1-minute Method 22	Monthly; if no visible emissions for 6 consecutive
months, then semi-annually; if no visible emissions for semi-annual
test, 	Semi-annually	6.B.7(a)

S145	#8 Rail Scale	Visible Emission Monitoring	No visible emissions
1-minute Method 22	Monthly; if no visible emissions for 6 consecutive
months, then semi-annually; if no visible emissions for semi-annual
test, 	Semi-annually	6.B.7(a)

S176	#9 Truck Scale	Visible Emission Monitoring	No visible emissions
1-minute Method 22	Monthly; if no visible emissions for 6 consecutive
months, then semi-annually; if no visible emissions for semi-annual
test, 	Semi-annually	6.B.7(a)

S179	Rail Car Surge Bin Top	Visible Emission Monitoring	No visible
emissions 	1-minute Method 22	Monthly; if no visible emissions for 6
consecutive months, then semi-annually; if no visible emissions for
semi-annual test, 	Semi-annually	6.B.7(a)

S183	Truck Load Out Silo	Visible Emission Monitoring	No visible
emissions 	1-minute Method 22	Monthly; if no visible emissions for 6
consecutive months, then semi-annually; if no visible emissions for
semi-annual test, 	Semi-annually	6.B.7(a)

S184	Truck Load Out Silo	Visible Emission Monitoring	No visible
emissions 	1-minute Method 22	Monthly; if no visible emissions for 6
consecutive months, then semi-annually; if no visible emissions for
semi-annual test, 	Semi-annually	6.B.7(a)

S185	Truck Load Out Silo	Visible Emission Monitoring	No visible
emissions 	1-minute Method 22	Monthly; if no visible emissions for 6
consecutive months, then semi-annually; if no visible emissions for
semi-annual test, 	Semi-annually	6.B.7(a)

S186	Truck Load Out Silo	Visible Emission Monitoring	No visible
emissions 	1-minute Method 22	Monthly; if no visible emissions for 6
consecutive months, then semi-annually; if no visible emissions for
semi-annual test, 	Semi-annually	6.B.7(a)

S63	#1 Truck Scale	Opacity Monitoring	10% Opacity	6-minute Method 9	No
later than 1 hour after visible emissions observed during a Method 22
Test if the equipment continues to operate	Semi-Annual	6.B.7(a)

S64	#2 Truck/Rail Scale	Opacity Monitoring	10% Opacity	6-minute Method 9
No later than 1 hour after visible emissions observed during a Method 22
Test if the equipment continues to operate	Semi-Annual	6.B.7(a)

S65	#3 Truck/Rail Scale	Opacity Monitoring	10% Opacity	6-minute Method 9
No later than 1 hour after visible emissions observed during a Method 22
Test if the equipment continues to operate	Semi-Annual	6.B.7(a)

S66	#4 Truck Scale	Opacity Monitoring	10% Opacity	6-minute Method 9	No
later than 1 hour after visible emissions observed during a Method 22
Test if the equipment continues to operate	Semi-Annual	6.B.7(a)

S67	East Packer	Opacity Monitoring	10% Opacity	6-minute Method 9	No
later than 1 hour after visible emissions observed during a Method 22
Test if the equipment continues to operate	Semi-Annual	6.B.7(a)

S68	West Packer	Opacity Monitoring	10% Opacity	6-minute Method 9	No
later than 1 hour after visible emissions observed during a Method 22
Test if the equipment continues to operate	Semi-Annual	6.B.7(a)

S85	Cement Dome Conveyor and Collection Box	Opacity Monitoring	10%
Opacity	6-minute Method 9	No later than 1 hour after visible emissions
observed during a Method 22 Test if the equipment continues to operate
Semi-Annual	6.B.7(a)

S86	Cement Dome Alleviator	Opacity Monitoring	10% Opacity	6-minute
Method 9	No later than 1 hour after visible emissions observed during a
Method 22 Test if the equipment continues to operate	Semi-Annual
6.B.7(a)

S87	Cement Dome Top	Opacity Monitoring	10% Opacity	6-minute Method 9	No
later than 1 hour after visible emissions observed during a Method 22
Test if the equipment continues to operate	Semi-Annual	6.B.7(a)

S88	Cement Dome Reclaim Tower	Opacity Monitoring	10% Opacity	6-minute
Method 9	No later than 1 hour after visible emissions observed during a
Method 22 Test if the equipment continues to operate	Semi-Annual
6.B.7(a)

S89	Cement Dome Surge Bin	Opacity Monitoring	10% Opacity	6-minute Method
9	No later than 1 hour after visible emissions observed during a Method
22 Test if the equipment continues to operate	Semi-Annual	6.B.7(a)

S90	#5 Truck Scale	Opacity Monitoring	10% Opacity	6-minute Method 9	No
later than 1 hour after visible emissions observed during a Method 22
Test if the equipment continues to operate	Semi-Annual	6.B.7(a)

S91	#6 Truck Scale	Opacity Monitoring	10% Opacity	6-minute Method 9	No
later than 1 hour after visible emissions observed during a Method 22
Test if the equipment continues to operate	Semi-Annual	6.B.7(a)

S113	Rainbow Products	Opacity Monitoring	10% Opacity	6-minute Method 9
No later than 1 hour after visible emissions observed during a Method 22
Test if the equipment continues to operate	Semi-Annual	6.B.7(a)

S122	Cement Transport to Rail Loading Bin	Opacity Monitoring	10% Opacity
6-minute Method 9	No later than 1 hour after visible emissions observed
during a Method 22 Test if the equipment continues to operate
Semi-Annual	6.B.7(a)

S137	Cement Transport Elevator Bottom	Opacity Monitoring	10% Opacity
6-minute Method 9	No later than 1 hour after visible emissions observed
during a Method 22 Test if the equipment continues to operate
Semi-Annual	6.B.7(a)

S138	Cement Transport Elevator Top	Opacity Monitoring	10% Opacity
6-minute Method 9	No later than 1 hour after visible emissions observed
during a Method 22 Test if the equipment continues to operate
Semi-Annual	6.B.7(a)

S144	#7 Rail Scale	Opacity Monitoring	10% Opacity	6-minute Method 9	No
later than 1 hour after visible emissions observed during a Method 22
Test if the equipment continues to operate	Semi-Annual	6.B.7(a)

S145	#8 Rail Scale	Opacity Monitoring	10% Opacity	6-minute Method 9	No
later than 1 hour after visible emissions observed during a Method 22
Test if the equipment continues to operate	Semi-Annual	6.B.7(a)

S176	#9 Truck Scale	Opacity Monitoring	10% Opacity	6-minute Method 9	No
later than 1 hour after visible emissions observed during a Method 22
Test if the equipment continues to operate	Semi-Annual	6.B.7(a)

S179	Rail Car Surge Bin Top	Opacity Monitoring	10% Opacity	6-minute
Method 9	No later than 1 hour after visible emissions observed during a
Method 22 Test if the equipment continues to operate	Semi-Annual
6.B.7(a)

S183	Truck Load Out Silo	Opacity Monitoring	10% Opacity	6-minute Method
9	No later than 1 hour after visible emissions observed during a Method
22 Test if the equipment continues to operate	Semi-Annual	6.B.7(a)

S184	Truck Load Out Silo	Opacity Monitoring	10% Opacity	6-minute Method
9	No later than 1 hour after visible emissions observed during a Method
22 Test if the equipment continues to operate	Semi-Annual	6.B.7(a)

S185	Truck Load Out Silo	Opacity Monitoring	10% Opacity	6-minute Method
9	No later than 1 hour after visible emissions observed during a Method
22 Test if the equipment continues to operate	Semi-Annual	6.B.7(a)

S186	Truck Load Out Silo	Opacity Monitoring	10% Opacity	6-minute Method
9	No later than 1 hour after visible emissions observed during a Method
22 Test if the equipment continues to operate	Semi-Annual	6.B.7(a)

TABLE 6.8 MONITORING AND REPORTING – ID 07 TANK SYSTEM

Stack ID	Unit Description	Pollutant/ Parameter	Limit	Required Monitoring
Monitoring Frequency	Reporting Frequency	Condition Number

S111, S128	HWDF Tanks and Closed Vent System	General Regulatory
Requirements	See Condition	See Condition	See Condition	See Condition
6.B.8(a)

S111, S128	HWDF Tanks and Closed Vent System	General Reporting
Requirements	See Condition	See Condition	Semi -Annually	See Condition
6.B.8(b)

S111, S128	HWDF Tanks and Closed Vent System	VOC	500 ppmv above
background	Portable Flame Ionization Detector	Daily	Semi-annually
6.B.8(c)

S111, S128	HWDF Tanks and Closed Vent System	VOC	N/A	Monitoring of
Pumps	See Condition	Semi-Annually	6.B.8(d)

S111, S128	HWDF Tanks and Closed Vent System	VOC	N/A	Visual Inspection
of Closed Vent System	Initially, and Quarterly Thereafter	Semi-Annually
6.B.8(e)

S111, S128	HWDF Tanks and Closed Vent System	HWDF Tank Requirements	500
ppmv above background	Visual Inspection, and Portable Flame Ionization
Detector	Initially, and Quarterly Thereafter	Semi-Annually	6.B.8(f)

S111, S128	HWDF Tanks and Closed Vent System	Monitoring of Closed Vent
System	N/A	Portable Flame Ionization Detector	Monthly	Semi annual LDAR
report	6.B.8(g)

S111, S128	HWDF Tanks and Closed Vent System	Closed Vent System Bypass
Requirements	N/A	Visual Inspection of Closed Vent System Bypass	Daily
(Valves); Monthly (Monitoring Devices)	Semi-Annually	6.B.8(h)

07	HWDF Delivery System	VOC	See Condition	See Condition	See Condition
See Condition	6.B.8(a-h)

S111, S128)	HWDF Tanks and Closed Vent System	Visual Inspections of
Benzene Emissions from HWDF System	N/A	Monitoring, Record Keeping	As
Performed	N/A	6.B.8(i)

S111, S128)	HWDF Tanks and Closed Vent System	Records of Tests of No
Detectable Emissions for HWDF System	No Detectable Emissions	Monitoring,
Record Keeping	Annual	N/A	6.B.8(j)

S111, S128)	HWDF Tanks and Closed Vent System	Recordkeeping for Closed
Vent System Control Device	N/A	Record Keeping	N/A	N/A	6.B.8(k)

S111, S128)	HWDF Tanks and Closed Vent System	Opacity	20%	Visual
inspection	Semi-annual	Semi-annual	6.B.8(l)

T100, T147, T148, T149	NHWDF tanks	Operational requirements	See
Condition	See Condition	See Condition	See Condition	6.B.8(m)

TABLE 6.9 MONITORING AND REPORTING – PERFORMANCE TESTING

Stack

ID	Unit Description	Pollutant/ Parameter	Limit	Required Monitoring
Monitoring Frequency	Reporting Frequency	Condition Number

ID03 (S95)

and

ID04 (S95)	Preheater/ Precalciner Kiln and Coal Mill	HWC MACT Compliance
See Condition	See Condition	See Condition	See Condition	6.B.9(a)

Facility Wide	Facility Wide except ID 03 S95 and ID 04 S94	PC MACT
Performance Testing Requirements	See Condition	See Condition	See
Condition	See Condition	6.B.9(b)

ID03 (S95)	Coal Mill	Coal Mill System Performance Testing Requirements
0.031 gr/dscf PM	Method 5	See Condition	See Condition	6.B.9(c)

Facility Wide	All Affected Sources	Source Testing Requirements	See
Condition	Monitoring (Performance Testing)	N/A	As Performed	6.B.9(d)

B.	MONITORING AND REPORTING CONDITIONS

6.B.1 GENERAL

The Notification of Compliance with 40 CFR 63 standards shall contain
the information listed in paragraphs (a)(1) through (a)(7) of this
condition.  The operating requirements specified in the Notification of
Compliance will be incorporated in the Title V permit through the use of
a Section 502(b)(10) change or a minor permit modification.

(1)	The methods that were used to determine compliance.

(2)	The results of any performance tests, opacity or visible emission
observations, CMS performance evaluations, and/or other monitoring
procedures or methods that were conducted.

(3)	The methods that will be used for determining continuing compliance,
including a description of monitoring and reporting requirements and
test methods.

(4)	The type and quantity of hazardous air pollutants emitted by the
source (or surrogate pollutants if specified in the relevant standard),
reported in units and averaging times and in accordance with the test
methods specified in the relevant standard.

(5)	An analysis demonstrating whether the affected source is a major
source or an area source (using the emissions data generated for this
notification).

(6)	A description of the air pollution control equipment (or method) for
each emission point, including each control device (or method) for each
hazardous air pollutant and the control efficiency (percent) for each
control device (or method);

(7)	A statement by the owner or operator of the affected existing, new,
or reconstructed source as to whether the source has complied with the
relevant standard or other requirements.

A notification of compliance status with 40 CFR 63 standards must be
submitted before a Title V Operating Permit will be renewed or reissued
to the Permittee.  The notification must be submitted before the close
of business on the 60th day following the completion of the compliance
demonstration.  The notification must contain the following information
(40 CFR 63.9(h)):

(1)	Methods used to determine compliance;

(2)	Results from any monitoring procedures or methods conducted;

(3)	Methods to be used to determine continuing compliance, including a
description of monitoring and reporting requirements and test methods;

(4)	The type and quantity of hazardous air pollutants emitted by the
source, accompanied by units of measurement and averaging times;

(5)	An analysis demonstrating whether the source is a major or area
source;

(6)	A description of the air pollution control equipment and its
associated control efficiency; and

(7)	A statement from the owner or operator as to whether the source has
complied with the relevant standard or other requirements.

An excess emissions and monitoring system performance testing summary
report shall be submitted no later than 30 days following the end of
each calendar half or quarter that presents the results of all
performance testing, monitoring system performance tests, and excess
emissions episodes.  (40 CFR 63.10(e)(3))

(1)	The following information must be included in the summary report
entitled “Summary Report - Gaseous and Opacity Excess Emission and
Continuous Monitoring System Performance”:

(i)	Company name and address;

(ii)	Each hazardous air pollutant monitored;

(iii)	Beginning and ending dates of the reporting period;

(iv)	Brief description of process units;

(v)	Emission and operating parameter limitations;

(vi)	Monitoring equipment manufacturer(s) and model number(s)

(vii)	Date of latest CMS certification or audit;

(viii)	Total operating time of the source during the monitoring period;

(ix)	An emission data summary or control system parameter summary that
illustrates excess emission episodes and their causes;

(x)	A CMS performance summary or control system parameter summary that
describes CMS downtime periods and their causes;

(xi)	A description of CMS, process, or control changes since the last
reporting period;

(xii)	The name, title, and signature of the responsible official
certifying the accuracy of the report; and

(xiii)	The report date.

(2)	If the total duration of excess emissions for the reporting period
is less than 1 percent of total operating time for the period and CMS
downtime for the reporting period is less than 5 percent of total
operating time for the period, then only the summary report will need to
be submitted.  The full excess emissions and performance testing report
need not be submitted unless otherwise stated.

(3)	If the total duration of excess emissions is greater than or equal
to 1 percent of total operating time for the period and CMS downtime for
the reporting period is greater than or equal to 5 percent of total
operating time for the period, then the summary report and full excess
emissions and performance testing reports must be submitted.

For all sources subject to 40CFR63 Subpart A, if actions taken by the
Permittee 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, then the Permittee shall state such information in a
startup, shutdown, and malfunction report. Reports shall only be
required if a startup, shutdown, or malfunction occurred during the
reporting period. The report shall consist of a letter, containing the
name, title, and signature of the responsible official who is certifying
its accuracy, which shall be submitted to the Department semiannually.
It shall be delivered or postmarked by the 30th day following the end of
each calendar half (or other calendar reporting period, as appropriate).
 If the Permittee is required to submit excess emissions and continuous
monitoring system performance (or other periodic) reports, then the
startup, shutdown, and malfunction reports may be submitted
simultaneously with the excess emissions and continuous monitoring
system performance (or other) reports.  If startup, shutdown, and
malfunction reports are submitted with excess emissions and continuous
monitoring system performance (or other periodic) reports and the
Permittee receives approval to reduce the frequency of reporting for the
latter as specified by 40CFR63.10(e), the frequency of reporting for the
startup, shutdown, and malfunction reports also may be reduced if the
Department does not object to the intended change. The procedures to
implement the allowance in the preceding sentence shall be the same as
the procedures specified in 40CFR63.10(e)(3).  A copy of the report
shall also be kept on-site and on-file and made available to Department
personnel upon request.

Notwithstanding the allowance to reduce the frequency of reporting for
periodic startup, shutdown, and malfunction reports as specified in
condition 6.B.1(d), any time an action taken by the Permittee  during a
startup, shutdown, or malfunction (including actions taken to correct a
malfunction) is not consistent with the procedures specified in the
affected source's startup, shutdown, and malfunction plan, the Permittee
 shall report the actions taken for that event within 24-hours after
commencing actions inconsistent with the plan followed by a letter
within seven (7) working days after the end of the event.  The immediate
report shall consist of a telephone call (or facsimile [FAX]
transmission) to the appropriate Trident District Office and Lower
Savannah District Office personnel within 24 hours after commencing
actions inconsistent with the plan, and it shall be followed by a
letter, delivered or postmarked within seven (7) working days after the
end of the event, that contains the name, title, and signature of the
responsible official who is certifying its accuracy, 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.  The
letter shall also be sent to Technical Management Section of the Bureau
of Air Quality.

The owner or operator shall prepare for each affected source, a written
operations and maintenance plan, per 40 CFR 63 Subpart A.  The plan
shall be submitted to the Bureau for review and approval for applicable
40 CFR 63 Subpart LLL sources as part of the renewal or reissue
application for a Title V permit.

All reports required by 40CFR63, Subpart A shall be submitted as
required including:

(1)	The results of performance tests (including opacity test results)
and results of the performance evaluation of the continuous monitoring
system,

(2)	Startup, shutdown, or malfunction report if consistent with the
startup, shutdown, or malfunction plan required by 40 CFR63.10(d)(5)
(semi-annual), if not consistent with above plan a report shall be made
within 24-hours by phone or fax.  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 emission and/or parameter monitoring exceedances are believed to
have occurred,

(3)	All failures to comply with any provisions of the operation and
maintenance plan.

The owner/operator shall maintain on file all measurements required by
this permit including continuous monitoring system or monitoring device
performance measurements; all continuous monitoring system performance
evaluations; all continuous monitoring system or monitoring device
calibration checks; adjustments and maintenance performed on these
systems or devices; and all other information required in a permanent
form suitable for inspection by Department personnel for at least five
(5) years following the date of such measurement, maintenance, report
and record.

The Permittee shall implement a program for routine inspection and
subsequent maintenance on all air pollution control equipment including
duct work, piping, or any other materials pertaining to material
transport or storage where there is potential for generation or release
of regulated air pollutants.  Maintenance events shall be recorded in a
permanent form suitable and available for inspection by representatives
of this Department.  These records shall be retained for at least five
years following the date of such maintenance.  A reasonable inventory of
routine replacement items shall be kept on site to facilitate timely
repair of any malfunctioning systems.

All notifications as required by 40CFR63, Subpart A shall be submitted
as required to the Technical Management Section, including notification
of performance tests, opacity and visible emission observations,
continuous emission monitor performance evaluation and compliance
status.

This permit contains compliance certification, testing, monitoring,
reporting, and record keeping requirements sufficient to assure
compliance with the terms and conditions of this permit.  All submittals
required by these conditions shall be sent to the South Carolina
Department of Health and Environmental Control - Bureau of Air Quality
(SC DHEC - BAQ) at the following address:

SC DHEC - BAQ

Technical Management Section

2600 Bull Street

Columbia, SC 29201

Failure to comply with any provision of the operations and maintenance
plan developed shall be in noncompliance with 40CFR63, Subpart LLL.

The Bureau of Air Quality has reviewed and approved a Leak Detection and
Repair (LDAR) program as an acceptable preventative maintenance program
for the existing facility.  The Permittee must submit an updated program
and gain Bureau approval prior to the operation of the new equipment at
the facility.  The plan should also incorporate all applicable
provisions of 40 CFR 61 Subpart V (National Emission Standard for
Equipment Leaks (Fugitive Emission Sources)) including monitoring,
recordkeeping and reporting frequencies as required.  The Permittee must
adhere to all terms and conditions contained in the approved LDAR
program, including all required reporting and recordkeeping
requirements.  All reports shall be submitted to the Manager of the
Technical Management Section, Bureau of Air Quality.  The LDAR plan
shall be maintained on site for inspection and review by a Department
representative.

The facility shall submit a source test protocol in compliance with the
appropriate federal regulations and also SC Regulations 61-62.1, Section
IV - Source Tests.  A copy of the comprehensive test plan shall also be
submitted to the Director of the Division of Engineering Services.

In accordance with 40 CFR63.1356, any affected source subject to the
provisions of 40CFR63 Subpart LLL is exempted from 40 CFR 60, Subpart F.

The emission limitations for NOx and CO are based on several process
assumptions such as raw material moisture content, carbon content,
nitrogen content and sulfur content.  The facility shall monitor raw
material moisture content, carbon content, nitrogen content and sulfur
content on a semi-annual basis for the first two years of commercial
operation and annually thereafter.  The Department reserves the right to
request material testing at any time that conditions warrant, or to
increase the frequency of testing.  The method of testing shall be
approved by the Department.  Records of the material testing shall be
maintained on site for a period of at least five (5) years from the date
generated and shall be made available to a Department representative
upon request.  Annual reports including all recorded parameters and
calculated values shall be submitted to the Manager of the Technical
Management Section, Bureau of Air Quality, postmarked no later than 30
calendar days after the end of the reporting period.

The kiln system is subject to all applicable provisions of 40CFR63,
Subpart A (General Provisions) and Interim Subpart EEE (National
Emission Standards for Hazardous Air Pollutants from Hazardous Waste
Combustors) until the permittee:

(1)	Ceases hazardous waste-derived fuel burning operations (i.e.,
hazardous waste-derived fuel is no longer in the combustion chamber);
and

(2)	Complies with all other applicable federal and state regulations.

If any changes are made in the design, operation, or maintenance of the
system that may adversely affect compliance with any standard that is
not monitored by a CEM, the change must be determined, and 40 CFR §
63.1206(b)(5) must be complied with.  A change is defined for this
condition as any change in design, operation, or maintenance practices
that were documented in the comprehensive performance test plan,
Notification of Compliance, or startup, shutdown, and malfunction plan.
(40 CFR § 63.1206(b)(5))

If an emergency safety vent (ESV) opens when hazardous waste remains in
the combustion chamber such that combustion gases are not treated as
during the most recent comprehensive performance test, it is evidence of
the permittee’s failure to comply with the emissions limitations of
the HWC MACT.  An ESV operating plan must be developed, complied with
and kept in the operating record.  The plan requirements are listed in
40 CFR § 63.1206(c)(4). A written report is required within 5 days of
an ESV opening that results in failure to meet the emission limitations
documenting the result of the investigation and corrective measures
taken. (40 CFR § 63.1206(c)(4))

The permittee must establish training programs for all categories of
personnel whose activities may reasonably be expected to directly affect
emissions of hazardous air pollutants from the source. Such persons
include, but are not limited to, chief facility operators, control room
operators, continuous monitoring system operators, persons that sample
and analyze feed streams, persons that manage and charge feed streams to
the combustor, persons that operate emission control devices, and ash
and waste handlers. Each training program shall be of a technical level
commensurate with the person's job duties specified in the training
manual. Each commensurate training program shall require an examination
to be administered by the instructor at the end of the training course.
Passing of this test shall be deemed the "certification" for personnel,
except that, for control room operators, the training and certification
program shall be as specified in paragraphs (c)(6)(iii) through
(c)(6)(vi) of 40 CFR 63.1206.

6.B.2 QUARRY SYSTEM

These sources are subject to all applicable requirements of Federal New
Source Performance Standards (NSPS) 40 CFR Part 60, Subpart OOO.  The
requirements for inspections, testing, reporting, monitoring, etc.
listed in 40 CFR Parts 60, Subparts A and OOO shall be completed and
reported as specified.

In accordance with 40 CFR Part 60, Subpart OOO - Standards of
Performance for Nonmetallic Mineral Processing Plants, crushers shall
not exhibit an opacity greater than 15%.  In accordance with 40 CFR Part
60, Subpart OOO (Standards of Performance for Nonmetallic Mineral
Processing Plants), belt conveyors or other affected facilities as
defined in 40 CFR § 60.670 except crushers shall not exhibit an opacity
greater than 10% when conveying unsaturated materials.  Source tests for
opacity indicating compliance with permit standards are required prior
to a permit to operate being issued.  The owner/operator of these
sources may use the alternative Method 9 testing to show compliance with
the appropriate opacity standard.  This Method 9 allows belt conveyor
transfer points and screens without emission capture systems to reduce
the duration of observations of fugitive emissions from 3 hours (thirty
6-minute averages) to 1 hour (ten 6-minute averages) if there are no
individual readings greater than 15 percent opacity for crushers or 10
percent opacity for other affected emission units and there are no more
than 3 readings of 15 percent for crushers or 10 percent for other
affected emission units for the first 1-hour period.   If the
alternative Method 9 testing fails to prove compliance, the traditional
Method 9 testing is required.  These tests shall be performed within 60
days of achieving the maximum production rate, but no later than 180
days after the initial startup.  Source test methodology must be
approved by the BAQ.  The Manager of Source Evaluation, BAQ shall be
notified of the anticipated date of the required opacity testing,
postmarked not less than 45 days prior to such date so that a Bureau
representative may be present if desired.  Rescheduled source tests
require 7 days notification.

6.B.3 RAW MILL SYSTEM

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 40 CFR 60. The test must be conducted while the affected source is in
operation.  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.  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.  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.

All emission limitations for the roller mill, which is considered as
part of an in-line raw mill/ kiln system, are included in section 6.B.5.

Fugitive emissions shall be controlled using dust suppression techniques
including paving, brooming and watering for problem areas.

6.B.4 COAL MILL SYSTEM

These sources are subject to all applicable provisions of 40 CFR 60
Subpart A (General Provisions) and Subpart Y (Coal Preparation Plants).

The permittee shall perform a visual inspection on a monthly basis.
Visual Inspection means a qualitative observation of opacity during
daylight hours where the inspector records results in a log, noting
color, duration, density (heavy or light), cause and corrective action
taken for any abnormal emissions.  The observer does not need to be
certified to conduct valid visual inspections.  However, at a minimum,
the observer should be trained and knowledgeable about the effects on
visibility of emissions caused by background contrast, ambient lighting,
observer position relative to lighting, wind, and the presence of
uncombined water.  Logs shall be kept to record all visual inspections,
including cause and corrective action taken for any abnormal emissions
and visual inspections from date of recording.  The logs shall be
maintained for a period of five (5) years and be made available to the
Department upon request.  The owner/operator shall submit semi-annual
reports to the Manager of the Technical Management Section, Bureau of
Air Quality postmarked no later than 30 calendar days after the end of
the reporting period.

(c)	Opacity for the coal mill shall be monitored using a continuous
opacity monitor (COM).  If the COM should go off-line, opacity shall be
monitored daily using a 30-minute EPA Method 9 test.  Logs shall be kept
to record all visual inspections, including cause and corrective action
taken for any abnormal emissions and visual inspections from date of
recording.  The logs shall be maintained for a period of five (5) years
and be made available to the Department upon request.  Continuous
Opacity Monitors are required in order to verify compliance with the
emission limitations for the coal mill.  Quarterly reports detailing any
excursions (if applicable) or downtime shall be submitted to the Manager
of the Technical Management Section, Bureau of Air Quality postmarked no
later than 30 calendar days after the end of the reporting period.
Semi-annual Continuous Opacity Monitor reports shall be submitted to the
Manager of the Technical Management Section, Bureau of Air Quality
postmarked no later than 30 calendar days after the end of the reporting
period. Monitor operations shall be subject to South Carolina’s
“Continuous Monitoring System Evaluation Plan”(9/96), as amended.
The report shall include the following minimum information:

All opacity measurements for periods during which the above emission
limitations for opacity have been exceeded, together with their nature
and cause.

For periods of monitoring system malfunction:

i.	The date and time identifying each period during which the monitoring
system was inoperative, except for zero and span checks.

ii.	The nature of monitoring system repairs or adjustments.

iii.	Proof of COM system performance may be required by the Department
whenever repairs or adjustments have been made.

Particulate matter emissions from the coal mill shall be monitored every
2.5 years.

The owner or operator of any thermal dryer shall install, calibrate,
maintain, and continuously operate 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 F.  The
monitoring device is to be calibrated annually.

(f)	VOC emissions shall be monitored every 2.5 years from the coal mill
stack.

Continuous Emission Monitors for SO2, CO and NOx are required in order
to verify compliance with the emission limitations for the kiln system.
CEMs shall be installed on both the coal mill stack and on the main kiln
stack.  Quarterly reports detailing any excursions (if applicable) or
downtime shall be submitted to the Manager of the Technical Management
Section, Bureau of Air Quality postmarked no later than 30 calendar days
after the end of the reporting period. These reports shall include the
30-day rolling average (24 1-hour measurements in tonnage of SO2, CO and
NOx summed together and added to the previous 29 day sum). The lb/ton
clinker value shall be calculated using the daily production records for
clinker.  These records shall be maintained as required. Quarterly
Continuous Emission Monitor reports shall be submitted to the Manager of
the Technical Management Section, Bureau of Air Quality postmarked no
later than 30 calendar days after the end of the reporting period.
Monitor operations shall be subject to South Carolina’s “Continuous
Monitoring System Evaluation Plan” (9/96), as amended. The report
shall include the following minimum information:

a.	All measurements for periods during which the above emission
limitations have been exceeded, together with their nature and cause.

b.	For periods of monitoring system malfunction:

i.	The date and time identifying each period during which the monitoring
system was inoperative, except for zero and span checks.

ii.	The nature of monitoring system repairs or adjustments.

iii.	Proof of the monitoring system performance may be required by the
Department whenever repairs or adjustments have been made.

(h)	These sources are subject to all applicable provisions of 40 CFR 60
Subpart A (General Provisions) and Subpart Y (Coal Preparation Plants).

(i)	The coal mill stack (S95) is subject to applicable provisions of
40CFR63 Interim Subpart EEE (Hazardous Waste Combustors).

6.B.5 KILN SYSTEM

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 40 CFR 60. The test must be conducted while the affected source is in
operation.  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.  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.  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.

The owner or operator subject to opacity limitations for the other
sources under this permit besides the in-line kiln/raw mill shall
monitor opacity in accordance with the operation and maintenance plan
developed for those situations when the in-line kiln/raw mill is in
operation using non-hazardous fuels.

Logs shall be kept to record all visual inspections, including cause and
corrective action taken for any abnormal emissions and visual
inspections from date of recording.  The logs shall be maintained for a
period of five (5) years and be made available to the Department upon
request.  The owner/operator shall submit semi-annual reports to the
Manager of the Technical Management Section, Bureau of Air Quality
postmarked no later than 30 calendar days after the end of the reporting
period.

(b)	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 (at
both the main kiln stack and the coal mill stack).  The COM shall be
installed maintained, calibrated, and operated as required by 40 CFR 63
Subpart A and PS-1 of Appendix B of 40 CFR 60.  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 for those situations when
the in-line kiln/raw mill is in operation using non-hazardous fuels.
Quarterly reports detailing any excursions (if applicable) or downtime
shall be submitted to the Manager of the Technical Management Section,
Bureau of Air Quality postmarked no later than 30 calendar days after
the end of the reporting period. Semi-annual Continuous Opacity Monitor
reports shall be submitted to the Manager of the Technical Management
Section, Bureau of Air Quality postmarked no later than 30 calendar days
after the end of the reporting period. Monitor operations shall be
subject to South Carolina’s “Continuous Monitoring System Evaluation
Plan”(9/96), as amended. The report shall include the following
minimum information:

a.	All opacity measurements for periods during which the above emission
limitations for opacity have been exceeded, together with their nature
and cause.

b.	For periods of monitoring system malfunction:

i.	The date and time identifying each period during which the monitoring
system was inoperative, except for zero and span checks.

ii.	The nature of monitoring system repairs or adjustments.

iii.	Proof of COM system performance may be required by the Department
whenever repairs or adjustments have been made.

The permittee must comply with the dioxin and furans emission standard
by establishing and complying with the following operating parameter
limits. The permittee must base the limits on operations during the
comprehensive performance test, unless the limits are based on
manufacturer specifications.

	(1)	For hazardous waste burning incinerators and cement kilns, if the
combustor is equipped with an electrostatic precipitator, baghouse
(fabric filter), or other dry emissions control device where particulate
matter is suspended in contact with combustion gas, the permittee must
establish a limit on the maximum temperature of the gas at the inlet to
the device on an hourly rolling average. The permittee must establish
the hourly rolling average limit as the average of the test run
averages.

	(2)	The permittee must measure the temperature of each combustion
chamber at a location that best represents, as practicable, the bulk gas
temperature in the combustion zone. The permittee must document the
temperature measurement location in the test plan the permittee submits
under 40CFR63.1207(e) and (f); the permittee must establish a minimum
hourly rolling average limit as the average of the test run averages.

	(3)	As an indicator of gas residence time in the control device, the
permittee must establish and comply with a limit on the maximum flue gas
flowrate, the maximum production rate, or another parameter that the
permittee documents in the site-specific test plan as an appropriate
surrogate for gas residence time, as the average of the maximum hourly
rolling averages for each run.  The permittee must comply with this
limit on an hourly rolling average basis.

	(4) 	The permittee must establish limits on the maximum pumpable and
total (pumpable and non-pumpable) waste feedrate for each location where
waste is fed.  The permittee must establish the limits as the average of
the maximum hourly rolling averages for each run.  The permittee must
comply with the feedrate limit(s) on an hourly rolling average basis.

	(5) 	The permittee shall maintain these records on-site for a period of
at least five (5) years.  These records shall be made available to a
Department representative upon request.  Quarterly reports including all
recorded parameters and calculated values shall be submitted to the
Manager of the Technical Management Section, Bureau of Air Quality
postmarked no later than 30 calendar days after the end of the reporting
period.

The permittee must install, calibrate, maintain, and operate a
particulate matter CEMS to demonstrate and monitor compliance with the
particulate matter standards under this subpart. However, compliance
with the requirements in this section to install, calibrate, maintain
and operate the PM CEMS is not required until such time that the Agency
promulgates all performance specifications and operational requirements
applicable to PM CEMS.

(e)	A thermocouple shall be installed, calibrated, maintained, and
continuously operated to monitor the temperature of the exhaust kiln
gases from the in-line kiln/raw mill and alkali bypass at the inlet of
the particulate matter control device.  Quarterly reports detailing any
excursions (if applicable) or downtime shall be submitted to the Manager
of the Technical Management Section, Bureau of Air Quality postmarked no
later than 30 calendar days after the end of the reporting period.
Semi-annual Continuous Monitor reports shall be submitted to the Manager
of the Technical Management Section, Bureau of Air Quality postmarked no
later than 30 calendar days after the end of the reporting period.
Monitor operations shall be subject to South Carolina’s “Continuous
Monitoring System Evaluation Plan”(9/96), as amended. The report shall
include the following minimum information:

All temperature measurements for periods during which the above
temperature limitations have been exceeded, together with their nature
and cause.

For periods of monitoring system malfunction:

i.	The date and time identifying each period during which the monitoring
system was inoperative, except for zero and span checks.

ii.	The nature of monitoring system repairs or adjustments.

iii.	Proof of system performance may be required by the Department
whenever repairs or adjustments have been made.

All notifications required for those situations when the in-line
kiln/raw mill is in operation using non-hazardous fuels, shall be
submitted as required including notification of performance tests,
opacity and visible emission observations, continuous emission monitor
performance evaluation and compliance status.

All reports required for submission include, but are not limited to, the
following:

(1)	The results of performance tests (including opacity test results)
and results of the performance evaluation of the continuous monitoring
system,

(2)	Startup, shutdown, or malfunction report if consistent with the
startup, shutdown, or malfunction plan required by 40 CFR § 63.10(d)(5)
(semi-annual), if not consistent with above plan a report shall be made
within 24-hours by phone or fax.  The immediate report shall be followed
by a letter within seven (7) days, 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 emission and/or parameter monitoring
exceedances are believed to have occurred,

(3)	All failures to comply with any provisions of the operation and
maintenance plan.

The kiln system is subject to all applicable provisions of 40 CFR 61,
Subpart A (General Provisions) and Subpart FF (National Emission
Standard for Benzene Waste Operations).

The owner or operator shall design, install, operate, and maintain a
treatment process that destroys benzene from the waste stream by
incinerating the waste in a combustion unit that achieves a destruction
efficiency of 99% or greater for benzene.  (40 CFR § 61.348(a)(1))

The treatment process consisting of an industrial furnace burning
hazardous waste for energy recovery which has been issued a final permit
under 40 CFR 270 and complies with 40 CFR 266 Subpart D is exempt from
performance test requirements of 40 CFR 61 Subpart FF (40 CFR 61.348
(d)).

The kiln must be equipped with a monitoring device equipped with a
continuous recorder to measure a parameter (such as temperature) that
indicates good combustion operating practices are being used at the
point of control or treatment.

For each occurrence mentioned below, reports shall be submitted to the
Manager of the Technical Management Section, Bureau of Air Quality as
required in 40 CFR § 61.357(d).

(1)	Each occurrence when there is a change in the location at which the
vent stream is introduced into the flame zone of an industrial furnace.

(k)	The emission limitations for NOx and CO are based on several process
assumptions such as raw material moisture content, carbon content,
nitrogen content and sulfur content.  The facility shall monitor raw
material moisture content, carbon content, nitrogen content and sulfur
content on a semi-annual basis for the first two years of commercial
operation and annually thereafter.  The Department reserves the right to
request material testing at any time that conditions warrant or to
increase the frequency of testing.  The method of testing shall be
approved by the Department.  Records of the material testing shall be
maintained on site for a period of at least five (5) years from the date
generated and shall be made available to a Department representative
upon request.  Semi-annual reports including all recorded parameters and
calculated values shall be submitted to the Manager of the Technical
Management Section, Bureau of Air Quality postmarked no later than 30
calendar days after the end of the reporting period.

Quarterly Continuous Opacity Monitor reports shall be submitted to the
Manager of the Technical Management Section, Bureau of Air Quality,
postmarked no later than 30 calendar days after the end of the reporting
period. Monitor operations shall be subject to South Carolina’s
“Continuous Monitoring System Evaluation Plan”(6/99), as amended.
The report shall include the following minimum information:

(1)	All integrated six minute opacity measurements for periods during
which the applicable emission limitations have been exceeded, together
with their nature and cause.

(2)	For periods of monitoring system malfunction:

(i)	The date and time identifying each period during which the
monitoring system was inoperative, except for zero and span checks.

(ii)	The nature of monitoring system repairs or adjustments.

(iii)	Proof of opacity monitoring system performance may be required by
the Department whenever repairs or adjustments have been made.

The waste feed rate shall be monitored continuously and recorded as
required by SC Regulation 61-62.5 Standard No. 3, section VI(A)(2)(k).

The owner/operator shall submit to the Bureau prior to operation of the
kiln system a plan detailing the specifics of the burner, process and
kiln optimization that will be done on the source which is considered to
be part of the BACT determination.  This plan shall be submitted to the
Director of Engineering Services, Bureau of Air Quality.

Continuous Emission Monitors for SO2, CO, and NOx are required in order
to verify compliance with the above emission limitations for the kiln
system.  CEMs shall be installed on both the coal mill stack and on the
main kiln stack.  Quarterly reports detailing any excursions (if
applicable) or downtime shall be submitted to the Manager of the
Technical Management Section, Bureau of Air Quality, postmarked no later
than 30 calendar days after the end of the reporting period. These
reports shall include the 30 day rolling average (24 1-hour measurements
in tonnage of SO2, CO, and NOx summed together and added to the previous
29 day sum). The lb/ton clinker value shall be calculated using the
daily production records for clinker.  These records shall be maintained
on-site for a period of at least five (5) years from the date generated.
 These records shall be made available to Department personnel upon
request.  Quarterly Continuous Emission Monitor reports shall be
submitted to the Manager of the Technical Management Section, Bureau of
Air Quality, postmarked no later than 30 calendar days after the end of
the reporting period. Monitor operations shall be subject to South
Carolina’s “Continuous Monitoring System Evaluation Plan”(9/96),
as amended. The report shall include the following minimum information:

(1)	All measurements for periods during which the above emission
limitations have been exceeded, together with their nature and cause.

(2)	For periods of monitoring system malfunction:

(i)	The date and time identifying each period during which the
monitoring system was inoperative, except for zero and span checks.

(ii)	The nature of monitoring system repairs or adjustments.

(iii)	Proof of the monitoring system performance may be required by the
Department whenever repairs or adjustments have been made.

Emission limitations and requirements applicable to the main kiln stack
are also applicable to the coal mill stack when the stack gas from the
kiln system is vented through the coal mill.

This source is limited to a maximum production rate of 2,462,318 short
tons of clinker per year.  The Permittee must record the actual monthly
production rates and maintain these records on-site for a period of at
least five (5) years from the date generated.  The facility shall also
maintain daily clinker production records for the calculation of the
NOx, CO, and SO2 emissions.  These records shall be made available to
Department personnel upon request. Semi-annual reports including
applicable recorded parameters and applicable calculated values
including the annual clinker production rate shall be submitted to the
Manager of the Technical Management Section, Bureau of Air Quality,
postmarked no later than 30 calendar days after the end of the reporting
period.  These conditions shall not supersede any State or Federal
requirements such as National Emission Standards for Hazardous Air
Pollutants, unless these conditions would impose a more restrictive
limit.

The owner or operator shall demonstrate initial compliance with the
emission limits 180 days after initial start-up of burning HWDF using
the test methods and procedures listed in 40 CFR § 63.7.  Performance
test results shall be documented in complete test report that contain
the information required by 40 CFR § 63.7, as well as all other
relevant information.  The plan to be followed during testing shall be
made available to the Bureau prior to testing as required by SC
Regulation 61-62.1 Section IV - Source Testing.

The owner or operator of any in-line kiln/raw mill subject to a D/F
emission limit shall conduct an inspection of the components of the
combustion system of each in-line kiln raw mill at least annually.
Records of the inspection and repairs made shall be maintained on site
for a period of at least five (5) years from the date generated and
shall be made available to a Department representative upon request.
Semi-Annual reports including all recorded parameters and calculated
values shall be submitted to the Manager of the Technical Management
Section, Bureau of Air Quality postmarked no later than 30 calendar days
after the end of the reporting period.

(t)	The owner or operator using a treatment process and control device
shall maintain the following records.  The documentation shall be
retained for the life of the control device.

(1)	Engineering design documentation;

(2)	A statement signed and dated by the owner or operator certifying
that the system as both a treatment process and control device is
designed to operate at the documented performance level when the waste
management unit vented to the control device is or would be operating at
the highest load or capacity expected to occur;

(3)	A design analysis including all requirements applicable in 40 CFR §
61.356(e and f)(2); and

(4)	If performance tests are used to determine performance all
requirements in 40 CFR § 61.356(e), and 40 CFR § 61.356(f)(3).

(u)	A source test for PM, Metals, POHC removal and reduction efficiency,
CO, O2, and HCl emissions from the kiln system will be required.  The
tests shall be performed within 60 days after achieving maximum
production but not later than 180 days after initial start-up of burning
HWDF’s.  The Bureau must be notified at least two weeks prior to any
source test so that a Bureau representative may be present.  The testing
shall be done at least every two and a half years.  Source test
methodology must be approved by the Bureau and comply with SC Regulation
62.1, Section IV, Source Testing.

The particulate matter emission rate must be computed by the equation
specified in 40 CFR § 63.1204(a)(7)(ii).  E=(Cs x Qsd)/P.

The kiln system shall achieve a DRE of 99.99% for each principle organic
hazardous constituent (POHC) designated.  To calculate the DRE for each
POHC use the equation in 40 CFR § 63.1204(c)(1).  The POHC shall be
designated as required by 40 CFR § 63.1204(c)(3).

(w)	The DRE standard must be documented only once provided that no
modifications of the source are done which could affect the ability of
the source to achieve the DRE standard.  The facility shall prove
compliance during the initial comprehensive performance test (40 CFR §
63.1206(b)(7)).

(x)	The emission standards and operating requirements set forth apply at
all times except: during periods of startup, shutdown, and malfunction;
and when hazardous waste is not in the combustion chamber (i.e., the
hazardous waste feed to the combustor has been cut off for a period of
time not less than the hazardous waste residence time) and the permittee
has documented in the operating record that the permittee is complying
with all otherwise applicable requirements and standards promulgated
under authority of sections 112 (e.g., 40 CFR 63 subpart LLL) or 129 of
the Clean Air Act in lieu of the emission standards of 40 CFR63.1203
through 63.1205; the monitoring and compliance standards of this section
and 40 CFR63.1207 through 63.1209, except the modes of operation
requirements of 40 CFR63.1209(q); and the notification, reporting, and
recordkeeping requirements of 40 CFR63.1210 through 63.1212. (40 CFR §
63.1206(b)(1)(ii)).

(y)	The hazardous waste residence time must be calculated and included
in the performance test plan and operating record with calculation.  The
hazardous waste residence time must also be provided in the
Documentation of Compliance and the Notification of Compliance (40 CFR
§ 63.1206(b)(11)).

The facility shall operate only under the operating requirements
specified in the Documentation of Compliance or the Notification of
Compliance except during performance tests under an approved test plan
required by the HWC MACT or if the facility has requested to be operated
in compliance without burning hazardous waste and has been granted
approval  (40 CFR § 63.1206(c)(1)).

A startup, shutdown, and malfunction plan requirements of 40 CFR §
63.6(e)(3) shall be complied with including a projected oxygen
correction factor based on normal operations to use during periods of
startup and shutdown and the plan must be recorded in the operating
record.  Even if the startup and shutdown procedures and the corrective
measures are followed upon a malfunction prescribed in the startup,
shutdown, and malfunction plan, the emission standards and operating
requirements of the HWC MACT and this permit apply if hazardous waste is
in the combustion chamber and the HWDF residency time has not expired
(40 CFR § 63.1206(c)(2)).

The hazardous waste combustor must operate with a functioning system
that automatically cuts off the hazardous waste feed in compliance with
40 CFR  § 63.1206(c)(3).  The system and associated alarms must be
tested at least weekly to verify operability unless documented in the
operation record that weekly inspection will unduly restrict or upset
operation and that less frequent inspections will be adequate.  At a
minimum, the operability testing shall be conducted at least monthly.
The testing procedures and results shall be documented and recorded in
the operating record.

Combustion system leaks must be controlled by one of the following:

(1)	Keeping the combustion zone sealed to prevent combustion system
leaks; or

(2)	Maintaining the maximum combustion zone pressure lower than ambient
pressure using an instantaneous monitor; or

(3)	Upon prior written approval of the Administrator, an alternative
means of control to provide control of combustion system leaks
equivalent to maintenance of combustion zone pressure lower than ambient
pressure.

	(4)	The method used must be specified in the operating record (40 CFR
§ 63.1206(c)(5)).

An operation and maintenance plan which describes in detail procedures
for operation, inspection, maintenance, and corrective measures for all
components of the combustor, including associated pollution control
equipment, that could affect emissions of regulated air pollutants must
be prepared and complied with at all times.  The plan requirements are
listed in 40 CFR § 63.1206(c)(7).  The plan must be recorded in the
operating record.

The facility shall install a CEM in the alkali bypass to demonstrate and
monitor compliance with the hydrocarbon emission limitations.  An oxygen
CEM must also be used to continuously correct hydrocarbon levels to 7%
oxygen (40 CFR § 63.1209(a)(1)(I)).

(ff)	The facility shall install a COM to demonstrate and monitor
compliance with the opacity limitations at each point (both the main
kiln stack and the coal mill stack) where emissions are vented from
these sources as required by 40 CFR § 63.1209(a)(1)(ii).  Daily Method
9 opacity readings will be required when the COM is off line.

(gg)	Prior to feeding the material to the kiln, an analysis of each
feedstream is required in order to document compliance with the feedrate
limits as required by 40 CFR § 63.1209(c).  A feedstream analysis plan
shall be developed and implemented and recorded into the operating
record.  The plan must include all requirements listed in 40 CFR §
63.1209(c).  This plan shall be submitted to the Bureau for approval.
The feedrate limits will be included in the aforementioned plan.
Compliance with these limits shall be monitored by determining and
recording the value of the parameter for each feedstream, the mass or
volume flowrate of each feedstream by a Continuous Monitoring System,
and calculating and recording the mass feedrate of the parameter per
unit time.

(hh)	The following are the operating parameters required to show
compliance with the emission limitations.  These operating parameters
are determined in the comprehensive performance test and shall be kept
in the operating record.  Operating record means a documentation
retained at the facility for ready inspection by authorized officials of
all information required by the standards to document and maintain
compliance with the applicable regulations, including data and
information, reports, notifications, and communications with regulatory
officials.  The permittee shall maintain these records on-site for a
period of at least five (5) years.  These records shall be made
available to a Department representative upon request.  Quarterly
reports including all recorded parameters and calculated values shall be
submitted to the Manager of the Technical Management Section, Bureau of
Air Quality postmarked no later than 30 calendar days after the end of
the reporting period.  The facility shall be in compliance with all
requirements in 40 CFR § 63.1209 with regards to each monitoring
system.

(1)	DRE - Minimum combustion chamber temperature (hourly rolling average
limit), maximum flue gas flowrate or production rate (indicator of gas
residence time - hourly rolling average limit), maximum hazardous waste
feedrate (maximum pumpable and total hazardous waste feedrate for each
location fed - hourly rolling average limit), operation of waste firing
system (parameters and limits to ensure that good operation of each
hazardous waste firing system is maintained).

(2)	D/F - maximum gas temperature at the inlet to a dry particulate
matter control device (hourly rolling average limit), minimum combustion
chamber temperature (hourly rolling average limit), maximum flue gas
flowrate or production rate (gas residence time - hourly rolling average
limit), maximum hazardous waste feedrate (maximum pumpable and total
hazardous waste feedrate for each location fed - hourly rolling average
limit).

(3)	Mercury - a hazardous waste feedrate corresponding to a maximum
theoretical emission concentration (MTEC) of 120 (g/dscm on a 12-hour
rolling average (40CFR63.1204(b)(2); 40CFR63.1206(b)(15)).

(4)	PM - Reserved.

(5)	Semivolatile and Low volatile metals - maximum gas temperature at
the inlet to a dry particulate matter control device (hourly rolling
average limit), feedrate of total mercury (12 hour rolling average) or
other allowed parameter, minimum pressure drop and maximum pressure drop
across each baghouse cell based on manufacturer’s specifications
(hourly rolling average), maximum total chlorine and chloride feedrate
(12 hour rolling average limit), maximum flue gas flowrate or production
rate (gas residence time - hourly rolling average limit).

(6)	HCl and Chlorine gas - maximum total chlorine and chloride feedrate
(12 hour rolling average limit), maximum flue gas flowrate or production
rate (gas residence time - hourly rolling average limit).

(7)	According to the alternative maintenance on the Differential
Pressure Ports granted to the facility (letter from BAQ dated May 25,
2005) the facility must abide by the following:

1.	Visual monitoring must be must be performed around the area each time
the port at the kiln inlet is taken off line and cleaned (this is
relevant only for when it is day light hours).

2.	The preventative cleaning can be preformed for no longer than 20
minutes in any 24-hour period.

3.	The ID Fan must be kept operational for the entire cleaning period
within ±10% of the speed (RPMs) it had prior to the port being taken
off-line for cleaning.

4.	Records of each maintenance period must be maintained for a period of
five (5) years and be made available to the Department upon request. The
records must include, at a minimum, the following

a.	Time and duration of the maintenance event.

b.	Any visual observations made (applicable only during daylight hours).

c.	ID Fan speed (RPMs).

If the facility operates under different modes of operation, operating
parameter limits of each mode must be determined.  The change of mode of
operation shall be documented in the operating record and the rolling
averages must be calculated.

(ii)	All notification requirements of 40 CFR § 63.1210 shall be
complied with as applicable.

(jj)	All recordkeeping and reporting requirements of 40 CFR § 63.1211
shall be complied with as applicable.

6.B.6 FINISH MILL SYSTEM

These sources are subject to all applicable provisions of 40 CFR 63
Subpart A (General Provisions) and LLL (Portland Cement Manufacturing).

Opacity Requirements

(1)	The owner or operator shall demonstrate initial compliance and then
every five years with the affected source opacity limit by conducting a
test in accordance with Method 9.  The performance test 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 maximum six-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 following apply: 1.  There are no individual readings greater
than 10 percent opacity.  2.  There are no more than three readings of
10 percent for the first 1-hour period.

(2)	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 40 CFR 60. The test must be conducted while the affected
source is in operation.  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.  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.  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 40 CFR 60. The
Method 9 test must begin within one hour of any observation of visible
emissions.

(3)	For baghouse sources S54, S96, and S97, a daily Method 22 must be
conducted.  If a visible emission is observed, then a follow up method
22 test must be conducted on that source which the visible emission was
observed within 24-hours.  If a visible emission is still observed after
the follow up Method 22 text, a 30-minute Method 9 test must then be
conducted for the stack which the visible emission was observed.

6.B.7 CEMENT LOADOUT

Opacity Requirements

(1)	The owner or operator shall demonstrate initial compliance and then
every five years with the affected source opacity limit by conducting a
test in accordance with Method 9.  The performance test 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 maximum six-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 listed below apply: 1.  There are no individual
readings greater than 10 percent opacity.  2.  There are no more than
three readings of 10 percent for the first 1-hour period.

(2)	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 40 CFR 60. The test must be conducted while the affected
source is in operation.  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.  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.  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 40 CFR 60. The
Method 9 test must begin within one hour of any observation of visible
emissions. When visible emissions are observed during a Method 22 test,
a 6-minute EPA Method 9 test shall follow the observation within one
hour.

6.B.8 TANKS

The HWDF tanks and closed vent system (S111, S128), including control
devices, are subject to all applicable provisions of 40 CFR Part 61
Subpart A (General Provisions), Subpart V (National Emission Standard
for Equipment Leaks (Fugitive Emission Sources)), and Subpart FF
(National Emission Standard for Benzene Waste Operations); and 40 CFR
Part 63 Subpart A (General Provisions) and performance standards only
for Subpart DD (National Emission Standards for Hazardous Air Pollutants
from Off-Site Waste and Recovery Operations).  The HWDF tank and closed
vent system, including control devices, are subject to all applicable
provisions of 40 CFR Part 60 Subpart A (General Provisions) and Subpart
Kb (Standards of Performance for VOL Storage Vessels).

Since this facility processes waste streams produced by facilities with
the total potential annual benzene quantity of greater than 10 Mg/yr,
then this facility is fully subject to all applicable requirements of 40
CFR 61 Subpart A (General Provisions) and Subpart FF (National Emission
Standard for Benzene Waste Operations).

	General Reporting Requirements

(1)	Quarterly reports shall be submitted to the Manager of the Technical
Management Section, Bureau of Air Quality, as required in
40CFR61.357(d).  These reports shall include:

(i)	Each occurrence when the carbon in a carbon adsorber system that is
not regenerated directly on site in the control device is not replaced
at the predetermined interval (40CFR61.357(d)(7) (iv)(J)).

(2)	Semi Annual reports shall be submitted to the Manager of the
Technical Management Section, Bureau of Air Quality as required in
40CFR61.357(d).  These reports shall include:

(i)	Beginning one year after the date that the equipment necessary to
comply with these standards has been certified in accordance with
paragraph of 40 CFR 61.357(d)(1) of this section, the owner or operator
shall submit annually to the Administrator a report that summarizes all
inspections required by 40 CFR61.342 through 61.354 during which
detectable emissions are measured or a problem (such as a broken seal,
gap or other problem) that could result in benzene emissions is
identified, including information about the repairs or corrective action
taken (40CFR61.357(d)(8)).

(c)	The closed vent system, per 40CFR61.349 (a)(1)(i), shall be designed
to operate with no detectable emission as indicated by an instrument
reading of less than 500 ppmv above background as determined initially
and thereafter at least once per year by the methods specified in
40CFR61.355(h). The permittee shall maintain records of these tests
on-site for a period of at least five (5) years.  These records shall be
made available to a Department representative upon request.  Semi-annual
reports including all recorded parameters and calculated values shall be
submitted to the Manager of the Technical Management Section, Bureau of
Air Quality postmarked no later than 30 calendar days after the end of
the reporting period.

(d)	Any pumps operating in the HWDF handling system are subject to
monthly monitoring to detect leaks per 40 CFR 61.242-2(a).  The dual
mechanical seal system is visually inspected weekly to determine if
dripping leaks are present per 242-2(d).

Each closed-vent system and control device shall be visually inspected
initially and quarterly thereafter.  The visual inspection shall include
inspection of ductwork and piping and connections to covers and control
devices for evidence of visible defects such as holes in ductwork or
piping and loose connections.  If visible defects are observed during an
inspection, or if other problems are identified, or if detectable
emissions are measured, a first effort to repair the closed-vent system
and control device shall be made as soon as practical but no later than
5 calendar days after detection.  Repair shall be completed no later
than 15 calendar days after the emissions are detected or the visible
defect is observed  (40CFR61.349(f-g)).

Requirements for tank controls and inspection.

(1)	Tanks T101-T106, T111, and T146 shall be equipped and controlled as
required by 40 CFR 61.343 in regards to the following:

(i)	Each tank shall be covered by a fixed roof as defined in
40CFR61.343(a)(1) and vented directly through a closed-vent system to a
control device in accordance with 40CFR61.349.

(ii)	The cover and all openings shall be designed to operate with no
detectable emission as indicated by an instrument reading of less than
500 ppmv above background as determined initially and thereafter at
least once per year by the methods specified in 40CFR61.355(h).

(2)	Each fixed-roof, seal, access door and all other openings shall be
checked by visual inspection initially and quarterly thereafter to
ensure that no cracks or gaps occur and that access doors and other
openings are closed and gasketed properly  (40CFR61.343(c)).

(g)	The following monitoring must be done for the control devices:

(1)	The kiln must be equipped with a monitoring device equipped with a
continuous recorder to measure a parameter that indicates good
combustion operating practices are being used.

(2)	The owner or operator may replace the carbon in the carbon
adsorption system with fresh carbon at a regular predetermined time
interval that is less than the carbon replacement interval that is
determined by the maximum design flow rate and either the organic
concentration or the benzene concentration in the gas stream vented to
the carbon adsorption system (40CFR61.354(c)(7))).

Owners or operators using a closed-vent system that contains any bypass
line that could divert a vent stream from a control device shall:

(1)	Visually inspect the bypass line valve at least once every month,
checking the position of the valve and the condition of the car-seal or
closure mechanism required under 40CFR61.349(a)(1)(ii) to ensure that
the valve is maintained in the closed position and the vent stream is
not diverted through the bypass line. Records of these activities and
any action taken shall be made and maintained on-site for a period of at
least five (5) years.  These records shall be made available to a
Department representative upon request.  Quarterly reports including all
recorded parameters and calculated values shall be submitted to the
Manager of the Technical Management Section, Bureau of Air Quality
postmarked no later than 30 calendar days after the end of the reporting
period.

(2)	Visually inspect the readings from each flow monitoring device
required by 40CFR61.349(a)(1)(ii) at least once each operating day to
check that vapors are being routed to the control device as required.
Records of these activities and any action taken shall be made and
maintained on-site for a period of at least five (5) years.  These
records shall be made available to a Department representative upon
request.  Quarterly reports including all recorded parameters and
calculated values shall be submitted to the Manager of the Technical
Management Section, Bureau of Air Quality postmarked no later than 30
calendar days after the end of the reporting period.

An owner or operator shall maintain a record for each visual inspection
required by 61.343 through 61.347 of this subpart that identifies a
problem (such as a broken seal, gap or other problem) which could result
in benzene emissions. The record shall include the date of the
inspection, waste management unit and control equipment location where
the problem is identified, a description of the problem, a description
of the corrective action taken, and the date the corrective action was
completed (40CFR61.356(g)).  These records shall be maintained on-site
for a period of at least five (5) years.  These records shall be made
available to a Department representative upon request.  Quarterly
reports including all recorded parameters and calculated values shall be
submitted to the Manager of the Technical Management Section, Bureau of
Air Quality postmarked no later than 30 calendar days after the end of
the reporting period.

 An owner or operator shall maintain a record for each test of no
detectable emissions required by 61.343 through 61.347 and 61.349 of
this subpart. The record shall include the following information: date
the test is performed, background level measured during test, and
maximum concentration indicated by the instrument reading measured for
each potential leak interface. If detectable emissions are measured at a
leak interface, then the record shall also include the waste management
unit, control equipment, and leak interface location where detectable
emissions were measured, a description of the problem, a description of
the corrective action taken, and the date the corrective action was
completed.

For each control device, the owner or operator shall maintain
documentation that includes the following information regarding the
control device operation (40 CFR 61.356(j)):

(1)	Dates of startup and shutdown of the closed-vent system and control
device;

(2)	A description of the operating parameter to be monitored to ensure
that the control device will be operated in conformance with these
standards and the control device’s design specification, and an
explanation of the criteria used for selection of that parameter.  This
documentation shall be kept for the life of the control device.

(3)	Periods when the closed-vent system and control device are not
operated as designed including all periods and the duration when: Any
valve car-seal or closure mechanism is broken or the by-pass line valve
position has changed, or the flow monitoring devices indicate that
vapors are not routed to the control device as required.

(4)	For the kiln (as a control device), records of each occurrence when
there is a change in the location at which the vent stream is introduced
into the flame zone and continuous records of the parameter monitored in
accordance with the requirements of 40 CFR 61.354(c)(5)).

(5)	If a carbon adsorber that is not regenerated directly on site in the
control device is used, then the owner or operator shall maintain
records of dates and times when the control device is monitored, when
breakthrough is measured, and shall record the date and time then the
existing carbon in the control device is replaced with fresh carbon.

(l)	The permittee shall perform a visual inspection on a semi-annual
basis.  Visual Inspection means a qualitative observation of opacity
during daylight hours where the inspector records results in a log,
noting color, duration, density (heavy or light), cause and corrective
action taken for any abnormal emissions.  The observer does not need to
be certified to conduct valid visual inspections.  However, at a
minimum, the observer should be trained and knowledgeable about the
effects on visibility of emissions caused by background contrast,
ambient lighting, observer position relative to lighting, wind, and the
presence of uncombined water.  Logs shall be kept to record all visual
inspections, including cause and corrective action taken for any
abnormal emissions and visual inspections from date of recording.  The
logs shall be maintained for a period of five (5) years and be made
available to the Department upon request.  The owner/operator shall
submit semi-annual reports to the Manager of the Technical Management
Section, Bureau of Air Quality postmarked no later than 30 calendar days
after the end of the reporting period.

(m)	The facility is subject to the following operational requirements
for the NHWDF tanks:

(1)	Records of NHWDF Storage Tank Dimensions and Capacity
(40CFR60.116b(b)) The facility shall keep on-site and on-file for each
NHWDF Storage Tank a record showing the dimension of each tank and an
analysis showing the capacity of each tank. These records shall be kept
on-site and on-file for the life of each tank and shall be made
available to Department personnel upon request.

6.B.9 PERFORMANCE TESTING

The owner or operator of the kiln system shall demonstrate initial
compliance with the emission limits using the test methods and
procedures listed in 40CFR63.7.  Performance test results shall be
documented in complete test report that contain the information required
by 40CFR63.7, 40CFR63, Subpart EEE, as well as all other relevant
information.  The plan to be followed during testing shall be made
available to the Bureau 60 days prior to testing as required by SC
Regulation 61-62.1 Section IV - Source Testing.

The facility shall submit a source test protocol in compliance with the
appropriate federal regulations and also SC Regulations 61-62.1, Section
IV – Source Tests.  All performance testing shall be in compliance
with this regulation.

The owner or operator shall demonstrate initial compliance and then
every five years with the affected source opacity limit by conducting a
test in accordance with Method 9.  The performance test 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 maximum six-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 following apply:  1.  There are no individual readings greater
than 10 percent opacity.  2.  There are no more than three readings of
10 percent for the first 1-hour period.

(1)	Comprehensive kiln particulate matter, opacity, DRE, Hg, semi-and
low volatile metals, HCl and Cl gas, and maximum combustion chamber
pressure performance tests required above shall be repeated every five
years, except that the owner or operator of an in-line kiln/raw mill is
not required to repeat the initial performance test of opacity for the
in-line kiln/raw mill.  Confirmatory D/F performance tests shall be
repeated every 30 months (40CFR63.1207(b)(2)(i), 40CFR63.1207(d)).

(2)	The owner or operator is required to repeat the performance tests
for the in-line kiln/raw mills within 90 days of initiating any
significant change in the feed or fuel from that used in the previous
performance test.

(3)	A source test for VOC emissions from the kiln system will be
required.  The tests shall be performed within 60 days after achieving
maximum production but not later than 180 days after initial start-up of
burning HWDF.  The Bureau must be notified at least two weeks prior to
any source test so that a Bureau representative may be present.  This
testing shall then hereafter be done with the comprehensive and
confirmatory testing required by 40CFR63, Subpart EEE.  The testing
shall be done at least every 30 months.  Source test methodology must be
approved by the Bureau and comply with SC Regulation 62.1, Section IV,
Source testing.

(4)	Since the coal mill uses a part of the kiln exhaust stream,
emissions from the coal mill must also be included in the above
performance testing.

Performance test to demonstrate initial compliance shall be conducted as
specified below and in compliance with all requirements of 40CFR63,
Interim Subpart EEE:

Performance testing must be conducted when the raw mill is on-line and
when the mill is off-line to demonstrate compliance with the emission
standards, and separate operating parameters shall be established as
required by 40 CFR § 63.1209 for each mode of operation.  Each time the
mode of operation is changed to an alternative mode with different
operating parameter limits the change must be documented.  When the mode
of operation changes, the permittee must establish rolling averages for
the operating parameter limits based on one of the following methods: 1.
Retrieval Approach, 2. Start Anew, or 3. Seamless Transition (40 CFR §
63.1204(d)(1); 40 CFR § 63.1209(q)(1)).

Comprehensive performance testing must be done to demonstrate compliance
with the emission limitations, establish limits for the operating
parameters required by 40 CFR § 63.1209, and to demonstrate compliance
with the performance specifications for continuous monitoring systems.
This testing will be done in compliance with 40 CFR § 63.1207.  The
initial comprehensive performance test must commence within 180 days of
startup of HWDF.  The comprehensive performance test must commence no
later than 61 months after the date of commencing the previous
comprehensive performance test.  A notification of your intention to
conduct a comprehensive performance test and CMS performance evaluation
and a site-specific test plan and CMS performance evaluation plan must
be submitted at least one year before the performance test and
performance evaluation are scheduled to begin.  The required content of
the comprehensive performance test plan is listed in 40 CFR §
63.1207(f)(1).

For sources subject to the Portland Cement MACT (40CFR63 Subpart LLL),
the owner or operator shall demonstrate initial compliance and then
every five years with the affected source opacity limit by conducting a
test in accordance with Method 9.  The performance test 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 maximum six-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 following apply: 1.  There are no individual readings greater
than 10 percent opacity.  2.  There are no more than three readings of
10 percent for the first 1-hour period.

Within 60 days after achieving the maximum production rate at which the
affected facility will be operated, but no later than 180 days after
initial startup of burning HWDF a performance test shall be conducted
for the coal mill system.  The source test shall be conducted in
compliance with both 40CFR60 and SC Regulation 62.1, Section IV - Source
Tests.

The facility shall submit a site-specific test plan in compliance with
the appropriate federal regulations and also SC Regulations 61-62.1,
Section IV – Source Tests.  All performance testing shall be in
compliance with this regulation.  A copy of the comprehensive test plan
shall be submitted to the Source Evaluation Section.

(part 7 updated 5/14/03)

PART 7.0	ADDITIONAL CONDITIONS

A.	SPECIFIC CONDITIONS

Operator Training and Certification

(EFFECTIVE September 30, 2003, 40CFR63.1206(c)(6)) Prior to start-up of
burning HWDF, the Permittee shall establish training programs for all
categories of personnel whose activities may reasonably be expected to
directly affect emissions of hazardous air pollutants from the
source(s).  Such persons include, but are not limited to, chief facility
operators, control room operators, continuous monitoring system
operators, persons that sample and analyze feedstreams, persons that
manage and charge feedstreams to the combustor (kiln), persons that
operate emission control devices, and ash and waste handlers.  Each
training program shall be of a technical level commensurate with the
person's job duties specified in the training manual.  Each commensurate
training program shall require an examination to be administered by the
instructor at the end of the training course.  Passing of this test
shall be deemed the “certification” for personnel.  The Permittee
shall ensure that a source is operated and maintained at all times by
persons who are trained and certified to perform these and any other
duties that may affect emissions of hazardous air pollutants.  Since the
Permittee operates hazardous waste burning cement kilns, the training
and certification program may be reviewed by the Department and be
complete, reliable and conform to principles of good operator and
operating practices (including training and certification).  The
operator training and certification program shall be recorded in the
facility operating record.

B.	OPERATIONAL FLEXIBILITY [SC Regulation 61-62.70.7(e)(5)]

The permittee seeks operational flexibility to operate in one or more of
the following scenarios:

The permittee has developed a startup, shutdown, and malfunction plan
(SSMP) pursuant to 40 CFR 63, Subpart A.  During periods of startup,
shutdown, or malfunction, the permittee will follow the procedures set
forth in the SSMP.  No hazardous waste will be burned during periods of
startup or shutdown.

The primary operating mode for control of VOC emissions from T-111 is
treatment in the industrial furnace (K300A).  During periods of startup,
shutdown, or malfunction, VOC emissions from T-111 will be controlled by
a carbon adsorption device (VRU112).

The primary operating mode for the industrial furnace (K300A) is burning
hazardous waste for energy recovery pursuant to 40 CFR 63, Subpart EEE.
During periods when the unit is not burning hazardous waste and the
hazardous waste residence time has expired, limits imposed by Subpart
EEE (THC limit on emissions in the bypass (K300B), kiln differential
pressure, 40 CFR63 Subpart EEE metal limits, and the minimum combustion
chamber temperature) will no longer be applicable or required.

The Permittee will develop a Transition Plan (Plan) and submit the Plan
to the Department for review and comment prior to operation of the new
kiln system.  This Plan will address how the Holly Hill Plant plans to
operate the facility during the time period when the portions of the
existing plant equipment, including the two wet kilns, are being shut
down; and the new portions of the plant, including the new
preheater/precalciner kiln system, new coal mill, and new Finish Mills 5
and 6 are being brought online.

C.	COMPLIANCE SCHEDULE [SC Regulation 61-62.70.5(c)(8)]

Not applicable at this time.

D.	PERMIT SHIELD [SC Regulation 61-62.70.6(f)]  (Revised 11/13/98)

A copy of the “applicability determination” Holcim submitted with
its Part 70 permit application is included as Attachment C.  Compliance
with the terms and conditions of this permit shall be deemed compliance
with any applicable requirements as of the date of permit issuance.  The
permittee shall also be shielded from any non-applicable requirements as
agreed upon by the Department as specified in Attachment C with the
exception of the following.

SC Regulation 61-62.5, Standard No. 7

Nothing in the permit shield or in any Part 70 permit shall alter or
affect the provisions of Section 303 of the Act, Emergency Orders, of
the Clean Air Act; the liability of the permittee for any violation of
applicable requirements prior to or at the time of permit issuance; the
applicable requirements of the Acid Rain Program, consistent with
Section 408(a) of the Clean Air Act; or the ability of EPA to obtain
information from a source pursuant to Section 114 of the Clean Air Act.
In addition, the permit shield shall not apply to emission units in
noncompliance at the time of permit issuance, minor permit modifications
(SC Regulation 61-62.70.7(e)(2)), group processing of minor permit
modifications (SC Regulation 61-62.70.7(e)(3)), or operational
flexibility (SC Regulation 61-62.70.7(e)(5)), except as specified in SC
Regulation 61-62.70.7(e)(5)(iii).

(part 8 updated 5/14/03)

PART 8.0	EMISSION UNIT REQUIREMENTS – EXISTING FACILITY

A.	EMISSION UNIT DESCRIPTION

Table 8.1 is a description of emission units located at this facility.

TABLE 8.1 EMISSION UNITS

Unit ID	Unit Description	Control Device Description

08	VOID - Raw Material Processing	--

09	VOID - Kiln System	VOID - ESP (Kilns), Baghouses (CKD Tanks)

10	VOID - Clinker Cooling and Handling, Coal Handling, Cement Kiln Dust
(CKD) Handling	VOID - Baghouses

11	VOID - Marl Dryer	VOID - Baghouse

12	VOID - Finish Mill System	VOID - Baghouses

13	VOID - Lime Handling	VOID - Baghouse

14	VOID - Off Spec Cement Handling and Storage	VOID - Baghouses

15	VOID - Bagging Operations	VOID - Baghouses

16	VOID - Scales	VOID - Baghouses

17	VOID - Tanks, HWDF Delivery System	VOID - Carbon Adsorption System
(HWDF tanks only)

NAAQS EMISSION RATES (New Plant)

STACK	Modeled Emission Rates (lbs/hr)

	TSP	PM10	SO2	NOX	CO

Kiln (S94)	59.9*	53.9*	854.1*	1141	4768

Coal Mill (S95)	2.7*	2.3*	61.9*	118	524

	*  These emissions were not modeled due to these emissions decreasing
at the facility.

CLASS II PREVENTION OF SIGNIFICANT DETERIORATION - STANDARD 7 (New
Plant)

STACK	Modeled Emission Rates (lbs/hr)

	PM10	SO2	NOX

Kiln (S94)	53.9*	854.1*	1141

Coal Mill (S95)	2.3*	61.9*	118

NAAQS EMISSION RATES, Existing Plant

Source Identification	TSP

(LBS/HR)	PM10

(LBS/HR)	SO2

(LBS/HR)	NO2

(LBS/HR)	CO

(LBS/HR)	HF

(LBS/HR)

(01) Dust Tank	0.0127	0.107	-	-	-	-

(02) Dust Tank Load Spout	0.0114	0.0096	-	-	-	-

(03) Dust Tank	0.0127	0.0107	-	-	-	-

(04) Dust Tank Load Spout	0.0114	0.0096	-	-	-	-

(05) #1 Kiln Clinker Cooler	3.27	2.742	-	-	-	-

(06) #2 Kiln Clinker Cooler	10.20	8.571	-	-	-	-

(07) B’Drag Chain – West	0.00135	0.00019	-	-	-	-

(07R) Clinker Elevator #1	0.43	.43	-	-	-	-

(08) B’Drag Chain – Middle	0.00135	0.00019	-	-	-	-

(08R) Clinker Elevator #2	0.43	0.43	-	-	-	-

(09) B’Drag Chane – East	0.00135	0.00019	-	-	-	-

(09R) Clinker Elevator #3	0.43	0.43	-	-	-	-

(10) A’Drag Chain – West	0.00135	0.00019	-	-	-	-

(10R) Clinker Elevator #4	0.43	0.43	-	-	-	-

(11) A’Drag Chain – Middle	0.00135	0.00019	-	-	-	-

(11R) A Drag Conveyor	0.17	0.17	-	-	-	-

(12) A’Drag Chain – East	0.00135	0.00019	-	-	-	-

(12R) B Drag Conveyor	0.17	0.17	-	-	-	-

(13) Cpmmpn Conveyor	0.00136	0.00114	-	-	-	-

(13R) Common Drag Conveyor	0.40	0.4	-	-	-	-

(14) Pan Conveyor – North	0.00136	0.00114	-	-	-	-

(14R) Clinker Silo #1	0.17	0.17	-	-	-	-

(15) Pan Conveyor – South	0.00136	0.00114	-	-	-	-

(15R) Pan Conveyor Discharge	0.29	0.29	-	-	-	-

(16) Dome Reclaim Feeder A*	See B1	See B1	-	-	-	-

(17) Dome Reclaim Feeder B*	See B1	See B1	-	-	-	-

(18) Dome Reclaim Feeder C*	See B1	See B1	-	-	-	-

(19) Dome Reclaim Feeder D*	See B1	See B1	-	-	-	-

(20) Dome Reclaim Feeder E*	See B1	See B1	-	-	-	-

(21) Dome Reclaim Feeder F*	See B1	See B1	-	-	-	-

(22) Clinker Reclaim Stamler	0.0180	0.01508	-	-	-	-

(24) Head, Dome Reclaim Belt*	See B1	See B1	-	-	-	-

(33) Carbon Dust Tank	0.0203	0.0170	-	-	-	-

(34) Carbon Feeder D. C.	0.000117	0.000098	-	-	-	-

(35) Coal Silo - East	00.54	0.00452	-	-	-	-

(36) Coal Silo - WEst	0.0054	0.00452	-	-	-	-

(37) #1 FM Main D. C. N.	1.08	0.905	-	-	-	-

(38) #1 FM Main D. C. S.	1.08	0.905	-	-	-	-

(39) #1 FM Incline Belt	0.00048	0.00040	-	-	-	-

(40) #1 FM Clk Feeder #2 (East)	0.000225	0.00019	-	-	-	-

(41) #1 FM Clk Feeder #1 (West)	0.000225	0.00019	-	-	-	-

(42) #1 FM Gyp Weigh Belt**	See B41 – 44	See B41 – 44	-	-	-	-

(42A) #1 FM Gyp Apron Feeder**	See B41 – 44	See B41 – 44	-	-	-	-

(43) #2 FM Main D. C.	1.68	1.4127	-	-	-	-

(44) #2 FM Clk Belt D. C.	0.000470	0.000395	-	-	-	-

(45) #2 FM Incline Belt D. C.	0.000470	0.000395	-	-	-	-

(46) #2 FM Gyp Apron Feeder D. C.**	See B41 – 44	See B41 – 44	-	-	-
-

(47) #2 FM Gyp Weigh Belt D. C.**	See B41 – 44	See B41 – 44	-	-	-	-

(48) #3 FM Main D. C.	3.36	2.82	-	-	-	-

(49) #3 FM Coll. Belt - East	0.00047	0.000395	-	-	-	-

(50) #3 FM Coll. Belt - Middle	0.00047	0.000395	-	-	-	-

(51) #3 FM Coll. Belt - West	0.00094	0.00079	-	-	-	-

(52) #3 FM Gyp Weigh Feeder	0.00006	0.00005	-	-	-	-

(53) #3 FM Gyp Apron Feeder**	See B41 – 44	See B41 – 44	-	-	-	-

(54) #4 FM Main D. C. 	1.98	1.667	-	-	-	-

(55) #4 FM Classifier	1.98	1.667	-	-	-	-

(56) #4 FM Fines Airslide D. C.	0.0264	0.0222	-	-	-	-

(57) #4 FM Coll. Belt D. C.**	See B41 – 44	See B41 – 44	-	-	-	-

(58) #4 Gyp Weigh Belt D. C.**	See B41 – 44	See B41 – 44	-	-	-	-

(59) #4 FM Clk Weigh Belt D. C.**	See B41 – 44	See B41 – 44	-	-	-	-

(60) D/Marl D. C.	3.33	2.80	62.86	11.01	1.0	-

(61) Lime Tank D. C.	0.00675	0.00567	-	-	-	-

(62) Off Spec Silo D. C.	0.000162	0.000136	-	-	-	-

(63) #1 Load Scale D. C.	0.0557	0.0468	-	-	-	-

(64) #2 Load Scale D. C.***	See B51 – 54	See B51 – 54	-	-	-	-

(65) #3 Load Scale D. C.***	See B51 – 54	See B51 – 54	-	-	-	-

(66) #4 Load Scale D. C.	0.0557	0.0468	-	-	-	-

(67) Cement Bagging	0.0160	0.0135	-	-	-	-

(68) Mortar Bagging	0.0160	0.0135	-	-	-	-

(69) #3 FM D. C. Top of Silos	0.0324	0.0272	-	-	-	-

(70) #4 FM D. C. Top of Silos	0.0297	0.0249	-	-	-	-

(71) #1 FM D. C. Top of Silos	0.0162	0.0136	-	-	-	-

(72) #2 FM D. C. Top of Silos	0.0162	0.0136	-	-	-	-

(73) Dribble Bin D. C. - North****	0.000081	0.000068	-	-	-	-

(74) Dribble Bin D. C. - South****	See 74	See 74	-	-	-	-

(76) #2 Clinker Silo D. C.**	See B41 – 44	See B41 – 44	-	-	-	-

(78) #4 Clinker Silo D. C.**	See B41 – 44	See B41 – 44	-	-	-	-

(81) #1 Kiln ESP	40.00	34.00	478-.48	431.83	218.74	0.055

(82) #2 Kiln ESP	54.6	46.43	1493.73	1348.02	422.65	0.172

(83) Reclaim Elevator, East/West Reclaim Belt, #4 Clinker Silo Conveyor,
and #4 Clinker Silo	0.0460	0.0387	-	-	-	-

(84) East Reclaim Belt	0.0232	0.00194	-	-	-	-

(B1) Dome Reclaim Feeders (S16, S17, S18, S19, S20, S21, S24)	0.00578
0.00484	-	-	-	-

(B41) Sources grouped together (S42, S42A, S46, S47, S53, S57, S58, S59,
S76, S78) 	0.00213	0.00164	-	-	-	-

(B42) Sources grouped together (S42, S42A, S46, S47, S53, S57, S58, S59,
S76, S78)	0.00213	0.00164	-	-	-	-

(B43) Sources grouped together (S42, S42A, S46, S47, S53, S57, S58, S59,
S76, S78)	0.00213	0.00164	-	-	-	-

(B44) Sources grouped together (S42, S42A, S46, S47, S53, S57, S58, S59,
S76, S78)	0.00213	0.00164	-	-	-	-

(B51) Nos. 2 and 3 Load Scale D. C. (S64, S65)	0.01265	0.01063	-	-	-	-

(B52) Nos. 2 and 3 Load Scale D. C. (S64, S65)	0.01265	0.01063	-	-	-	-

(B53) Nos. 2 and 3 Load Scale D. C. (S64, S65)	0.01265	0.01063	-	-	-	-

(B54) Nos. 2 and 3 Load Scale D. C. (S64, S65)	0.01265	0.01063	-	-	-	-

(RAI) Rainbow Sources	0.72	0.600	-	-	-	-

(S85) Pneumatic Transfer System	0.58	0.58	-	-	-	-

(S86) Top of Dome	1.03	1.03	-	-	-	-

(S87) Top of Dome	0.59	0.59	-	-	-	-

(S88) Reclaim Belt Discharge/Bucket Elevator	0.37	0.37	-	-	-	-

(S89) Top of 450 Metric Ton Surge Bin	0.17	0.17	-	-	-	-

(S90) Located Above Truck Loading Spout #1	0.15	0.15	-	-	-	-

(S91) Located Above Truck Loading Spout #2	0.15	0.15	-	-	-	-

(U09) Transfer Point: 450' Belt to Hopper / Tripper Belt	2.83	1.40	-	-	-
-

(U10) Transfer Point: Radial Stacker to Pile	1.43	0.492	-	-	-	-

(U11) Transfer Point: Front End Loader to Reclaim Hopper	1.43	0.492	-	-
-	-

(U12) Transfer Points: Marl Hopper to Pan Feeder to Collector Belt to
Incline Plane	0.342	0.175	-	-	-	-

(U13) Transfer Point: Sand Bin to Weigh Feeder to Collector Belt	0.3046
0.155	-	-	-	-

(U14) Transfer Points: Iron Ore Bin to Weigh Feeder to Collector Belt
0.00161	0.000817	-	-	-	-

(U15) Transfer Point: Collector Belt to Collector Belt	0.01611	0.00817	-
-	-	-

(U16) Transfer Point: Collector Belt to Incline Belt	0.07934	0.04087	-	-
-	-

(U18) Transfer Point: Feeder to Inclined Belt	0.00095	0.00084	-	-	-	-

(U19) Transfer Point: Dry Marl Tank to Weigh Feeder	0.00095	0.00084	-	-
-	-

(U20) Transfer Point: Dribble Bin to Inclined Belt	0.00095	0.00084	-	-	-
-

(U22) Transfer Point: Lime Tank to Weigh Feeder	0.00095	0.00084	-	-	-	-

(U24) Transfer Point: Drag Chain to Dust Chute	0.500	0.425	-	-	-	-

(U25) Transfer Point: Drag Conveyor to Dust Chute	0.500	0.425	-	-	-	-

	* These stacks are grouped in 1 stack named B1

** These stacks are grouped and divided equally among four stacks
labeled as volume sources B41, B42, B43, B44

*** These stacks are grouped and divided equally among four stacks
labeled as point sources B51, B52, B53, B54

**** These stacks are grouped in 1 stack labeled as point source
73(Attachment B updated 5/14/03)

The following table contains a list of activities which are considered
insignificant pursuant to South Carolina Regulation 61-62.70.5(c).
Sources listed below are not exempt from any otherwise applicable state
or federal requirements including, but not limited to, opacity
standards, ambient air quality standards, and air toxic standards.

TABLE 1. INSIGNIFICANT QUARRY EQUIPMENT

Equipment Description	Unit ID	Design

Capacity

(tpy)	Equipment

Manufacture

Date	De Minimis

Emission Rate	Reason(s)

Insignificant

Clay Overburden Bulldozing	NP1	1,931,230	2003	PM10 Emissions < 5 tpy
PM10 Emissions < 5 tpy

Front End Loader (FEL) to Clay Truck	NP2	1,931,230	2003	PM10 Emissions <
5 tpy	PM10 Emissions < 5 tpy

Clay Truck to Clay Hopper	NP3	1,931,230	2003	PM10 Emissions < 5 tpy	PM10
Emissions < 5 tpy

TABLE 2. INSIGNIFICANT RAW MILL SYSTEM EQUIPMENT

Equipment Description	 Unit

ID	Design

Capacity

(tpy)	Equipment

Manufacture

Date	De Minimis

Emission Rate	Reason(s)

Insignificant

FEL to Iron Ore Hopper	NP33	202,777	2003	PM10 Emissions < 5 tpy	PM10
Emissions < 5 tpy

FEL to Wet Fly Ash Hopper	NP34 a	1,158,730	2003	PM10 Emissions < 5 tpy
PM10 Emissions < 5 tpy

FEL to Wet Fly Ash Hopper	NP34b	1,158,730	2003	PM10 Emissions < 5 tpy
PM10 Emissions < 5 tpy

Truck to Iron Ore Pile	NP30	51,416	2003	PM10 Emissions < 5 tpy	PM10
Emissions < 5 tpy

Truck to Fly Ash Pile #1	NP31	170,871	2003	PM10 Emissions < 5 tpy	PM10
Emissions < 5 tpy

Marl Stockpile	P3	40,785	N/A	PM10 Emissions < 5 tpy	PM10 Emissions < 5
tpy

Clay Stockpile	P5	11,905	N/A	PM10 Emissions < 5 tpy	PM10 Emissions < 5
tpy

Fly Ash Stockpile	P6, P7	7,716	N/A	PM10 Emissions < 5 tpy	PM10 Emissions
< 5 tpy

Iron Ore Stockpile	P8, P9	3,473	N/A	PM10 Emissions < 5 tpy	PM10
Emissions < 5 tpy

FEL to Clay Crusher	NP132	3,473	2003	PM10 Emissions < 5 tpy	PM10
Emissions < 5 tpy

FEL to Iron Ore Hopper	NP133	23,150	2003	PM10 Emissions < 5 tpy	PM10
Emissions < 5 tpy

TABLE 3. INSIGNIFICANT COAL MILL SYSTEM EQUIPMENT

Equipment Description	 Unit ID	Design

Capacity

(tpy)	Equipment

Manufacture

Date	De Minimis

Emission Rate	Reason(s)

Insignificant

Coal/SVF Pile#1	P2	27,558	N/A	PM10 Emissions < 5 tpy	PM10 Emissions < 5
tpy

FEL to Coal Hopper	NP60	402,347	2003	PM10 Emissions < 5 tpy	PM10
Emissions < 5 tpy

Coal/SVF Pile#2	P12	27,558	N/A	PM10 Emissions < 5 tpy	PM10 Emissions < 5
tpy

TABLE 4. INSIGNIFICANT KILN SYSTEM EQUIPMENT

Equipment Description	Unit ID	Design

Capacity

(tpy)	Equipment

Manufacture

Date	De Minimis

Emission Rate	Reason(s)

Insignificant

Truck to Tire Chip Pile	NP53	32,836	2003	PM10 Emissions < 5 tpy	PM10
Emissions < 5 tpy

Front End Loader to Tire Hopper	NP54	29,959	2003	PM10 Emissions < 5 tpy
PM10 Emissions < 5 tpy

Tire Chip Stockpile	P10	276	N/A	PM10 Emissions < 5 tpy	PM10 Emissions <
5 tpy

Tire Hopper, Conveyor, Tire Elevator	NP55, NP56, NP92	29,959	2003	PM10
Emissions < 5 tpy	PM10 Emissions < 5 tpy

TABLE 5. INSIGNIFICANT FINISH MILL SYSTEM EQUIPMENT

Equipment Description	 Unit

ID	Design

Capacity

(tph)	Equipment

Manufacture

Date	De Minimis

Emission Rate	Reason(s)

Insignificant

Truck to Syn. Gypsum/Pigment/

Slag Hopper	NP71a

NP71b

NP71c	965,615

965,615

965,615	2003	PM10 Emissions < 5 tpy	PM10 Emissions < 5 tpy

Sugar Truck to Silo	NP73	9,636	2003	PM10 Emissions < 5 tpy	PM10
Emissions < 5 tpy

Truck to Wet Slag Pile	NP76	93,588	2003	PM10 Emissions < 5 tpy	PM10
Emissions < 5 tpy

Truck to Syn. Gypsum Pile	NP77	93,588	2003	PM10 Emissions < 5 tpy	PM10
Emissions < 5 tpy

Front End Loader to Slag/Syn. Gypsum Hopper	NP78a

NP78b	276,133

276,133	2003	PM10 Emissions < 5 tpy	PM10 Emissions < 5 tpy

Synthetic Gypsum Stockpile	P1, P14	4,960	N/A	PM10 Emissions < 5 tpy	PM10
Emissions < 5 tpy

Slag Stockpile	P4, P15	4,740	N/A	PM10 Emissions < 5 tpy	PM10 Emissions <
5 tpy

Truck to Calcium Fluoride Pile	NP130	5,986,772	2003	PM10 Emissions < 5
tpy	PM10 Emissions < 5 tpy

Truck to Mill Scale Pile	NP131	23,150	2003	PM10 Emissions < 5 tpy	PM10
Emissions < 5 tpy

Natural Gypsum Stockpile	P13	16,535	N/A	PM10 Emissions < 5 tpy	PM10
Emissions < 5 tpy

Clay Overburden Pile	P16	110,230	N/A	PM10 Emissions < 5 tpy	PM10
Emissions < 5 tpy

Calcium Fluoride Stockpile	P17	5,512	N/A	PM10 Emissions < 5 tpy	PM10
Emissions < 5 tpy

Mill Scale Stockpile	P18	27,558	N/A	PM10 Emissions < 5 tpy	PM10
Emissions < 5 tpy

Pigment Stockpile	P11	1,323	N/A	PM10 Emissions < 5 tpy	PM10 Emissions <
5 tpy

TABLE 6. INSIGNIFICANT TANK EQUIPMENT

Equipment Description	 Unit

ID	Design

Capacity

(gal)	Equipment

Manufacture

Date	De Minimis

Emission Rate	Reason(s)

Insignificant

Diesel Fuel Storage Tank	S112	500	Before 1985	Tank size < 10,000 gal
Tank is insignificant based on size.

Quarry Gasoline Tank	S139	2,000	Before 1985	Tank size < 10,000 gal	Tank
is insignificant based on tank size.

FM#5 & #6 Grinding Aid Tank	S140	9,988	2003	Tank size < 10,000 gal	Tank
is insignificant based on tank size.

FM #4 Grinding Aid Tank	S141	9,789	Before 1978	VOC Emissions < 5 tpy and
HAP emissions < 1,000 lb/yr	VOC emissions < 5 tpy and individual HAP
emissions < 1,000 lb/yr

FM #4 Air Entraining Tank	S142	9,988	Before 1978	VOC Emissions < 5 tpy
and HAP emissions < 1,000 lb/yr	VOC emissions < 5 tpy and individual HAP
emissions < 1,000 lb/yr

FM #4 Tall Oil Storage Tank	S148	9,988	Before 1978	VOC Emissions < 5 tpy
and HAP emissions < 1,000 lb/yr	VOC emissions < 5 tpy and individual HAP
emissions < 1,000 lb/yr

Hydraulic Oil Storage Tank	S150	1,000	1998	Tank Size < 10,000 gal	Tank
is insignificant based on tank size

Motor Oil Storage Tank	S151	1,000	1998	Tank Size < 10,000 gal	Tank is
insignificant based on tank size

Gear Oil Storage Tank	S152	1,000	1998	Tank Size < 10,000 gal	Tank is
insignificant based on tank size.

Used Oil Storage Tank	S153	1,000	1998	Tank Size < 10,000 gal	Tank is
insignificant based on tank size.

Heating Oil Storage Tank	S154	500	1998	Tank Size < 10,000 gal	Tank is
insignificant based on tank size.

Transmission Oil Storage Tank	S155	1,000	1998	Tank Size < 10,000 gal
Tank is insignificant based on tank size

Heating Oil Storage Tank	S156	1,000	1998	Tank Size < 10,000 gal	Tank is
insignificant based on tank size

Used Oil Storage Tank	S157	500	Before 1980	Tank Size < 10,000 gal	Tank
is insignificant based on tank size

Heating Oil Storage Tank	S158	500	Before 1980	Tank Size < 10,000 gal
Tank is insignificant based on tank size

Motor Oil Storage Tank	S159	500	Before 1980	Tank Size < 10,000 gal	Tank
is insignificant based on tank size

Used Oil Storage Tank	S160	500	Before 1980	Tank Size < 10,000 gal	Tank
is insignificant based on tank size

Hydraulic Oil Storage Tank	S161	500	Before 1980	Tank Size < 10,000 gal
Tank is insignificant based on tank size

Diesel Fuel Storage Tank	S162	200	1965	Tank Size < 10,000 gal	Tank is
insignificant based on tank size

Diesel Fuel Storage Tank	S163	200	1974	Tank Size < 10,000 gal	Tank is
insignificant based on tank size

Drum Storage - Various Oils	S166	<10,000	Before 1989	Tank Size < 10,000
gal	Tank is insignificant based on tank size

Drum Storage - Various Oils	S167	<10,000	Before 1989	Tank Size < 10,000
gal	Tank is insignificant based on tank size

Drum Storage - Various Oils	S168	<10,000	Before 1989	Tank Size < 10,000
gal	Tank is insignificant based on tank size

Container and Drum Storage - Various Oils	S169	<10,000	Before 1989	Tank
Size < 10,000 gal	Tank is insignificant based on tank size

Mobile Oil Storage Tank - Used Oil	S170	250	Before 1989	Tank Size <
10,000 gal	Tank is insignificant based on tank size

Mobile Oil Storage Tank - Diesel Fuel	S171	250	Before 1989	Tank Size <
10,000 gal	Tank is insignificant based on tank size

Mobile Oil Storage Tank - Used Oil	S172	250	Before 1989	Tank Size <
10,000 gal	Tank is insignificant based on tank size

Sulfuric Acid Storage Tank	S173	6,000	1998	Tank Size < 10,000 gal	Tank
is insignificant based on tank size

HWDF Drum Handling and Storage	N/A	11,000	2001	VOC Emissions < 5 tpy	VOC
emissions < 5 tpy

(Attachment C updated 5/14/03)

The following contains the Federal and South Carolina air pollution
regulations, which were specified in the Part 70, permit application and
determined as applicable and non-applicable by the Department as of the
date of this permit issuance.  This attachment may be revised by the
Department in the event of a change in the nature or emission of
pollutants at the source or promulgation of new or revised regulations.

TABLE 1.  STATE REGULATIONS

South Carolina Air Quality Rule	Applicable	Not Applicable	Reason

62.1 Section I - Definitions	X

Definitions for terms used in permitting source

62.1 Section II - Permit Requirements	X

Cement manufacturing equipment is a source of air contaminants

62.1 Section III - Emissions Inventory	X

Facility required to submit annual emissions inventory

62.1 Section IV - Source Tests	X

Is required to be tested

62.2 Prohibition of Open Burning	X

Open burning prohibited at the plant

62.3 Air Pollution Episodes	X

Facility is a major source that can contribute to pollution

62.4 Hazardous Air Pollutant Conditions	X

Cement manufacturing equipment is a source of HAP’s and fugitive dust

62.5 Standard 1

Fuel Burning Operations

X	No sources of indirect heating at the facility

62.5 Standard 2

Ambient Air Quality Standards	X

Cement manufacturing equipment emits criteria pollutants

62.5 Standard 3

Waste Combustion and Reduction	X

Hazardous and Non-Hazardous wastes

are used as kiln fuels

62.5 Standard 3.1

Medical Waste Incineration

X	No medical waste is incinerated at this facility

62.5 Standard 4

Emissions from Process Industries	X

Kilns are specified as subject to this regulation

62.5 Standard 5

Volatile Organic Compounds	X

Burn tanks T111 and T146 are subject to this rule

62.5 Standard 5.1 VOC LAER	X

Net VOC emissions from kiln system > 100 tpy

62.5 Standard 6

Alternative Emission Limitation Options

X	This facility has not requested any alternative emission limitations,

therefore this is not applicable.

62.5 Standard 7

Prevention of Significant Deterioration	X

The change from actual emissions to future potential emissions for some

criteria pollutants is greater than the

PSD threshold.

62.5 Standard 8

Toxic Air Pollutants

X	All affected sources are covered by a MACT regulation

62.6 Section I

Control of Fugitive Particulate Matter

In Non-Attainment Area

X	Plant is located in an attainment area

62.6 Section II

Control of Fugitive Particulate Matter

In Problem Areas

X	Plant is not located in a problem area

62.6 Section III

Control of Fugitive Particulate Matter Statewide	X

Cement manufacturing equipment is a source of fugitive dust

62.7 Good Engineering Practice Stack Height	X

Kilns emit through stacks

62.63 Subparts A, DD, LLL, EEE National Emission Standards

For Hazardous Air Pollutants	X

Plant is a major HAP source

62.68 Chemical Accident Prevention Provisions

X	Liquid hazardous waste fuels are not stored on-site

62.70 Title V Operating Permit Program	X

Facility emissions are greater than thresholds

62.72 Acid Rain Program

X	A cement plant is not a source type listed in “Section III
Applicability”

62.630 Subparts A, Kb, Y and OOO	X

State Regulation

TABLE 2.   FEDERAL REGULATIONS

Federal Rule	Applicable	Not Applicable	Reason

40CFR50

National Ambient Air Quality Standards	X

Facility is a major source that contributes

to air pollution

40CFR51

X	Applies only to states

40CFR52

X	Does not apply to facilities

40CFR53

X	Specifies reference methods and is not an applicable requirement

40CFR54

X	Applies only to citizens’ suits

40CFR55

X	Specifies a requirement not applicable to Holcim’s operations

40CFR56

X	Specifies a requirement not applicable to Holcim’s operations

40CFR57

X	Specifies a requirement not applicable to Holcim’s operations

40CFR58

X	Specifies a requirement not applicable to Holcim’s operations

40CFR60 Subpart A

NSPS General Provisions	X

Plant is applicable to 40CFR60 Subpart Kb, Subpart Y, and Subpart OOO

40CFR60 Subpart B through Subpart Eb

X	This facility is not a source type or does

not have any equipment subject to these regulations

40CFR60 Subpart F

NSPS for Portland Cement Plants

X	Plant complies with PC MACT regulations and is not subject

40CFR60 Subpart G through Subpart J

X	This facility is not a source type or does

not have any equipment subject to these regulations

40CFR60 Subpart K

NSPS for Storage Vessels for Petroleum Liquids

X	Storage tanks do not exceed threshold capacity

40CFR60 Subpart Ka

NSPS for Storage Vessels for Petroleum Liquids

X	Storage tanks do not exceed threshold capacity

40CFR60 Subpart Kb

NSPS for

Volatile Organic Liquid Storage Vessels	X

Various storage tanks exceed threshold capacity

40CFR60 Subpart L through Subpart X

X	This facility is not a source type or does

not have any equipment subject to these regulations

40CFR60 Subpart Y	X

Kiln exhaust is vented through coal mill to “thermally dry” the coal

40CFR60 Subpart Z through Subpart NNN

X	This facility is not a source type or does

not have any equipment subject to these regulations

40CFR60 Subpart OOO	X

The modified facility has its own quarry operations

40CFR60 Subpart PPP through WWW

X	This facility is not a source type or does

not have any equipment subject to these regulations

40CFR61 Subpart A

General Provisions	X

This facility is subject to 40CFR61

Subpart V and FF

40CFR61 Subpart B through Subpart U

X	This facility is not a source type or does

not have any equipment subject to these regulations

40CFR61 Subpart V	X

Hazardous waste fuel delivery system is a source of fugitive VOC
emissions.

40CFR61 Subpart W through Subpart EE

X	This facility is not a source type or does

not have any equipment subject to these regulations

40CFR61 Subpart FF

NESHAP for Benzene Waste Operations	X

Facility receives benzene containing wastes from off-site

40CFR62

X	Specifies a requirement not applicable to Holcim’s operations

40CFR63 Subpart A

General Provisions

X	Specifies a requirement not applicable to Holcim’s operations

40CFR63 Subpart B

Requirements for

Control Technology Determinations

for

Major Sources In Accordance

With Clean Air Act

Sections 112(g) and 112(j)

X	Facility was constructed before effective date of section 112(g)(2)(B)

40CFR63 Subpart C through Subpart Y

X	This facility is not a source type or does

not have any equipment subject to these regulations

40CFR63 Subpart AA through CC

X	This facility is not a source type or does

not have any equipment subject to these regulations

40CFR63 Subpart DD

National Emission Standards

for

Hazardous Air Pollutants

From Off-Site Waste And Recovery Operations	X

The facility is subject to the performance standards of 40 CFR 63
Subpart DD because the facility receives off-site waste and meets the
applicability requirements of this regulation; however, the facility is
not subject to the monitoring, reporting, and record keeping
requirements of 40 CFR 63 Subpart DD because the facility operates in
compliance with 40 CFR 61 Subpart FF

40CFR63 Subpart EE through Subpart YY

X	This facility is not a source type or does

not have any equipment subject to these regulations

40CFR63 Subpart CCC and Subpart DDD

X	This facility is not a source type or does

not have any equipment subject to these regulations

40CFR63 Interim Subpart EEE

National Emission Standards

For

Hazardous Air Pollutants

From Hazardous Waste Combustors	X

The facility uses hazardous waste derived fuel.  The kiln is the only
affected sources

40CFR63 Subpart FFF through Subpart JJJ

X	This facility is not a source type or does

not have any equipment subject to these regulations

40CFR63 Subpart LLL	X

S94 and S95 are not subject to this MACT standard, since they are
subject to 40CFR63 Interim Subpart EEE

40CFR63 Subpart MMM through Subpart XXX

X	This facility is not a source type or does

not have any equipment subject to these regulations

40CFR64

X	Specifies a requirement not applicable to the Holcim (US) Inc.
operations

40CFR65

X	Specifies a requirement not applicable to the Holcim (US) Inc.
operations

40CFR66

X	Specifies a requirement not applicable to the Holcim (US) Inc.
operations

40CFR67

X	Specifies a requirement not applicable to the Holcim (US) Inc.
operations

40CFR68

X	Specifies a requirement not applicable to the Holcim (US) Inc.
operations

40CFR69

X	Specifies a requirement not applicable to the Holcim (US) Inc.
operations

40CFR70	X

Requirement for CAA Title V air permit

for the Holcim (US) Inc. operations

40CFR71

X	Specifies a requirement not applicable to the Holcim (US) Inc.
operations

40CFR72

X	Specifies a requirement not applicable

since Holcim (US) Inc. operations are not subject to acid rain
prohibitions

40CFR73

X	Specifies a requirement not applicable to the Holcim (US) Inc.
operations

40CFR74

X	Specifies a requirement not applicable to the Holcim (US) Inc.
operations

40CFR75

X	Specifies a requirement not applicable

since Holcim (US) Inc. operations are not subject to acid rain
prohibitions

40CFR76

X	Specifies a requirement not applicable

since Holcim (US) Inc. operations are not subject to acid rain
prohibitions

40CFR77

X	Specifies a requirement not applicable

since Holcim (US) Inc. operations are not subject to acid rain
prohibitions

40CFR78

X	Specifies a requirement not applicable

since Holcim (US) Inc. operations are not subject to acid rain
prohibitions

40CFR79

X	Specifies a requirement not applicable

since Holcim (US) Inc. operations are not subject to acid rain
prohibitions

40CFR80

X	Specifies a requirement not applicable

since Holcim (US) Inc. operations are not subject to acid rain
prohibitions

40CFR81

X	Specifies a requirement not applicable to the Holcim (US) Inc.
operations

40CFR82

X	Specifies a requirement not applicable to the Holcim (US) Inc.
operations

40CFR85

X	Specifies a requirement not applicable to the Holcim (US) Inc.
operations

40CFR86

X	Specifies a requirement not applicable to the Holcim (US) Inc.
operations

40CFR87

X	Specifies a requirement not applicable to the Holcim (US) Inc.
operations

40CFR88

X	Specifies a requirement not applicable to the Holcim (US) Inc.
operations

40CFR89

X	Specifies a requirement not applicable to the Holcim (US) Inc.
operations

40CFR93

X	Specifies a requirement not applicable to the Holcim (US) Inc.
operations

VIA CERTIFIED MAIL

April 15, 2003

Holcim (US) Inc. – Holly Hill Plant

200 Safety Street / Highway 453

Holly Hill, South Carolina 29059

ATTENTION:	Glenn Raynor

Dear Mr. Raynor:

Enclosed with this letter is your Part 70 Air Quality (Title V
Operating) Permit No. TV-1860-0005 that will become effective on July 1,
2003.  Please note the conditions and limitations imposed.  This permit
will be valid through June 30, 2008, unless otherwise provided for by SC
Regulation 61-62.70.7(c)(1)(ii).

Please review this permit carefully.  Should you notice any errors or
omissions, notify your permit engineer, Veronica Barringer, of this
office, at<PHONE_NUMBER> or e-mail at<EMAIL_ADDRESS>within 15
days of receipt of this letter.

Sincerely,

Carl W. Richardson, P.E., Director

Engineering Services Division

Bureau of Air Quality

CWR:EAVB:pe

Enclosure

cc:	Mark Hiott, Trident EQC District Office

	Scott Miller, EPA Region IV (via e-mail)

	TV-1860-0005

May 14, 2003

Holcim (US) Inc. – Holly Hill Plant

200 Safety Street / Highway 453

Holly Hill, South Carolina 29059

ATTENTION:	Mr. Glenn Raynor

Dear Mr. Raynor:

Enclosed with this letter is your updated Part 70 Air Quality (Title V
Operating) Permit No. TV-1860-0005.    Please replace page 2, Sections 5
through 10, (pages 16 through 138) and Attachments B and C of your
permit issued April 15, 2003 with these new updated pages.  See page 2
for details of changes made in your permit.  This permit will have the
same expiration as the previous permit.

If there are questions please do not hesitate to contact me at either
(803) 898-4074 or<EMAIL_ADDRESS>
Sincerely,

Kevin J. Clark, P.E.

Engineering Services Division

Bureau of Air Quality

KJC:pe

Enclosure

cc:	Mark Hiott, Trident EQC District Office

	Scott Miller, EPA Region IV (via e-mail)

	TV-1860-0005

September 23, 2003

Holcim (US) Inc. – Holly Hill Plant

200 Safety Street / Highway 453

Holly Hill, South Carolina 29059

ATTENTION:	Mr. Glenn Raynor

Dear  Mr. Raynor:

Enclosed please find Pages 2, 18, and 24 of Title V Operating Permit No.
1860-0005 which will replace Pages 2, 18, and 24 of the Title V
operating permit previously issued April 15, 2003.  These pages reflects
changes made to Table 5.6 for the control device description change
(BH85) and to Table 5.14 for the venting of vapors from the hazardous
waste storage tanks (T111 and T146) to the kiln.

Please do not hesitate to contact the appropriate staff member, Veronica
Barringer at<PHONE_NUMBER>) or e-mail at<EMAIL_ADDRESS>promptly if
you need any further assistance.

Sincerely,

Carl W. Richardson, P.E., Director

Engineering Services Division

Bureau of Air Quality

CWR:EAVB:pe

Enclosure

cc:	Mark Hiott, Trident District EQC Office

Scott Miller, EPA Region IV (via e-mail)

Permit File:  1860-0005

Main File:  1900-0005

October 22, 2003

Holcim (US) Inc. – Holly Hill Plant

200 Safety Street / Highway 453

Holly Hill, South Carolina 29059

ATTENTION:	Mr. Glenn Raynor

Dear Mr. Raynor:

Enclosed please find Pages 2, 19, 20, 21, 22, 23, 24 and 24 of Title V
Operating Permit No. 1860-0005 which will replace Pages 2, 19, 20, 21,
22, 23, 23 and 25 of the Title V operating permit previously issued
April 15, 2003.  These pages reflects the following changes:

R170, R171, R174, R175, R178, R180, R195, R204 has been moved from Table
5.16 and Table 5.9 into Table 5.15 and Table 5.8, to reflect
applicability to NSPS, Subpart OOO and not MACT, Subpart LLL.

R183 and R185 has been moved from Table 5.15 and Table 5.9 into Table
5.16 and Table 5.8, to reflect applicability to MACT, subpart LLL and
not NSPS, Subpart OOO.

Please do not hesitate to contact the appropriate staff member, Veronica
Barringer at<PHONE_NUMBER>) or e-mail at<EMAIL_ADDRESS>promptly if
you need any further assistance.

Sincerely,

Carl W. Richardson, P.E., Director

Engineering Services Division

Bureau of Air Quality

CWR:EAVB:pe

Enclosure

cc:	Mark Hiott, Trident District EQC Office

Scott Miller, EPA Region IV (via e-mail)

Permit File:  1860-0005

Main File:  1900-0005

June 27, 2005

Holcim (US) Inc. – Holly Hill Plant

200 Safety Street / Highway 453

Holly Hill, South Carolina 29059

ATTENTION:	Mr. Glenn Raynor

Dear Mr. Raynor:

Enclosed please find an updated Part 70 Air Quality (Title V Operating)
Permit No. 1860-0005, which will replace the Part 70 Air Quality (Title
V Operating) Permit previously issued October 23, 2003. This updated
permit includes previously issued construction permits 1860-0005-CZ, DA,
DB and DC, the addition of maintenance activities to be perform on the
inlet pressure port without shutting off the HWDF, the voiding out of
all references to the old facility, and the update of condition 4.B.6.
Attachments A, B and C remain the same and will not be re-issued.

Please examine this updated permit carefully for errors or omissions and
notify the appropriate staff member, Veronica Barringer,<PHONE_NUMBER>)
or e-mail at<EMAIL_ADDRESS>promptly if any are discovered.

Sincerely,

Carl W. Richardson, P.E., Director

Engineering Services Division

Bureau of Air Quality

CWR:EAVB:pe

Enclosure

cc:	Mark Hiott, Trident District EQC Office

Scott Miller, EPA Region IV (via e-mail)

Permit File:  1860-0005

Main File:  1860-0005

August 19, 2005

Holcim (US) Inc. – Holly Hill Plant

200 Safety Street / Highway 453

Holly Hill, South Carolina 29059

ATTENTION:	Mr. Glenn Raynor

Dear Mr. Raynor:

Enclosed please find an updated Part 70 Air Quality (Title V Operating)
Permit No. 1860-0005, which will replace the Part 70 Air Quality (Title
V Operating) Permit previously issued June 27, 2005. This updated permit
includes the removal of non-applicable 40 CFR 63, Subpart DD
requirements to the NHWDF storage tanks (ID T-100, T-147, T-148 and
T-149).  Attachments A, B and C remain the same and will not be
re-issued.

Please examine this updated permit carefully for errors or omissions and
notify the appropriate staff member, Veronica Barringer,<PHONE_NUMBER>)
or e-mail at<EMAIL_ADDRESS>promptly if any are discovered.

Sincerely,

Carl W. Richardson, P.E., Director

Engineering Services Division

Bureau of Air Quality

CWR:EAVB:pe

Enclosure

cc:	Mark Hiott, Region 7, Charleston EQC Office

Scott Miller, EPA Region IV (via e-mail)

Permit File:  1860-0005

Main File:  1860-0005

Holcim (US) Inc. – Holly Hill Plant

TV-1860-0005

Page   PAGE  2  of 106

(permit updated 6/27/05 and 8/19/05)

ATTACHMENT A

Modeled Emission Rates

Holcim (US) Inc. – Holly Hill Plant

TV-1860-0005

PAGE   PAGE  3  OF 6

ATTACHMENT B

Insignificant Activities

Holcim (US) Inc. – Holly Hill Plant

TV-1860-0005

PAGE   PAGE  4  OF 5

ATTACHMENT C

Regulatory applicability

Holcim (US) Inc. – Holly Hill Plant

TV-1860-0005

PAGE   PAGE  6  OF 7

ATTACHMENT C