MISSISSIPPI COMMISSION ON ENVIRONMENTAL QUALITY

"AIR EMISSION REGULATIONS FOR THE PREVENTION, ABATEMENT, AND CONTROL OF
AIR CONTAMINANTS"

APC-S-1

Amended December 11, 2008

APC-S-1

TABLE OF CONTENTS

SECTION 1: GENERAL	PAGE 1

SECTION 2: DEFINITIONS	PAGE 1

SECTION 3: SPECIFIC CRITERIA FOR SOURCES OF PARTICULATE MATTER	PAGE 5

SECTION 4: SPECIFIC CRITERIA FOR SOURCES OF SULFUR COMPOUNDS

	PAGE 10

SECTION 5: SPECIFIC CRITERIA FOR SOURCES OF CHEMICAL EMISSIONS

	PAGE 15

SECTION 6: NEW SOURCES	PAGE 15

SECTION 7: EXCEPTIONS	PAGE 17

SECTION 8: PROVISIONS FOR HAZARDOUS AIR POLLUTANTS	PAGE 17

SECTION 9: STACK HEIGHT CONSIDERATIONS	PAGE 18

SECTION 10: PROVISIONS FOR UPSETS, STARTUPS, AND SHUTDOWNS

	PAGE 23

SECTION 11: SEVERABILITY	PAGE 25

SECTION 12: PROVISIONS FOR EXISTING HOSPITAL/MEDICAL/INFECTIOUS

 WASTE INCINERATORS	PAGE 26

SECTION 13: PROVISIONS FOR EXISTING COMMERCIAL AND INDUSTRIAL

SOLID WASTE INCINERATION UNITS	PAGE 61

SECTION 14: PROVISIONS FOR THE CLEAN AIR INTERSTATE RULE	PAGE 66

MISSISSIPPI COMMISSION ON ENVIRONMENTAL QUALITY

AIR EMISSION REGULATIONS FOR THE PREVENTION, ABATEMENT,

AND CONTROL OF AIR CONTAMINANTS

APC-S-1

Amended December 11, 2008

SECTION 1.	GENERAL

1.	Authority.  Pursuant to the authority granted by Miss. Code Ann.
 49-17-17, the following regulations are adopted for the purpose of
preventing, abating, and controlling air pollution caused by air
contaminants being discharged into the atmosphere as particulates,
smoke, fly ash, solvents, and other chemicals or combinations thereof.

2.	Except as otherwise noted herein, stack emissions testing for
demonstration of compliance with the regulations herein may be performed
in accordance with the Test Methods of the U. S. Environmental
Protection Agency in place at the time testing is performed or as
otherwise approved by the staff of the Mississippi Office of Pollution
Control and the U. S. Environmental Protection Agency.

Notwithstanding this or any other provision in these or any other
regulations, the owner or operator may use any credible evidence or
information relevant to whether a source would have been in compliance
with applicable requirements if the appropriate performance or
compliance test had been performed, for the purpose of submitting
compliance certifications.

Notwithstanding any other provision in these or any other air pollution
control regulations, any credible evidence or information relevant to
whether a source would have been in compliance with applicable
requirements if the appropriate performance or compliance test had been
performed, can be used to establish whether or not a person has violated
or is in violation of any standard or applicable requirement.

3.	In the event of a conflict between any of the requirements of these
regulations and/or applicable requirements of any other regulation or
law, the more stringent requirements shall be applied.

SECTION 2.	DEFINITIONS

The terms used in the regulations shall, unless the context otherwise
requires, have the following meanings:

 1.	"Air cleaning device."  Any method, process or equipment which
removes, reduces or renders less noxious air contaminants discharged
into the atmosphere.  This term is synonymous with air pollution control
device.

 2.	"Air contaminant."  Particulate matter, dust, fumes, gas, mist,
smoke, or vapor, or any combination thereof produced by processes other
than natural.

 3.	"Air contamination."  The presence in the outdoor ambient air of one
or more air contaminants which contribute to a condition of air
pollution.

 4.	"Air contamination source."  Any source at, from, or by reason of
which there is emitted into the ambient air any air contaminant,
regardless of who the person may be who owns or operates the building,
premises, or other property in, at, or on which such source is located,
or the facility, equipment or other property by which the emission is
caused or from which the emission comes.

 5.	"Air contaminant point source."  Any single point of emissions of
any air contaminant such as from an individual machine or combustion
device.

 6.	"Air pollution."  The presence in the outdoor ambient air of one or
more air contaminants in quantities, of characteristic, and of a
duration which are materially injurious or can be reasonably expected to
become materially injurious to human, plant, or animal life or to
property, or which unreasonably interfere with enjoyment of life or use
of property throughout the State or throughout such area of the State as
shall be affected thereby.

 7.	"Ambient air."  The encompassing atmosphere existing in the matter
of space and to which life of this earth is adapted.  For the purposes
of these regulations, that portion of the atmosphere outside of
buildings, stacks, and ducts.

 8.	"Atmosphere."  The air that envelopes or surrounds the earth.  This
term is synonymous with ambient air.

 9.	"Commission."  The Mississippi Commission on Environmental Quality.

10.	"Excess (or excessive) emission."  The operation of a facility in
which the emission of one or more pollutants exceeds the applicable
limit(s).

11.	"Fly ash."  Particulate matter capable of being gasborne or airborne
or carried in the gas stream and consisting essentially of ash, fused
ash, and/or unburned material.

12.	"Ground level."  Unless otherwise specified in sampling techniques,
will be considered to be in the range of one to twenty (20) feet of
ground level.  For ambient sampling, it shall also be outside the
boundaries of the property which contains the air pollution source.

13.	"Incinerator."  A combustion device specifically designed for the
destruction by high temperature burning of solid, semi-solid, liquid or
gaseous combustible wastes and from which the solid residues contain
little or no combustibles.

14.	"Modification."  Any physical change in, or change in the method of
operation of, an affected facility which increases the amount of any air
pollutant emitted by such facility or which results in the emission of
any air pollutant not previously emitted, except that:

(1)	Routine maintenance, repair and replacement shall not be considered
physical changes, and

(2)	An increase in the production rate or hours of operation shall not
be considered a change in the method of operation, unless it is
prohibited by a permit.

15.	"Multiple chamber incinerator."  Any article, machine, equipment,
contrivance, structure, or any part thereof used to dispose of
combustible refuse by burning, which consists of three or more
refractory walls, interconnected by gas passage points or ducts and
employing adequate design parameters necessary for maximum combustion of
the material to be burned.

16.	"Opacity."  The degree to which emissions reduce the transmission of
light and obscure the background.

17.	"Open burning."  The combustion of solid waste without (1) control
of combustion air to maintain adequate temperature for efficient
combustion, (2) containment of the combustion reaction in an enclosed
device to provide sufficient residence time and mixing for complete
combustion, and (3) control of the emission of the combustion products.

18.	"Ozone Action Day."  A day(s) occurring between March 1 and October
31 of each year which the Executive Director has designated as being
conducive to high rates of ozone formation for a named county(ies) among
DeSoto, Hancock, Harrison, and Jackson Counties.

19.	"Particulate matter."  Any airborne finely divided solid or liquid
material with an aerodynamic diameter smaller than 100 micrometers.

20.	"Particulate matter emissions."  All finely divided solid or liquid
material, other than uncombined water, emitted to the ambient air as
measured by an applicable EPA Test Method, an equivalent or alternative
method specified by the EPA, or by a test method specified in the
approved State Implementation Plan.

21.	"Person."  The State or other agency, or institution thereof, any
municipality, political subdivision, public or private corporation,
individual, partnership, association, or other entity, and includes any
officer or governing or managing body of any municipality, political
subdivision, or public or private corporation, or the United States or
any officer or employee thereof.

22.	"PM2.5"  Particulate matter with an aerodynamic diameter less than
or equal to a nominal 2.5 micrometers as measured by a reference method
based on Appendix L of 40 CFR 50 and designated in accordance with
40 CFR 53 or by an equivalent method designated in accordance with
40 CFR Part 53.

23.	"PM2.5 emissions."  Finely divided solid or liquid material, with an
aerodynamic diameter less than or equal to a nominal 2.5 micrometers,
emitted to the ambient air as measured by an applicable EPA Test Method,
an equivalent or alternate method specified by the EPA, or by a test
method specified in the approved State Implementation Plan.

24.	"PM10."  Particulate matter with an aerodynamic diameter less than
or equal to a nominal 10 micrometers as measured by a reference method
based on Appendix J of 40 CFR 50 and designated in accordance with
40 CFR 53 or by an equivalent method designated in accordance with
40 CFR Part 53.

25.	"PM10 emissions."  Finely divided solid or liquid material, with an
aerodynamic diameter less than or equal to a nominal 10 micrometers,
emitted to the ambient air as measured by an applicable EPA Test Method,
an equivalent or alternate method specified by the EPA, or by a test
method specified in the approved State Implementation Plan.

26.	"Process weight."  The total weight of all materials introduced into
a source operation including solid fuels and water.  Excluded materials
are as follows: Liquids and gases used solely as fuels or as a means of
conveyance, liquids used as a pollutant removal medium, recycled process
materials counted at initial introduction, and air introduced for
purposes of combustion.

27.	"Recreational area."  Recreational area means:

a.	a national, state, county, or city designated park; or

b.	an outdoor recreational area, such as a golf course or swimming pool,
owned by a city, county, or other public agency.

28.	"Residential area."  Residential area means:

a.	a group of 20 or more single family dwelling units on contiguous
property and having an average density of two or more units per acre, or

b.	a group of 40 or more single family dwelling units on contiguous
property and having an average density of one or more units per acre, or

c.	a subdivision containing at least 20 constructed houses, in which the
subdivision plat is recorded in the chancery clerk's office of the
appropriate county.

29.	"Shutdown."  The termination of operation of equipment.  Relative to
fuel-burning equipment, a shutdown shall be construed to occur only when
a unit is taken from a fired to a non-fired state.

30.	"Smoke."  Small gasborne particles resulting from incomplete
combustion and consisting predominantly, but not exclusively, of carbon,
ash, and other combustible material.

31.	"Soot."  Aggregated particles consisting mainly of carbonaceous
material.

32.	"Soot blowing."  The removal by mechanical means of accumulated
carbon and/or ash from heat transfer surfaces of an operating
fuel-burning unit.

33.	"Standard conditions."  Standard conditions for gas measurement and
calculation will be a temperature of 60 degrees Fahrenheit and a
pressure of 14.7 pounds per square inch absolute except where set by
Applicable Rules and Regulations.

34.	"Startup."  The bringing into operation from a non-operative
condition.  Relative to fuel-burning equipment, a startup shall be
construed to occur only when a unit is taken from a non-fired to a fired
state.

35.	"Total reduced sulfur, (TRS)" means hydrogen sulfide, mercaptans,
dimethyl sulfide, and any other organic sulfides present.

36.	"Total suspended particulate."  Particulate matter as measured by
the method described in Appendix B of 40 CFR 50.

37.	"Upset."  An unexpected and unplanned condition of operation of the
facility in which equipment operates outside of the normal and planned
parameters.  An upset shall not include a condition of operation caused
by improperly designed equipment, lack of preventive maintenance,
careless or improper operation, operator error, or an intentional
startup or shutdown of equipment.

SECTION 3.	SPECIFIC CRITERIA FOR SOURCES OF PARTICULATE MATTER

1.	Smoke

(a)	No person shall cause, permit, or allow the emission of smoke from a
point source into the open air from any manufacturing, industrial,
commercial or waste disposal process which exceeds forty (40) percent
opacity subject to the exceptions provided in (b) & (c).

(b)	Startup operations may produce emissions which exceed 40% opacity
for up to fifteen (15) minutes per startup in any one hour and not to
exceed three (3) startups per stack in any twenty-four (24) hour period.

(c)	Emissions resulting from soot blowing operations shall be permitted
provided such emissions do not exceed 60 percent opacity, and provided
further that the aggregate duration of such emissions during any
twenty-four (24) hour period does not exceed ten (10) minutes per
billion BTU gross heating value of fuel in any one hour.

2.	Equivalent Opacity.  No person shall cause, allow, or permit the
discharge into the ambient air from any point source or emissions, any
air contaminant of such opacity as to obscure an observer's view to a
degree in excess of 40% opacity, equivalent to that provided in Section
3.1(a).  This shall not apply to vision obscuration caused by uncombined
water droplets.

3.	General Nuisances.  No person shall cause, permit, or allow the
emission of particles, or any contaminants in sufficient amounts or of
such duration from any process as to be injurious to humans, animals,
plants, or property, or to be a public nuisance, or create a condition
of air pollution.

(a)	No person shall cause or permit the handling or transporting or
storage of any material in a manner which allows or may allow
unnecessary amounts of particulate matter to become airborne.

(b)	When dust, fumes, gases, mist, odorous matter, vapors, or any
combination thereof escape from a building or equipment in such a manner
and amount as to cause a nuisance to property other than that from which
it originated or to violate any other provision of this regulation, the
Commission may order such corrected in a way that all air and gases or
air and gasborne material leaving the building or equipment are
controlled or removed prior to discharge to the open air.

4.	Fuel Burning

(a)	Fossil Fuel Burning.  The maximum permissible emission of ash and/or
particulate matter from fossil fuel burning installations shall be
limited as follows:

(1)	Emissions from installations of less than 10 million BTU per hour
heat input shall not exceed 0.6 pounds per million BTU per hour heat
input.

(2)	Emissions from installations equal to or greater than 10 million BTU
per hour heat input but less than 10,000 million BTU per hour heat input
shall not exceed an emission rate as determined by the relationship

E = 0.8808 * I-0.1667

where E is the emission rate in pounds per million BTU per hour heat
input and I is the heat input in millions of BTU per hour.

(3)	Emissions from installations equal to or greater than 10,000 million
BTU per hour heat input shall not exceed 0.19 pounds per million BTU per
hour heat input.

(b)	Combination Boilers.  Fuel burning operations utilizing a mixture of
combustibles such as, but not limited to, fossil fuels plus bark, oil
plus bark, or spent wood, or water treatment by-products sludge, to
produce steam or heat water or any other heat transfer medium through
indirect means may be allowed emission rates up to 0.30 grains per
standard dry cubic foot.

5.	Kraft Process Recovery Boilers.  The emissions of particulate matter
from a recovery furnace stack shall not exceed four (4) pounds per ton
of equivalent air-dried Kraft pulp produced at any given time.

6.	Manufacturing Processes.

(a)	General.  Except as otherwise specified, no person shall cause,
permit, or allow the emission of particulate matter in total quantities
in any one hour from any manufacturing process, which includes any
associated stacks, vents, outlets, or combination thereof, to exceed the
amount determined by the relationship

E = 4.1 p 0.67

where E is the emission rate in pounds per hour and p is the process
weight input rate in tons per hour.

Conveyor discharge of coarse solid matter may be allowed if no nuisance
is created beyond the property boundary where the discharge occurs.

(b)	Kraft Pulping Mills.  All mills existing prior to
January 25, 1972, and not modified subsequent thereto shall comply
with the following emission limits:

(1)	Recovery Furnaces.  The emission of particulate matter from recovery
furnace stacks shall not exceed four pounds per ton of equivalent
air-dried Kraft pulp.

(2)	Lime Kilns.  The emission of particulate matter from lime kilns
shall not exceed one pound per ton of equivalent air-dried Kraft pulp.

(3)	Smelt Tanks.  The emission of particulate matter from smelt tanks
shall not exceed one-half pound per ton of equivalent air-dried Kraft
pulp.

7.	Open Burning.  The open burning of residential, commercial,
institutional, or industrial solid waste, is prohibited.  This
prohibition does not apply to infrequent burning of agricultural wastes
in the field, silvicultural wastes for forest management purposes,
land-clearing debris, debris from emergency clean-up operations, and
ordnance; and permitted open burning at hazardous waste disposal
facilities subject to regulation under Subtitle C of the Federal
Resource Conservation and Recovery Act (RCRA).

(a)	Fires set for the burning of agricultural wastes in the field and/or
silvicultural wastes for forest management purposes must meet the
following conditions.

A Permit must be obtained from the Mississippi Forestry Commission.

(2)	The open burning must occur within a time period allowing adequate
diffusion of air pollutants as defined by the permit and the daily
weather guides issued by the National Weather Forecast Office.

(3)	Starter or auxiliary fuels may consist of dried vegetation,
petroleum derived fuels of the gasoline, kerosene, or light fuel oil
types (diesel), or a combination thereof.  Use of or burning of other
combustible material that causes excessive visible emission (e.g.,
rubber tires, plastic materials, etc.) is prohibited.

(b)	Open burning of land-clearing debris must not use starter or
auxiliary fuels which cause excessive smoke (rubber tires, plastics,
etc.); must not be performed if prohibited by local ordinances; must not
cause a traffic hazard; must not take place where there is a High Fire
Danger Alert declared by the Mississippi Forestry Commission or
Emergency Air Pollution Episode Alert imposed by the Executive Director
and must meet the following buffer zones.

(1)	Open burning without a forced-draft air system must not occur within
500 yards of an occupied dwelling.

(2)	Open burning utilizing a forced-draft air system on all fires to
improve the combustion rate and reduce smoke may be done within 500
yards of but not within 50 yards of an occupied dwelling.

(3)	Burning must not occur within 500 yards of commercial airport
property, private air fields, or marked off-runway aircraft approach
corridors unless written approval to conduct burning is secured from the
proper airport authority, owner or operator.

Permitted open burning at a hazardous waste disposal facility subject to
regulation under Subtitle C of RCRA is considered a stationary source
of air pollution subject to Mississippi air emission permitting
regulations.

Ozone Action Days in DeSoto County, Hancock County, Harrison County and
Jackson County.  In DeSoto County, Hancock County, Harrison County, or
Jackson County, open burning of agricultural wastes and silvicultural
wastes described in 7(a) above, open burning of land-clearing debris
described in 7(b) above, and permitted open burning at a hazardous waste
disposal facility described in 7(c) above are prohibited in said county
when an Ozone Action Day is declared by the Executive Director for the
county(ies). Ozone Action Days shall be noticed the evening before on
the MDEQ website at http://deq.state.ms.us, and/or with local news
media.  The Mississippi Department of Transportation, Mississippi State
Forestry Commission and local fire officials shall also be notified the
evening before an Ozone Action Day.

8.	Incineration.

(a)	The maximum discharge of particulate matter from any incinerator,
except those specified in paragraph (b) or (c) of this section, or those
specified in Section 6 and Section 12 shall not exceed 0.2 grains per
standard dry cubic foot of flue gas calculated to twelve percent (12%)
carbon dioxide by volume for products of combustion.  This limitation
shall apply when the incinerator is operating at design capacity.

The carbon dioxide produced by combustion of any auxiliary fuels shall
be excluded from the calculation to twelve percent (12%) carbon dioxide.
 After May 8, 1970, any new equipment shall be of the multiple chamber
type or its equivalent for emission control.  In critical areas where an
installation is in close proximity to a residential area, an
incinerator, except those specified in paragraph (b) of this section, or
those specified in Section 6 and Section 12, shall be limited to
emissions of 0.1 grains per standard dry cubic foot of flue gases
calculated to twelve percent (12%) carbon dioxide by volume for products
of combustion.

(b)	The maximum discharge of smoke from the incineration of waste
material resulting totally from the ginning of cotton shall not obscure
an observer's view to a degree in excess of 40% opacity.

Start-up operations may produce emissions which exceed 40% opacity for
up to fifteen minutes per start-up in any one hour not to exceed three
(3) start-ups in any twenty-four (24) hour period.

After July 1, 1994, the emission limitation specified in paragraph (a)
of this section shall also be applicable to cotton gin waste
incinerators.

(c)	The emission limitation in paragraph (a) above does not apply to
afterburners, flares, thermal oxidizers, and other similar devices used
to reduce the emissions of air pollutants from processes.

Sampling Ports.

(a)	New Equipment:  The owner or operator of any new air pollution
control equipment, obtained after May 8, 1970, and vented to the
atmosphere, shall have necessary sampling ports and ease of
accessibility.

(b)	Existing Equipment:  The owner or operator of air pollution control
equipment that is in existence prior to May 8, 1970, shall provide the
necessary sampling ports and ease of accessibility when deemed necessary
by the Permit Board.

10.	More Restrictive Emission Limits.  The Commission reserves the right
to prescribe more stringent emission limits as it deems necessary in
problem areas.  The expansion, alteration, or establishment of a new
industry may also result in the prescription of more stringent emission
limits.

SECTION 4.	SPECIFIC CRITERIA FOR SOURCES OF SULFUR COMPOUNDS

1.	Sulfur Dioxide Emissions from Fuel Burning

(a)	The maximum discharge of sulfur oxides from any fuel burning
installation in which the fuel is burned primarily to produce heat or
power by indirect heat transfer shall not exceed 4.8 pounds (measured as
sulfur dioxide) per million BTU heat input.

(b)	No person shall cause or permit the burning of fuel in any fuel
burning equipment that results in an average emission of sulfur dioxide
from any calendar year at a rate greater than was emitted by said fuel
burning equipment for the corresponding calendar year 1970 unless
otherwise authorized by the Commission.  Installations under
construction on January 25, 1972, are excluded from this requirement.

(c)	The maximum discharge of sulfur dioxide from any modified fuel
burning unit whose generation capacity is less than 250 million BTU per
hour and in which the fuel is burned primarily to produce heat or power
by indirect heat transfer shall not exceed 2.4 pounds (measured as
sulfur dioxide) per million BTU heat input.  For the purposes of Section
4 of these regulations only, "modification" shall mean any physical
change in an Air Contaminant Source which increases the amount of any
air pollutant (to which a standard applies) emitted by such source or
which results in the emission of any air pollutant (to which a standard
applies) not previously emitted.

2.	Sulfur Dioxide Emissions from Processes

(a)	Except as otherwise provided herein, no person shall cause or permit
the emission of gas containing sulfur oxides (measured as sulfur
dioxide) in excess of 2,000 ppm (volume) from any process equipment in
existence on January 25, 1972, or in excess of 500 ppm (volume) from any
process equipment constructed after January 25, 1972. The 500 ppm
(volume) requirement shall apply for equipment constructed after January
25, 1972 unless otherwise provided by the Commission.

(b)	Except as otherwise provided in paragraph 2(f)(1), no person shall
cause or permit the emission of any gas stream which contains hydrogen
sulfide in excess of one grain per 100 standard cubic feet.

Gas streams containing hydrogen sulfide in excess of one grain per 100
standard cubic feet shall be incinerated at temperatures of not less
than 1600oF for a period of not less than 0.5 seconds, or processed in
such manner which is equivalent to or more effective for the removal of
hydrogen sulfide.

Sulfur dioxide concentration limitations in the gas streams resulting
from such incineration or processing shall be determined for each
emission point on a case-by-case basis to insure that the resulting
maximum ground level concentration of sulfur dioxide as determined by
acceptable method or methods will be in compliance with the National
Ambient Air Quality Standards for sulfur dioxide. Testing to determine
the productive capacity of new fields shall be exempted from emission
limitation provisions of the paragraph of the regulation providing such
testing has been previously negotiated and approved by the Mississippi
Office of Pollution Control.

This regulation shall not apply to sulfur recovery plants.

(c)	No person shall cause or permit acid mist emissions from sulfuric
acid manufacturing plants to exceed 0.5 pounds/ton of acid produced.
Sulfur trioxide emissions from sulfuric acid manufacturing plants shall
not exceed 0.2 pounds/ton of acid produced.

(d)	No person shall cause or permit emission of sulfur oxides,
calculated as sulfur dioxide, from a sulfur recovery plant to exceed
0.12 pounds per pound of sulfur processed.

(e)	No person shall cause or permit emissions of sulfur oxides,
calculated as sulfur dioxide, from primary nonferrous smelters, in
excess of the emission calculated as follows:

Copper smelters:  Y = 0.2X

Zinc smelters:      Y = 0.564X0.85

Lead smelters:     Y = 0.98X0.77

Where X is the total sulfur fed to the smelter in pounds/hour and Y is
the allowable sulfur emissions in pounds/hour.

(f)	Kraft Pulp Mills

1.	All mills existing prior to November 1, 1987, and not modified
subsequent thereto, excluding mills or facilities subject to New Source
Performance Standards, shall control the emission of total reduced
sulfur compounds (TRS) so as to not exceed the emission limits set forth
below:

a.	Straight recovery boiler systems - twenty (20) parts per million TRS,
expressed as hydrogen sulfide on a dry gas basis corrected to 8% oxygen,
on a 12-hour average basis, except that:

i.	the International Paper Company, Vicksburg, Mississippi, shall be
allowed 40 parts per million TRS, expressed as hydrogen sulfide on a dry
gas basis corrected to 8% oxygen, on a 12-hour average basis,

ii.	the International Paper Company, Natchez, Mississippi, Recovery
Boilers 4 & 5, shall be allowed 40 parts per million TRS, expressed as
hydrogen sulfide on a dry gas basis corrected to 8% oxygen, on a 12-hour
average basis, and

iii.	the Georgia-Pacific Corporation, Monticello, Mississippi, shall be
allowed 40 parts per million TRS, expressed as hydrogen sulfide on a dry
gas basis corrected to 8% oxygen, on a 12-hour average basis.

b.	Lime kiln systems - twenty (20) parts per million of TRS, expressed
as hydrogen sulfide on a dry gas basis corrected to 10% oxygen, on a
12-hour average basis.

c.	Digester systems - five (5) parts per million of TRS, expressed as
hydrogen sulfide on a dry gas basis corrected to 10% oxygen, on a
12-hour average basis.

Multiple effect evaporator systems - five (5) parts per million of TRS,
expressed as hydrogen sulfide on a dry gas basis corrected to 10%
oxygen, on a 12-hour average basis.

e.	Condensate stripper systems - five (5) parts per million of TRS,
expressed as hydrogen sulfide on a dry gas basis corrected to 10%
oxygen, on a 12-hour average basis.

f.	Smelt dissolving tank - 0.016 gram of TRS, expressed as hydrogen
sulfide on a dry gas basis, per kilogram of black liquor solids (dry
weight).

g.	Equivalent control systems (controls for treating collected
noncondensible gases in a manner equivalent to incineration in a lime
kiln) - five (5) parts per million TRS, expressed as hydrogen sulfide on
a dry gas basis, corrected to the actual oxygen content of the untreated
gas stream, on a 12-hour average basis.

2.	All mills, as defined above, shall, by February 1, 1988, demonstrate
compliance with the TRS emission limits set forth above.  Compliance
demonstration for recovery boilers, lime kilns, smelt tanks, and
equivalent control systems for collected noncondensible gases shall be
by testing in accordance with EPA Test Method 16 or 16A and submittal of
a stack test report.  Compliance demonstration for digester systems,
multiple effect evaporator systems and condensate stripper systems shall
be by certification that these systems are fully connected to a
noncondensible gas collection system followed by incineration in the
lime kiln or equivalent control and testing of lime kiln or equivalent
control as specified above. A compliance schedule may be submitted, as
set forth below, on any or all systems not expected to comply with the
emission limit and such submittal will negate the requirement for
immediate compliance demonstration, as referenced above, on those
systems.

Any mill defined above which, on November 1, 1987, is unable to comply
with the emission limits set forth above, shall, within three (3) months
thereafter, submit a schedule for attaining compliance with these
limits.  The compliance schedule shall not extend past November 1,
1990.  Compliance with emission limits shall be demonstrated by the
methods specified above, as appropriate, no later than the end of the
compliance schedule.  Compliance demonstration for recovery boilers,
lime kilns, smelt tanks, and equivalent control systems for collected
noncondensible gases shall be by testing in accordance with EPA Test
Method 16 or 16A and submittal of a stack test report.  Compliance
demonstration for digester systems, multiple effect evaporator systems
and condensate stripper systems shall be by certification that these
systems are fully connected to a noncondensible gas collection system
followed by incineration in the lime kiln or equivalent control and
testing of lime kiln or equivalent control as specified above.

3.	All mills, as defined above, shall monitor the emission of TRS and/or
other gas constituents as described below:

a.	The TRS emission concentration in recovery boiler flue gas shall be
monitored by either:

i.	A continuous monitoring device which meets the requirements of
40 CFR 60, Performance Specification 5; or

ii.	Performance of EPA Method 16 or 16A on no less than a (calendar)
quarterly basis.

b.	The oxygen concentration in recovery boiler flue gas shall be
continuously monitored by a device which meets the requirements of
40 CFR 60, Performance Specification 3.

The TRS concentration in lime kiln flue gas shall be continuously
monitored by a device which meets the requirements of 40 CFR 60,
Performance Specification 5.

d.	The oxygen concentration in lime kiln flue gas shall be continuously
monitored by a device which meets the requirements of 40 CFR 60,
Performance Specification 3.

All mills, as defined above, shall obtain the necessary continuous
monitoring equipment and begin monitoring by November 1, 1988, or no
later than the date of final compliance with the regulation, if
compliance is not immediate.  For mills choosing to use EPA Method 16
or 16A for recovery boiler monitoring, the necessary equipment and/or
monitoring capability must be obtained by February 1, 1988.  Also, when
Method 16 or 16A is used, each successive quarter's testing shall be
separated from the previous quarter's by a period of not less than
sixty (60) days and prior notice to the Mississippi Office of Pollution
Control of all testing shall be made.

All mills, as defined above, shall calculate and record, on a daily
basis, the 12-hour average TRS concentration and O2 concentration for
the two consecutive operating periods of each operating day for both the
recovery boiler (if continuously monitored) and lime kiln.  Each 12-hour
average shall be determined as the arithmetic mean of the appropriate 12
continuous 1-hour average concentrations.  Each 12-hour average TRS
concentration shall be corrected to 10%, or 8% O2, as appropriate to the
emission limit, using the equation defined in 40 CFR 60.284(c)(3).

All mills, as defined above, shall report, for each calendar quarter,
the periods of emissions which exceed the TRS limits specified above
from the recovery boiler and lime kiln.  The report shall specify the
12-hour period of each exceedance by time and date, the average
emissions concentration for the period, and total number of 12-hour
periods of mill operation during the quarter.  The report shall also
detail all outages of the monitoring devices by time and date.  The
report shall be due within forty-five (45) days following the end of the
calendar quarter.

SECTION 5.	SPECIFIC CRITERIA FOR SOURCES OF CHEMICAL EMISSIONS

1.	Fluorides.  No person shall allow the emission of fluorides into the
ambient air in excess of four-tenths (0.4) pound per ton of P2O5 or
equivalent.  The allowable emission of fluorides shall be calculated by
multiplying the unit emission, specified above, times the expressed
design production capacity of the installation or plant.

2.	Miscellaneous Chemical Emissions.  No person shall cause, permit, or
allow the emission of toxic, noxious, or deleterious substances, in
addition to those considered in these regulations, into the ambient air
in concentrations sufficient to affect human health and well-being, or
unreasonably interfere with the enjoyment of property or unreasonably
and adversely affect plant or animal life beyond the boundaries of the
property containing the air pollution source.

SECTION 6.	NEW SOURCES

The provisions of this section apply to the owner or operator of any
source listed herein, the construction or modification of which is
commenced after the date of adoption of specific emission limitations
applicable to such source.

1.	Kraft Pulping Mills.  All sources shall minimize gaseous and
particulate emission by use of modern equipment, devices, maintenance,
and operating practices in accordance with best current technology.  In
no case shall emissions exceed the limits set forth in any applicable
Federal Standard of Performance for New Stationary Sources.

2.	Other Limitations.  The Mississippi Pollution Control Permit Board,
in accordance with Commission Regulation APC-S-2, may require more
stringent emission limitations which it deems necessary to meet
applicable national primary and secondary ambient air quality standards,
necessary to insure that ambient air pollution concentrations do not
exceed ambient air increments or violate other requirements under
Federal Prevention of Significant Deterioration (PSD) regulations
promulgated by the U.S. Environmental Protection Agency as of
August 23, 1989, pursuant to Section 160 through 169 of the Federal
Clean Air Act as amended, or necessary to meet other Federal law or
regulations enacted or promulgated subsequent to this regulation.

3.	New Source Performance Standards.  The Federal New Source Performance
Standards are those duly promulgated by the U.S. Environmental
Protection Agency in (or to be printed in) 40 C.F.R. Part 60,
pursuant to Section 111 of the Federal Clean Air Act, as amended, and
Consolidated Federal Air Rule provisions duly promulgated by the U.S.
Environmental Protection Agency in (or to be printed in) 40 C.F.R Part
65.  All such regulations promulgated by the U.S. Environmental
Protection Agency as of October 3, 2008, are incorporated herein and
adopted by reference by the Commission as official regulations of the
State of Mississippi and shall hereafter be enforceable as such (except
the word "Administrator" in said standards and general implementing
regulations shall be replaced by the words "Executive Director" and the
word "Agency" shall be replaced by the word "Department".)  Hereafter,
any facility subject to the Federal New Source Performance Standards
shall comply with the emission limitations and other requirements of
said standards.

4.	Additional Requirements for Infectious Waste Incineration.

a.	Infectious waste incinerators which incinerate only those wastes
generated on-site and are installed after December 9, 1993, shall
comply with the following:

i.	Daily records shall be kept of the times of operation, quantity of
wastes incinerated and the temperature of the secondary chamber which
temperature shall be monitored continuously.  Records shall be
maintained on hand for at least two (2) years.

ii.	Only wastes generated on-site may be incinerated.  Disposal of
wastes from off-site shall cause the incinerator to be classified as a
commercial incinerator and, therefore, subject to the requirements
applicable to such units.

b.	Commercial Incinerators.  For purposes of this regulation, a
commercial incinerator is any infectious waste incinerator that
incinerates wastes other than or in addition to wastes generated
on-site.  A commercial infectious waste incinerator installed or
modified after December 9, 1993, shall comply with the following:

i.	A manifest system, including a detailed description of the waste
collection and transportation system shall be employed.  Daily records
shall be kept of the times of incinerator operation, quantity of wastes
incinerated and temperature of the secondary chamber which temperature
shall be monitored continuously.  Records shall be maintained on hand
for at least two (2) years.

ii.	Notwithstanding the requirements of Section 6.4.b.i and Section 12,
the Permit Board may in any permit, in accordance with Regulation
APC-S-2, establish more stringent requirements for emissions, operating
parameters, monitoring, and recordkeeping subject to the provisions of
Miss. Code Ann. 49-17-34(2) and (3).

SECTION 7.	EXCEPTIONS

If any single source of emission or combination of sources of emissions
is found to compromise the ambient air quality in the State, beyond the
limitations set forth in any national primary and secondary ambient air
quality standards now or hereafter established by the Administrator of
the Environmental Protection Agency pursuant to the Clean Air Act as
amended December 31, 1970, (Public Law 91-640) notwithstanding
compliance with any maximum allowable emission rate allowed by this
regulation, the Mississippi Commission on Environmental Quality may
require such further reduction in emission from this or these sources as
is necessary to obtain compliance with said national primary and
secondary ambient air quality standards.

SECTION 8.	PROVISIONS FOR HAZARDOUS AIR POLLUTANTS

1.	Hazardous Air Pollutant Emission Standards

Hazardous air pollutant emission standards are National Emission
Standards for Hazardous Air Pollutants duly promulgated by the U. S.
Environmental Protection Agency in (or to be printed in)
40 C.F.R. Part 61 pursuant to Section 112 of the Federal Clean Air
Act, as amended; National Emission Standards for Hazardous Air
Pollutants for Source Categories duly promulgated by the U.S.
Environmental Protection Agency in (or to be printed in) 40 C.F.R.
Part 63 pursuant to Section 112 of the Federal Clean Air Act, as
amended; and Consolidated Federal Air Rule provisions duly promulgated
by the U.S. Environmental Protection Agency in (or to be printed in) 40
C.F.R. Part 65.  All such regulations promulgated by the U.S.
Environmental Protection Agency as of October 3, 2008, are incorporated
herein and adopted by reference by the Commission as official
regulations of the State of Mississippi and shall hereafter be
enforceable as such (except the word "Administrator" in said standards
and general implementing regulations shall be replaced by the words
"Executive Director" and the word "Agency" shall be replaced by the word
"Department").  Hereafter, any facility subject to the National Emission
Standards for Hazardous Air Pollutants and/or the National Emission
Standards for Hazardous Air Pollutants for Source Categories shall
comply with the emission limitations and other requirements of said
standards.

National Emission Standards for Hazardous Air Pollutants; Compliance
Extensions for Early Reductions.

The National Emission Standards for Hazardous Air Pollutants: Compliance
Extensions for Early Reductions are regulations duly promulgated by the
U.S. Environmental Protection Agency in (or to be printed in) 40 C.F.R.
Part 63 pursuant to Section 112 of the Federal Clean Air Act, as
amended.  All such regulations promulgated by the U.S. Environmental
Protection Agency are incorporated herein and adopted by reference by
the Commission as official regulations of the State of Mississippi and
shall hereafter be enforceable as such.

3.	Case by Case Maximum Achievable Control Technology Requirements

The Mississippi Pollution Control Permit Board, in accordance with
Commission Regulation APC-S-6, may require emissions limitations
necessary to meet case by case maximum achievable control technology
("MACT") requirements in accordance with Section 112(j) and (g) of the
Federal Act.

4.	Mercury Emissions from Electric Utilities.

Mercury emissions from electric utilities are regulated in accordance
with the Emission Guidelines for the Control of Mercury Emissions from
Coal-Fired Electric Steam Generating Units promulgated by the U.S.
Environmental Protection Agency in 40 CFR Part 60, Subpart HHHH,
pursuant to Section 111 of the Federal Clean Air Act, as amended.  All
such regulations duly promulgated by the U.S. Environmental Protection
Agency as of October 3, 2008, are incorporated herein and adopted by
reference by the Commission as official regulations of the State of
Mississippi and shall hereafter be enforceable as such, except for the
changes noted in (a) and (b). Hereafter, any facility subject to the
Federal Emission Guidelines shall comply with all applicable
requirements of the regulation.

(a)	The phrase "permitting authority" shall mean "Mississippi
Environmental Quality Permit Board" except when used in the definitions
of "Allocate or allocation" and "Hg allowance" in 40 CFR 60.4102.

(b)	The permitting authority will allocate mercury allowances in
accordance with the procedures outlined in 40 CFR 60.4142 and by the
dates specified in 40 CFR 60.4141.

SECTION 9.	STACK HEIGHT CONSIDERATIONS

1.	Definitions

(a)	"Emission limitation" and "emission standard."  A requirement
established which limits the quantity, rate, or concentration of
emissions of air pollutants on a continuous basis, including any
requirements which limit the level of opacity, prescribe equipment, set
fuel specifications, or prescribe operation or maintenance procedures
for a source to assure continuous emission reduction.

(b)	"Stack."  Any point in a source designed to emit solids, liquids, or
gases into the air, including a pipe or duct but not including flares.

(c)	"A stack in existence."  The owner or operator had either:

(1)	Begun, or caused to begin, a continuous program of physical on-site
construction of the stack, or

(2)	Entered into binding agreements or contractual obligations, which
could not be cancelled or modified without substantial loss to the owner
or operator, to undertake a program of construction of the stack to be
completed in a reasonable time.

(d)	"Dispersion technique."  Any technique which attempts to affect the
concentration of a pollutant in the ambient air by using that portion of
a stack which exceeds good engineering practice stack height, varying
the rate of emission of a pollutant according to atmospheric conditions
or ambient concentrations of that pollutant, or increasing final exhaust
gas plume rise by manipulating source process parameters, exhaust gas
parameters, stack parameters, or combining exhaust gases from several
existing stacks into one stack; or other selective handling of exhaust
gas streams so as to increase the exhaust gas plume rise.  The preceding
sentence does not include:

(1)	The reheating of a gas stream, following use of a pollution control
system, for the purpose of returning the gas to the temperature at which
it was originally discharged from the facility generating the gas
stream:

(2)	The merging of exhaust gas streams where:

(i)	The source owner or operator demonstrates that the facility was
originally designed and constructed with such merged gas streams;

(ii)	After July 8, 1985, such merging is part of a change in operation
at the facility that includes the installation of pollution controls and
is accompanied by a net reduction in the allowable emissions of a
pollutant.  This exclusion from the definition of "dispersion
techniques" shall apply only to the emission limitation for the
pollutant affected by such change in operation; or

(iii)	Before July 8, 1985, such merging was part of a change in
operation at the facility that included the installation of emissions
control equipment or was carried out for sound economic or engineering
reasons.  Where there was an increase in the emission limitation or, in
the event that no emission limitation was in existence prior to the
merging, an increase in the quantity of pollutants actually emitted
prior to the merging, the reviewing agency shall presume that merging
was significantly motivated by an intent to gain emissions credit for
greater dispersion.  Absent a demonstration by the source owner or
operator that merging was not significantly motivated by such intent,
the reviewing agency shall deny credit for the effects of such merging
in calculating the allowable emissions for the source;

(3)	The use of smoke management in agricultural or silvicultural
prescribed burning programs; or

(4)	Episodic restrictions on residential woodburning and open burning;
or

(5)	Techniques under Paragraph 9.1(d) which increase final exhaust gas
plume rise where the resulting allowable emissions of sulfur dioxide
from the facility do not exceed 5,000 tons per year.

(e)	"Good engineering practice (GEP) stack height."  The greater of:

(1)	65 meters measured from the ground-level elevation at the base of
the stack;

(2)	(i)	For stacks in existence on January 12, 1979, and for which the
owner or operator had obtained all applicable preconstruction permits or
approvals required,  Hg = 2.5 H, provided the owner or operator
produces evidence that this equation was actually relied on in
establishing an emission limitation;

(ii)	For all other stacks,

Hg =	H + 1.5L, where

Hg =	good engineering practice stack height, measured from the
ground-level elevation at the base of the stack,

H =	height of nearby structure(s) measured from the ground-level
elevation at the base of the stack, and

L =	lesser dimension (height or projected width) of nearby structure(s),

provided that the U. S. Environmental Protection Agency or the
Commission may require the use of a field study or fluid model to verify
GEP stack height for the source; or

(3)	The height demonstrated by a fluid model or a field study approved
by the U. S. Environmental Protection Agency or the Commission, which
ensures that the emissions from a stack do not result in excessive
concentrations of any air pollutant as a result of atmospheric downwash,
wakes, or eddy effects created by the source itself, nearby structures,
or nearby terrain features.

(f)	"Nearby," As used in Paragraph 9.1(e)(2)(ii) is defined for a
specific structure or terrain feature and means:

(1)	For purposes of applying the formulae provided in
Paragraph 9.1(e)(2) that distance up to five times the lesser of the
height or the width dimension of a structure, but not greater than
0.8 km (1/2 mile), and

(2)	For conducting demonstrations under Paragraph 9.1(e)(3) that
distance not greater than 0.8 km (1/2 mile), except that the portion of
a terrain feature may be considered to be nearby which falls within a
distance of up to 10 times the maximum height (Ht) of the feature, not
to exceed 2 miles if such feature achieves a height (ht) 0.8 km from
the stack that is at least 40 percent of the GEP stack height determined
by the formulae provided in Paragraph 9.1(e)(2)(ii) of this part or 26
meters, whichever is greater, as measured from the ground-level
elevation at the base of the stack.  The height of the structure or
terrain feature is measured from the ground-level elevation at the base
of the stack.

(g)	"Excessive concentration."  For the purpose of determining good
engineering practice stack height under Paragraph 9.1(e)(3), excessive
concentration means:

(1)	For sources seeking credit for stack height exceeding that
established under Paragraph 9.1(e)(2), a maximum ground-level
concentration due to emissions from a stack due in whole or part to
downwash, wakes, and eddy effects produced by nearby structures or
nearby terrain features which individually is at least 40 percent in
excess of the maximum concentration experienced in the absence of such
downwash, wakes, or eddy effects and which contributes to a total
concentration due to emissions from all sources that is greater than an
ambient air quality standard.  For sources subject to the Prevention of
Significant Deterioration program, an excessive concentration
alternatively means a maximum ground-level concentration due to
emissions from a stack due in whole or part to downwash, wakes, or eddy
effects produced by nearby structures or nearby terrain features which
individually is at least 40 percent in excess of the maximum
concentration experienced in the absence of such downwash, wakes, or
eddy effects and greater than a prevention of significant deterioration
increment.  The allowable emission rate to be used in making
demonstrations under this part shall be prescribed by the new source
performance standard that is applicable to the source category unless
the owner or operator demonstrates that this emission rate is
infeasible.  Where such demonstrations are approved by the U. S.
Environmental Protection Agency or the Commission, an alternative
emission rate shall be established in consultation with the source owner
or operator.

(2)	For sources seeking credit after October 11, 1983, for increases
in existing stack heights up to the heights established under
Paragraph 9.1(e)(2), either a maximum ground-level concentration due in
whole or part to downwash, wakes, or eddy effects as provided in
Paragraph 9.1(g)(1) of this section, except that the emission rate
specified by the State implementation plan (or, in the absence of such a
limit, the actual emission rate) shall be used, or the actual presence
of a local nuisance caused by the existing stack, as determined by the
Commission, and

(3)	For sources seeking credit after January 12, 1979, for a stack
height determined under Paragraph 9.1(e)(2) where the U. S.
Environmental Protection Agency or the Commission requires the use of a
field study or fluid model to verify GEP stack height, for sources
seeking stack height credit after November 9, 1984, based on the
aerodynamic influence of cooling towers, and for sources seeking stack
height credit after December 31, 1970, based on the aerodynamic
influence of structures not adequately represented by the equations in
Paragraph 9.1(e)(2), a maximum ground-level concentration due in whole
or part to downwash, wakes, or eddy effects that is at least 40 percent
in excess of the maximum concentration experienced in the absence of
such downwash, wakes, or eddy effects.

2.	Stack Height Effect on Emission Limitations

(a)	The degree of emission limitation required of any source for control
of any air pollutants shall not be affected by so much of any source's
stack height that exceeds good engineering practice (GEP) or by any
other dispersion technique, except as provided in (b) of this paragraph.

(b)	The provisions of Paragraph 9.2(a) shall not apply to stack heights
in existence, or dispersion techniques implemented, prior to
December 31, 1970, except where pollutants are being emitted from such
stacks or using such dispersion techniques by sources, as defined in
Section 111(a)(3) of the Clean Air Act, which were constructed, or
reconstructed or for which major modifications, as defined pursuant to
Section 6, New Sources, were carried out after December 31, 1970.

(c)	If any existing source, after appropriate application of the
preceding limitations and provisions, is found to exceed or potentially
exceed an air quality standard or increment, as appropriate, when
operating within previously established emission limitations, the
emission limitations applicable to that source shall be modified so as
to eliminate and prevent the exceedance.

(d)	If any new source or source modification, after appropriate
application of the preceding limitations and provisions, is predicted to
exceed an air quality standard, or increment, as appropriate, when
considered as operating under emission limitations consistent with other
Applicable Rules and Regulations, the emission limitations considered
shall be deemed inadequate and different emission limits, based on air
quality considerations, shall be made applicable.

(e)	If any source provides a field study or fluid modeling demonstration
proposing a GEP stack height greater than that allowed by
Paragraph 9.1(e)(1) and (2), then the public will be notified of the
availability of the study and provided the opportunity for a public
hearing before any new or revised emission limitation or permit is
approved.

The actual stack height used or proposed by a source shall not be
restricted in any manner by requirements of this paragraph.

SECTION 10.  PROVISIONS FOR UPSETS, STARTUPS, AND SHUTDOWNS

1.	Upsets

(a)	The occurrence of an upset as defined in Section 2 constitutes an
affirmative defense to an enforcement action brought for noncompliance
with emission standards or other requirements of Applicable Rules and
Regulations or any applicable permit if the source demonstrates through
properly signed contemporaneous operating logs, or other relevant
evidence that include information as follows:

(1)	an upset occurred and that the source can identify the cause(s) of
the upset;

(2)	the source was at the time being properly operated;

(3)	during the upset the source took all reasonable steps to minimize
levels of emissions that exceeded the emission standards, or other
requirements of Applicable Rules and Regulations or any applicable
permit;

(4)	the source submitted notice of the upset to the DEQ within 5 working
days of the time the upset began; and

(5)	the notice of the upset shall contain a description of the upset,
any steps taken to mitigate emissions, and corrective actions taken.

(b)	In any enforcement proceeding, the source seeking to establish the
occurrence of an upset has the burden of proof.

(c)	This provision is in addition to any upset provision contained in
any applicable requirement.

2.	Startups and Shutdowns

(a)	Startups and shutdowns are part of normal source operation.
Emissions limitations applicable to normal operation apply during
startups and shutdowns except as follows:

(1)	when sudden, unavoidable breakdowns occur during a startup or
shutdown, the event may be classified as an upset subject to the
requirements above;

(2)	when a startup or shutdown is infrequent, the duration of excess
emissions is brief in each event, and the design of the source is such
that the period of excess emissions cannot be avoided without causing
damage to equipment or persons; or

(3)	when the emissions standards applicable during a startup or shutdown
are defined by other requirements of Applicable Rules and Regulations or
any applicable permit.

(b)	In any enforcement proceeding, the source seeking to establish the
applicability of any exception during a startup or shutdown has the
burden of proof.

(c)	In the event this startup and shutdown provision conflicts with
another applicable requirement, the more stringent requirement shall
apply.

3.	Maintenance.

(a)	Maintenance should be performed during planned shutdown or repair of
process equipment such that excess emissions are avoided.  Unavoidable
maintenance that results in brief periods of excess emissions and that
is necessary to prevent or minimize emergency conditions or equipment
malfunctions constitutes an affirmative defense to an enforcement action
brought for noncompliance with emission standards, or other regulatory
requirements if the source can demonstrate the following:

(1)	the source can identify the need for the maintenance;

(2)	the source was at the time being properly operated;

(3)	during the maintenance the source took all reasonable steps to
minimize levels of emissions that exceeded the emission standards, or
other requirements of Applicable Rules and Regulations or any applicable
permit;

(4)	the source submitted notice of the maintenance to the DEQ within 5
working days of the time the maintenance began or such other times as
allowed by DEQ; and

(5)	the notice shall contain a description of the maintenance, any steps
taken to mitigate emissions, and corrective actions taken.

(b)	In any enforcement proceeding, the source seeking to establish the
applicability of this section has the burden of proof.

(c)	In the event this maintenance provision conflicts with another
applicable requirement, the more stringent requirement shall apply.

SECTION 11.  SEVERABILITY

If any provision, section, subsection, sentence, clause or phrase of any
of these regulations, or the application of same to any person or set of
circumstances is for any reason challenged or held to be invalid or
void, the validity of the remaining regulations and/or portions thereof
or their application to other persons or sets of circumstances shall not
be affected thereby.

SECTION 12.  PROVISIONS FOR EXISTING HOSPITAL/MEDICAL/INFECTIOUS WASTE
INCINERATORS

1.	Applicability.

(a)	Except as provided in subparagraphs (b) through (h) of this
paragraph, the designated or affected facility to which Section 12
applies is each individual hospital/medical/infectious waste incinerator
(HMIWI) for which construction was commenced on or before June 20, 1996.

(b)	A combustor is not subject to Section 12 of these regulations during
periods when only pathological waste, low-level radioactive waste,
and/or chemotherapeutic waste is burned, provided the owner or operator
of the combustor:

(1)	Notifies the Department of an exemption claim; and

(2)	Keeps records on a calendar quarter basis of the periods of time
when only pathological waste, low-level radioactive waste, and/or
chemotherapeutic waste is burned.

(c)	Any co-fired combustor is not subject to Section 12 of these
regulations if the owner or operator of the co-fired combustor:

(1)	Notifies the Department of an exemption claim;

(2)	Provides an estimate of the relative weight of hospital waste,
medical/infectious waste, and other fuels and/or wastes to be combusted;
and

(3)	Keeps records on a calendar quarter basis of the weight of hospital
waste and medical/infectious waste combusted, and the weight of all
other fuels and wastes combusted at the co-fired combustor.

(d)	Any combustor required to have a permit under Section 3005 of the
Solid Waste Disposal Act is not subject to Section 12 of these
regulations.

(e)	Any combustor which meets the applicability requirements in
standards or guidelines for certain municipal waste combustors under
Subpart Cb, Ea, or Eb of 40 C.F.R. 60 is not subject to Section 12 of
these regulations.

(f)	Any pyrolysis unit is not subject to Section 12 of these
regulations.

(g)	Cement kilns firing hospital waste and/or medical/infectious waste
are not subject to Section 12 of these regulations.

(h)	Physical or operational changes made to an existing HMIWI unit
solely for the purpose of complying with Section 12 of these regulations
are not considered a modification and do not result in an existing HMIWI
unit becoming subject to the new source provisions under Section 6 of
these regulations and Subpart Ec of 40 C.F.R. 60.

(i)	Each existing HMIWI is subject to the permitting requirements in Air
Emissions Operating Permit Regulations for the Purposes of Title V of
the Federal Clean Air Act, APC-S-6.  Each owner and operator of an
existing HMIWI shall submit an application for a Title V permit to the
Department by December 15, 1999.

(j)	Beginning September 15, 2000, designated facilities subject to
Section 12 of these regulations shall operate pursuant to a permit
issued under Air Emissions Operating Permit Regulations for the Purposes
of Title V of the Federal Clean Air Act, APC-S-6.

2.	For the purpose of the requirements in Section 12 of these
regulations, the following definitions apply:

(a)	"Administrator of EPA" means the Administrator of the United States
Environmental Protection Agency or his authorized representative.

(b)	"Batch HMIWI" means an HMIWI that is designed such that neither
waste charging nor ash removal can occur during combustion.

(c)	"Biologicals" means preparations made from living organisms and
their products, including vaccines, cultures, etc., intended for use in
diagnosing, immunizing, or treating humans or animals or in research
pertaining thereto.

(d)	"Blood Products" means any product derived from human blood,
including but not limited to blood plasma, platelets, red or white blood
corpuscles, and other derived licensed products, such as interferon,
etc.

(e)	"Body Fluids" means liquid emanating or derived from humans and
limited to blood; dialysate; amniotic, cerebrospinal, synovial, pleural,
peritoneal and pericardial fluids; and semen and vaginal secretions.

(f)	"Bypass stack" means a device used for discharging combustion gases
to avoid severe damage to the air pollution control device or other
equipment.

(g)	"Chemotherapeutic waste" means waste material resulting from the
production or use of antineoplastic agents used for the purpose of
stopping or reversing the growth of malignant cells.

(h)	"Co-fired combustor" means a unit combusting hospital waste and/or
medical/infectious waste with other fuels or wastes (e.g., coal,
municipal solid waste) and subject to an enforceable requirement
limiting the unit to combusting a fuel feed stream, 10 percent or less
of the weight of which is comprised, in aggregate, of hospital waste and
medical/infectious waste as measured on a calendar quarter basis.  For
purposes of this definition, pathological waste, chemotherapeutic waste,
and low-level radioactive waste are considered "other" wastes when
calculating the percentage of hospital waste and medical/infectious
waste combusted.

(i)	"Continuous emission monitoring system or CEMS" means a monitoring
system for continuously measuring and recording the emissions of a
pollutant from an affected facility.

(j)	"Continuous HMIWI" means an HMIWI that is designed to allow waste
charging and ash removal during combustion.

(k)	"Dioxins/furans" means the combined emissions of tetra-through
octa-chlorinated dibenzo-para-dioxins and dibenzofurans, as measured by
EPA Reference Method 23.

(l)	"Dry scrubber" means an add-on air pollution control system that
injects dry alkaline sorbent (dry injection) or sprays an alkaline
sorbent (spray dryer) to react with and neutralize acid gases in the
HMIWI exhaust stream forming a dry powder material.

(m)	"Fabric filter or baghouse" means an add-on air pollution control
system that removes particulate matter (PM) and nonvaporous metals
emissions by passing flue gas through filter bags.

(n)	"Facilities manager" means the individual in charge of purchasing,
maintaining, and operating the HMIWI or the owner’s or operator’s
representative responsible for the management of the HMIWI.  Alternative
titles may include Director of Facilities or Vice President of Support
Services.

(o)	"High-air phase" means the stage of the batch operating cycle when
the primary chamber reaches and maintains maximum operating
temperatures.

(p)	"Hospital" means any facility which has an organized medical staff,
maintains at least six inpatient beds, and where the primary function of
the institution is to provide diagnostic and therapeutic patient
services and continuous nursing care primarily to human inpatients who
are not related and who stay on average in excess of 24 hours per
admission.  This definition does not include facilities maintained for
the sole purpose of providing nursing or convalescent care to human
patients who generally are not acutely ill but who require continuing
medical supervision.

(q)	"Hospital/medical/infectious waste incinerator or HMIWI or HMIWI
unit" means any device that combusts any amount of hospital waste and/or
medical/infectious waste.

(r)	"Hospital/medical/infectious waste incinerator operator or HMIWI
operator" means any person who operates, controls, or supervises the
day-to-day operation of an HMIWI.

(s)	"Hospital waste" means discards generated at a hospital, except
unused items returned to the manufacturer.  The definition of hospital
waste does not include human corpses, remains, and anatomical parts that
are intended for interment or cremation.

(t)	"Infectious agent" means any organism (such as a virus or bacteria)
that is capable of being communicated by invasion and multiplication in
body tissues and capable of causing disease or adverse health impacts in
humans.

(u)	"Intermittent HMIWI" means an HMIWI that is designed to allow waste
charging, but not ash removal, during combustion.

(v)	"Large HMIWI" means:

(1)	Except as provided in subparagraph (2);

(i)	An HMIWI whose maximum design waste burning capacity is more than
500 pounds per hour; or

(ii)	A continuous or intermittent HMIWI whose maximum charge rate is
more that 500 pounds per hour; or

(iii)	A batch HMIWI whose maximum charge rate is more that 4,000 pounds
per day.

(2)	The following are not large HMIWI:

(i)	A continuous or intermittent HMIWI whose maximum charge rate is less
than or equal to 500 pounds per hour; or

(ii)	A batch HMIWI whose maximum charge rate is less than or equal to
4,000 pounds per day.

(w)	"Low-level radioactive waste" means waste material which contains
radioactive nuclides emitting primarily beta or gamma radiation, or
both, in concentrations or quantities that exceed applicable Federal or
State standards for unrestricted release.  Low-level radioactive waste
is not high-level radioactive waste, spent nuclear fuel, or by-product
material as defined by the Atomic Energy Act of 1954 [42 U.S.C. 2014
(e)(2)].

(x)	"Malfunction" means any sudden, infrequent, and not reasonably
preventable failure of air pollution control equipment, process
equipment, or a process to operate in a normal or usual manner.
Failures that are caused, in part, by poor maintenance or careless
operation are not malfunctions.  During periods of malfunction the
operator shall operate within established parameters as much as
possible, and monitoring of all applicable operating parameters shall
continue until all waste has been combusted or until the malfunction
ceases, whichever comes first.

(y)	"Maximum charge rate" means:

(1)	For continuous and intermittent HMIWI, 110 percent of the lowest
3-hour average charge rate measured during the most recent performance
test demonstrating compliance with all applicable emission limits.

(2)	For batch HMIWI, 110 percent of the lowest daily charge rate
measured during the most recent performance test demonstrating
compliance with all applicable emission limits.

(z)	"Maximum design waste burning capacity" means:

For intermittent and continuous HMIWI,

Where:

C = HMIWI capacity, lb/hr

PV = primary chamber volume, ft3

15,000 = primary chamber heat release rate factor, Btu/ft3/hr

8,500 = standard waste heating value, Btu/lb;

(2)	 For batch HMIWI,

Where:

C = HMIWI capacity, lb/hr

PV = primary chamber volume, ft3

4.5 = waste density, lb/ft;

8 = typical hours of operation of a batch HMIWI, hours.

(aa)	"Maximum fabric filter inlet temperature" means 110 percent of the
lowest 3-hour average temperature at the inlet to the fabric filter
(taken, at a minimum, once every minute) measured during the most recent
performance test demonstrating compliance with the dioxin/furan emission
limit.

(bb)	"Maximum flue gas temperature" means 110 percent of the lowest
3-hour average temperature at the outlet from the wet scrubber (taken,
at a minimum, once every minute) measured during the most recent
performance test demonstrating compliance with the mercury (Hg) emission
limit.

(cc)	"Medical/infectious waste" means any waste generated in the
diagnosis, treatment, or immunization of human beings or animals, in
research pertaining thereto, or in the production or testing of
biologicals that is listed in paragraphs (1) through (7) of this
definition.  The definition of medical/infectious waste does not include
ash from incineration of medical/infectious waste, once the incineration
process has been completed; human corpses, remains, and anatomical parts
that are intended for interment or cremation; and domestic sewage
materials, hazardous waste, and household waste identified, listed, or
defined in Part 261 of Mississippi Hazardous Waste Management
Regulations.

(1)	Cultures and stocks of infectious agents and associated biologicals,
including: cultures from medical and pathological laboratories; cultures
and stocks of infectious agents from research and industrial
laboratories; wastes from the production of biologicals; discarded live
and attenuated vaccines; and culture dishes and devices used to
transfer, inoculate, and mix cultures.

(2)	Human pathological waste, including tissues, organs, and body parts
and body fluids that are removed during surgery or autopsy, or other
medical procedures, and specimens of body fluids and their containers.

(3)	Human blood and blood products including:

(i)	Liquid waste human blood;

(ii)	Products of blood;

(iii)	Items saturated and/or dripping with human blood; or

(iv)	Items that were saturated and/or dripping with human blood that are
now caked with dried human blood; including serum, plasma, and other
blood components, and their containers, which were used or intended for
use in either patient care, testing and laboratory analysis or the
development of pharmaceuticals.  Intravenous bags are also included in
this category.

(4)	Sharps that have been used in animal or human patient care or
treatment or in medical, research, or industrial laboratories, including
hypodermic needles, syringes (with or without the attached needle),
Pasteur pipettes, scalpel blades, blood vials, needles with attached
tubing, and culture dishes (regardless of presence of infectious
agents).  Also included are other types of broken or unbroken glassware
that were in contact with infectious agents, such as used slides and
cover slips.

(5)	Animal waste including contaminated animal carcasses, body parts,
and bedding of animals that were known to have been exposed to
infectious agents during research (including research in veterinary
hospitals), production of biologicals or testing of pharmaceuticals.

(6)	Isolation wastes including biological waste and discarded materials
contaminated with blood, excretions, exudates, or secretions from humans
who are isolated to protect others from certain highly communicable
diseases, or isolated animals known to be infected with highly
communicable diseases.

(7)	Unused sharps including the following unused, discarded sharps:
hypodermic needles, suture needles, syringes, and scalpel blades.

(dd)	"Medium HMIWI" means:

(1)	Except as provided in subparagraph (2);

(i)	An HMIWI whose maximum design waste burning capacity is more than
200 pounds per hour but less than or equal to 500 pounds per hour; or

(ii)	A continuous or intermittent HMIWI whose maximum charge rate is
more than 200 pounds per hour but less than or equal to 500 pounds per
hour; or

(iii)	A batch HMIWI whose maximum charge rate is more than 1,600 pounds
per day but less than or equal to 4,000 pounds per day.

(2)	The following are not medium HMIWI:

(i)	A continuous or intermittent HMIWI whose maximum charge rate is less
than or equal to 200 pounds per hour or more than 500 pounds per hour;
or

(ii)	A batch HMIWI whose maximum charge rate is more than 4,000 pounds
per day or less than or equal to 1,600 pounds per day.

(ee)	"Minimum dioxin/furan sorbent flow rate" means 90 percent of the
highest 3-hour average dioxin/furan sorbent flow rate (taken, at a
minimum, once every hour) measured during the most recent performance
test demonstrating compliance with the dioxin/furan emission limit.

(ff)	"Minimum Hg sorbent flow rate" means 90 percent of the highest
3-hour average Hg sorbent flow rate (taken, at a minimum, once every
hour) measured during the most recent performance test demonstrating
compliance with the Hg emission limit.

(gg)	"Minimum hydrogen chloride (HCl) sorbent flow rate" means 90
percent of the highest 3-hour average HCl sorbent flow rate (taken, at a
minimum, once every hour) measured during the most recent performance
test demonstrating compliance with the HCl emission limit.

(hh)	"Minimum horsepower or amperage" means 90 percent of the highest
3-hour average horsepower or amperage to the wet scrubber (taken, at a
minimum, once every minute) measured during the most recent performance
test demonstrating compliance with the applicable emission limits.

(ii)	"Minimum pressure drop across the wet scrubber" means 90 percent of
the highest 3-hour average pressure drop across the wet scrubber PM
control device (taken, at a minimum, once every minute) measured during
the most recent performance test demonstrating compliance with the PM
emission limit.

(jj)	"Minimum scrubber liquor flow rate" means 90 percent of the highest
3-hour average liquor flow rate at the inlet to the wet scrubber (taken,
at a minimum, once every minute) measured during the most recent
performance test demonstrating compliance with all applicable emission
limits.

(kk)	"Minimum scrubber liquor pH" means 90 percent of the highest 3-hour
average liquor pH at the inlet to the wet scrubber (taken, at a minimum,
once every minute) measured during the most recent performance test
demonstrating compliance with the HCl emission limit.

(ll)	"Minimum secondary chamber temperature" means 90 percent of the
highest 3-hour average secondary chamber temperature (taken, at a
minimum, once every minute) measured during the most recent performance
test demonstrating compliance with the PM, CO, or dioxin/furan emission
limits.

(mm)	"Modification or Modified HMIWI" means any change to an HMIWI unit
after March 16, 1998, such that:

(1)	The cumulative costs of the modifications, over the life of the
unit, exceed 50 per centum of the original cost of the construction and
installation of the unit (not including the cost of any land purchased
in connection with such construction or installation) updated to current
costs, or

(2)	The change involves a physical change in or change in the method of
operation of the unit which increases the amount of any air pollutant
emitted by the unit for which standards have been established under
Section 129 or Section 111 of the Federal Clean Air Act.

(nn)	"Operating day" means a 24-hour period between 12:00 midnight and
the following midnight during which any amount of hospital waste or
medical/infectious waste is combusted at any time in the HMIWI.

(oo)	"Operation" means the period during which waste is combusted in the
incinerator excluding periods of startup or shutdown.

(pp)	"Particulate matter or PM" means the total particulate matter
emitted from an HMIWI as measured by EPA Reference Method 5 or EPA
Reference Method 29.

(qq)	"Pathological waste" means waste material consisting of only human
or animal remains, anatomical parts, and/or tissue, the bags/containers
used to collect and transport the waste material, and animal bedding (if
applicable).

(rr)	"Primary chamber" means the chamber in an HMIWI that receives waste
material, in which the waste is ignited, and from which ash is removed.

(ss)	"Pyrolysis" means the endothermic gasification of hospital waste
and/or medical/infectious waste using external energy.

(tt)	"Secondary chamber" means a component of the HMIWI that receives
combustion gases from the primary chamber and in which the combustion
process is completed.

(uu)	"Shutdown" means the period of time after all waste has been
combusted in the primary chamber.  For continuous HMIWI, shutdown shall
commence no less than 2 hours after the last charge to the incinerator.
For intermittent HMIWI, shutdown shall commence no less than 4 hours
after the last charge to the incinerator.  For batch HMIWI, shutdown
shall commence no less than 5 hours after the high-air phase of
combustion has been completed.

(vv)	"Small HMIWI" means:

(1)	Except as provided in subparagraph (2);

(i)	An HMIWI whose maximum design waste burning capacity is less than or
equal to 200 pounds per hour; or

(ii)	A continuous or intermittent HMIWI whose maximum charge rate is
less than or equal to 200 pounds per hour; or

(iii)	A batch HMIWI whose maximum charge rate is less than or equal to
1,600 pounds per day.

(2)	The following are not small HMIWI:

(i)	A continuous or intermittent HMIWI whose maximum charge rate is more
than 200 pounds per hour.

(ii)	A batch HMIWI whose maximum charge rate is more than 1,600 pounds
per day.

(ww)	"Standard conditions" means a temperature of 20C and a pressure
of 101.3 kilopascals.

(xx)	"Standard Metropolitan Statistical Area or SMSA" means any areas
listed in OMB Bulletin No. 93-17 entitled "Revised Statistical
Definitions for Metropolitan Areas" dated June 30, 1993.

(yy)	"Startup" means the period of time between the activation of the
system and the first charge to the unit.  For batch HMIWI, startup means
the period of time between activation of the system and ignition of the
waste.

(zz)	"Wet scrubber" means an add-on air pollution control device that
utilizes an alkaline scrubbing liquor to collect particulate matter
(including nonvaporous metals and condensed organic) and/or to absorb
and neutralize acid gases.

3.	Emission limits.

(a)	Except as provided for in subparagraph (b), no owner or operator of
an affected facility shall cause to be discharged into the atmosphere
from that affected facility any gases that contain stack emissions in
excess of the limits presented in Table 1 of this paragraph.

(b)	The emission limits in Table 2 shall apply to any small HMIWI which
is located more than 50 miles from the boundary of the nearest Standard
Metropolitan Statistical Area (SMSA) and which burns less than 2,000
pounds per week of hospital waste and medical/infectious waste.  The
2,000 lb/week limitation does not apply during performance tests.

(c)	No owner or operator of an affected facility shall cause to be
discharged into the atmosphere from the stack of that affected facility
any gases that exhibit greater than 10 percent opacity (6-minute block
average).

TABLE 1.  EMISSION LIMITS FOR SMALL, MEDIUM, AND LARGE HMIWI

Pollutant

Units (7 percent oxygen, dry basis)

Emission Limits

HMIWI Size

Small

Medium

Large

Particulate matter

Milligrams per dry standard cubic meter (grains per dry standard cubic
foot)

115 (0.05)

69 (0.03)

34 (0.015)

Carbon monoxide

Parts per million by volume

40

40

40

Dioxins/furans

Nanograms per dry standard cubic meter total dioxins/furans (grains per
billion dry standard cubic feet) or nanograms per dry standard cubic
meter TEQ (grains per billion dry standard cubic feet)

125 (55)

or

2.3 (1.0)

125 (55)

or

2.3 (1.0)

125 (55)

or

2.3 (1.0)

Hydrogen chloride

Parts per million by volume or percent reduction

100 or 93%

100 or 93%

100 or 93%

Sulfur dioxide

Parts per million by volume

55

55

55

Nitrogen oxides

Parts per million by volume

250

250

250

Lead

Milligrams per dry standard cubic meter (grains per thousand dry
standard cubic feet) or percent reduction

1.2 (0.52)

or

70%

1.2 (0.52)

or

70%

1.2 (0.52)

or

 70%

Cadmium

Milligrams per dry standard cubic meter (grains per thousand dry
standard cubic feet) or percent reduction

0.16 (0.07)

or

65%

0.16 (0.07)

or

65%

0.16 (0.07)

or

65%

Mercury

Milligrams per dry standard cubic meter (grains per thousand dry
standard cubic feet) or percent reduction

0.55 (0.24)

or

85%

0.55

(0.24)

or 85%

0.55

(0.24)

or 85%

TABLE 2.  EMISSION LIMITS FOR SMALL RURAL HMIWI

Pollutant

Units (7 percent oxygen, dry basis)

HMIWI

Emission

Limits

Particulate matter

Milligrams per dry standard cubic meter (grains per dry standard cubic
foot)

197 (0.086)

Carbon monoxide

Parts per million by volume

40

Dioxins/furans

Nanograms per dry standard cubic meter total dioxins/furans (grains per
billion dry standard cubic feet) or nanograms per dry standard cubic
meter TEQ (grains per billion dry standard cubic feet)

800 (350)

 or

15 (6.6)

Hydrogen chloride

Parts per million by volume

3100

Sulfur dioxide

Parts per million by volume

55

Nitrogen oxides

Parts per million by volume

250

Lead

Milligrams per dry standard cubic meter (grains per thousand dry
standard cubic feet)

10 (4.4)

Cadmium

Milligrams per dry standard cubic meter (grains per thousand dry
standard cubic feet)

4 (1.7)

Mercury

Milligrams per dry standard cubic meter (grains per thousand dry
standard cubic feet)

7.5 (3.3)

4.	Operator Training and Qualification Requirements.

(a)	Compliance with the requirements of this paragraph shall occur no
later than September 15, 2000.

(b)	No owner or operator of an affected facility shall allow the
affected facility to operate at any time unless a fully trained and
qualified HMIWI operator is accessible, either at the facility or
available within 1 hour.  The trained and qualified HMIWI operator may
operate the HMIWI directly or be the direct supervisor of one or more
HMIWI operators.

(c)	Operator training and qualification shall be obtained through a
State-approved program that meets the requirements included in
subparagraphs (d) through (k) of this paragraph.

(d)	Training shall be obtained by completing an HMIWI operator training
course that includes, at a minimum, the following provisions:

(1)	24 hours of training on the following subjects:

(i)	Environmental concerns, including pathogen destruction and types of
emissions;

(ii)	Basic combustion principles, including products of combustion;

(iii)	Operation of the type of incinerator to be used by the operator,
including proper startup, waste charging, and shutdown procedures;

(iv)	Combustion controls and monitoring;

(v)	Operation of air pollution control equipment and factors affecting
performance (if applicable);

(vi)	Methods to monitor pollutants (continuous emission monitoring
systems and monitoring of HMIWI and air pollution control device
operating parameters) and equipment calibration procedures (where
applicable);

(vii)	Inspection and maintenance of the HMIWI, air pollution control
devices, and continuous emission monitoring systems;

(viii)	Actions to correct malfunctions or conditions that may lead to
malfunction;

(ix)	Bottom and fly ash characteristics and handling procedures;

(x)	Applicable Federal, State, and local regulations;

(xi)	Work safety procedures;

(xii)	Pre-startup inspections; and

(xiii)	Recordkeeping requirements.

(2)	An examination designed and administered by the instructor.

(3)	Reference material distributed to the attendees covering the course
topics.

(e)	Qualification shall be obtained by:

(1)	Completion of a training course that satisfies the criteria under
subparagraph (d) of this paragraph; and

(2)	Either 6 months experience as an HMIWI operator, 6 months experience
as a direct supervisor of an HMIWI operator, or completion of at least
two burn cycles under the observation of two qualified HMIWI operators.

(f)	Qualification is valid from the date on which the examination is
passed or the completion of the required experience, whichever is later.

(g)	To maintain qualification, the trained and qualified HMIWI operator
shall complete and pass an annual review or refresher course of at least
4 hours covering, at a minimum, the following:

(1)	Update of regulations;

(2)	Incinerator operation, including startup and shutdown procedures;

(3)	Inspection and maintenance;

(4)	Responses to malfunctions or conditions that may lead to
malfunction; and

(5)	Discussion of operating problems encountered by attendees.

(h)	A lapsed qualification shall be renewed by one of the following
methods:

(1)	For a lapse of less than 3 years, the HMIWI operator shall complete
and pass a standard annual refresher course described in subparagraph
(g) of this paragraph above.

(2)	For a lapse of 3 years or more, the HMIWI operator shall complete
and pass a training course with the minimum criteria described in
subparagraph (d) of this paragraph above.

(i)	The owner or operator of an affected facility shall maintain
documentation at the facility that address the following:

(1)	Summary of the applicable standards under Section 12 of these
regulations;

(2)	Description of basic combustion theory applicable to an HMIWI;

(3)	Procedures for receiving, handling, and charging waste;

(4)	HMIWI startup, shutdown, and malfunction procedures;

(5)	Procedures for maintaining proper combustion air supply levels;

(6)	Procedures for operating the HMIWI and associated air pollution
control systems within the standards established under Section 12 of
these regulations;

(7)	Procedures for responding to periodic malfunction or conditions that
may lead to malfunction;

(8)	Procedures for monitoring HMIWI emissions;

(9)	Reporting and recordkeeping procedures; and

(10)	Procedures for handling ash.

(j)	The owner or operator of an affected facility shall establish a
program for reviewing the information listed in subparagraph (i) of this
paragraph annually with each HMIWI operator.

(1)	The initial review of the information listed in subparagraph (i) of
this paragraph shall be conducted by March 15, 2000, or prior to
assumption of responsibilities affecting HMIWI operation, whichever date
is later.

(2)	Subsequent reviews of the information listed in subparagraph (i) of
this paragraph shall be conducted annually.

(k)	The information listed in subparagraph (i) of this paragraph shall
be kept in a readily accessible location for all HMIWI operators.  This
information, along with records of training shall be available for
inspection by the Department upon request.

5.	Waste Management Guidelines.

The owner or operator of an affected facility shall prepare a waste
management plan.  The waste management plan shall identify both the
feasibility and the approach to separate certain components of solid
waste from the health care waste stream in order to reduce the amount of
toxic emissions from incinerated waste.  A waste management plan may
include, but is not limited to, elements such as paper, cardboard,
plastics, glass, battery, or metal recycling; or purchasing recycled or
recyclable products.  A waste management plan may include different
goals or approaches for different areas or departments of the facility
and need not include new waste management goals for every waste stream.
It should identify, where possible, reasonably available additional
waste management measures, taking into account the effectiveness of
waste management measures already in place, the costs of additional
measures, the emission reductions expected to be achieved, and any other
environmental or energy impacts they might have.  The American Hospital
Association publication entitled "An Ounce of Prevention: Waste
Reduction Strategies for Health Care Facilities" shall be considered in
the development of the waste management plan.

6.	Inspection Guidelines.

(a)	The requirements of this paragraph apply to any small HMIWI subject
to the emission limits in Table 2 of paragraph 3 in Section 12 of these
regulations.

(b)	No later than September 15, 2000 and annually thereafter (no more
than 12 months following the previous annual equipment inspection) an
equipment inspection shall be performed.

(1)	At a minimum, an inspection shall include the following:

(i)	Inspect all burners, pilot assemblies, and pilot sensing devices for
proper operation; clean pilot flame sensor, as necessary;

(ii)	Ensure proper adjustment of primary and secondary chamber
combustion air, and adjust as necessary;

(iii)	Inspect hinges and door latches, and lubricate as necessary;

(iv)	Inspect dampers, fans, and blowers for proper operation;

(v)	Inspect HMIWI door and door gaskets for proper sealing;

(vi)	Inspect motors for proper operation;

(vii)	Inspect primary chamber refractory lining; clean and
repair/replace lining as necessary;

(viii)	Inspect incinerator shell for corrosion and/or hot spots;

(ix)	Inspect secondary/tertiary chamber and stack, clean as necessary;

(x)	Inspect mechanical loader, including limit switches, for proper
operation, if applicable;

(xi)	Visually inspect waste bed (grates), and repair/seal, as
appropriate;

(xii)	For the burn cycle that follows the inspection, document that the
incinerator is operating properly and make any necessary adjustments;

(xiii)	Inspect air pollution control devices(s) for proper operation, if
applicable;

(xiv)	Inspect waste heat boiler systems to ensure proper operation, if
applicable;

(xv)	Inspect bypass stack components;

(xvi)	Ensure proper calibration of thermocouples, sorbent feed systems,
and any other monitoring equipment; and

(xvii)	Generally observe that the equipment is maintained in good
operating condition.

(2)	Within 10 operating days following an equipment inspection, all
necessary repairs shall be completed unless the owner or operator
obtains written approval from the Department establishing a date whereby
all necessary repairs of the designated facility shall be completed.

7.	Compliance and Performance Testing.

(a)	The emission limits under paragraph 3 in Section 12 of these
regulations shall apply at all times except during periods of startup,
shutdown, or malfunction, provided that no hospital waste or
medical/infectious waste is charged to the affected facility during
startup, shutdown, or malfunction.

(b)	The owner or operator of an affected facility shall conduct an
initial performance test in accordance with the performance test
requirements contained in 40 C.F.R. 60.8 to determine compliance with
the emission limits using the procedures and test methods listed in
subparagraphs (b)(1) through (b)(11) of this paragraph.  The use of the
bypass stack during a performance test shall invalidate the performance
test.

(1)	All performance tests shall consist of a minimum of three test runs
conducted under representative operating conditions.

(2)	The minimum sample time shall be 1 hour per test run unless
otherwise indicated.

(3)	EPA Reference Method 1 of Appendix A of 40 C.F.R. 60 shall be used
to select the sampling location and number of traverse points.

(4)	EPA Reference Method 3 or 3A of Appendix A of 40 C.F.R. 60 shall be
used for gas composition analysis, including measurement of oxygen
concentration.  EPA Reference Method 3 or 3A of Appendix A of 40 C.F.R.
60 shall be used simultaneously with each reference method.

(5)	The pollutant concentrations shall be adjusted to 7 percent oxygen
using the following equation:

Where:

Cadj = pollutant concentration adjusted to 7 percent oxygen;

Cmeas = pollutant concentration measured on a dry basis;

(20.9-7) = 20.9 percent oxygen - 7 percent oxygen (defined oxygen
correction basis);

20.9 = oxygen concentration in air, percent; and

%O2 = oxygen concentration measured on a dry basis, percent.

(6)	EPA Reference Method 5 or 29 Appendix A of 40 C.F.R. 60 shall be
used to measure the particulate matter emissions.

(7)	EPA Reference method 9 of Appendix A of 40 C.F.R. 60 shall be used
to measure stack opacity.

(8)	EPA Reference Method 10 or 10B of Appendix A of 40 C.F.R. 60 shall
be used to measure the CO emissions.

(9)	EPA Reference Method 23 of Appendix A of 40 C.F.R. 60 shall be used
to measure total dioxin/furan emissions.  The minimum sample time shall
be 4 hours per test run.  If the affected facility has selected the
toxic equivalency standards for dioxin/furans, under paragraph 3 in
Section 12 of these regulations, the following procedures shall be used
to determine compliance:

(i)	Measure the concentration of each dioxin/furan tetra-through
octa-congener emitted using EPA Reference Method 23.

(ii)	For each dioxin/furan congener measured in accordance with
subparagraph (b)(9)(i) of this paragraph, multiply the congener
concentration by its corresponding toxic equivalency factor specified in
Table 3 in Section 12 of these regulations.

(iii)	Sum the products calculated in accordance with subparagraph
(b)(9)(ii) of this paragraph to obtain the total concentration of
dioxins/furans emitted in terms of toxic equivalency.

(10)	EPA Reference Method 26 of Appendix A of 40 C.F.R. 60 shall be used
to measure HCl emissions.  If the affected facility has selected the
percentage reduction standards for HCl under paragraph 3 in Section 12
of these regulations, the percentage reduction in HCl emissions (%RHCl)
is computed using the following formula:

Where:

(%RHCl)= percentage reduction of HCl emissions achieved;

Ei = HCl emission concentration measured at the control device inlet,
corrected to 7 percent oxygen (dry basis); and

Eo = HCl emission concentration measured at the control device outlet,
corrected to 7 percent oxygen (dry basis).

(11)	EPA Reference Method 29 of Appendix A of 40 C.F.R. 60 shall be used
to measure Pb, Cd, and Hg emissions.  If the affected facility has
selected the percentage reduction standards for metals under paragraph 3
in Section 12 of these regulations, the percentage reduction in
emissions (%Rmetal) is computed using the following formula:

Where:

(%Rmetal)= percentage reduction of metal emission (Ph, Cd, or Hg)
achieved;

 	Ei = metal emission concentration (Pb, Cd, or Hg) measured at the
control device inlet, corrected to 7 percent oxygen (dry basis); and

 	Eo = metal emission concentration (Pb, Cd, or Hg) measured at the
control device outlet, corrected to 7 percent oxygen (dry basis).

TABLE 3.  TOXIC EQUIVALENCY FACTORS

Dioxin/Furan Congener

Toxic Equivalency

Factor

2,3,7,8-tetrachlorinated dibenzo-p-dioxin

1

1,2,3,7,8-pentachlorinated dibenzo-p-dioxin

0.5

1,2,3,4,7,8- hexachlorinated dibenzo-p-dioxin

0.1

1,2,3,7,8,9-hexachlorinated dibenzo-p-dioxin

0.1

1,2,3,6,7,8-hexachlorinated dibenzo-p-dioxin

0.1

1,2,3,4,6,7,8-heptachlorinated dibenzo-p-dioxin

0.01

octachlorinated dibenzo-p-dioxin

0.001

2,3,7,8-tetrachlorinated dibenzofuran

0.1

2,3,4,7,8-pentachlorinated dibenzofuran

0.5

1,2,3,7,8-pentachlorinated dibenzofuran

0.05

1,2,3,4,7,8-hexachlorinated dibenzofuran

0.1

1,2,3,6,7,8-hexachlorinated dibenzofuran

0.1

1,2,3,7,8,9-hexachlorinated dibenzofuran

0.1

2,3,4,6,7,8-hexachlorinated dibenzofuran

0.1

1,2,3,4,6,7,8-heptachlorinated dibenzofuran

0.01

1,2,3,4,7,8,9-heptachlorinated dibenzofuran

0.01

octachlorinated dibenzofuran

0.001

(c)	Following the date on which the initial performance test is
completed or is required to be completed under the performance test
requirements contained in 40 C.F.R. 60.8, whichever date comes first,
the owner or operator of an affected facility shall:

(1)	Determine compliance with the opacity limit by conducting an annual
performance test (no more than 12 months following the previous
performance test) using the applicable procedures and test methods
listed in subparagraph (b) of this paragraph.

(2)	Determine compliance with the PM, CO, and HCl emission limits by
conducting an annual performance test (no more than 12 months following
the previous performance test) using the applicable procedures and test
methods listed in subparagraph (b) of this paragraph.  If all three
performance tests over a 3-year period indicate compliance with the
emission limit for a pollutant (PM, CO, or HCl), the owner or operator
may forego a performance test for that pollutant for the subsequent 2
years.  At a minimum, a performance test for PM, CO, and HCl shall be
conducted every third year (no more than 36 months following the
previous performance test).  If a performance test conducted every third
year indicates compliance with the emission limit for a pollutant (PM,
CO, or HCl), the owner or operator may forego a performance test for
that pollutant for up to an additional 2 years.  If any performance test
indicates noncompliance with the respective emission limit, a
performance test for that pollutant shall be conducted annually until
all annual performance tests over a 3-year period indicate compliance
with the emission limit.  The use of the bypass stack during a
performance test shall invalidate the performance test.

(3)	Facilities using a CEMS to demonstrate compliance with any of the
emission limits under paragraph 3 in Section 12 of these regulations
shall:

(i)	Determine compliance with the appropriate emission limit(s) using a
12-hour rolling average, calculated each hour as the average of the
previous 12 operating hours (not including startup, shutdown, or
malfunction).

(ii)	Operate all CEMS in accordance with the applicable procedures under
Appendices B and F of 40 C.F.R. 60.

(d)	The owner or operator of an affected facility equipped with a dry
scrubber followed by a fabric filter, a wet scrubber, or a dry scrubber
followed by a fabric filter and wet scrubber shall:

(1)	Establish the appropriate maximum and minimum operating parameters,
indicated in Table 4 of Section 12 of these regulations for each control
system, as site specific operating parameters during the initial
performance test to determine compliance with the emission limits; and

(2)	Following the date on which the initial performance test is
completed or is required to be completed under the performance test
requirements contained in 40 C.F.R. 60.8, whichever date comes first,
ensure that the affected facility does not operate above any of the
applicable maximum operating parameters or below any of the applicable
minimum operating parameters listed in Table 4 in Section 12 of these
regulations and measured as 3-hour rolling averages (calculated each
hour as the average of the previous 3 operating hours) at all times
except during periods of startup, shutdown, and malfunction.  Operating
parameter limits do not apply during performance tests.  Operation above
the established maximum or below the established minimum operating
parameter(s) shall constitute a violation of established operating
parameter(s).

(e)	Except as provided in subparagraph (h) of this paragraph, for
affected facilities equipped with a dry scrubber followed by a fabric
filter:

(1)	Operation of the affected facility above the maximum charge rate and
below the minimum secondary chamber temperature (each measured on a
3-hour rolling average) simultaneously shall constitute a violation of
the CO emission limit.

(2)	Operation of the affected facility above the maximum fabric filter
inlet temperature, above the maximum charge rate, and below the minimum
dioxin/furan sorbent flow rate (each measured on a 3-hour rolling
average) simultaneously shall constitute a violation of the dioxin/furan
emission limit.

(3)	Operation of the affected facility above the maximum charge rate and
below the minimum HCl sorbent flow rate (each measured on a 3-hour
rolling average) simultaneously shall constitute a violation of the HCl
emission limit.

(4)	Operation of the affected facility above the maximum charge rate and
below the minimum Hg sorbent flow rate (each measured on a 3-hour
rolling average) simultaneously shall constitute a violation of the Hg
emission limit.

(5)	Use of the bypass stack (except during startup, shutdown, or
malfunction) shall constitute a violation of the PM, dioxin/furan, HCl,
Pb, Cd and Hg emission limits.

(f)	Except as provided in subparagraph (h) of this paragraph, for
affected facilities equipped with a wet scrubber:

(1)	Operation of the affected facility above the maximum charge rate and
below the minimum pressure drop across the wet scrubber or below the
minimum horsepower or amperage to the system (each measured on a 3-hour
rolling average) simultaneously shall constitute a violation of the PM
emission limit.

(2)	Operation of the affected facility above the maximum charge rate and
below the minimum secondary chamber temperature (each measured on a
3-hour rolling average) simultaneously shall constitute a violation of
the CO emission limit.

(3)	Operation of the affected facility above the maximum charge rate,
below the minimum secondary chamber temperature, and below the minimum
scrubber liquor flow rate (each measured on a 3-hour rolling average)
simultaneously shall constitute a violation of the dioxin/furan emission
limit.

(4)	Operation of the affected facility above the maximum charge rate and
below the minimum scrubber liquor pH (each measured on a 3-hour rolling
average) simultaneously shall constitute a violation of the HCl emission
limit.

(5)	Operation of the affected facility above the maximum flue gas
temperature and above the maximum charge rate (each measured on a 3-hour
rolling average) simultaneously shall constitute a violation of the Hg
emission limit.

(6)	Use of the bypass stack (except during startup, shutdown, or
malfunction) shall constitute a violation of the PM, dioxin/furan, HCl,
Pb, Cd and Hg emission limits.

(g)	Except as provided in subparagraph (h) of this paragraph, for
affected facilities equipped with a dry scrubber followed by a fabric
filter and a wet scrubber:

(1)	Operation of the affected facility above the maximum charge rate and
below the minimum secondary chamber temperature (each measured on a
3-hour rolling average) simultaneously shall constitute a violation of
the CO emission limit.

(2)	Operation of the affected facility above the maximum fabric filter
inlet temperature, above the maximum charge rate, and below the minimum
dioxin/furan sorbent flow rate (each measured on a 3-hour rolling
average) simultaneously shall constitute a violation of the dioxin/furan
emission limit.

(3)	Operation of the affected facility above the maximum charge rate and
below the minimum scrubber liquor pH (each measured on a 3-hour rolling
average) simultaneously shall constitute a violation of the HCl emission
limit.

(4)	Operation of the affected facility above the maximum charge rate and
below the minimum Hg sorbent flow rate (each measured on a 3-hour
rolling average) simultaneously shall constitute a violation of the Hg
emission limit.

(5)	Use of the bypass stack (except during startup, shutdown, or
malfunction) shall constitute a violation of the PM, dioxin/furan, HCl,
Pb, Cd and Hg emission limits.

(h)	The owner or operator of an affected facility may conduct a repeat
performance test within 30 days of violation of applicable operating
parameter(s) to demonstrate that the affected facility is not in
violation of the applicable emission limit(s).  Repeat performance tests
conducted pursuant to this paragraph shall be conducted using the
identical operating parameters that indicated a violation under
subparagraph (e), (f), or (g) of this paragraph.

(i)	The owner or operator of an affected facility using an air pollution
control device other than a dry scrubber followed by a fabric filter, a
wet scrubber, or a dry scrubber followed by a fabric filter and a wet
scrubber to comply with the emission limits under paragraph 3 in Section
12 of these regulations shall petition the Administrator for other
site-specific operating parameters to be established during the initial
performance test and continuously monitored thereafter.  The owner or
operator shall not conduct the initial performance test until after the
petition has been approved by the Administrator.

(j)	The owner or operator of an affected facility may conduct a repeat
performance test at any time to establish new values for the operating
parameters.  The Department may request a repeat performance test at any
time.

(k)	Any small HMIWI subject to the emission limits in Table 2 of
paragraph 3 in Section 12 of these regulations shall meet the following
compliance and performance testing requirements:

(1)	Conduct the performance testing requirements in subparagraphs (a),
(b)(1) through (b)(9), (b)(11) (mercury only), and (c)(1) of this
paragraph.  The 2,000 lb/week limitation does not apply during
performance tests.

(2)	Establish maximum charge rate and minimum secondary chamber
temperature as site-specific operating parameters during the initial
performance test to determine compliance with applicable emission
limits.

(3)	Following the date on which the initial performance test is
completed or is required to be completed under the performance test
requirements contained in 40 C.F.R. 60.8, whichever date comes first,
ensure that the designated facility does not operate above the maximum
charge rate or below the minimum secondary chamber temperature measured
as 3-hour rolling averages (calculated each hour as the average of the
previous 3 operating hours) at all times except during periods of
startup, shutdown, or malfunction.  Operating parameter limits do not
apply during performance tests.  Operation above the maximum charge rate
or below the minimum secondary chamber temperature shall constitute a
violation of the established operating parameter(s).

(4)	Except as provided in subparagraph (k)(5) of this paragraph below,
operation of the designated facility above the maximum charge rate and
below the minimum secondary chamber temperature (each measured on a
3-hour rolling average) simultaneously shall constitute a violation of
the PM, CO, and dioxin/furan emission limits.

(5)	The owner or operator of a designated facility may conduct a repeat
performance test within 30 days of violation of applicable operating
parameter(s) to demonstrate that the designated facility is not in
violation of the applicable emission limit(s).  Repeat performance tests
conducted pursuant to this paragraph must be conducted using the
identical operating parameters that indicated a violation under
subparagraph (k)(4), of this paragraph above.

8.	Monitoring.

(a)	The owner or operator of an affected facility shall install,
calibrate (to manufacturer’s specifications), maintain, and operate
devices (or establish methods) for monitoring the applicable maximum and
minimum operating parameters listed in Table 4 in Section 12 of these
regulations such that these devices (or methods) measure and record
values for these operating parameters at the frequencies indicated in
Table 4 in Section 12 of these regulations at all times except during
periods of startup and shutdown.

(b)	The owner of operator of an affected facility shall install,
calibrate (to manufacturer’s specifications), maintain, and operate a
device or method for measuring the use of the bypass stack including
date, time, and duration.

(c)	The owner or operator of an affected facility using something other
than a dry scrubber followed by a fabric filter, a wet scrubber, or a
dry scrubber followed by a fabric filter and a wet scrubber to comply
with the emission limits under paragraph 3 in Section 12 of these
regulations shall install, calibrate (to the manufacturer’s
specifications), maintain, and operate the equipment necessary to
monitor the site-specific operating parameters developed pursuant to
subparagraph 7(i) in Section 12 of these regulations.

(d)	The owner or operator of an affected facility shall obtain
monitoring data at all times during HMIWI operation except during
periods of monitoring equipment malfunction, calibration, or repair.  At
a minimum, valid monitoring data shall be obtained for 75 percent of the
operating hours per day and for 90 percent of the operating days per
calendar quarter that the affected facility is combusting hospital waste
and/or medical/infectious waste.

(e)	Any small HMIWI subject to the emission limits in Table 2 of
paragraph 3 in Section 12 of these regulations shall meet the following
monitoring requirements:

(1)	Install, calibrate (to manufacturer’s specifications), maintain,
and operate a device for measuring and recording the temperature of the
secondary chamber on a continuous basis, the output of which shall be
recorded, at a minimum, once every minute throughout operation.

(2)	Install, calibrate (to manufacturer’s specifications), maintain,
and operate a device which automatically measures and records the date,
time, and weight of each charge fed into the HMIWI.

(3)	The owner or operator of a designated facility shall obtain
monitoring data at all times during HMIWI operation except during
periods of monitoring equipment malfunction, calibration, or repair.  At
a minimum, valid monitoring data shall be obtained for 75 percent of the
operating hour per day and for 90 percent of the operating hour per
calendar quarter that the designated facility is combusting hospital
waste and/or medical/infectious waste.

TABLE 4.  OPERATING PARAMETERS TO BE MONITORED AND MINIMUM

MEASUREMENT AND RECORDING FREQUENCIES

Operating Parameters to be Monitored

Minimum Frequency

Control System

Data Measurement

Data Recording

Dry Scrubber followed by Fabric Filter

Wet Scrubber

Dry Scrubber followed by Fabric Filter and Wet Scrubber

Maximum operating parameters:

Maximum charge rate

Continuous

1 x hour

X

X

X

Maximum fabric filter inlet temperature

Continuous

1 x minute

X

X

Maximum flue gas temperature

Continuous

1 x minute

X

X

Minimum operating parameters:

Minimum secondary chamber temperature

Continuous

1 x minute

X

X

X

Minimum dioxin/furan sorbent flow rate

Hourly

1 x hour

X

X

Minimum HCl sorbent flow rate

Hourly

1 x hour

X

X

Minimum mercury (Hg) sorbent flow rate

Hourly

1 x hour

X

X

Minimum pressure drop across the wet scrubber or minimum horsepower or
amperage to wet scrubber

Continuous

1 x minute

X

X

Minimum scrubber liquor flow rate

Continuous

1 x minute

X

X

Minimum scrubber liquor pH

Continuous

1 x minute

X

X

9.	Reporting and Recordkeeping Requirements.

(a)	The owner or operator of an affected facility shall maintain the
following information (as applicable) for a period of at least 5 years:

(1)	Calendar date of each record;

(2)	Records of the following data:

(i)	Concentrations of any pollutant listed in paragraph 3 in Section 12
of these regulations or measurements of opacity as determined by the
continuous emission monitoring system (if applicable);

(ii)	Results of fugitive emissions (by EPA Reference Method 22) tests,
if applicable;

(iii)	HMIWI charge dates, times, and weights and hourly charge rates;

(iv)	Fabric filter inlet temperatures during each minute of operation,
as applicable;

(v)	Amount and type of dioxin/furan sorbent used during each hour of
operation, as applicable;

(vi)	Amount and type of Hg sorbent used during each hour of operation,
as applicable;

(vii)	Amount and type of HCl sorbent used during each hour of operation,
as applicable;

(viii)	Secondary chamber temperatures recorded during each minute of
operation;

(ix)	Liquor flow rate to the wet scrubber inlet during each minute of
operation, as applicable;

(x)	Horsepower or amperage to the wet scrubber during each minute of
operation, as applicable;

(xi)	Pressure drop across the wet scrubber system during each minute of
operation, as applicable;

(xii)	Temperature at the outlet from the wet scrubber during each minute
of operation, as applicable;

(xiii)	pH at the inlet to the wet scrubber during each minute of
operation, as applicable;

(xiv)	Records indicating use of the bypass stack, including dates,
times, and durations; and

(xv)	For affected facilities complying with subparagraphs 7(i) and 8(c)
in Section 12 of these regulations, the owner or operator shall maintain
all operating parameter data collected.

(3)	Identification of calendar days for which data on emission rates or
operating parameters specified under subparagraph (a)(2) of this
paragraph have not been obtained, with an identification of the emission
rates or operating parameters not measured, reasons for not obtaining
the data, and a description of corrective actions taken.

(4)	Identification of calendar days, times and durations of
malfunctions, a description of the malfunction and the corrective action
taken.

(5)	Identification of calendar days for which data on emission rates or
operating parameters specified under subparagraph (a)(2) of this
paragraph exceeded the applicable limits, with a description of the
exceedances, reasons for such exceedances, and a description of
corrective actions taken.

(6)	The results of the initial, annual, and any subsequent performance
tests conducted to determine compliance with the emission limits and/or
to establish operating parameters, as applicable.

(7)	Records showing the names of HMIWI operators who have completed
review of the information in subparagraph 4(i) as required by
subparagraph 4(j), including the date of the initial review and all
subsequent annual reviews;

(8)	Records showing the names of the HMIWI operators who have completed
the operator training requirements, including documentation of training
and the dates of the training;

(9)	Records showing the names of the HMIWI operators who have met the
criteria for qualification under paragraph 4 in Section 12 of these
regulations and the dates of their qualification; and

(10)	Records of calibration of any monitoring devices as required under
subparagraphs 8(a), (b), and (c) in Section 12 of these regulations.

(b)	The owner or operator of an affected facility shall submit the
information specified in subparagraphs (b)(1) through (b)(3) of this
paragraph no later than 60 days following the initial performance test.
All reports shall be signed by the facilities manager.

(1)	The initial performance test data as recorded under subparagraphs
7(b)(1) through (b)(11), as applicable.

(2)	The values for the site-specific operating parameters established
pursuant to subparagraphs 7(d) or (i), as applicable.

(3)	The waste management plan as specified in paragraph 5 in Section 12
of these regulations.

(c)	An annual report shall be submitted 1 year following the submission
of the information in subparagraph (b) of this paragraph and subsequent
reports shall be submitted no more than 12 months following the previous
report (once the unit is subject to permitting requirements in Air
Emissions Operating Permit Regulations for the Purposes of Title V of
the Federal Clean Air Act, APC-S-6, the owner or operator of an affected
facility must submit these reports semiannually).  The annual report
shall include the information specified in subparagraphs (c)(1) through
(c)(8) of this paragraph.  All reports shall be signed by the facilities
manager.

(1)	The values for the site-specific operating parameters established
pursuant to subparagraph 7(d) or (i), as applicable.

(2)	The highest maximum operating parameter and the lowest minimum
operating parameter, as applicable, for each operating parameter
recorded for the calendar year being reported, pursuant to subparagraph
7(d) or (i), as applicable.

(3)	The highest maximum operating parameter and the lowest minimum
operating parameter, as applicable for each operating parameter recorded
pursuant to subparagraph 7(d) or (i) for the calendar year preceding the
year being reported, in order to provide the Department with a summary
of the performance of the affected facility over a 2-year period.

(4)	Any information recorded under subparagraphs (a)(3) through (a)(5)
of this paragraph for the calendar year being reported.

(5)	Any information recorded under subparagraphs (a)(3) through (a)(5)
of this paragraph for the calendar year preceding the year being
reported, in order to provide the Department with a summary of the
performance of the affected facility over a 2-year period.

(6)	If a performance test was conducted during the reporting period, the
results of that test.

(7)	If no exceedances or malfunctions were reported under subparagraphs
(a)(3) through (a)(5) of this paragraph for the calendar year being
reported, a statement that no exceedances occurred during the reporting
period.

(8)	Any use of the bypass stack, the duration, reason for malfunction,
and corrective action taken.

(d)	The owner or operator of an affected facility shall submit
semiannual reports containing any information recorded under
subparagraphs (a)(3) through (a)(5) of this paragraph no later than 60
days following the reporting period.  The first semiannual reporting
period ends 6 months following the submission of information in
subparagraph (b) of this paragraph.  Subsequent reports shall be
submitted no later than 6 calendar months following the previous report.
 All reports shall be signed by the facilities manager.

(e)	All records specified under subparagraph (a) of this paragraph shall
be maintained onsite in either paper copy or computer-readable format,
unless an alternative format is approved by the Department.

(f)	Any small HMIWI subject to the emission limits in Table 2 of
paragraph 3 in Section 12 of these regulations shall meet the following
reporting and recordkeeping requirements:

(1)	Maintain records of the annual equipment inspections, any required
maintenance, and any repairs not completed within 10 days of an
inspection or the timeframe established by the Department; and

(2)	Submit an annual report containing information recorded under
subparagraph (f)(1) above no later than 60 days following the year in
which data were collected.  Subsequent reports shall be sent no later
than 12 calendar months following the previous report (once the unit is
subject to permitting requirements in Air Emissions Operating Permit
Regulations for the Purposes of Title V of the Federal Clean Air Act,
APC-S-6, the owner or operator must submit these reports semiannually).
The report shall be signed by the facilities manager.

10.	Compliance Schedules.

(a)	Except as provided in subparagraph (b), designated or affected
facilities to which the provisions in Section 12 of these regulations
applies (as defined in paragraph 1) shall comply with all requirements
in Section 12 of these regulations on or before September 15, 2000,
regardless of whether the Department has identified a designated or
affected facility in the State Plan inventory required by Subpart B of
40 C.F.R. 60.

(b)	For designated facilities planning to install the necessary air
pollution control equipment, the Department may allow compliance on or
before September 15, 2002, but as expeditiously as possible.  No later
than December 15, 1999, these facilities shall petition the Department
in writing, as outlined in subparagraphs (1) through (2) below.  Under
no circumstances can compliance with the provisions in Section 12 of
these regulations extend beyond September 15, 2002.

(1)	Documentation of the analyses undertaken to support the need for an
extension, including an explanation of why September 15, 2002, is
sufficient time to comply while September 15, 2000, is not sufficient.
The documentation shall also include an evaluation of the option to
transport the waste offsite to a commercial medical waste treatment and
disposal facility on a temporary or permanent basis; and

(2)	Documentation of measurable and enforceable incremental steps of
progress to be taken towards compliance with the requirements in Section
12 of these regulations, as defined in subparagraphs (i) through (x)
below:

(i)	Date for submitting a petition for site specific operating
parameters under subparagraph 7(i) in Section 12 of these regulations;

(ii)	Date for obtaining services of an architectural and engineering
firm regarding the air pollution control device(s);

(iii)	Date for obtaining design drawings of the air pollution control
device(s);

(iv)	Date for ordering the air pollution control device(s);

(v)	Date for obtaining the major components of the air pollution control
device(s);

(vi)	Date for initiation of site preparation for installation of the air
pollution control device(s);

(vii)	Date for initiation of installation of the air pollution control
device(s);

(viii)	Date for initial startup of the air pollution control device(s);
and

(ix)	Date for initial compliance test(s) of the air pollution control
device(s);

(x)	Date for final compliance.

(c)	Designated facilities planning to shut down permanently to
demonstrate compliance with subparagraph (a) of this paragraph shall
notify the Department in writing, no later than December 15, 1999.  The
notification shall include documentation of measurable and enforceable
incremental steps of progress to be taken towards compliance with the
requirements in Section 12 of these regulations, as defined in
subparagraphs (1) through (6) below:

(1)	Date for designated facility plan for shut down;

(2)	Date for contract with the appropriate vendor (off-site hauler or
alternative waste treatment equipment);

(3)	Date to begin construction of alternative waste treatment equipment
(if applicable);

(4)	Date for complete installation of alternative waste treatment
equipment (if applicable);

(5)	Date for shut down of incinerator;

(6)	Date for dismantling incinerator.

(d)	Department Actions on Petitions.  On receipt of a petition, the
Department will authorize one of the following actions, as it shall
determine:

(i)	The petition may be dismissed if the Department determines that it
is not adequate under subparagraph (b) of this paragraph.

(ii)	The Department may grant the request of the petition, as petitioned
or by imposing such conditions as the requirements in Section 12 of
these regulations may require in the Title V permit, including the
establishment of schedules of compliance.

(iii)	The Department may deny the petition.  If such a denial is made,
the Department shall notify the petitioner in writing, state the reasons
for denial and outline procedures for appeal.

(e)	Termination Procedures.  Any petition granted by the Department may
be terminated by the Department whenever the Department finds, after an
opportunity for the petitioner to demonstrate compliance and after
notice and an opportunity for hearing, that the petitioner is in
violation of any requirement, condition, schedule, limitation or any
other provision of the petition or that operation under the petition
does not meet the minimum requirements established by State and Federal
laws and regulations or is unreasonably threatening the public health.

SECTION 13. PROVISIONS FOR EXISTING COMMERCIAL AND INDUSTRIAL SOLID
WASTE INCINERATION UNITS

1.	Emission Standards. Provisions under this paragraph that apply to
existing commercial and industrial solid waste incineration (CISWI)
units are the requirements that are contained in 40 CFR 60.2575 through
60.2875. All such requirements are hereby adopted by reference by the
Commission as official regulations of the State of Mississippi and shall
hereafter be enforceable as such.

2.	Applicability. The requirements of Section 13 shall apply to each
existing commercial and industrial solid waste incineration unit that
commenced construction on or before November 30, 1999 and meets the
following criteria:

(a)	Commercial and industrial solid waste incineration (CISWI) unit
means any combustion device that combusts commercial and industrial
waste. The boundaries of a CISWI unit are defined as, but not limited
to, the commercial or industrial solid waste fuel feed system, grate
system, flue gas system, and bottom ash. The CISWI unit does not include
air pollution control equipment or the stack. The CISWI unit boundary
starts at the commercial and industrial solid waste hopper (if
applicable) and extends through two areas: (1) the combustion unit flue
gas system, which ends immediately after the last combustion chamber and
(2) the combustion unit bottom ash system, which ends at the truck
loading station or similar equipment that transfers the ash to final
disposal. It includes all ash handling systems connected to the bottom
ash handling system.

(b)	Commercial and industrial waste means solid waste combusted in an
enclosed device using controlled flame combustion without energy
recovery that is a distinct operating unit of any commercial or
industrial facility (including field-erected, modular, and custom built
incineration units operating with starved or excess air), or solid waste
combusted in an air curtain incinerator without energy recovery that is
a distinct operating unit of any commercial or industrial facility.

(c)	Solid waste means any garbage, refuse, sludge from a waste treatment
plant, water supply treatment plant, or air pollution control facility
and other discarded material, including solid, liquid, semisolid, or
contained gaseous material resulting from industrial, commercial,
mining, agricultural operations, and from community activities but does
not include solid or dissolved material in domestic sewage, or solid or
dissolved materials in irrigation return flows or industrial discharges
which are point sources subject to permits under Section 402 of the
Federal Water Pollution Control Act, as amended (42 U.S.C. 1342), or
source, special nuclear, or byproduct material as defined by the Atomic
Energy Act of 1954, as amended (42 U.S.C. 2014).

(d)	Solid waste combustion units are exempt from the requirements of
Section 13 as described and set forth below:

(1)	Pathological waste incineration units. Incineration units burning 90
percent or more by weight (on a calendar quarter basis and excluding the
weight of auxiliary fuel and combustion air) of pathological waste,
low-level radioactive waste, and/or chemotherapeutic waste as defined in
40 CFR 60.2875 are not subject to the requirements of Section 13 if the
owner or operator of the CISWI unit meets the two requirements specified
in (1)(i) and (ii) of this paragraph.