking Operations Number of Max. electrode Max. electrode HAPSStations h a max heat input capacity of 0.15 MMBtu/hour) (lbs/hr)

WELDING station (lbs/hr) station (lbs/day) PM = PM10 Mn Ni Cr PM = PM10 Mn Ni Cr

Submerged Arc 1 0.07 1.68 0.036 0.011 0.003 0.001 0.000 0 0.001Metal Inert Gas (MIG)(carbon steel) 0.0055 0.0005 0.000 0.000 0.000 0 0.000Stick (E7018 electrode) 1 0.035 0.84 0.0211 0.0009 0.001 3.2E-05 0.000 0 3.2E-05Tungsten Inert Gas (TIG)(carbon steel) 0.0055 0.0005 0.000 0.000 0.000 0 0.000Oxyacetylene(carbon steel) 0.0055 0.0005 0.000 0.000 0.000 0 0.000

Number of Max. Metal Max. Metal Max. Metal HAPSStations Thickness Cutting Rate Cutting Rate (lbs/hr)

FLAME CUTTING Cut (in.) (in./minute) (in./hour) PM = PM10 Mn Ni Cr PM = PM10 Mn Ni Cr

Oxyacetylene 4 0.125 1 60 0.1622 0.0005 0.0001 0.0003 0.005 1.5E-05 0.000 0.000 2.7E-05Oxymethane 0.0815 0.0002 0.0002 0.000 0.000 0.000 0.000 0.000Plasma** 0.0039 0.000 0.000 0.000 0.000 0.000

EMISSION TOTALSPotential Emissions lbs/hr 0.01 0.001 0.00 0.00 0.001Potential Emissions lbs/day 0.19 0.02 0.00 0.00 0.02Potential Emissions tons/year 0.04 0.004 0.00 0.00 0.004

Methodology:

Welding emissions, lb/hr: (# of stations)(max. lbs of electrode used/hr/station)(emission factor, lb. pollutant/lb. of electrode used)Emissions, lbs/day = emissions, lbs/hr x 24 hrs/dayEmissions, tons/yr = emissions, lb/hr x 8,760 hrs/year x 1 ton/2,000 lbs.

*Emission Factors are default values for carbon steel unless a specific electrode type is noted in the Process column.**Emission Factor for plasma cutting from American Welding Society (AWS). Trials reported for wet cutting of 8 mm thick mild steel with 3.5 m/min cutting speed (at 0.2 g/min emitted). Therefore, the emission factor for plasma cutting is for 8 mm thick rather than 1 inch and the maximum metal thickness is not used in calculting the emissions Using AWS average values: (0.25 g/min)/(3.6 m/min) x (0.0022 lb/g)/(39.37 in./m) x (1,000 in.) = 0.0039 lb/1,000 in. cut, 8 mm thickPlasma cutting emissions, lb/hr: (# of stations)(max. cutting rate, in./min.)(60 min./hr.)(emission factor, lb. pollutant/1,000 in. cut, 8 mm thick)Cutting emissions, lb/hr: (# of stations)(max. metal thickness, in.)(max. cutting rate, in./min.)(60 min./hr.)(emission factor, lb. pollutant/1,000 in. cut, 1" thick)

(lb pollutant/1,000 inches cut, 1" thick)** (lbs/hr)

EMISSION FACTORS* EMISSIONS (lb pollutant/lb electrode) (lbs/hr)

EMISSION FACTORS EMISSIONS

Page 48: Notice of Decision: Approvalpermits.air.idem.in.gov/35251f.pdf · 2015. 1. 7. · Permit Number: 121 - 35251 - 00020 . Source Location: 6429 W. 100 N., Montezuma, Indiana . Type of

App. A to TSD Page 11 of 15

Appendix A: Emission CalculationsGasoline Fuel Transfer and Dispensing Operation

Volatile Organic Compounds and Hazardous Air Pollutants (HAPs)

Company Name: Superior HardwoodsSource Address: 6429 W. 100 North, Montezuma, IN 47862Permit Number: 121-35255-00020

Reviewer: Brian Wright

Gasoline Throughput = 65.8 gallons/dayGasoline Throughput = 24.00 kgal/yr

Volatile Organic Compounds (VOC)

Emission Source

Emission Factor (lb/kgal of throughput)*

PTE of VOC (tons/yr)

Filling storage tank (splash filling) 11.50 0.1380Tank breathing and emptying 1.00 0.0120Vehicle refueling (displaced losses - uncontrolled) 11.00 0.1320Spillage 0.70 0.0084

Total 0.152

MethodologyThe gasoline throughput was provided by the source.*Emission Factors from AP-42 Chapter 5.2 Transportation And Marketing Of Petroleum Liquids (dated 6/08), Table 5.2-7Gasoline Throughput (kgal/yr) = [Gasoline Throughput (gallons/day)] * [365 days/yr] * [kgal/1000 gal]PTE of VOC (tons/yr) = [Gasoline Throughput (kgal/yr)] * [Emission Factor (lb/kgal)] * [ton/2000 lb]

Hazardous Air Pollutants (HAPs)

Volatile Organic HAP CAS#

Hazardous Air Pollutant (HAP) Content (vapor mass fraction)**

PTE of HAP (tons/yr)

Benzene 71-43-2 0.37% 5.6E-04n-Hexane 110-54-3 0.34% 5.2E-04Toluene 108-88-3 0.40% 6.1E-04m-Xylenes 108-38-3 0.11% 1.7E-04

Total PTE of HAPs (tons/yr) 1.9E-03PTE of Worst Single HAP (tons/yr) 6.1E-04 (Toluene)

Methodology**Source: US EPA TANKS Version 4.09 programPTE of Total HAPs (tons/yr) = [Total HAP Content (% by weight)] * [PTE of VOC (tons/yr)]PTE of HAP (tons/yr) = [Hazardous Air Pollutant (HAP) Content (vapor mass fraction)] * [PTE of VOC (tons/yr)]

AbbreviationsVOC = Volatile Organic Compounds HAP = Hazardous Air PollutantPTE = Potential to Emit

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App. A to TSD Page 12 of 15

Appendix A: Emission CalculationsFugitive Dust Emissions - Unpaved Roads

Company Name: Superior HardwoodsSource Address: 6429 W. 100 North, Montezuma, IN 47862Permit Number: 121-35255-00020

Reviewer: Brian Wright

Unpaved Roads at Industrial Site

(3 wood-fired stoves, each with a max heat input capacity of 0.15 MMBtu/hour)Vehicle Information (provided by source)

Type

Maximum number of vehicles

Number of one-way trips per day per

vehicle

Maximum trips per day

(trip/day)

Maximum Weight Loaded

(tons/trip)

Total Weight driven per day

(ton/day)

Maximum one-way distance

(feet/trip)

Maximum one-way distance

(mi/trip)

Maximum one-way

miles (miles/day)

Maximum one-way

miles (miles/yr)

Semi Truck (entering plant) (one-way trip) 320 1 320 40.0 12800.0 1003 0.19 60.8 22192.0Semi Truck (leaving plant) (one-way trip) 320 1 320 17.5 5600.0 1003 0.19 60.8 22192.0Forklifts (logs, loaded) (one-way trip) 6 128 768 16.0 12288.0 1003 0.19 145.9 53260.8Forklifts (logs, empty) (one-way trip) 6 128 768 12.5 9600.0 1003 0.19 145.9 53260.8Forklifts (lumber, loaded) (one-way trip) 6 128 768 16.0 12288.0 1003 0.19 145.9 53260.8Forklifts (lumber, empty) (one-way trip) 6 128 768 12.5 9600.0 1003 0.19 145.9 53260.8Shop Truck 1 128 128 1.5 192.0 1003 0.19 24.3 8876.8Work Trucks 5 8 40 1.8 70.0 1003 0.19 7.6 2774.0Knuckle Booms 2 16 32 15.0 480.0 53 0.01 0.3 116.8Golf Cart 1 192 192 0.2 28.8 1003 0.19 36.5 13315.2

Totals 4104.0 62946.8 774.0 282510.0

Average Vehicle Weight Per Trip = 15.3 tons/tripAverage Miles Per Trip = 0.19 miles/trip

Unmitigated Emission Factor, Ef = k*[(s/12)^a]*[(W/3)^b] (Equation 1a from AP-42 13.2.2)

PM PM10 PM2.5where k = 4.9 1.5 0.15 lb/mi = particle size multiplier (AP-42 Table 13.2.2-2 for Industrial Roads)

s = 4.8 4.8 4.8 % = mean % silt content of unpaved roads (AP-42 Table 13.2.2-1 Sand/Gravel Plant)a = 0.7 0.9 0.9 = constant (AP-42 Table 13.2.2-2 for Industrial Roads)

W = 15.3 15.3 15.3 tons = average vehicle weight (provided by source)b = 0.45 0.45 0.45 = constant (AP-42 Table 13.2.2-2 for Industrial Roads)

Taking natural mitigation due to precipitation into consideration, Mitigated Emission Factor, Eext = E * [(365 - P)/365] (Equation 2 from AP-42 13.2.2)Mitigated Emission Factor, Eext = E * [(365 - P)/365]

where P = 125 days of rain greater than or equal to 0.01 inches (see Fig. 13.2.2-1)

PM PM10 PM2.5Unmitigated Emission Factor, Ef = 5.38 1.37 0.14 lb/mileMitigated Emission Factor, Eext = 3.54 0.90 0.09 lb/mile

Dust Control Efficiency = 0% 0% 0% (pursuant to control measures outlined in fugitive dust control plan)

Process

Unmitigated PTE of PM

(tons/yr)

Unmitigated PTE of PM10

(tons/yr)

Unmitigated PTE of PM2.5

(tons/yr)

Mitigated PTE of PM

(tons/yr)

Mitigated PTE of PM10

(tons/yr)

Mitigated PTE of PM2.5

(tons/yr)

Controlled PTE of PM

(tons/yr)

Controlled PTE of PM10

(tons/yr)

Controlled PTE of PM2.5

(tons/yr)Semi Truck (entering plant) (one-way trip) 59.66 15.21 1.52 39.23 10.00 1.00 39.23 10.00 1.00Semi Truck (leaving plant) (one-way trip) 59.66 15.21 1.52 39.23 10.00 1.00 39.23 10.00 1.00Forklifts (logs, loaded) (one-way trip) 143.19 36.49 3.65 94.15 24.00 2.40 94.15 24.00 2.40Forklifts (logs, empty) (one-way trip) 143.19 36.49 3.65 94.15 24.00 2.40 94.15 24.00 2.40Forklifts (lumber, loaded) (one-way trip) 143.19 36.49 3.65 94.15 24.00 2.40 94.15 24.00 2.40Forklifts (lumber, empty) (one-way trip) 143.19 36.49 3.65 94.15 24.00 2.40 94.15 24.00 2.40Shop Truck 23.86 6.08 0.61 15.69 4.00 0.40 15.69 4.00 0.40Work Trucks 7.46 1.90 0.19 4.90 1.25 0.12 4.90 1.25 0.12Knuckle Booms 0.31 0.08 0.01 0.21 0.05 0.01 0.21 0.05 0.01Golf Cart 35.80 9.12 0.91 23.54 6.00 0.60 23.54 6.00 0.60

Totals 759.5 193.6 19.4 499.4 127.3 12.7 499.4 127.3 12.7

MethodologyTotal Weight driven per day (ton/day) = [Maximum Weight Loaded (tons/trip)] * [Maximum trips per day (trip/day)]Maximum one-way distance (mi/trip) = [Maximum one-way distance (feet/trip) / [5280 ft/mile]Maximum one-way miles (miles/day) = [Maximum trips per year (trip/day)] * [Maximum one-way distance (mi/trip)]Average Vehicle Weight Per Trip (ton/trip) = SUM[Total Weight driven per day (ton/day)] / SUM[Maximum trips per day (trip/day)]Average Miles Per Trip (miles/trip) = SUM[Maximum one-way miles (miles/day)] / SUM[Maximum trips per year (trip/day)]Unmitigated PTE (tons/yr) = (Maximum one-way miles (miles/yr)) * (Unmitigated Emission Factor (lb/mile)) * (ton/2000 lbs)Mitigated PTE (tons/yr) = (Maximum one-way miles (miles/yr)) * (Mitigated Emission Factor (lb/mile)) * (ton/2000 lbs)Controlled PTE (tons/yr) = (Mitigated PTE (tons/yr)) * (1 - Dust Control Efficiency)

AbbreviationsPM = Particulate MatterPM10 = Particulate Matter (<10 um)PM2.5 = Particulate Matter (<2.5 um)PTE = Potential to Emit

Page 50: Notice of Decision: Approvalpermits.air.idem.in.gov/35251f.pdf · 2015. 1. 7. · Permit Number: 121 - 35251 - 00020 . Source Location: 6429 W. 100 N., Montezuma, Indiana . Type of

App. A to TSD Page 13 of 15

Appendix A: Emission CalculationsVeneer Operations

Company Name: Superior HardwoodsSource Address: 6429 W. 100 North, Montezuma, IN 47862Permit Number: 121-35255-00020

Reviewer: Brian Wright

Potential Emissions from Lumber Soaking Operations

Maximum Production 425.63 boardfeet/hr 1135.00 SF (3/8")(4)

Pollutant(lb/hr) (ton/yr)

VOC 0.0744 lb/MSF 0.08 0.37Acetaldehyde 0.0047 lb/MSF 0.01 0.02Alpha-pinene 0.0560 lb/MSF 0.06 0.28Beta-Pinene 0.0064 lb/MSF 0.01 0.03Methanol 0.0073 lb/MSF 0.01 0.04

Total HAPs 0.0120 lb/MSF 0.01 0.06(1) Potential emissions are based on maximum production throughput and published emission factors.(2) The amount of boardfeet per hour was converted to an equivalent 3/8" SF by multiplying by (2.67 or 1/0.375 3/8 equivalents per boardfoot).

Potential Emissions from Veneer Slicing Operations

Maximum Production 425.63 boardfeet/hr 1135.00 SF (3/8")(4)

Pollutant(lb/hr) (ton/yr)

VOC 0.0720 lb/MSF 0.08 0.36Acetaldehyde 0.00081 lb/MSF 0.00 0.00Formaldehyd 0.00034 lb/MSF 0.00 0.00Methanol 0.0087 lb/MSF 0.01 0.04Phenol 0.0019 lb/MSF 0.00 0.01

Total HAPs 0.0118 lb/MSF 0.01 0.06(1) Potential emissions are based on maximum production throughput and published emission factors.(2) The amount of boardfeet per hour was converted to an equivalent 3/8" SF by multiplying by (2.67 or 1/0.375 3/8 equivalents per boardfoot).

Veneer Slicing Operations

AP-42 Table 10.5-7 (SCC 3-07-007-90)

Emission Factor Calculations Potential Emissions(1)

Emission Factor SourceAP-42 Table 10.5-7 (SCC 3-07-007-90)AP-42 Table 10.5-7 (SCC 3-07-007-90)AP-42 Table 10.5-7 (SCC 3-07-007-90)AP-42 Table 10.5-7 (SCC 3-07-007-90)AP-42 Table 10.5-7 (SCC 3-07-007-90)

AP-42 Table 10.5-7 (SCC 3-07-007-90)AP-42 Table 10.5-7 (SCC 3-07-007-89)

Lumber Soaking Operations

AP-42 Table 10.5-7 (SCC 3-07-007-90)

Emission Factor Calculations Potential Emissions(1)

Emission Factor SourceAP-42 Table 10.5-7 (SCC 3-07-007-89)AP-42 Table 10.5-7 (SCC 3-07-007-89)AP-42 Table 10.5-7 (SCC 3-07-007-90)

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App. A to TSD Page 14 of 15

Appendix A: Emission CalculationsVeneer Drying

Company Name: Superior HardwoodsSource Address: 6429 W. 100 North, Montezuma, IN 47862Permit Number: 121-35255-00020

Reviewer: Brian Wright

Potential Emissions from Veneer Drying OperationIndirect Heated Veneer Drying Operation - Three (3) Heating Zones and One (1) Cooling Zone

Maximum Production 425.63 bd-ft/hr 1,135.00 SF (3/8")(4)

Source Pollutant(lb/hr) (ton/yr) (lb/hr) (ton/yr)

PM/PM10/PM2.5 0.350 lb/MSF 0.40 1.74 1.19 5.22NOx ND lb/MSF 0.00 0.00 0.00 0.00CO 0.0088 lb/MSF 0.01 0.04 0.03 0.13CO2 ND lb/MSF 0.00 0.00 0.00 0.00VOC 0.28 lb/MSF 0.32 1.39 0.95 4.18

Acetaldehyd 0.0043 lb/MSF 0.00 0.02 0.01 0.06Formaldehy 0.0011 lb/MSF 0.00 0.01 0.00 0.02Methanol 0.041 lb/MSF 0.05 0.20 0.14 0.61MIBK 0.0022 lb/MSF 0.00 0.01 0.01 0.03Phenol 0.0030 lb/MSF 0.00 0.01 0.01 0.04

Total HAPs 0.052 lb/MSF 0.06 0.26 0.18 0.77NOx ND lb/MSF 0.00 0.00 0.00 0.00CO 0.099 lb/MSF 0.11 0.49 0.11 0.49CO2 ND lb/MSF 0.00 0.00 0.00 0.00VOC 0.72 lb/MSF 0.82 3.58 0.82 3.58

Acetaldehyd 0.032 lb/MSF 0.04 0.16 0.04 0.16Formaldehy 0.007 lb/MSF 0.01 0.03 0.01 0.03Methanol 0.021 lb/MSF 0.02 0.10 0.02 0.10MIBK 0.029 lb/MSF 0.03 0.14 0.03 0.14

Total HAPs 0.089 lb/MSF 0.10 0.44 0.10 0.44PM/PM10/PM2.5 0.350 lb/MSF 0.40 1.74 1.19 5.22NOx ND lb/MSF 0.00 0.00 0.00 0.00CO 0.108 lb/MSF 0.12 0.54 0.14 0.62CO2 ND lb/MSF 0.00 0.00 0.00 0.00VOC 1.000 lb/MSF 1.14 4.97 1.77 7.76

Acetaldehyd 0.036 lb/MSF 0.04 0.18 0.05 0.22Formaldehy 0.008 lb/MSF 0.01 0.04 0.01 0.05Methanol 0.062 lb/MSF 0.07 0.31 0.16 0.72MIBK 0.031 lb/MSF 0.04 0.16 0.04 0.18Phenol 0.003 lb/MSF 0.00 0.01 0.01 0.04

Total HAPs 0.140 lb/MSF 0.16 0.70 0.28 1.21(1) Emissions are based on drying emissions with three (3) heating zones and (1) cooling zone.(2) Potential Emissions are based on maximum capacity of the veneer slicer and published emission factors.(3) The particulate emission factor for indirect heating for softwoods was used as a conservative estimate because there is no value for hardwood listed.(4) The amount of boardfeet per hour was converted to an equivalent 3/8" SF by multiplying by (2.67 or 1/0.375 3/8 equivalents per boardfoot).

Total Dryer Emissions See Above

Emission Factor Source

3 Heating Zones

AP-42 Table 10.5-1 (SCC 3-07-007-62)(3)

AP-42 Table 10.5-2 (SCC 3-07-007-56)

AP-42 Table 10.5-2 (SCC 3-07-007-52)

Potential Emissions(1)(2)

Veneer Drying Emissions

Emission Factor Calculations Potential Emissions

1 Cooling Zone AP-42 Table 10.5-7 (SCC 3-07-007-57)

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App. A to TSD Page 15 of 15

Appendix A: Emission CalculationsNew Natural Gas Boiler (Veneer Operations)

MM BTU/HR <100

Company Name: Superior HardwoodsSource Address: 6429 W. 100 North, Montezuma, IN 47862Permit Number: 121-35255-00020

Reviewer: Brian Wright

HHVMMBtu/hr mmBtu MMCF/yr

mmscf10.043 1020 86.3

Pollutant PM* PM10* direct PM2.5* SO2 NOx VOC COEmission Factor in lb/MMCF 1.9 7.6 7.6 0.6 100 5.5 84

0.08 0.33 0.33 0.03 4.31 0.24 3.62

PM2.5 emission factor is filterable and condensable PM2.5 combined.

Methodology

HAPS Calculations

Benzene Dichlorobenzene Formaldehyde Hexane Toluene Total - Organics

2.1E-03 1.2E-03 7.5E-02 1.8E+00 3.4E-039.1E-05 5.2E-05 3.2E-03 0.08 1.5E-04 0.08

Lead Cadmium Chromium Manganese Nickel Total - Metals5.0E-04 1.1E-03 1.4E-03 3.8E-04 2.1E-032.2E-05 4.7E-05 6.0E-05 1.6E-05 9.1E-05 2.4E-04

Total HAPs 0.08Worst HAP 0.08

Greenhouse Gas Calculations

CO2 CH4 N2O120,000 2.3 2.25,175 0.1 0.1

Summed Potential Emissions in tons/yr 5,175CO2e Total in tons/yr 5,206

The N2O Emission Factor for uncontrolled is 2.2. The N2O Emission Factor for low Nox burner is 0.64.

Global Warming Potentials (GWP) from Table A-1 of 40 CFR Part 98 Subpart A.Emission Factors are from AP 42, Table 1.4-2 SCC #1-02-006-02, 1-01-006-02, 1-03-006-02, and 1-03-006-03.

Emission (tons/yr) = Throughput (MMCF/yr) x Emission Factor (lb/MMCF)/2,000 lb/tonCO2e (tons/yr) = CO2 Potential Emission ton/yr x CO2 GWP (1) + CH4 Potential Emission ton/yr x CH4 GWP (25) + N2O Potential Emission ton/yr x N2O GWP (298).

Methodology

Greenhouse Gas

Emission Factor in lb/MMcf

Emission Factor in lb/MMcfPotential Emission in tons/yr

HAPs - Metals

Emission Factor in lb/MMcfPotential Emission in tons/yr

Potential Emission in tons/yr

HAPs - Organics

Potential Throughput

Potential Emission in tons/yr*PM emission factor is filterable PM only. PM10 emission factor is filterable and condensable PM10 combined.

**Emission Factors for NOx: Uncontrolled = 100, Low NOx Burner = 50, Low NOx Burners/Flue gas recirculation = 32

All emission factors are based on normal firing.MMBtu = 1,000,000 BtuMMCF = 1,000,000 Cubic Feet of GasEmission Factors are from AP 42, Chapter 1.4, Tables 1.4-1, 1.4-2, 1.4-3, SCC #1-02-006-02, 1-01-006-02, 1-03-006-02, and 1-03-006-03Potential Throughput (MMCF) = Heat Input Capacity (MMBtu/hr) x 8,760 hrs/yr x 1 MMCF/1,020 MMBtuEmission (tons/yr) = Throughput (MMCF/yr) x Emission Factor (lb/MMCF)/2,000 lb/ton

Methodology is the same as above.The five highest organic and metal HAPs emission factors are provided above. Additional HAPs emission factors are available in AP-42, Chapter 1.4.

Page 53: Notice of Decision: Approvalpermits.air.idem.in.gov/35251f.pdf · 2015. 1. 7. · Permit Number: 121 - 35251 - 00020 . Source Location: 6429 W. 100 N., Montezuma, Indiana . Type of

INDIANA DEPARTMENT OF ENVIRONMENTAL MANAGEMENT We Protect Hoosiers and Our Environment.

100 N. Senate Avenue • Indianapolis, IN 46204

(800) 451-6027 • (317) 232-8603 • www.idem.IN.gov

Michael R. Pence Thomas W. Easterly Governor Commissioner

SENT VIA U.S. MAIL: CONFIRMED DELIVERY AND SIGNATURE REQUESTED TO: Rick Chubb

Superior Hardwoods PO Box 406

Montezuma, IN 47862 DATE: January 7, 2015 FROM: Matt Stuckey, Branch Chief Permits Branch Office of Air Quality SUBJECT: Final Decision MSOP - Administrative Amendment 121 - 35251 - 00020 Enclosed is the final decision and supporting materials for the air permit application referenced above. Please note that this packet contains the original, signed, permit documents. The final decision is being sent to you because our records indicate that you are the contact person for this application. However, if you are not the appropriate person within your company to receive this document, please forward it to the correct person. A copy of the final decision and supporting materials has also been sent via standard mail to: Dorsie Bailey, GM Jody Lindsey Environmental Compliance Services OAQ Permits Branch Interested Parties List If you have technical questions regarding the enclosed documents, please contact the Office of Air Quality, Permits Branch at (317) 233-0178, or toll-free at 1-800-451-6027 (ext. 3-0178), and ask to speak to the permit reviewer who prepared the permit. If you think you have received this document in error, please contact Joanne Smiddie-Brush of my staff at 1-800-451-6027 (ext 3-0185), or via e-mail at [email protected].

Final Applicant Cover letter.dot 6/13/2013

An Equal Opportunity Employer

Recycled Paper

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Mail Code 61-53

IDEM Staff LPOGOST 1/7/2015 Superior Hardwoods 121 - 35251 - 00020 /final)

AFFIX STAMP HERE IF USED AS CERTIFICATE OF MAILING

Name and address of Sender ►

Indiana Department of Environmental Management Office of Air Quality – Permits Branch 100 N. Senate Indianapolis, IN 46204

Type of Mail:

CERTIFICATE OF MAILING ONLY

Line Article

Number Name, Address, Street and Post Office Address Postage Handing

Charges Act. Value (If Registered)

Insured Value

Due Send if COD

R.R. Fee

S.D. Fee S.H. Fee

Rest. Del. Fee Remarks

1 Rick Chubb Superior Hardwoods PO Box 406 Montezuma IN 47862 (Source CAATS) Via confirmed delivery 2 Dorsie Bailey GM Superior Hardwoods PO Box 406 Montezuma IN 47862 (RO CAATS) 3 Parke County Commissioners 116 West High Street Rockville IN 47872 (Local Official) 4 Mr. Gary Hanner Hanner Hanner & Hanner P.O. Box 122 Rockville IN 47872 (Affected Party) 5 Parke County Health Department 116 W. High St. Room 10 Rockville IN 47872 (Health Department) 6 Montezuma Town Council P.O. Box 26 Montezuma IN 47862 (Local Official) 7 Jody Lindsey Environmental Compliance Services, Inc. PO Box 356 Sherman MS 33869 (Consultant) 8 Todd Crane 428 East Cran Road Rosedale IN 47872 (Affected Party) 9 Robert Mathis 858 North Canal Road Montezuma IN 47862 (Affected Party) 10 William Kautz 2905 East 700 South Dana IN 47847 (Affected Party) 11 Jim Busenbark 5718 West Leatherwood Road Montezuma IN 47862 (Affected Party) 12 13 14 15 Total number of pieces Listed by Sender

Total number of Pieces Received at Post Office

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The full declaration of value is required on all domestic and international registered mail. The maximum indemnity payable for the reconstruction of nonnegotiable documents under Express Mail document reconstructing insurance is $50,000 per piece subject to a limit of $50, 000 per occurrence. The maximum indemnity payable on Express mil merchandise insurance is $500. The maximum indemnity payable is $25,000 for registered mail, sent with optional postal insurance. See Domestic Mail Manual R900, S913, and S921 for limitations of coverage on inured and COD mail. See International Mail Manual for limitations o coverage on international mail. Special handling charges apply only to Standard Mail (A) and Standard Mail (B) parcels.

FACSIMILIE OF PS Form 3877