COUNTY OF KNOX

PERMIT NO. V-0008R3



# TITLE V OPERATING PERMIT

ISSUED BY KNOX COUNTY DEPARTMENT OF AIR QUALITY MANAGEMENT

140 DAMERON AVENUE, SUITE 242 KNOXVILLE, TN 37917

ISSUED TO: CEMEX, Inc., Knoxville Cement Plant

MAILING ADDRESS: P.O. Box 14009, Knoxville, TN 37914

FACILITY LOCATION: 6212 Cement Plant Road

RESPONSIBLE OFFICIAL

NAME: Mr. William V. Fleming TITLE: Plant Manager

MAILING ADDRESS: P.O. Box 14009, Knoxville, TN 37914

PHONE: (865) 541-5500

PERMIT CONTACT PERSON FOR THE FACILITY

NAME: Kathy Sharp TITLE: Environmental Manager

MAILING ADDRESS: P.O. Box 14009, Knoxville TN 37914 PHONE: (865) 541-5514

THIS PERMIT IS ISSUED PURSUANT TO THE PROVISIONS OF THE STATE OF TENNESSEE AIR POLLUTION CONTROL REGULATIONS; PUBLIC CHAPTER NO. 367 AMENDED; PRIVA TE CHAPTER NO. 37; AND SECTION 25 OF THE KNOX COUNTY AIR

POLLUTION CONTROL REGULATIONS. THIS PERMIT FULFILLS THE REQUIREMENTS OF TITLE V OF THE FEDERAL CLEAN AIR

ACT AND THE FEDERAL REGULATIONS PROMULGATED THERE UNDER AT 40 CFR PART 70. THE PERMITTEE HAS BEEN

GRANTED PERMISSION TO OPERATE AN AIR CONTAMINANT S OURCE IN ACCORDANCE WITH EMISSION LIMITATIONS AND MONTORING REQUIREMENTS SET FORTH HEREIN.

THIS PERMIT IS ISSUED SUBJECT TO THE ACCURACY OF ALL INFORMATION SUBMITTED RELATING TO THE PERMIT

APPLICATION AND TO ANY CONDITIONS NOTED AND IS NOT TRANSFERABLE.

THIS PERMIT MAY BE REVOKED AT ANY TIME A VI OLATION OF THE KNOX COUNTY AIR QUALITY MANAGEMENT

REGULATIONS OR THE TENNESSEE AIR POLLUTION CONTROL REGULATIONS, WHICHEVER IS APPLICABLE, OCCURS.

A COPY OF THIS PERMIT MUST BE KEPT AT THE FACILTY LOCATION LISTED ABOVE

DATE ISSUED : March 14, 2007

RENEWAL APPLICATION DEADLINE : May 5, 2011

EXPIRATION DATE : N OVEMBER 5, 2011

### M ODIFICATIONS TO PERMIT 

### :

Administrative Amendments – 04/04/2002 Significant Modifications and Administrative Amendments – 11/30/04

Administrative Amendment - 03/14/07



### CONTENTS

Introduction



### A. GENERAL PERMIT CONDITIONS A1. Severability clause A2. Duty to comply A3. Need to halt or reduce activity not a defense A4. Modification, revocation, etc for cause A5. No property rights A6. Duty to provide information A7. Inspection and entry A8. Payment of fees A9. Emission trading A10. Certification of all documents and reports A11. Compliance certification A12. Federally-enforceable requirements A13. Re-openings for cause A14. Record keeping and monitoring requirements

A15. Retention of records A16. Reporting requirements

A17. Definitions A18. Duty to supplement and correct

A19. Asbestos A20. Stratospheric ozone and climate protection A21. Emergency provision A22. Off-permit changes A23. Section 502(b)(10) changes

A24. New source review A25. Permit renewal and expiration A26. 112(r)

A27. Violations A28. Malfunction of EquipmentB



### . SPECIFIC FACILITY CONDITIONS B1. Fee Payment: Actual Emission Basis B2. Operational Restrictions B3. Reporting B4. Monitoring and Record Keeping B5. Testing Requirements B6. Insignificant Activities B7. Locally Enforceable Regulations B8. Miscellaneous Requirements

C



### . SOURCE SPECIFIC CONDITIONS



### , OPERATING LIMITATIONS



### , AND MONITORING



### , RECORD KEEPING



### , AND REPORTING REQUIREMENTS FOR EMISSION UNIT THE

PRIMARY AND SECONDARY CRUSHER 

### :

C1. Emission limits C2. Operational restrictions C3. Monitoring and/or record keeping requirements C4. Reporting requirements C5. Testing requirements C6. Miscellaneous requirements



### D. SOURCE SPECIFIC CONDITIONS



### , OPERATING LIMITATIONS



### , AND MONITORING



### , RECORD KEEPING



### , AND REPORTING REQUIREMENTS FOR ALL MISCELLANEOUS

SOURCES 

### :

D1. Emission limits D2. Operational restrictions D3. Monitoring and/or record keeping requirements D4. Reporting requirements D5. Testing requirements D6. Miscellaneous requirements



### E. SOURCE SPECIFIC CONDITIONS



### , OPERATING LIMITATIONS



### , AND MONITORING



### , RECORD KEEPING



### , AND REPORTING REQUIREMENTS FOR THE COAL MILL 

### :

E1. Emission limits E2. Operational restrictions E3. Monitoring and/or record keeping requirements E4. Reporting requirements E5. Testing requirements E6. Miscellaneous requirements



### F. SOURCE SPECIFIC CONDITIONS



### , OPERATING LIMITATIONS



### , AND MONITORING



### , RECORD KEEPING



### , AND REPORTING REQUIREMENTS FOR THE KILN



### , CRUSHER 

### / DRYER



### , AND CLINKER COOLER 

### :F1. Emission limits F2. Operational restrictions F3. Monitoring and/or record keeping requirements F4. Reporting requirements F5. Testing requirements F6. Miscellaneous requirements F7. NESHAP Requirements



### G. SOURCE SPECIFIC CONDITIONS



### , OPERATING LIMITATIONS



### , AND MONITORING



### , RECORD KEEPING



### , AND REPORTING REQUIREMENTS FOR FUGITIVE SOURCES 

### :

G1. Emission limits G2. Operational restrictions G3. Monitoring and/or record keeping requirements G4. Reporting requirements G5. Testing requirements G6. Miscellaneous requirements

ATTACHMENTS A. NSPS 40 CFR 60 Subpart OOO B. NSPS 40 CFR 60 Subpart Y C. NESHAP 40 CFR 63 Subpart LLL

D. Emission Factor Information

### CEMEX Title V Operating Permit

Introduction

The CEMEX, Inc., Knoxville Facility manufactures cement and masonry products by the thermal processing of specially blended sources of calcium, aluminum, silica, and iron. The primary source of fuel for this thermal conversion is coal. However, natural gas, petroleum products, tires, and used oil are also utilized as an energy source. In addition, non-hazardous plant generated waste such as oily materials/rags/absorbent and spill clean-up materials are periodically transferred to

the kiln.

Used oils and other supplemental fuels (e.g. natural gas, petroleum products) are utilized on an intermittent basis and provide a mechanism to respond quickly and effectively to variations in the burning coal. The used oil can also be used at times when the coal mill is operating below production needs or to enhance the BTU input to the kiln. In addition, during periods of electrical/natural gas outages the petroleum products and used oil can provide sufficient heat to the kiln to prevent major damages to the system from sudden loss of electricity.

The manufacturing of cement and masonry products involves the grinding and special blending of raw materials such as mined limestone, clay and sand. Other non-mining sources of calcium, aluminum, silica, and iron are also available. These non-mining sources are typically non-hazardous by-products that can be beneficially used as an alternative or additive to limestone, clay and sand mixtures.A. GENERAL PERMIT CONDITIONS :

A1. Severability clause. If any part of this permit is declared invalid, the remainder of this permit shall remain in effect and enforceable (Section 25.70-F.1.e)

A2. Duty to comply. The permittee must comply with all conditions of the Part 70 permit. Any permit noncompliance constitutes a violation of the Act and is grounds for enforcement action; for permit termination, revocation and reissuance, or modification; or for denial of a permit renewal application. (Section 25.70-F.1.f(1))

A3. Need to halt or reduce activity not a defense. It shall not be a defense for a permittee in an enforcement action that it would have been necessary to halt or reduce the permitted activity in order to maintain compliance with the conditions of this permit. (Section 25.70- F.1.f(2))

A4. Modification, revocation, etc for cause. The permit may be modified, revoked, reopened, and reissued, or terminated for cause. The filing of a request by the permittee for a permit modification, revocation and reissuance, or termination, or of a notification of planned changes or anticipated noncompliance does not stay any permit condition. (Section 25.70.F-1.f(3))

A5. No property rights. The permit does not convey any property rights of any sort, or any exclusive privilege (Section 25.70.F.1.f(4))

A6. Duty to provide information. The permittee shall furnish to the Department, within a reasonable time, any information that the Department may request in writing to determine whether cause exists for modifying, revoking and reissuing, or terminating the permit or to determine compliance with the permit. Upon request, the permittee shall also furnish to the Department copies of records required to be kept by the permit. For information claimed to be confidential, the permittee may furnish such records directly to the Director along with a claim of confidentiality. (Section 25.70-F.1.f(5))

A7. Inspection and entry. Inspection and entry requirements that require that, upon presentation of credentials and other documents as may be required by law, the permittee shall allow the Director or an authorized representative to perform the following:

(1) Enter upon the permittee's premises where a Part 70 source is located or emissions-related activity is conducted, or where records must be kept under the conditions of the permit;

(2) Have access to and copy, at reasonable times, any records that must be kept under the conditions of the permit;

(3) Inspect at reasonable times any facilities, equipment (including monitoring and airpollution control equipment), practices, or operations regulated or required under the permit; and

(4) As authorized by the Act, sample or monitor at reasonable times substances or parameters for the purpose of assuring compliance with the permit or applicable requirements. (Section 25.70-F.3.b)

A8. Payment of Fees. The source must pay fees to the Knox County Department of Air Quality Management consistent with the approved fee schedule (Section 25.70-F.1.g)

A9. Emissions trading. No permit revision shall be required, under any approved economic incentives, marketable permits, emission trading and other similar programs or processes for changes that are provided for in the permit. Such provisions must meet the requirements of 40 CFR 70.4(b)(12)(i) and (iii). (Section 25.70-F.1.h)

A10. Certification of all documents and reports. Any application form, report, or compliance certification submitted pursuant to these regulations shall contain certification by a responsible official of truth, accuracy, and completeness. This certification and any other certification required under this part shall state that, based on information and belief formed after reasonable inquiry, the statements and information in the document are true, accurate, and complete. (Section 25.70-F.3.a)

A11. Compliance certification. Compliance certifications shall be submitted by January

25 th of each year for the previous calendar year beginning with the effective date of the permit. Compliance certifications shall be submitted to the Knox County Department of Air Quality Management and EPA.

Compliance certifications shall include:

(1) The identification of each term or condition of the permit that is the basis of the certification;

(2) The compliance status;

(3) Whether compliance was continuous or intermittent;

(4) The method(s) used for determining the compliance status of the source, currently and over the reporting period consistent with required monitoring; and

(5) Such other facts as the Knox County Department of Air Quality Management may require to determine the compliance status of the source (Section 25.70-F.3.e(3))

EPA Address: U.S. EPA Region 4Air and EPCRA Enforcement Branch 61 Forsyth Street, SW Atlanta, GA 30303

KCDAQM Address: 140 Dameron Avenue

Suite 242 Knoxville, Tennessee 37917

A12. Federally-enforceable requirements. All terms and conditions in a Part 70 permit, including any provisions designed to limit a source's potential to emit, are enforceable by the Administrator and citizens under the Act.(Section 25.70-F.2.a.)

A13. Reopenings for Cause. Each issued permit shall include provisions specifying the conditions under which the permit will be reopened prior to the expiration of the permit. A permit shall be reopened and revised under any of the following circumstances:

(1) Additional applicable requirements under the Act become applicable to a major Part 70 source with a remaining permit term of 3 or more years. Such a reopening shall be completed not later than 18 months after promulgation of the applicable requirement. No such reopening is required if the effective date of the requirement is later than the date on which the permit is due to expire, unless the original permit or any of its terms and conditions has been extended by an EPA approved program pursuant to

Section 25.70-M.

(2) Reserved

(3) The Department or EPA determines that the permit contains a material mistake or that inaccurate statements were made in establishing the emissions standards or other terms or conditions of the permit.

(4) The Administrator or the Department determines that the permit must be revised or revoked to assure compliance with the applicable requirements.(Section 25.70-G.6.a)

A14. Recordkeeping and Monitoring requirements. Where applicable, the permittee must maintain the following: Records of required monitoring information that include the following:

(1) The date, place as defined in the permit, and time of sampling or

measurements;

(2) The date(s) analyses were performed;(3) The company or entity that performed the analyses;

(4) The analytical techniques or methods used;

(5) The results of such analyses; and

(6) The operating conditions as existing at the time of sampling or

measurement; (Section 25.70-F.1.c(1) and c(2))

A15 Retention of records. The permitee must retain records of all required monitoring data and support information for a period of at least 5 years from the date of the monitoring sample, measurement, report, or application. Support information includes all calibration and maintenance records and all original strip-chart recordings for continuous monitoring instrumentation, and copies of all reports required by the permit. (Section 25.70-F.1.c(2))

A16. Reporting Requirements. The permittee must:

(1) Submit reports of any required monitoring at least every six months as specified in B3 of this permit. All instances of deviations from permit requirements must be clearly identified in such reports. All required reports must be certified by a responsible official consistent with 25.70-E.4. All reports shall be submitted to the Knox County Department of Air Quality Management.

(2) Promptly report to Knox County Department of Air Quality Management deviations from permit requirements, including those attributable to malfunction of equipment as specified in Knox County Air Quality Management Regulation 34.0, the probable cause of such deviations, and any corrective actions or preventive measures taken. The term "prompt", in relation to the degree and type of permit deviations likely to occur, is defined to be within 24 hours of when the permit deviation occurs. (Section 25.70- F.1.c(3))

A17. Definitions . The terms not otherwise defined in this permit have the meaning assigned to them in the referenced regulations.

A18. Duty to supplement and correct. Duty to supplement or correct application. Any applicant who fails to submit any relevant facts or who has submitted incorrect information in a permit application shall, upon becoming aware of such failure or incorrect submittal, promptly submit such supplementary facts or corrected information. In addition, an applicant shall provide additional information as necessary to address any requirements that become applicable to the source after the date it filed a complete application but prior to release of a draft permit. (Section 25.70-E.2)

A19. Asbestos . The permittee shall comply with 40 CFR part 61, subpart M (asbestosNESHAP) when conducting any renovation or demolition at the facility.

A20. Stratospheric ozone and climate protection . The permittee shall comply with the standards for recycling and emissions reducti on as provided in 40 CFR part 82, subpart F.

A21. Emergency provision. (1) Definition. An "emergency" means any situation arising from sudden and reasonably unforeseeable events beyond the control of the source, including acts of God, which situation requires immediate corrective action to restore normal operation, and that causes the source to exceed a technology-based emission limitation under the permit, due to unavoidable increases in emissions attributable to the emergency. An emergency shall not include noncompliance to the extent caused by improperly designed equipment, lack of preventative maintenance, careless or improper operation, or

operator error.

(2) Effect of an emergency. An emergency constitutes an affirmative defense to an action brought for noncompliance with such technology-based emission limitations if the conditions of paragraph 3 of this section are met.

(3) The affirmative defense of emergency shall be demonstrated through properly signed, contemporaneous operating logs, or other relevant evidence that:

(a) An emergency occurred and that the permittee can identify the cause(s) of the emergency; (b) The permitted facility was at the time being properly operated;

(c) During the period of the emergency the permittee took all reasonable steps to minimize levels of emissions that exceeded the emission standards, or other requirements in the permit; and

(d) The permittee immediately notified the Department by phone or fax and submitted written notice of the emergency to the Department within 24

hours of the time when emission limitations were exceeded due to the emergency. This notice fulfills the requirement of paragraph A.16.(2) of this permit. This notice must contain a description of the emergency, any steps taken to mitigate emissions, and corrective actions taken.

(4) In any enforcement proceeding, the permittee seeking to establish the occurrence of an emergency has the burden of proof.

(5) This provision is in addition to any emer gency or upset provision contained in any applicable requirement. (Section 25.70-F.7)

A22. Off-permit changes.(1) The Department will allow changes that are not addressed or prohibited by the permit, other than those described in Section 25.70.P, to be made without a permit revision providing they meet the requirements of 25.70.O.1.a through c.

(a) Each such change shall meet all applicable requirements and shall not violate any existing permit term or condition.

(b) Sources must provide contemporaneous written notice to the Department and EPA of each such change, except for changes that qualify as insignificant under the provisions adopted pursuant to 25.70.E.3. Such written notice shall describe each such change, including the date, any change in emissions, pollutants emitted, and any applicable requirement that would apply as a result of the change.

(c) Reserved

(d) The permittee shall keep a record describing changes made at the source that result in emissions of a regulated air pollutant subject to an applicable requirement, but not otherwise regulated under the permit, and the emissions resulting from those changes.

(2) General off-permit prohibitions

Sources are prohibited from making, without a permit revision, changes that are not addressed or prohibited by the Part 70 permit, if such changes are subject to any requirements under Title IV of the Act or are modifications under any provision of Title I of the Act. (Section 25.70-P and O)

A23. Section 502(b)(10) changes. Consistent with paragraph 2 of this section the Department will allow changes within a permitted facility without requiring a permit revision if the changes are not modifications under any provision of Title I of the Act and the changes do not exceed the emissions allowable under the permit (whether expressed therein as a rate of emissions or in the terms of total emissions): provided that the facility provides the Administrator and the Department with written notification as required below in advance of the proposed changes, which shall be a minimum of 21 days, unless the Department provides in its regulations a different time frame for emergencies. The source, Department, and EPA shall attach each such notice to their copy of the relevant permit. The following provisions implement this requirement of an approvable Part 70 permit program:

(1) The Department shall allow permitted sources to make Section 502(b)(10) changes without requiring a permit revision if the changes are not modifications under any provision of Title I of the Act and the changes do not exceed the emission allowable under the permit (whether expressed therein as a rate ofemissions or in terms of total emissions).

(2) For each such change, the written notification required above shall include a brief description of the change within the permitted facility, the date on which the change will occur, any change in emissions, and any permit term or condition that is no longer applicable as a result of the change. (Section 25.70-N.1)

A24. New source review . The permittee shall not construct or make modifications to the source required to be reviewed under Departme nt regulations without receiving an approval or permit under such provisions.

A25. Permit renewal and expiration. Permit expiration terminates the source's right to operate unless a timely and complete renewal application has been submitted consistent with the following paragraph of this section and 25.70-E.1.a(3).

For purposes of permit renewal, a timely application is one that is submitted at least six months prior to the date of permit expiration, or such other longer time as may be approved by the Administrator that ensures that the term of the permit will not expire before the permit is renewed. In no event shall this time be greater than 18 months.(Section 25.70-E.1.a(3))

A26. 112(r). The permittee shall comply with the requirement to submit to the Administrator or designated State Agency a risk management pl an, including a registration that reflects all covered processes, by June 21, 1999, if the permittee's facility is required pursuant to 40 CFR, 68, to submit such a plan.

A27. Violations.

(1) Violation of any regulation duly adopt ed by the Board is declared to be a misdemeanor punishable as provided by Tennessee law.

(2) Violation of any regulation or section of the regulations is considered a separate offense.

(3) Each day of violation of any regula tion or section of the regulations is considered a separate offense.

(4) The Director shall have the power and authority to issue an order which assesses civil penalties against any person responsible for the violation of the regulations as provided by Tenness ee law. These penalties shall be

recoverable in a maximum amount of $25,000 per day per violation as provided by state law.(5) Whenever evidence has been obtained or received establishing that a violation of the regulations has been committed, the Director shall have the power and authority to initiate proceedings to prosecute the violator.

(6) The Director may cause to be ins tituted a civil action in any court of competent jurisdiction for injunctive relief to prevent violation of any regulation promulgated by the Board or of any order duly issued by the Director (as confirmed or modified by th e Board, if this be the case). Such actions may be taken by the Director without the necessity of a prior revocation of any permit.

(7) Nothing in these regulations shall prevent the Director from making efforts to obtain voluntary compliance with the regulations by issuing a notice to correct or cease the violation. Such notice shall briefly set forth the general nature of the violation and specify a reasonable time within which the violation shall be rectified or stopped. If the violation is not corrected within the time so specified, or the violation stopped, or reasonable steps taken to rectify the violation, the Director shall have the power and authority to issue an order requiring the violator to cease or suspend operation of the facility causing the violation until the violation has been corrected. The Director has the authority to restrain or enjoin immediately and effectively any person, by order or by suit in court, from engaging in any activity in violation of a permit or the Knox County Air Quality Management Regulations that is presenting an imminent and substantial endangerment to the public health or welfare, or the environment.

(8) Where a time for compliance schedule has been established in the regulations, failure to comply with the time schedule by any person shall be considered a violation of the regulations.

(9) When any person has been requested by the Director to submit to the Director an acceptable proposal and time schedule and fails to do so in the time allocated by the Director fo r submitting such proposal and time schedule, such person shall be considered in violation of the regulations.

(10) Where an acceptable proposal and timetable has been submitted to the Director by any person, failure to comply with the proposal and time schedule shall be considered a violation of the regulations.

(11) Where a violation of the regulations occurs by any person, it shall be presumed that such violation occurred with the knowledge and consent of such person.

Authority for requirement: KCDAQM Regulations section 30.0A28. Malfunction of Equipment : The permittee shall comply with the regulations delineated in section 34.0 of the Knox County Department of Air Quality Management Regulations during periods of malfunction. (Section 34.0)B. SPECIFIC FACILITY CONDITIONS:

B1. Fee Payment: Actual Emission Basis

Fee Emissions Summary for CEMEX Inc., Knoxville Cement Plant.

REGULATED POLLUTANTS ACTUAL

EMISSIONS (tons per AAP*) COMMENTS

PM AEAR

SO 2 AEAR VOC AEAR This includes, but is not limited to, THC in Attachment D of this permit.

NO X AEAR

HAP’s AEAR This is the summation of all the HAPs excluding VOC and PM in the above

column.

NOTES

* AAP The Annual Accounting Period ( AAP ) is a twelve (12) consecutive month period that begins each January 1st and ends December 31 st

. The

present Annual Accounting Period began January 1, 2001 and ends December 31, 2001. The next Annual Accounting Period begins January 1, 2002 and ends December 31, 2002.

AEAR indicates that an A ctual E missions A nalysis is required to determine the

actual emissions of:

Each regulated pollutant (PM, SO 2 , VOC, NO X and HAP’s)

END NOTES

(a) The permittee shall: (1) Prepare an actual emissions analysis beginning January 1, 2002 in accordance with the

above Fee Emissions Summary Table. The actual emissions analysis shall include: (a) the completed Fee EmissionsSummary Table

, (b) each AEAR required by the above Fee Emissions Summary Table, and (c) the records required by record keeping Conditions of this permit. These records shall be used to complete the

AEARs required by the above Fee Emissions Summary Table

. (2) Submit the actual emissions analysis at the time the fees are paid in full.

(3) Calculate the fee due based upon the actual emissions analysis , and submit the payment within 30 days after January 1 st following the end of the annual accounting period . If the fee is not paid within fifteen (15) days of the due date, penalties shall at once accrue as specified in KCDAQM Regulations 25.8.H. Major sources may request an extension of time to file their emissions analysis with the Director.

Payment of the fee due and the actual emissions analysis shall be submitted to Knox County Department of Air Quality Management at the following

address:

140 Dameron Avenue

Suite 242 Knoxville, Tennessee 37917

B2. Emission Limitations

1. The annual emissions from this facility are limited as follows:

Pollutant Emissions Limit, tons

per year NO X 1980.1

SO 2 289.4

CO 970.5

VOC 53.1

PM

2. The hourly and process based emissions from this facility are limited as follows:Pollutant Emission Limit, pounds per hour * Emission Limit, pounds per ton kiln feed

NO X 619.00

SO 2 90.00

CO 303.00

VOC 16.60

PM from

Kiln 0.30

PM from

Clinker

Cooler 0.10

*30 day rolling one hour average

Authority for requirement: KCDAQM Regulations section 25.3 I.

B3. Operating Restrictions

CEMEX shall, on the original effective date of this permit, meet the requirements of 40 CFR 60 Subpart F subsumed in sections 63.1343-1345, 63.1347, 63.1348, 1350 (a)(4), 1350 (d), and 1350 (e) of 40 CFR 63 Subpart LLL (Attachment C) as contained in Attachment D and F7. of this permit.

CEMEX shall meet the remaining requirements contained in 40 CFR 63 Subpart LLL (Attachment C of this permit) by the specified time period contained therein.

Authority for requirement: KCDAQM Regulations section 35.0

CEMEX shall meet the following requirements for reductions in NO X emissions:

Definitions

For the purpose of this section, the following definitions apply:

“Clinker” shall mean the product of a Po rtland cement kiln from which finished cement is manufactured by milling or grinding.

“Low-NOX burners” shall mean combusti on equipment designed to reduce flame turbulence, delay fuel/air mixing, and establish fuel rich zones for initial

combustion.

“Malfunction” shall mean any sudden, in frequent, and not reasonably preventablefailure of air pollution control equipment, process equipment, or a process to operate in a normal or usual manner. Failures that are caused in part, or in whole, by poor maintenance or careless operation are not malfunctions.

“Mid-kiln firing” shall mean the secondary firing in kiln systems by injecting fuel at an intermediate point in the kiln system using specially designed feed injection mechanisms for the purpose of decreasing NOX emissions through:

Burning part of the fuel at lower temperature; and

Reducing conditions at the fuel inj ection point that may destroy some of the NOX upstream in the kiln-burning zone.

“Portland cement” shall mean a hydraulic cement produced by pulverizing clinker consisting essentially of hydraulic calcium silicates, usually containing one or more of the forms of calcium sulfate as an interground

addition.

“Portland cement kiln” shall mean a system, including any solid, gaseous or liquid fuel combustion equipment, used to calcine and fuse raw materials, including limestone and clay, to produce Portland cement clinker.

“Precalciner kiln” shall mean a kiln system where the feed to the kiln system is preheated in cyclone chambers and utilize a second burner to calcine material in a separate vessel attached to the preheater prior to the final

fusion in a kiln which forms clinker.

“Preheater kiln” shall mean a kiln system where the feed to the kiln system is preheated in cyclone chambers prior to final fusion in a kiln which forms

clinker.

“Shutdown” shall mean the cessation of operation of a Portland cement kiln for any purpose.

“Startup” shall mean the setting in opera tion of a Portland cement Kiln for any

purpose.

Operating Requirements

After May 31, 2004, no owner or operator of any Portland cement kiln subject to this rule shall operate the kiln during May 1 through September 30 unless the kiln has installed and operates during May 1 through September 30 at least one of the following:

Low-NOx burners;Mid-kiln system firing; Alternative control techniques approved by the Director and the EPA as achieving at least the same emissions decreases as with low NOx burners or mid-kiln system firing; or Reasonably available control technology approved by the Director and EPA.

CEMEX shall comply with the requirements as follows:

By May 31, 2004, submit to the Director the identification number and type of each unit subject to this section, the name and address of the plant where the unit is located, and the name and telephone num ber of the person responsible for demonstrating compliance with paragraph 1 of this section.

By October 31, 2004, submit a report to the Director documenting for that kiln the total NOX emissions from May 31, 2004, through September 30, 2004, and beginning in 2005 submit by October 31 of each year to the Director a report documenting NOx emissions from May 1 through September 30 of that year.

By May 31, 2004, the owner or operator of a k iln subject to this rule shall submit to the Director a demonstration of complian ce with the requirements of paragraph 1.If compliance is being achieved by use of prescribed equipment, for example lowNOx burners or mid-kiln system firing, th e demonstration of compliance shall be a

written certification to the Director that this equipment is installed and is in use. If compliance is being achieved by use of a lternative control techniques approved by the Director and the EPA, demonstration of compliance shall be as specified by the Director and EPA. In the case of comp liance proposed to be achieved by use of alternative control techniques, a plan for compliance demonstration shall be submitted to the Director by May 31, 2003. Upon receipt the Director shall immediately forward a copy of the plan to the EPA. By November 1, 2003, the Director shall specify in writing to th e owner or operator of the kiln how compliance shall be demonstrated, this specification consistent with methods and requirements specified by the EPA following its review of the submitted plan.

By December 31 of each year, beginning in 2004, the owner or operator of a kiln subject to this rule shall submit to the Director a written compliance certification that compliance with the requirements of Paragraph 1 has been maintained during the five month period May 1 thr ough September 30, except for 2004 when compliance is to be maintained from May 31 through September 30. The methods for determining that this compliance has b een maintained shall be specified on the major source operating permit issued for the facility at which the kiln is operated

Record Keeping

Beginning May 31, 2004, CEMEX shall main tain records from May 31 through September 30 of that year, and in subsequent years for May 1 through September 30, that include the data as follow:a. The date, time, and duration of a ny startup, shutdown, or malfunction in the operation of the cement kiln or its emissions monitoring equipment or of any scheduled main tenance activity that affects NOx emissions or emissions monitoring.

b. The results of any compliance testing.

c. Other data required by permit to be maintained.

Records shall be retained on-site for a mini mum of 5 years following the calendar year for which they are made and shall be made av ailable to the Director for his review upon

request.

D. Exceptions

The requirements of this rule shall not apply during periods of operation as

follows:

1. Periods of scheduled maintenance that affect NOx emissions.

2. Periods of malfunctions, startups , and shutdowns. These periods are subject to the requirements of Section 34.0 of the Knox County Department of Air Quality Management Regulations.

Authority for requirement: KCDAQM Regulations section 51.0

B4. Reporting

.

The permittee must prepare and submit semi-annual reports of all required monitoring and recordkeeping contained in this permit to this Department no later than July 31 st and January 31 st of each year.

The permittee shall use CEM (continuous emissions monitoring) systems data or emission factors set forth in Attachment D of this permit to calculate emissions of SO 2 , NO

x , CO, and PM. The emission factors provided in Attachment D may be revised to incorporate the results of additional testing; however, the emissions inventory must document the source of the data. A summary of emission calculations shall be submitted by Janauary 31 st of each

year.

Authority for requirement: KCDAQM Regulations section 26.5.B

B5. Monitoring and Record Keeping

CEMEX shall meet the monitoring and recordkeeping requirements contained in this permit.CEMEX shall install and operate a CEM system for NOX, SO2, and CO within 30 days of the issuance of this permit. These monitors shall be operated under the quality assurance of requirements of 40 CFR 75. Additionally, CEMEX shall calculate the VOC emissions rate using data from the hourly average CO and SO 2 CEMS along with the hourly average percentage of CO2 and O2. The VOC emission rate shall be calculated using the following equation:

EM VOC = -38.9824 + (EM CO2 X 1.6274) + (EM O2 X 1.3600) + (EM SO2 X -0.0232),

Where,

EM VOC is the emission rate of VOC in lb/hr;

EM CO2 is the percentage of CO 2 in the flue gas;

EM O2 is the percentage of O 2 in the flue gas; and

EM SO2 is the emission rate of SO 2 in lb/hr.

B6. Testing Requirements.

A stack test shall be conducted once every 30 months for Dioxins/Furans emissions. The first test shall be conducted in accordance with the testing schedule for Dioxin/Furans in 40 CFR 63, Subpart LLL.

Stack tests shall be performed once every 30 months for PM. The first must be conducted within 36 months of the initial issuance date of this permit (November 5, 2001).

Stack tests shall be performed once every 12 months for VOC. The first must be conducted within 6 months of the issuance date of this permit.

For each stack test, CEMEX must submit a test plan to the Department for review. The Department will approve or disapprove the test plan within 30 days. After the test plan is approved, CEMEX must notify the Department of the dates of the stack test at least 30 days prior to conducting the stack test. The results of the stack test shall be submitted directly to the Department from the stack test within 60 days.

Authority for requirement: KCDAQM Regulations section 26.4.B.3 and 35.0

B7. Insignificant Activities

.

The following is an insignificant activities description based on the Part 70 operating permit application:

1. All storage tanks used exclusively to store fuel oils, kerosene, diesel, jet fuel, natural gas, or liquefied petroleum gas. These include:Three fixed roof diesel tanks, one 10000 and two 300 gallons capacity One fixed roof gasoline tank, 1000 gallons capacity built in 04/93 Three 500 gallon capacity lube oil or waste oil tanks built in 1989 One 6000 gallon hydrophobe tank built in 1975 One 12000 gallon grinding aid tank built in 1975 One 250 gallon Mobile Oil Wagon built in 1993 One 300 gallon Kerosene Tank One 38,415 Grinding Aid Tank One 38,415 Used Oil Tank One 300 gallon antifreeze tank

2. Two Diesel Emergency Generators

B8. Locally Enforceable Regulations.

The following requirements are locally enforceable only.

No person shall cause, suffer, allow, or permit open burning of any kind except as specifically permitted in section 16.0 of the Knox County Department of Air Quality Management Regulations.

Authority for requirement: KCDAQM Regulations section 16.0

No person shall cause, suffer, or allow any emissions of gases, vapors, or “objectionable” odors beyond the property line from which such emissions occur to be in sufficient quantities and of such characteristics and duration as to be injurious, to human health and welfare, plant and animal life, or which unreas onably interferes with the enjoyment of life

or property.

Authority for requirement: KCDAQM Regulations section 21.0

B9. Miscellaneous Requirements

Unless otherwise specified, the averaging times for the applicable emission and/or opacity limits in this permit are tied to or based upon the run time of the test methods used for determining compliance.

Authority for requirement: KCDAQM Regulations section 25.70.F.1C. SOURCE SPECIFIC CONDITIONS, OPERATING LIMITATIONS, AND MONITORING, RECORD KEEPING, AND REPORTING REQUIREMENTS FOR

EMISSION UNIT GROUP 003 AND 004:

Emission unit description :

Emission unit group 003 is comprised one emission unit. Emission unit 003-02 is the Primary Crusher for the cement plant. 003-02 is an impact crusher that has a design capacity of 800 tons per hour and is manufactured by Hazemag (model # APP-1822-GP). This emission unit is controlled by the Primary Crusher Baghouse (control equipment I.D. 0001).

Emission unit group 004 is comprised of emission unit 004-01. Emission unit 004-01 is the secondary crusher for the cement plant. 004-01 is manufactured by Hammermills, Inc. (Model # MH1-06-C1). This emission unit is controlled by a baghouse (control equipment I.D. 0002).

C1. Emission limits:

Emission unit group 003 and 004 shall meet the standard for particulate matter in section 60.672 Attachment A of this permit.

Authority for requirement: KCDAQM Regulations section 40.0

C2. Operating Restrictions:

Both emission unit groups (003 and 04) are applicable to 40 CFR 60 Subpart OOO. The provisions of Subpart OOO are contained in Attachment A of this permit. CEMEX shall maintain compliance with all applicable parts of 40 CFR 60 Subpart

OOO.

Authority for requirement: KCDAQM Regulations section 40.0

C3. Monitoring and/or record keeping requirements:

1. These emission units shall meet the reporting and record keeping requirements (section 60.676) of Attachment A.

2. All records required by section 60.676 of Attachment A shall be maintained at the facility for a minimum of five years.

Authority for requirement: KCDAQM Regulations section 40.0

C4. Reporting Requirements.These emission units shall meet the reporting and record keeping requirements (section 60.676) of Attachment A and the semi-annual reporting requirements contained in section A16 of this permit.

Authority for requirement: KCDAQM Regulations section 40.0

C5. Testing requirements.

These emission units shall meet the test methods and procedures requirements (section 60.675) of Attachment A.

Authority for requirement: KCDAQM Regulations section 40.0

C6. Miscellaneous requirements.

These emission units shall meet the reconstruction requirements (section 60.673) of

Attachment A.

Authority for requirement: KCDAQM Regulations section 40.0D. SOURCE SPECIFIC CONDITIONS, OPERATING LIMITATIONS, AND MONITORING, RECORD KEEPING, AND REPORTING REQUIREMENTS FOR EMISSION UNIT GROUP 005, 006, 007, 008, 00B,00C, 00D, 00E, 00F, 00G, 00H, 00I, 00J, 00L, 00N, 00P, 00Q, 00R, 00S, 00T, 00U, 00V, 00W, 00X, 00Y, 00Z, 010, 011, 012, 014, 015, 016, 017, 018, 019, 01A, 01F, 01G, 01I, 01J, 01K, 01N, 01P, 01Q AND 01R :

The emission unit descriptions below are de scriptions only and are not a regulatory limitation (i.e. limestone may occasionally be stored in “Gypsum Silo #6”).

Emission Unit Group 005 Description : Emission Unit Group 005 is comprised of three emission units. These include Gypsum Silo #6 (emission unit 005-04), Additives Elevator (emission unit 005-05), and Additive Belt Conveyor (emission unit 005-06). All three emission units are controlled by a common baghouse (control equipment I.D. 0003).

Gypsum Silo # 6 (emission unit 005-04) has a 15’-10” I.D. and a capacity of 9,660 Cu.ft (510 tons) and is used to store gypsum and other material.

Additive Belt Conveyor (emission unit 005-06) moves the gypsum to the Additives Elevator (emission unit 005-05) where it is then dropped into Gypsum Silos #6, #5, #11 and

#12.

Emission Unit Group 006 Description : Emission Unit Group 006 is comprised of three emission units. These include Gypsum Silo #5 (emission unit 006-04), Weigh Belts and Conveyors (emission unit 006-05), and Iron Ore Storage Silo #11 (emission unit 006- 06). All three emission units are controlled by a common baghouse (control equipment I.D. 0004).

Gypsum Silo # 5 (emission unit 006-04) ) has a 15’-10” I.D. and a capacity of 9,660 Cu.ft (510 tons) and is used to store gypsum and other material. This emission unit discharges to the gypsum weigh feeder.

Weigh Belts and Conveyors (emission unit 006-05) conveys the gypsum from gypsum silo

# 5 to the #1 Finish mill.

Iron Ore Storage Silo #11 (emission unit 006-06) discharges to the iron feed belt.

Emission Unit Group 007 Description: Emission Unit Group 007 is comprised of four emission units. These include Limestone Silo # 3 (emission unit 007-01), Limestone Silo # 9 (emission unit 007-02), Belt Conveyor (emission unit 007-03), and Belt Conveyor (emission unit 007-04). All four emission units are controlled by a common baghouse (control equipment I.D. 0005).

Limestone Silo #3 (emission unit 007-01) conveys material to the weigh feeder conveyor

belts.

Limestone Silo #9 (emission unit 007-02) discharges material to the crusher dryer feed beltBelt Conveyor (emission unit 007-03) conveys limestone rock to silos #3 and #15

Belt Conveyor (emission unit 007-04) conveys material to silo #15

Emission Unit Group 008 Description : Emission unit group 008 is comprised of three emission units. These include Limestone Silo #14 (emission unit 008-01), Limestone Silo #15 (emission unit 008-02) and a Belt Conveyor (emission unit 008-03). All three emission units are controlled by a common baghouse (control equipment I.D. 0006)

Emission Unit Group 009 Description: Emission unit group 009 is comprised of two emission units. These include Limestone Silo #13 (emission unit 009-01) and a Belt Conveyor (emission unit 009-02). Both emission units are controlled by a common baghouse (control equipment I.D. 00007).

Emission Unit Group’s 00B, 00C, and 00D Description : 00B: This group is comprised of three emission units. These include Weigh Feeder Silo # 15 (emission unit 00B-01), Belt Conveyor (emission unit 00B-02), and Belt Conveyor (00B-03). All three emission units are controlled by a common baghouse (control equipment I.D. 000C).

Weigh Feeder Silo # 15 conveys material to the raw mill feed belt. Belt Conveyor (emission unit 00B-02) conveys material to the raw mill. Belt Conveyor (emission unit 00B-03) conveys material to the crusher/dryer.

00C: This group is comprised of two emission units. These include Weigh Feed Conveyor (Silo 3)(emission unit 00C-01) and Weigh Feed Conveyor (Silo 9)(emission unit 00C-02). Both emission units are controlled by a common baghouse (control equipment I.D. 000H).

Weigh Feed Conveyor (Silo 3) conveys material to the crusher/dryer feed belt. Weigh Feed Conveyor (Silo 9) conveys material to the crusher/dryer feed belt.

00D: This group is comprised of two emission units. These include Raw Mill (emission unit 00D-01) and Screw Conveyor (00D-02). Both emission units are controlled by a common baghouse (control equipment I.D. 000I).

The Raw Mill grinds the raw materials and discharges them to the screw conveyor. The Screw Conveyor conveys raw material to the raw mill elevator.

Emission Unit Group 00E Description : Emission unit group OOE is comprised of six emission units. These include Screw Conveyor (emission unit 00E-01), Bucket Elevator (emission unit 00E-02), Air Separator (emission unit 00E-03), Screw Conveyor (emission unit 00E-04), Hopper (emission unit 00E-05), and Hopper (emission unit 00E-06). All six emission units are controlled by a common baghouse (control equipment I.D. 000J).Screw Conveyor (emission unit 00E-01) conveys material to the bucket elevator. The Bucket Elevator conveys material to the 7 th floor screw conveyor. The Air Separator separates fines from coarse materials. Fines are sent to a pump and coarse material recirculates through the mill system. Screw Conveyor (emission unit 00E-04) conveys material to the air separator. Hopper (emission unit 00E-05 and 00E-06) conveys fines from air separator to the blending

silos

Emission Unit Group 00F Description : Emission unit group OOF is comprised of six emission units. These include Airlift Disengagement Chamber #1 (emission unit 00F-01), Airlift Disengagement Chamber #2 (emission unit 00F-02), Constant Head Feed Box (emission unit 00F-03), Weightometer West Kiln (00F-04), Weightometer East K iln (00F-05), and Check Pot (00F-06). All emission units are controlled by a common baghouse (control equipment I.D. 000K).

Airlift Disengagement Chambers #1 and # 2 lift material to the constant head feed box.

Constant Head Feed Box holds materials until th ey are ready to be withdrawn to the kiln

feed screw. Weightometer West and East weigh material before entering the preheater tower. Check Pot conveys material to the blending silos.

Emission Unit Group 00G Description : Emission unit group OOG is comprised of four emission units. These include Cyclone (emission unit 00G-01), Distribution Vessel (emission unit 00G-02), Storage Silo #1 (emission unit 00G-03), and Storage Silo #2 (emission unit 00G-04). All emission units are controlled by a common baghouse (control equipment I.D. 000L).

The Cyclone discharges feed to the distribution vessel. The Distribution Vessel conveys material to the blending silos. Storage Silo #1 and #2 blend material and release to the air slides.

Emission Unit Group 00H Description : Emission unit group OOH is comprised of four emission units. These include Distribution Vessel (emission unit 00H-01), Mixing Silo #5 (emission unit 00H-02), Mixing Silo #6 (emission unit 00H-03) Diversion Bin (emission unit 00H-04). All emission units are controlled by a common baghouse (control equipment I.D. 000M).

The Distribution Vessel distributes raw material to Silos # 5 and #6. Silos # 5 and #6 both

distribute feed to the diversion bin. The Dive rsion Bin distributes material to the flow

meter.

Emission Unit Group 00I Description : Emission unit group OOI is comprised of four emission units. These include Air Slides (emission unit 00I-01), Mixing Silo # 3 (emission unit 00I-02), Mixing Silo #4 (emission unit 00I-03), and Distribution Vessel (emission unit 00I-04). All emission units arecontrolled by a common baghouse (This particular baghouse unit was not identified in the Title V application; therefore, the control I.D. will be the facility Control I.D. which is 10- 10).

The Air Slides convey material to the distri bution vessel. Mixing Silos #3 and #4 distribute feed to the air slides. The Distribution Vessel distributes material to the mixing silos.

Emission Unit Group 00J Description : Emission unit group OOJ is comprised of four emission units. These include Flowmeter Cyclone (emission unit 00J-01), Distribution Vessel (emission unit 00J-02), Airlift #1 (emission unit 00J-03), and Airlift #2 (emission unit 00J-04). All emission units are controlled by a common baghouse (control equipment I.D. 000N).

The Flowmeter Cyclone weighs material and conveys it to the distribution vessel. The

Distribution Vessel distributes material to the airlift blower. Airlift #1 and #2 lifts material to the airlift disengagement chamber.

Emission Unit Group 00L Description : Emission unit group OOL is comprised of one emission unit. The Dust Bin (emission unit 00L-01) recycles dust to the blending silos. This emission unit is controlled by a baghouse (control equipment I.D. 000P).

Emission Unit Group 00N Description : Emission unit group OON is comprised of two emission unit. These include a Bucket Elevator (emission unit 00N-01) and Dust Bi n (emission unit 00N-02). All emission units are controlled by a common baghouse (control equipment I.D. 000Q).

The Bucket Elevator conveys alkali dust to the dust bin. The Dust Bin stores the cement kiln dust and discharges the material to the synthetic gypsum weigh feeder.

Emission Unit Group 00P Description : Emission unit group OOP is comprised of one emission unit which is a Belt Conveyor (emission unit 00P-01). This emission unit is controlled by a baghouse (control equipment I.D. 000T).

The Belt Conveyor conveys clinker to the south bucket elevator

Emission Unit Group 00Q Description : Emission unit group 00Q is comprised of one emission unit. This emission unit is the south Bucket Elevator (00Q-01). This emission unit is controlled by a baghouse (control equipment I.D. 000U). This unit conveys material to the north or south belt and/or to the

outside.

Emission Unit Group 00R Description : Emission unit group 00R is comprised of one emission unit. This emission unit is the northBucket Elevator (emission unit 00R-01). This emission unit is controlled by a baghouse (control equipment I.D. 000V). This unit conveys clinker to the silo feed belt.

Emission Unit Group 00S Description : Emission unit group 00S is comprised of one emission unit. This emission unit is the Craneway Feed Conveyor (emission unit 00S-01). The emission unit is controlled by a baghouse (control equipment I.D. 000W). This unit conveys material to the clinker storage building.

Emission Unit Group 00T Description : Emission unit group 00T is comprised of two emission units. These include two Weigh Feeder Conveyors (emission unit 00T-01 and emission unit 00T-02). All emission units are controlled by a common baghouse (control equipment I.D. 0008). Emission unit 00T-01 conveys clinker to the #1 finish mill feed belt. Emission unit 00T-02 conveys material to

the finish mill feed belt.

Emission Unit Group 00U Description : Emission unit group 00U is comprised of four emission units. These include three Belt Conveyors (emission unit 00U-01)(emission unit 00U-03)(emission unit 00U-04) and Clinker Silo #7 (emission unit 00U-02). All emission units are controlled by a common baghouse (control equipment I.D. 000E).

Emission unit 00U-01 conveys clinker to silo #7. Clinker Silo #7 stores the clinker. Emission unit 00U-03 conveys clinker to silo #2 and emission unit 00U-04 conveys

material to clinker silo #8.

Emission Unit Group 00V Description : Emission unit group 00V is comprised of three emission units. These include Clinker Silo #1 (emission unit 00V-01) and two Belt Conveyors (emission units 00V-02 and 00V-03). All emission units are controlled by a common baghouse (control equipment I.D. 000F).

Clinker Silo #1 stores clinker. Belt Conveyor 00V-02 conveys material to Clinker Silo#2 and Belt Conveyor 00V-03 feeds clinker to Clinker Silo #1

Emission Unit Group 00W Description : Emission unit group 00W is comprised of three emission units. These include Weigh Feeder Silo #15 (emission unit 00W-01), Belt Conveyor (emission unit 00W-02) and Weigh Feeder Silo #13 (emission unit 00W-03). All emission units are controlled by a common baghouse (control equipment I.D. 0009).

Weigh Feeder Silo #15 conveys material from the silo to the raw mill feed belt. The Belt Conveyor (emission unit 00W-02) conveys limestone/rock to silo #13 and the Weigh Feeder Silo #13 conveys material from the silo to the raw mill feed belt.

Emission Unit Group 00X Description : Emission unit group 00X is comprised of two emission units. These include a BeltConveyor (emission unit 00X-01) and a Weigh Feeder (emission unit 00X-02). All emission units are controlled by a common baghouse (control equipment I.D. 000X).

The Belt Conveyor (emission unit 00X-01) send material to the feed belt which is then sent to Finish Mill #1. The Weigh Feeder feeds the feed belt which feeds clinker to the mill.

Emission Unit Group 00Y Description : Emission unit group 00Y is comprised of two emission units. These include a Belt Conveyor (emission unit 00Y-01) and a Weigh Feeder (emission unit 00Y-02). All emission units are controlled by a common baghouse (control equipment I.D. 000C)

The Belt Conveyor (emission unit 00Y-01) feeds material to Finish Mill #2. The Weigh Feeder (emission unit 00Y-02) feeds the feed belt which feeds clinker to the mill.

Emission Unit Group 00Z Description : Emission unit group 00Z is comprised of two emission units. These include Finish Mill #1 (emission unit 00Z-01) and Screw Conveyors (emission unit 00Z-02). All emission units are controlled by a common baghouse (control equipment I.D. 000X).

Finish Mill #1 grinds clinker and discharges the material to screw conveyors. The Screw Conveyors convey material from Finish Mill #1 to the bucket elevator.

Emission Unit Group 010 Description : Emission unit group 010 is comprised of two emission units. These include Clinker Finish Mill #2 (emission unit 010-01) and a Screw Conveyor (emission unit 0010-02). All emission units are controlled by a common baghouse (control equipment I.D. 000Y).

Finish Mill #2 grinds clinker and discharges to the screw conveyor. The Screw Conveyor (emission unit 010-02) conveys material from the finish mill to the bucket elevator.

Emission Unit Group 011 Description : Emission unit group 011 is comprised of four emission units. These include Finish Mill #1 Separator (emission unit 011-01), Bucket Elevator #1 (emission unit 011-02), Air Separator (emission unit 011-03), and F-K Pump Hopper (emission unit 011-04). All emission units are controlled by a common baghouse (control equipment I.D. 000Z).

The Finish Mill #1 Separator separates coarse from fine material. Bucket Elevator #1 conveys material to the airslide which feeds to the separator. The Air Separator separates fines from coarse materials (the fines are sent to the pump and the coarse material is sent to the mill). The F-K Pump Hopper conveys material to the airslide which feeds the separator.

Emission Unit Group 012 Description : Emission unit group 012 is comprised of four emission units. These include Finish Mill #2 Separator (emission unit 012-01), Bucket Elevator #2 (emission unit 012-02), Air Separator (emission unit 012-03), and F-K Pump Hopper (emission unit 012-04). All emission units are controlled by a common baghouse (control equipment I.D. 0010).The Finish Mill #2 Separator separates coarse from fine material (the fines are sent to the pump and the coarse material is sent to the mill). Bucket Elevator #2 conveys material to the airslide which feeds to the separator. The Air Separator separates fines from coarse materials. The F-K Pump Hopper conveys material to the airslide which feeds the

separator.

Emission Unit Group’s 014, 015, and 016 Description : Emission unit group 014, 015, and 016 are Cement Silos. Emission unit group 014 is comprised of Cement Silos #1 to 15, 015 is comprised of cement silos #16 to 26, and 016 is comprised of cement silos #27-34. Emission unit group 014 is controlled by a baghouse (control equipment I.D. 0011), Emission unit group 015 is controlled by a baghouse (control equipment I.D. 0012), Emission unit group 016 is controlled by a baghouse (control equipment I.D. 0013). All cement silos are used to store the cement.

Emission Unit Group 017 Description : Emission unit group 017 is comprised of three emission units. These include Cement Bins #1 to 4 (emission unit 017-01), a Bucket Elevator (emission unit 017-02), and a Truck Loading Spout (emission unit 017-03). All emission units are controlled by a common baghouse (control equipment I.D. 001A).

Cement Bins #1 to 4 are truck loading bins that discharge cement through the truck loading spout. The Bucket Elevator conveys cement to the cement bins

Emission Unit Group 018 Description : Emission unit group 018 is comprised of three emission units. These include a Bucket Elevator (emission unit 018-01), Packer # 5 (emission unit 018-02), and a Palitizer (emission unit 018-03). All emission units are controlled by a common baghouse (control equipment I.D. 0015).

The Bucket Elevator coveys cement to the cement packer. Packer #5 packages cement. The palitizer stacks bags onto pallets.

Emission Unit Group 019 Description : Emission unit group 019 is comprised of three emission units. These include a Bucket Elevator (emission unit 019-01), Packer # 6 (emission unit 019-02), and a Palitizer (emission unit 019-03). All emission units are controlled by a common baghouse (control equipment I.D. 0017).

The Bucket Elevator coveys cement to the cement packer. Packer #5 packages cement. The palitizer stacks bags onto pallets.

Emission Unit Group 01A Description : Emission unit group 01A is comprised of one emission unit which is Rail Loading. All emission units are controlled by a common baghouse (control equipment I.D. 0019). This process loads cement into rail cars.Emission Unit Group 01F Description : Emission unit group 01F is comprised of three emission units. These include a Bucket Elevator (emission unit 01F-01), a Screen (emission unit 01F-02), and a Belt Elevator (emission unit 01F-03). All emission units are controlled by a common baghouse (control equipment I.D. 000D).

The Bucket Elevator conveys material to the screen. The Screen screens materials from the crusher/dryer and the Belt Conveyor conveys material to the crusher/dryer.

Emission Unit Group 01G Description : Emission unit group 01G is a Vertical Impact Elev ator to Screen that conveys material to screens where the coarse and fine material is separated. All emission units are controlled by a common baghouse (control equipment I.D. 001F).

Emission Unit Group 01I Description : Emission unit group 01I is comprised of two emission units. These include the VIC North

Elevator and the VIC New North Elevator. The VIC North Elevator conveys material to the north or south belt, or to the clinker storage building. Emission unit 01I-01 is controlled by a baghouse (control equipment I.D. 001F), Emission unit 01I-02 is controlled by a baghouse (control equipment I.D. 001I).

Emission Unit Group 01J Description : Emission unit group 01J is comprised of two emission units. These include the Belt Conveyor to the Vertical Impact Crusher (emission unit 01J-01), which conveys material to the crusher, and the VIC Belt Conveyor (emission unit 01J-02) that conveys material from the crusher to the elevator. All emission units are controlled by a common baghouse (control equipment I.D. 001I).

Emission Unit Group 01K Description : Emission unit 01K is a Vertical Impact Discharge which discharges material from the crusher on to the belt. This emission unit is controlled by a baghouse (control equipment I.D. 001J).

Emission Unit Group 01N Description : Emission unit group 01N is the Iron Slag Bin wh ich stores iron slag and other material. This emission unit is controlled by a baghouse (control equipment I.D. 001N).

Emission Unit Group 01P Description : Emission unit group 01P is the Railcar Loadout Elevator. This emission unit is controlled by a baghouse (control I.D. 001M).

Emission Unit Group 01Q Description: Emission Unit Group 01Q is the grind-out silo. This emission unit stores marginal cement and other material. Material from the silo is conveyed to the finish mill. The emission unit is controlled by a baghouse (control equipment I.D. 001O).Emission Unit Group 01R Description: Emission Unit Group 01R is the craneway reclaim. This emission unit returns clinker from the outside storage bin to the South elevator. The emission unit is controlled by a baghouse (control equipment I.D. 001P).

D1. Emission limits

.

1. The owner or operator of each new or existing raw material, clinker, or finished product storage bin; conve ying system transfer point; bagging system; and bulk loading or unloading system; and each existing raw material dryer, at a facility which is a major source subject to the provisions of this subpart shall not cause to be discharged any gases from these affected sources which exhibit opacity in excess of ten percent.

2. The owner or operator of each new or existing raw mill or finish mill at a facility which is a major source subject to the provisions of this subpart shall not cause to be discharged from the mill sweep or air separator air pollution control devices of these affected sources any gases which exhibit opacity in excess of ten percent.

Authority for requirement: KCDAQM Regulations section 35.0

D2. Operating Restrictions: None

D3. Monitoring and/or record keepin g requirements (40 CFR 63, Subpart LLL section 63.1350):CEMEX shall meet the following provisions upon issuance of this permit:

1. Standards for all emission units excluding the raw and finish mills (emission point I.D.’s 00D-01, 00E-03, 00Z-01, 010-01, 011-03, and 012-03).

a. At the discharge of the Air Polluti on Control Device, the owner/operator shall conduct a monthly one-minute vi sible emission (VE) test on the baghouse in accordance with Method 22. The test must be conducted while the affected source is in operation. If visible emissions are observed during any Method 22 test, the owner/operato r must conduct a 6-minute test of opacity in accordance with Method 9 within one hour of the observation.

b. If no visible emissions are observed in six consecutive monthly tests for any affected source, the owner/operator may decrease the frequency of testing from monthly to semi-annually for the affected source. If visible observations are observed during the se mi-annual tests, the owner/operator must resume testing of that source on a monthly basis and maintain that

schedule until no visible emissions are observed in six consecutive monthly

tests.

c. If no visible emissions are observed during the semi-annual test for an affected source, the owner/operator may decrease the frequency of testing from semi-annually to annually for that affected source. If visible observations are observed during any annua l test, the owner or operator must resume testing at that affected source on a monthly basis and maintain that

schedule until no visible emissions are observed in six consecutive monthly

tests.

d. If visible emissions are observed dur ing any method 22 test, the owner or operator must conduct a 6-minute test of opacity in accordance with Method 9 of Appendix A of 40 CFR 60. The Met hod 9 test must begin within one hour of any observation of visible emissions.

e. A copy of VE readings shall be recorded on the following log and maintained on file at the facility fo r a minimum of five years. These inspection logs shall include the following information:

Control I.D.

Number Date Time VE’s present Corrective

Action Taken Detail description if

VE’s are

present (i.e.0001)Authority for requirement: KCDAQM Regulations section 35.0

2. Standard for the Raw and Finish M ill (emission point I.D.’s 00D-01, 00E-03, 00Z-01, 010-01, 011-03, and 012-03)

The owner or operator of a raw mill or finish mill shall monitor opacity by conducting daily visual emissions observations of the mill sweep and air separator PMCDs of these affected sources, in accordance with the procedures of Method 22 of appendix A of 40 CFR 60. The Method 22 test shall be conducted while the affected source is operating at the representative performance conditions

. The duration of the Method 22 test shall be six

minutes. If visible emissions are observed during any Method 22 visible emissions test, the owner or operator must:

(i) initiate, within one-hour, the corrective actions specified in the site specific operating and maintenance plan; and (ii) Within 24 hours of the end of the Method 22 test in which visible emissions were observed, conduct a followup

Method 22 test of each stack from which visible emissions were observed during the previous Method 22 test. If visible emissions are observed during the followup Method 22 test from any stack from which visible emissions were observed during the previous Method 22 test, conduct avisual opacity test of each stack from which emissions were observed during the follow up Method 22 test in accordance with Method 9 of appendix A to 40 CFR 60. The duration

of the Method 9 test shall be 30 minutes.

Authority for requirement: KCDAQM Regulations section 26.5and 35.2.2 LLL.

D4. Reporting Requirements.

1. The permittee must prepare and submit semi-annual reports of all required monitoring and recordkeeping contained in this permit to this Department no later than July 31 st and January 31 st of each year.

2. The permittee must prepare and submit reports as specified in 40 CFR 63, Subpart LLL.

Authority for requirement: KCDAQM Regulations section 26.5 and 35.2.2 LLL.

D5. Testing requirements.

The permittee shall meet the performance test requirements of 40 CFR 63, Subpart

LLL.

The owner or operator of any affected source subject to limitations on opacity under this subpart that is not subject to paragraph (b)(1) of this section shall demonstrate initial compliance with the affected source opacity limit by conducting a test in accordance with Method 9 of appendix A to 40 CFR 60. The performance test shall be conducted under the conditions that exist when the affected source is operating at the representative performance conditions in accordance with 40 CFR 63.7(e). The maximum 6-minute average opacity exhibited during the test period shall be used to determine whether the affected source is in initial compliance with the standard. The duration of the Method 9 performance test shall be 3 hours (30 6-minute averages), except that the duration of the Method 9 performance test may be reduced to 1 hour if the conditions of paragraphs (b)(2)(i) through (ii) of this section apply: (i) There are no individual readings greater than 10 percent opacity; (ii) There are no more than three readings of 10 percent for the first 1-hour period.

Authority for requirement: KCDAQM Regulations section 35.2.2 LLL.

D6. Miscellaneous requirements. noneE. SOURCE SPECIFIC CONDITIONS, OPERATING LIMITATIONS, AND MONITORING, RECORD KEEPING, AND REPORTING REQUIREMENTS FOR

EMISSION UNIT GROUP OOA :

Emission Unit Description : Emission unit group OOA is comprised of two emission units. These include emission a Coal Mill (emission unit 00A-01) and a Holding Bin (emission unit 00A-02). Both emission units are controlled by a common baghouse (control equipment I.D. 0014).

The Coal Mill (emission unit 00A-01) crushes coal and conveys to a pump.

The Holding Bin stores coal and transfers the coal to the kiln

E1. Emission limits

. 1. This process is subject to the requirements of 40 CFR 60, Subpart Y, Standards of Performance for Coal Preparation Plants (as specified in Attachment B), including but not limited to the following:

a. Emissions to the atmosphere of particulate matter from dryer vents shall not exceed 0.031 grains per dry standard cubic foot of thermal dryer stack gases.

b. The opacity of emissions from the thermal dryer vent(s) shall not exceed 20

percent.

Authority for requirement: KCDAQM Regulations section 40.0

E2. Operating Restrictions: None

E3. Monitoring and/or record keeping requirements:

1. The owner or operator of this source must maintain records of the following for a minimum of five years:

a. The owner or operator of any thermal dryer shall install, calibrate, maintain, and continuously operate monitoring devices as follows: (i). A monitoring device for the measurement of the temperature of the gas stream at the exit of the thermal dryer on a continuous basis. The monitoring device is to be certified by the manufacturer to be accurate within ± 3 degrees Farenheit. (ii) The monitoring device shall be recalibrated annually in accordance with the procedures under 40 CFR § 60.13 (b).

b. Total daily operating hours of each thermal dryer.

Authority for requirement: KCDAQM Regulations section 40.02. CEMEX shall meet the following provisions upon issuance of this permit:

a. At the discharge of the Air Pollu tion Control Device, the owner/operator shall conduct a monthly one-minute vi sible emission (VE) test on the baghouse in accordance with Method 22. The test must be conducted while the affected source is in operation. If visible emissions are observed during any Method 22 test, the owner/operato r must conduct a 6-minute test of opacity in accordance with Method 9 within one hour of the observation.

b. If no visible emissions are observed in six consecutive monthly tests for any affected source, the owner/operator may decrease the frequency of testing from monthly to semi-annually for the affected source. If visible observations are observed during the se mi-annual tests, the owner/operator must resume testing of that source on a monthly basis and maintain that

schedule until no visible emissions are observed in six consecutive monthly

tests.

c. If no visible emissions are observed during the semi-annual test for an affected source, the owner/operator may decrease the frequency of testing from semi-annually to annually for that affected source. If visible observations are observed during any annua l test, the owner or operator must resume testing at that affected source on a monthly basis and maintain that

schedule until no visible emissions are observed in six consecutive monthly

tests.

d. If visible emissions are observed dur ing any method 22 test, the owner or operator must conduct a 6-minute test of opacity in accordance with Method 9 of Appendix A of 40 CFR 60. The Met hod 9 test must begin within one hour of any observation of visible emissions.

e. A copy of VE readings shall be recorded on the following log and maintained on file at the facility fo r a minimum of five years. These inspection logs shall include the following information:

CEMEX, Inc. Visible Emissions Log

Date Time VE Reader VE’s present Control I.D. # Detail description if VE’s are

present Corrective Action if VE’s

present

e.g. 4/1/01 e.g. 11:00am e.g. John

Smith e.g. No 0003 NA NA.

e.g. 4/5/01 e.g. 3:30pm e.g. John

Smith e.g. Yes State and explain reasons of

emission. Describe corrective action

taken.

Authority for requirement: KCDAQM Regulations section 26.5

E4. Reporting Requirements.The permittee must prepare and submit semi-annual reports of all required monitoring and recordkeeping contained in this permit to this Department no later than July 31 st and January 31 st of each year.

Authority for requirement: KCDAQM Regulations section 26.5

E5. Testing requirements.

Testing shall be conducted as specified in 40 CFR 60 Subpart Y

Authority for requirement: KCDAQM Regulations section 40.0

E6. Miscellaneous requirements. noneF . SOURCE SPECIFIC CONDITIONS, OPERATING LIMITATIONS, AND MONITORING, RECORD KEEPING, AND REPORTING REQUIREMENTS FOR EMISSION UNIT GROUP 00K, 00O :

Emission Unit Group Description : Emission unit group OOK is comprised of two emission units. These include the Kiln (emission unit 00K-01), and the Crusher/ Dryer. Both emission units are controlled by a common baghouse (control I.D. 000O).

The Kiln produces clinker and discharges the material to the clinker cooler. The Crusher/Dryer crusher and dries material and discharges to a screw conveyor.

Emission Unit Group Description : Emission unit group 00O is comprised of one emission unit. The Clinker Cooler (emission unit 00O-01) cools the clinker produced in the Kiln and sends it to the drag conveyors. This emission unit is controlled by a baghouse (control equipment I.D. 000S).

F1. Emission limits

.

CEMEX is applicable to the emission limits contained in section F7 below.

F2. Operating Restrictions:

1. The following fuels can be utilized in the kiln system:

a. Fossil fuels: coal., crude oil, gasoline, kerosene, fuel oil, diesel, and lubricating

oil

b. Natural gas

c. Used oil (as specified in the miscellaneous requirements of this section)

d. On-site generated non-hazardous oil materials/rags/absorbent/spill clean-up materials (as specified in miscellaneous requirements of this section)

e. Vehicle tires

f. Petroleum Coke

g. Other non-hazardous fuels that do not increase emissions with the prior approval of the Department.

2. Each source of raw materials substitutes must be analyzed quarterly for the following: sulfur, arsenic, beryllium, cadmium, chromium, lead, mercury, and total halogens.3. No hazardous wastes may be transferred to the kiln.

4. Each monthly emission report must include the general description required per the Quality Assurance Plan for each raw material substitutes source.

5. For the purpose of this permit, the term “TDF” will mean vehicle tires derived fuels.

6. TDF may only be charged to the rotary kiln, not to the preheater/calciner assembly (ies). TDF may only be charged into the kiln at the same end as the kiln feed materials (referred to as the “East End” or the Southeast end).

7. TDF may not be charged to the kiln at a rate that exceeds the mass of 3 individual tires per minute or 1 tire per 20 seconds. The actual charging rate of TDF will automatically set and be monitored by an electronic system at the facility.

8. The daily TDF charged to the kiln (by both tire count and weight) will be calculated, and recorded in a log, along with the daily total TDF charging time period. This log must be maintained at the facility for a minimum of five years.

9. Optimal combustion conditions, as defined here, must be maintained in the kiln during the use of TDF. This means a kiln exit gas level of at least 1% O 2 , a kiln speed of at least 2.95 RPM, and continuous operation of the kiln’s induced draft fan. The optimal combustion conditions referred to here will be electronically monitored. The charging of TDF will be automatically shut off if the kiln fails to meet these optimal combustion

conditions.

F3. Monitoring and/or record keeping requirements:

1. The owner or operator of this source must maintain records of the following for a minimum of five years:

a. Total daily coal consumption and the average sulfur content. The average sulfur content of the coal will be determined by weekly testing of a composite prepared from daily samples.

b. Total daily operating hours of the kiln.

Authority for requirement: KCDAQM Regulations section 26.5

2. All laboratory analysis sheets and other manifests/records required by law and/or any Knox County Department of Air Quality Management permit issued to this facility of coal, any other fuels (used oils, etc.), and raw materials substitutes fed to the kiln shall be maintained on file for a minimum of five years. Copies of these records shall be submitted to the Department upon request.Authority for requirement: KCDAQM Regulations section 26.5

3. The owner or operator shall maintain the following records and reports as specified

below:

a. Records of the following shall be maintained at the facility and made available upon the request of the Department:

(i) Summary of the analytical data obtained for the testing of used oil and raw material substitutes as specified in the Quality Assurance Plan (miscellaneous requirements of this section).

(ii) Emission summary for used oils and raw material substitutes as specified in the Emission Protocol (miscellaneous requirements of this permit) or by another method of emissions estimation approved by this Department.

(iii) Total daily fossil fuel (other than coal) consumption and fuel type.

Authority for requirement: KCDAQM Regulations section 26.5

F4. Reporting Requirements.

1. A report shall be submitted to the Department no later than January 31 of the following year, containing, as a minimum, the following:

a. Total annual consumption (pounds) of coal and the annual average sulfur percent content of the coal.

b. Total annual consumption (pounds) of any fossil fuel (other than coal) and the average sulfur content of the fossil fuel.

c. Aggregate total annual consumption (pounds) of used oil and raw material

substitutes.

d. Aggregate total amount (pounds) of plant generated waste transferred to the

kiln.

2. The permittee must prepare and submit semi-annual reports of all required monitoring and record keeping contained in this permit to this Department no later than July 31 st and January 31 st of each year.

Authority for requirement: KCDAQM Regulations section 26.5F5. Testing requirements.

1. Each source of used oils or tank containing used oils must be analyzed prior to transfer to the kiln for the following: sulfur, beryllium, mercury, and lead, as specified in section 3.

Authority for requirement: KCDAQM Regulations section 26.4

2. Receipt of Used Oils – Off-site Sources

Any used oils received from off-site sources must be evaluated and meet the criteria specified below. (Note: Used oil, by EPA designation is neither a hazardous waste nor a PCB-contaminated waste. These products are defined as any oil that has been refined from crude oil, or any synthetic oil that has been used and, as a result of that use, is contaminated by physical or chemical impurities.)

Prior to shipment to the facility, used oils will be tested by the supplier or the permittee for the following parameters:

TABLE 1

– M AXIMUM CONCENTRATION LEVELS FOR OFF

- SITE USED OIL

Parameter Maximum Allowable Level

Arsenic 83 ppm

Cadmium 500 ppm

Chromium 3000 ppm

Mercury 5.15 ppm

Lead 4000 ppm

Total Halogens 5%

PCBs <50 ppm

True Vapor Pressure If ≥ 15.0 kPa, CEMEX must notify KCDAQM prior to storage

Prior to ordering/purchasing used oil from the supplier, the analytical results will be reviewed and compared against the limitations specified above in TABLE 1. Only used oils meeting the above limitations will be obtained form the supplier and scheduled for shipment to the Knoxville facility.

Upon receipt, the shipment of used oils will be off-loaded into the storage tanks or will be staged for direct transfer. The used oils will not be transferred to the kiln until the evaluations detailed below in Section 3.0 are conducted. Analytical testing of the suppliers used oil for the parameters in TABLE 1 must be repeated on an annual basisAuthority for requirement: KCDAQM Regulations section 26.4

3. Energy Recover of Used Oil in the Cement Kiln

a. OFF-SITE SOURCES OF USED OIL

As stated above, used oils approved for energy recovery will be either transferred to Storage Tank #1 or staged for direct transfer. Prior to transferring the used oils from the storage tanks to the kiln or connecting for direct transfers to the kiln, the tank contents/used oil will be tested for sulfur, beryllium, mercury, and lead. The analytical results from this testing are subject to the emission calculations specified in the Quality Assurance Plan.

No used oils can be transferred from tanks or pumped directly to the kiln for energy recovery until the emission calculations and evaluations detailed in Part II of the quality assurance plan are conducted. If the used oil is within the limitations specified in Section A, the material will be authorized for the

transfer to the kiln.

b. ON-SITE SOURCES OF USED OIL/OILY MATERIALS

On-site generated liquid oils will be transferred to the storage tanks. Since this material has been previously tested, testing is not required to unload the material into the tank. However, all transfers on-site generated used oils from the tank to the kiln are subject to testing for sulfur, beryllium, mercury, and lead. The analytical results from this testing are subject to the emission calculations specified in Part II of the quality assurance plan.

All on-site generated solid, semi-solid, and/or liquid oily mixtures will be packaged into six gallon pails and will be transferred to the kiln. Additional analytical testing will not be required. However, the analytical results from previous testing will be utilized to satisfy the requirements specified in the Emissions Protocol (Part II of the quality assurance plan).

4. Raw Material Substitutions

Raw material substitutions (non-mining sources ) of calcium, aluminum, silica, and iron will be evaluated prior to purchasing or receiving the material. The product supplier will be required to submit a general description of the material, a MSDS (if available), and a total metal analysis for Sulfur, Arsenic, Beryllium, Cadmium, Chromium, Lead, Mercury, and Total Halogens. Analytical data will be repeated on a quarterly basis. The analytical data will be utilized to perform the calculations detailed in Part II of the Quality Assurance Plan before the raw materials are purchased/contracted for use in the

kiln feed.Authority for requirement: KCDAQM Regulations section 26.4

F6. Miscellaneous requirements

QUALITY ASSURANCE PLAN

USED OIL AND

RAW MATERIAL SUBSTITUTES

PART I

The following Quality Assurance Plan was developed to demonstrate compliance with the Emissions Protocol (Part II) and only allows for the following applications:

1. The receipt of commercially available “on specification and off specification

used oils” as defined in 40 CFR 279.

2. The burning of “used oil” materials stor ed in Tank #1 or Direct Transfers.

3. The use of raw material substitutions in the kiln feed.

PART II

Section A ACTUAL EMISSIONS (MONTHLY) Regulated Pollutants: Pb, Be, Hg, SO 2

1. Determine the total mass (lb.) of contaminant input to the kiln system by way of

materials/fuels:

a. For Used Oil (Input #1)

D/UO M D = ∑ 1 (Act. Conc. ppm) (Weight of Input #1 burned/Day)(1/10 6 )(lb./day)(ton/2000 lbs.)

b. For on-site generated solid/semi-solid oily material (Input #2) – Repeat the procedure in 1.a.

c. For raw material substitutes (Input #3) – Repeat the procedure in 1.a. for each raw material input.

2. Determine the removal/retention factor for each pollutant based on the 1991 stack testdata; default values are:

RF (Hg) (1.0 – 0.690189) = 0.309811

RF (Be) (1.0 – 0.999947) = 0.000053

RF (Pb) (1.0 – 0.999673) = 0.000327

RF (SO 2 ) (1.0 – 0.908442) = 0.091558

3. Calculate the actual emissions for each pollutant by multiplying the sum of the contaminants inputs (fuels and feed) by the associated removal/retention factor:

(Input #1 M D + Input #2 M D + Input #3 M D x RF = E ACT

Note: To convert E ACT (S) and E ACT (SO 2 ), multiply E ACT (S) by 2.

4. A record of the calculations required in Part II and all associated analytical data, Section A, Item 3, shall be maintained at the facility for a minimum of five years.

SECTION B

MAXIMUM ALLOWABLE ANNUAL EMISSIONS

1. The maximum allowable emissions during any consecutive twelve month period, as calculated in Part II Section A, for the raw materials substitute and used oil are:

SO 2 - 40 Tons per Year Lead - 0.6 Tons per Year Mercury- 0.1 Tons per Year Beryllium – 0.0004 Tons per Year

This limit was established, under mutual agreement with CEMEX, to synthesize

below the PSD thresholds.

Authority for requirement: KCDAQM Regulations section 25.3.I

2. The following table must be updated monthly and maintained at the facility for a minimum of five years. Actual emissions shall be calculated monthly, as specified in Part II Section A, and logged in the following table:

CEMEX KNOXVILLE, TNEMISSIONS REPORT

Month SO 2 (tons) *Tons

SO 2 per 12-month Lead (tons) *Tons Lead per 12-

month Mercury (tons) *Tons Mercury per 12-

month Beryllium (tons) *Tons Beryllium per 12-month

November

2000

December

2000

January

2001

Etc..

* The tons of pollutant per 12 Month value is the sum of the tons produced in the 11 months preceding the month just completed + the tons in the month just completed. If data is not available for the 11 months preceding the initial use of this log, this value will be equal to the value for tons per month. For the second month it will be the sum of the first month and the second month. Indicate in parentheses the number of months summed, that is, 6 (2) represents 6 tons emitted in 2 months.

Authority for requirement: KCDAQM Regulations section 26.5.B

3. Any exceedance of the emission limits specified in item number 1 of this section is a violation of the Knox County Department of Air Quality Management Regulations and must be reported to this Department within 24 hours of discovery.

4. All records required by this section must be maintained on site at the facility for a minimum of five years.

5. Calculate the actual emissions for each pollutant by multiplying the sum of the contaminants inputs by the associated removal/retention factor:

(Input #1 M D + Input #2 M D + Input #3 M D x RF = E ACT

Note: To convert E ACT (S) and E ACT (SO 2 ), multiply E ACT (S) by 2.

A record of the calculations required in Part II and all associated analytical data, Section A, Item 3 shall be maintained at the facility for a minimum of five years.

F7. NESHAP Requirements For Emission unit group 00K and 00O (40 CFR 63, Subpart LLL). Attachment C of this permit.

The compliance date for the owner or operator of an existing affected source subject to the provisions of this subpart is June 10, 2002, unless otherwise noted below.The compliance date for the owner or operator of an existing affected source subject to the provisions of this subpart that commences new construction or reconstruction after March 24, 1998 is June 9, 1999 or immediately upon startup of operations,

whichever is later.

This facility is applicable to 40 CFR 63, Subpart A. The applicable sections are outlined in Table 1 to Subpart LLL (see Attachment C).

1. Standards for kilns and in-line kiln/raw mills

. ( (a)(1) and (2) are Applicable Upon Permit Issuance)

(a) Existing, reconstructed, or new brownfield/major sources. No owner or operator of an existing, reconstructed or new brownfield k iln or an existing, reconstructed or new brownfield in-line kiln/raw mill at a facility that is a major source subject to the provisions of this subpart shall cause to be discharged into the atmosphere from these affected sources, any gases which: (1) Contain particulate matter (PM) in excess of 0.15 kg per Mg (0.30 lb per ton) of feed (dry basis) to the kiln. When there is an alkali bypass associated with a kiln or in-line kiln /raw mill, the combined particulate matter emissions from the kiln or in-line kiln/raw mill and the alkali bypass are subject to this emission limit. (2) Exhibit opacity greater than 20 percent. (3) Contain D/F in excess of: (i) 0.20 ng per dscm (8.7 x 10-11 gr per dscf) (TEQ) corrected to seven percent oxygen; or (ii) 0.40 ng per dscm (1.7 x 10-10 gr per dscf) (TEQ) corrected to seven percent oxygen, when the average of the performance test run average temperatures at the inlet to the particulate matter control device is 204 deg.C (400 deg.F) or less.

2. Standards for clinker coolers

. (Applicable Upon Permit Issuance)

No owner or operator of a new or existing clinker cooler at a facility which is a major source subject to the provisions of this subpart shall cause to be discharged into the atmosphere from the clinker cooler any gases which: (1) Contain particulate matter in excess of 0.050 kg per Mg (0.10 lb per ton) of feed (dry basis) to the kiln. (2) Exhibit opacity greater than ten percent

3. Operating limits for kilns and in-line kiln/raw mills.

(a) The owner or operator of a kiln subject to a D/F emission limitation under Sec. 63.1343 must operate the kiln such that the temperature of the gas at the inlet to the kiln particulate matter control device (PMCD) and alkali bypass PMCD, if applicable, does not exceed the applicable temperature limit specified in paragraph (b) of this section. The owner or operator of an in-line kiln/raw mill subject to a D/F emission limitation under Sec. 63.1343 must operate the in-line kiln/raw mill, such that: (1) When the raw mill of the in-line kiln/raw mill is operating, the applicable temperature limit for the main in-line kiln/raw mill exhaust, specified in paragraph (b) of this section and established during the performance test when the raw mill was operating is not exceeded. (2) When the raw mill of the in-line kiln/raw mill is not operating, theapplicable temperature limit for the main in-line kiln/raw mill exhaust, specified in paragraph (b) of this section and established during the performance test when the raw mill was not operating, is not exceeded. (3) If the in-line kiln/raw mill is equipped with an alkali bypass, the applicable temperature limit for the alkali bypass, specified in paragraph (b) of this section and established during the performance test when the raw mill was operating, is not exceeded. (b) The temperature limit for affected sources meeting the limits of paragraph (a) of this section or paragraphs (a)(1) through (a)(3) of this section is determined in accordance with Sec. 63.1349(b)(3)(iv). (c) The owner or operator of an affected source subject to a D/F emission limitation under Sec. 63.1343 that employs carbon injection as an emission control technique must operate the carbon injection system in accordance with paragraphs (c)(1) and (c)(2) of this section. (1) The three-hour rolling average activated carbon injection rate shall be equal to or greater than the activated carbon injection rate determined in accordance with Sec. 63.1349(b)(3)(vi). (2) The owner or operator shall either: (i) Maintain the minimum activated carbon injection carrier gas flow rate, as a three-hour rolling average, based on the manufacturer's specifications. These specifications must be documented in the test plan developed in accordance with Sec. 63.7(c), or (ii) Maintain the minimum activated carbon injection carrier gas pressure drop, as a three-hour rolling average, based on the manufacturer's specifications. These specifications must be documented in the test plan developed in accordance with Sec. 63.7(c). (d) Except as provided in paragraph (e) of this section, the owner or operator of an affected source subject to a D/F emission limitation under Sec. 63.1343 that employs carbon injection as an emission control technique mu st specify and use the brand and type of activated carbon used during the performance test until a subsequent performance test is conducted, unless the site-specific performance test plan contains documentation of key parameters that affect adsorption and the owner or operator establishes limits based on those parameters, and the limits on these parameters are maintained. (e) The owner or operator of an affected source subject to a D/F emission limitation under Sec. 63.1343 that employs carbon injection as an emission control technique may substitute, at any time, a different brand or type of activated carbon provided that the replacement has equivalent or improved properties compared to the activated carbon specified in the site-specific performance test plan and used in the performance test. The owner or operator must maintain documentation that the substitute activated carbon will provide the same or better level of control as the original activated carbon.

4. Performance testing requirements.

(a) The owner or operator of an affected source subject to this subpart shall demonstrate initial compliance with the emission limits of Sec. 63.1343 and Secs. 63.1345 through 63.1348 using the test methods and procedures in paragraph (b) of this section and Sec. 63.7. Performance test results shall be documented in complete test reports that contain the information required by paragraphs (a)(1) through (a)(10) of this section, as well as all other relevant information. The plan to be followed during testing shall be made available to the Administrator prior to testing, if requested. (1) A brief description of the process and the air pollution control system; (2) Sampling location description(s);(3) A description of sampling and analyti cal procedures and any modifications to standard procedures; (4) Test results; (5) Quality assurance procedures and results; (6) Records of operating conditions during the test, preparation of standards, and calibration procedures; (7) Raw data sheets for field sampling and field and laboratory analyses; (8) Documentation of calculations; (9) All data recorded and used to establish parameters for compliance monitoring; and (10) Any other information required by the

test method. (b) Performance tests to demonstrate initial compliance with this subpart shall be conducted as specified in paragraphs (b)(1) through (b)(2) of this section.

(1) The owner or operator of a kiln subject to limitations on particulate matter emissions shall demonstrate initial compliance by conducting a performance test as specified in paragraphs (b)(1)(i) through (b)(1)(iv) of this section. The owner or operator of an in-line kiln/raw mill subject to limitations on particulate matter emissions shall demonstrate initial compliance by conducting separate performance tests as specified in paragraphs (b)(1)(i) through (b)(1)(v) of this section while the raw mill of the in-line kiln/raw mill is under normal operating conditions and while the raw mill of the in-line kiln/raw mill is not ope rating. The owner or operator of a clinker cooler subject to limitations on particulate matter emissions shall demonstrate initial compliance by conducting a performance test as specified in paragraphs (b)(1)(i) through (b)(1)(iii) of this section. The opacity exhibited during the period of the Method 5 of Appendix A to part 60 of this chapter performance tests required by paragraph (b)(1)(i) of this section shall be determined as required in paragraph (b)(1)(v) of this section. (i) EPA Method 5 of appendix A to part 60 of this chapter shall be used to determine PM emissions. Each performance test shall consist of three separate runs under the conditions that exist when the affected source is operating at the highest load or capacity level reasonably expected to occur. Each run shall be conducted for at least one hour, and the minimum sample volume shall be 0.85 dscm (30 dscf). The average of the three runs shall be used to determine compliance. A determination of the particulate matter collect ed in the impingers (``back half'') of the Method 5 particulate sampling train is not required to demonstrate initial compliance with the PM standards of this subpart. However this shall not preclude the permitting authority from requiring a determination of the ``back half'' for other purposes. (ii)

Suitable methods shall be used to determine the kiln or inline kiln/raw mill feed rate, except for fuels, for each run. (iii) The emission rate, E, of PM shall be computed for each run using equation 1:

E = (C

s Q sd )/P (Eq. 1)

Where: E = emission rate of particulate matter, kg/Mg of kiln feed.

C

s = concentration of PM, kg/dscm. Q sd = volumetric flow rate of effluent gas, dscm/hr. P = total kiln feed (dry basis), Mg/hr.

(iv) Except as provided in paragraph (b)(1)(vi) of this section the opacityexhibited during the period of the Method 5 performance tests required by paragraph (b)(1)(i) of this section shall be determined through the use of a continuous opacity monitor (COM). The maximum six- minute average opacity during the three Method 5 test runs shall be determined during each Method 5 test run, and used to demonstrate initial compliance with the applicable opacity limits of Sec. 63.1343(b)(2), Sec. 63.1343(c)(2), or Sec. 63.1345(a)(2).

(1) The owner or operator of an affected source subject to limitations on D/F emissions shall demonstrate initial compliance with the D/F emission limit by conducting a performance test using Method 23 of appendix A to part 60 of this chapter. The owner or operator of an in-line kiln/raw mill shall demonstrate initial compliance by conducting separate performance tests while the raw mill of the in-line kiln/raw mill is under normal operating conditions and while the raw mill of the in-line kiln/raw mill is not operating. The owner or operator of a kiln or in-line kiln/raw mill equipped with an alkali bypass shall conduct simultaneous performance tests of the kiln or in-line kiln/raw mill exhaust and the alkali bypass, however the owner or ope rator of an in- line kiln/raw mill is not required to conduct a performance test of the alkali bypass exhaust when the raw mill of the in-line kiln/raw mill is not operating. (i) Each performance test shall consist of three separate runs; each run

shall be conducted under the conditions that exist when the affected source is operating at the highest load or capacity level reasonably expected to occur. The duration of each run shall be at least three hours and the sample volume for each run shall be at least 2.5 dscm (90 dscf). The concentration shall be determined for each run and the arithmetic average of the concentrations measured for the three runs shall be calculated and used to determine compliance. (ii) The temperature at the inlet to the kiln or in-line kiln/raw mill PMCD, and where applicable, the temperature at the inlet to the alkali bypass PMCD, must be continuously recorded during the period of the Method 23 test, and the continuous temperature record(s) must be included in the performance test report. (iii) One-minute average temperatures must be calculated for each minute

of each run of the test. (iv) The run average temperature must be calculated for each run, and the average of the run average temperatures must be determined and included in the performance test report and will determine the applicable temperature limit in accordance with Sec. 63.1344(b). (v) If activated carbon injection is used for D/F control, the rate of activated carbon injection to the kiln or in-line kiln/raw mill exhaust, and where applicable, the rate of activated carbon injection to the alkali bypass exhaust, must be continuously recorded during the period of the Method 23 test, and the continuous injection rate record(s) must be included in the performance test report. In addition, the performance test report must include the brand and typeof activated carbon used during the performance test and a continuous record of either the carrier gas flow rate or the carrier gas pressure drop for the duration of the test. Activated carbon injection rate parameters must be determined in accordance with paragraphs (b)(3)(vi) of this section. (vi) The run average injection rate must be calculated for each run, and the average of the run average injection rates must be determined and included in the performance test report and will determine the applicable injection rate limit in accordance with Sec. 63.1344(c)(1). (c) Except as provided in paragraph (e) of this section, performance tests required under paragraphs (b)(1) of this section shall be repeated every five years, except that the owner or operator of a kiln, in-line kiln/raw mill or clinker cooler is not required to repeat the initial performance test of opacity for the kiln, in-line kiln/raw mill or

clinker cooler. (d) Performance tests required under paragraph (b)(2) of this section shall be repeated every 30 months. (e) The owner or operator is required to repeat the performance tests for kilns or in-line kiln/raw mills as specified in paragraphs (b)(1) and (b)(2) of this section within 90 days of initiating any significant change in the feed or fuel from that used in the previous performance test.

5. Monitoring requirements.

(a) The owner or operator of each portland cement plant shall prepare for each affected source subject to the provisions of this subpart, a written operations and maintenance plan. The plan shall be submitted to the Administrator for review and approval as part of the application for a part 70 permit and shall include the following information: (1) Procedures for proper operation and maintenance of the affected source and air pollution control devices in order to meet the emission limits and operating limits of Secs. 63.1343 through 63.1348; (2) Procedures to be used during an inspection of the components of the combustion system of each kiln and each in-line kiln raw mill located at the facility at least once per year; and

(b) Failure to comply with any provision of the operations and maintenance plan developed in accordance with paragraph (a) of this section shall be a violation of the

standard.

(c) (Applicable Upon Permit Issuance) The owner or operator of a kiln or in-line kiln/raw mill shall monitor opacity at each point where emissions are vented from th ese affected sources including alkali bypasses in accordance with paragraphs (c)(1) and (c)(2) of this section.

(1) The owner or operator shall install, calibrate, maintain, and continuously operate a continuous opacity monitor (COM) located at the outlet of the PM control device to continuously monitor the opacity. The COM shall be installed,maintained, calibrated, and operated as required by subpart A, general provisions of this part, and according to PS-1 of appendix B to part 60 of 40

CFR.

(2) To remain in compliance, the opacity must be maintained such that the 6-minute average opacity for any 6-minute block period does not exceed 20 percent. If the average opacity for any 6-minute block period exceeds 20 percent, this shall

constitute a violation of the standard.

(d) (Applicable Upon Permit Issuance) The owner or operator of a clinker cooler shall monitor opacity at each point where emissions are vented from the clinker cooler in accordance with paragraphs (d)(1) through (d)(2) of this section. (1) The owner or operator shall install, calibrate, maintain, and continuously operate

a COM located at the outlet of the clinker cooler PM control device to continuously monitor the opacity. The COM shall be installed, maintained, calibrated, and operated as required by subpart A, general provisions of this part, and according to PS-1 of appendix B to part 60 of this chapter.

(2) To remain in compliance, the opacity must be maintained such that the 6-minute average opacity for any 6-minute block period does not exceed 10 percent. If the average opacity for any 6-minute block period exceeds 10 percent, this shall

constitute a violation of the standard.

(e) The owner or operator of an affected source subject to a limitation on D/F emissions shall monitor D/F emissions in accordance with paragraphs (d)(1) through (d)(6) of this

section.

(1) The owner or operator shall install, calibrate, maintain, and continuously operate a continuous monitor to record the temperature of the exhaust gases from the kiln, in-line kiln/raw mill and alkali bypass, if applicable, at the inlet to, or upstream of, the kiln, in-line kiln/raw mill and/or alkali bypass PM control

devices.

(i) The recorder response range must include zero and 1.5 times either of the average temperatures established according to the requirements in Sec. 63.1349(b)(3)(iv). (ii) The reference method must be a National Institute of Standards and Technology calibrated reference thermocouple-potentiometer system or alternate reference, subject to approval by the Administrator.

(2) The owner or operator shall monitor and continuously record the temperature of the exhaust gases from the kiln, in-line kiln/raw mill and alkali bypass, if applicable, at the inlet to the kiln, in-line kiln/raw mill and/or alkali bypass

PMCD.(3) The three-hour rolling average temperature shall be calculated as the average of 180 successive one-minute average temperatures.

(4) Periods of time when one-minute averages are not available shall be ignored when calculating three-hour rolling averages. When one-minute averages become available, the first one-minute average is added to the previous 179 values to calculate the three-hour rolling average.

(5) When the operating status of the raw mill of the in-line kiln/raw mill is changed from off to on, or from on to off the calculation of the three-hour rolling average temperature must begin anew, without considering previous recordings.

(6) The calibration of all thermocouples and other temperature sensors shall be verified at least once every three months.

(f) The owner or operator of an affected source subject to a limitation on D/F emissions that employs carbon injection as an emission control technique shall comply with the monitoring requirements of paragraphs (d)(1) through (d)(6) and (e)(1) through (e)(6) of this section to demonstrate continuous compliance with the D/F emission standard.

(1) Install, operate, calibrate and maintain a continuous monitor to record the rate of activated carbon injection. The accuracy of the rate measurement device must be <plus-minus>1 percent of the rate being measured.

(2) Verify the calibration of the device at least once every three months.

(3) The three-hour rolling average activated carbon injection rate shall be calculated as the average of 180 successive one-minute average activated carbon injection

rates.

(4) Periods of time when one-minute averages are not available shall be ignored when calculating three-hour rolling averages. When one-minute averages become available, the first one-minute average is added to the previous 179 values to calculate the three-hour rolling average.

(5) When the operating status of the raw mill of the in-line kiln/raw mill is changed from off to on, or from on to off the calculation of the three-hour rolling average activated carbon injection rate must begin anew, without considering previous recordings.

(6) The owner or operator must install, operate, calibrate and maintain a continuous monitor to record the activated carbon injection system carrier gas parameter (either the carrier gas flow rate or the carrier gas pressure drop) establishedduring the D/F performance test in accordance with paragraphs (e)(6)(i) through (e)(6)(iii) of this section.

(i) The owner or operator shall install, calibrate, operate and maintain a device to continuously monitor and record the parameter value. (ii) The owner or operator must calculate and record three-hour rolling averages of the parameter value. (iii) Periods of time when one-minute averages are not available shall be ignored when calculating three-hour rolling averages. When one-minute averages become available, the first one-minute average shall be added to the previous 179 values to calculate the three-hour rolling average.

(g) The owner or operator of any kiln or in-line kiln/raw mill subject to a D/F emission limit under this subpart shall conduct an inspection of the components of the combustion system of each kiln or in-line kiln raw mill at least once per year.

(h) The owner or operator of an affected source subject to a limitation on opacity under Sec. 63.1346 or Sec. 63.1348 shall monitor opacity in accordance with the operation and maintenance plan developed in accordance with paragraph (a) of this section.

(i) The owner or operator of an affected source subject to a particulate matter standard under Sec. 63.1343 shall install, calibrate, maintain and operate a particulate matter continuous emission monitoring system (PM CEMS) to measure the particulate matter discharged to the atmosphere. The compliance deadline for installing the PM CEMS and all requirements relating to performance of the PM CEMS and implementation of the PM CEMS requirement is deferred pending further rulemaking.

(j) An owner or operator may submit an application to the Administrator for approval of alternate monitoring requirements to demonstrate compliance with the emission standards of this subpart, except for emission standards for THC.

(1) The Administrator will not approve averaging periods other than those specified in this section, unless the owner or operator documents, using data or information, that the longer averaging period will ensure that emissions do not exceed levels achieved during the performance test over any increment of time equivalent to the time required to conduct three runs of the performance test.

(2) If the application to use an alternate monitoring requirement is approved, the owner or operator must continue to use the original monitoring requirement until approval is received to use another monitoring requirement.

(3) The owner or operator shall submit the application for approval of alternate monitoring requirements no later than the notification of performance test. Theapplication must contain the information specified in paragraphs (i)(3)(i) through (i)(3)(iii) of this section:

(i) Data or information justifying the request, such as the technical or economic infeasibility, or the impracticality of using the required approach;

(ii) A description of the proposed alternative monitoring requirement, including the operating parameter to be monitored, the monitoring approach and technique, the averaging period for the limit, and how the limit is to be calculated; and

(iii) Data or information documenting that the alternative monitoring requirement would provide equivalent or better assurance of compliance

with the relevant emission standard.

(4) The Administrator will notify the owner or operator of the approval or denial of the application within 90 calendar days after receipt of the original request, or within 60 calendar days of the receipt of any supplementary information, whichever is later. The Administrator will not approve an alternate Monitoring application unless it would provide equivalent or better assurance of compliance with the relevant emission standard. Before disapproving any alternate monitoring application, the Administrator will provide:

(i) Notice of the information and findings upon which the intended disapproval is based; and

(ii) Notice of opportunity for the owner or operator to present additional supporting information before final action is taken on the application. This notice will specify how much additional time is allowed for the owner or operator to provide additional supporting information.

(5) The owner or operator is responsible for submitting any supporting information in a timely manner to enable the Administrator to consider the application prior to the performance test. Neither submittal of an application, nor the Administrator's failure to approve or disapprove the application relieves the owner or operator of the responsibility to comply with any provision of this subpart.

(6) The Administrator may decide at any time, on a case-by-case basis that additional or alternative operating limits, or alternative approaches to establishing operating limits, are necessary to demonstrate compliance with the emission standards of this subpart.

6. Additional Test Methods.(a) Owners or operators conducting tests to determine the rates of emission of hydrogen chloride (HCl) from kilns, in-line kiln/raw mills and associated bypass stacks at portland cement manufacturing facilities, for use in applicability determinations under Sec. 63.1340 are permitted to use Method 320 or Method 321 of appendix A of this part. (b) Owners or operators conducting tests to determine the rates of emission of hydrogen chloride (HCl) from kilns, in-line kiln/raw mills and associated bypass stacks at portland cement manufacturing facilities, for use in applicability determinations under Sec. 63.1340 are permitted to use Methods 26 or 26A of appendix A to part 60 of this chapter, except

that the results of these tests shall not be used to establish status as an area source. (c) Owners or operators conducting tests to determine the rates of emission of specific organic HAP from raw material dryers, kilns and in-line kiln/raw mills at portland cement manufacturing facilities, for use in applicability determinations under Sec. 63.1340 of this subpart are permitted to use Method 320 of appendix A to this part, or Method 18 of appendix A to part 60 of this chapter.

7. Notification Requirements

(a) The notification provisions of 40 CFR part 63, subpart A that apply and those that do not apply to owners and operators of affected sources subject to this subpart are listed in Table 1 of this subpart. If any State requires a notice that contains all of the information required in a notification listed in this section, the owner or operator may send the Administrator a copy of the notice sent to the State to satisfy the requirements of this

section for that notification. (b) Each owner or operator subject to the requirements of this subpart shall comply with the notification requirements in Sec. 63.9 as follows: (1) Initial notifications as required by Sec. 63.9(b) through (d). For the purposes of this subpart, a Title V or 40 CFR part 70 permit application may be used in lieu of the initial notification required under Sec. 63.9(b), provided the same information is contained in the permit application as required by Sec. 63.9(b), and the State to which the permit application has been submitted has an approved operating permit program under part 70 of this chapter and has received delegation of authority from the EPA. Permit applications shall be submitted by the same due dates as those specified for

the initial notification. (2) Notification of performance tests, as required by Secs. 63.7 and 63.9(e). (3) Notification of opacity and visible emission observations required by Sec. 63.1349 in accordance with Secs. 63.6(h)(5) and 63.9(f). (4) Notification, as required by Sec. 63.9(g), of the date that the continuous emission monitor performance evaluation required by Sec. 63.8(e) is scheduled to begin. (5) Notification of compliance status, as required by Sec. 63.9(h).

8. Reporting requirements.(a) The reporting provisions of subpart A of this part that apply and those that do not apply to owners or operators of affected sources subject to this subpart are listed in Table 1 of this subpart. If any State requires a report that contains all of the information required in a report listed in this section, the owner or operator may send the Administrator a copy of the report sent to the State to satisfy the requirements of this section for that report. (b) The owner or operator of an aff ected source shall comply with the reporting requirements specified in Sec. 63.10 of the general provisions of this part 63, subpart A as

follows:

(1) As required by Sec. 63.10(d)(2), the owner or operator shall report the results of performance tests as part of the notification of compliance status. (2) As required by Sec. 63.10(d)(3), the owner or operator of an affected source shall report the opacity results from tests required by Sec. 63.1349. (3) As required by Sec. 63.10(d)(4), the owner or operator of an affected source who is required to submit progress reports as a condition of receiving an extension of compliance under Sec. 63.6(i) shall submit such reports by the dates specified in the written extension of compliance. (4) As required by Sec. 63.10(d)(5), if actions taken by an owner or operator during a startup, shutdown, or malfunction of an affected source (including actions taken to correct a malfunction) are consistent with the procedures specified in the source's startup, shutdown, and malfunction plan specified in Sec. 63.6(e)(3), the owner or operator shall state such information in a semiannual report. Reports shall only be required if a startup, shutdown, or malfunction occurred during the reporting period. The startup, shutdown, and malfunction report may be submitted simultaneously with the excess emissions and continuous monitoring system performance reports; and (5) Any time an action taken by an owner or operator during a startup, shutdown, or malfunction (including actions taken to correct a malfunction) is not consistent with the procedures in the startup, shutdown, and malfunction plan, the owner or operator shall make an immediate report of the actions taken for that event within 2 working days, by telephone call or facsimile (FAX) transmission. The immediate report shall be followed by a letter, certified by the owner or operator or other responsible official, explaining the circumstances of the event, the reasons for not following the startup, shutdown, and malfunction plan, and whether any excess emissions and/or parameter monitoring exceedances are

believed to have occurred. (6) As required by Sec. 63.10(e)(2), the owner or operator shall submit a written report of the results of the performance evaluation for the continuous monitoring system required by Sec. 63.8(e). The owner or operator shall submit the report simultaneously with the results of the performance test. (7) As required by Sec. 63.10(e)(2), the owner or operator of an affected source using a continuous opacity monitoring system to determine opacity compliance during any performance test required under Sec. 63.7 and described in Sec.63.6(d)(6) shall report the results of the continuous opacity monitoring system performance evaluation conducted under Sec. 63.8(e). (8) As required by Sec. 63.10(e)(3), the owner or operator of an affected source equipped with a continuous emission monitor shall submit an excess emissions and continuous monitoring system performance report for any event when the continuous monitoring system data indicate the source is not in compliance with the applicable emission limitation or operating parameter limit. (9) The owner or operator shall submit a summary report semiannually which contains the information specified in Sec. 63.10(e)(3)(vi). In addition, the summary report shall include:

(i) All exceedences of maximum control device inlet gas temperature limits specified in Sec. 63.1344(a) and (b);

(ii) All failures to calibrate thermocouples and other temperature sensors as required under Sec. 63.1350(f)(7) of this subpart; and

(iii) All failures to maintain the activated carbon injection rate, and the activated carbon injection carrier gas flow rate or pressure drop, as applicable, as required under Sec. 63.1344(c).

(iv) The results of any combustion system component inspections conducted within the reporting period as required under Sec. 63.1350(i).

(v) All failures to comply with any provision of the operation and maintenance plan developed in accordance with Sec. 63.1350(a).

(10) If the total continuous monitoring system downtime for any CEM or any continuous monitoring system (CMS) for the reporting period is ten percent or greater of the total operating time for the reporting period, the owner or operator shall submit an excess emissions and continuous monitoring system performance report along with the summary report.

9. Recordkeeping requirements.

(a) The owner or operator shall maintain files of all information (including all reports and notifications) required by this section recorded in a form suitable and readily available for inspection and review as required by Sec. 63.10(b)(1). The files shall be retained for at least five years following the date of each occurrence, measurement, maintenance, corrective action, report, or record. At a minimum, the most recent two years of data shall be retained on site. The remaining three years of data may be retained off site. The files may be maintained on microfilm, on a computer, on floppy disks, on magnetic tape, or on microfiche. (b) The owner or operator shall maintain records for each affected source as required by Sec. 63.10(b)(2) and (b)(3) of this part; and(1) All documentation supporting initial notifications and notifications of compliance status under Sec. 63.9; (2) All records of applicability determination, including supporting analyses; and (3) If the owner or operator has been granted a waiver under Sec. 63.8(f)(6), any information demonstrating whether a source is meeting the requirements for a waiver of recordkeeping or reporting requirements.

(c) In addition to the recordkeeping requirements in paragraph (b) of this section, the owner or operator of an affected source equipped with a continuous monitoring system shall maintain all records required by Sec. 63.10(c).

10. Exemption from new source performance standards.

(a) Except as provided in paragraphs (a)(1) and (a)(2) of this section, any affected source subject to the provisions of this subpart is exempted from any otherwise applicable new source performance standard contained in 40 CFR part 60, subpart F.

(1) Kilns and in-line kiln/raw mills, as applicable under 40 CFR 60.60(b), located at area sources are subject to PM and opacity limits and associated reporting and recordkeeping, under 40 CFR part 60, subpart F. (2) Greenfield raw material dryers, as applicable under 40 CFR 60.60(b), located at area sources are subject to opacity limits and associated reporting and recordkeeping under 40 CFR part 60, subpart F.

11. Temporary, conditioned exemption from particulate matter and opacity

standards

.

(a) Subject to the limitations of paragraphs (b ) through (f) of this section, an owner or operator conducting PM CEMS correlation tests (that is, correlation with manual stack methods) is exempt from:

(1) Any particulate matter and opacity standards of part 60 or part 63 of this chapter that are applicable to cement kilns and in-line kiln/raw mills. (2) Any permit or other emissions or operating parameter or other limitation on workplace practices that are applicable to cement kilns and in-line kiln raw mills to ensure compliance with any particulate matter and opacity standards of this part or part 60 of this chapter.

(b) The owner or operator must develop a PM CEMS correlation test plan. The plan must be submitted to the Administrator for approval at least 90 days before the correlation test is scheduled to be conducted. The plan must include:

(1) The number of test conditions and the number of runs for each test condition; (2) The target particulate matter emission level for each test condition;(3) How the operation of the affected source will be modified to attain the desired particulate matter emission rate; and (4) The anticipated normal particulate matter emission level.

(c) The Administrator will review and approve or disapprove the correlation test plan in accordance with Sec. 63.7(c)(3)(i) and (iii). If the Administrator fails to approve or disapprove the correlation test plan within the time period specified in Sec. 63.7(c)(3)(iii), the plan shall be considered approved, unless the Administrator has requested additional information.

(d) The stack sampling team must be on-site and prepared to perform correlation testing no later than 24 hours after operations are modified to attain the desired particulate matter emissions concentrations, unless the correlation test plan documents that a longer period is appropriate.

(e) The particulate matter and opacity standards and associated operating limits and conditions will not be waived for more than 96 hours, in the aggregate, for a correlation test, including all runs and

conditions.

(f) The owner or operator must return the affected source to operating conditions indicative of compliance with the applicable particulate matter and opacity standards as soon as possible after correlation testing is completed.

12. Delegation of authority

.

(a) In delegating implementation and enforcement authority to a State under subpart E of this part, the authorities contained in paragraph (b) of this section shall be retained by

the Administrator and not transferred to a State. (b) Authority which will not be delegated to States:

(1) Approval of alternative non-opacity emission standards under Sec. 63.6(g). (2) Approval of alternative opacity standards under Sec. 63.6(h)(9). (3) Approval of major changes to test methods under Secs. 63.7(e)(2)(ii) and 63.7(f). A major change to a test method is a modification to a federally enforceable test method that uses unproven technology or procedures or is an entirely new method (sometimes necessary when the required test method is unsuitable). (4) Approval of major changes to monitoring under Sec. 63.8(f). A major change to monitoring is a modification to federally enforceable monitoring that uses unproven technology or procedures, is an entirely new method (sometimes necessary when the required monitoring is unsuitable), or is a change in the averaging period.

(5) Waiver of recordkeeping under Sec. 63.10(f).Authority for requirement: KCDAQM Regulations section 35.0G. SOURCE SPECIFIC CONDITIONS, OPERATING LIMITATIONS, AND MONITORING, RECORD KEEPING, AND REPORTING REQUIREMENTS FOR EMISSION UNIT GROUP 01B, 01C, 01D, 01E :

Emission Unit Description : Emission unit group 01B are Volatile Organic Liqui d Storage Tanks which are used to store used oil or diesel fuel. Emission unit group 01C is comprised of Road Emissions (01C-01) and Roads (01C-02). Emission unit group 01D is Piles and Internal Transfers. Emission unit group 01E is Fugitive Process Sources.

G1. Emission limits

.

The permittee shall take all reasonable precautions to prevent particulate matter from becoming airborne on haul roads. This includes: applying water, as needed, to haul roads, paving of roadways, and maintaining roadways in a clean condition.

Authority for requirement: KCDAQM Regulations section 22.0

G2. Operating Restrictions: n one

G3. Monitoring and/or record keeping requirements: none

G4. Reporting Requirements. none

G5. Testing requirements. none

G6. Miscellaneous Requirements. none

### ATTACHMENT A NSPS 40 CFR 60 Subpart OOO

Subpart OOO-Standards of Performance for Nonmetallic Mineral Processing Plants Source: 51 FR 31337, Aug. 1, 1985, unless otherwise noted.

§ 60.670 Applicability and designation of affected facility. (a) (1) Except as provided in paragraphs (a)(2), (b), (c), and (d) of this section, the provisions of this subpart are applicable to the following affected facilities in fixed or portable nonmetallic mineral processing plants: each 479crusher, grinding mill, screening operation, bucket elevator, be lt conveyor, bagging operation, storage bin, enclosed truck or railcar loading station. Also, crushers and grinding mills at hot mix asphalt facilities that reduce the size of nonmetallic minerals embedded in recycled asphalt pavement and subsequent affected facilities up to, but not including, the first storage silo or bin are subject to the provisions of this subpart.

(2)The provisions of this subpart do not apply to the following operations: All facilities located in underground mines; and stand-alone screening operations at plants without crushers or grinding mills.

(b) An affected facility that is subject to the provisions of subpart F or I or that follows in the plant process any facility subject to the provisions of subparts F or I of this part is not subject to the provisions of this subpart.

(c) Facilities at the following plants are not subject to the provisions of this subpart:

(1) Fixed sand and gravel plants and crushed stone plants with capacities, as defined in §60.671, of 23 megagrams per hour (25 tons per hour) or less;

(2) Portable sand and gravel plants and crushed stone plants with capacities, as defined in §60.671, of 136 megagrams per hour (150 tons per hour) or less; and

(3) Common clay plants and pumice plants with capacities, as defined in §60.671, of 9 megagrams per hour (10 tons per hour) or less.

(d) (1) When an existing facility is replaced by a piece of equipment of equal or smaller size, as defined in §60.671, having the same function as the existing facility, the new facility is exempt from the provisions of §§60.672, 60.674, and 60.675 except as provided for in paragraph (d)(3) of this section.

(2)An owner or operator complying with paragraph (d)(1) of this section shallsubmit the information required in §60.676(a).

(3)An owner or operator replacing all existing facilities in a production line with new facilities does not qualify for the exemption described in paragraph (d)(1) of this section and must comply with the provisions of §§60.672, 60.674 and 60.675.

(e) An affected facility under paragraph (a) of this section that commences construction, reconstruction, or modification after August 31, 1983 is subject to the requirements of this part.

(f) Table 1 of this subpart specifies the provi sions of subpart A of this part 60 that apply and those that do not apply to owners and operators of affected facilities subject to this subpart.

Table 1--Applicability of Subpart A To Subpart OOO

_________________________________________________________________________

_____ Applies to Subpart Subpart A reference OOO Comment

_________________________________________________________________________

_____ 60.1, Applicability... Yes................. 60.2, Definitions..... Yes................. 60.3, Units and Yes.................

abbreviations. 60.4, Address: (a)............... Yes................. (b)............... Yes................. 60.5, Determination of Yes.................

construction or

modification. 60.6, Review of plans. Yes................. 60.7, Notification and Yes.............. Except in (a)(2) report of recordkeeping. anticipated date of initial startup is not required (§60.676(h)). 60.8, Performance Yes................ Except in (d), after 30 days tests. Notice for an initially scheduled performance test, any rescheduled performance testrequires 7 days notice, not 30 days (§60.675(g)). 60.9, Availability of Yes.................

information. 60.10, State authority Yes................. 60.11, Compliance with Yes................. Except in (b) under certain standards and conditions (§§60.675 (c)(3) and maintenance (c)(4)), Method 9 observation requirements. may be reduced from 3 hours to

1 hour. Some affected facilities exempted from Method 9 tests (§60.675(h)). 60.12, Circumvention.. Yes................. 60.13, Monitoring Yes................. requirements. 60.14, Modification... Yes................. 60.15, Reconstruction. Yes................. 60.16, Priority list.. Yes................. 60.17, Incorporations Yes................. by reference. 60.18, General control No.................. Flares will not be used to device. comply with the emission

limits. 60.19, General Yes.................

notification and reporting requirements.

_________________________________________________________________________

_____

[51 FR 31337, Aug. 1, 1985, as amended at 62 FR 31359, June 9, 1997]

§ 60.671 Definitions.

All terms used in this subpart, but not specifically defined in this section, shall have the meaning given them in the Act and in subpart A of this part.

Bagging operation means the mechanical process by which bags are filled with

nonmetallic minerals.

Belt conveyor means a conveying device that transports material from one location to another by means of an endless belt that is carried on a series of idlers and routed around a pulley at each end.

Bucket elevator means a conveying device of nonmetallic minerals consisting of a head and foot assembly which supports and drives an endless single or double strand chain orbelt to which buckets are attached.

Building means any frame structure with a roof.

Capacity means the cumulative rated capacity of all initial crushers that are part of the plant.

Capture system means the equipment (including enclosures, hoods, ducts, fans, dampers, etc.) used to capture and transport particulate matter generated by one or more process operations to a control device.

Control device means the air pollution control equipment used to reduce particulate matter emissions released to the atmosphere from one or more process operations at a nonmetallic mineral processing plant.

Conveying system means a device for transporting materials from one piece of equipment or location to another location within a plant. Conveying systems include but are not limited to the following: Feeders, belt conveyors, bucket elevators and pneumatic systems.

Crusher means a machine used to crush any nonmetallic minerals, and includes, but is not limited to, the following types: jaw, gyratory, cone, roll, rod mill, hammermill, and impactor.

Enclosed truck or railcar loading station means that portion of a nonmetallic mineral processing plant where nonmetallic minerals are loaded by an enclosed conveying system

into enclosed trucks or railcars.

Fixed plant means any nonmetallic mineral processing plant at which the processing equipment specified in §60.670(a) is attached by a cable, chain, turnbuckle, bolt or other means (except electrical connections) to any anchor, slab, or structure including bedrock.

Fugitive emission means particulate matter that is not collected by a capture system and is released to the atmosphere at the point of generation.

Grinding mill means a machine used for the wet or dry fine crushing of any nonmetallic mineral. Grinding mills include, but are not limited to, the following types: hammer, roller, rod, pebble and ball, and fluid energy. The grinding mill includes the air conveying system, air separator, or air classifier, where such systems are used.

Initial crusher means any crusher into which nonmetallic minerals can be fed without prior crushing in the plant.

Nonmetallic mineral means any of the following minerals or any mixture of which the majority is any of the following minerals: (a) Crushed and Broken Stone, including Limestone, Dolomite, Granite, Traprock, Sandstone, Quartz, Quartzite, Marl, Marble, Slate, Shale, Oil Shale, and Shell.(b) Sand and Gravel. (c) Clay including Kaolin, Fireclay, Bentonite, Fuller's Earth, Ball Clay, and Common Clay. (d) Rock Salt. (e) Gypsum.481 (f) Sodium Compounds, including Sodium Carbonate, Sodium Chloride, and Sodium

Sulfate. (g) Pumice. (h) Gilsonite. (i) Talc and Pyrophyllite. (j) Boron, including Borax, Kernite, and Colemanite. (k) Barite. (l) Fluorospar. (m) Feldspar. (n) Diatomite. (o) Perlite. (p) Vermiculite. (q) Mica. (r) Kyanite, including Andalusite, Sillimanite, Topaz, and Dumortierite.

Nonmetallic mineral processing plant means any combination of equipment that is used to crush or grind any nonmetallic mineral wherever located, including lime plants, power plants, steel mills, asphalt concrete plants, portland cement plants, or any other facility processing nonmetallic minerals except as provided in §60.670 (b) and (c).

Portable plant means any nonmetallic mineral processing plant that is mounted on any chassis or skids and may be moved by the application of a lifting or pulling force. In addition, there shall be no cable, chain, turnbuckle, bolt or other means (except electrical connections) by which any piece of equipment is attached or clamped to any anchor, slab, or structure, including bedrock that must be re moved prior to the application of a lifting or pulling force for the purpose of transporting the unit.

Production line means all affected facilities (crushers, grinding mills, screening operations, bucket elevators, belt conveyors, bagging operations, storage bins, and enclosed truck and railcar loading stations) which are directly connected or are connected together by a conveying system.

Screening operation means a device for separating material according to size by passing undersize material through one or more mesh surfaces (screens) in series, and retaining oversize material on the mesh surfaces (screens).

Size means the rated capacity in tons per hour of a crusher, grinding mill, bucket elevator, bagging operation, or enclosed truck or railcar loading station; the total surface area of the top screen of a screening operation; the width of a conveyor belt; and the rated capacity in tons of a storage bin.Stack emission means the particulate matter that is released to the atmosphere from a

capture system.

Storage bin means a facility for storage (including surge bins) or nonmetallic minerals prior to further processing or loading.

Transfer point means a point in a conveying operation where the nonmetallic mineral is transferred to or from a belt conveyor except where the nonmetallic mineral is being transferred to a stockpile.

Truck dumping means the unloading of nonmetallic minerals from movable vehicles designed to transport nonmetallic minerals from one location to another. Movable vehicles include but are not limited to: trucks, front end loaders, skip hoists, and railcars.

Vent means an opening through which there is mechanically induced air flow for the purpose of exhausting from a building air carrying particulate matter emissions from one or

more affected facilities.

Wet mining operation means a mining or dredging operation designed and operated to extract any nonmetallic mineral regulated under this subpart from deposits existing at or below the water table, where the nonmetallic mineral is saturated with water.

Wet screening operation means a screening operation at a nonmetallic mineral processing plant which removes unwanted material or which separates marketable fines from the product by a washing process which is designed and operated at all times such that the product is saturated with water. [51 FR 31337, Aug. 1, 1985, as amended at 62 FR 31359, June 9, 1997]

§ 60.672 Standard for particulate matter. (a) On and after the date on which the performance test required to be conducted by §60.8 is completed, no owner or operator subject to the provisions of this subpart shall cause to be discharged into the atmosphere from any transfer point on belt conveyors or from any other affected facility any stack emissions which:

(1) Contain particulate matter in excess of 0.05 g/dscm; and

(2) Exhibit greater than 7 percent opacity, unless the stack emissions are discharged from an affected facility using a wet scrubbing control device. Facilities using a wet scrubber must comply with the reporting provisions of §60.676 (c), (d), and (e).

(b) On and after the sixtieth day after achieving the maximum production rate at which the affected facility will be operated, but not later than 180 days after initial startup as required under §60.11 of this part, no owner or operator subject to the provisions of this subpart shall cause to be discharged into the atmosphere from any transfer point on belt conveyors or from any other affected facility any fugitive emissions which exhibit greater than 10 percent opacity, except as provided in paragraphs (c),(d), and (e) of this section.

(c) On and after the sixtieth day after achieving the maximum production rate at which the affected facility will be operated, but not later than 180 days after initial startup as required under §60.11 of this part, no owner or operator shall cause to be discharged into the atmosphere from any crusher, at which a capture system is not used, fugitive emissions which exhibit greater than 15 percent opacity.

(d) Truck dumping of nonmetallic minerals into any screening operation, feed hopper, or crusher is exempt from the requirements of this section.

(e) If any transfer point on a conveyor belt or any other affected facility is enclosed in a building, then each enclosed affected fac ility must comply with the emission limits in paragraphs (a), (b) and (c) of this section, or the building enclosing the affected facility or facilities must comply with the following emission limits:

(1) No owner or operator shall cause to be discharged into the atmosphere from any building enclosing any transfer point on a conveyor belt or any other affected facility any visible fugitive emissions except emissions from a vent as defined in §60.671.

(2) No owner or operator shall cause to be discharged into the atmosphere from any vent of any building enclosing any transf er point on a conveyor belt or any other affected facility emissions which exceed the stack emissions limits in paragraph (a) of this section.

(f) On and after the sixtieth day after achieving the maximum production rate at which the affected facility will be operated, but not later than 180 days after initial startup as required under §60.11 of this part, no owner or operator shall cause to be discharged into the atmosphere from any baghouse that controls emissions from only an individual, enclosed storage bin, st ack emissions which exhibit greater than 7 percent opacity.

(g) Owners or operators of multiple storage bins with combined stack emissions shall comply with the emission limits in paragraph (a)(1) and (a)(2) of this section.

(h) On and after the sixtieth day after achieving the maximum production rate at which the affected facility will be operated, but not later than 180 days after initial startup, no owner or operator shall cause to be discharged into the atmosphere any visible

emissions from:

(1) Wet screening operations and subsequent screening operations, bucket elevators, and belt conveyors that process saturated material in the production line up to the next crusher, grinding mill or storage bin.(2) Screening operations, bucket elevators, and belt conveyors in the production line downstream of wet mining operations, where such screening operations, bucket elevators, and belt conveyors process saturated materials up to the first crusher, grinding mill, or storage bin in the production line.

[51 FR 31337, Aug. 1, 1985, as amended at 62 FR 31359, June 9, 1997]

§ 60.673 Reconstruction. (a) The cost of replacement of ore-contact surfaces on processing equipment shall not be considered in calculating either the ``fixed capital cost of the new components'' or the ``fixed capital cost that would be required to construct a comparable new facility'' under §60.15. Ore-contact surfaces are crushing surfaces; screen meshes, bars, and plates; conveyor belts; and elevator buckets.

(b) Under §60.15, the ``fixed capital cost of the new components'' includes the fixed capital cost of all depreciable components (except components specified in paragraph (a) of this section) which are or will be replaced pursuant to all continuous programs of component replacement commenced within any 2-year period following August 31, 1983.

§ 60.674 Monitoring of operations.

The owner or operator of any affected facility subject to the provisions of this subpart which uses a wet scrubber to control emissions shall install, calibrate, maintain and operate the following monitoring devices:

(a) A device for the continuous measurement of the pressure loss of the gas stream through the scrubber. The monitoring device must be certified by the manufacturer to be accurate within ±250 pascals ±1 inch water gauge pressure and must be

calibrated on an annual basis in accordance with manufacturer's instructions.

(b) A device for the continuous measurement of the scrubbing liquid flow rate to the wet scrubber. The monitoring device must be certified by the manufacturer to be accurate within ±5 percent of design scrubbing liquid flow rate and must be

calibrated on an annual basis in accordance with manufacturer's instructions.

§ 60.675 Test methods and procedures.

(a) In conducting the performance tests required in §60.8, the owner or operator shall use as reference methods and procedures the test methods in appendix A of this part or other methods and procedures as specified in this section, except as provided in §60.8(b). Acceptable alternative methods and procedures are given in paragraph (e)

of this section.(b) The owner or operator shall determine compliance with the particulate matter standards in §60.672(a) as follows:

(1) Method 5 or Method 17 shall be used to determine the particulate matter concentration. The sample volume shall be at least 1.70 dscm (60 dscf). For Method 5, if the gas stream being sampled is at ambient temperature, the sampling probe and filter may be operated without heaters. If the gas stream is above ambient temperature, the sampling probe and filter may be operated at a temperature high enough, but no higher than 121 °C (250 °F), to prevent water

condensation on the filter.

(2) Method 9 and the procedures in §60.11 shall be used to determine opacity.

(c) (1) In determining compliance with the particulate matter standards in §60.672 (b) and (c), the owner or operator shall use Method 9 and the procedures in §60.11, with the following additions:

(i)The minimum distance between the observer and the emission source shall be 4.57 meters (15 feet).

(ii) The observer shall, when possible, select a position that minimizes interference from other fugitive emission sources (e.g., road dust). The required observer position relative to the sun (Method 9, Section 2.1) must

be followed.

(iii) For affected facilities using wet dust suppression for particulate matter control, a visible mist is sometimes generated by the spray. The water mist must not be confused with particulate matter emissions and is not to be considered a visible emission. When a water mist of this nature is present, the observation of emissions is to be made at a point in the plume where the mist is no longer visible.

(2)In determining compliance with the opacity of stack emissions from any baghouse that controls emissions only from an individual enclosed storage bin under §60.672(f) of this subpart, using Method 9, the duration of the Method 9 observations shall be 1 hour (ten 6-minute averages).

(3) When determining compliance with the fugitive emissions standard for any affected facility described under §60.672(b) of this subpart, the duration of the Method 9 observations may be reduced from 3 hours (thirty 6-minute averages) to 1 hour (ten 6-minute averages) only if the following conditions apply:

(i) There are no individual readings greater than 10 percent opacity; and(ii) There are no more than 3 readings of 10 percent for the 1-hour period.

(4) When determining compliance with the fugitive emissions standard for any crusher at which a capture system is not used as described under 484§60.672(c) of this subpart, the duration of the Method 9 observations may be reduced from 3 hours (thirty 6-minute averages) to 1 hour (ten 6-minute averages) only if the following conditions apply:

(i) There are no individual readings greater than 15 percent opacity; and (ii) There are no more than 3 readings of 15 percent for the 1-hour period.

(d) In determining compliance with §60.672(e), the owner or operator shall use Method 22 to determine fugitive emissions. The performance test shall be conducted while all affected facilities inside the building are operating. The performance test for each building shall be at least 75 minutes in duration, with each side of the building and the roof being observed for at least 15 minutes.

(e) The owner or operator may use the following as alternatives to the reference methods and procedures specified in this section:

(1) For the method and procedure of paragraph (c) of this section, if emissions from two or more facilities continuously interf ere so that the opacity of fugitive emissions from an individual affected facility cannot be read, either of the following procedures may be used:

(i)Use for the combined emission stream the highest fugitive opacity standard applicable to any of the individual affected facilities contributing to

the emissions stream.

(ii) Separate the emissions so that the opacity of emissions from each affected facility can be read.

(f) To comply with §60.676(d), the owner or operator shall record the measurements as required in §60.676(c) using the monitoring devices in §60.674 (a) and (b) during each particulate matter run and shall determine the averages.

(g) If, after 30 days notice for an initially scheduled performance test, there is a delay (due to operational problems, etc.) in conducting any rescheduled performance test required in this section, the owner or operator of an affected facility shall submit a notice to the Administrator at least 7 days prior to any rescheduled performance test.

(h) Initial Method 9 performance tests under §60.11 of this part and §60.675 of this subpart are not required for:(1) Wet screening operations and subsequent screening operations, bucket elevators, and belt conveyors that process saturated material in the production line up to, but not including the next crusher, grinding mill or storage bin.

(2) Screening operations, bucket elevators, and belt conveyors in the production line downstream of wet mining operations, that process saturated materials up to the first crusher, grinding mill, or storage bin in the production line.

[54 FR 6680, Feb. 14, 1989, as amended at 62 FR 31360, June 9, 1997]

§ 60.676 Reporting and recordkeeping.

(a) Each owner or operator seeking to comply with §60.670(d) shall submit to the Administrator the following information about the existing facility being replaced and the replacement piece of equipment.

(1) For a crusher, grinding mill, bucket elevator, bagging operation, or enclosed truck or railcar loading station:

(i) The rated capacity in tons per hour of the existing facility being replaced and (ii) The rated capacity in tons per hour of the replacement equipment.

(2) For a screening operation:

(i) The total surface area of the top screen of the existing screening operation being replaced and (ii) The total surface area of the top screen of the replacement screening operation.

(3) For a conveyor belt:

(i) The width of the existing belt being replaced and (ii) The width of the replacement conveyor belt.

(4) For a storage bin:

(i) The rated capacity in tons of the existing storage bin being replaced and (ii) The rated capacity in tons of replacement storage bins.

(b) [Reserved]

(c) During the initial performance test of a wet scrubber, and daily thereafter, the owner or operator shall record the measurements of both the 485change in pressure of the gas stream across the scrubber and the scrubbing liquid flow rate.(d) After the initial performance test of a we t scrubber, the owner or operator shall submit semiannual reports to the Administrator of occurrences when the measurements of the scrubber pressure loss (or gain) and liquid flow rate differ by more than ±30 percent from the averaged determined during the most recent performance test.

(e) The reports required under paragraph (d) shall be postmarked within 30 days following end of the second and fourth calendar quarters.

(f) The owner or operator of any affected facility shall submit written reports of the results of all performance tests conducted to demonstrate compliance with the standards set forth in §60.672 of this subpart, including reports of opacity observations made using Method 9 to demonstrate compliance with §60.672(b), (c), and (f), and reports of observations using Method 22 to demonstrate compliance with §60.672(e).

(g) The owner or operator of any screening operation, bucket elevator, or belt conveyor that processes saturated material and is subject to §60.672(h) and subsequently processes unsaturated materials, shall submit a report of this change within 30 days following such change. This screening operation, bucket elevator, or belt conveyor is then subject to the 10 percent opacity limit in §60.672(b) and the emission test requirements of §60.11 and this subpart. Likewise a screening operation, bucket elevator, or belt conveyor that processes unsaturated material but subsequently processes saturated material shall submit a report of this change within 30 days following such change. This screening operation, bucket elevator, or belt conveyor is then subject to the no visible emission limit in §60.672(h).

(h) The subpart A requirement under §60.7(a)(2) for notification of the anticipated date of initial startup of an affected facility shall be waived for owners or operators of affected facilities regulated under this subpart.

(i) A notification of the actual date of initial startup of each affected facility shall be

submitted to the Administrator.

(1) For a combination of affected facilities in a production line that begin actual initial startup on the same day, a single notification of startup may be submitted by the owner or operator to the Administrator. The notification shall be postmarked within 15 days after such date and shall include a description of each affected facility, equipment manufacturer, and serial number of the equipment, if available.(2) For portable aggregate processing plants, the notification of the actual date of initial startup shall include both the home office and the current address or location of the portable plant.

(j) The requirements of this section remain in force until and unless the Agency, in delegating enforcement authority to a State under section 111(c) of the Act, approves reporting requirements or an alternative means of compliance surveillance adopted by such States. In that event, a ffected facilities within the State will be relieved of the obligation to comply with the reporting requirements of this section, provided that they comply with requirements established by the State.

[51 FR 31337, Aug. 1, 1985, as amended at 54 FR 6680, Feb. 14, 1989; 62 FR 31360, June 9, 1997]

### ATTACHMENT B NSPS 40 CFR 60 Subpart Y

Subpart Y-Standards of Performance for Coal Preparation Plants

§ 60.250 Applicability and designation of affected facility.

(a) The provisions of this subpart are applicable to any of the following affected facilities in coal preparation plants which process more than 200 tons per day: Thermal dryers, pneumatic coal-cleaning equipment (air tables), coal processing and conveying equipment (including breakers and crushers), coal storage systems, and coal transfer and loading systems.

(b) Any facility under paragraph (a) of this section that commences construction or modification after October 24, 1974, is subject to the requirements of this subpart.

[42 FR 37938, July 25, 1977; 42 FR 44812, Sept. 7, 1977]

§ 60.251 Definitions.

As used in this subpart, all terms not defined herein have the meaning given them in the Act and in subpart A of this part.

(a) Coal preparation plant means any facility (excluding underground mining operations) which prepares coal by one or more of the following processes: breaking, crushing, screening, wet or dry cleaning, and thermal drying.

(b) Bituminous coal means solid fossil fuel classified as bituminous coal by ASTM Designation D388-77 (incorporated by reference-see §60.17).

(c) Coal means all solid fossil fuels classified as anthracite, bituminous, subbituminous, or li1gnite by ASTM Designation D388-77 (incorporated by reference-see §60.17).

(d) Cyclonic flow means a spiraling movement of exhaust gases within a duct or stack.

(e) Thermal dryer means any facility in which the moisture content of bituminous coal is reduced by contact with a heated gas stream which is exhausted to the atmosphere.

(f) Pneumatic coal-cleaning equipment means any facility which classifies bituminous coal by size or separates bituminous coal from refuse by application of airstream(s).

(g) Coal processing and conveying equipment means any machinery used to reduce the size of coal or to separate coal from refuse, and the equipment used to convey coal to or remove coal and refuse from the machinery. This includes, but is not limited to, breakers, crushers, screens, and conveyor belts.

(h) Coal storage system means any facility used to store coal except for open storage piles.

(i) Transfer and loading system means any facility used to transfer and load coal for shipment.

[41 FR 2234, Jan. 15, 1976, as amended at 48 FR 3738, Jan. 27, 1983]

§ 60.252 Standards for particulate matter. \

(a) On and after the date on which the performance test required to be conducted by §60.8 is completed, an owner or operator subject to the provisions of this subpart shall not cause to be discharged into the atmosphere from any thermal dryer gases

which:

(1) Contain particulate matter in excess of 0.070 g/dscm (0.031 gr/dscf). (2) Exhibit 20 percent opacity or greater.

(b) On and after the date on which the performance test required to be conducted by §60.8 is completed, an owner or operator subject to the provisions of this subpart shall not cause to be discharged into the atmosphere from any pneumatic coal cleaning equipment, gases which:

(1) Contain particulate matter in excess of 0.040 g/dscm (0.018 gr/dscf). (2) Exhibit 10 percent opacity or greater.

(c) On and after the date on which the performance test required to be conducted by §60.8 is completed, an owner or operator subject to the provisions of this subpart shall not cause to be discharged into the atmosphere from any coal processing and conveying equipment, coal storage system, or coal transfer and loading system processing coal, gases which exhibit 20 percent opacity or greater.

[41 FR 2234, Jan. 15, 1976]

§ 60.253 Monitoring of operations.

(a) The owner or operator of any thermal dryer shall install, calibrate, maintain, andcontinuously operate monitoring devices as follows:

(3) A monitoring device for the measurement of the temperature of the gas stream at the exit of the thermal dryer on a continuous basis. The monitoring device is to be certified by the manufacturer to be accurate within ±3° Fahrenheit.

(4) For affected facilities that use venturi scrubber emission control equipment:

(i)A monitoring device for the continuous measurement of the pressure loss through the venturi constriction of the control equipment. The monitoring device is to be certified by the manufacturer to be accurate within ±1 inch

water gage.

(ii) A monitoring device for the continuous measurement of the water supply pressure to the control equipment. The monitoring device is to be certified by the manufacturer to be accurate within ±5 percent of design water supply pressure. The pressure sensor or tap must be located close to the water discharge point. The Administrator may be consulted for approval of

alternative locations.

(b) All monitoring devices under paragraph (a) of this section are to be recalibrated annually in accordance with procedures under §60.13(b).

[41 FR 2234, Jan. 15, 1976, as amended at 54 FR 6671, Feb. 14, 1989]

§ 60.254 Test methods and procedures.

(a) In conducting the performance tests required in §60.8, the owner or operator shall use as reference methods and procedures the test methods in appendix A of this part or other methods and procedures as specified in this section, except as provided in §60.8(b).

(b) The owner or operator shall determine compliance with the particular matter standards in §60.252 as follows:

(2) Method 5 shall be used to determine the particulate matter concentration. The sampling time and sample volume for each run shall be at least 60 minutes and 0.85 dscm (30 dscf). Sampling shall begin no less than 30 minutes after startup and shall terminate before shutdown procedures begin.

(2) Method 9 and the procedures in §60.11 shall be used to determine opacity.

[54 FR 6671, Feb. 14, 1989]

### ATTACHMENT C NESHAP 40 CFR 63 Subpart LLL

Subpart LLL_National Emission Standards for Hazardous Air Pollutants From the Portland Cement Manufacturing Industry

Source: 64 FR 31925, June 14, 1999, unless otherwise noted.

General

Sec. 63.1340 Applicability and designation of affected sources.

(a) Except as specified in paragraphs (b) and (c) of this section, the provisions of this subpart apply to each new and existing portland cement plant which is a major source or an area source as defined in

Sec. 63.2. (b) The affected sources subject to this subpart are: (1) Each kiln and each in-line kiln/raw mill at any major or area source, including alkali bypasses, except for kilns and in-line kiln/raw mills that burn hazardous waste and are subject to and regulated under subpart EEE of this part; (2) Each clinker cooler at any portland cement plant which is a major source; (3) Each raw mill at any portland cement plant which is a major

source; (4) Each finish mill at any portland cement plant which is a major

source; (5) Each raw material dryer at any portland cement plant which is a major source and each greenfield raw material dryer at any portland cement plant which is a major or area source; (6) Each raw material, clinker, or finished product storage bin at any portland cement plant which is a major source; (7) Each conveying system transfer point including those associated with coal preparation used to convey coal from the mill to the kiln at any portland cement plant which is a major source; and (8) Each bagging and bulk loading and unloading system at any portland cement plant which is a major source. (c) For portland cement plants with on-site nonmetallic mineral processing facilities, the first affected source in the sequence of materials handling operations subject to this subpart is the raw material storage, which is just prior to the raw mill. Any equipment of the on-site nonmetallic mineral processing plant which precedes the raw material storage is not subject to this subpart. In addition, the primary and secondary crushers of the on-site nonmetallic mineral processing plant, regardless of whether they precede the raw material storage, are not subject to this subpart. Furthermore, the first conveyor transfer point subject to this subpart is the transfer point associated with the conveyor transferring material from the raw material storage to the raw mill. (d) The owner or operator of any affected source subject to the provisions of this subpart is subject to title V permitting requirements.

[64 FR 31925, June 14, 1999, as amended at 67 FR 16619, Apr. 5, 2002; 67 FR 72584, Dec. 6, 2002]

Sec. 63.1341 Definitions.

All terms used in this subpart that are not defined in this sectionhave the meaning given to them in the CAA and in subpart A of this part. Alkali bypass means a duct between the feed end of the kiln and the preheater tower through which a portion of the kiln exit gas stream is withdrawn and quickly cooled by air or water to avoid excessive buildup of alkali, chloride and/or sulfur on the raw feed. This may also be referred to as the ``kiln exhaust gas bypass''. Bagging system means the equipment which fills bags with portland

cement. Bin means a manmade enclosure for storage of raw materials, clinker, or finished product prior to further processing at a portland cement plant. Clinker cooler means equipment into which clinker product leaving the kiln is placed to be cooled by air supplied by a forced draft or natural draft supply system. Continuous monitor means a device which continuously samples the regulated parameter specified in Sec. 63.1350 of this subpart without interruption, evaluates the detector response at least once every 15 seconds, and computes and records the average value at least every 60 seconds, except during allowable periods of calibration and except as defined otherwise by the continuous emission monitoring system performance specifications in appendix B to part 60 of this chapter. Conveying system means a device for transporting materials from one piece of equipment or location to another location within a facility. Conveying systems include but are not limited to the following: feeders, belt conveyors, bucket elevators and pneumatic systems. Conveying system transfer point means a point where any material including but not limited to feed material, fuel, clinker or product, is transferred to or from a conveying system, or between separate parts of a conveying system. Dioxins and furans (D/F) means tetra-, penta-, hexa-, hepta-, and

octa-chlorinated dibenzo dioxins and furans. Facility means all contiguous or adjoining property that is under common ownership or control, including properties that are separated only by a road or other public right-of-way. Feed means the prepared and mixed materials, which include but are not limited to materials such as limestone, clay, shale, sand, iron ore, mill scale, cement kiln dust and flyash, that are fed to the kiln. Feed does not include the fuels used in the kiln to produce heat to form the clinker product. Finish mill means a roll crusher, ball and tube mill or other size reduction equipment used to grind clinker to a fine powder. Gypsum and other materials may be added to and blended with clinker in a finish mill. The finish mill also includes the air separator associated with

the finish mill. Greenfield kiln, in-line kiln/raw mill, or raw material dryer means a kiln, in-line kiln/raw mill, or raw material dryer for which construction is commenced at a plant site (where no kilns and no in-line kiln/raw mills were in operation at any time prior to March 24, 1998) after March 24, 1998. Hazardous waste is defined in Sec. 261.3 of this chapter. In-line kiln/raw mill means a system in a portland cement production process where a dry kiln system is integrated with the raw mill so that all or a portion of the kiln exhaust gases are used to perform the drying operation of the raw mill, with no auxiliary heat source used. In this system the kiln is capable of operating without the raw mill operating, but the raw mill cannot operate without the kiln gases, and consequently, the raw mill does not generate a separate exhaust gas

stream. Kiln means a device, including any associated preheater or precalciner devices, that produces clinker by heating limestone and other materials for subsequent production of portland cement.Kiln exhaust gas bypass means alkali bypass. Monovent means an exhaust configuration of a building or emission control device (e. g. positive pressure fabric filter) that extends the length of the structure and has a width very small in relation to its length (i. e., length to width ratio is typically greater than 5:1). The exhaust may be an open vent with or without a roof, louvered vents, or a

combination of such features. New brownfield kiln, in-line kiln raw mill, or raw material dryer means a kiln, in-line kiln/raw mill or raw material dryer for which construction is commenced at a plant site (where kilns and/or in-line kiln/raw mills were in operation prior to March 24, 1998) after March 24, 1998. One-minute average means the average of thermocouple or other sensor responses calculated at least every 60 seconds from responses obtained at least once during each consecutive 15 second period. Portland cement plant means any facility manufacturing portland

cement.Raw material dryer means an impact dryer, drum dryer, paddleequipped rapid dryer, air separator, or other equipment used to reduce

the moisture content of feed materials. Raw mill means a ball and tube mill, vertical roller mill or other size reduction equipment, that is not part of an in-line kiln/raw mill, used to grind feed to the appropriate size. Moisture may be added or removed from the feed during the grinding operation. If the raw mill is used to remove moisture from feed materials, it is also, by definition, a raw material dryer. The raw mill also includes the air separator

associated with the raw mill. Rolling average means the average of all one-minute averages over the averaging period. Run average means the average of the one-minute parameter values for

a run. TEQ means the international method of expressing toxicity equivalents for dioxins and furans as defined in U.S. EPA, Interim Procedures for Estimating Risks Associated with Exposures to Mixtures of Chlorinated Dibenzo-p-dioxins and -dibenzofurans (CDDs and CDFs) and 1989 Update, March 1989.

[64 FR 31925, June 14, 1999, as amended at 67 FR 16619, Apr. 5, 2002]

Emission Standards and Operating Limits

Sec. 63.1342 Standards: General.

(a) Table 1 to this subpart provides cross references to the 40 CFR part 63, subpart A, general provisions, indicating the applicability of the general provisions requirements to subpart LLL. (b) Table 1 of this section provides a summary of emission limits and operating limits of this subpart.Table 1 to Sec. 63.1342--Emission Limits and Operating Limits----------------------------------------------------------------------------------------------------------------Affected source Pollutant or opacity Emission and operating limit----------------------------------------------------------------------------------------------------------------All kilns and in-line kiln/raw mills at PM..................................... 0.15 kg/Mg of feed (drymajor sources (including alkali Opacity................................ basis).bypass). 20 percent.All kilns and in-line kiln/raw mills at D/F.................................... 0.20 ng TEQ/dscmmajor and area sources (including oralkali bypass). 0.40 ng TEQ/dscm when theaverage of the performancetest run average particulatematter control device (PMCD)inlet temperatures is 204[deg]C or less. [Corrected to7 percent oxygen]Operate such that the three-hour rolling average PMCDinlet temperature is nogreater than the temperatureestablished at performancetest.If activated carbon injectionis used: Operate such thatthe three-hour rollingaverage activated carboninjection rate is no lessthan rate established atperformance test. Operatesuch that either the carriergas flow rate or carrier gaspressure drop exceeds thevalue established atperformance test. Injectcarbon of equivalentspecifications to that usedat performance test.New greenfield kilns and in-line kiln/ THC.................................... 50 ppmvd, as propane,raw mills at major and area sources. corrected to 7 percentoxygen.All clinker coolers at major sources... PM..................................... 0.050 kg/Mg of feed (dryOpacity................................ basis)10 percent.All raw mills and finish mills at major Opacity................................ 10 percent.sources.New greenfield raw material dryers at THC.................................... 50 ppmvd, as propane,major and area sources. corrected to 7 percentoxygen.All raw material dryers and material Opacity................................ 10 percent.handling points at major sources.Sec. 63.1343 Standards for kilns and in-line kiln/raw mills.

(a) General. The provisions in this section apply to each kiln, each in-line kiln/raw mill, and any alkali bypass associated with that kiln or in-line kiln/raw mill. (b) Existing, reconstructed, or new brownfield/major sources. No owner or operator of an existing, reconstructed or new brownfield kiln or an existing, reconstructed or new brownfield in-line kiln/raw mill at a facility that is a major source subject to the provisions of this subpart shall cause to be discharged into the atmosphere from these affected sources, any gases which: (1) Contain particulate matter (PM) in excess of 0.15 kg per Mg (0.30 lb per ton) of feed (dry basis) to the kiln. When there is an alkali bypass associated with a kiln or in-line kiln/raw mill, the combined particulate matter emissions from the kiln or in-line kiln/raw mill and the alkali bypass are subject to this emission limit. (2) Exhibit opacity greater than 20 percent. (3) Contain D/F in excess of: (i) 0.20 ng per dscm (8.7x10 -11 gr per dscf) (TEQ) corrected to seven percent oxygen; or (ii) 0.40 ng per dscm (1.7x10 -10 gr per dscf) (TEQ) corrected to seven percent oxygen, when the average of the performance test run average temperatures at the inlet to the particulate matter control device is 204 [deg]C (400 [deg]F) or less. (c) Greenfield/major sources. No owner or operator that commences construction of a greenfield kiln or greenfield inline kiln/raw mill at a facility which is a major source subject to the provisions of this subpart shall cause to be discharged into the atmosphere from these affected sources any gases which: (1) Contain particulate matter in excess of 0.15 kg per Mg (0.30 lb per ton) of feed (dry basis) to the kiln. When there is an alkali bypass associated with a kiln or in-line kiln/raw mill, the combined particulate matter emissions from the kiln or in-line kiln/raw mill and the bypass stack are subject to this emission limit. (2) Exhibit opacity greater than 20 percent. (3) Contain D/F in excess of: (i) 0.20 ng per dscm (8.7x10 -11 gr per dscf) (TEQ) corrected to seven percent oxygen; or (ii) 0.40 ng per dscm (1.7x10 -10 gr per dscf) (TEQ) corrected to seven percent oxygen, when the average of the performance test run average temperatures at the inlet to the particulate matter control device is 204 [deg]C (400 [deg]F) or less. (4) Contain total hydrocarbon (THC), from the main exhaust of the kiln or in-line kiln/raw mill, in excess of 50 ppmvd as propane, corrected to seven percent oxygen. (d) Existing, reconstructed, or new brownfield/area sources. No owner or operator of an existing, reconstructed, or new brownfield kiln or an existing, reconstructed or new brownfield in-line kiln/raw mill at a facility that is an area source subject to the provisions of this subpart shall cause to be discharged into the atmosphere from these affected sources any gases which contain D/F in excess of: (1) 0.20 ng per dscm (8.7x10 -11 gr per dscf) (TEQ) corrected to seven percent oxygen; or (2) 0.40 ng per dscm (1.7x10 -10 gr per dscf) (TEQ) corrected to seven percent oxygen, when the average of the performance test run average temperatures at the inlet to the particulate matter control device is 204 [deg]C (400 [deg]F) or less. (e) Greenfield/area sources. No owner or operator of a greenfield kiln or a greenfield in-line kiln/raw mill at a facility that is an areasource subject to the provisions of this subpart shall cause to be discharged into the atmosphere from these affected sources any gases

which: (1) Contain D/F in excess of: (i) 0.20 ng per dscm (8.7x10 -11 gr per dscf) (TEQ) corrected to seven percent oxygen; or (ii) 0.40 ng per dscm (1.7x10 -11 gr per dscf) (TEQ) corrected to seven percent oxygen, when the average of the performance test run average temperatures at the inlet to the particulate matter control device is 204 [deg]C (400 [deg]F) or less. (2) Contain THC, from the main exhaust of the kiln or in-line kiln/ raw mill, in excess of 50 ppmvd as propane, corrected to seven percent

oxygen.

Sec. 63.1344 Operating limits for kilns and in-line kiln/raw mills.

(a) The owner or operator of a kiln subject to a D/F emission limitation under Sec. 63.1343 must operate the kiln such that the temperature of the gas at the inlet to the kiln particulate matter control device (PMCD) and alkali bypass PMCD, if applicable, does not exceed the applicable temperature limit specified in paragraph (b) of this section. The owner or operator of an in-line kiln/raw mill subjectto a D/F emission limitation under Sec. 63.1343 must operate the inline kiln/raw mill, such that: (1) When the raw mill of the in-line kiln/raw mill is operating, the applicable temperature limit for the main in-line kiln/raw mill exhaust, specified in paragraph (b) of this section and established during the performance test when the raw mill was operating is not exceeded. (2) When the raw mill of the in-line kiln/raw mill is not operating, the applicable temperature limit for the main in-line kiln/raw mill exhaust, specified in paragraph (b) of this section and established during the performance test when the raw mill was not operating, is not

exceeded. (3) If the in-line kiln/raw mill is equipped with an alkali bypass, the applicable temperature limit for the alkali bypass specified in paragraph (b) of this section and established during the performance test, with or without the raw mill operating, is not exceeded. (b) The temperature limit for affected sources meeting the limits of paragraph (a) of this section or paragraphs (a)(1) through (a)(3) of this section is determined in accordance with Sec. 63.1349(b)(3)(iv). (c) The owner or operator of an affected source subject to a D/F emission limitation under Sec. 63.1343 that employs carbon injection as an emission control technique must operate the carbon injection system in accordance with paragraphs (c)(1) and (c)(2) of this section. (1) The three-hour rolling average activated carbon injection rate shall be equal to or greater than the activated carbon injection rate determined in accordance with Sec. 63.1349(b)(3)(vi). (2) The owner or operator shall either: (i) Maintain the minimum activated carbon injection carrier gas flow rate, as a three-hour rolling average, based on the manufacturer's specifications. These specifications must be documented in the test plan developed in accordance with Sec. 63.7(c), or (ii) Maintain the minimum activated carbon injection carrier gas pressure drop, as a three-hour rolling average, based on the manufacturer's specifications. These specifications must be documented in the test plan developed in accordance with Sec. 63.7(c). (d) Except as provided in paragraph (e) of this section, the owner or operator of an affected source subject to a D/F emission limitation under Sec. 63.1343 that employs carbon injection as an emission control technique must specify and use the brand and type of activated carbon used during the performance test until a subsequent performance test isconducted, unless the site-specific performance test plan contains documentation of key parameters that affect adsorption and the owner or operator establishes limits based on those parameters, and the limits on these parameters are maintained. (e) The owner or operator of an affected source subject to a D/F emission limitation under Sec. 63.1343 that employs carbon injection as an emission control technique may substitute, at any time, a different brand or type of activated carbon provided that the replacement has equivalent or improved properties compared to the activated carbon specified in the site-specific performance test plan and used in the performance test. The owner or operator must maintain documentation that the substitute activated carbon will provide the same or better level of control as the original activated carbon.

[64 FR 31925, June 14, 1999, as amended at 67 FR 72585, Dec. 6, 2002]

Sec. 63.1345 Standards for clinker coolers.

(a) No owner or operator of a new or existing clinker cooler at a facility which is a major source subject to the provisions of this subpart shall cause to be discharged into the atmosphere from the clinker cooler any gases which: (1) Contain particulate matter in excess of 0.050 kg per Mg (0.10 lb per ton) of feed (dry basis) to the kiln. (2) Exhibit opacity greater than ten percent.

(b) [Reserved]

Sec. 63.1346 Standards for new and reconstructed raw material dryers.

(a) Brownfield/major sources. No owner or operator of a new or reconstructed brownfield raw material dryer at a facility which is a major source subject to this subpart shall cause to be discharged into the atmosphere from the new or reconstructed raw material dryer any gases which exhibit opacity greater than ten percent. (b) Greenfield/area sources. No owner or operator of a greenfield raw material dryer at a facility which is an area source subject to this subpart shall cause to be discharged into the atmosphere from the greenfield raw material dryer any gases which contain THC in excess of 50 ppmvd, reported as propane, corrected to seven percent oxygen. (c) Greenfield/major sources. No owner or operator of a greenfield raw material dryer at a facility which is a major source subject to this subpart shall cause to be discharged into the atmosphere from the greenfield raw material dryer any gases which: (1) Contain THC in excess of 50 ppmvd, reported as propane, corrected to seven percent oxygen. (2) Exhibit opacity greater than ten percent.

Sec. 63.1347 Standards for raw and finish mills.

The owner or operator of each new or existing raw mill or finish mill at a facility which is a major source subject to the provisions of this subpart shall not cause to be discharged from the mill sweep or air separator air pollution control devices of these affected sources any gases which exhibit opacity in excess of ten percent.

Sec. 63.1348 Standards for affected sources other than kilns; in-line kiln/raw mills; clinker coolers; new and reconstructed raw material dryers; and raw and finish mills.

The owner or operator of each new or existing raw material, clinker, or finished product storage bin; conveying system transfer point;bagging system; and bulk loading or unloading system; and each existing raw material dryer, at a facility which is a major source subject to the provisions of this subpart shall not cause to be discharged any gases from these affected sources which exhibit opacity in excess of ten

percent.

Monitoring and Compliance Provisions

Sec. 63.1349 Performance testing requirements.

(a) The owner or operator of an affected source subject to this subpart shall demonstrate initial compliance with the emission limits of Sec. 63.1343 and Sec. Sec. 63.1345 through 63.1348 using the test methods and procedures in paragraph (b) of this section and Sec. 63.7. Performance test results shall be documented in complete test reports that contain the information required by paragraphs (a)(1) through (a)(10) of this section, as well as all other relevant information. The plan to be followed during testing shall be made available to the Administrator prior to testing, if requested. (1) A brief description of the process and the air pollution control

system; (2) Sampling location description(s); (3) A description of sampling and analytical procedures and any modifications to standard procedures;

(4) Test results; (5) Quality assurance procedures and results; (6) Records of operating conditions during the test, preparation of standards, and calibration procedures; (7) Raw data sheets for field sampling and field and laboratory analyses; (8) Documentation of calculations; (9) All data recorded and used to establish parameters for compliance monitoring; and (10) Any other information required by the test method. (b) Performance tests to demonstrate initial compliance with this subpart shall be conducted as specified in paragraphs (b)(1) through (b)(4) of this section. (1) The owner or operator of a kiln subject to limitations on particulate matter emissions shall demonstrate initial compliance by conducting a performance test as specified in paragraphs (b)(1)(i) through (b)(1)(iv) of this section. The owner or operator of an in-line kiln/raw mill subject to limitations on particulate matter emissions shall demonstrate initial compliance by conducting separate performance tests as specified in paragraphs (b)(1)(i) through (b)(1)(iv) of this section while the raw mill of the in-line kiln/raw mill is under normal operating conditions and while the raw mill of the in-line kiln/raw mill is not operating. The owner or operator of a clinker cooler subject to limitations on particulate matter emissions shall demonstrate initial compliance by conducting a performance test as specified in paragraphs (b)(1)(i) through (b)(1)(iii) of this section. The opacity exhibited during the period of the Method 5 of Appendix A to part 60 of this chapter performance tests required by paragraph (b)(1)(i) of this section shall be determined as required in paragraphs (b)(1)(v) through (vi) of this section. (i) Method 5 of appendix A to part 60 of this chapter shall be used to determine PM emissions. Each performance test shall consist of three separate runs under the conditions that exist when the affected source is operating at the representative performance conditions in accordance with Sec. 63.7(e). Each run shall be conducted for at least 1 hour, and the minimum sample volume shall be 0.85 dscm (30 dscf). The average of the three runs shall be used to determine compliance. A determination of the PM collected in the impingers (``back half'') of the Method 5particulate sampling train is not required to demonstrate initial compliance with the PM standards of this subpart. However, this shall not preclude the permitting authority from requiring a determination of the ``back half'' for other purposes. (ii) Suitable methods shall be used to determine the kiln or inline kiln/raw mill feed rate, except for fuels, for each run. (iii) The emission rate, E, of PM shall be computed for each run using equation 1: [GRAPHIC] [TIFF OMITTED] TR14JN99.001

Where:

E = emission rate of particulate matter, kg/Mg of kiln feed.

c s = concentration of PM, kg/dscm.

Q sd = volumetric flow rate of effluent gas, dscm/hr. P = total kiln feed (dry basis), Mg/hr.

(iv) When there is an alkali bypass associated with a kiln or inline kiln/raw mill, the main exhaust and alkali bypass of the kiln or in-line kiln/raw mill shall be tested simultaneously and the combined emission rate of particulate matter from the kiln or in-line kiln/raw mill and alkali bypass shall be computed for each run using equation 2, [GRAPHIC] [TIFF OMITTED] TR14JN99.002

Where:

E

c = the combined emission rate of particulate matter from the kiln or in-line kiln/raw mill and bypass stack, kg/Mg of kiln feed.

c sk = concentration of particulate matter in the kiln or inline kiln/raw mill effluent, kg/dscm.

Q sdk = volumetric flow rate of kiln or in-line kiln/raw mill effluent, dscm/hr.

c sb = concentration of particulate matter in the alkali bypass gas, kg/dscm.

Q sdb = volumetric flow rate of alkali bypass gas, dscm/hr. P=total kiln feed (dry basis), Mg/hr.

(v) Except as provided in paragraph (b)(1)(vi) of this section the opacity exhibited during the period of the Method 5 performance tests required by paragraph (b)(1)(i) of this section shall be determinedthrough the use of a continuous opacity monitor (COM). The maximum sixminute average opacity during the three Method 5 test runs shall be determined during each Method 5 test run, and used to demonstrate initial compliance with the applicable opacity limits of Sec. 63.1343(b)(2), Sec. 63.1343(c)(2), or Sec. 63.1345(a)(2). (vi) Each owner or operator of a kiln, in-line kiln/raw mill, or clinker cooler subject to the provisions of this subpart using a fabric filter with multiple stacks or an electrostatic precipitator with multiple stacks may, in lieu of installing the continuous opacity monitoring system required by paragraph (b)(1)(v) of this section, conduct an opacity test in accordance with Method 9 of appendix A to part 60 of this chapter during each Method 5 performance test required by paragraph (b)(1)(i) of this section. If the control device exhausts through a monovent, or if the use of a COM in accordance with the installation specifications of Performance Specification 1 (PS-1) of appendix B to part 60 of this chapter is not feasible, a test shall be conducted in accordance with Method 9 of appendix A to part 60 of this chapter during each Method 5 performance test required by paragraph (b)(1)(i) of this section. The maximum six-minute average opacity shall be determined during the three Method 5 test runs, and used to demonstrate initial compliance with the applicable opacity limits ofSec. 63.1343(b)(2), Sec. 63.1343(c)(2), or Sec. 63.1345(a)(2). (2) The owner or operator of any affected source subject to limitations on opacity under this subpart that is not subject to paragraph (b)(1) of this section shall demonstrate initial compliance with the affected source opacity limit by conducting a test in accordance with Method 9 of appendix A to part 60 of this chapter. The performance test shall be conducted under the conditions that exist when the affected source is operating at the representative performance conditions in accordance with Sec. 63.7(e). The maximum 6-minute average opacity exhibited during the test period shall be used to determine whether the affected source is in initial compliance with the standard. The duration of the Method 9 performance test shall be 3 hours (30 6-minute averages), except that the duration of the Method 9 performance test may be reduced to 1 hour if the conditions of paragraphs (b)(2)(i) through (ii) of this section apply: (i) There are no individual readings greater than 10 percent opacity; (ii) There are no more than three readings of 10 percent for the first 1-hour period. (3) The owner or operator of an affected source subject to limitations on D/F emissions under this subpart shall demonstrate initial compliance with the D/F emission limit by conducting a performance test using Method 23 of appendix A to part 60 of this chapter. The owner or operator of an in-line kiln/raw mill shall demonstrate initial compliance by conducting separate performance tests while the raw mill of the in-line kiln/raw mill is under normal operating conditions and while the raw mill of the in-line kiln/raw mill is not operating. The owner or operator of a kiln or in-line kiln/raw mill equipped with an alkali bypass shall conduct simultaneous performance tests of the kiln or in-line kiln/raw mill exhaust and the alkali bypass. However, the owner or operator of an in-line kiln/raw mill may conduct a performance test of the alkali bypass exhaust when the raw mill of the in-line kiln/raw mill is operating or not operating. (i) Each performance test shall consist of three separate runs; each

run shall be conducted under the conditions that exist when the affected source is operating at the representative performance conditions in accordance with Sec. 63.7(e). The duration of each run shall be at least 3 hours, and the sample volume for each run shall be at least 2.5 dscm (90 dscf). The concentration shall be determined for each run, and the arithmetic average of the concentrations measured for the three runs shall be calculated and used to determine compliance. (ii) The temperature at the inlet to the kiln or in-line kiln/raw mill PMCD, and where applicable, the temperature at the inlet to the alkali bypass PMCD, must be continuously recorded during the period of the Method 23 test, and the continuous temperature record(s) must be included in the performance test report. (iii) One-minute average temperatures must be calculated for each

minute of each run of the test. (iv) The run average temperature must be calculated for each run, and the average of the run average temperatures must be determined and included in the performance test report and will determine the applicable temperature limit in accordance with Sec. 63.1344(b). (v) If activated carbon injection is used for D/F control, the rate of activated carbon injection to the kiln or in-line kiln/raw mill exhaust, and where applicable, the rate of activated carbon injection to the alkali bypass exhaust, must be continuously recorded during the period of the Method 23 test, and the continuous injection rate record(s) must be included in the performance test report. In addition, the performance test report must include the brand and type of activated carbon used during the performance test and a continuous record of either the carrier gas flow rate or the carrier gas pressure drop forthe duration of the test. Activated carbon injection rate parameters must be determined in accordance with paragraphs (b)(3)(vi) of this

section. (vi) The run average injection rate must be calculated for each run, and the average of the run average injection rates must be determined and included in the performance test report and will determine the applicable injection rate limit in accordance with Sec. 63.1344(c)(1). (4) The owner or operator of an affected source subject to limitations on emissions of THC shall demonstrate initial compliance with the THC limit by operating a continuous emission monitor in accordance with Performance Specification 8A of appendix B to part 60 of this chapter. The duration of the performance test shall be three hours, and the average THC concentration (as calculated from the one-minute averages) during the three hour performance test shall be calculated. The owner or operator of an in-line kiln/raw mill shall demonstrate initial compliance by conducting separate performance tests while the raw mill of the in-line kiln/raw mill is under normal operating conditions and while the raw mill of the in-line kiln/raw mill is not operating. (c) Except as provided in paragraph (e) of this section, performance tests required under paragraphs (b)(1) and (b)(2) of this section shall be repeated every five years, except that the owner or operator of a kiln, in-line kiln/raw mill or clinker cooler is not required to repeat the initial performance test of opacity for the kiln, in-line kiln/raw

mill or clinker cooler. (d) Performance tests required under paragraph (b)(3) of this section shall be repeated every 30 months. (e)(1) If a source plans to undertake a change in operations that may adversely affect compliance with an applicable D/F standard under this subpart, the source must conduct a performance test and establish new temperature limit(s) as specified in paragraph (b)(3) of this

section. (2) If a source plans to undertake a change in operations that may adversely affect compliance with an applicable PM standard under Sec. 63.1343, the source must conduct a performance test as specified in paragraph (b)(1) of this section. (3) In preparation for and while conducting a performance test required in paragraph (e)(1) of this section, a source may operate under the planned operational change conditions for a period not to exceed 360 hours, provided that the conditions in paragraphs (e)(3)(i) through (iv) of this section are met. The source shall submit temperature and other monitoring data that are recorded during the pretest operations. (i) The source must provide the Administrator written notice at least 60 days prior to undertaking an operational change that may adversely affect compliance with an applicable standard under this subpart, or as soon as practicable where 60 days advance notice is not feasible. Notice provided under this paragraph shall include a description of the planned change, the emissions standards that may be affected by the change, and a schedule for completion of the performance test required under paragraph (e)(1) of this section, including when the planned operational change period would begin. (ii) The performance test results must be documented in a test report according to paragraph (a) of this section. (iii) A test plan must be made available to the Administrator prior to testing, if requested. (iv) The performance test must be conducted, and it must be completed within 360 hours after the planned operational change period begins. (f) Table 1 of this section provides a summary of the performance test requirements of this subpart.Table 1 to Sec. 63.1349--Summary of Performance Test Requirements

------------------------------------------------------------------------ Affected source and pollutant Performance test

------------------------------------------------------------------------ New and existing kiln and in-line kiln/ EPA Method 5 a.

raw mil b c PM. New and existing kiln and in-line kiln/ COM if feasibled e or EPA raw mill b c Opacity. Method 9 visual opacity readings. New and existing kiln and in-line kiln/ EPA Method 23 h. raw mill b c f g D/F. New greenfield kiln and in-line kiln/ THC CEM (EPA PS-8A) i.

raw mill c THC. New and existing clinker cooler PM..... EPA Method 5 a. New and existing clinker cooler opacity COM d j or EPA Method 9 visual opacity readings. New and existing raw and finish mill EPA Method 9 a j. opacity.

New and existing raw material dryer and EPA Method 9 a j. materials handling processes (raw material storage, clinker storage, finished product storage, conveyor transfer points, bagging, and bulk loading and unloading systems) opacity. New greenfield raw material dryer THC.. THC CEM (EPA PS-8A) i.

------------------------------------------------------------------------ a Required initially and every 5 years thereafter. b Includes main exhaust and alkali bypass. c In-line kiln/raw mill to be tested with and without raw mill in operation. d Must meet COM performance specification criteria. If the fabric filter or electrostatic precipitator has multiple stacks, daily EPA Method 9 visual opacity readings may be taken instead of using a COM. e Opacity limit is 20 percent. f Alkali bypass is tested with the raw mill operating or not operating. g Temperature and (if applicable) activated carbon injection parameters determined separately with and without the raw mill operating. h Required initially and every 30 months thereafter. i EPA Performance Specification (PS)-8A of appendix B to part 60 of this chapter. j Opacity limit is 10 percent.

[64 FR 31925, June 14, 1999, as amended at 67 FR 16619, Apr. 5, 2002; 67 FR 72585, Dec. 6, 2002]

Sec. 63.1350 Monitoring requirements.

(a) The owner or operator of each portland cement plant shall prepare for each affected source subject to the provisions of this subpart, a written operations and maintenance plan. The plan shall be submitted to the Administrator for review and approval as part of the application for a part 70 permit and shall include the following

information: (1) Procedures for proper operation and maintenance of the affected source and air pollution control devices in order to meet the emission limits and operating limits of Sec. Sec. 63.1343 through 63.1348; (2) Corrective actions to be taken when required by paragraph (e) of this section;(3) Procedures to be used during an inspection of the components of the combustion system of each kiln and each in-line kiln raw mill located at the facility at least once per year; and (4) Procedures to be used to periodically monitor affected sources subject to opacity standards under Sec. Sec. 63.1346 and 63.1348. Such procedures must include the provisions of paragraphs (a)(4)(i) through (a)(4)(iv) of this section. (i) The owner or operator must conduct a monthly 1-minute visible

emissions test of each affected source in accordance with Method 22 of Appendix A to part 60 of this chapter. The test must be conducted while the affected source is in operation. (ii) If no visible emissions are observed in six consecutive monthly tests for any affected source, the owner or operator may decrease the frequency of testing from monthly to semi-annually for that affected source. If visible emissions are observed during any semi-annual test, the owner or operator must resume testing of that affected source on a monthly basis and maintain that schedule until no visible emissions are observed in six consecutive monthly tests. (iii) If no visible emissions are observed during the semi-annual test for any affected source, the owner or operator may decrease the frequency of testing from semi-annually to annually for that affected source. If visible emissions are observed during any annual test, the owner or operator must resume testing of that affected source on a monthly basis and maintain that schedule until no visible emissions are observed in six consecutive monthly tests. (iv) If visible emissions are observed during any Method 22 test, the owner or operator must conduct a 6-minute test of opacity in accordance with Method 9 of appendix A to part 60 of this chapter. The Method 9 test must begin within one hour of any observation of visible

emissions. (v) The requirement to conduct Method 22 visible emissions monitoring under this paragraph shall not apply to any totally enclosed conveying system transfer point, regardless of the location of the transfer point. ``Totally enclosed conveying system transfer point'' shall mean a conveying system transfer point that is enclosed on all sides, top, and bottom. The enclosures for these transfer points shall be operated and maintained as total enclosures on a continuing basis in accordance with the facility operations and maintenance plan. (vi) If any partially enclosed or unenclosed conveying system transfer point is located in a building, the owner or operator of the portland cement plant shall have the option to conduct a Method 22 visible emissions monitoring test according to the requirements of paragraphs (a)(4)(i) through (iv) of this section for each such conveying system transfer point located within the building, or for the building itself, according to paragraph (a)(4)(vii) of this section. (vii) If visible emissions from a building are monitored, the requirements of paragraphs (a)(4)(i) through (iv) of this section apply to the monitoring of the building, and you must also test visible emissions from each side, roof and vent of the building for at least 1 minute. The test must be conducted under normal operating conditions. (b) Failure to comply with any provision of the operations and maintenance plan developed in accordance with paragraph (a) of this

section shall be a violation of the standard. (c) The owner or operator of a kiln or in-line kiln/raw mill shall monitor opacity at each point where emissions are vented from these affected sources including alkali bypasses in accordance with paragraphs (c)(1) through (c)(3) of this section. (1) Except as provided in paragraph (c)(2) of this section, the owner or operator shall install, calibrate, maintain, and continuously operate a continuous opacity monitor (COM) located at the outlet of the PM control device to continuously monitor the opacity. The COM shall beinstalled, maintained, calibrated, and operated as required by subpart A, general provisions of this part, and according to PS-1 of appendix B to part 60 of this chapter. (2) The owner or operator of a kiln or in-line kiln/raw mill subject to the provisions of this subpart using a fabric filter with multiple stacks or an electrostatic precipitator with multiple stacks may, in lieu of installing the continuous opacity monitoring system required by paragraph (c)(1) of this section, monitor opacity in accordance with paragraphs (c)(2)(i) through (ii) of this section. If the control device exhausts through a monovent, or if the use of a COM in accordance with the installation specifications of PS-1 of appendix B to part 60 of this chapter is not feasible, the owner or operator must monitor opacity in accordance with paragraphs (c)(2)(i) through (ii) of this section. (i) Perform daily visual opacity observations of each stack in accordance with the procedures of Method 9 of appendix A to part 60 of this chapter. The Method 9 test shall be conducted while the affected source is operating at the representative performance conditions. The duration of the Method 9 test shall be at least 30 minutes each day. (ii) Use the Method 9 procedures to monitor and record the average opacity for each six-minute period during the test. (3) To remain in compliance, the opacity must be maintained such that the 6-minute average opacity for any 6-minute block period does not exceed 20 percent. If the average opacity for any 6-minute block period exceeds 20 percent, this shall constitute a violation of the standard. (d) The owner or operator of a clinker cooler shall monitor opacity at each point where emissions are vented from the clinker cooler in accordance with paragraphs (d)(1) through (d)(3) of this section. (1) Except as provided in paragraph (d)(2) of this section, the owner or operator shall install, calibrate, maintain, and continuously operate a COM located at the outlet of the clinker cooler PM control device to continuously monitor the opacity. The COM shall be installed, maintained, calibrated, and operated as required by subpart A, general provisions of this part, and according to PS-1 of appendix B to part 60 of this chapter. (2) The owner or operator of a clinker cooler subject to the provisions of this subpart using a fabric filter with multiple stacks or an electrostatic precipitator with multiple stacks may, in lieu of installing the continuous opacity monitoring system required by paragraph (d)(1) of this section, monitor opacity in accordance with paragraphs (d)(2)(i) through (ii) of this section. If the control device exhausts through a monovent, or if the use of a COM in accordance with the installation specifications of PS-1 of appendix B to part 60 of this chapter is not feasible, the owner or operator must monitor opacity in accordance with paragraphs (d)(2)(i) through (ii) of this section. (i) Perform daily visual opacity observations of each stack in accordance with the procedures of Method 9 of appendix A to part 60 of this chapter. The Method 9 test shall be conducted while the affected source is operating at the representative performance conditions. The duration of the Method 9 test shall be at least 30 minutes each day. (ii) Use the Method 9 procedures to monitor and record the average opacity for each six-minute period during the test. (3) To remain in compliance, the opacity must be maintained such that the 6-minute average opacity for any 6-minute block period does not exceed 10 percent. If the average opacity for any 6-minute block period exceeds 10 percent, this shall constitute a violation of the standard. (e) The owner or operator of a raw mill or finish mill shall monitor opacity by conducting daily visual emissions observations of the mill sweep and air separator PMCD of these affected sources in accordance with the procedures of Method 22 of appendix A to part 60 of this chapter. The Method 22 test shall be conducted while the affected source is operating at the representative performance conditions. The durationof the Method 22 test shall be 6 minutes. If visible emissions are observed during any Method 22 visible emissions test, the owner or

operator must: (1) Initiate, within one-hour, the corrective actions specified in the site specific operating and maintenance plan developed in accordance with paragraphs (a)(1) and (a)(2) of this section; and (2) Within 24 hours of the end of the Method 22 test in which visible emissions were observed, conduct a followup Method 22 test of each stack from which visible emissions were observed during the previous Method 22 test. If visible emissions are observed during the followup Method 22 test from any stack from which visible emissions were observed during the previous Method 22 test, conduct a visual opacity test of each stack from which emissions were observed during the follow up Method 22 test in accordance with Method 9 of appendix A to part 60 of this chapter. The duration of the Method 9 test shall be 30 minutes. (f) The owner or operator of an affected source subject to a limitation on D/F emissions shall monitor D/F emissions in accordance with paragraphs (f)(1) through (f)(6) of this section. (1) The owner or operator shall install, calibrate, maintain, and continuously operate a continuous monitor to record the temperature of the exhaust gases from the kiln, in-line kiln/raw mill and alkalibypass, if applicable, at the inlet to, or upstream of, the kiln, inline kiln/raw mill and/or alkali bypass PM control devices. (i) The recorder response range must include zero and 1.5 times either of the average temperatures established according to the requirements in Sec. 63.1349(b)(3)(iv). (ii) The reference method must be a National Institute of Standards and Technology calibrated reference thermocouple-potentiometer system or alternate reference, subject to approval by the Administrator. (2) The owner or operator shall monitor and continuously record the temperature of the exhaust gases from the kiln, in-line kiln/raw mill and alkali bypass, if applicable, at the inlet to the kiln, in-line kiln/raw mill and/or alkali bypass PMCD. (3) The three-hour rolling average temperature shall be calculated as the average of 180 successive one-minute average temperatures. (4) Periods of time when one-minute averages are not available shall be ignored when calculating three-hour rolling averages. When one-minute averages become available, the first one-minute average is added to the previous 179 values to calculate the three-hour rolling average. (5) When the operating status of the raw mill of the in-line kiln/ raw mill is changed from off to on, or from on to off the calculation of the three-hour rolling average temperature must begin anew, without considering previous recordings. (6) The calibration of all thermocouples and other temperature sensors shall be verified at least once every three months. (g) The owner or operator of an affected source subject to a limitation on D/F emissions that employs carbon injection as an emission control technique shall comply with the monitoring requirements of paragraphs (f)(1) through (f)(6) and (g)(1) through (g)(6) of this section to demonstrate continuous compliance with the D/F emission

standard. (1) Install, operate, calibrate and maintain a continuous monitor to record the rate of activated carbon injection. The accuracy of the rate

measurement device must be ± ≤ 1 percent of the rate being measured. (2) Verify the calibration of the device at least once every three

months. (3) The three-hour rolling average activated carbon injection rate shall be calculated as the average of 180 successive one-minute average activated carbon injection rates. (4) Periods of time when one-minute averages are not available shall be ignored when calculating three-hour rolling averages. When one-minuteaverages become available, the first one-minute average is added to the previous 179 values to calculate the three-hour rolling average. (5) When the operating status of the raw mill of the in-line kiln/ raw mill is changed from off to on, or from on to off the calculation of the three-hour rolling average activated carbon injection rate must begin anew, without considering previous recordings. (6) The owner or operator must install, operate, calibrate and maintain a continuous monitor to record the activated carbon injection system carrier gas parameter (either the carrier gas flow rate or the carrier gas pressure drop) established during the D/F performance test in accordance with paragraphs (g)(6)(i) through (g)(6)(iii) of this

section. (i) The owner or operator shall install, calibrate, operate and maintain a device to continuously monitor and record the parameter

value. (ii) The owner or operator must calculate and record three-hour rolling averages of the parameter value. (iii) Periods of time when one-minute averages are not availableshall be ignored when calculating three-hour rolling averages. When oneminute averages become available, the first one-minute average shall be added to the previous 179 values to calculate the three-hour rolling

average. (h) The owner or operator of an affected source subject to a limitation on THC emissions under this subpart shall comply with the monitoring requirements of paragraphs (h)(1) through (h)(3) of this section to demonstrate continuous compliance with the THC emission

standard: (1) The owner or operator shall install, operate and maintain a THC continuous emission monitoring system in accordance with Performance Specification 8A, of appendix B to part 60 of this chapter and comply with all of the requirements for continuous monitoring systems found in the general provisions, subpart A of this part. (2) The owner or operator is not required to calculate hourly rolling averages in accordance with section 4.9 of Performance Specification 8A. (3) Any thirty-day block average THC concentration in any gas discharged from a greenfield raw material dryer, the main exhaust of a greenfield kiln, or the main exhaust of a greenfield in-line kiln/raw mill, exceeding 50 ppmvd, reported as propane, corrected to seven percent oxygen, is a violation of the standard. (i) The owner or operator of any kiln or in-line kiln/raw mill subject to a D/F emission limit under this subpart shall conduct an inspection of the components of the combustion system of each kiln or in-line kiln raw mill at least once per year. (j) The owner or operator of an affected source subject to a limitation on opacity under Sec. 63.1346 or Sec. 63.1348 shall monitor opacity in accordance with the operation and maintenance plan developed in accordance with paragraph (a) of this section. (k) The owner or operator of an affected source subject to a particulate matter standard under Sec. 63.1343 shall install, calibrate, maintain, and operate a particulate matter continuous emission monitoring system (PM CEMS) to measure the particulate matter discharged to the atmosphere. All requirements relating to installation, calibration, maintenance, operation or performance of the PM CEMS and implementation of the PM CEMS requirement are deferred pending further rulemaking. (l) An owner or operator may submit an application to the Administrator for approval of alternate monitoring requirements to demonstrate compliance with the emission standards of this subpart, except for emission standards for THC, subject to the provisions of paragraphs (l)(1) through (l)(6) of this section.(1) The Administrator will not approve averaging periods other than those specified in this section, unless the owner or operator documents, using data or information, that the longer averaging period will ensure that emissions do not exceed levels achieved during the performance test over any increment of time equivalent to the time required to conduct three runs of the performance test. (2) If the application to use an alternate monitoring requirement is approved, the owner or operator must continue to use the original monitoring requirement until approval is received to use another monitoring requirement. (3) The owner or operator shall submit the application for approval of alternate monitoring requirements no later than the notification of performance test. The application must contain the information specified in paragraphs (l)(3)(i) through (l)(3)(iii) of this section: (i) Data or information justifying the request, such as the technical or economic infeasibility, or the impracticality of using the required approach; (ii) A description of the proposed alternative monitoring requirement, including the operating parameter to be monitored, the monitoring approach and technique, the averaging period for the limit, and how the limit is to be calculated; and (iii) Data or information documenting that the alternative monitoring requirement would provide equivalent or better assurance of compliance with the relevant emission standard. (4) The Administrator will notify the owner or operator of the approval or denial of the application within 90 calendar days after receipt of the original request, or within 60 calendar days of the receipt of any supplementary information, whichever is later. The Administrator will not approve an alternate monitoring application unless it would provide equivalent or better assurance of compliance with the relevant emission standard. Before disapproving any alternate monitoring application, the Administrator will provide: (i) Notice of the information and findings upon which the intended disapproval is based; and (ii) Notice of opportunity for the owner or operator to present additional supporting information before final action is taken on the application. This notice will specify how much additional time is allowed for the owner or operator to provide additional supporting

information. (5) The owner or operator is responsible for submitting any supporting information in a timely manner to enable the Administrator to consider the application prior to the performance test. Neither submittal of an application, nor the Administrator's failure to approve or disapprove the application relieves the owner or operator of the responsibility to comply with any provision of this subpart. (6) The Administrator may decide at any time, on a case-by-case basis that additional or alternative operating limits, or alternative approaches to establishing operating limits, are necessary to demonstrate compliance with the emission standards of this subpart. (m) The requirements under paragraph (e) of this section to conduct daily Method 22 testing shall not apply to any specific raw mill or finish mill equipped with a continuous opacity monitor COM or bag leak detectionsystem (BLDS). If the owner or operator chooses to install a COM in lieu of conducting the daily visual emissions testing required under paragraph (e) of this section, then the COM must be installed at the outlet of the PM control device of the raw mill or finish mill, and the COM must be installed, maintained, calibrated, and operated as requiredby the general provisions in subpart A of this part and according to PS1 of appendix B to part 60 of this chapter. To remain in compliance, the opacity must be maintained such that the 6-minute average opacity for any 6-minute block period does not exceed 10 percent. If the averageopacity for any 6-minute block period exceeds 10 percent, this shall constitute a violation of the standard. If the owner or operator chooses to install a BLDS in lieu of conducting the daily visual emissions testing required under paragraph (e) of this section, the requirements in paragraphs (m)(1) through (9) of this section apply to each BLDS: (1) The BLDS must be certified by the manufacturer to be capable of detecting PM emissions at concentrations of 10 milligrams per actual cubic meter (0.0044 grains per actual cubic foot) or less. ``Certify''

shall mean that the instrument manufacturer has tested the instrument on gas streams having a range of particle size distributions and confirmed by means of valid filterable PM tests that the minimum detectable concentration limit is at or below 10 milligrams per actual cubic meter (0.0044 grains per actual cubic foot) or less. (2) The sensor on the BLDS must provide output of relative PM

emissions. (3) The BLDS must have an alarm that will activate automatically when it detects a significant increase in relative PM emissions greater than a preset level. (4) The presence of an alarm condition should be clearly apparent to facility operating personnel. (5) For a positive-pressure fabric filter, each compartment or cell must have a bag leak detector. For a negative-pressure or induced-air fabric filter, the bag leak detector must be installed downstream of the fabric filter. If multiple bag leak detectors are required (for either type of fabric filter), detectors may share the system instrumentation

and alarm. (6) All BLDS must be installed, operated, adjusted, and maintained so that they are based on the manufacturer's written specifications and recommendations. The EPA recommends that where appropriate, the standard operating procedures manual for each bag leak detection system includeconcepts from EPA's ``Fabric Filter Bag Leak Detection Guidance'' (EPA454/R-98-015, September 1997). (7) The baseline output of the system must be established as

follows: (i) Adjust the range and the averaging period of the device; and (ii) Establish the alarm set points and the alarm delay time. (8) After initial adjustment, the range, averaging period, alarm set points, or alarm delay time may not be adjusted except as specified in the operations and maintenance plan required by paragraph (a) of this section. In no event may the range be increased by more than 100 percent or decreased by more than 50 percent over a 1 calendar year period unless a responsible official as defined in Sec. 63.2 certifies in writing to the Administrator that the fabric filter has been inspected and found to be in good operating condition. (9) The owner or operator must maintain and operate the fabric filter such that the bag leak detector alarm is not activated and alarm condition does not exist for more than 5 percent of the total operating time in a 6-month block period. Each time the alarm activates, alarm time will be counted as the actual amount of time taken by the owner or operator to initiate corrective actions. If inspection of the fabric filter demonstrates that no corrective actions are necessary, no alarm time will be counted. The owner or operator must continuously record the output from the BLDS during periods of normal operation. Normal operation does not include periods when the BLDS is being maintained or during startup, shutdown or malfunction. (n) A summary of the monitoring requirements of this subpart is given in Table 1 to this section.Table 1 to Sec. 63.1350--Monitoring Requirements

------------------------------------------------------------------------ Affected source/pollutant or Monitor type/ Monitoring opacity operation/process requirements

------------------------------------------------------------------------ All affected sources........ Operations and Prepare written plan maintenance plan. for all affected

sources and control

devices. All kilns and in-line kiln Continuous opacity Install, calibrate, raw mills at major sources monitor, if maintain and (including alkali bypass)/ applicable. operate in opacity. accordance with general provisions

and with PS-1. Method 9 opacity Daily test of at test, if applicable. least 30-minutes,

while kiln is at representative performance

conditions.

Kilns and in-line raw mills Particulate matter Deferred at major sources (including continuous alkali bypass)/particulate monitoring systems.

matter. Kilns and in-line kiln raw Combustion system Conduct annual mills at major and area inspection. inspection of sources (including alkali components of bypass)/D/F. combustion system. Continuous Install, operate, temperature calibrate and monitoring at PMCD maintain continuous inlet. temperature monitoring and recording system;

calculate three- hour rolling averages; verify

temperature sensor

calibration at least quarterly. Activated carbon Install, operate, injection rate calibrate and monitor, if maintain continuous applicable. activated carbon injection rate monitor; calculate three-hour rolling averages; verify

calibration at least quarterly; install, operate,

calibrate and

maintain carrier gas flow rate

monitor or carrier gas pressure drop monitor; calculate three-hour rolling averages; document

carbonspecifications. New greenfield kilns and Total hydrocarbon Install, operate,

inline kiln raw mills at continuous emission and maintain THC major and area sources/THC. monitor. CEM in accordance

with PS-8A; calculate 30-day block average THC

concentration. Clinker coolers at major Continuous opacity Install, calibrate, sources/opacity. monitor, if maintain and applicable. operate in

accordance with general provisions

and with PS-1. Method 9 opacity Daily test of at test, if applicable. least applicable 30- minutes, while kiln

is at representative performance

conditions. Raw mills and finish mills Method 22 visible Conduct daily 6- at major sources/opacity. emissions test. minute Method 22 (This requirement visible emissions does not apply to a test while mill is raw mill or finish operating at mill equipped with representative a continuous performance opacity monitor or conditions; if bag leak detection visible emissions system.). are observed,

initiate corrective

action within 1

hour and conduct follow up Method 22

test. If visible

emissions are observed, conduct

30-minute Method 9

test. Continuous opacity Install, operate, monitor, if and maintain in applicable. accordance with general provisions

and with PS-1. A six-minute average greater than 10% opacity is a

violation. Bag leak detection Install, operate, system, if and maintain in applicable. accordance with Sec. 63.1350(m). Operate and

maintain such that

alarm is not

activated and alarm

condition does not

exist for more than

5% of the total operating time in a6-month period. If alarm sounds,

initiate corrective

action. New greenfield raw material Total hydrocarbon Install, operate, dryers at major and area continuous emission and maintain THC sources/THC. monitor. CEM in accordance

with PS-8A; calculate 30-day block average THC

concentration.

[[Page 372]]

Raw material dryers; raw Method 22 visible As specified in material, clinker, finished emissions test. operation and product storage bins; maintenance plan. conveying system transfer points, excluding totally enclosed conveying system transfer points; bagging systems; and bulk loading and unloading systems at major sources/opacity.

------------------------------------------------------------------------

[64 FR 31925, June 14, 1999, as amended at 64 FR 53070, Sept. 30, 1999; 67 FR 16620, Apr. 5, 2002; 67 FR 44769, July 5, 2002; 67 FR 72585, Dec. 6, 2002]

Sec. 63.1351 Compliance dates.

(a) The compliance date for an owner or operator of an existing affected source subject to the provisions of this subpart is June 14,

2002. (b) The compliance date for an owner or operator of an affected source subject to the provisions of this subpart that commences new construction or reconstruction after March 24, 1998 is June 14, 1999 or upon startup of operations, whichever is later.

[67 FR 16622, Apr. 5, 2002]

Sec. 63.1352 Additional test methods.

(a) Owners or operators conducting tests to determine the rates of emission of hydrogen chloride (HCl) from kilns, in-line kiln/raw mills and associated bypass stacks at portland cement manufacturing facilities, for use in applicability determinations under Sec. 63.1340 are permitted to use Method 320 or Method 321 of appendix A of this

part. (b) Owners or operators conducting tests to determine the rates of emission of hydrogen chloride (HCl) from kilns, in-line kiln/raw mills and associated bypass stacks at portland cement manufacturing facilities, for use in applicability determinations under Sec. 63.1340 are permitted to use Methods 26 or 26A of appendix A to part 60 of this chapter, except that the results of these tests shall not be used to

establish status as an area source. (c) Owners or operators conducting tests to determine the rates of emission of specific organic HAP from raw material dryers, kilns and in-line kiln/raw mills at portland cement manufacturing facilities, for use in applicability determinations under Sec. 63.1340 of this subpart are permitted to use Method 320 of appendix A to this part, or Method 18 of appendix A to part 60 of this chapter.

Notification, Reporting and Recordkeeping

Sec. 63.1353 Notification requirements.

(a) The notification provisions of 40 CFR part 63, subpart A that apply and those that do not apply to owners and operators of affected sources subject to this subpart are listed in Table 1 of this subpart. If any State requires a notice that contains all of the information required in a notification listed in this section, the owner or operator may send the Administrator a copy of the notice sent to the State to satisfy the requirements of this section for that notification. (b) Each owner or operator subject to the requirements of this subpart shall comply with the notification requirements in Sec. 63.9 as

follows: (1) Initial notifications as required by Sec. 63.9(b) through (d). For the purposes of this subpart, a Title V or 40 CFR part 70 permit application may be used in lieu of the initial notification required under Sec. 63.9(b), provided the same information is contained in the permit application as required by Sec. 63.9(b), and the State to which the permit application has been submitted has an approved operating permit program under part 70 of this chapter and has received delegation of authority from the EPA. Permit applications shall be submitted by the same due dates as those specified for the initial notification. (2) Notification of performance tests, as required by Sec. Sec. 63.7 and 63.9(e). (3) Notification of opacity and visible emission observations required by Sec. 63.1349 in accordance with Sec. Sec. 63.6(h)(5) and 63.9(f). (4) Notification, as required by Sec. 63.9(g), of the date that the continuous emission monitor performance evaluation required by Sec. 63.8(e) is scheduled to begin. (5) Notification of compliance status, as required by Sec. 63.9(h).

Sec. 63.1354 Reporting requirements.

(a) The reporting provisions of subpart A of this part that apply and those that do not apply to owners or operators of affected sources subject to this subpart are listed in Table 1 of this subpart. If any State requires a report that contains all of the information required in a report listed in this section, the owner or operator may send the Administrator a copy of the report sent to the State to satisfy the requirements of this section for that report. (b) The owner or operator of an affected source shall comply with the reporting requirements specified in Sec. 63.10 of the general provisions of this part 63, subpart A as follows: (1) As required by Sec. 63.10(d)(2), the owner or operator shall report the results of performance tests as part of the notification of compliance status. (2) As required by Sec. 63.10(d)(3), the owner or operator of an affected source shall report the opacity results from tests required by

Sec. 63.1349. (3) As required by Sec. 63.10(d)(4), the owner or operator of an affected source who is required to submit progress reports as a condition of receiving an extension of compliance under Sec. 63.6(i) shall submit such reports by the dates specified in the written extension of compliance.(4) As required by Sec. 63.10(d)(5), if actions taken by an owner or operator during a startup, shutdown, or malfunction of an affected source (including actions taken to correct a malfunction) are consistent with the procedures specified in the source's startup, shutdown, and malfunction plan specified in Sec. 63.6(e)(3), the owner or operator shall state such information in a semiannual report. Reports shall only be required if a startup, shutdown, or malfunction occurred during the reporting period. The startup, shutdown, and malfunction report may be submitted simultaneously with the excess emissions and continuous monitoring system performance reports; and (5) Any time an action taken by an owner or operator during a startup, shutdown, or malfunction (including actions taken to correct a malfunction) is not consistent with the procedures in the startup, shutdown, and malfunction plan, the owner or operator shall make an immediate report of the actions taken for that event within 2 working days, by telephone call or facsimile (FAX) transmission. The immediate report shall be followed by a letter, certified by the owner or operator or other responsible official, explaining the circumstances of the event, the reasons for not following the startup, shutdown, and malfunction plan, and whether any excess emissions and/or parameter monitoring exceedances are believed to have occurred. (6) As required by Sec. 63.10(e)(2), the owner or operator shall submit a written report of the results of the performance evaluation for the continuous monitoring system required by Sec. 63.8(e). The owner or operator shall submit the report simultaneously with the results of the performance test. (7) As required by Sec. 63.10(e)(2), the owner or operator of an affected source using a continuous opacity monitoring system to determine opacity compliance during any performance test required under Sec. 63.7 and described in Sec. 63.6(d)(6) shall report the results of the continuous opacity monitoring system performance evaluation conducted under Sec. 63.8(e). (8) As required by Sec. 63.10(e)(3), the owner or operator of an affected source equipped with a continuous emission monitor shall submit an excess emissions and continuous monitoring system performance report for any event when the continuous monitoring system data indicate the source is not in compliance with the applicable emission limitation or operating parameter limit. (9) The owner or operator shall submit a summary report semiannually which contains the information specified in Sec. 63.10(e)(3)(vi). In addition, the summary report shall include:

(i) All exceedences of maximum control device inlet gas temperature limits specified in Sec. 63.1344(a) and (b); (ii) All failures to calibrate thermocouples and other temperature sensors as required under Sec. 63.1350(f)(7) of this subpart; and (iii) All failures to maintain the activated carbon injection rate, and the activated carbon injection carrier gas flow rate or pressure drop, as applicable, as required under Sec. 63.1344(c). (iv) The results of any combustion system component inspections conducted within the reporting period as required under Sec. 63.1350(i). (v) All failures to comply with any provision of the operation and maintenance plan developed in accordance with Sec. 63.1350(a). (10) If the total continuous monitoring system downtime for any CEM or any continuous monitoring system (CMS) for the reporting period is ten percent or greater of the total operating time for the reporting period, the owner or operator shall submit an excess emissions and continuous monitoring system performance report along with the summary

report.Sec. 63.1355 Recordkeeping requirements.

(a) The owner or operator shall maintain files of all information (including all reports and notifications) required by this section recorded in a form suitable and readily available for inspection and review as required by Sec. 63.10(b)(1). The files shall be retained for at least five years following the date of each occurrence, measurement, maintenance, corrective action, report, or record. At a minimum, the most recent two years of data shall be retained on site. The remaining three years of data may be retained off site. The files may be maintained on microfilm, on a computer, on floppy disks, on magnetic tape, or on microfiche. (b) The owner or operator shall maintain records for each affected source as required by Sec. 63.10(b)(2) and (b)(3) of this part; and (1) All documentation supporting initial notifications and notifications of compliance status under Sec. 63.9; (2) All records of applicability determination, including supporting analyses; and (3) If the owner or operator has been granted a waiver under Sec. 63.8(f)(6), any information demonstrating whether a source is meeting the requirements for a waiver of recordkeeping or reporting requirements. (c) In addition to the recordkeeping requirements in paragraph (b) of this section, the owner or operator of an affected source equipped with a continuous monitoring system shall maintain all records required by Sec. 63.10(c).

Other

Sec. 63.1356 Exemption from new source performance standards.

(a) Except as provided in paragraphs (a)(1) and (2) of this section, any affected source subject to the provisions of this subpart is exempt from any otherwise applicable new source performance standard contained in subpart F or subpart OOO of part 60 of this chapter. (b) The requirements of subpart Y of part 60 of this chapter, ``Standards of Performance for Coal Preparation Plants,'' do not apply to conveying system transfer points used to convey coal from the mill to the kiln that are associated with coal preparation at a portland cement plant that is a major source under this subpart.

[64 FR 31925, June 14, 1999, as amended at 67 FR 16622, Apr. 5, 2002]

Sec. 63.1357 Temporary, conditioned exemption from particulate matter and opacity standards.

(a) Subject to the limitations of paragraphs (b) through (f) of this section, an owner or operator conducting PM CEMS correlation tests (that is, correlation with manual stack methods) is exempt from: (1) Any particulate matter and opacity standards of part 60 or part 63 of this chapter that are applicable to cement kilns and in-line kiln/

raw mills. (2) Any permit or other emissions or operating parameter or other limitation on workplace practices that are applicable to cement kilns and in-line kiln raw mills to ensure compliance with any particulate matter and opacity standards of this part or part 60 of this chapter. (b) The owner or operator must develop a PM CEMS correlation test plan. The plan must be submitted to the Administrator for approval at least 90 days before the correlation test is scheduled to be conducted. The plan must include: (1) The number of test conditions and the number of runs for eachtest condition; (2) The target particulate matter emission level for each test condition; (3) How the operation of the affected source will be modified to attain the desired particulate matter emission rate; and (4) The anticipated normal particulate matter emission level. (c) The Administrator will review and approve or disapprove the correlation test plan in accordance with Sec. 63.7(c)(3)(i) and (iii). If the Administrator fails to approve or disapprove the correlation test plan within the time period specified in Sec. 63.7(c)(3)(iii), the plan shall be considered approved, unless the Administrator has requested

additional information. (d) The stack sampling team must be on-site and prepared to perform correlation testing no later than 24 hours after operations are modified to attain the desired particulate matter emissions concentrations, unless the correlation test plan documents that a longer period is appropriate. (e) The PM and opacity standards and associated operating limits and conditions will not be waived for more than 96 hours, in the aggregate, for the purposes of conducting tests to correlate PM CEMS with manual method test results, including all runs and conditions, except as described in this paragraph. Where additional time is required to correlate a PM CEMS device, a source may petition the Administrator for an extension of the 96-hour aggregate waiver of compliance with the PM and opacity standards. An extension of the 96-hour aggregate waiver is

renewable at the discretion of the Administrator. (f) The owner or operator must return the affected source to operating conditions indicative of compliance with the applicable particulate matter and opacity standards as soon as possible after correlation testing is completed.

[64 FR 31925, June 14, 1999, as amended at 67 FR 16622, Apr. 5, 2002]

Sec. 63.1358 Implementation and enforcement.

(a) This subpart can be implemented and enforced by the U.S. EPA, or a delegated authority such as the applicable State, local, or Tribal agency. If the U.S. EPA Administrator has delegated authority to a State, local, or Tribal agency, then that agency, in addition to the U.S. EPA, has the authority to implement and enforce this subpart. Contact the applicable U.S. EPA Regional Office to find out if this subpart is delegated to a State, local, or Tribal agency. (b) In delegating implementation and enforcement authority of this subpart to a State, local, or Tribal agency under subpart E of this part, the authorities contained in paragraph (c) of this section are retained by the Administrator of U.S. EPA and cannot be transferred to the State, local, or Tribal agency. (c) The authorities that cannot be delegated to State, local, or Tribal agencies are as specified in paragraphs (c)(1) through (4) of

this section. (1) Approval of alternatives to the requirements in Sec. Sec. 63.1340, 63.1342 through 63.1348, and 63.1351. (2) Approval of major alternatives to test methods under Sec. 63.7(e)(2)(ii) and (f), as defined in Sec. 63.90, and as required in this subpart. (3) Approval of major alternatives to monitoring under Sec. 63.8(f), as defined in Sec. 63.90, and as required in this subpart. (4) Approval of major alternatives to recordkeeping and reporting under Sec. 63.10(f), as defined in Sec. 63.90, and as required in this subpart.[68 FR 37359, June 23, 2003]

Sec. 63.1359 [Reserved]Table 1 to Subpart LLL of Part 63--Applicability of General Provisions----------------------------------------------------------------------------------------------------------------Citation Requirement Applies to Subpart LLL Explaination----------------------------------------------------------------------------------------------------------------63.1(a)(1)-(4)....................... Applicability.......... Yes....................63.1(a)(5)........................... ....................... No..................... [Reserved]63.1(a)(6)-(8)....................... Applicability.......... Yes....................63.1(a)(9)........................... ....................... No..................... [Reserved]63.1(a)(10)-(14)..................... Applicability.......... Yes....................63.1(b)(1)........................... Initial Applicability No..................... Sec. 63.1340Determination. specifiesapplicability.63.1(b)(2)-(3)....................... Initial Applicability Yes....................Determination.63.1(c)(1)........................... Applicability After Yes....................Standard Established.63.1(c)(2)........................... Permit Requirements.... Yes.................... Area sources mustobtain Title Vpermits.63.1(c)(3)........................... ....................... No..................... [Reserved]63.1(c)(4)-(5)....................... Extensions, Yes....................Notifications.63.1(d).............................. ....................... No..................... [Reserved]63.1(e).............................. Applicability of Permit Yes....................Program.63.2................................. Definitions............ Yes.................... Additional definitionsin Sec. 63.1341.63.3(a)-(c).......................... Units and Abbreviations Yes....................63.4(a)(1)-(3)....................... Prohibited Activities.. Yes....................63.4(a)(4)........................... ....................... No..................... [Reserved]63.4(a)(5)........................... Compliance date........ Yes....................63.4(b)-(c).......................... Circumvention, Yes....................Severability.63.5(a)(1)-(2)....................... Construction/ Yes....................Reconstruction.63.5(b)(1)........................... Compliance Dates....... Yes....................63.5(b)(2)........................... ....................... No..................... [Reserved]63.5(b)(3)-(6)....................... Construction Approval, Yes....................Applicability.63.5(c).............................. ....................... No..................... [Reserved]63.5(d)(1)-(4)....................... Approval of Yes....................Construction/Reconstruction.63.5(e).............................. Approval of Yes....................Construction/Reconstruction.63.5(f)(1)-(2)....................... Approval of Yes....................Construction/Reconstruction.63.6(a).............................. Compliance for Yes....................Standards andMaintenance.63.6(b)(1)-(5)....................... Compliance Dates....... Yes....................63.6(b)(6)........................... ....................... No..................... [Reserved]63.6(b)(7)........................... Compliance Dates....... Yes....................63.6(c)(1)-(2)....................... Compliance Dates....... Yes....................63.6(c)(3)-(4)....................... ....................... No..................... [Reserved]63.6(c)(5)........................... Compliance Dates....... Yes....................63.6(d).............................. ....................... No..................... [Reserved]63.6(e)(1)-(2)....................... Operation & Maintenance Yes....................63.6(e)(3)........................... Startup, Shutdown Yes....................Malfunction Plan.63.6(f)(1)-(3)....................... Compliance with Yes....................Emission Standards.63.6(g)(1)-(3)....................... Alternative Standard... Yes....................63.6(h)(1)-(2)....................... Opacity/VE Standards... Yes....................63.6(h)(3)........................... ....................... No..................... [Reserved]63.6(h)(4)-(h)(5)(i)................. Opacity/VE Standards... Yes....................63.6(h)(5)(ii)-(iv).................. Opacity/VE Standards... No..................... Test duration specifiedin subpart LLL.63.6(h)(6)........................... Opacity/VE Standards... Yes....................63.6(h)(7)........................... Opacity/VE Standards... Yes....................63.6(i)(1)-(14)...................... Extension of Compliance Yes....................63.6(i)(15).......................... ....................... No..................... [Reserved]63.6(i)(16).......................... Extension of Compliance Yes....................63.6(j).............................. Exemption from Yes....................Compliance.63.7(a)(1)-(3)....................... Performance Testing Yes.................... Sec. 63.1349 hasRequirements. specific requirements.63.7(b).............................. Notification........... Yes....................63.7(c).............................. Quality Assurance/Test Yes....................Plan.63.7(d).............................. Testing Facilities..... Yes....................63.7(e)(1)-(4)....................... Conduct of Tests....... Yes....................63.7(f).............................. Alternative Test Method Yes....................63.7(g).............................. Data Analysis.......... Yes....................63.7(h).............................. Waiver of Tests........ Yes....................[[Page 377]]63.8(a)(1)........................... Monitoring Requirements Yes....................63.8(a)(2)........................... Monitoring............. No..................... Sec. 63.1350 includesCEMS requirements.63.8(a)(3)........................... ....................... No..................... [Reserved]63.8(a)(4)........................... Monitoring............. No..................... Flares not applicable.63.8(b)(1)-(3)....................... Conduct of Monitoring.. Yes....................63.8(c)(1)-(8)....................... CMS Operation/ Yes.................... PerformanceMaintenance. specificationsupersedesrequirements for THCCEMS Temperature andactivated carboninjection monitoringdata reductionrequirements given insubpart LLL.63.8(d).............................. Quality Control........ Yes....................63.8(e).............................. Performance Evaluation Yes.................... Performancefor CMS. specificationsupersedesrequirements for THCCEMS.63.8(f)(1)-(5)....................... Alternative Monitoring Yes.................... Additional requirementsMethod. in Sec. 63.1350(l).63.8(f)(6)........................... Alternative to RATA Yes....................Test.63.8(g).............................. Data Reduction......... Yes....................63.9(a).............................. Notification Yes....................Requirements.63.9(b)(1)-(5)....................... Initial Notifications.. Yes....................63.9(c).............................. Request for Compliance Yes....................Extension.63.9(d).............................. New Source Notification Yes....................for Special ComplianceRequirements.63.9(e).............................. Notification of Yes....................Performance Test.63.9(f).............................. Notification of VE/ Yes.................... Notification notOpacity Test. required for VE/opacity test underSec. 63.1350(e) and(j).63.9(g).............................. Additional CMS Yes....................Notifications.63.9(h)(1)-(3)....................... Notification of Yes....................Compliance Status.63.9(h)(4)........................... ....................... No..................... [Reserved]63.9(h)(5)-(6)....................... Notification of Yes....................Compliance Status.63.9(i).............................. Adjustment of Deadlines Yes....................63.9(j).............................. Change in Previous Yes....................Information.63.10(a)............................. Recordkeeping/Reporting Yes....................63.10(b)............................. General Requirements... Yes....................63.10(c)(1).......................... Additional CMS Yes.................... PS-8A supersedesRecordkeeping. requirements for THCCEMS.63.10(c)(2)-(4)...................... ....................... No..................... [Reserved]63.10(c)(5)-(8)...................... Additional CMS Yes.................... PS-8A supersedesRecordkeeping. requirements for THCCEMS.63.10(c)(9).......................... ....................... No..................... [Reserved]63.10(c)(10)-(15).................... Additional CMS Yes.................... PS-8A supersedesRecordkeeping. requirements for THCCEMS.63.10(d)(1).......................... General Reporting Yes....................Requirements.63.10(d)(2).......................... Performance Test Yes....................Results.63.10(d)(3).......................... Opacity or VE Yes....................Observations.63.10(d)(4).......................... Progress Reports....... Yes....................63.10(d)(5).......................... Startup, Shutdown, Yes....................Malfunction Reports.63.10(e)(1)-(2)...................... Additional CMS Reports. Yes....................63.10(e)(3).......................... Excess Emissions and Yes.................... Exceedances are definedCMS Performance in subpart LLL.Reports.63.10(f)............................. Waiver for Yes....................Recordkeeping/Reporting.63.11(a)-(b)......................... Control Device No..................... Flares not applicable.Requirements.63.12(a)-(c)......................... State Authority and Yes....................Delegations.63.13(a)-(c)......................... State/Regional Yes....................Addresses.63.14(a)-(b)......................... Incorporation by Yes....................Reference.63.15(a)-(b)......................... Availability of Yes....................Information.110 [67 FR 16622, Apr. 5, 2002]111 

## Attachment D

Emission Factor Information

A. Kiln Stack Emissions

Kiln stack emissions shall be estimated from CEM concentrations and volumetric flow rates or the

default emission rates listed below.

Criteria Pollutants:

PM 0.055 lb/ton kiln feed

CO 1.804 lb/ton kiln feed

NOx 2.876 lb/ton kiln feed

SO2 0.588 lb/ton kiln feed

THC 0.034 lb/ton kiln feed

Metals

Chromium 0.00011 lb/ton kiln feed

Lead 0.00004 lb/ton kiln feed Mercury 0.00021 lb/ton kiln feed

B. Point Sources (excluding Kiln) Cooler APCD – Based on NSPS (0.1 lb/ton feed)

All other APCD – Grain Loadings of 0.03 gr /dscf are based on engineering judgment. Actual TSP emissions are based on grain loading multiplied by the flow rate and hours of operation.

Allowable emissions are based on grain loading and maximum permitted operating hours, except

for cooler which is based on NSPS.

C. Paved Road Emission Factors (AP-42 section 13.2.1)

E = k (sL/2) 0.65 (W/3) 1.5

Where:

E = particulate emission factor k = base emission factor for particle size range and units of interest (assumed to equal 0.16 lb/Vehicle Mile Traveled). sL = road surface silt loading (grams per square meter) for concrete batching sL average is 12 g/m 2 and for quarry operations it is 8.2 g/m 2

. W = mean vehicle weight (tons)

D. Unpaved Road Emission Factors (AP-42 section 13.2.2)112 E = k (s/12) a (W/3) b

(M/0.2) C

Where:

E = emission factor

k TSP = 10 lb/VMT

a TSP = 0.8 lb/VMT

b TSP = 0.5 lb/VMT

c TSP = 0.4 lb/VMT

k

pm10 = 2.6 lb/VMT

a PM10 = 0.8lb/VMT

b PM10 =0.5 lb/VMT

c PM10 = 0.3 lb/VMT

E. PILES:

TSP transfer factors derived from AP-42 Section 11.2.3 (Pile Transfers).

TSP wind erosion derived from AP- 42 Section 8.19.1 (Pile Wind Erosion). No wind erosion assumed on rain days.

F. CEMEX Process Fugitives

CEMEX currently uses the following emission factors to calculate fugitive emissions. These emission factors are applied to the fugitive emission points as appropriate.

TSP Emission Factor (lb/ton) PM10 Fraction Reference

0.000033 48% AP-42 Table 11.19 2-2, 01/95, and Engineering Estimate by CEMEX

0.002917 48% AP-42 Table 11.19 2-2, 01/95, and Engineering Estimate by CEMEX

0.2700 50% AP-42 Table 11.12-2, 01/95, and Engineering Estimate by CEMEX

0.2400 50% AP-42 Table 11.12-2, 01/95, and Engineering Estimate by CEMEX

0.0290 50% AP-42 Table 11.12-2, 01/95, and Engineering Estimate by CEMEX 1.0 50% Engineering Estimate by CEMEX 0.5 50% Engineering Estimate by CEMEX

G. Emissions from Transfers:

CEMEX uses the following emission factors to cal culate emissions from transferring material:

Operation AP-42 Reference (01/95) PM10/TSP Ratio TSP lb/ton PM10 lb/ton113 Truck Unloading Table 11.19.2-2 0.48 0.000033 0.000016

Conveyor

Transfer Table 11.19.2-2 0.48 0.002916667 0.0014

Cement

Transfer Table 11.12-2 0.5 0.27 0.135

Cement

Transfer Table 11.12-2 0.5 0.24 0.12

Sand and Aggregate

Transfer Table 11.12-2 0.5 0.029 0.0145

Clinker, drop to bin Engineering Estimate 0.2 1.00 0.20

Clinker,

normal

transfer Engineering Estimate 0.2 0.50 0.10



### END OF PERMIT114 

### Permit V-0008 Revision Log

DATE PAGE SECTION REVI SION TYPE OF REVISION 7/24/06 20 B.4 DELETED THE REQUIREMENTS FOR A VOC CEM AND ADDED THE REQUIREMET

FOR AN ANNUAL VOC STACK TEST AS A

RESULT OF A SIGNIFICANT PERMIT MODIFICATION REQUEST. Significant

Modification